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Transcript of Projections of GHG emissions to 2030 in Tajikistan
Projections of GHG emissions to 2030 in Tajikistan
1
Prepared by:
Gauss International Consulting S.L.
María José López Blanco
Juan Luis Martín Ortega
Ioannis Sempos
With contributions from national experts:
Muzaffar Shodmonov
Firuz Saidov
Anvar Khamidov
Zafar Abdulhamidzoda
The findings, interpretations and conclusions expressed herein are entirely those of the authors and do not necessarily reflect the view of UNDP. UNDP cannot guarantee the accuracy of the data included in this work.
Copyright © UNDP 2020
United Nations Development Programme Tajikistan Ayni Street 39, Dushanbe, Tajikistan +992 44 600 5600
@UNDP_Tajikistan / @UNDPTJK / https://www.tj.undp.org
UNDP Tajikistan
Projections of GHG emissions to 2030 in Tajikistan
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Table of content
EXECUTIVE SUMMARY ......................................................................................................... 8
SECTION 1 - INTRODUCTION ................................................................................................ 8
1. BACKGROUND .................................................................................................................. 8
2. OBJECTIVES AND SCOPE OF THIS ASSIGNMENT .......................................................................... 9
3. STRUCTURE OF THE DOCUMENT ............................................................................................ 9
SECTION 2 - OVERALL METHODOLOGY ............................................................................... 10
1. APPROACH .................................................................................................................... 10
2. METHODOLOGICAL PRINCIPLES ........................................................................................... 10
SECTION 3 - CURRENT GHG EMISSION PROFILE ................................................................... 14
SECTION 4 - WITHOUT MEASURES SCENARIO ..................................................................... 18
1. METHODOLOGICAL APPROACH ........................................................................................... 19
1.1. PROJECTION OF ACTIVITY DATA ................................................................................................ 20
1.2. PROJECTION OF EMISSION FACTORS .......................................................................................... 22
1.3. PROJECTION OF EMISSION ....................................................................................................... 22
2. METHODOLOGY AND ASSUMPTIONS BY SECTOR ...................................................................... 23
2.1. ENERGY ................................................................................................................................ 23
1A1 Fuel combustion in Energy industries .................................................................................. 23
1A2 Fuel combustion in Manufacturing industries and construction ......................................... 23
1A3 Fuel combustion in transport ............................................................................................... 23
1A4 Other sectors ....................................................................................................................... 24
1B Fugitive emissions .................................................................................................................. 24
2.2. IPPU ................................................................................................................................... 24
Projections of GHG emissions to 2030 in Tajikistan
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2A Mineral Industry ..................................................................................................................... 24
2C3 Aluminium production ......................................................................................................... 25
2F Product Uses as Substitutes for Ozone Depleting Substances ............................................... 25
2.3. AFOLU ................................................................................................................................ 25
3A1 Enteric fermentation and 3A2 Manure Management Fuel combustion in Energy industries
..................................................................................................................................................... 25
3B1 Forest land ........................................................................................................................... 26
3B2 Cropland and 3B3 Grassland ................................................................................................ 26
3C3 Urea application, 3C4 Direct N2O Emissions from managed soils and 3C6 Indirect N2O
Emissions from manure management ........................................................................................ 26
3C7 Rice cultivation ..................................................................................................................... 26
2.4. WASTE................................................................................................................................. 26
4A Solid Waste Disposal .............................................................................................................. 26
4C Incineration and open burning of waste ................................................................................ 27
4D Wastewater treatment and discharge ................................................................................... 27
SECTION 5 - IMPLEMENTED AND ADOPTED MITIGATION ACTIONS ...................................... 28
1. ENERGY ........................................................................................................................ 28
1.1. REGIONAL POWER TRANSMISSION PROJECT ............................................................................... 28
1.2. GREEN ENERGY FACILITY PROJECT ............................................................................................ 31
1.3. OBIGARM-NUROBOD ROAD PROJECT........................................................................................ 33
1.4. KHATLON ENERGY LOSS REDUCTION PROJECT ............................................................................ 35
1.5. KHATLON PUBLIC TRANSPORT .................................................................................................. 36
1.6. QAIROKKUM HPP CLIMATE RESILIENCE UPGRADE ...................................................................... 38
1.7. GOLOVNAYA 240-MEGAWATT HYDROPOWER PLANT REHABILITATION PROJECT .............................. 40
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1.8. KULYAB-KHALAIKUMB ROAD ................................................................................................... 42
1.9. RECONSTRUCTION OF RAVSHAN ELECTRICITY SUBSTATION PROJECT (ISLAMIC DEVELOPMENT BANK)... 43
1.10. REGIONAL POWER TRANSMISSION .......................................................................................... 45
1.11. WHOLESALE METERING AND TRANSMISSION............................................................................ 47
1.12. REGIONAL: PROMOTING LOW-CARBON DEVELOPMENT IN CENTRAL ASIA REGIONAL ECONOMIC
COOPERATION PROGRAM CITIES ........................................................................................................ 48
1.13. REGIONAL CORRIDOR 1 ........................................................................................................ 49
1.14. REGIONAL CORRIDOR 2 ........................................................................................................ 50
1.15. REGIONAL CORRIDOR 3 ........................................................................................................ 51
1.16. REGIONAL ELECTRICITY TRANSPORT PROJECT ........................................................................... 52
1.17. NUREK HYDROPOWER REHABILITATION PROJECT ...................................................................... 53
1.18. DUSHANBE PUBLIC TRANSPORT ............................................................................................. 54
1.19. DUSHANBE PUBLIC TRANSPORT – KHUJAND BUSES .................................................................... 56
1.20. RURAL ELECTRIFICATION PROJECT .......................................................................................... 58
1.21. SUGD – ENERGY LOSS REDUCTION PROJECT ............................................................................. 60
1.22. LONG-TERM SMALL HYDRO POWER PLANT CONSTRUCTION PROGRAM ........................................ 61
1.23. SUSTAINABLE FUELS ............................................................................................................. 63
2. INDUSTRIAL PROCESSES AND PRODUCT USE ........................................................................... 65
3. AFOLU ........................................................................................................................ 66
3.1. LIVESTOCK AND PASTURE DEVELOPMENT PROJECT ...................................................................... 66
3.2. LIVESTOCK AND PASTURE DEVELOPMENT PROJECT II ................................................................... 70
3.3. PROJECT "SUPPORT TO AGRICULTURE IN THE COMMUNITY" ......................................................... 73
3.4. TAJIKISTAN AGRICULTURE COMMERCIALIZATION PROJECT ............................................................ 75
3.5. DANGARA VALLEY IRRIGATION PROJECT, PHASE III ...................................................................... 77
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3.6. TAJIKISTAN SECOND PUBLIC EMPLOYMENT FOR SUSTAINABLE AGRICULTURE AND WATER RESOURCES
MANAGEMENT PROJECT ................................................................................................................... 80
3.7. PROJECT "RECONSTRUCTION OF THE IRRIGATION SYSTEM AND IMPROVEMENT OF ITS MANAGEMENT IN
THE ZERAFSHAN RIVER BASIN" ........................................................................................................... 82
3.8. BUILDING CLIMATE RESILIENCE IN THE PYANJ RIVER BASIN PROJECT .............................................. 84
3.9. CLIMATE ADAPTATION AND MITIGATION PROGRAM FOR ARAL SEA BASIN CAMP4ASB ................... 86
3.10. CLIMATE ADAPTATION THROUGH SUSTAINABLE FORESTRY IN IMPORTANT RIVER CATCHMENT AREAS IN
TAJIKISTAN (CAFT) .......................................................................................................................... 88
3.11. IMPROVEMENT OF WATER RESOURCES MANAGEMENT IN KHATLON REGION PROJECT .................... 90
3.12. THE AGRICULTURE REFORM PROGRAMME OF THE REPUBLIC OF TAJIKISTAN FOR 2012-2020 .......... 92
3.13. PROGRAMME OF DEVELOPMENT OF BIOTECHNOLOGY OF CATTLE IN THE REPUBLIC OF TAJIKISTAN ..... 94
3.14. PASTURE DEVELOPMENT PROGRAM OF THE REPUBLIC OF TAJIKISTAN ........................................... 96
3.15. HORTICULTURE AND GRAPEVINE DEVELOPMENT PROGRAM........................................................ 99
3.16. STATE TARGET PROGRAM FOR THE DEVELOPMENT OF THE TRANSPORT COMPLEX OF THE REPUBLIC OF
TAJIKISTAN ................................................................................................................................... 102
3.17. DEVELOPMENT PROGRAM FOR SEED PRODUCTION OF THE REPUBLIC OF TAJIKISTAN ..................... 104
3.18. COMPREHENSIVE LIVESTOCK DEVELOPMENT PROGRAM ............................................................ 107
3.19. NATIONAL CLIMATE CHANGE ADAPTATION STRATEGY FOR THE PERIOD UP TO 2030 ..................... 112
3.20. THE STATE PROGRAM FOR THE DEVELOPMENT OF NEW IRRIGATED LAND AND THE RESTORATION OF
LAND THAT HAS BEEN ABANDONED FROM AGRICULTURAL CIRCULATION IN THE REPUBLIC OF TAJIKISTAN ...... 114
4. WASTE ....................................................................................................................... 116
4.1. SECOND DUSHANBE WATER SUPPLY PROJECT .......................................................................... 116
4.2. DUSHANBE WATER SUPPLY AND SANITATION PROJECT .............................................................. 118
4.3. KJUHAND WATER SUPPLY IMPROVEMENT PROGRAMME (PHASE III) ............................................ 120
4.4. NUREK WATER AND WASTEWATER PROJECT ............................................................................ 123
4.5. KULOB WATER AND WASTEWATER PROJECT ............................................................................ 125
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4.6. VAHDAT SOLID WASTE PROJECT............................................................................................. 127
4.7. YAVAN SOLID WASTE SUB-PROJECT ........................................................................................ 129
4.8. KULOB SOLID WASTE SUB-PROJECT ........................................................................................ 131
4.9. KHUJAND SOLID WASTE SUB-PROJECT .................................................................................... 133
4.10. RURAL WATER SUPPLY AND SANITATION PROJECT .................................................................. 135
4.11. KHOROG SOLID WASTE SUB-PROJECT ................................................................................... 136
4.12. TURSUN-ZADE SOLID WASTE ............................................................................................... 138
4.13. KURGAN-TYUBE SOLID WASTE ............................................................................................. 140
SECTION 6 - PLANNED MITIGATION ACTIONS ................................................................... 142
1. ENERGY ...................................................................................................................... 142
1.1. ROGUN HYDROPOWER PLANT ............................................................................................... 142
1.2. EBRD SUSTAINABLE ENERGY FINANCING FACILITIES .................................................................. 144
1.3. SCALING UP HYDROPOWER SECTOR CLIMATE RESILIENCE ........................................................... 146
1.4. INSTITUTIONAL DEVELOPMENT OF THE STATE AGENCY FOR HYDROMETEOROLOGY OF TAJIKISTAN ..... 148
2. INDUSTRIAL PROCESSES AND PRODUCT USE ......................................................................... 150
3. AFOLU ...................................................................................................................... 151
3.1. FOREST SECTOR DEVELOPMENT STRATEGY FOR 2016-2030 ...................................................... 151
3.2. CLIMATE ADAPTATION AND MITIGATION PROGRAM FOR THE ARAL SEA BASIN .............................. 154
3.3. BUILDING CLIMATE RESILIENCE OF VULNERABLE AND FOOD INSECURE COMMUNITIES THROUGH
CAPACITY STRENGTHENING AND LIVELIHOOD DIVERSIFICATION IN MOUNTAINOUS REGIONS OF TAJIKISTAN . 156
4. WASTE ....................................................................................................................... 158
SECTION 7 - MITIGATION OPTIONS ................................................................................... 159
1. ENERGY ...................................................................................................................... 159
1.1. ENERGY EFFICIENCY IN THE RESIDENTIAL/COMMERCIAL/INSTITUTIONAL SECTOR ............................. 159
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1.2. REDUCTION OF ELECTRICITY CONSUMPTION IN ALUMINIUM PRODUCTION...................................... 161
2. INDUSTRIAL PROCESSES AND PRODUCT USE ......................................................................... 164
2.1. REDUCTION OF CLINKER CONTENT OF CEMENT .......................................................................... 164
2.2. PHASE DOWN OF F-GASES ..................................................................................................... 166
3. AFOLU ...................................................................................................................... 167
3.1. ENHANCING REMOVALS BY CREATING NEW FRUIT ORCHARDS AND VINEYARDS ................................ 167
3.2. AGROFORESTRY AND / OR SILVO-PASTORAL SYSTEMS ................................................................. 169
3.3. MINIMAL OR NO TILLAGE/RESIDUE MANAGEMENT .................................................................... 171
3.4. IMPROVED AGRONOMIC PRACTICES THROUGH THE CONTINUATION OF THE DEVELOPMENT PROGRAM FOR
SEED PRODUCTION OF THE REPUBLIC OF TAJIKISTAN ............................................................................ 173
3.5. LIVESTOCK MANAGEMENT THROUGH THE CONTINUATION OF THE COMPREHENSIVE LIVESTOCK
DEVELOPMENT PROGRAM................................................................................................................ 176
3.6. FAT SUPPLEMENTATION IN RUMINANTS’ DIETS .......................................................................... 178
3.7. RICE CULTIVATION MANAGEMENT .......................................................................................... 180
3.8. CONTINUATION OF THE PASTURE DEVELOPMENT PROGRAMME AFTER 2020................................. 182
4. WASTE ....................................................................................................................... 184
4.1. REDUCTION OF OPEN BURNING .............................................................................................. 184
4.2. IMPROVED WASTEWATER MANAGEMENT PRACTICES .................................................................. 186
SECTION 8- WITH EXISTING MEASURES SCENARIO ............................................................ 189
SECTION 9 - WITH ADDITIONAL MEASURES SCENARIO ...................................................... 191
ANALYSIS OF THE FUTURE GHG EMISSION PROFILE AND MITIGATION OPTIONS AVAILABLE...................... 191
SECTION 10 – SUMMARY OF RESULTS .............................................................................. 194
SECTION 11 – SENSITIVITY OF THE ESTIMATES .................................................................. 196
SECTION 12 - CONCLUSIONS ............................................................................................. 199
Projections of GHG emissions to 2030 in Tajikistan
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Executive Summary
Introduction
The United Nations Framework Convention on Climate Change (UNFCCC) is an
international treaty whose overall objective is to “stabilise greenhouse gas (GHG)
concentrations in the atmosphere at a level that would prevent dangerous anthropogenic
interference”1 with the Earth’s climate system. Tajikistan became a Party to the UNFCCC
in 1992 and ratified the Convention on October 31, 1994.
The commitment for Parties to communicate to the Conference of Parties (COP)
information relating to the implementation of the Convention is guided by Articles 4 and
12 of the UNFCCC.
In accordance with Article 4, paragraph 1, each Party, taking into account their common
but differentiated responsibilities and their specific national and regional development
priorities, objectives and circumstances, shall, among other things, formulate,
implement, publish and regularly update national and, where appropriate, regional
programmes containing measures to mitigate climate change, and measures to facilitate
adequate adaptation to climate change.
Further, in accordance with Article 12, paragraph 1, each Party shall communicate to the
COP, through the secretariat in the form of a national communication, the following
elements of information:
a) A national inventory of anthropogenic emissions by sources and removals by sinks of
all GHGs not controlled by the Montreal Protocol, to the extent its capacities permit, using
comparable methodologies to be promoted and agreed upon by the COP;
b) A general description of steps taken or envisaged by the Party to implement the
Convention; and
i. Programmes containing measures to facilitate adequate adaptation to
climate change
ii. Programmes containing measures to mitigate climate change
1 “Article 2”. The United Nations Framework Convention on Climate Change. Retrieved 10 April, 2019.
Projections of GHG emissions to 2030 in Tajikistan
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c) Any other information that the Party considers relevant to the achievement of the
objective of the Convention and suitable for inclusion in its communication, including, if
feasible, materials relevant for calculation of global emission trends.
At COP 16 in Cancun in 2010, the Parties decided to enhance reporting in national
communications from non-Annex I Parties on national GHG inventories, mitigation
actions and their effects, and support received in a form of a Biennial Update Report
(BUR). BURs are intended to provide updates on actions undertaken by a Party to
implement the Convention, including the status of its greenhouse gas emissions and
removals by sinks, as well as on the actions to reduce emissions or enhance sinks, and
support needed and received to implement these actions.
In both National Communications and Biennial Update Reports Non-Annex I parties such
as Tajikistan need to report information on mitigation of climate change. This project
contributes to fulfilling the information provisions of the national communications, as it
assess the programmes and measures to mitigate climate change detailing the methods
used and results obtained, and provides information relevant to the BUR, as it provides
information on estimated emission reductions and methodologies and assumptions for
the mitigation actions involving direct GHG emission reductions.
With the ratification of the Paris Agreement in 2017, Tajikistan pledged its national
determined contribution, with conditional and unconditional mitigation objectives. The
two mitigation targets established in the NDC are:
1- without attracting new substantial international funding: not exceeding 80-90% of
the 1990 level by 2030, which amounts to 1.7-2.2 tons in CO2 equivalent per
capita
2- subject to new substantial international funding and technology transfer: a target
of 65-75% of the 1990 level by 2030, which amounts to 1.2-1.7 tons in CO2
equivalent per capita.
The NDC specified that the scope of these targets includes the following activities:
Power industry and water resources;
Industry and construction;
Land use, agriculture and gardening and grazing;
Forestry and biodiversity; and
Transportation and infrastructure.
In this regard, this assignment allows Tajikistan to assess its programs and measures
implemented or planned that result in the mitigation of human-induced climate change
and progress in achieving its NDC. The assignment also allows Tajikistan to identify
additional mitigation alternatives that could be implemented in the country in the
future, that could be considered in a potential review of the NDC.
Projections of GHG emissions to 2030 in Tajikistan
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Overall Methodology
The overarching working principles followed in the projection of GHG emissions are
the following:
The projections are consistent with the GHG emissions of the historical period.
The nomenclatures and good practice of 2006 IPCC Guidelines have been
followed for estimating projections.
The differences between scenarios are only explained by the impact of mitigation
actions or mitigation options.
The projections are consistent with the overall macroeconomic framework of the
country, defined in the National Development Strategy.
The lack of information has been addressed with assumptions made by the
working team and validated by national experts.
All the working files generated during project have been provided aiming at
facilitating future updates of the work.
The guiding principle for the development of this report is transparency. Thence,
the data used, methodologies applied, and results obtained are provided at a
detailed breakdown to facilitate the understanding of the work developed.
All the developments made have been validated by national stakeholders.
Following these principles is essential for ensuring the results of the GHG emissions
projections are robust and consistent for assessing mitigation trends and tracking
progress towards the achievement of the NDC.
Approach
The project started with a first workshop to present the project to the main climate change
stakeholders of the country. This first workshop was used to engage with the
stakeholders and to start the data gathering process and was followed by a set of bilateral
interviews to facilitate the data gathering. The information raised during the inception
workshop and these bilateral interviews was the foundation for the development of the
GHG emission projections.
From a technical point of view, the project started with the identification of mitigation
actions implemented, under implementation and planned in the country and with the
estimation of a “Without Measures Scenario” using the national GHG emission inventory
as a reference. This scenario does not take into account the implementation of any
mitigation action but is projected considering the main macroeconomic perspectives of
the county.
All mitigation actions identified were assessed by the working team to obtain the impact
in terms of GHG emissions reductions due to their implementation. Once the assessment
of mitigation actions implemented, under implementation and planned was completed,
additional mitigation alternatives (mitigation options) were identified and assessed by
Projections of GHG emissions to 2030 in Tajikistan
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IPCC sector. All mitigation actions and additional options assessed were used to develop
GHG emissions scenarios.
The results of this project were validated by national stakeholders.
The project also included a capacity building program, which involved the development
of a set of videos on the development of GHG emission projections using the tools which
have been developed under the project.
Figure. Methodological approach for the implementation of the project.
The following paragraphs provide key insights on the main methodological steps followed
to estimate the GHG emission projections of Tajikistan.
Estimating a Without Measures (WoM) scenario
The Without Measures Scenario is estimated from the emissions of years 2004-2016
(i.e. the GHG emissions inventory2) using national forecasts for 2016 to 2030,
assumptions on the evolution of the key parameters and basic statistical techniques. This
scenario does not consider specifically the impact of any mitigation action under
implementation since 2015.
2 The GHG emission inventory has been adjusted for improving its completeness aiming at providing exhaustive GHG emission scenarios.
Projections of GHG emissions to 2030 in Tajikistan
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From the methodology and emissions estimated in the WoM, the different policy
scenarios (With Existing Measures scenario and With Additional Measures Scenario)
were estimated by subtracting the impact of mitigation policies and options to the
corresponding sector.
What mitigation policies and mitigation options do we consider in each
scenario?
Not all mitigation actions implemented in the country have been considered in this GHG
emission mitigation assessment. The criteria for selecting mitigation actions is the
following:
The mitigation action is under implementation in or after year 2015. This also
includes actions which are planned to be implemented in the future.
The mitigation action involves direct GHG emission reductions (studies or
feasibility projects have not been assessed)
It is not just a good idea or intention reflected in a policy/strategy, but it is a real
action to be implemented with GHG emissions associated.
There is no double counting with other mitigation actions assessed. For instance,
if a project to install a solar plant is included in a strategy to increase solar
generation capacity is estimated at the national level.
The mitigation actions are not only projects implemented, but also plans which are
described within general policy frameworks. Policy frameworks are not necessarily
mitigation actions. They include overall objectives and strategic lines to follow that,
sometimes, are not translated into real lines of action. Thence, it is important to highlight
that this GHG mitigation assessment has not included aspirational objectives which are
not translated into lines of action. The policy frameworks evaluated for identifying
mitigation actions are the following:
National Development Strategy of the Republic of Tajikistan for the period up to
2030
National Climate Change Adaptation Strategy
Water Sector Reform Program of the Republic of Tajikistan
Program for providing the population with clean drinking water
Development Program for Housing and Public Utilities of the Republic of
Tajikistan
State Target Program for the Development of the Transport Complex of the
Republic of Tajikistan
Agricultural Reform Programme of the Republic of Tajikistan
Pasture Development Program of the Republic of Tajikistan
Strategy for the development of industry in the Republic of Tajikistan
Projections of GHG emissions to 2030 in Tajikistan
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The state program for the development of new irrigated land and the restoration
of land that has been abandoned from agricultural circulation in the Republic of
Tajikistan
Comprehensive livestock development program
State environmental program
Power Sector Development Master Plan
These policies, strategies and programmes led to the implementation of various
mitigation actions in line with the main objectives established in them.
Nevertheless, in the context of this assignment, several of these strategies have been
directly considered in the different emission scenarios. This is the case, for instance, for
the “Forest Sector Development Strategy for 2016-2030”, for which a direct GHG
emission impact for its implementation has been estimated.
Regarding the scenarios, we have selected mitigation actions and mitigation options for
showing the mitigation effort made since 2015 (the implementation of the NDC), the effort
which is planned to be made in the future and the possibilities to make further effort to
raise the mitigation ambition of the country. With this idea, several scenarios have been
designed:
Table. Mitigation actions and mitigation options included in the scenarios
Mitigation actions and options included WoM WeM WaM
Mitigation actions implemented/finished after
2015
× ×
Mitigation actions adopted after 2015 × ×
Mitigation actions planned ×
Mitigation options (additional) ×
With Existing Measures (WeM) Scenario: This policy scenario is built from the WoM
considering the effect of mitigation actions under implementation since 2015. This
includes mitigation actions that were adopted after 2015 but their implementation not yet
finalized.
With Additional Measures (WaM) Scenario: This policy scenario is built from the WeM
considering the mitigation actions planned to be implemented in the future and the impact
of the main mitigation options identified additionally to the previous actions. This policy
scenario represents the maximum GHG emission level that Tajikistan could achieve with
the implementation of the key mitigation alternatives available.
How is the mitigation impact of the mitigation actions assessed?
Three steps are followed for estimating the mitigation impact of actions:
1. Identify the IPCC category or categories affected by the mitigation action.
Projections of GHG emissions to 2030 in Tajikistan
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2. With the information available regarding the scope of the action, evaluate how
the mitigation action impact the activity data and/or emission factors of the
emissions estimated in the WoM.
3. Design an estimation method for obtaining the overall impact of the mitigation
action. Overall, there are two types of estimation methods for estimating the
mitigation impact:
A) Estimate the GHG emissions in two scenarios for the mitigation action:
a reference scenario and a reduction scenario. The impact of the action
is then calculated as GHG Emissions in the reference scenario minus
the GHG emissions in the reduction scenario.
The reference scenario is ideally consistent with the WoM, and only
considers the activity data affected by the mitigation action. It represents
the technology and process in place before policy implementation.
The reduction scenario includes an estimation of the emissions of the
new situation, after policy implementation. Assumption are often needed
on the scope and the new technology/process implemented.
B) Estimate directly the mitigation impact of the action, i.e. the GHG
emissions reduction applicable to the change produced by the
implementation of the mitigation action. In these cases, only the
difference between the scenarios for mitigation action (reference and
reduction scenarios) is estimated.
Methodology
This project follows the nomenclature, good practices and allocation of emissions
specified in the 2006 IPCC Guidelines.
The global warming potentials used for the calculation of the total GHG emissions are
those used in the NDC, i.e. the GWP of the IPCC Fourth Assessment Report (AR4). The
decision about the GWP was made aiming at achieving consistency with the NDC, as
AR4 GWP were used in the NDC of Tajikistan.
Current GHG emission profile
The following table shows the detailed GHG emissions at category level, to provide a
better understanding of the mitigation possibilities from the current GHG emission level:
Table. Breakdown of GHG emissions in Tajikistan
IPCC Category 2004 2010 2015 2016
Energy
1A1 Energy Industries 283 251 1,099 1,736
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IPCC Category 2004 2010 2015 2016 1A2 Manufacturing industries and
construction 488 392 260 309
1A3 Transport 408 256 255 149
1A4 Commercial/residential/institutional 2,835 484 2,166 1,239
1B1 Fugitive emissions from solid fuels 2 5 25 33 1B2 Fugitive emissions from oil and natural
gas 29 41 37 38
IPPU
2A Mineral Industry 118 177 744 1,032
2C Metal Industry 1,806 1,761 702 652
2F Product Uses as substitutes for ODS 237 267 300 307
AFOLU
3A1 Enteric fermentation 2,370 3,485 4,053 4,173
3A2 Manure management 476 690 793 818
3B Land -1,461 -1,512 -1,591 -1,598 3C Aggregate sources and non-CO2
emissions sources on land 572 555 678 611
Waste
4A Solid waste disposal 163 218 259 266
4C Incineration and open Burning 403 452 510 522
4D Wastewater treatment and discharge 533 576 650 666
Total 9,263 8,097 10,942 10,953
Note – The categories/emission sources with no emissions estimated in the historical
period have not been included in this table.
The analysis of the emissions estimated in the historical period at category level
(illustrated in the previous table) is essential to understand the GHG emission projections
estimated and the mitigation potential of the country.
The largest contributor to historical period GHG emissions is enteric fermentation
(IPCC sub-category 3A1), with a contribution that ranges from a 25.6 per cent in 2004 to
a 38.1 per cent of national total emissions in year 2016. The increasing contribution of
this sub-category is driven by the growing population of cattle, which increased by a 95.8
per cent in the period 2004-2016. This is also the reason for the growing emissions from
manure management, that contributed with a 7.5 per cent to national total GHG
emissions in 2016.
The second contributing activity to national total GHG emissions is energy industries
(IPCC sub-category 1A1), with an increasing share that reached a 15.9 per cent of
national total emissions in 2016, from only 3.1 per cent in 2004. This increasing trend is
explained by the commissioning of a new power plant in Dushanbe in year 2014, which
reduced energy shortages but significantly increased anthracite consumption and GHG
emissions.
The carbon stock changes which occurred as a result of land use change and forestry
activities (IPCC category 3B) leaded to steady CO2 removals from the atmosphere,
within the range 14.6-18.7 per cent of national total GHG emissions in the period 2004-
Projections of GHG emissions to 2030 in Tajikistan
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2016. This contribution makes this category the third largest contributor to Tajikistan
GHG emissions in the historical period.
Fuel consumption in the residential, commercial, and institutional sectors (IPCC
sub-category 1A4) is shown as the fourth largest contributor to national total GHG
emissions, with a decreasing contribution from 30.6 per cent in 2004 to a 11.3 per cent
in 2016. This decrease is explained by a sharp reduction of natural gas consumption,
which was partially covered by anthracite consumption in these sectors, specially from
year 2014.
The activity levels of the mineral industry (IPCC category 2A) raised substantially in the
historical period, leading this category to reach a 9.4 per cent of national total GHG
emissions in 2016. This increase is explained by the abrupt grow of clinker production
levels due to the commissioning of new production plants in years 2014-2016.
Emissions from solid waste management systems, represented in categories 4A solid
waste disposal and 4C incineration and open burning represented a 7.2 per cent of
national total emissions in 2016, with slight variations in the historical time series. The
emissions from solid waste are driven by the number of population, as the waste
generation rate is assumed to remain constant in this period.
The remaining emission categories and subcategories of Tajikistan have lower
contribution to national total GHG emissions. Nevertheless, these other sources together
account for a 25.2 per cent of national total GHG emissions in 2016. Sources with
significant GHG emissions within this group includes industry emissions within
categories 2C Metal Industry, 4D Wastewater treatment and discharge and 1A2
Manufacturing industries and construction.
Projecting national GHG emissions – the Without Measures
Scenario
The Without Measures Scenario (WoM) represents the GHG emissions of Tajikistan with
no changes in the circumstances of the latest year for which observed information is
available, i.e. 2016. In the context of our assignment, this means that this scenario does
not consider the future mitigation impact of any mitigation action under implementation
after 2015. Nevertheless, the GHG emissions estimated for the historical period might be
influenced by the impact of mitigation actions implemented before 2015; the effect of
these mitigation actions is thus which is already incorporated in the observed in years
2004-2015. This impact is estimated from year 2015 within the policy scenarios.
The estimation of the WoM scenario is the key methodological step for obtaining
national total GHG emission projections. The other policy scenarios considering different
degree of policy implementation (the WeM and WaM scenarios) are calculated from the
WoM considering the mitigation impact estimated for the different mitigation actions and
mitigation options identified.
Projections of GHG emissions to 2030 in Tajikistan
17
The WoM is projected relying on available forecasts that explain the future context of the
country, such as GDP, population, or electricity demand. The methodological details of
the projections, data used, and results obtained are detailed in this section. The summary
of the GHG emissions obtained is illustrated in the following figure.
Figure. GHG emission projections by scenario and NDC targets of Tajikistan (Gg
CO2-eq)
The GHG emission profile of the country remains relatively stable in the WoM. In line
with the GDP forecast of the Industrial scenario of the National Development Strategy,
the contribution of agriculture to national total emissions is reduced, while the Energy
and IPPU emissions increase its contribution. The contribution of the Waste and FOLU
sectors are also slightly reduced.
The emissions from the national GHG emission inventory (time series 2004-2016) have
been generally projected differentiating between activity data and emission factors
following the basic IPCC 2006 equation for GHG emission calculation, as follows
1 𝐸𝑚𝑖𝑠𝑠𝑖𝑜𝑛𝑠𝑐,𝑔,𝑡 = 𝐴𝐷𝑐,𝑡 ∙ 𝐸𝐹𝑐,𝑔,𝑡
Where
𝐸𝑚𝑖𝑠𝑠𝑖𝑜𝑛𝑠𝑐,𝑔,𝑡 = 𝑒𝑚𝑖𝑠𝑠𝑖𝑜𝑛𝑠 𝑜𝑓 𝑐𝑎𝑡𝑒𝑔𝑜𝑟𝑦 𝑐, 𝑔𝑎𝑠 𝑔 𝑎𝑛𝑑 𝑦𝑒𝑎𝑟 𝑡
𝐴𝐷𝑐,𝑡 = 𝑎𝑐𝑡𝑖𝑣𝑖𝑡𝑦 𝑑𝑎𝑡𝑎 𝑜𝑓 𝑐𝑎𝑡𝑒𝑔𝑜𝑟𝑦 𝑐, 𝑦𝑒𝑎𝑟 𝑡
𝐸𝐹𝑐,𝑔,𝑡 = 𝐸𝑚𝑖𝑠𝑠𝑖𝑜𝑛 𝑓𝑎𝑐𝑡𝑜𝑟 𝑜𝑓 𝑒𝑚𝑖𝑠𝑠𝑖𝑜𝑛𝑠 𝑜𝑓 𝑐𝑎𝑡𝑒𝑔𝑜𝑟𝑦 𝑐, 𝑔𝑎𝑠 𝑔 𝑎𝑛𝑑 𝑦𝑒𝑎𝑟 𝑡
Projections estimates have been performed at the highest disaggregation level available
in the inventory. The projection of the activity data of the inventory is driven by different
factors, such as the level of activity (production, population or energy demand, among
others), while the evolution of the emission factors is driven by other factors such as
technology.
In the cases where complex methodologies are used by the inventory, the same
methodology has been used for projections. In the cases were the same methodology
could not be used, the implied emission factor and the most representative activity data
series have been used for projecting.
Projections of GHG emissions to 2030 in Tajikistan
18
The projections of the activity data have been done using different methods, depending
of the nature of the variables and its temporal evolution. In certain occasions, proxies
(the variables shown in previous table) can be used for projecting the activity data.
However, this is not always possible. The following are the type methods that have
been used for projecting the activity data of the inventory:
[1] Using the value of the latest inventory year or any arithmetic calculation.
Applying a growing rate
1) A specific growing rate [2a]
𝐴𝑐𝑡𝑖𝑣𝑖𝑡𝑦 𝑑𝑎𝑡𝑎𝑡 = 𝐴𝑐𝑡𝑖𝑣𝑖𝑡𝑦 𝑑𝑎𝑡𝑎𝑡−1 ∙ 𝐺𝑟𝑜𝑤𝑖𝑛𝑔 𝑟𝑎𝑡𝑒𝑡
2) The same growing rate of a correlated proxy [2b]
𝐴𝑐𝑡𝑖𝑣𝑖𝑡𝑦 𝑑𝑎𝑡𝑎𝑡 = 𝐴𝑐𝑡𝑖𝑣𝑖𝑡𝑦 𝑑𝑎𝑡𝑎𝑡−1 ∙ 𝑃𝑟𝑜𝑥𝑦𝑡
𝑃𝑟𝑜𝑥𝑦𝑡−1
Using linear regression models with proxies [3]
𝐴𝑐𝑡𝑖𝑣𝑖𝑡𝑦 𝑑𝑎𝑡𝑎𝑡 =∝ + 𝛽 ∙ 𝑃𝑟𝑜𝑥𝑦𝑡
The technological and process conditions and characteristics remain unchanged
(constant) in the projected period. Therefore, the projection of emission factor in the WoM
scenario is generally made using the latest emission factor value of the inventory. The
emission factors used are all default IPCC 2006 emission factors, as used in the national
GHG emissions inventory.
List of mitigation actions assessed
The following table shows the list of mitigation actions which have been assessed in this
assignment, specifying the scenario where they are included.
Name of the action Status of
implementation
Mitigation
Scenario
Annual
Mitigation
Impact by
2030 (CO2-
eq)
Tajikistan: Regional Power Transmission Project
(ADB) Implemented/Finished WeM 11.71
Tajikistan Green Energy Facility (EBRD) Adopted/ongoing WeM 7.01
Obigarm-Nurobod road project (EBRD) Adopted/ongoing WeM NA
Khatlon Energy Loss Reduction Project (EBRD) Adopted/ongoing WeM IE
Khatlon Public Transport (EBRD) Adopted/ongoing WeM 0.12
Qairokkum HPP Climate Resilience Upgrade
(EBRD) Implemented/Finished WeM 0.60
Projections of GHG emissions to 2030 in Tajikistan
19
Name of the action Status of
implementation
Mitigation
Scenario
Annual
Mitigation
Impact by
2030 (CO2-
eq)
Tajikistan: Golovnaya 240-Megawatt Hydropower
Plant Rehabilitation Project (ADB) Adopted/ongoing WeM 0.23
Construction of Kulyab-Khalaikumb Road,
Sections A and F (Kulyab-Shurobad and Shkev-
Kalaikhumb) (Islamic Development Bank)
Implemented/Finished WeM NA
Reconstruction of Ravshan Electricity Substation
Project (Islamic Development Bank) Implemented/Finished WeM NA
Tajikistan: Regional Power Transmission Project
(ADB) Implemented/Finished WeM NA
Tajikistan: Wholesale Metering and Transmission
Reinforcement Project (ADB) Implemented/Finished WeM NA
Regional: Promoting Low-Carbon Development in
Central Asia Regional Economic Cooperation
Program Cities (ADB)
Adopted/ongoing WeM NA
Tajikistan: Central Asia Regional Economic
Cooperation Corridors 2, 5, and 6 (Dushanbe-
Kurgonteppa) Road Project - Additional Financing
(ADB)
Adopted/ongoing WeM NA
Tajikistan: Central Asia Regional Economic
Cooperation Corridors 2, 5, and 6 (Dushanbe–
Kurgonteppa) Road Project (ADB)
Adopted/ongoing WeM NA
Tajikistan: Central Asia Regional Economic
Cooperation Corridors 3 and 5 Enhancement
Project (ADB)
Implemented/Finished WeM NA
Regional Electricity Transport Project (CASA -
1000) (EBRD) Planned WeM NA
Nurek Hydropower Rehabilitation Project, Phase 1
(WB) Adopted/ongoing WeM IE
Dushanbe Public Transport (EBRD) Adopted/ongoing WeM 0.00
Khujand Public Transport Project (EBRD) Adopted/ongoing WeM 0.00
Rural Electrification Project (WB) Adopted/ongoing WeM 0.43
Sugd - Energy Loss Reduction project (EBRD) Implemented/Finished WeM IE
Long-Term Small Hydro Power Plant Construction
Program Implemented/Finished WeM 1.50
State Target Program for the Development of the
Transport Complex of the Republic of Tajikistan -
Sustainable fuels
Adopted/ongoing WeM 10.58
Strategy for the development of industry in the
Republic of Tajikistan Adopted/ongoing WeM NA
Livestock and Pasture Development Project (IFAD) Implemented/Finished WeM 14.65
Livestock and Pasture Development Project II
(IFAD) Adopted/ongoing WeM 18.12
Project "Support to Agriculture in the Community"
(IFAD) Adopted/ongoing WeM NA
Agriculture Commercialization Project (WB) Adopted/ongoing WeM NA
Dangara Valley Irrigation Project, Phase III (Islamic
Development Bank) Implemented/Finished WeM 0.64
Tajikistan second public employment for
sustainable agriculture and water resources
management project (WB)
Implemented/Finished WeM 92.23
Projections of GHG emissions to 2030 in Tajikistan
20
Name of the action Status of
implementation
Mitigation
Scenario
Annual
Mitigation
Impact by
2030 (CO2-
eq)
Project "Reconstruction of the irrigation system and
improvement of its management in the Zerafshan
River Basin" (WB)
Adopted/ongoing WeM 7.70
«Building Climate Resiliense in the Pyanj River
Basin Project» (ADB) Implemented/Finished WeM 0.53
Improvement of Water Resources Management in
Khatlon Region Project (Islamic Development
Bank)
Implemented/Finished WeM 1.23
Zarafshon Irrigation Rehabilitation and
Management Improvement Project (WB) Implemented/Finished WeM NA
Climate Adaptation and Mitigation Program for Aral
Sea Basin CAMP4ASB(WB) Adopted/ongoing WeM NA
Climate Adaptation through Sustainable Forestry in
Important River Catchment Areas in Tajikistan
(CAFT) - German Development Bank
Implemented/Finished WeM 89.96
Agricultural Reform Programme of the Republic of
Tajikistan Implemented/Finished WeM NA
Programme of development of biotechnology of
cattle in the Republic of Tajikistan Implemented/Finished WeM NA
Pasture Development Program of the Republic of
Tajikistan Adopted/ongoing WeM 0.25
Horticulture and Grapevine Development Program Implemented/Finished WeM 122.35
State Target Program for the Development of the
Transport Complex of the Republic of Tajikistan -
Land use and afforestation
Adopted/ongoing WeM 2.27
Development Program for Seed Production of the
Republic of Tajikistan Implemented/Finished WeM 33.06
The state program for the development of new
irrigated land and the restoration of land that has
been abandoned from agricultural circulation in the
Republic of Tajikistan
Implemented/Finished WeM 9.79
Comprehensive livestock development program Adopted/ongoing WeM 14.02
State environmental program Implemented/Finished WeM NA
Forest Sector Development Strategy for 2016-2030 Planned WaM 353.15
Second Dushanbe Water Supply Project (WB) Implemented/Finished WeM NA
Tajikistan: Dushanbe Water Supply and Sanitation
Project (ADB) Adopted/ongoing WeM 23.57
Khujand Water Supply Improvement Programme
(Phase III) - EBRD Implemented/Finished WeM 15.23
Nurek Water and Wastewater Project (EBRD) Implemented/Finished WeM 0.10
Kulob Water and Wastewater Project (EBRD) Adopted/ongoing WeM 8.02
Vahdat Solid Waste Project (EBRD) Adopted/ongoing WeM 1.49
Yavan Solid Waste Sub-project (EBRD) Adopted/ongoing WeM 0.90
Kulob Solid Waste Sub-project (EBRD) Implemented/Finished WeM 3.71
Khujand Solid Waste Sub-project (EBRD) Implemented/Finished WeM 7.04
Rural Water Supply and Sanitation Project (WB) Adopted/ongoing WeM NA
Khorog Solid Waste Sub-Project (EBRD) Implemented/Finished WeM 1.55
Tursun-Zade Solid Waste (EBRD) Implemented/Finished WeM 2.01
Kurgan-Tyube Solid Waste (EBRD) Implemented/Finished WeM 4.15
Projections of GHG emissions to 2030 in Tajikistan
21
Name of the action Status of
implementation
Mitigation
Scenario
Annual
Mitigation
Impact by
2030 (CO2-
eq)
State Target Program for the Development of the
Transport Complex of the Republic of Tajikistan Adopted/ongoing WeM NA
Power Sector Master Plan - Construction of Rogun
HPP Planned WaM 67.62
EBRD Sustainable Energy Financing Facilities Planned WaM NA
Scaling Up Hydropower Sector Climate Resilience Planned WaM IE
Institutional Development of the State Agency for
Hydrometeorology of Tajikistan Planned WaM NA
Climate Adaptation and Mitigation Program for the
Aral Sea Basin Planned WaM NA
Building Climate Resilience of Vulnerable and
Food Insecure Communities through Capacity
Strengthening and Livelihood Diversification in
Mountainous Regions of Tajikistan
Planned WaM NA
NA – Not applicable. The mitigation impact could not be estimated due to either the lack of information or
the characteristics of the mitigation action
IE – the impact of the action is included in other mitigation action
The previous table is limited to the actions which are implemented, under implementation
or planned in the country, i.e. the additional mitigation actions which have been identified
are not included in this table.
Projections of GHG emissions to 2030 in Tajikistan
22
Summary of Results
The following figure illustrate the GHG emission projections of Tajikistan up to 2030
under the WoM, WeM and WaM scenarios. These GHG emission projections are in line
with the macroeconomic framework projected in the National Development Strategy to
2030 for the industrial scenario3.
Figure. GHG emission projections by scenario and NDC targets of Tajikistan (Gg
CO2-eq)
The GHG emissions of the WoM will growth an average of 3.3 per cent by year in the
period 2016-2030, compared to the 6 per cent annual growth of GDP and the 2.1 per
cent annual growth of population. The projection of the WoM has been developed at
category level, considering the different determinant of each emission source.
The GHG emission projections estimated in the WoM are below the unconditional
mitigation target set in the NDC for 2030, without considering the impact of any mitigation
action. The unconditional NDC objective is defined as 80-90% of the 1990 emission
levels, i.e. 20,400 Gg emissions of CO2-eq for year 2020.
However, WoM emissions are above the conditional mitigation target defined in the NDC,
which is defined as a 65-75% of the 1990 level by 2030, ie. 16,575 Gg emissions of CO2-
eq for the lower range.
3 Three scenarios are considered in the National Development Strategy, an inertial scenario, an industrial scenario and an innovative scenario. The inertial scenario is not relevant for this type of exercise. The innovative scenario assumes a structural change in the economy which is not feasible with the existent policy framework. The industrial scenario assumes that the economy reduces the weight of agriculture, shifting to a more industrial intensive economy. This is in line with national policies and programmes, such as the “Strategy for the development of industry in the Republic of Tajikistan”. For this reason, the industrial scenario has been chosen as a core for this GHG emissions projections.
Projections of GHG emissions to 2030 in Tajikistan
23
The absolute levels for the NDC targets mentioned in the previous paragraph are
calculations which considered that the emissions of year 1990 were 25,500 Gg CO2-eq.
Nevertheless, the GHG emissions of year 1990 have not been re-calculated with the
methodology used in this exercise, so the absolute value for the NDC target can only be
seen as an approximate value. For this reason, it would be recommendable that
Tajikistan either recalculates its 1990 emissions or sets a new NDC target using a more
recent year (for instance, 2010 or 2015).
Considering the effect of the main projects and programmes implemented or adopted in
the country, Tajikistan will not meet its conditional NDC target, as these mitigation actions
have a limited mitigation impact in terms of GHG emissions (this impact is considered in
the WeM scenario). The mitigation actions which showed higher mitigation impact in the
country are the following:
Horticulture and Grapevine Development Program. The estimated mitigation impact
for this action in 2030 is 122 Gg CO2-eq.
Second public employment for sustainable agriculture and water resources
management project. The estimated mitigation impact for this action in 2030 is 92
Gg CO2-eq.
Climate Adaptation through Sustainable Forestry in Important River Catchment
Areas in Tajikistan (CAFT). The estimated mitigation impact for this action in 2030
is 90 Gg CO2-eq.
The aggregated impact of all implemented or adopted actions is 507 Gg CO2-eq by 2030.
The impact of these actions is shown in the WeM scenario.
Given the modest mitigation impact of these actions, Tajikistan will require to implement
additional mitigation actions for achieving its conditional NDC target.
Tajikistan is already making efforts to further reduce its GHG emissions in the future and
is planning the future implementation of substantial mitigation initiatives. This is the case
of the Forest Sector Development Strategy, which is not yet adopted, but has an
estimated mitigation impact of 353 Gg CO2-eq by 2030. This is also the case for the
commissioning of the Rogun Hydroelectricity power plant, which is undergoing and is
expected to finalised by 2026. The effect of this strategy and the commissioning of the
Rogun Hydroelectricity power plant are included in the WaM scenario, together with
additional mitigation actions with potential to reduce GHG emission which have been
identified in the framework of this project. As shown in the figure above, the
implementation of all actions included in the WaM scenario, for which the country will
need substantial international support, will allow Tajikistan to significantly reduce its
emissions by 2030, reaching its conditional NDC target.
Analysis of the future GHG emission profile and mitigation
options available
Projections of GHG emissions to 2030 in Tajikistan
24
In the energy sector, the greatest mitigation potential is found in the energy industries
and in the residential, commercial and institutional sectors, the areas producing the
largest GHG emissions in both the historical and projected (i.e. in the WoM) periods
within this sector.
In energy industries, the high levels of installed hydroelectric capacity limits the current
GHG emissions of the electricity sector. Future GHG emissions in energy industries
depend on the finalization of the Rogun Hydropower plant. This power plant will
represent an addition of 3,600 MW to the electricity generation capacity of the country,
limiting the need of fossil fuel generation for meeting national electricity demand.
Conversely, if this plant is not finally commissioned, additional fossil generation capacity
will be needed to avoid shortages in the winter period. This will also involve significantly
higher GHG emissions in the energy sector (as represented in the WoM scenario).
Notwithstanding the foregoing, the greatest mitigation opportunity identified for the
energy sector is in the residential, commercial, and institutional sector. The use of coal
(anthracite) in these sectors is one of the biggest emission sources of the inventory. The
replacement of boilers, kitchens and stoves using coal for equivalent electric appliances
will significantly reduce the emissions of these emission sources. Complementarily,
energy efficiency measures to reduce energy consumption could be also considered to
reduce the contribution of these sector to national GHG emissions.
Aluminium production is one of the key industries operating in Tajikistan and is highly
energy intensive. The reduction of the energy intensity in the production of aluminum
through the incentive of secondary aluminum production practices is another possibility
to reduce the GHG emissions of the energy sector significantly. The promotion of Best
Available Techniques4 in the industry will reduce the energy consumption requirements
of the industry, limiting its GHG emissions. Tajikistan should consider addressing this
issue in the framework of its Strategy for the development of industry in the Republic of
Tajikistan, by including specific actions for future implementation.
The transport sector has a limited contribution to energy sector GHG emissions.
However, the transport sector is an essential sector for the development of the country,
and it should be considered in the core of the mitigation strategy of the country.
Continuing the renovation of the public transport infrastructure and providing incentives
to stimulate its use should be a priority for the climate change action of the country in the
future.
Industrial processes and product use emissions (IPPU) are dominated by the
contribution of the cement industry, in which the recent commissioning of cement plants
sharply increased its emissions. Measures to promote the reduction of the clinker content
4 https://eippcb.jrc.ec.europa.eu/reference
Projections of GHG emissions to 2030 in Tajikistan
25
of cement will reduce largely the emissions of the IPPU sector and have been identified
as a key mitigation potential alternative for the country.
Additionally, the refrigeration and air conditioning market of Tajikistan is increasingly
using F-gases to replace CFC and HCFC. However, these gases have a very high global
warming potential, affecting the GHG emission profile of the country. The future
replacement of F-gases for climate friendly alternatives will also have a representative
mitigation potential.
In the waste sector, Tajikistan is making substantial efforts to improve its solid waste and
wastewater management practices, in line with the national policy framework. The
expansion of the solid waste management practices and the reduction of open burning
of wastes in the rural areas is identified as a key opportunity for reducing GHG emissions
with outstanding co-benefits in terms of health and air quality. Furthermore, continuing
with the renovation of wastewater treatment plants have been also identified as a
relevant mitigation opportunity for the country.
Sensitivity of the estimates
An assessment of the sensitivity of the estimates was developed in the assignment
related to the possible development pathways which can occur in the country, specifically
related to the different trends of GDP and population growth, which are the key proxies
defining the national macro and socioeconomic framework of the country.
The main insight extracted from the sensitivity analysis is that under lower prospects of
economic and population growth, Tajikistan would achieve both its conditional and non-
conditional NDC targets without additional efforts. This analysis shows the approximate
GHG emission pathway of the country under pessimistic international macroeconomic
scenarios, as could be the case as a result of the coronavirus epidemic of year 2020.
This analysis also indicated that Tajikistan has room to increase its mitigation ambition
in the revision of the NDC, aiming at maximizing the possibilities of obtaining international
climate finance.
Conclusions
This project involved the estimation of impact of all mitigation actions implemented and
planned in Tajikistan and has identified and approximated the GHG emission reduction
impact of additional mitigation options for the country. Different scenarios have been
estimated illustrating the possible mitigation pathways of Tajikistan.
The results of this exercise show that Tajikistan needs to implement additional mitigation
actions for meeting its conditional NDC target, set at 65% of 1990 GHG emission levels
by year 2030. The impact of the actions under implementation since 2015 is thus not
sufficient to achieve the conditional NDC target. As shown in the sensitivity analysis,
Projections of GHG emissions to 2030 in Tajikistan
26
under lower prospects of economic and population growth, Tajikistan would achieve both
its conditional and non-conditional NDC targets without additional efforts.
The assessment of progress towards the achievement of the NDC targets made in this
report can only be seen as an approximation, as these targets refer to the GHG
emissions of year 1990, which were calculated following a different methodology (IPCC
Good Practice guidelines were used) than the one used in the latest GHG emission
inventory and also this exercise, so the differences between reference year emissions
(i.e. 1990), emissions of year 2016 and year 2030 are partially explained by the different
methodologies used. For this reason, it would be recommendable to either
recalculating the GHG emissions of year 1990 using consistently 2006 IPCC
Guidelines or updating the NDC target using the results of this exercise, i.e. the
GHG emissions of the period 2004-2030 which are calculated using the same
methodology.
Tajikistan counts with a sectoral policy framework which form the foundation for the
future low carbon development of the country. Nevertheless, the objectives and strategic
lines defined in these policy frameworks are not always translated into mitigation actions
with real GHG emission reductions. This is in fact the reason for the limited GHG
emission reduction impact of the mitigation actions implemented in Tajikistan.
Streamlining climate change in the existent policy instruments and including a
roadmap of specific mitigation actions should be a priority to achieve a low carbon
development pathway in Tajikistan.
The GHG emissions and mitigation profile of Tajikistan are strongly driven by the
contribution of the Agriculture, Forestry and Other Land Use sector, with over 40% of
national total emissions attributable to this sector in the historical and projected period in
both the WoM and the WeM scenarios. Given its impact in national total GHG emissions
and its prospects, the AFOLU sector should be prioritized within the mitigation
efforts of the country. In particular, the implementation of the Forest Sector
Development Strategy for 2016-2030 and the continuation of the Comprehensive
livestock development program, Pasture Development Programme after 2020 and
Development Program for Seed Production of the Republic of Tajikistan, are key for the
low carbon development of the country.
Apart from the AFOLU sector, the future GHG emission profile of Tajikistan is highly
dependent on the finalization of the Rogun Hydropower plant. This power plant will
represent an addition of 3,600 MW to the electricity generation capacity of the country,
limiting the need of fossil fuel generation for meeting national electricity demand.
The mitigation options with the greatest potential to reduce future GHG emissions
have been identified under this assignment, and include:
Replacement of anthracite consumption by electricity in the residential,
commercial and institutional sectors. This action has the higher estimated
mitigation potential, with 1,929 Gg CO2-eq by 2030.
Projections of GHG emissions to 2030 in Tajikistan
27
Incentivise the reduction of the clinker content of the cement produced in the
country. The reduction of clinker production in national cement production plants
has an estimated mitigation potential of 510 Gg CO2-eq by 2030.
Improving solid waste management practices. In line with national efforts to
improve solid waste practices, the waste management system could be extended
to rural areas, reducing the GHG emissions that occur in the open burning of
waste. This mitigation action has an estimated mitigation potential of 328 Gg
CO2-eq by 2030.
Enhancing removals by creating new fruit orchards and vineyards in addition to
those referred in the "Horticulture and Viticulture Development Program in the
Republic of Tajikistan for 2016 – 2020". This mitigation action has an estimated
mitigation potential of 125 Gg CO2-eq by 2030.
Agroforestry and / or silvo-pastoral systems. This mitigation option is associated
to the improving agroforestry and/or silvo-pastoral systems by planting shrubs
and trees in pastures and agricultural land. This mitigation action has an
estimated mitigation potential of 125 Gg CO2-eq by 2030.
The implementation of the forestry Sector Development Strategy for 2016-2030, the
continuation of the key programmes in the AFOLU sector, the finalization of the Rogun
Hydropower plant and the implementation of the key mitigation options identified will
allow Tajikistan to reduce its GHG emissions well below its conditional NDC target,
contributing to achieve the objectives of the Paris Agreements and the United Nations
Convention of Climate Change.
Projections of GHG emissions to 2030 in Tajikistan
Section 1 - Introduction
1. Background
The United Nations Framework Convention on Climate Change (UNFCCC) is an
international treaty whose overall objective is to “stabilise greenhouse gas (GHG)
concentrations in the atmosphere at a level that would prevent dangerous anthropogenic
interference”5 with the Earth’s climate system. Tajikistan became a Party to the UNFCCC
in 1992 and ratified the Convention on October 31, 1994.
The commitment for Parties to communicate to the Conference of Parties (COP)
information relating to the implementation of the Convention is guided by Articles 4 and
12 of the Convention.
In accordance with Article 4, paragraph 1, each Party, taking into account their common
but differentiated responsibilities and their specific national and regional development
priorities, objectives and circumstances, shall, among other things, formulate,
implement, publish and regularly update national and, where appropriate, regional
programmes containing measures to mitigate climate change, and measures to facilitate
adequate adaptation to climate change.
Further, in accordance with Article 12, paragraph 1, each Party shall communicate to the
COP, through the secretariat in the form of a national communication, the following
elements of information:
a) A national inventory of anthropogenic emissions by sources and removals by sinks of
all GHGs not controlled by the Montreal Protocol, to the extent its capacities permit, using
comparable methodologies to be promoted and agreed upon by the COP;
b) A general description of steps taken or envisaged by the Party to implement the
Convention; and
i. Programmes containing measures to facilitate adequate adaptation to
climate change
ii. Programmes containing measures to mitigate climate change
c) Any other information that the Party considers relevant to the achievement of the
objective of the Convention and suitable for inclusion in its communication, including, if
feasible, materials relevant for calculation of global emission trends.
5 “Article 2”. The United Nations Framework Convention on Climate Change. Retrieved 10 April, 2019.
Projections of GHG emissions to 2030 in Tajikistan
At COP 16 in Cancun in 2010, the Parties decided to enhance reporting in national
communications from non-Annex I Parties on national GHG inventories, mitigation
actions and their effects, and support received in a form of a Biennial Update Report
(BUR). BURs are intended to provide updates on actions undertaken by a Party to
implement the Convention, including the status of its greenhouse gas emissions and
removals by sinks, as well as on the actions to reduce emissions or enhance sinks, and
support needed and received to implement these actions.
In both National Communications and Biennial Update Reports Non-Annex I parties such
as Tajikistan need to report information on mitigation of climate change. The following
table shows the information provisions of National Communication and Biennial Update
Reports regarding mitigation:
Table 1. Mitigation information provisions in NC and BUR
Decision 17/CP.18: National
Communications Decision 2/CP.17: BURs
(III) General description of steps….to
implement the Convention
(a) Programmes and measures to
mitigate
• General requirements
• Methods and assessment /analysis
(results)
(III) Mitigation actions and their effects
• Methodologies and assumptions
• Objectives of the action and steps taken
or envisaged to achieve that action
• Progress of implementation and the
underlying steps taken or envisaged, and
the results achieved, such as estimated
outcomes (metrics depending on type of
action) and estimated emission
reductions, to the extent possible
• International market mechanisms
• Description of domestic MRV
arrangements
This project contributes to fulfilling the information the information provisions of the
national communications, as it assess the programmes and measures to mitigate climate
change detailing the methods used and results obtained, and provides information
relevant to the BUR, as it provides information on estimated emission reductions and
methodologies and assumptions for the mitigation actions involving direct GHG emission
reductions.
With the ratification of the Paris Agreement in 2017, Tajikistan pledged its national
determined contribution, with conditional and unconditional mitigation objectives. The
two mitigation targets established in the NDC are:
Projections of GHG emissions to 2030 in Tajikistan
3- without attracting new substantial international funding: not exceeding 80-90% of
the 1990 level by 2030, which amounts to 1.7-2.2 tons in CO2 equivalent per
capita
4- subject to new substantial international funding and technology transfer: a target
of 65-75% of the 1990 level by 2030, which amounts to 1.2-1.7 tons in CO2
equivalent per capita.
The NDC specified that the scope of these targets includes the following activities:
Power industry and water resources;
Industry and construction;
Land use, agriculture and gardening and grazing;
Forestry and biodiversity; and
Transportation and infrastructure.
In this regard, this assignment allows Tajikistan to assess its programs and measures
implemented or planned that result in the mitigation of human-induced climate change
and progress in achieving its NDC. The assignment also allows Tajikistan to identify
additional mitigation alternatives that could be implemented in the country in the future,
that could be considered in a potential review of the NDC.
2. Objectives and scope of this assignment
Tajikistan has implemented in recent years a number of policies and measures (PAMs)6
to mitigate climate change reducing greenhouse gas emissions. Assessing the impact of
these measures, and additional PAMs that will be implemented in the future, is key for
tracking progress of the achievement of national targets (i.e. NDC), facilitating
policymaking and improving the understanding on the drivers of national GHG emissions.
In this context, this project aims at assessing the GHG emission reduction impact of
national PAMs, projecting national GHG emissions to 2030 and developing different
mitigation scenarios considering different development pathways and the
implementation of different PAMs.
Specifically, this project encompasses the development of the following activities:
Collect official country information needed to complete the task.
Development of terms of reference for national experts. Collection of official
information on key sectors (energy, industrial processes, agriculture, forestry and
land use, waste) necessary for the calculations.
Analyse the GHG emission features of Tajikistan.
6 this document refer to policies and measures to reduce GHG emissions as PAMs or mitigation actions.
Projections of GHG emissions to 2030 in Tajikistan
Development of guidelines and handouts for trainings of local experts and young
specialists.
Conducting at least 5 workshops (with translation to Tajik language) to train local experts and young specialists in forecasting GHG emissions in key sectors, taking into account various development scenarios. At least two specialists should be trained in key sectors: energy, industrial processes, agriculture, forestry and land use, waste.
Providing an algorithm and programs for calculating GHG emissions projections
applying top-down or bottom-up approaches to different sectors and policies and
measures as appropriate. Compose and transfer user instructions and programs.
Development of indicators for Individual activities of the mitigation actions.
Indicators should reflect what the mitigation actions seek to achieve and should
define the specific interventions included in the mitigation actions (taxes, grants,
etc.); who monitors the indicators; timing and frequency of monitoring of
indicators.
Providing a detailed methodology for research and projection of GHG emissions
in key sectors. Develop projections of GHG emissions in key sectors by 2030,
taking into account various scenarios, following the UNFCCC recommendations
to analyse three scenarios (business as usual, with measures and with additional
measures). Methodology and research results should be translated to Tajik
language also.
Analysing the existing climate policies and measures in Tajikistan and their
impacts.
Preparing and providing a list of mitigation policies and measures based on the
developed GHG emissions projections, considering various development
scenarios.
3. Structure of the document
This technical report is structured in the following sections:
Section 1. Introduction
This section includes a description of the background for the GHG mitigation
assessment, its scope, and objectives to introduce and contextualize the technical report.
Section 2. Overall methodology
This section provides a description of the overall methodological approach followed for
developing the GHG mitigation assessment.
Section 3. Current GHG emissions profile
This section includes a description of the historical GHG emissions that have been used
as a reference in this GHG emissions projections.
Projections of GHG emissions to 2030 in Tajikistan
Section 4. Without Measures scenario
This section addresses the description of the Without Measures scenario developed by
sector.
Section 5. Implemented mitigation actions
This section provides an assessment of the mitigation actions implemented in the country
with direct GHG emission reduction impact.
Section 6. Planned mitigation actions
This section provides an assessment of the mitigation actions planned to be
implemented in Tajikistan with direct GHG emission reduction impact.
Section 7. Mitigation options
This section includes a description of the mitigation alternatives identified and provides
an approximation to its impact.
Section 8. With Existing Measures scenario
This section covers the description of the With Existing Measures scenario developed
considering the mitigation impact of the actions described in section 5.
Section 9. With Additional Measures scenario
This section covers the description of the With Additional Measures scenario developed
considering the mitigation impact of the actions described in sections 6 and 7.
Section 10. Summary of results
This section provides a summary of the GHG emission projections estimated in this
project, as a summary of the previous sections 4 – 10.
Section 11. Sensitivity analysis
This section includes an assessment of the sensitivity of the results, considering different
GDP and population pathways.
Section 12. Conclusions of the GHG mitigation assessment
This section concludes the technical report describing with the main results of the project
and highlighting the key messages derived from it.
Projections of GHG emissions to 2030 in Tajikistan
Section 2 - Overall methodology
This project builds from the work carried out previously in the country, specifically the
GHG emission inventory 2004-2016, the identification of mitigation actions made in the
BUR1 and several sectoral policy frameworks and background documents.
The overarching working principles followed in the projection of GHG emissions are
the following:
The projections are consistent with the GHG emissions of the historical period.
The nomenclatures and good practice guidance of 2006 IPCC Guidelines have
been followed for estimating projections.
The differences between scenarios are only explained by the impact of mitigation
actions or mitigation options.
The projections are consistent with the overall macroeconomic framework of the
country, defined in the National Development Strategy.
The lack of information has been addressed with assumptions made by the
working and validated by national experts.
All the working files generated during project have been provided aiming at
facilitating future updates of the work.
The guiding principle for the development of this report is transparency. Thence,
the data used, methodologies applied, and results obtained are provided at a
detailed breakdown to facilitate the understanding of the work developed.
All the developments made have been validated by the main stakeholders
involved in climate change mitigation.
Following these principles is essential for ensuring the results of the GHG emissions
projections are robust and consistent for assessing mitigation trends and tracking
progress towards the achievement of the NDC.
1. Approach
The project started with a first workshop to present the project to the main stakeholders
of the country. This first workshop was used to engage with the stakeholders and to start
the data gathering process and was followed by a set of bilateral interviews to facilitate
the data gathering. The information raised during the inception workshop and these
bilateral interviews was the foundation for the development of the GHG emission
projections.
From a technical point of view, the project started with the identification of mitigation
actions implemented and planned in the country and with the estimation of a “Without
Measures Scenario” using the national GHG emission inventory as a reference. This
scenario does not take into account the implementation of any mitigation action but is
projected considering the main macroeconomic perspectives of the county.
Projections of GHG emissions to 2030 in Tajikistan
All mitigation actions identified were assessed by the working team to obtain the impact
in terms of GHG emissions reductions due to their implementation. Once the assessment
of mitigation actions implemented and planned was completed, additional mitigation
alternatives (mitigation options) were identified and assessed by IPCC sector. All
mitigation actions and additional options assessed were used to develop GHG emissions
scenarios.
The project included a capacitation workshop of four days, from 22-25 June, targeting
national experts on the estimation of GHG emission projections. Due to the Coronavirus
outbreak, this workshop was replaced by the development of an e-learning course for
national consultants.
Figure 1. Methodological approach for the implementation of the project.
The following paragraphs provide key insights on the main methodological steps followed
to estimate the GHG emission projections of Tajikistan.
Estimating a Without Measures (WoM) scenario
The Without Measures Scenario is estimated from the emissions of years 2004-2016
(i.e. the GHG emissions inventory) using national forecasts for 2016 to 2030,
assumptions on the evolution of the key parameters and basic statistical techniques. This
scenario does not consider specifically the impact of any mitigation action under
implementation since 2015.
From the methodology and emissions estimated in the WoM, the different policy
scenarios were estimated by subtracting the impact of mitigation policies and options to
the corresponding sector.
Projections of GHG emissions to 2030 in Tajikistan
What mitigation policies and mitigation options do we consider in each
scenario?
Not all mitigation actions implemented in the country have been considered in this GHG
emission mitigation assessment. The criteria for selecting mitigation actions is the
following:
The mitigation action is under implementation in or after year 2015. This also
includes actions which are planned to be implemented in the future.
The mitigation action involves direct GHG emission reductions (studies or
feasibility projects have not been assessed)
It is not just a good idea or intention reflected in a policy/strategy, but it is a real
action to be implemented with GHG emissions associated.
There is no double counting with other mitigation actions assessed.
For instance, if a project to install a solar plant is included in a strategy
to increase solar generation capacity is estimated at the national
level.
The mitigation actions are not only projects implemented, but also plans which are
described within general policy frameworks. Policy frameworks are not necessarily
mitigation actions. They include overall objectives and strategic lines to follow that,
sometimes, are not translated into real lines of action. Thence, it is important to highlight
that this GHG mitigation assessment has not included aspirational objectives which are
not translated into lines of action. The policy frameworks evaluated for identifying
mitigation actions are the following:
National Development Strategy of the Republic of Tajikistan for the period up to
2030
National Climate Change Adaptation Strategy
Water Sector Reform Program of the Republic of Tajikistan
Program for providing the population with clean drinking water
Development Program for Housing and Public Utilities of the Republic of
Tajikistan
State Target Program for the Development of the Transport Complex of the
Republic of Tajikistan
Agricultural Reform Programme of the Republic of Tajikistan
Pasture Development Program of the Republic of Tajikistan
Strategy for the development of industry in the Republic of Tajikistan
The state program for the development of new irrigated land and the restoration
of land that has been abandoned from agricultural circulation in the Republic of
Tajikistan
Comprehensive livestock development program
State environmental program
Power Sector Development Master Plan
Projections of GHG emissions to 2030 in Tajikistan
These policies, strategies and programmes led to the implementation of various
mitigation actions in line with the main objectives established in them.
Nevertheless, in the context of this assignment, several of these strategies have been
directly considered in the different emission scenarios. This is the case, for instance, for
the “Forest Sector Development Strategy for 2016-2030”, for which a direct GHG
emission impact for its implementation has been estimated.
Regarding the scenarios, we have selected mitigation actions and mitigation options for
showing the mitigation effort made since 2015 (the implementation of the NDC), the effort
which is planned to be made in the future and the possibilities to make further effort to
raise the mitigation ambition of the country. With this idea, several scenarios have been
designed:
Table 2. Mitigation actions and mitigation options included in the scenarios
Mitigation actions and options included WoM WeM WaM
Mitigation actions implemented/finished after
2015
× ×
Mitigation actions adopted after 2015 × ×
Mitigation actions planned ×
Mitigation options (additional) ×
With Existing Measures (WeM) Scenario: This policy scenario is built from the WoM
considering the effect of mitigation actions under implementation since 2015. This
includes mitigation actions that were adopted after 2015 but their implementation not yet
finalized.
With Additional Measures (WaM) Scenario: This policy scenario is built from the WeM
considering the mitigation actions planned to be implemented in the future and the impact
of the main mitigation options identified additionally to the previous actions. This policy
scenario represents the maximum GHG emission level that Tajikistan could achieve with
the implementation of the key mitigation alternatives available.
The differences between scenarios are only explained by the different policy
implementation, i.e. the underlying projection methodology is the same in all scenarios.
How is the mitigation impact of the mitigation actions assessed?
Three steps are followed for estimating the mitigation impact of actions:
1. Identify the IPCC category or categories affected by the mitigation action.
2. With the information available regarding the scope of the action, evaluate how
the mitigation action impact the activity data and/or emission factors of the
emissions estimated in the WoM.
Projections of GHG emissions to 2030 in Tajikistan
3. Design an estimation method for obtaining the overall impact of the mitigation
action. Overall, there are two types of estimation methods for estimating the
mitigation impact:
C) Estimate the GHG emissions in two scenarios for the mitigation action:
a reference scenario and a reduction scenario. The impact of the action
is then calculated as GHG Emissions in the reference scenario minus
the GHG emissions in the reduction scenario.
The reference scenario is ideally consistent with the WoM, and only
considers the activity data affected by the mitigation action. It represents
the technology and process in place before policy implementation.
The reduction scenario includes an estimation of the emissions of the
new situation, after policy implementation. Assumption are often needed
on the scope and the new technology/process implemented.
D) Estimate directly the mitigation impact of the action, i.e. the GHG
emissions reduction applicable to the change produced by the
implementation of the mitigation action. In these cases, only the
difference between the scenarios for mitigation action (reference and
reduction scenarios) is estimated.
2. Methodological principles
As mentioned above, this project follows the nomenclature, good practices and allocation
of emissions specified in the 2006 IPCC Guidelines. Therefore, the nomenclature used
is the following:
Table 3. Nomenclature used
Inventory sector Code
Energy 1
Industrial Process and Products Use (IPPU) 2
Agriculture, Forest and Other Land Use (AFOLU) 3
Waste 4
Each sector comprises individual categories (in capital letter), sub-categories (number)
and sources/sinks (lowercase letter).
The following table briefly describe the nature of the emissions allocated in each sector:
Projections of GHG emissions to 2030 in Tajikistan
Table 4. Emissions by sector
Inventory
sector
GHG emissions
Energy All GHG emissions arising from combustion and fugitive releases of
fuels. Emissions from the non-energy uses of fuels are generally not
included here, but reported under Industrial Processes and Product
Use
Industrial Process
and Products Use
(IPPU)
GHG emissions from industrial processes that chemically or physically
transform materials; and GHG emissions from the consumption of
products (refrigerants, non-energy consumption of fuels, solvents, etc)
Agriculture, Forest
and Other Land
Use (AFOLU)
GHG emissions from managed lands and ecosystems
Waste GHG emissions from the treatment of waste and wastewater.
The basic equation for estimating the emission of one category is the following:
1 𝐸𝑚𝑖𝑠𝑠𝑖𝑜𝑛𝑠𝑐,𝑔,𝑡 = 𝐴𝐷𝑐,𝑡 ∙ 𝐸𝐹𝑐,𝑔,𝑡
Where
𝐸𝑚𝑖𝑠𝑠𝑖𝑜𝑛𝑠𝑐,𝑔,𝑡 = 𝑒𝑚𝑖𝑠𝑠𝑖𝑜𝑛𝑠 𝑜𝑓 𝑐𝑎𝑡𝑒𝑔𝑜𝑟𝑦 𝑐, 𝑔𝑎𝑠 𝑔 𝑎𝑛𝑑 𝑦𝑒𝑎𝑟 𝑡
𝐴𝐷𝑐,𝑡 = 𝑎𝑐𝑡𝑖𝑣𝑖𝑡𝑦 𝑑𝑎𝑡𝑎 𝑜𝑓 𝑐𝑎𝑡𝑒𝑔𝑜𝑟𝑦 𝑐, 𝑦𝑒𝑎𝑟 𝑡
𝐸𝐹𝑐,𝑔,𝑡 = 𝐸𝑚𝑖𝑠𝑠𝑖𝑜𝑛 𝑓𝑎𝑐𝑡𝑜𝑟 𝑜𝑓 𝑒𝑚𝑖𝑠𝑠𝑖𝑜𝑛𝑠 𝑜𝑓 𝑐𝑎𝑡𝑒𝑔𝑜𝑟𝑦 𝑐, 𝑔𝑎𝑠 𝑔 𝑎𝑛𝑑 𝑦𝑒𝑎𝑟 𝑡
The estimates of emissions and removals– in its simplest form- correspond to a direct relation
between an emission factor (emission rate by unit of activity) and the activity data which
represents the corresponding level of activity.
The activity data describes the annual magnitude of one activity (for instance, production, fuel
consumption, etc., at national level, for one category and one year).
The emission factor is the amount of gas emitted by unit of activity (for instance, Gg of CH4 by
tonne of fuel consumed). Default emission factors are provided by the 2006 IPCC Guidelines
for the direct GHGs emissions.
In many cases, the activity data available do not correspond to the emission factor available
or used. In these cases, the data need to be converted using conversion factors. In such cases,
the equation is the following:
2 𝐸𝑚𝑖𝑠𝑠𝑖𝑜𝑛𝑠𝑐,𝑔,𝑡 = 𝐴𝐷𝑐,𝑡 ∙ 𝐸𝐹𝑐,𝑔,𝑡 ∙ 𝐶𝑜𝑛𝑣𝑒𝑟𝑠𝑖ó𝑛 𝑓𝑎𝑐𝑡𝑜𝑟
All the equations require a statistical value which needs to be obtained from the entities which
regularly collect the data.
Projections of GHG emissions to 2030 in Tajikistan
Several IPCC methods can be used for estimating emissions and removals. The choice of one
method depends on the availability of data, the current circumstances of the country, and the
human and financial resources to elaborate on the inventory.
The global warming potentials used for the calculation of the total GHG emissions are those
used in the NDC, i.e. the GWP of the AR4, as follows:
Table 5. Global Warming Potentials (GWP) used
Global Warming
Potential
Gas GWP
CO2 1
CH4 25
N2O 298
PFC - 14 7 390
PFC - 116 12 200
Source: IPCC Fourth Assessment Report (AR4)
The decision about the GWP was due to the fact that the NDC of Tajikistan used AR4
GWP.
Further, it is worth highlighting that the principles followed in this GHG emission
assessment are also those of 2006 IPCC for inventories calculation, as follows:
Transparency means clear documentation and reporting at a level of disaggregation that
sufficiently allows the reader to understand how the estimation was performed. The
transparency of the estimation is fundamental to enable its use and improvement.
Consistency means that estimates for any different years, gases and source categories
are made in such a way that differences in the results between years and source
categories reflect real differences in emissions. Annual emissions, as far as possible,
should be calculated using the same method and data sources for all years, and resultant
trends should reflect real fluctuations in emissions and not the changes resulting from
methodological differences.
Comparability means that the estimates made can be compared with other estimates
made following 2006 IPCC Guidelines, such as the national inventories of other
countries. This can be achieved by using accepted methodologies of 2006 IPCC
Guidelines.
Completeness means that estimates are reported for all gases, all relevant source
categories and all years and for the entire territorial areas.
Accuracy means that emissions are neither overestimated nor underestimated, as far
as can be judged and with uncertainties reduced as far as practicable.
Projections of GHG emissions to 2030 in Tajikistan
Section 3 - Current GHG emission
profile
The GHG emissions of Tajikistan are dominated by the contribution of the Agriculture,
Forestry and Other Land Use sector, followed by the Energy, Industrial Process and
Product Use (IPPU) and waste sectors, in this order.
Table 6. GHG emissions by sector in Tajikistan
IPCC sector 2004 2010 2011 2012 2013 2014 2015 2016
1 Energy 4,046 1,430 2,131 1,581 2,069 2,364 3,843 3,504
2 Industrial Processes and Product Use
2,161 2,204 1,849 1,804 1,605 1,510 1,746 1,991
3 Agriculture, Forestry, and Other Land Use
1,958 3,217 3,684 3,781 3,891 3,910 3,934 4,003
4 Waste 1,099 1,246 1,283 1,317 1,351 1,382 1,419 1,454
Total National Emissions and Removals
9,263 8,097 8,948 8,483 8,916 9,165 10,942 10,953
To obtain these emissions, several adjustments have been made from the GHG
national inventory in order to use this information for the development of GHG
emission scenarios and the estimation of impact of mitigation actions. The most
relevant changes from the inventory are the following:
Category 4D1 Domestic wastewater has been recalculated. These
emissions were assumed to be zero in the inventory. However, the discharges of
water of the 100% of the population have to be considered by the inventory,
according to 2006 IPCC Guidelines. To solve this issue, a tier 1 approach of the
2006 IPCC Guidelines have been followed for estimating the emissions of this
category in the historical period.
Category 4C Incineration and open burning of waste has been calculated to
account for 100% of the emissions of the solid waste generated. Category 4A
Solid Waste Disposal only considered the urban population, of which 74% of
waste was sent to landfills. The emissions from the remaining 26% of waste are
not considered by the inventory. Based on 2006 IPCC Guidelines, "In a
developing country, mainly in urban areas, Fraction of population burning waste
can be roughly estimated as being the sum of population whose waste is not
collected by collection structures and population whose waste is collected and
disposed in open dumps that are burned." Additionally, the emissions from the
rural population are not considered. Open burning practices may occur in the
rural areas of the country. Indeed, open burning practices occur in Tajikistan, as
ascertained in the following sources:
Projections of GHG emissions to 2030 in Tajikistan
http://www.seas.columbia.edu/earth/wtert/sofos/Boboeva
_thesis.pdf
https://issuu.com/zoienvironment/docs/ca-waste-eng
https://www.weinternational.asia/solid-waste-
management-in-tajikistan/
Therefore, in order to consider 100% of the emissions from solid waste in the
country, category 4C Incineration and open burning of waste has been calculated,
considering that the 26% of the urban population and all population of rural areas
of Tajikistan burn wastes (half of the wastes generated), assuming that all food
and wood wastes are re-used.
Category 2F Product Uses as substitutes for ODS has been calculated. The
emissions from the use of fluorinated gases in refrigeration and air conditioning,
foam blowing agents and aerosols occur in the country, but these emissions were
not estimated in the national inventory. As there is no data available to implement
2006 IPCC methodologies, an estimate based in the inventory of Armenia7 has
been performed to complete the national GHG emissions of the inventory.
The following table shows the detailed GHG emissions at category level, to provide a
better understanding of the mitigation possibilities from the current GHG emission level:
Table 7. Breakdown of GHG emissions in Tajikistan
IPCC Category 2004 2010 2015 2016
Energy
1A1 Energy Industries 283 251 1,099 1,736 1A2 Manufacturing industries and
construction 488 392 260 309
1A3 Transport 408 256 255 149
1A4 Commercial/residential/institutional 2,835 484 2,166 1,239
1B1 Fugitive emissions from solid fuels 2 5 25 33 1B2 Fugitive emissions from oil and natural
gas 29 41 37 38
IPPU
2A Mineral Industry 118 177 744 1,032
2C Metal Industry 1,806 1,761 702 652
2F Product Uses as substitutes for ODS 237 267 300 307
AFOLU
3A1 Enteric fermentation 2,370 3,485 4,053 4,173
3A2 Manure management 476 690 793 818
3B Land - 1,461 - 1,512 - 1,591 - 1,598
7 Armenia has been chosen as is the closest country with a complete inventory. The estimate followed assumed that per capita emissions of F-gases in Tajikistan are half the per capita emissions of Armenia, assuming the differences in the economic structure between countries would involve significant differences in the consumption of these gases.
Projections of GHG emissions to 2030 in Tajikistan
3C Aggregate sources and non-CO2 emissions sources on land 572 555 678 611
Waste
4A Solid waste disposal 163 218 259 266
4C Incineration and open Burning 403 452 510 522
4D Wastewater treatment and discharge 533 576 650 666 Total 9,263 8,097 10,942 10,953
Note – The categories/emission sources with no emissions estimated in the historical
period have not been included in this table.
Some emission sources occurring in Tajikistan have not been considered in this
assignment, as they were not included in the national inventory and could not be
estimated by the working team. These missing categories are the following:
Emissions from N2O in Anaesthesia
Use of F-gases (SF6) in electrical equipment
Emissions of NMVOC and indirect CO2 from solvent use and products containing
solvents (such as paints) used.
Nevertheless, it has to be noted that the magnitude of these emissions is not likely to be
significant for national total GHG emissions.
The analysis of the emissions estimated in the historical period at category level
(illustrated in the previous table) is essential to understand the GHG emission projections
estimated and the mitigation potential of the country.
The largest contributor to historical period GHG emissions is enteric fermentation
(IPCC sub-category 3A1), with a contribution that ranges from a 25.6 per cent in 2004 to
a 38.1 per cent of national total emissions in year 2016. The increasing contribution of
this sub-category is driven by the growing population of cattle, which increased by a 95.8
per cent in the period 2004-2016. This is also the reason for the growing emissions from
manure management, that contributed with a 7.5 per cent to national total GHG
emissions in 2016.
The second contributing activity to national total GHG emissions is energy industries
(IPCC sub-category 1A1), with an increasing share that reached a 15.9 per cent of
national total emissions in 2016, from only 3.1 per cent in 2004. This increasing trend is
explained by the commissioning of a new power plant in Dushanbe in year 2014, which
reduced energy shortages but significantly increased anthracite consumption and GHG
emissions.
The carbon stock changes which occurred as a result of land use change and forestry
activities (IPCC category 3B) leaded to steady CO2 removals from the atmosphere,
within the range 14.6-18.7 per cent of national total GHG emissions in the period 2004-
2016. This contribution makes this category the third largest contributor to Tajikistan
GHG emissions in the historical period.
Projections of GHG emissions to 2030 in Tajikistan
Fuel consumption in the residential, commercial, and institutional sectors (IPCC
sub-category 1A4) is shown as the fourth largest contributor to national total GHG
emissions, with a decreasing contribution from 30.6 per cent in 2004 to a 11.3 per cent
in 2016. This decrease is explained by a sharp reduction of natural gas consumption,
which was partially covered by anthracite consumption in these sectors, specially from
year 2014.
The activity levels of the mineral industry (IPCC category 2A) raised substantially in the
historical period, leading this category to reach a 9.4 per cent of national total GHG
emissions in 2016. This increase is explained by the abrupt grow of clinker production
levels due to the commissioning of new production plants in years 2014-2016.
Emissions from solid waste management systems, represented in categories 4A solid
waste disposal and 4C incineration and open burning represented a 7.2 per cent of
national total emissions in 2016, with slight variations in the historical time series. The
emissions from solid waste are driven by the number of population, as the waste
generation rate is assumed to remain constant in this period.
The remaining emission categories and subcategories of Tajikistan have lower
contribution to national total GHG emissions. Nevertheless, these other sources together
account for a 25.2 per cent of national total GHG emissions in 2016. Sources with
significant GHG emissions within this group includes industry emissions within
categories 2C Metal Industry, 4D Wastewater treatment and discharge and 1A2
Manufacturing industries and construction.
Projections of GHG emissions to 2030 in Tajikistan
Section 4 - Without Measures Scenario
The Without Measures Scenario (WoM) represents the GHG emissions of Tajikistan with
no changes in the circumstances of the latest year for which observed information is
available, i.e. 2016. In the context of our assignment, this means that this scenario does
not consider the future mitigation impact of any mitigation action under implementation
after 2015. Nevertheless, the GHG emissions estimated for the historical period might be
influenced by the impact of mitigation actions implemented before 2015; the effect of
these mitigation actions is thus which is already incorporated in the observed in years
2004-2015. This impact is estimated from year 2015 within the policy scenarios.
The estimation of the WoM scenario is the key methodological step for obtaining national
total GHG emission projections. The other policy scenarios considering different degree
of policy implementation (the WeM and WaM scenarios) are calculated from the WoM
considering the mitigation impact estimated for the different mitigation actions and
mitigation options identified.
The WoM is projected relying on available forecasts that explain the future context of the
country, such as GDP, population, or electricity demand. The methodological details of
the projections, data used, and results obtained are detailed in this section. The summary
of the GHG emissions obtained is illustrated in the following figure.
Figure 2. GHG emission projections by scenario and NDC targets of Tajikistan
(Gg CO2-eq)
The GHG emission profile of the country remains relatively stable in the WoM. In line
with the GDP forecast of the Industrial scenario of the National Development Strategy,
the contribution of agriculture to national total emissions is reduced, while the Energy
and IPPU emissions increase its contribution. The contribution of the Waste and FOLU
sectors are also slightly reduced.
Projections of GHG emissions to 2030 in Tajikistan
Figure 3. Sectoral Contribution to GHG emissions in 2016 and 2030 (%)
The following sections provide additional details on the general approach for calculating
the WoM and the details of the estimations made at sectoral level.
1. Methodological approach
The emissions from the national GHG emission inventory (time series 2004-2016) have
been generally projected differentiating between activity data and emission factors
following equation 1. Projections estimates have been performed at the highest
disaggregation level available in the inventory. The projection of the activity data of the
inventory is driven by different factors, such as the level of activity (production, population
or energy demand, among others), while the evolution of the emission factors is driven
by other factors such as technology.
The projection methodologies used in the project are framed under the methodological
approach defined in chapter 8, Part A, of EMEP/EEA 2019 Guidebooks8.
In the cases where complex9 methodologies are used by the inventory, the same
methodology has been used for projections. In the cases were the same methodology
could not be used, the implied emission factor and the most representative activity data
series have been used for projecting.
8 https://www.eea.europa.eu/publications/emep-eea-guidebook-2019/part-a-general-guidance-chapters/8-projections/view
9 Methodologies not following the basic estimation equation of activity data multiplied by emission factor, but other methodological approaches such as mass balances, models or multivariate equations.
Projections of GHG emissions to 2030 in Tajikistan
1.1. Projection of activity data
The projections of GHG emissions are performed considering the industrial scenario10 of
the national development strategy 2030 as a main macroeconomic reference. A set of
projected variables that define a future macroeconomic framework for the country have
been used for projecting the activity data of the inventory to 2030. The variables available
are the following:
Table 8. Projections of variables (proxies) available at national level
Name of the Proxi Units 2004 2016 2020 2025 2030
GDP Agriculture Million USD 399 1,417 1,701 2,277 3,047
GDP Industry Million USD 553 1,055 1,500 2,036 2,829
GDP construction Million USD 88 838 760 1,032 1,433
GDP Services Million USD 342 1,069 1,296 1,734 2,321
GDP transport Million USD 138 883 767 1,027 1,374
GDP Other Million USD 326 906 1,685 2,255 3,018
GDP total Million USD 2,076 6,953 8,604 11,557 15,623
Total fleet Thousand vehicles
289,544 435,408 471,798 519,663 572,620
Cars Thousand vehicles
236,486 376,171 412,786 455,749 503,184
Trucks Thousand Vehicles
35,290 39,262 40,400 42,461 44,627
Passenger transport (buses, minibuses)
Thousand vehicles
13,999 15,660 14,594 17,333 20,586
Special cars Thousand vehicles
3,770 4,315 4,019 4,120 4,225
Total population Thousand inhabitants
6,599 8,551 9,318 10,361 11,521
Rural population Thousand inhabitants
4,846 6,291 6,869 7,659 8,540
Urban population Thousand inhabitants
1,753 2,260 2,454 2,723 3,021
Note – the sources of this information are the national development strategy 2030 and
the Agency for Statistics under the President of the Republic of Tajikistan
The projections of the activity data have been done using different methods, depending
of the nature of the variables and its temporal evolution. In certain occasions, proxies
(the variables shown in previous table) can be used for projecting the activity data.
10 The inertial and innovative scenarios considered under the national development strategy have not been used in this project. The innovative scenario considers a set of policies that would transform the economic structure of Tajikistan. The equivalent to the innovate scenario in this project would be the WaM.
Projections of GHG emissions to 2030 in Tajikistan
However, this is not always possible. The following are the type methods that have
been used for projecting the activity data of the inventory:
Methods for projecting the activity data:
The method selected for the projection of the activity data depends on the analysis of
the historical trend of the activity data and its relationship with those proxies available
which have a theoretical relationship with the activity data.
If the correlation and theoretical relationship of the activity variable with any proxy is
found to be high, and the characteristics of the data allows, the use of regression models
is preferred. However, the use of proxies in linear regression models is not always
possible, as it depends on the statistical characteristics of the series and its relationship
(stationarity and normality are required for both time series, and heteroscedasticity
should be avoided).
For this reason, other methods are also used for projecting the activity data. In some
cases, the growing rate of highly correlated proxies has been applied to the latest
observed data (i.e. the latest year available in the inventory). This assumes an elasticity
of 1, an equivalent marginal growth rate of the variables.
If the historical time series present a clear trend, stabilising at a certain level, the
projections reproduce the latest time period using the latest inventory year or any
arithmetic calculation.
The following methods have been generally used for projecting the activity data:
[1] Using the value of the latest inventory year or any arithmetic calculation.
Applying a growing rate
A specific growing rate [2a]
𝐴𝑐𝑡𝑖𝑣𝑖𝑡𝑦 𝑑𝑎𝑡𝑎𝑡 = 𝐴𝑐𝑡𝑖𝑣𝑖𝑡𝑦 𝑑𝑎𝑡𝑎𝑡−1 ∙ 𝐺𝑟𝑜𝑤𝑖𝑛𝑔 𝑟𝑎𝑡𝑒𝑡
The same growing rate of a correlated proxy [2b]
𝐴𝑐𝑡𝑖𝑣𝑖𝑡𝑦 𝑑𝑎𝑡𝑎𝑡 = 𝐴𝑐𝑡𝑖𝑣𝑖𝑡𝑦 𝑑𝑎𝑡𝑎𝑡−1 ∙ 𝑃𝑟𝑜𝑥𝑦𝑡
𝑃𝑟𝑜𝑥𝑦𝑡−1
Using linear regression models with proxies [3]
𝐴𝑐𝑡𝑖𝑣𝑖𝑡𝑦 𝑑𝑎𝑡𝑎𝑡 =∝ + 𝛽 ∙ 𝑃𝑟𝑜𝑥𝑦𝑡 + µ
In Tajikistan, the very high volatility of the historical time series of the inventory made
numerous time series non-stationary. This issue caused the relationship with the proxies
to be unstable, preventing the use of this method in many occasions.
Projections of GHG emissions to 2030 in Tajikistan
1.2. Projection of Emission factors
The technological and process conditions and characteristics remain unchanged
(constant) in the projected period. Therefore, the projection of emission factor in the WoM
scenario is generally made using the latest emission factor value of the inventory. The
emission factors used are all default IPCC 2006 emission factors, as used in the national
GHG emissions inventory.
1.3. Projection of Emission
Once the activity data and emission factor are projected at sub-category level, the
emissions are calculated multiplying both variables, using appropriate conversion factors
to obtain emissions in terms of Gigagrams (Gg).
Projections of GHG emissions to 2030 in Tajikistan
2. Methodology and assumptions by sector
2.1. Energy
1A1 Fuel combustion in Energy industries
The activity data of this category consists in fuel consumption by type in the production
of electricity, heat and in petroleum refining.
Fuel consumption in electricity and heat generation have been estimated applying the
growing rate of the time series of population (method [2b]). It is assumed that the
electricity and heat demand will evolve in line with population growth. This implies that
the electricity generation mix will remain constant, i.e. generating electricity with the
same electricity generation mix.
Petroleum refining is projected along category 1A2 using an annual growth rate of 5 per
cent (see further explanation below for category 1A2).
1A2 Fuel combustion in Manufacturing industries and
construction
The activity data of this category consists in fuel consumption by type in manufacturing
industries and construction.
The emissions of this category are theoretically highly correlated with GDP industry.
However, that is not the case for the historical years. The emission growth is lower than
the GDP growth (elasticity lower than 1) so we assumed a 5 per cent annual growth rate,
which is lower than the growth rate of GDP.
1A3 Fuel combustion in transport
The activity data of this category consists in fuel consumption by type in road
transportation and railways.
The consumption of diesel and gasoline have been projected using the method [3] with
the GDP component of transport. Nevertheless, this method cannot be used for natural
gas liquids and LPG due to the volatile time series for years 2004-2016. For this reason,
these two fuels have been estimated applying an annual growth rate of 2.5 %, assuming
the evolution of LPG and natural gas will remain growing at lower levels than gasoline
and diesel.
Projections of GHG emissions to 2030 in Tajikistan
The emissions in railways have been projected applying the method [2b] with population,
assuming the GHG emissions of railways are highly correlated with the number of
inhabitants.
1A4 Other sectors
The activity data of this category consists in fuel consumption by type in the residential,
commercial and institutional sectors, as well as in agriculture, forestry, fishing and fish
farms.
The projection for the commercial and institutional sectors has been performed applying
the method [2b] with GDP, assuming the evolution of the activity levels will depend on
the evolution of GDP.
The projection for the residential sector has been performed applying the method [2b]
with the population, assuming the activity levels are driven by the number of inhabitants.
The projection for agriculture, forestry, fishing and fish farms has been performed
applying the method [2b] with GDP, assuming the evolution of the activity levels will
depend on the evolution of GDP.
1B Fugitive emissions
The activity data of this category consists in tonnes of coal, oil and gas produced in the
country. The relationship with the proxies available is not clear. For this reason, the
projection of these activity variables has been done extending the evolution of the
historical time series into the future following the adjusted equation resulting from the
trend in the historical series.
For the production of natural gas an annual grow rate of 2% has been applied.
2.2. IPPU
2A Mineral Industry
The activity data of this category consists in amounts of clinker, lime and glass produced,
as well as carbonates consumed in the ceramics industry.
The production of clinker, lime and glass should be highly correlated with GDP industry.
However, the statistical characteristics of the series do not allow to make a regression
between these variables. An annual growth rate of 5 per cent has been used instead.
Projections of GHG emissions to 2030 in Tajikistan
The prospective growth of the consumption of carbonates is assumed to be lower than
GDP, as the nature of this industry (craftsmanship) cannot reproduce rapid growth levels.
2C3 Aluminium production
The activity data of this category consists in amounts of aluminium produced.
The projections of this sub-category are estimated using the method [2b] with the GDP.
The aluminium industry will meet the demand of product needed for increasing national
added value at a rate of GDP growth.
2F Product Uses as Substitutes for Ozone Depleting
Substances
This category was not estimated in the national inventory. For this reason, an estimate
based on the GHG emissions per capita has been followed (see section 3 Current GHG
emission profile for further information). The same rate per capita is applied to the time
series of population to obtain the GHG emissions in all the projections period.
2.3. AFOLU
3A1 Enteric fermentation and 3A2 Manure Management
Fuel combustion in Energy industries
The activity data of this category consists of annual average population of livestock by
animal category. Livestock is disaggregated to the following categories:
Dairy Cows
Other Cattle
Sheep
Goats
Camels
Horses
Mules and Asses
Swine
Other (please specify) Poultry
For the years 2017-2020, the official data from the "Comprehensive Program for the
Development of the Livestock Industry in the Republic of Tajikistan for the years 2018-
2022" were used. For the remaining projection period, the 12 years regression method
with GDP of Agriculture was used, because GDP of agriculture of Tajikistan is highly
correlated to livestock population.
Projections of GHG emissions to 2030 in Tajikistan
3B1 Forest land
The activity data of this category consists of the total area of forest land. The area of
forest land has a low inter-annual variation. Therefore, for forecasting the area of forest
land, the five-year average method was selected.
3B2 Cropland and 3B3 Grassland
According to the national inventory, the only significant source / sink category of 3.B is
3.B.1. The other categories contribute to a net sink of 0.13kt CO2, which is lower than
the uncertainty level of the projections. These minor sinks were projected by simple
extrapolation of the historical emissions.
3C3 Urea application, 3C4 Direct N2O Emissions from
managed soils and 3C6 Indirect N2O Emissions from
manure management
The activity data of this category consists of the annual amount of urea fertilization. To
forecast the urea fertilization the “5 years regression total GDP Agriculture” method was
applied, because it is considered that fertilizer application is highly correlated to GDP
Agriculture.
3C7 Rice cultivation
The activity data of this category consists of the annual harvested area. To forecast the
future rice area the “5 years average” method was applied. This method was selected
because the trend of rice cultivation area of the last 3 years seems to stabilize.
2.4. Waste
4A Solid Waste Disposal
The IPCC 2006 FOD model11 has been used to calculate the CH4 emissions of this
category for both the historical and the projected period. The time series of population
and the parameters used in the national GHG emission inventory for waste composition,
11 https://www.ipcc-nggip.iges.or.jp/public/2006gl/pdf/5_Volume5/IPCC_Waste_Model.xls
Projections of GHG emissions to 2030 in Tajikistan
waste generation per capita, percentage of waste going to landfill and distribution of solid
waste disposal sites for the calculation of the methane correction factor.
4C Incineration and open burning of waste
This category was not estimated in the national inventory. For this reason, an estimate
based on population has been estimated (see section 3 Current GHG emission profile
for further information). The same approach using the time series of population is
followed to obtain the GHG emissions in all the projections period.
4D Wastewater treatment and discharge
This category was only partially estimated in the national inventory. For this reason, an
estimate based on population has been estimated (see section 3 Current GHG emission
profile for further information). The same approach using the time series of population is
followed to obtain the GHG emissions in all the projections period.
Projections of GHG emissions to 2030 in Tajikistan
Section 5 - Implemented and adopted
mitigation actions
The following are the mitigation actions under implementation since 2015 which lead to
GHG emission reductions in Tajikistan. Even if the mitigation action was implemented
before 2015, its impact is only estimated since 2015. The rationale for choosing 2015
as the reference year is to show the mitigation effort in Tajikistan since the first
submission of the NDC, i.e. 2015. The impact of these actions is considered in the WeM
scenario.
1. Energy
The following are the mitigation actions which lead to GHG emission reductions in the
energy sector in Tajikistan.
1.1. Regional Power Transmission Project
Background documents: The description of the project is available at
https://www.adb.org/projects/43150-022/main#project-overview.
Description of the action: The project is critical for energy security in Tajikistan and will
improve regional connectivity and support power trade. Additionally, the project will also
improve energy efficiency and overall performance in the power sector.
It targets the expansion and modernization of the electricity transmission network by
building two new 220 kV single-circuit transmission lines totaling 140 km of overhead line
(OHL). It will also in whole or partially rehabilitate six transmission substations at
Kairakkum, Asht, Geran, Rumi, Baipaza, and Regar. A third output is to put a SCADA
system in place which is linked to a National Dispatch Centre in Dushanbe, and 32 priority
substations across the country (capable of expansion to 204 national substations). The
construction of these facilities will be done through three design, supply and install
contracts, including testing and commissioning.
The project will also pave the way for much needed reforms by implementing a sector
operational performance improvement program targeting Barki Tojik. This program
comprises the following activities: the development of strategic and business plans and
corporate governance changes; commercial, operating and financial plans; project
management and training; the preparation of accounting and management information
systems; and the preparation of technical or operational performance audits. The
program also includes reviews of sector-wide policy and institutional issues followed by
a sector reform program with specific action plans and their implementation. The reform
Projections of GHG emissions to 2030 in Tajikistan
program will be supported by ADB through the proposed project implementation. Least-
cost sector infrastructure development master plan is an additional output.
Assumptions: The estimation of the mitigation impact is based on the assumption that
the grid loss will be reduced in the new transmission network, reducing the GHG
emissions of the national electricity system. GHG emissions loses from the transmission
network are calculated applying a default loss rate to the total emissions estimated for all
the electricity produced in the country. Total emissions from the production of electricity
are calculated using the grid emission factor, which is estimated splitting the GWh
produced (from the electric balance from the Agency for Statistics) by the emissions of
category 1A1ai Electricity generation, which accounts for all the emissions from fuel
combustion in national Power Plants.
The projections of electricity production follow the same approach used in the WoM for
category 1A1 Energy Industries, growing as the population forecast.
The impact of the mitigation action is estimated as a difference of the emissions
calculated in a reference scenario and a reduction scenario. The reference scenario
represents the emissions (in the scope of the action) before policy implementation. The
reduction scenario represents the emissions after policy implementation.
Calculation by scenario = Electricity production (GWh) x Grid EF (Gg CO2-eq / GWh) x
Grid loss (%) = Gg CO2-eq
Implementation period: 2010-2020. The impact of the project is accounted since its
completion in 2020.
Table 9. Reference scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units Source
Grid loss 18.60 %
UNEP-
GACMO
Amount transmitted National Total production GWh
Agency
for
Statistics
Grid emission factor 0.0052 Gg CO2-eq / GWh Calculated
Table 10. Reduction scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units Source
Grid loss 10 % Link
Amount transmitted National Total production GWh
Agency
for
Statistics
Grid emission factor 0.0052 Gg CO2-eq / GWh Calculated
Projections of GHG emissions to 2030 in Tajikistan
Results:
Table 11. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 20.48 11.01 9.47
2025 22.77 12.24 10.53
2030 25.32 13.61 11.71
Proposal of monitoring indicator: The implementation of the Regional Power
Transmission Project has been completed, however, the operational aspect will be
monitored through the following indicators:
Amount of electricity in GWh transported through the rehabilitated transmission
substations at Kairakkum, Asht, Geran, Rumi, Baipaza, and Regar.
Amount of electricity in GWh transported through the new single-circuit
transmission lines.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the usage of the new network will be the Ministry of Energy and Water Resources of the
Republic of Tajikistan.
Timing: The operation of this action will be monitored on a biannual basis.
Projections of GHG emissions to 2030 in Tajikistan
1.2. Green Energy Facility Project
Background documents: The description of the project is available at
https://www.ebrd.com/work-with-us/projects/psd/51666.html.
Description of the action: The project will enable authorities to rehabilitate the existing
electricity distribution and transmission infrastructure, improve energy efficiency and
reduce CO2 emissions. This will be achieved through the installation of smart meters and
the introduction of ASKUE (automated system for commercial metering of electricity) with
overall target of improving access to reliable power infrastructure.
Assumptions: There is no information about the number of meters installed, but the size
of the project is quite big (200,000,000 EUR), so it is assumed that smart meters are
installed in all households and business with current access to electricity. The impact of
other mitigation actions addressing the implementation of smart metering (such as
wholesale metering and transmission) are thus included under the impact of this
mitigation action.
Total GHG emissions from electricity are calculated using the grid emission factor, which
is estimated splitting the GWh produced (from the electric balance from the Agency for
Statistics) by the emissions of category 1A1ai Electricity generation, which accounts for
all the emissions from fuel combustion in national Power Plants for the production of
electricity.
The reduction of electricity consumption as a result of the installation of the smart
metering system is assumed to be 10%, as the average of the energy savings obtained
in several studies from the existent literature12.
Additionally, the energy demand and electricity consumption are projected using the
growth of the projected time series of population.
This project is complemented with other smart metering projects, which are not estimated
but considered in this calculation.
The impact of the mitigation action is estimated as follows:
Electricity consumption (GWh) x Reduction of energy consumption due to smart meters
x Grid EF (Gg CO2-eq / GWh) = Gg CO2-eq
Implementation period: 2020-2024
12 See for instance: https://www.eci.ox.ac.uk/research/energy/downloads/smart-metering-report.pdf https://www.sciencedirect.com/science/article/abs/pii/S0301421517302793?via%3
Projections of GHG emissions to 2030 in Tajikistan
Table 12. Reference scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Number of meters 0 Number
Grid emission factor 0.0052 Gg CO2-eq / GWh
Table 13. Reduction scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Reduction of electricity consumption 10 %
Number of meters ? Number
Grid emission factor 0.0052 Gg CO2-eq / GWh
Results:
Table 14. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 63.07 56.76 6.31
2030 70.13 63.12 7.01
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Number of smart meters installed in households.
Number of smart meters installed in businesses.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the installation of smart meters will be the Statistics Agency under the President of the
Republic of Tajikistan.
Timing: The implementation of this action will be monitored on a biannual basis.
Projections of GHG emissions to 2030 in Tajikistan
1.3. Obigarm-Nurobod Road Project
Background documents: The description of the project is available at
https://www.ebrd.com/work-with-us/projects/psd/49650.html.
Description of the action: The project consists of the construction of a 75 km long
detour of the existing section of M41 road between the towns of Obigarm and Nurobod,
which is planned to be inundated by the end of 2023. The M41 road is Tajikistan's primary
east to west road, which connects Dushanbe with the border to Kyrgyz Republic and
onwards to Kazakhstan and China.
The road is part of the CAREC corridor programme which seeks to expand economic
cooperation among the region's neighboring countries and is actively supported by
bilateral and multilateral development institutions. The Project will target one of the key
barriers to economic and social development in the country and efficient and reliable
functioning of transport corridors. The Project's principal objectives are the promotion of
regional trade via the development of reliable and safe road corridors, the development
of sustainable mechanisms for roads maintenance, and road safety improvements and
improvement of environmental and social operation standards.
Assumptions: This project will increase the vh*km, as the connection with neighboring
countries will be enhanced. Therefore, this project will have a positive impact on GDP,
but not in terms of GHG emissions. This PAM has not been estimated as its
implementation does not involve a direct GHG emission reduction.
Implementation period: 2019-2024
Results:
Table 15. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 NA NA NA
2030 NA NA NA
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Kilometers of road constructed.
Number of personal cars using the newly developed Obigarm-Nurobod road.
Number of freight transport using the newly developed Obigarm-Nurobod road.
Projections of GHG emissions to 2030 in Tajikistan
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the construction and the usage of the road will be the Ministry of Transport of the
Republic of Tajikistan.
Timing: The operation of this action will be monitored on a biannual basis.
Projections of GHG emissions to 2030 in Tajikistan
1.4. Khatlon Energy Loss Reduction Project
Background documents: The description of the project is available at
https://www.ebrd.com/work-with-us/projects/psd/49930.html.
Description of the action: This project will target the modernization of a low-voltage
distribution grid in the cities of Kulob and Bokhtar, the construction of a new and an
upgrade of the existing 110/35/10 kW substation in Kulob, and the installation of
automatic billing and metering systems in both cities.
Assumptions: The impact of this action is already considered under 1.1. Regional
Power Transmission Project and under 1.2. Green Energy Facility Project. Therefore, its
implementation does not involve additional GHG emission reductions.
Implementation period: 2019-2029
Results:
Table 16. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 IE IE IE
2020 IE IE IE
2025 IE IE IE
2030 IE IE IE
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Number of smart meters installed in Kulob.
Number of households equipped with automatic billing system in Kulob.
Number of smart meters installed in Bokhtar.
Number of households equipped with automatic billing system in Bokhtar.
Amount of electricity in GWh transported through the upgraded substation in
Kulob.
Amount of electricity in GWh transported through the new substation in Kulob.
Proposal of entity responsible for monitoring: The entities responsible for monitoring
this action will be the Statistics Agency under the President of the Republic of Tajikistan
and the Ministry of Energy and Water Resources of the Republic of Tajikistan.
Timing: The implementation of this action will be monitored on a biannual basis.
Projections of GHG emissions to 2030 in Tajikistan
1.5. Khatlon Public Transport
Background documents: The description of the project is available at
https://www.ebrd.com/work-with-us/projects/psd/khatlon-public-transport.html.
Description of the action: The project involves establishing a municipally owned
passenger transport operator providing services on basic routes in Kurgan-Tyube and its
suburban area in order to ensure a minimum standard of public transport service and
transport links.
It aims to improve public transport services in Khatlon Oblast, where the sector is poorly
regulated and lacking transparency. Regulation is currently limited and poorly enforced,
resulting in impaired service standards and environmental practices, and operational
efficiency is sub-optimal due to a lack of investment and operational resources.
Assumptions: The increase in GHG emissions in the transport sector in the area of the
project will be reduced by the implementation of public transport in the area of the project.
Because the project will only address a minimum standard of public transport that is in
place in the area, the impact of the mitigation action is not expected to be very significant.
The estimation of the impact of a mitigation action shifting private transportation to public
transportation requires information about the expected fleet, routes, and potential
passengers of the new public transport route. However, this information is not available
and only a rough estimate can be made.
Only 10 per cent of the population will use public transport (based on the share of public
transport in all transport modes of other countries
https://assets.publishing.service.gov.uk/government/uploads/system/uploads/attachme
nt_data/file/787488/tsgb-2018-report-summaries.pdf). For this 10 percent of the
population, the emissions will be reduced by a 70% (based on the assumption that on
average, public transport consumes 3.4 times less energy per passenger kilometer than
automobiles. This ratio is even more favorable during rush hour
(https://www.uitp.org/sites/default/files/Decarbonisation%20-
%20the%20public%20transport%20contribution.pdf)).
For the reference scenario, it uses category 1A3b Road transportation in the WoM
scenario. The emissions attributable to Kurgan-Tyube are estimated using the population
series.
Implementation period: 2017-2021
Table 17. Reduction scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Percentage of the population using public transport 0.1 %
Projections of GHG emissions to 2030 in Tajikistan
Variable Value Units
Reduction of emissions for the shift to public transport 0.7 %
Results:
Table 18. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 3.89 3.78 0.12
2030 4.04 3.92 0.12
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Number of provided services on the relevant routes.
Number of people in Kurgan-Tyube using private means of transport.
Number of people in Kurgan-Tuybe using public transport.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the shift to public transport will be the Ministry of Transport of the Republic of Tajikistan.
Timing: The implementation of this action will be monitored on a biannual basis.
Projections of GHG emissions to 2030 in Tajikistan
1.6. Qairokkum HPP Climate Resilience Upgrade
Background documents: The description of the project is available at
https://www.ebrd.com/work-with-us/projects/psd/qairokkum-hpp-climate-resilience-
upgrade.html.
Description of the action: The Project will complete rehabilitation and modernization of
the Qairokkum hydro power plant (the "Qairokkum HPP"), which is the only power
generation facility in the Sugb region of Northern Tajikistan. The Project is expected to:
increase the installed capacity by 32 MW which, together with the 16 MW increase
under the first phase (OPID 41553), will result in an increase of the existing
installed capacity from 126MW to 174MW by installing new turbines;
prevent unnecessary discharge of water through spillways and allow generation
of more electricity with the same flow of water;
raise the safety level of the power plant and the dam; and
strengthen the power plant’s resilience to the expected impacts of climate change
through continued physical upgrades designed to take into account projected
increases in climatic and hydrological variability.
The project has been finalized in 2020.
Assumptions: The estimation of the impact is performed applying the grid emission
factor to the new energy produced using the new generated capacity, with the emissions
of the new hydro plant assumed to be zero.
Total GHG emissions from electricity are calculated using the grid emission factor, which
is estimated splitting the GWh produced (from the electric balance from the Agency for
Statistics) by the emissions of category 1A1ai Electricity generation, which accounts for
all the emissions from fuel combustion in national Power Plants for the production of
electricity.
The capacity factor (hours of operation of the installed capacity) are calculated using
current data of electricity produced and capacity installed.
It is also assumed that in the absence of this action, the energy demand would have been
met using the same energy mix of year 2016 (the last inventory year).
Implementation period: 2016-2020
Table 19. Reference scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Grid emission factor 0.0052 Gg CO2-eq / GWh
Projections of GHG emissions to 2030 in Tajikistan
Table 20. Reduction scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
New capacity 32 MW
Capacity factor 3,590 Full time hours
Mew annual electricity generated 115 GWh
Grid emission factor 0.0052 Gg CO2-eq / GWh
Results:
Table 21. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 0.60 0.00 0.60
2025 0.60 0.00 0.60
2030 0.60 0.00 0.60
Proposal of monitoring indicator: The implementation of the modernization of the
Qairokkum power plant has been concluded, however, the operational aspect will be
monitored through the following indicators:
Amount of electricity in GWh generated by the modernized Qairokkum hydro
power plant.
Amount of electricity in GWh generated before the completed rehabilitation and
modernization of the Qairokkum hydro power plant.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the increased capacity of the hydro power plant will be the Ministry of Energy and Water
Resources of the Republic of Tajikistan.
Timing: The operation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
1.7. Golovnaya 240-Megawatt Hydropower Plant
Rehabilitation Project
Background documents: The description of the project is available at
https://www.adb.org/projects/46418-001/main#project-pds.
Description of the action: The proposed Project will increase supply of renewable
energy to national and regional power systems and refurbish electric and mechanical
equipment for power generation at Golovnaya Hydropower Plant (HPP) in Tajikistan. This
will increase availability of year-round clean power for domestic sales and for export to
Afghanistan. Furthermore, the Project will increase the generation capacity and
operational efficiency of the power plant.
The impact of the Project will be increased supply of renewable energy to national and
regional power systems from 743 GWh in 2012 to 1,130 GWh in 2026. It will generate an
increased weighted average generation efficiency of the power plant from a maximum
83% to 89%. Additionally, the rehabilitated Golovnaya HPP will have an increased
generation capacity from 240 MW to 252 MW.
Assumptions: The estimation of the impact is performed applying the grid emission
factor to the new energy produced using the new generated capacity, with the emissions
of the new hydro plant assumed to be zero.
Total GHG emissions from electricity are calculated using the grid emission factor, which
is estimated splitting the GWh produced (from the electric balance from the Agency for
Statistics) by the emissions of category 1A1ai Electricity generation, which accounts for
all the emissions from fuel combustion in national Power Plants for the production of
electricity.
The capacity factor (hours of operation of the installed capacity) are calculated using
current data of electricity produced and capacity installed.
It is also assumed that in the absence of this action, the energy demand would have been
met using the same energy mix of year 2016 (the last inventory year).
Implementation period: 2014-2022
Table 22. Reference scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Grid emission factor 0.0052 Gg CO2-eq / GWh
Table 23. Reduction scenario for the estimation of the potential GHG mitigation
impact
Projections of GHG emissions to 2030 in Tajikistan
Variable Value Units
New capacity 12 MW
Capacity factor 3,590 Full time hours
New annual electricity generated 43 GWh
Grid emission factor 0.0052 Gg CO2-eq / GWh
Results:
Table 24. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 0.23 0.00 0.23
2030 0.23 0.00 0.23
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Amount of electricity in GWh generated by the rehabilitated Golovnava hydro
power plant.
Amount of electricity in GWh generated before the completed rehabilitation of the
Golovnava hydro power plant.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the increased capacity of the hydro power plant will be the Ministry of Energy and Water
Resources of the Republic of Tajikistan.
Timing: The implementation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
1.8. Kulyab-Khalaikumb Road
Background documents: The description of the project is available at
https://www.isdb.org/projects/data/uid-pj0032508;.
Description of the action: The overall development objective of the project is to improve
the living conditions of the population and to support the economic growth of the country
by providing year-round, reliable and direct land transport service between the western
part of Tajikistan, including the Capital Dushanbe, and the eastern Region of Gorno-
Badakhshan.
Assumptions: This project will increase the vh*km, as the connection with neighboring
countries will be enhanced. Therefore, this project will have a positive impact on GDP,
but not in terms of GHG emissions. This PAM has not been estimated as its
implementation does not involve a direct GHG emission reduction.
Implementation period: 2017-2020
Results:
Table 25. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 NA NA NA
2030 NA NA NA
Proposal of monitoring indicator: The implementation of the Kulayab-Khalaikumb
Road has been completed, however, the operational aspect will be monitored through
the following indicators:
Number of personal cars using the newly developed Kulyab-Khalaikumb road.
Number of freight transport using the newly developed Kulyab-Khalaikumb road.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the usage of the newly developed road will be the Ministry of Transport of the Republic
of Tajikistan.
Timing: The operation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
1.9. Reconstruction of Ravshan Electricity
Substation Project (Islamic Development
Bank)
Background documents: The description of the project is available at
https://www.isdb.org/tenders/reconstruction-of-the-ravshan-electricity-substation-project
and at https://www.linerji-global.com/single-post/2015/10/27/Reconstruction-of-the-
Ravshan-Electricity-Substation.
Description of the action: The project aims at promoting economic growth and
improving the living standards in the Tursunzade city and Shahrinav regions through
supplying reliable electricity. The project would provide a huge support to agricultural
growth and setting up of small industries in these two regions and thus contribute to
poverty reduction.
The project consists of the supply and installation of two Power Transformers 220/110/10
kV (2x125MVA), Replacement of Electro Technical Equipment, Replacement of
Measuring and Control Equipment, Replacement of Relay Protection and Automation
Equipment, Replacement of Communication Equipment, Replacement of 220 kV SF6
Circuit Breakers, Replacement of 220 kV Current Transformers and Replacement of
Auxiliary Equipment, as well as equipment installation, reconstruction and site
improvement.
Assumptions: This project has an impact on the SF6 used in the electrical equipment.
However, this is not estimated in the inventory/WoM, so this PAM has not been
estimated.
Implementation period: 2014-2019
Results:
Table 26. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 NA NA NA
2030 NA NA NA
Proposal of monitoring indicator: The implementation of the reconstruction of the
Ravshan Electricity Substation has been concluded, however, the operational aspect will
be monitored through the following indicators:
Projections of GHG emissions to 2030 in Tajikistan
Amount of electricity in GWh transported through the reconstructed Ravshan
Electricity Substation.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the increased capacity of the electricity substation will be the Ministry of Energy and
Water Resources of the Republic of Tajikistan.
Timing: The operation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
1.10. Regional Power Transmission
Background documents: The description of the project is available at
https://www.adb.org/projects/43150-022/main#project-pds.
Description of the action: The Project will help Tajikistan achieve energy security,
improve regional connectivity, and support power trade. The Project will also improve
energy efficiency and overall performance in the power sector.
The project will build two new 220 kV single-circuit transmission lines totaling 140 km of
overhead line (OHL). It will also rehabilitate in whole or part six transmission substations
at Kairakkum, Asht, Geran, Rumi, Baipaza, and Regar. A third output is to put in place a
SCADA system linked to a National Dispatch Centre in Dushanbe, and 32 priority
substations across the country (capable of expansion to 204 national substations). By
doing so, it will expand and modernize electricity transmission systems, which will boost
energy trading with neighboring countries to meet winter shortages.
Assumptions: Transmission network modernization is a precondition to cutting system
losses, improving energy efficiency, and facilitating energy trade with neighboring
countries. However, this does not have direct GHG emission impacts that could be
estimated with the information available. This PAM has therefore not been estimated.
Implementation period: 2010-2020
Results:
Table 27. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 NA NA NA
2030 NA NA NA
Proposal of monitoring indicator: The implementation of the new single-circuit
transmission lines at the substations have been completed, however, the operational
aspect will be monitored through the following indicators:
Number of substations rehabilitated in whole.
Number of substations rehabilitated in part.
Number of SCADA systems put in place.
Amount of electricity in GWh transported through the rehabilitated six substations
at Kairakkum, Asht, Geran, Rumi, Baipaza, and Regar.
Amount of electricity in GWh transported through the newly implemented singe-
circuit transmission lines.
Projections of GHG emissions to 2030 in Tajikistan
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the increased capacity of the electricity substation will be the Ministry of Energy and
Water Resources of the Republic of Tajikistan.
Timing: The operation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
1.11. Wholesale Metering and Transmission
Background documents: The description of the project is available at
https://www.adb.org/projects/47017-003/main#project-pds;.
Description of the action: This project introduces a wholesale metering and billing
system for the national power company, Barki Tojik. The project will fund over 2,700
meters and introduce a new billing system to help reduce system power losses and
improve efficiencies. It will also build a 90 km transmission line connecting Panjakent
and Ayni regions to meet rising demand for power.
Assumptions: This PAM has not been estimated as it considered under 1.1. Regional
Power Transmission Project and 1.2 Green Energy Facility, and therefore does not
involve additional direct reductions of GHG emissions.
Implementation period: 2015-2020
Results:
Table 28. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 NA NA NA
2030 NA NA NA
Proposal of monitoring indicator: The implementation of this project has been
finalized, however, the operational aspect of this project will be monitored through the
following indicators:
Number of smart meters installed.
Number of households equipped with automatic billing system.
Amount of electricity in GWh transported through the new transmission line.
Proposal of entity responsible for monitoring: The entities responsible for monitoring
this action will be the Statistics Agency under the President of the Republic of Tajikistan
and the Ministry of Energy and Water Resources of the Republic of Tajikistan.
Timing: The operation of this action will be monitored on a biannual basis.
Projections of GHG emissions to 2030 in Tajikistan
1.12. Regional: Promoting Low-Carbon
Development in Central Asia Regional Economic
Cooperation Program Cities
Background documents: The description of the project is available at
https://www.adb.org/projects/52122-001/main#project-overview;.
Description of the action: In order to synchronize the systems and achieve power trade
target so that Tajikistan can start to export power to Uzbekistan on an islanded mode,
the relay protection system in Tajikistan has to be modernized and new interconnection
points have to be established. The project will install modern relays, circuit breakers,
instrumental transformers and ancillary equipment and systems at eight 220kV and two
500kV interconnection points, establish two new 500kV interconnections, and provide
capacity building to Barki Tojik staff in reliability of parallel operations.
Assumptions: Transmission network modernization is a precondition to cutting system
losses, improving energy efficiency, and facilitating energy trade with neighboring
countries. However, this does not have direct GHG emission impacts that could be
estimated with the information available. This PAM has therefore not been estimated.
Implementation period: 2019-2022
Results:
Table 29. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 NA NA NA
2030 NA NA NA
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Number of installed modern relays, circuit breakers, instrumental transformers
and ancillary equipment and systems.
Number of staff trained in reliability of parallel operations.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the modernization of Tajikistan’s relay protection system is the Ministry of Energy and
Water Resources of the Republic of Tajikistan.
Timing: The implementation of this action will be monitored on a biannual basis.
Projections of GHG emissions to 2030 in Tajikistan
1.13. Regional Corridor 1
Background documents: The description of the project is available at
https://www.adb.org/projects/49042-005/main#project-pds;.
Description of the action: The proposed additional financing will support an increase
in the scope of the current project by improving road section connecting Chashmasoron
to Kurgonteppa in Khalton province, improving safety in priority sections of the national
highway network.
Assumptions: This project will increase the vh*km, as the connection with neighboring
countries will be enhanced. Therefore, this project will have a positive impact on GDP,
but not in terms of GHG emissions. This PAM has not been estimated as its
implementation does not involve a direct GHG emission reduction.
Implementation period: 2018-2023
Results:
Table 30. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 NA NA NA
2030 NA NA NA
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Number of safety measures put in place.
Length in kilometers of improved road section.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the improved safety measures will be the Ministry of Transport of the Republic of
Tajikistan.
Timing: The implementation of this action will be monitored on a biannual basis.
Projections of GHG emissions to 2030 in Tajikistan
1.14. Regional Corridor 2
Background documents: The description of the project is available at
https://www.adb.org/projects/49042-004/main#project-pds;.
Description of the action: The project will improve the connectivity between the capital
Dushanbe and Kurgonteppa, which are two major cities and economic hubs in Tajikistan.
The road is a strategic north-south link, and one of the most heavily traveled roads in the
country.
Assumptions: This project will increase the vh*km, as the connection with neighboring
countries will be enhanced. Therefore, this project will have a positive impact on GDP,
but not in terms of GHG emissions. This PAM has not been estimated as its
implementation does not involve a direct GHG emission reduction.
Implementation period: 2017-2021
Results:
Table 31. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 NA NA NA
2030 NA NA NA
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Number of safety measures put in place.
Length in kilometers of improved road section.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the improved safety measures will be the Ministry of Transport of the Republic of
Tajikistan.
Timing: The implementation of this action will be monitored on a biannual basis.
Projections of GHG emissions to 2030 in Tajikistan
1.15. Regional Corridor 3
Background documents: The description of the project is available at
https://www.adb.org/projects/46543-002/main#project-pds;.
Description of the action: The impact of the project will be enhanced regional economic
cooperation and inclusive economic growth in Tajikistan. The outcome will be improved
regional network connectivity.
Assumptions: This project will increase the vh*km, as the connection with neighboring
countries will be enhanced. Therefore, this project will have a positive impact on GDP,
but not in terms of GHG emissions. This PAM has not been estimated as its
implementation does not involve a direct GHG emission reduction.
Implementation period: 2014-2019
Results:
Table 32. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 NA NA NA
2030 NA NA NA
Proposal of monitoring indicator: The implementation of this project has been
completed, however, the operational aspect of the project will be monitored through the
following indicators:
Number of safety measures put in place.
Length in kilometers of improved road section.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the improved safety measures will be the Ministry of Transport of the Republic of
Tajikistan.
Timing: The operation of this action will be monitored on a biannual basis.
Projections of GHG emissions to 2030 in Tajikistan
1.16. Regional Electricity Transport Project
Background documents: The description of the project is available at http://www.casa-
1000.org/indexr.php
Description of the action: This project demonstrates landmark cooperation among the
Kyrgyz Republic, Tajikistan, Pakistan, and Afghanistan. The modern and efficient CASA-
1000 electricity transmission system will help transform the region and signify an
important step toward realizing the planned Central Asia-South Asia Regional Electricity
Market (CASAREM).
Assumptions: It was assumed that this project would be covered in the estimate made
under Regional Power transmission project.
Implementation period: ongoing negotiations between countries
Results:
Table 33. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 IE IE IE
2020 IE IE IE
2025 IE IE IE
2030 IE IE IE
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Length in kilometers of newly developed transmission line system (PTL)
connecting the four countries.
Proposal of entity responsible for monitoring: The entity responsible for
implementing and realizing the new electricity transmission system will be the Ministry of
Energy and Water Resources of the Republic of Tajikistan.
Timing: The implementation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
1.17. Nurek Hydropower Rehabilitation Project
Background documents: The description of the project is available at
https://projects.worldbank.org/en/projects-operations/project-detail/P150816.
Description of the action: The objectives of the First Phase of Nurek Hydropower
Rehabilitation Project for Tajikistan are to rehabilitate and restore the generating capacity
of three power generating units of Nurek hydropower plant, improve their efficiency, and
strengthen the safety of the Nurek dam.
Assumptions: The electricity generation capacity is operating in the country in the
historical period. The project is essential to ensure the generation of electricity of the
plant, but additional capacity is not installed in the project. Additionally, the electricity
generation efficiency can be improved, but this leads to minimum GHG emission
reductions. For this reason, and for avoiding overlaps with other mitigation actions, the
impact of this action has not been estimated.
Implementation period: 2017-2023
Results:
Table 34. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 IE IE IE
2020 IE IE IE
2025 IE IE IE
2030 IE IE IE
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Number of rehabilitated and restored power generating units.
Amount of electricity in GWh generated by the rehabilitated Nurek hydro power
plant.
Amount of electricity in GWh generated before the completed rehabilitation of the
Nurek hydro power plant.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the improved hydropower measures will be the Ministry of Energy and Water Resources
of the Republic of Tajikistan.
Timing: The implementation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
1.18. Dushanbe Public Transport
Background documents: The description of the project is available at
https://www.ebrd.com/work-with-us/projects/psd/dushanbe-public-transport.html.
Description of the action: The Project will help the Dushanbe State Communal Unitary
Trolleybus Company to rehabilitate its trolleybus infrastructure in the City, increase
energy efficiency and make the trolleybus services in the City more sustainable.
The project will bring substantial benefits due to improving quality, reliability and safety
of the public transportation in Dushanbe and contribute to the overall improvement of
energy efficiency and environmental conditions. It has the potential to attract more
passengers, which in turn reduces traffic congestion on roads and therefore decreasing
fumes and emissions from vehicles. However, the project can potentially increase the
electrical consumption in the city of Dushanbe.
Assumptions: There is no information in the project documentation about potential
energy efficiency improvements, but as similar technologies have the same electricity
consumption reduction, it is assumed that the electricity consumption is reduced by 20%.
The electricity consumption for transport in Dushanbe is estimated using population as a
proxy.
GHG emissions are calculated applying the grid emission factor to total electricity
consumption for transport in Dushanbe. The grid emission factor is estimated splitting
the GWh produced (from the electric balance from the Agency for Statistics) by the
emissions of category 1A1ai Electricity generation, which accounts for all the emissions
from fuel combustion in national Power Plants for the production of electricity.
Implementation period: 2010-2021
Table 35. Reference scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Electricity consumption for transport - -
Table 36. Reduction scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Reduction of electricity consumption 20 %
Grid emission factor 0.0052 Gg CO2-eq / GWh
Projections of GHG emissions to 2030 in Tajikistan
Results:
Table 37. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 0.0214 0.0172 0.0043
2030 0.0238 0.0190 0.0048
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Number of rehabilitated power distribution infrastructures.
Number of rehabilitated power substations.
Number of operational trolleybuses.
Number of people in Dushanbe using private means of transport.
Number of people in Dushanbe using public transport.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the improved public transport system will be the Ministry of Transport of the Republic of
Tajikistan.
Timing: The implementation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
1.19. Dushanbe Public Transport – Khujand
buses
Background documents: The description of the project is available at
https://www.ebrd.com/work-with-us/projects/psd/dushanbe-public-transport.html.
Description of the action: The Project will help rehabilitate the trolleybus infrastructure
in the city of Khujand, increase energy efficiency and make the trolleybus services in the
city more sustainable.
The project will bring substantial benefits due to improving quality, reliability and safety
of the public transportation in Khujand and contribute to the overall improvement of
energy efficiency and environmental conditions. It has the potential to attract more
passengers, which in turn reduces traffic congestion on roads and therefore decreasing
fumes and emissions from vehicles. However, the project can potentially increase the
electrical consumption in the city of Khujand.
Assumptions: There is no information in the project documentation about potential
energy efficiency improvements, but as similar new trolleybus technologies have reduced
electricity consumption by 20% in other countries, it is also assumed that the electricity
consumption for this project will be 20%. The electricity consumption for transport in
Khujand is estimated using population as a proxy.
GHG emissions are calculated applying the grid emission factor to total electricity
consumption for transport in Dushanbe. The grid emission factor is estimated splitting
the GWh produced (from the electric balance from the Agency for Statistics) by the
emissions of category 1A1ai Electricity generation, which accounts for all the emissions
from fuel combustion in national Power Plants for the production of electricity.
Implementation period: 2015-2021
Table 38. Reference scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Electricity consumption for transport - -
Table 39. Reduction scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Reduction of electricity consumption 20 %
Grid emission factor 0.0052 Gg CO2-eq / GWh
Projections of GHG emissions to 2030 in Tajikistan
Results:
Table 40. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 0.0048 0.0039 0.0010
2030 0.0054 0.0043 0.0011
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Number of rehabilitated power distribution infrastructures.
Number of rehabilitated power substations.
Number of operational trolleybuses.
Number of people in Khujand using private means of transport.
Number of people in Khujand using public transport.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the improved public transport system will be the Ministry of Transport of the Republic of
Tajikistan.
Timing: The implementation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
1.20. Rural Electrification Project
Background documents: The description of the project is available at
http://documents.worldbank.org/curated/en/133181571939952501/pdf/Disclosable-
Version-of-the-ISR-Rural-Electrification-Project-P170132-Sequence-No-01.pdf.
Description of the action: The project development objective is to provide electricity
access to target settlements in GBAO and Khatlon regions. It will provide 43,126 people
with access to electricity under the project by household connections (grid or off-grid).
Assumptions: The estimation of the impact of the project is performed by applying the
grid emission factor to the energy demand of the people of this area, assuming the
necessary renewable capacity will be installed. The annual electricity consumption needs
are calculated using the data of population and energy consumption of Tajikistan.
GHG emissions are calculated applying the grid emission factor to total energy demand.
The grid emission factor is estimated splitting the GWh produced (from the electric
balance from the Agency for Statistics) by the emissions of category 1A1ai Electricity
generation, which accounts for all the emissions from fuel combustion in national Power
Plants for the production of electricity.
It is assumed that new renewable electricity capacity will be commissioned to meet the
demand of 43,126 people and that the emissions of the new renewable plant are zero.
Additionally, it is assumed that in the absence of this action, the energy demand would
have been met using the same energy mix of year 2016 (the last inventory year).
Implementation period: 2019-2025
Table 41. Reference scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Grid emission factor 0.0052 Gg CO2-eq / GWh
Table 42. Reduction scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Per capita electricity demand 0.001903 GWh
Population affected 43,126 Inhabitants
New annual electricity generated 82 GWh
Grid emission factor 0.0052 Gg CO2-eq / GWh
Projections of GHG emissions to 2030 in Tajikistan
Results:
Table 43. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 0.43 0.00 0.43
2025 0.43 0.00 0.43
2030 0.43 0.00 0.43
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Number of people with access to electricity by household grid connections.
Number of people with access to electricity by household off-grid connections.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the improved electricity access will be the Ministry for Energy and Water Resources of
the Republic of Tajikistan.
Timing: The implementation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
1.21. Sugd – Energy Loss Reduction Project
Background documents: The description of the project is available at
https://www.ebrd.com/work-with-us/projects/psd/sugd---energy-loss-reduction-
project.html.
Description of the action: The projects will supply and install new electricity meters,
meter reading systems and automated billing systems in the Sugd region of Tajikistan.
Its objectives are to reduce distribution network losses, improve quality of supply and
increase energy efficiency. As part of the project implementation, significant power loads
in the distribution network were pointed out resulting in poor quality of power supply and
associated losses; construction of new 110/10kV substations was considered.
Assumptions: The impact of this action is already considered under 1.1. Regional
Power Transmission Project and under 1.2. Green Energy Facility Project. Therefore, its
implementation does not involve additional GHG emission reductions.
Implementation period: 2015-2016
Results:
Table 44. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 IE IE IE
2020 IE IE IE
2025 IE IE IE
2030 IE IE IE
Proposal of monitoring indicator: The implementation of this project has been
finalized, however, the operational aspect of this project will be monitored through the
following indicators:
Number of newly installed electricity meters.
Number of newly installed meter reading systems.
Number of newly installed automated billing systems.
Number of newly constructed substations.
Proposal of entity responsible for monitoring: The entities responsible for monitoring
this action will be the Statistics Agency under the President of the Republic of Tajikistan
and the Ministry of Energy and Water Resources of the Republic of Tajikistan.
Timing: The operation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
1.22. Long-Term Small Hydro Power Plant
Construction Program
Background documents: The description of the project is available at
https://policy.asiapacificenergy.org/sites/default/files/Long-
term%20Program%20on%20Small%20Scale%20Power%20Plants%20Construction%2
0for%202009-2020%20%28RU%29.pdf.
Description of the action: This project involves the construction of 66 small hydropower
plants with a total capacity of 80 MW.
Assumptions: The estimation of the impact of the project is performed by applying the
grid emission factor to the new energy produced using the new generated capacity. The
capacity factor (hours of operation of the installed capacity) are calculated using current
data of electricity produced and capacity installed.
GHG emissions are calculated applying the grid emission factor to the new electricity
generated. The grid emission factor is estimated splitting the GWh produced (from the
electric balance from the Agency for Statistics) by the emissions of category 1A1ai
Electricity generation, which accounts for all the emissions from fuel combustion in
national Power Plants for the production of electricity.
It is assumed that the emissions of the new hydro plant are zero and that in the absence
of this action, the energy demand would have been met using the same energy mix of
year 2016 (the last inventory year).
Implementation period: 2009-2020
Table 45. Reference scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Grid emission factor 0.0052 Gg CO2-eq / GWh
Table 46. Reduction scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
New capacity 80 MW
Capacity factor 3,590 Full time hours
New annual electricity generated 287 GWh
Grid emission factor 0.0052 Gg CO2-eq / GWh
Projections of GHG emissions to 2030 in Tajikistan
Results:
Table 47. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 1.50 0.00 1.50
2025 1.50 0.00 1.50
2030 1.50 0.00 1.50
Proposal of monitoring indicator: The implementation of this project has been
finalized, however, the operational aspect of this project will be monitored through the
following indicators:
Number of small hydropower plants constructed.
Amount of electricity in GWh generated by the constructed small hydropower
plants.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the constructed small hydropower plants will be the Ministry of Energy and Water
Resources of the Republic of Tajikistan.
Timing: The operation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
1.23. Sustainable Fuels
Background documents: The description of the project is available at
https://www.mintrans.tj/sites/default/files/2017/gosudarstvennaya_celevaya_programm
a_razvitiya.pdf.
Description of the action: This mitigation action is encompassed under the "State
Target Program for the Development of the Transport Complex of the Republic of
Tajikistan". As part of this target program, Tajikistan will incentivize the change of
technologies in passenger cars, from diesel/gasoline cars to other cleaner alternatives
Assumptions: The estimation of the impact is based on the calculation of average
emissions by vehicle in 2026, with the project estimating that by 2026, 330 thousand
vehicles have shifted to gas.
Implementation period: 2012 - 2026
Table 48. Reference scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Average GHG emissions by vehicle 0.00033 Gg CO2-eq / vehicle
Table 49. Reduction scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
GHG emission reduction of LPG vehicles 0.11 %
Number of vehicles affected 330,000 Vehicles
Results:
Table 50. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 0.00 0.00 0.00
2020 45.88 40.83 5.05
2025 93.66 83.36 10.30
2030 96.17 85.59 10.58
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Number of incentivized technologies for passenger cars.
Number of diesel/gasoline cars in use in Tajikistan.
Projections of GHG emissions to 2030 in Tajikistan
Number of electric cars sold in Tajikistan.
Number of hybrid cars sold in Tajikistan.
Proposal of entity responsible for monitoring: The entities responsible for monitoring
the change of technologies will be the Ministry of Transport and the Ministry for Energy
and Water Resources of the Republic of Tajikistan.
Timing: The implementation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
2. Industrial Processes and Product Use
In the project no actions under implementation since 2015 and with impact in IPPU
emissions have been identified.
Projections of GHG emissions to 2030 in Tajikistan
3. AFOLU
The following projects, National Programmes and Strategies are the mitigation actions
which lead to GHG emission reductions in the AFOLU sector in Tajikistan.
3.1. Livestock and Pasture Development Project
Background documents: The impact brief of the project is available at
https://www.ifad.org/documents/38714170/41114919/TJ_LPDP_IA+brief.pdf/6221aa89-
fc03-2de0-892c-3376ce273cc5.
Description of the action: The Livestock and Pasture Development Project (LPDP) was
designed to increase the nutritional status and incomes of poor rural households in the
Khatlon region by boosting livestock productivity through (a) improvement of the
productive capacity of pastures and (b) through breeding and mating techniques
combined with (c) easier access to water.
The implementation of a rotational plan for pasture was expected to restore pasture land
and reduce degradation. According to the impact brief, 81,171 Ha of pasture land were
improved.
In addition, livestock and pasture development activities provided farming equipment and
improved seeds and fertilizers, built water points and sheds, and improved households’
access to rams for breeding and veterinary services. These activities were expected to
increase the water available for livestock, reduce the incidence of animal disease, and
improve self-sufficiency in fodder and grass production for the harshest seasons when
pastures cannot be reached. According to the impact brief of the project, the above
activities resulted in an increase of sheep and cattle weight by 17% and 27%
respectively.
The Project is supported by the International Fund for Agricultural Development.
Project duration: 2011-2017
Assumptions: The estimation of the mitigation impact is consistent with the data and
methods applied in the National Inventory of Tajikistan. The mitigation impact was
calculated by considering that the baseline emissions are those as included in the
inventory. Since the IPCC Tier 1 method was applied for the inventory, the same method
was applied to estimate the mitigation impact.
The potential GHG mitigation impact is associated to the following:
Increase of soil carbon stock by pastures’ improvement
Improve of livestock productivity
Projections of GHG emissions to 2030 in Tajikistan
Increase of soil carbon stock by pastures’ improvement
The general assumptions for the estimation of the mitigation impact that is linked to the
improvement of pastures are presented in the following table.
Table 51. General assumptions for the estimation of the soil carbon stock
increment due to pastures’ improvement
Land-use
category
Reference
soil
carbon
stock
Stock change factors
Representative
soil carbon
stock Parameter
s source
SOCref
(tC/ha) F(LU) F(MG) F(I) SOC (tC/ha)
Grassland
(pasture)
before
LPDP
4 1 0.9 1 3.6 National
inventory
Grassland-
improved
pasture
after LPDP
4 1 1.14 1 4.56
National
inventory
& 2006
IPCC GLs
Pasture land improved 81,171 Ha
Transition period for soils 20 years
Mitigation effect 14.29 ktCO2/year
Improve of livestock productivity
Main assumption: the animal population would have increased to cover meat demand in
the absence of productivity increase. It is assumed that sheep and cattle population
would have increased by 17% and 27%, respectively, as the respective weight
increments according to the impact brief of the project.
Table 52. General assumptions for the estimation of the mitigation impact due to
Improvement of sheep livestock productivity
Variable Value Units Source Comment
Increase of weight 17%
Impact brief
of the
project
Annual equivalent
of affected sheep
livestock in project
area
16,045 heads
Project
Supervision
report
(2017)
1 ram for 34 sheep, 510 rams in
total (147 day gestation period
averaged over an entire year).
1-2 young sheep per birth.
EF enteric
fermentation 5 kg CH4/head/yr
National
inventory
Projections of GHG emissions to 2030 in Tajikistan
Variable Value Units Source Comment
Increase in EF due
to 17% more
weight
1.1475 kg CH4/head/yr Tier 1 2006
IPCC GLs
EF manure
management for
sheep
0.15 kg CH4/head/yr National
inventory
GWP of CH4 21 SAR IPCC
Mitigation effect 0.23 kt CO2eq/year
Table 53. General assumptions for the estimation of the mitigation impact due to
Improvement of cattle livestock productivity
Variable Value Units Source Comment
Increase of weight 27 %
Impact brief
of the
project
Annual equivalent
of affected cattle
livestock in project
area
625 heads
Project
Supervision
report
(2017)
50 bulls, bull per cattle 1/50
(281 day gestation period
averaged over an entire year).
EF enteric
fermentation 47
kg
CH4/head/yr
National
inventory
Increase in EF due
to 27% more
weight
11 kg
CH4/head/yr
Tier 1 2006
IPCC GLs
EF manure
management for
cattle
1 kg
CH4/head/yr
National
inventory
GWP of CH4 21 - SAR IPCC
Mitigation effect 0.13 kt CO2eq/year
Results:
Table 54. GHG emission reduction impact (Gg CO2-eq)
Year Impact of Mitigation
action
2018 14.65
2020 14.65
2025 14.65
2030 14.65
Proposal of monitoring indicator: The implementation of this project has been
finalized, however, the operational aspect of this project will be monitored through the
following indicators:
Hectares of improved pasture land.
Number of provided farm equipment to households.
Projections of GHG emissions to 2030 in Tajikistan
Number of built water points and sheds.
Number of households with access to rams.
Number of households with access to veterinary services.
Number of livestock owned per household.
Proposal of entity responsible for monitoring: The entities responsible for monitoring
the Livestock and Pasture Development Project will be the Ministry of Agriculture and
the Ministry of Energy and Water Resources of the Republic of Tajikistan.
Timing: The operation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
3.2. Livestock and Pasture Development Project
II
Background documents: The description of the project is available at
https://www.ifad.org/en/web/operations/project/id/2000000977/country/tajikistan.
Description of the action: The Livestock and Pasture Development Project II builds on
LPDP Phase I. The second of the project will reach out to an additional 38,000 rural
households in at least five communities in five districts of the Khatlon region. The project's
development goal is to contribute to the reduction of poverty in the Khatlon region and to
increase the nutritional status and incomes of some 38,000 poor households by
enhancing livestock productivity and resilience to climate change. In particular, the
project will focus on:
developing institutions
enhancing productivity and improving animal health
developing pasture management
The Project is supported by the International Fund for Agricultural Development.
Project duration: 2015-2021
Assumptions: The estimation of the mitigation impact is consistent with the data and
methods applied in the National Inventory of Tajikistan. The mitigation impact was
calculated by considering that the baseline emissions are those as included in the
inventory. Since the IPCC Tier 1 method was applied for the inventory, the same method
was applied to estimate the mitigation impact.
The potential GHG mitigation impact is associated to the following:
Increase of soil carbon stock by pastures’ improvement
Improve of livestock productivity
Increase of soil carbon stock by pastures’ improvement
The general assumptions for the estimation of the mitigation impact that is linked to the
improvement of pastures are presented in the following table.
Table 55. General assumptions for the estimation of the soil carbon stock
increment due to pastures’ improvement
Projections of GHG emissions to 2030 in Tajikistan
Land-use
category
Reference
soil
carbon
stock
Stock change factors
Representative
soil carbon
stock Parameter
s source
SOCref
(tC/ha) F(LU) F(MG) F(I) SOC (tC/ha)
Grassland
(pasture)
before
LPDP
4 1 0.9 1 3.6 National
inventory
Grassland-
improved
pasture
after LPDP
4 1 1.14 1 4.56
National
inventory
& 2006
IPCC GLs
Pasture land improved 95,000 Ha
Transition period for soils 20 years
Mitigation effect 16.72 ktCO2/year
Improve of livestock productivity
Main assumption: the animal population would have increased to cover meat demand in
the absence of productivity increase. It is assumed that sheep and cattle population
would have increase by 17% and 27%, respectively, as the respective weight increments
according to the impact brief of the LPDP I project.
Table 56. General assumptions for the estimation of the mitigation impact due to
Improvement of sheep livestock productivity
Variable Value Units Source Comment
Increase of weight 17%
Impact brief
of the
project
Annual equivalent
of affected sheep
livestock in project
area
50,431 heads
Project
Supervision
report
(2017)
1 ram for 34 sheep, 1603 rams
in total (147 day gestation
period averaged over an entire
year). 1-2 young sheep per
birth.
EF enteric
fermentation 5
kg
CH4/head/yr
National
inventory
Increase in EF due
to 17% more
weight
1.1475 kg
CH4/head/yr
Tier 1 2006
IPCC GLs
EF manure
management for
sheep
0.15 kg
CH4/head/yr
National
inventory
GWP of CH4 21 SAR IPCC
Mitigation effect 0.72 kt CO2eq/year
Projections of GHG emissions to 2030 in Tajikistan
Table 57. General assumptions for the estimation of the mitigation impact due to
Improvement of cattle livestock productivity
Variable Value Units Source Comment
Increase of weight 27%
Impact brief
of the
project
Annual equivalent
of affected cattle
livestock in project
area
3,227 heads
Project
Supervision
report
(2017)
258 bulls, bull per cattle 1/50
(281 day gestation period
averaged over an entire year).
EF enteric
fermentation 47
kg
CH4/head/yr
National
inventory
Increase in EF due
to 27% more
weight
11 kg
CH4/head/yr
Tier 1 2006
IPCC GLs
EF manure
management for
cattle
1 kg
CH4/head/yr
National
inventory
GWP of CH4 21 SAR IPCC
Mitigation effect 0.68 kt CO2eq/year
Results:
Table 58. GHG emission reduction impact (Gg CO2-eq)
Year Impact of Mitigation
action
2022 18.12
2025 18.12
2030 18.12
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Hectares of improved pasture land.
Number of households with access to veterinary services.
Number of livestock owned per household.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the second phase of the Livestock and Pasture Development Project will be the Ministry
of Agriculture of the Republic of Tajikistan.
Timing: The implementation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
3.3. Project "Support to Agriculture in the
Community"
Background documents: The description of the project is available at
https://www.ifad.org/en/web/operations/project/id/2000001284. The most recent
document about the project is the "Tajikistan 2000001284: CASP Supervision Report
January 2020".
Description of the action: The project is designed to stimulate inclusive economic
growth and poverty reduction in poor rural communities through improving access to
productive infrastructure and services that lead to sustainable agricultural production and
equitable returns. It aims to tackle the lack of access to modern farming technologies of
the poorest smallholders in remote villages and at supporting private-sector mechanized
service providers and maintenance services.
Project activities are organized into two components:
a) Strengthening rural institutions, by developing business-oriented small-plots
farmers groups and building the capacities of implementation service providers;
and
b) Improving agricultural productivity and business linkages, through stimulating the
use of modern agricultural technologies and infrastructures.
The project areas include some 225 villages in selected areas of Soghd and Khatlon
Regions and the Districts of Republican Subordination Region, thus reaching up to
48,160 households. Primary target groups are rural people living in extreme poverty, who
are either landless or producing a bare subsistence minimum on household plots;
subsistence and semi-subsistence farmers; rural underemployed.
The Project is supported by the International Fund for Agricultural Development.
Project duration: 2017-2024
Assumptions: The most recent document about the project ("Tajikistan 2000001284:
CASP Supervision Report January 2020") contains some quantitative information
(indicators) under Component 2, which might be linked with potential GHG mitigation
impact.
More specifically, the aim of component 2 of the project, which is entitled "Improvement
of agricultural productivity and business linkages", is to enhance the selected
communities’ productive capacity and production through the adoption of modern
agricultural technologies and equipment. This outcome will be measured by the following
indicators: (i) at least 20% increase in agricultural productivity (by main commodities);
and (ii) an additional 20,000 hectares serviced by machinery service providers (AMSPs).
We can make the following observations:
Projections of GHG emissions to 2030 in Tajikistan
i. The 20% in agriculture productivity seems that is not related to an increment of
perennial crops but annual cropping. An increase of annual cropping may result
in increased retain of crop residues and thus increase in soil organic content from
residue input to soils. However, this increase will be lower compared to the one
that could have been achieved by increasing the perennial crops.
ii. On the other hand, an additional 20,000 hectares serviced by machinery service
providers would probably be linked with an increase of tillage activities, which
result in a decrease of soil organic carbon content.
Due to the above opposite and uncertain potential effects on GHG emissions of the
project, it is decided not to estimate a potential GHG mitigation impact associated to its
implementation.
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Number of smallholders with access to modern farming technologies.
Number of smallholders with access to modern farming infrastructures.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the communal agricultural support will be the Ministry of Agriculture of the Republic of
Tajikistan.
Timing: The implementation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
3.4. Tajikistan Agriculture Commercialization
Project
Background documents: The description of the project is available at
https://projects.worldbank.org/en/projects-operations/project-detail/P132652. The most
resent "Implementation Status and results report" was issued on 10 NOV 2019.
Description of the action: The project development objective (PDO) of the Agriculture
Commercialization Project for Tajikistan is to increase the commercialization of farm and
agribusiness products by improving the performance of selected value chains and
productive partnerships through increased access to finance and strengthened capacity
of project beneficiaries. The project comprises three components. The first component,
Improvement of Technical Knowledge and Skills in Support of Commercialization, will
contribute to the PDO by improving the technical knowledge and skills of participants in
key agricultural value chains and productive partnerships. Support will be provided in the
form of group-based interventions (training) and individual technical assistance (advisory
services). An estimated 12,500 people will benefit, including male and female heads of
small-scale farms, and management and staff of agri-business enterprises and agro-
processors. The second component, Access to Finance for Agribusiness Enterprises and
Small-Scale Commercial Farms, will support the commercialization of agricultural
products by improving access to medium-term finance for the larger agri-business
enterprises, providing start-up capital in the form of grants for small-scale farms involved
in productive partnerships, and by ensuring the availability of financing for value chain
support, which often requires short-term financing (such as, for contract farming schemes
and post-harvest handling activities). Potential investments include improved on-farm
technology, storage, processing, new products, marketing, quality enhancement and
food safety. An estimated 350 sub-financings are expected to be provided under this
component. The third component, Institutional Capacity Building and Project
Management, will strengthen the critical elements of the institutional framework and the
sector's academic knowledge base.
The Project is supported by the World Bank.
Project duration: 2014-2022
Assumptions: According to WB website, the project is associated to 24% of mitigation
of climate change.
The project is comprised by 4 components, namely:
Component I: Improvement of Technical Knowledge and Skills in Support of
Commercialization:(Cost $6.70M)
Component II: Access to Finance for Agri-Business Enterprises and Small-Scale
Commercial Farms:(Cost $22.90 M)
Projections of GHG emissions to 2030 in Tajikistan
Component III: Institutional Capacity Building and Project Management:(Cost
$4.90 M)
Component IV: Entrepreneurship Training and Business Development Services
to MSMEs:(Cost $2.50 M)
However, no additional information is provided in the reports of the project (e.g. the recent
implementation and status report) that could be used to estimate the potential GHG
mitigation impact of the project. For example, no mitigation targets and respective
indicators were provided for the 4 components of the project, which are related to
activities, practices or technologies that could be linked to potential GHG impacts.
Example of such activities/practices/technologies could be the rotational grazing or
cultivation; agroforestry or silvo-pastoral systems; increase of the use of perennial crops;
feeding strategies to improve the quality of forage, changing herd management practices,
optimizing health and reproductive capacity, pasture management etc.
Therefore, the potential mitigation GHG impact of this project could not be estimated.
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Number of people with improved technical knowledge and skills key agricultural
value chains.
Number of larger agri-businesses with access to medium-term finance.
Number of small-scale farmers with access to start-up capital grants.
Number of people with access to finance for value chain support.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the commercialization of farm and agribusiness products will be the Ministry of
Agriculture of the Republic of Tajikistan.
Timing: The implementation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
3.5. Dangara Valley Irrigation Project, Phase III
Background documents: The description of the project is available at
https://www.akelik.az/en/dangara-valley-irrigation-project-phase-iii.html.
Description of the action: Dangara Valley Irrigation Project is aimed at increasing
agricultural productivity in Dangara district of the Republic of Tajikistan. The Project will
also improve the water resources management of irrigation infrastructure through further
improvement of outcomes achieved under the Dangara Valley Irrigation Project, Phase-
I and Phase-II. This Project places emphasis on the improved water management of
combined irrigation and drainage system in general and on the irrigation aspects of the
system in particular. It is anticipated that this contract shall be the contract for Package
2 to carry out civil works.
The Project is supported by the Islamic Development Bank.
Project duration: 2016-2018
Assumptions: Dangara Valley project aims at increasing agricultural productivity by
improving irrigation infrastructure. Irrigation development is undertaken because of its
potential benefits in increasing farm level physical productivity. However, the relative
contribution of irrigation could result to both an increase and decrease of emissions of
GHGs. More specifically according to Kulshreshtha & Junkins (2001)13:
1. When water is released and applied to the fields, there may be a change in
cultural practices, as well as in the enterprise mix on the farm. These changes
could significantly alter the production mix, input demand for factors of production,
and may lead to increased emissions of GHGs. Major sources of such emissions
include the application of fertilizer and manure to crops, the decomposition of crop
residues, production of legume crops leading to fixing of nitrogen in the soil, and
soil carbon sequestration through tillage practices. These production-related
emissions are the direct farm-level emissions from agriculture. Emissions are also
associated to the storage of water in new reservoirs.
2. One of the major changes under irrigation may be the retention of nitrogen and
carbon in the soils. Where levels under natural conditions were low, as in the case
of Tajikistan, an increase in the total nitrogen and total carbon in irrigated fields is
13 Surendra Kulshreshtha & Bruce Junkins (2001) Effect of Irrigation Development on Greenhouse Gas Emissions in Alberta and Saskatchewan , Canadian Water Resources Journal, 26:1, 107-127, DOI: 10.4296/cwrj2601107
Projections of GHG emissions to 2030 in Tajikistan
expected. However, where initial levels were high, irrigation led to lower levels of
total nitrogen and carbon.
In addition, Lueking and Schepers (1985)14 have concluded by conducting field studies
that irrigation development has increased the total N and total C in cases where these
values were very low in the native condition. Furthermore, according to the IPCC special
report on Land Use, Land-Use Change and Forestry (2000)15, because most irrigation is
located in arid and semi-arid regions, many irrigable soils are inherently low in soil organic
carbon in their native state converting dryland soils to irrigated agriculture may increase
soil organic carbon content in the soil by 0.05-0.15 t C ha-1 yr-1, with a modal rate of
0.10 t C ha-1 yr-1.
Given the poor organic matter content of soil in Tajikistan, it is decided to estimate the
potential GHG mitigation impact of the Dangara Valley irrigation project by assuming that
dryland soils were converted to irrigated agriculture which results in an increase of soil
organic carbon content in the soil by a modal rate of 0.10 t C ha-1 yr-1. .
Table 59. General assumptions for the estimation of the increase of SOC due to
improved irrigation
Variable Value Units
Area covered by the project 1750 ha
Increase of soil organic carbon content 0.1 t C ha-1 yr-1
Mitigation effect 0.64 ktCO2/year
Results:
Table 60. GHG emission reduction impact (Gg CO2-eq)
Year Impact of Mitigation
action
2019 0.64
2020 0.64
2025 0.64
2030 0.64
14 LUEKJNG & SCHEPERS: CHANGES IN CARBON AND NITROGEN DUE TO IRRIGATED CORN DEVELOPMENT, SOIL SCI. SOC. AM. J., VOL. 49, 1985.
15 IPCC, 2000 - Robert T. Watson, Ian R. Noble, Bert Bolin, N. H. Ravindranath, David J. Verardo and David J. Dokken (Eds.), Land Use, Land-Use Change and Forestry, Cambridge University Press, UK. pp 375
Projections of GHG emissions to 2030 in Tajikistan
Proposal of monitoring indicator: The implementation of this project has been
finalized, however, the operational aspect of this project will be monitored through the
following indicators:
Hectares of irrigated land after the implementation of the Dangara Valley Project.
Hectares of irrigated land before the implementation of the Dangara Valley
Project.
Agricultural productivity in the Dangara district.
Proposal of entity responsible for monitoring: The entities responsible for monitoring
the increased agricultural productivity will be the Ministry of Agriculture and the Ministry
of Energy and Water Resources of the Republic of Tajikistan.
Timing: The operation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
3.6. Tajikistan Second Public Employment for
Sustainable Agriculture and Water
Resources Management Project
Background documents: The description of the project is available at
https://projects.worldbank.org/en/projects-operations/project-
detail/P133327?lang=en#abstract. The most resent "Implementation Status and results
report" was issued on 30 DEC2019.
Description of the action: The development objectives of the Second Public
Employment for Sustainable Agriculture and Water Resources Management Project are
to: provide employment to food-insecure people through the rehabilitation of irrigation
and drainage infrastructure, increase crop production in response to improved irrigation
and drainage infrastructure, and support the development of improved policies and
institutions for water resource management, as a means to improve food availability and
food access for low-income people in poor rural areas supported by the project. There
are three components to the project. The first component of the project is public works
and rehabilitation of irrigation and drainage infrastructure. The second component of the
project is assistance in water resources management, including technical assistance for
policy and institutional reform. The third component of the project is project management.
A Project Management Unit (PMU) to be managed under the World Bank-financed
Ferghana valley water resource management project will be the main implementation
agency. It will be responsible for: implementation and coordination, financial
management and procurement, communication and awareness programs,
environmental management and safeguards, and monitoring and evaluation.
The Project is supported by the World Bank.
Project duration: 2012-2020
Assumptions: This project aims at increase crop production in response to improved
irrigation and drainage infrastructure, and support the development of improved policies
and institutions for water resource management
As in the case of Dangara Valley Irrigation Project, given the poor organic matter content
of soil in Tajikistan, it is decided to estimate the potential GHG mitigation impact of the
irrigation project by assuming that dryland soils were converted to irrigated agriculture
Projections of GHG emissions to 2030 in Tajikistan
which results in an increase of soil organic carbon content in the soil by a modal rate of
0.10 t C ha-1 yr-116.
Table 61. General assumptions for the estimation of the increase of SOC due to
improved irrigation
Variable Value Units
Area covered by the project 251528 ha
Increase of soil organic carbon content 0.1 t C ha-1 yr-1
Mitigation effect 92.23 ktCO2/year
Results:
Table 62. GHG emission reduction impact (Gg CO2-eq)
Year Impact of Mitigation
action
2020 92.23
2025 92.23
2030 92.23
Proposal of monitoring indicator: The implementation of this project has been
finalized, however, the operational aspect of this project will be monitored through the
following indicators:
Number of newly employed people through the rehabilitation of irrigation and
drainage infrastructure.
Number of newly developed or improved policies and institutions for water
resource management
Crop production after the implementation of the improved irrigation and drainage
infrastructure.
Proposal of entity responsible for monitoring: The entities responsible for monitoring
the project will be the Ministry of Agriculture and the Ministry of Energy and Water
Resources of the Republic of Tajikistan.
Timing: The operation of this action will be monitored on an annual basis.
16 IPCC, 2000 - Robert T. Watson, Ian R. Noble, Bert Bolin, N. H. Ravindranath, David J. Verardo and David J. Dokken (Eds.), Land Use, Land-Use Change and Forestry, Cambridge University Press, UK. pp 375
Projections of GHG emissions to 2030 in Tajikistan
3.7. Project "Reconstruction of the irrigation
system and improvement of its management
in the Zerafshan River Basin"
Background documents: The description of the project is available at
https://projects.worldbank.org/en/projects-operations/project-
detail/P133327?lang=en#abstract. The most resent "Implementation Status and results
report" was issued on 30 DEC2019.
Description of the action: The project development objectives are to help the
Government of Tajikistan (i) strengthen the institutional base for irrigation planning and
management in the Zarafshon river basin; and (ii) improve the condition and
management of irrigation infrastructure in the Zarafshon river basin and adjacent districts
in the Syr-Darya basin. The project will increase food availability for rural people in the
project area and as such, contribute to the overarching objective of improving food
security.
The Project is supported by the World Bank.
Project duration: 2018-2020
Assumptions: This project aims at increase of crop production in response to improved
irrigation and drainage infrastructure.
As in the case of Dangara Valley Irrigation Project, given the poor organic matter content
of soil in Tajikistan, it is decided to estimate the potential GHG mitigation impact of the
irrigation project by assuming that dryland soils were converted to irrigated agriculture
which results in an increase of soil organic carbon content in the soil by a modal rate of
0.10 t C ha-1 yr-117.
Table 63. General assumptions for the estimation of the increase of SOC due to
improved irrigation
Variable Value Units
Area covered by the project 21000 ha
Increase of soil organic carbon content 0.1 t C ha-1 yr-1
Mitigation effect 7.70 ktCO2/year
17 IPCC, 2000 - Robert T. Watson, Ian R. Noble, Bert Bolin, N. H. Ravindranath, David J. Verardo and David J. Dokken (Eds.), Land Use, Land-Use Change and Forestry, Cambridge University Press, UK. pp 375
Projections of GHG emissions to 2030 in Tajikistan
Results:
Table 64. GHG emission reduction impact (Gg CO2-eq)
Year Impact of Mitigation
action
2021 7.70
2025 7.70
2030 7.70
Proposal of monitoring indicator: The implementation of this project has been
finalized, however, the operational aspect of this project will be monitored through the
following indicators:
Crop production after the implementation of the improved irrigation and drainage
infrastructure.
Number of rural people in the Zarafshon river basin with sufficient access to food.
Proposal of entity responsible for monitoring: The entities responsible for monitoring
the increased crop production will be the Ministry of Agriculture and the Ministry of
Energy and Water Resources of the Republic of Tajikistan.
Timing: The operation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
3.8. Building Climate Resilience in the Pyanj
River Basin Project
Background documents: The description of the project is available at
https://www.adb.org/projects/45354-002/main#project-overview.
Description of the action: The project aims to increase resilience to climate vulnerability
and change of communities in the Pyanj River Basin. The project's impact will be
improved livelihoods of Pyanj River Basin communities vulnerable to climate variability
and change. The project's outcome will be reduced adverse effects of climate variability
and climate change in 59 villages in 19 jamoats in the Pyanj River Basin.
The project is protecting at least 1,700 hectares of land from floods; providing 1,450
hectares of land with irrigation water; providing at least 4,150 households with a safe
water supply; and making microfinance services available to at least 1,000 households.
The Project is supported by the Asian Development Bank.
Project duration: 2013-2019
Assumptions: This project aims at increase of crop production in response to improved
irrigation.
As in the case of Dangara Valley Irrigation Project, given the poor organic matter content
of soil in Tajikistan, it is decided to estimate the potential GHG mitigation impact of the
irrigation project by assuming that dryland soils were converted to irrigated agriculture
which results in an increase of soil organic carbon content in the soil by a modal rate of
0.10 t C ha-1 yr-118.
Table 65. General assumptions for the estimation of the increase of SOC due to
improved irrigation
Variable Value Units
Area covered by the project 1450 ha
Increase of soil organic carbon content 0.1 t C ha-1 yr-1
Mitigation effect 0.53 ktCO2/year
18 IPCC, 2000 - Robert T. Watson, Ian R. Noble, Bert Bolin, N. H. Ravindranath, David J. Verardo and David J. Dokken (Eds.), Land Use, Land-Use Change and Forestry, Cambridge University Press, UK. pp 375
Projections of GHG emissions to 2030 in Tajikistan
Results:
Table 66. GHG emission reduction impact (Gg CO2-eq)
Year Impact of Mitigation
action
2020 0.53
2025 0.53
2030 0.53
Proposal of monitoring indicator: The implementation of this project has been
finalized, however, the operational aspect of this project will be monitored through the
following indicators:
Hectares of protected land from floods.
Hectares of land equipped with water irrigation systems.
Number of households with a safe water supply.
Number of households with access to microfinance services.
Proposal of entity responsible for monitoring: The entities responsible for monitoring
the climate resiliency in the Pyanj River Basin will be the Ministry of Agriculture and the
Ministry of Energy and Water Resources of the Republic of Tajikistan.
Timing: The operation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
3.9. Climate Adaptation and Mitigation Program
for Aral Sea Basin CAMP4ASB
Background documents: The description of the project is available at
https://projects.worldbank.org/en/projects-operations/project-detail/P151363.
Description of the action: The development objective of the Climate Adaptation and
Mitigation Program for the Aral Sea Basin Project for Central Asia is to enhance regionally
coordinated access to improved climate change knowledge services for key stakeholders
(e.g., policy makers, communities, and civil society) in participating Central Asian
countries, as well as to increase investments and capacity building that, combined, will
address climate challenges common to these countries. The project comprises of three
components. The first component, regional climate knowledge services, will provide
technical assistance, as well as minor civil works, goods (including software and
equipment), and training, at both the regional and national levels, to develop a unified,
integrated regional analytical platform for climate-resilient and low emission
development, with improved data, information, knowledge, and decision-support tools.
The second component, regional climate investment facility, will provide technical
assistance and facilitation support to plan, implement, and manage climate investments.
The second component consists of following two sub-components: (i) investment
financing; and (ii) capacity building and community support. The third component,
regional and national coordination consists of the following two sub-components: (i)
regional coordination; and (ii) national coordination.
The Project is supported by the World Bank.
Project duration: 2015-2021
Assumptions: This project aims at enhancing regionally coordinated access to improved
climate change knowledge services for key stakeholders (e.g., policy makers,
communities, and civil society) in participating Central Asian countries, as well as to
increased investments and capacity building that, combined, will address climate
challenges common to these countries. It is not linked with a direct - quantifiable
mitigation impact, as it mainly refers to capacity building, regional cooperation and
coordination, improved knowledge services.
In addition, the information that is provided in the reports of the project (e.g. the recent
implementation and status report) is not adequate for estimating the potential GHG
mitigation impact of the project. For example, no mitigation targets and respective
indicators were provided, which are related to activities, practices or technologies that
could be linked to potential GHG impacts. Example of such
activities/practices/technologies could be the rotational grazing or cultivation;
agroforestry or silvo-pastoral systems; increase of the use of perennial crops; feeding
strategies to improve the quality of forage, changing herd management practices,
optimizing health and reproductive capacity, pasture management etc.
Projections of GHG emissions to 2030 in Tajikistan
Therefore, the potential mitigation GHG impact of this project could not be estimated.
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Number of stakeholders with climate change knowledge on climate-resilient and
low emission development.
Quantity of investments to address climate change challenges.
Number of capacity building and community support activities carried out.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the climate adaptation and mitigation program will be the Committee for Environmental
Protection under the Government of the Republic of Tajikistan.
Timing: The implementation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
3.10. Climate Adaptation through Sustainable
Forestry in Important River Catchment Areas
in Tajikistan (CAFT)
Background documents: The description of the project is available at
https://www.giz.de/en/worldwide/29916.html.
Description of the action: The objective of the CAFT project is: “Rehabilitation,
conservation and sustainable use of forests contribute to the adaptation of the country to
climate change and the conservation of biodiversity, as well as to the improvement of
livelihoods of the local population in the project areas”.
The CAFT project is the financial upscaling and follow up phase based on the lessons
learned and best practice of the GIZ project “Adaptation to Climate Change through
Sustainable Forest Management”. Both projects promoting Joint Forest Management
(JFM) and institutional capacity building of the Forestry Agency and State Forest
Enterprises (SFE) to be able to carry out sustainable forest management. The
components of the project are the following:
Afforestation and forest rehabilitation: Suitable project areas are identified, the
SFE and the JFM users carrying out forest planting activities according to the
approved Afforestation Manual.
Elaboration of forest management plans: Forest and Pasture Management Plans
are developed and implemented, including incentive packages and the promotion
of nurseries.
Joint Forest Management (JFM): Awareness campaigns along with a natural
resource assessment leading to an increase of JFM contracts with micro-forest
management plans.
Forest and plantation protection: On community level Pasture User Unions (PUU)
are supported with Pasture Mgt. Plans including incentives to reduce pasture and
forest user conflicts.
Institutional capacity building: The capacities of the Forestry Agency, staff of
SFEs and JFM user groups are increased to be able to carry out forest related
activities in a sustainable way.
The Project is supported by the German Development Bank.
Project duration: 2013-2018
Assumptions: Since the start of the project up to June 2018, 5,944 ha of forest area
were afforested and rehabilitated. The potential GHG mitigation impact will be estimated
by calculating the annual increase of biomass carbon stocks of afforested lands. The
same method and parameters are used as in the national inventory.
Projections of GHG emissions to 2030 in Tajikistan
Table 67. General assumptions for the estimation of the potential GHG mitigation
impact
Variable Value Units Source
Afforested land 5944 ha
Average annual above-ground
biomass growth, Gw 6 t dm/(ha yr)
2006 IPCC GLs,
subtropical steppe
Ratio of below-ground biomass
to above-ground biomass, R 0.56 2006 IPCC GLs
Average annual biomass
growth above- and below-
ground, Gtotal
9.36 t dm/(ha yr)
Carbon fraction of dry matter,
CF 0.49 tC / t dm 2006 IPCC GLs
Annual increase in biomass
carbon stocks due to biomass
growth ΔCG
27261.56 tC/yr
Annual loss of carbon ΔCL 10%
Mitigation effect 89.96 ktCO2/year
Results:
Table 68. GHG emission reduction impact (Gg CO2-eq)
Year Impact of Mitigation
action
2019 89.96
2020 89.96
2025 89.96
2030 89.96
Proposal of monitoring indicator: The implementation of this project has been
finalized, however, the operational aspect of this project will be monitored through the
following indicators:
Hectares of afforested and rehabilitated forest area.
Hectares of forest and plantations protected under the project.
Number of newly developed and implemented forest and pasture management
plans.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the sustainable forest management project will be the Forestry Agency under the
Government of the Republic of Tajikistan.
Timing: The operation of this action will be monitored on a biannual basis.
Projections of GHG emissions to 2030 in Tajikistan
3.11. Improvement of Water Resources
Management in Khatlon Region Project
Background documents: The description of the project is available at
https://www.adb.org/projects/45354-002/main#project-overview.
Description of the action: The Project development objective is to improve the
livelihood of the rural population, through improvement of water resources management
with resilience to climate change impacts. The project will result in increase of agriculture
production by 110,000 tons per year; 2,000 new permanent, and 15,000 seasonal job
opportunity will be created. 60,000 rural people will be provided with access to improved
water supply
The Project is supported by the Islamic Development Bank.
Project duration: 2019-2020
Assumptions: This project aims at increase of crop production in response to improved
irrigation.
As in the case of Dangara Valley Irrigation Project, given the poor organic matter content
of soil in Tajikistan, it is decided to estimate the potential GHG mitigation impact of the
irrigation project by assuming that dryland soils were converted to irrigated agriculture
which results in an increase of soil organic carbon content in the soil by a modal rate of
0.10 t C ha-1 yr-1.
The agricultural land covered by the project is not provided in the project's reports and
website. For that reason, it is estimated by using as driver the project cost.
Table 69. General assumptions for the estimation of the increase of SOC due to
improved irrigation
Variable Value Units
Khatlon Region Project cost 15,000,000 USD
Dangara Valley Irrigation Project cost 7,856,777 USD
Area covered by the Dangara project 1,750 ha
Estimated area covered by the Khatlon project 3,341 ha
Increase of soil organic carbon content 0.1 t C ha-1 yr-1
Mitigation effect 1.23 ktCO2/year
Results:
Table 70. GHG emission reduction impact (Gg CO2-eq)
Projections of GHG emissions to 2030 in Tajikistan
Year Impact of Mitigation
action
2020 1.23
2025 1.23
2030 1.23
Proposal of monitoring indicator: The implementation of this project has been
finalized, however, the operational aspect of this project will be monitored through the
following indicators:
Agricultural production in the Khatlon region after the implementation of the
project.
Number of newly created job opportunities due to the implementation of the
project.
Number of rural people with access to improved water supply.
Proposal of entity responsible for monitoring: The entities responsible for monitoring
the improvement of water resources management will be the Ministry of Agriculture and
the Agency for Reclamation and Irrigation under the Government of the Republic of
Tajikistan.
Timing: The operation of this action will be monitored on a biannual basis.
Projections of GHG emissions to 2030 in Tajikistan
3.12. The Agriculture Reform Programme of
the Republic of Tajikistan for 2012-2020
Background documents: The description of the Programme is available at
https://moa.tj/ru/agrarian%20reform.
Description of the action: The overall goal of the Programme intends to achieve two
major national aims:
Develop productive and profitable agriculture on the basis of sustainable
utilization and management of natural resources.
Conduct overall agricultural reform, including structural and institutional reforms
at national and sub-national levels.
Specific tasks (objectives) in achieving these aims include:
Raise profitability of farms through free selection of crops to cultivate, based on
the principles of Resolution #111 of the Republic of Tajikistan that provides for
farmers to choose what they want to grow and where they wish to market their
products along the market principles of demand and supply and without any
interference; and equitable access to land and water;
Create environment in which farmers will become free producers;
Continue developing, high value, high income crops;
Ensure rights for long-term land tenure, based on principles of equity, without any
discrimination of gender, ethnicity and others, thus amending the Land Code of
the Republic of Tajikistan that allows for long-term Land Use Rights that is
inheritable, exchangeable and transferable;
Develop land valuation and land market mechanisms providing for land to be
traded, but also Land Use Rights can be used as collateral for obtaining credit
from the banks;
Amend the Law on Mortgage to provide customary and normal protection for
debtors in cases of default;
Amend the Law on Dehkan Farm to improve the status of Dehkan farms in line
with the Resolution of the Government of the Republic of Tajikistan #111, of 5
March 2007 on freedom to farm “On endorsing the Action Plan for resolving the
debts of cotton farms for 2007-2009”, whereby shareholders freely elect their
managers without any interference by national or local government authorities,
thus attracting shareholders to invest in the sector.
The Agriculture Reform Programme of the Republic of Tajikistan for 2012-2020 contains
the following tasks and actions that are related to a potential mitigation GHG effect:
Improvement of land condition: irrigation projects to irrigate abandoned arable
land, sustainable use of land (rotation, crop diversification etc.);
Reduced use of fertilizers;
Projections of GHG emissions to 2030 in Tajikistan
Increase fruit trees croplands;
Pasture management to avoid deterioration and overgrazing – rotation of
pastures – scale up cultivation of fodder crops;
Strengthen seed-growing and access to high quality seed;
Livestock development through improved access to fodder, enhanced animal
health services and livestock breeding development.
The Agriculture Reform Programme of the Republic of Tajikistan for 2012-2020 was
approved by Government Decree dated August 1, 2012 No. 383.
Programme duration: 2012-2020
Assumptions: We consider that the potential GHG mitigation impact of the Agriculture
Reform Programme has been already included in the estimated effect of the other
Programmes and Projects that have been analyzed (e.g. Pasture Development Program
of the Republic of Tajikistan, Horticulture and Grapevine Development Program,
Development Program for Seed Production of the Republic of Tajikistan, etc.). Please
refer to the following Programmes.
Results:
Table 71. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 IE IE IE
2020 IE IE IE
2025 IE IE IE
2030 IE IE IE
Proposal of monitoring indicator: The implementation of the programme has been
finalized, however, the operational aspect of the programme will be monitored through
the following indicators:
Number of irrigation projects created under the programme.
Amount of used fertilizers on crop lands after the implementation of the
programme.
Number of households with access to high quality seed.
Number of households with access to fodder, animal health services and
livestock breeding development.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the agriculture reform programme will be the Ministry of Agriculture of the Republic of
Tajikistan and the Agency for Reclamation and Irrigation under the Government of the
Republic of Tajikistan.
Timing: The operation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
3.13. Programme of development of
biotechnology of cattle in the Republic of
Tajikistan
Background documents: The description of the Programme is available at
http://extwprlegs1.fao.org/docs/pdf/taj170824.pdf.
Description of the action: The scope of this Program shall be the development of
biotechnology of stockbreeding, research in this sphere with a view of conservation of
animal genetic resources (semen, embryos) of nationally bred pedigree stock and rare
animal species. The objective shall be improvement of animal reproduction methods. The
following arrangements shall be performed for implementation of the Program: (a)
purchase of highly productive pedigree stock from abroad and import thereof; (b) growing
of young stock with high reproduction rate; (c) purchase of laboratory equipment; (d)
creation of sperm bank; and (e) training of staff.
The Programme of development of biotechnology of cattle in the Republic of Tajikistan
for 2013 - 2017 was approved by Government Decree August 1, 2012, No. 384.
Programme duration: 2013-2017
Assumptions: This Programme is related to the development and improvement of
livestock biotechnology scientific, research and technical knowledge and capacity of
Tajikistan. The effect of the application of the outcomes of the research activities of this
Programme are included under the estimated potential GHG mitigation effect of
"Comprehensive livestock development program".
Results:
Table 72. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 IE IE IE
2020 IE IE IE
2025 IE IE IE
2030 IE IE IE
Proposal of monitoring indicator: The implementation of the programme has been
finalized, however, the operational aspect of the programme will be monitored through
the following indicators:
Number of improved animal reproduction methods.
Projections of GHG emissions to 2030 in Tajikistan
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the development of biotechnology of cattle will be the Ministry of Agriculture of the
Republic of Tajikistan.
Timing: The operation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
3.14. Pasture Development Program of the
Republic of Tajikistan
Background documents: The description of the Programme is available at
http://extwprlegs1.fao.org/docs/pdf/taj170827.pdf.
Description of the action: Improving the condition of pastures has a special place in
ensuring the food security of the country and reducing poverty. At the same time, it
should be noted that in recent years, most of the pastures have been degraded,
especially pastures located near settlements and some of them are turning into a desert
zone. In many pastures, water supply facilities are unsuitable for exploitation. Due to the
lack of cattle drive roads and bridges, watering and feeding areas, about 1 million
hectares of pastures are partially used, and some areas are not used at all. As a result
of mudflow rains, hail, fires and other natural and anthropogenic factors, more than a
thousand hectares of pastures annually undergo degradation and erosion. At the same
time, according to statistics, in comparison with 1991, the livestock population increased.
Due to the lack of grazing feed in the winter, livestock loss of small livestock from 10 to
25 percent occurs.
Failure to prevent this unfavorable situation can lead to dangerous irretrievable
consequences. For the development of animal husbandry, it is necessary to create a
solid fodder base. Based on this, improvement of quality, productivity, appropriate and
rational regulation and use of pastures are the main factors in the development of
agriculture production.
The Program is aimed at increasing the stocks of pasture vegetation using modern
technology by sowing seeds of natural vegetation of pastures and increasing their
productivity. This Program is designed to increase livestock, meat, milk, leather and wool
production in all types of households, to meet the needs of the population with
environmentally friendly food, industry - raw materials, organize new jobs and improve
the living standards of rural residents. As a result, it brings high profits to all types of
management and on the whole will create the basis for strengthening the country's
economic growth.
To ensure the implementation of the Program, the following tasks must be solved:
selection and preparation of land for sowing seeds of natural herbs;
improvement of pasture conditions by methods of root and surface treatment, as
well as their protection against erosion;
repair of cattle drive tracks and construction of cattle drive bridges;
revision of the distribution of seasonal pastures;
determination of the directions of cattle-driving routes and sites for cattle herding;
protection of sowing pasture plots;
import and production of seeds of natural pasture grasses;
acquisition and delivery of mineral fertilizers;
Projections of GHG emissions to 2030 in Tajikistan
acquisition of fuel and lubricants and other services.
The Pasture Development Program of the Republic of Tajikistan for 2016 - 2020 was
developed on the basis of the Law of the Republic of Tajikistan "On Pastures". It was
approved by Government Decree November 28, 2015, No. 724.
Programme duration: 2016-2020
Assumptions: At the expense of the Program’s funds, the pasture productivity of the
Gorno-Badakhshan Autonomous Region is being improved - 250 hectares by surface
treatment, Sogd region by root treatment - 70 hectares, surface treatment - 250 hectares,
Khatlon region pasture by root processing - 65 hectares, by surface cultivation of 540
hectares, Dekhkan farms of regions of republican subordination by the method of root
processing - 45 hectares and by surface treatment - 200 hectares. Total 1420 ha of
pastures will be improved.
The estimation of the mitigation impacts is consistent with the data and methods applied
in the National Inventory of Tajikistan. The mitigation impact was calculated by
considering that the baseline emissions are those as included in the inventory. Since the
IPCC Tier 1 method was applied for the inventory, the same method was applied to
estimate the mitigation impact.
The mitigation effect does not reflect any potential positive impact to livestock productivity
associated to increased availability of fodder and grass from pastures.
Table 73. General assumptions for the estimation of the soil carbon stock
increment due to pastures’ improvement
Land-use
category
Reference
soil
carbon
stock
Stock change factors
Representative
soil carbon
stock Parameter
s source
SOCref
(tC/ha) F(LU) F(MG) F(I) SOC (tC/ha)
Grassland
(pasture)
before
LPDP
4 1 0.9 1 3.6 National
inventory
Grassland-
improved
pasture
after LPDP
4 1 1.14 1 4.56
National
inventory
& 2006
IPCC GLs
Pasture land improved 1420 Ha
Transition period for soils 20 years
Mitigation effect 0.25 ktCO2/year
Results:
Projections of GHG emissions to 2030 in Tajikistan
Table 74. GHG emission reduction impact (Gg CO2-eq)
Year Impact of Mitigation
action
2020 0.25
2025 0.25
2030 0.25
Proposal of monitoring indicator: The implementation of the programme has been
finalized, however, the operational aspect of the programme will be monitored through
the following indicators:
Stocks of pasture vegetation after the implementation of the Pasture
Development Programme.
Household production of livestock, meat, milk, leather and wool after the
implementation of the Pasture Development Programme.
Number of newly created jobs due to the increased livestock, meat, milk, leather
and wool production.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the Pasture Development Programme will be the Ministry of Agriculture of the Republic
of Tajikistan.
Timing: The operation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
3.15. Horticulture and Grapevine Development
Program
Background documents: The description of the Programme is available at
http://extwprlegs1.fao.org/docs/pdf/taj170821.pdf.
Description of the action: Horticulture and viticulture is one of the key agricultural
sectors of the Republic of Tajikistan, able to provide the country's domestic market with
food, increase the export potential of the republic and provide the population with
permanent work.
The main objective of the Program is the erection of new orchards and vineyards, the
reconstruction of old orchards and vineyards, the replacement of old low-yielding with
high-yielding varieties for export, based on the construction of intensive orchards,
increasing productivity by creating nurseries using new seeds and cuttings as a whole
increase in fruit and grape production.
To achieve this goal, it is required from the executive bodies of state power of regions,
cities and districts, organizations and institutions, regardless of the form of ownership, to
build nursery plants on the basis of the indicators of this Program, to organize the
cultivation of seedlings of 11.7 million units with the use of new seeds for 5 years, invest
in the construction of orchards and vineyards on an area of 20.1 thousand hectares and
reconstruct old gardens and vineyards on an area of 6.9 thousand Hectares on rain fed
land, replace the old orchards and vineyards to new to 6.1 thousand Hectares, the
erection of 502 hectares intensive orchards.
The Horticulture and Viticulture Development Program in the Republic of Tajikistan for
2016 – 2020 was approved by Government Decree December 30, 2015, No. 793.
Programme duration: 2016-2020
Assumptions: The mitigation impact was calculated by considering that the baseline
emissions are those as included in the inventory. Since the IPCC Tier 1 method was
applied for the inventory, the same method was applied to estimate the mitigation impact.
Perennial woody vegetation in orchards and vineyards can store significant carbon in
long-lived biomass, the amount depending on species type and cultivar, density, growth
rates, and harvesting and pruning practices.
The mitigation potential that is associated to the plantation of new orchards and vineyards
on an area of 20.1 thousand hectares for the 5 years period will be estimated. According
to Appendix 2 of the Programme, the plantation of new orchards on an area of 17382 ha
and vineyards on an area of 2771 ha is foreseen.
We select apricot as a representative plantation to base our estimations of the potential
mitigation impact of new orchards. This assumption is based on the results of the
Projections of GHG emissions to 2030 in Tajikistan
Programme for the period 2010-2014 (10% were vineyards and more than 40% of fruit
orchards were apricot plantations).
It was assumed that these plantations accumulate biomass linearly until they reach
maturity, assumed to be at half the replacement cycle. During maturity biomass increases
are offset by losses from pruning - in order the tree to be retained to the desired form -
and natural mortality, and hence changes in living biomass are assumed to be zero. The
annual growth rate (GW), during the growth period, is derived thus by dividing biomass
stock at maturity by the time from crop establishment to maturity reach.
Table 75. General assumptions for the estimation of the Increase of above
ground biomass C stock due to new woody plantations (orchards and vineyards)
Tree crops
Average
Aboveground
fresh biomass
stock
Biomass
moisture
Average
Aboveground
biomass stock
Carbon
fraction of
dry matter
Average
aboveground
biomass C
stock
Harvest
cycle
Annual C
uptake from
crop growth
t fresh b/ha % t dm/ha t C/t dm t C/ha yr t C/ha yr
Vineyards 20 40 12 0.5 6 26 0.46153846
Fruit trees 80 40 48 0.5 24 26 1.84615385
Land of new woody plantations 20,153 Ha
Land of vineyards 2,771 Ha
Land of fruit plantations 17,382 Ha
Mitigation effect 122.35 ktCO2/year
Results:
Table 76. GHG emission reduction impact (Gg CO2-eq)
Year Impact of Mitigation
action
2020 122.35
2025 122.35
2030 122.35
Proposal of monitoring indicator: The implementation of the programme has been
finalized, however, the operational aspect of the programme will be monitored through
the following indicators:
Number of newly erected orchards and vineyards.
Number of reconstructed old orchards and vineyards.
Number of orchards and vineyards switched from low-yielding to high-yielding
varieties.
Number of created nurseries to increase fruit and grape production.
Projections of GHG emissions to 2030 in Tajikistan
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the horticulture and grapevine development will be the Ministry of Agriculture of the
Republic of Tajikistan.
Timing: The operation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
3.16. State Target Program for the
Development of the Transport Complex of
the Republic of Tajikistan
Background documents: The description of the Programme is available at
https://www.mintrans.tj/sites/default/files/2017/gosudarstvennaya_celevaya_programm
a_razvitiya.pdf.
Description of the action: The Programme includes actions for the creation of protective
forest belts (roadsides) along the roads, which can be linked to a GHG mitigation
potential. The area of protective forest strip is planned to be 150 hectares.
The State Target Program for the Development of the Transport Complex of the Republic
of Tajikistan until 2025 was approved by Government Decree dated April 1, 2011 No.
165.
Programme duration: 2012-2025
Assumptions: The Programme includes the establishment of 150 ha of protective forest
belts (roadsides) along the roads.
The potential GHG mitigation impact will be estimated by calculating the annual increase
of biomass carbon stocks of afforested lands. The same method and parameters will be
used as in the national inventory.
Table 77. General assumptions for the estimation of the potential GHG mitigation
impact
Variable Value Units Source
Afforested land 150 ha
Average annual above-ground
biomass growth, Gw 6 t dm/(ha yr)
2006 IPCC GLs,
subtropical steppe
Ratio of below-ground biomass
to above-ground biomass, R 0.56 2006 IPCC GLs
Average annual biomass
growth above- and below-
ground, Gtotal
9.36 t dm/(ha yr)
Carbon fraction of dry matter,
CF 0.49 tC / t dm 2006 IPCC GLs
Annual increase in biomass
carbon stocks due to biomass
growth ΔCG
687.96 tC/yr
Annual loss of carbon ΔCL 10%
Mitigation effect 2.27 ktCO2/year
Results:
Projections of GHG emissions to 2030 in Tajikistan
Table 78. GHG emission reduction impact (Gg CO2-eq)
Year Impact of Mitigation
action
2025 2.27
2030 2.27
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Hectares of created protective forest belts along roads.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the establishment of the forest belts will be the Forestry Agency under the Government
of the Republic of Tajikistan.
Timing: The implementation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
3.17. Development Program for Seed
Production of the Republic of Tajikistan
Background documents: The description of the Programme is available at
http://extwprlegs1.fao.org/docs/pdf/taj170757.pdf.
Description of the action: The main objective of the Program shall be promotion of
selection and seed-growing with a view of formation of this sector of the national economy
capable of the functioning in compliance with international norms and standards.
Selection and seed-growing must be aimed at the promotion of plant varieties,
introduction, testing and registration of plant varieties, use of different seed-growing
methods for the extension of crop cultivation through application of new technologies,
and also commercial production, reproduction, processing, certification and marketing of
high quality seeds for internal market and export. In particular, this Program is oriented
towards introduction of new high-yielding cotton varieties and production of high-quality
cotton seeds.
The Development Program for Seed Production of the Republic of Tajikistan for 2016 -
2020 was approved by Government Decree October 28, 2016, No. 438.
Programme duration: 2016-2020
Assumptions: According to the programme, a gradual increase in the area under elite
seeds is targeted. We assume that elite seeds will be used for 10-15% of agricultural
land used for the following agricultural crops: cotton, cereals, legumes, potatoes and
fodder crops. The mitigation potential will be correlated to the improved agronomic
practices that increase yields and generate higher inputs of carbon residue and by this
way can lead to increased soil carbon storage. The type of improved agronomic practice
is the use of improved crop varieties.
The mitigation impact will be calculated by using the guidance from the WGII of the 4th
AR of IPCC related to Agriculture (Smith et al 2007).
Smith, P., D. Martino, Z. Cai, D. Gwary, H. Janzen, P. Kumar, B. McCarl, S. Ogle, F.
O’Mara, C. Rice, B. Scholes, O. Sirotenko, 2007: Agriculture. In Climate Change 2007:
Mitigation. Contribution of Working Group III to the Fourth Assessment Report of the
Intergovernmental Panel on Climate Change [B. Metz, O.R. Davidson, P.R. Bosch, R.
Dave, L.A. Meyer (eds)], Cambridge University Press, Cambridge, United Kingdom and
New York, NY, USA.
Projections of GHG emissions to 2030 in Tajikistan
Table 79. Arable area per crop19
Crop Area Units
cotton 254830 ha
cereals 384940 ha
legumes 11790 ha
potatoes 29750 ha
fodder crops 166490 ha
Table 80. General assumptions for the estimation of the potential GHG mitigation
impact
Variable Value Units
Total area of cotton, cereals,
legumes, potatoes and fodder
crops
847800 ha
Percentage of land under
improved agronomy practices 10%
Annual mitigation potentials 0.39 tCO2eq/ha/yr
Mitigation impact 33.0642 ktCO2/yr
Results:
Table 81. GHG emission reduction impact (Gg CO2-eq)
Year Impact of Mitigation
action
2021 33.06
2025 33.06
2030 33.06
Proposal of monitoring indicator: The implementation of the programme has been
finalized, however, the operational aspect of the programme will be monitored through
the following indicators:
Number of newly used seed-growing methods
Number of newly introduced high-yielding cotton varieties.
Number of high-quality cotton seeds produced with the new methods.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the seed production will be the Ministry of Agriculture of the Republic of Tajikistan.
19 Source: STATE OF PLANT GENETIC RESOURCES FOR FOOD AND AGRICULTURE (PGRFA) IN THE REPUBLIC OF TAJIKISTAN, COUNTRY REPORT BY PROF. DR. HAFIZ MUMINJANOV, DUSHANBE 2008
Projections of GHG emissions to 2030 in Tajikistan
Timing: The operation of this action will be monitored on a biannual basis.
Projections of GHG emissions to 2030 in Tajikistan
3.18. Comprehensive livestock development
program
Background documents: The description of the Programme is available at
http://www.fao.org/faolex/results/details/ru/c/LEX-FAOC189453/.
Description of the action: Integrated Program of Livestock Sector Development in the
Republic of Tajikistan for the period of 2018-2022 is a cross-sectoral policy document
envisaging the development of the livestock sector, which covers a range of zootechnical,
biotechnological and economic measures aimed at growing, preserving and increasing
the number of cattle, poultry, bees, fish, and their breeds in the country, as well as the
breeding of new high-yielding breeds. At the same time, ensuring the development of
livestock breeding industries within the framework of measures aimed at organizing and
conducting selection and breeding works, improving growing technology and feeding
standards for livestock, poultry, fish and bees, and increasing productivity of pastures by
indigenous and surface methods with the use of modern achievements. For further
development of the livestock sector, it is very important to provide a stable fodder supply
and it is expedient to create enterprises for the production of mixed fodder. To implement
this Program, the implementation of breeding stock and technological measures have
the importance of protecting, preserving and improving genetic resources of type and
breed of animals raised in the country, as well as to increase their numbers: local Tajik
Schwyz humped cattle are resistant to very hot and dry climates and to infectious blood
diseases. In order to improve the quality of breeds and productivity of livestock, the
following seeds were used: (a) sperm of black-and-white bulls of Holstein, Schwyz,
Schwyz and Schwyz humped cattle; and (b) in sheep breeding and goat-breeding sperm
of stud rams of the Guissar, Tajik, Darvoz thin wool and Tajik woolen goats. It should be
noted that the number of livestock in the private sector is increasing, but that there is also
a risk of the disappearance of some breeds: Kazakh white-headed, Aberdeen Angus,
Kalmyk, Tajik sheep breed and of the Darvoz thin wool breeds. The Program provides
for the preservation and protection of the genetic fund livestock breeds subject to animal
husbandry on the national territory. To improve the quality of breeding stock and increase
productivity of cattle, sheep, and goats it is necessary to set up breeding and selection
work at the appropriate level. There are a number of reasons in cattle breeding that have
a negative impact on further development of this sector: (a) of diminution pure bred cattle
and failure of breeding practices at the appropriate level; (b) insufficient number of bull
breeders, bred heifers of black-and-white, Schwyz, Kazakh, white-headed, Aberdeen
Angus and Kalmyk, as well as stud rams of thin wool and Karakul breeds; (c) insufficient
provision with mixed fodder; (d) import of pure bred animals and breeding material from
abroad in small quantities; and (e) poor functioning of artificial insemination points. The
main objective of the Program is to increase the production of meat, milk, eggs, honey,
fish with the use of modern technologies, creation of new livestock farms to increase
efficiency and productivity of animals, birds, fish, bees in all forms of ownership, thus
ensuring provision of the population with ecologically clean foodstuffs, increase of
pasture yield by 1520 of hundredweight, the creation the stock of genetic species and
semen of livestock, the creation of new jobs and, in general, the production of import-
Projections of GHG emissions to 2030 in Tajikistan
substituting commodities and ensuring food security. In the field of providing sources of
animal and poultry production the following issues are to be addressed for the
implementation of the Program: (a) use of selection and breeding achievements and
biotechnological methods to preserve and strengthen national genetic species of herds
and national animal breeds, species of fish, crosses of birds and breeds of bees; (b) due
to the importance of the objectives regarding the improvement of breeds and productivity
of livestock, birds, bees, must be provides support for pedigree breeding and funds for
training of specialists; (c) promotion of growing turkeys, ducks, partridges and quails; (d)
ensuring protection of genetic resources of fish species; and (e) organization of the
processing of manufactured products and ensuring the development of market relations.
The Comprehensive livestock development program for 2018 - 2022 was approved by
Government Decree March 27, 2018, No. 160.
Programme duration: 2018-2022
Assumptions: the following quantitative indicators of the Programme for year 2022 will
be correlated to potential GHG mitigation impact associated to livestock:
Purchase of 2450 thoroughbred cows from abroad;
Purchase of 5850 sheep;
Artificial insemination 45 000 heads of which 40000 thoroughbred calves;
Production of 80000 bulls.
In addition, 320 ha of pastures will be improved.
The mitigation impact will be calculated by using the guidance from the WGII of the 4th
AR of IPCC related to Agriculture (Smith et al 2007).
Smith, P., D. Martino, Z. Cai, D. Gwary, H. Janzen, P. Kumar, B. McCarl, S. Ogle, F.
O’Mara, C. Rice, B. Scholes, O. Sirotenko, 2007: Agriculture. In Climate Change 2007:
Mitigation. Contribution of Working Group III to the Fourth Assessment Report of the
Intergovernmental Panel on Climate Change [B. Metz, O.R. Davidson, P.R. Bosch, R.
Dave, L.A. Meyer (eds)], Cambridge University Press, Cambridge, United Kingdom and
New York, NY, USA.
The affected livestock population from the Programme will be estimated based on the
quantitative indicators of the Programme and total livestock population in 2016 (national
inventory).
Increase of soil carbon stock by pastures’ improvement
The general assumptions for the estimation of the mitigation impact that is linked to the
improvement of pastures are presented in the following table.
Table 82. General assumptions for the estimation of the soil carbon stock
increment due to pastures’ improvement
Projections of GHG emissions to 2030 in Tajikistan
Land-use
category
Reference
soil
carbon
stock
Stock change factors
Representative
soil carbon
stock Parameter
s source
SOCref
(tC/ha) F(LU) F(MG) F(I) SOC (tC/ha)
Grassland
(pasture)
before
LPDP
4 1 0.9 1 3.6 National
inventory
Grassland-
improved
pasture
after LPDP
4 1 1.14 1 4.56
National
inventory
& 2006
IPCC GLs
Pasture land improved 320 Ha
Transition period for soils 20 years
Mitigation effect 0.06 ktCO2/year
Improvement of livestock productivity
Table 83. General assumptions for the estimation of the mitigation impact due to
Improvement of sheep livestock productivity
Variable Value Units Source
Purchase of sheep from abroad 5,850 heads Programme
Artificial insemination 5,000 heads Programme
Total sheep in 2016 3,489,997 heads National
inventory
Percentage of sheep affected by the programme 0.31%
Enteric methane production in 2016 17 kt CH4 National
inventory
GWP of CH4 21 SAR IPCC
Enteric methane production in 2016 366.45 kt CO2 eq National
inventory
Technical reduction potential (proportion of an
animal’s enteric methane production) for enteric
methane emissions due to (i) improved feeding
practices, (ii) specific
agents and dietary additives and (iii) longer term
structural/management change and animal
breeding
0.1% IPCC 2007
Efficiency of the programme 70%
Mitigation effect 0.0008 kt CO2
eq/year
Table 84. General assumptions for the estimation of the mitigation impact due to
Improvement of cattle livestock productivity
Projections of GHG emissions to 2030 in Tajikistan
Variable Value Units Source Comment
Purchase of
thoroughbred cows
from abroad during the
5 years of the
Programme
2,450 heads Programme
Annual equivalent of
young cattle from
thoroughbred cows
564 heads
281-day gestation period
averaged over an entire
year
Artificial insemination
of cattle (thoroughbred
calves) during the 5
years
40,000 heads Programme
Annual equivalent of
artificial inseminated
calves during the 5-
years
11,836
Cattle raised for beef have a
lifespan between 12 to 24
months (average 18
months)
Production of bulls for
the 5-year period 80,000 heads Programme
Equivalent annual
number of young cattle
produced from bulls
920,548 heads Bull per cattle 1/50 (281-day
gestation period)
Total Cattle in 2016 2,278,072 heads National
inventory
Percentage of cattle
affected by the
programme
40%
Enteric methane
production in 2016 132 kt CH4
National
inventory
GWP of CH4 21 SAR IPCC
Enteric methane
production in 2016 2763.747 kt CO2 eq
National
inventory
Technical reduction
potential (proportion of
an animal’s enteric
methane production)
for enteric methane
emissions due to
longer term
structural/management
change and animal
breeding
2% IPCC 2007
Efficiency of the
programme 70%
Mitigation effect 11.73 kt CO2
eq/year
Results:
Table 85. GHG emission reduction impact (Gg CO2-eq)
Projections of GHG emissions to 2030 in Tajikistan
Year Impact of Mitigation
action
2018 7.01
2019 8.76
2020 10.51
2021 12.27
2022 14.02
2023 14.02
2024 14.02
2025 14.02
2030 14.02
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Number of newly high-yielding breeds being bred.
Number of newly introduced modern technologies for the production of meat,
milk, eggs, honey and fish.
Number of specialists trained on breeding improvements.
Number of increased pasture yield in hundredweight.
Number of created genetic species and semen of livestock.
Number of newly created jobs in the livestock sector.
Number of turkeys, ducks, partridges and quails being bred.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the development of the livestock sector will be the Forestry Agency under the
Government of the Republic of Tajikistan.
Timing: The implementation of this action will be monitored on a biannual basis.
Projections of GHG emissions to 2030 in Tajikistan
3.19. National Climate Change Adaptation
Strategy for the period up to 2030
Background documents: The Strategy is available at
http://repo.mel.cgiar.org:8080/handle/20.500.11766/10876.
Description of the action: The Strategy deals with the ranking of risks and their impact
on key sectors of the economy (agriculture, transport, water and energy resources, the
environment and natural disasters), the identification of needs and options for adapting
to climate change, the development of priority projects for adapting to climate change in
key sectors of the economy. It contains the development of 33 project proposals for
various sectors of the economy.
The National Climate Change Adaptation Strategy for the period up to 2030 was
approved by Government Decree 02.10.2019, No.482.
Strategy duration: up to 2030
Assumptions: We consider that the potential mitigation GHG impact of the adaptation
projects of the Strategy, which are related to the AFOLU sector, has been already
included in the estimated effect of the Programmes and Projects that have been analyzed
(e.g. Pasture Development Program of the Republic of Tajikistan, Horticulture and
Grapevine Development Program, Development Program for Seed Production of the
Republic of Tajikistan, Forest Sector Development Strategy, etc.).
Results:
Table 86. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 IE IE IE
2020 IE IE IE
2025 IE IE IE
2030 IE IE IE
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Number of potential risks of on key sectors of the economy such as the
agricultural, transport, water and energy resources, the environment, and natural
disasters sectors.
Number of impacts of the potential risks of the identified key sectors.
Number of identified needs and options for adapting to climate change by the
identified sectors.
Projections of GHG emissions to 2030 in Tajikistan
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the climate change adaptation strategy will be the Committee for Environmental
Protection under the Government of the Republic of Tajikistan.
Timing: The implementation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
3.20. The state program for the development
of new irrigated land and the restoration of
land that has been abandoned from
agricultural circulation in the Republic of
Tajikistan
Background documents: The description of the Programme is available at
https://www.alri.tj/ru/state-program-for-the-development-of-new-irrigated-land.
Description of the action: The state program for the development of new irrigated lands
and the restoration of lands that have been abandoned from agricultural circulation in the
Republic of Tajikistan for 2012-2020 (hereinafter referred to as the Program) has been
drawn up in order to increase the efficiency of the country's agricultural production,
provide rural people with jobs and, on this basis, improve the living standards of citizens
of the Republic Tajikistan.
The main objective of this Program is to restore the abandoned land in agricultural
circulation and expand the area of irrigated land in the country in 2012-2020. This
Program is consistent with the objectives of other programs of the Government of the
Republic of Tajikistan to improve the standard of living of people and is intended to
contribute to the socio-economic development of the country.
Expected Programme results: The implementation of this Program will allow the
development of 18,890 hectares of new irrigated land, including 3,890 hectares at the
expense of the state budget, 15,000 hectares at the expense of state investment projects
and the restoration of 7,800 hectares in agricultural circulation, in general, to attract
26,690 hectares of land into agricultural production. It should be noted that each hectare
of irrigated land, based on crops and areas of its location, will provide jobs for 4 to 8
people. On average, the implementation of the Program will create more than 160
thousand new jobs in rural areas of the country.
The state program for the development of new irrigated land and the restoration of land
that has been abandoned from agricultural circulation in the Republic of Tajikistan was
approved by Government Decree dated August 31, 2012 No. 450.
Programme duration: 2012-2020
Assumptions: This programme aims at the restoration of abandoned land in agricultural
circulation and expansion of the area of irrigated land in the country in response to
improved irrigation.
As in the case of Dangara Valley Irrigation Project, given the poor organic matter content
of soil in Tajikistan, it is decided to estimate the potential GHG mitigation impact of the
irrigation project by assuming that dryland soils were converted to irrigated agriculture
Projections of GHG emissions to 2030 in Tajikistan
which results in an increase of soil organic carbon content in the soil by a modal rate of
0.10 t C ha-1 yr-1.
Table 87. General assumptions for the estimation of the increase of SOC due to
improved irrigation
Variable Value Units
Area covered by the project 26690 ha
Increase of soil organic carbon content 0.1 t C ha-1 yr-1
Mitigation effect 9.79 ktCO2/year
Results:
Table 88. GHG emission reduction impact (Gg CO2-eq)
Year Impact of Mitigation
action
2021 9.79
2025 9.79
2030 9.79
Proposal of monitoring indicator: The implementation of the programme has been
finalized, however, the operational aspect of the programme will be monitored through
the following indicators:
Hectares of restored abandoned land in agricultural circulation.
Hectares of expanded area of irrigated land.
Number of new jobs created by expanding the hectares of land into agricultural
production.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the increase of irrigated land will be the Ministry of Agriculture of the Republic of
Tajikistan.
Timing: The operation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
4. Waste
The following are the mitigation actions which lead to GHG emission reductions in the
waste sector in Tajikistan.
4.1. Second Dushanbe Water Supply Project
Background documents: The description of the project is available at
https://projects.worldbank.org/en/projects-operations/project-detail/P154729?lang=en.
Description of the action: The objective of the project is to assist the improvement of
water utility performance and water supply services in selected areas of Dushanbe. It will
support the completion of the metering program in the southern part of the city and the
installation of network re-chlorination systems. Additionally, it will support an additional
tranche of filter reconstruction at the Samatechnaya Water Treatment Plant (SAM WTP),
the automation of the coagulation process at SAM WTP, the replacement and
sectorization of network sections, the development of a tariff and connection fee study
and technical assistance to improve utility management capacities and to develop a non-
revenue water (NRW) reduction strategy.
Implementation period: 2011-2020
Assumptions: This project does not have direct impact on GHG emission reductions. It
affects the water supply, but not water discharges in a direct way. Therefore, no GHG
emission reductions have been estimated.
Results:
Table 89. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 NA NA NA
2030 NA NA NA
Proposal of monitoring indicator: The implementation of the project has been
finalized, however, the operational aspect of the project will be monitored through the
following indicators:
Number of meters installed in the southern part of the city of Dushanbe.
Number of installed re-chlorination systems.
Number of replaced and sectorized network sections.
Projections of GHG emissions to 2030 in Tajikistan
Number of reconstructed filters at SAM WTP.
Number of interviewed people through the tariff and connection fee study.
Number of households provided with technical assistance to improve utility
management capacities.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the water supply project will be the Ministry of Energy and Water Resources of the
Republic of Tajikistan.
Timing: The operation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
4.2. Dushanbe Water Supply and Sanitation
Project
Background documents: The description of the project is available at
https://www.adb.org/projects/50347-002/main#project-pds.
Description of the action: The project will support Tajikistan in rehabilitating and
expanding climate-resilient water supply and sanitation (WSS) infrastructure, pilot testing
the establishment of district metering areas (DMAs) for nonrevenue water (NRW)
management in selected districts of Dushanbe city and rehabilitation of the south sewage
collector, benefitting 352,000 people. Additionally, it will assist developing a business
model for the State Unitary Enterprise Dushanbevodokanal (DVK) to improve the
sustainability of operations, including an accountability and incentive mechanism with a
performance benchmarking matrix and smart management system.
Furthermore, the project will pilot test a behavior change component for raising public
awareness on water usage and conservation and the benefits of smart meters. This is
the first urban sector project of the Asian Development Bank (ADB) in Tajikistan,
demonstrating efficient network management with potential for scaling up citywide. It is
listed in the ADB country operations business plan for Tajikistan, 2018-2020.
Implementation period: 2018-2025
Assumptions: The component of the project leading to GHG emission reductions is the
rehabilitation of the south sewage collector, benefitting 352,000 people. The
implementation period of the project is 2018-2025, and it is assumed that the impact of
the action will start affecting GHG emissions in the year 2025. During these years, the
population growth is assumed to be at the same rate of national total population.
The improved sewerage will affect the emission factor for calculating the emissions of
category 4D1 Domestic wastewater in the WOM, which is calculated according to the tier
1 approach for category 4D1 and estimated consistently with the WoM.
Table 90. Reference scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Type of population affected Urban -
Type of treatment or discharge pathway Septic tank -
Population affected 352,000 Population
Biochemical Oxygen Demand (BOD) 14.6 kg BOD/capital/year
Emission factor sceptic tank 0.3 kg CH4/kg BOD
Degree of utilization sceptic tank 10 %
Emission factor sewer 0.15 kg CH4/kg BOD
Degree of utilization sewer 30 %
Projections of GHG emissions to 2030 in Tajikistan
Table 91. Reduction scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Type of population affected Urban -
Discharge pathway
Centralized, aerobic treatment
plant -
Population affected 352,000 Population
Biochemical Oxygen Demand
(BOD) 14.6
kg
BOD/capital/year
Emission factor 0 kg CH4/kg BOD
Degree of utilization 100 %
Results:
Table 92. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 21.20 0.00 21.20
2030 23.57 0.00 23.57
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Number of pilot district metering areas in place in Dushanbe city.
Kilometers of rehabilitated south sewage collector.
Number of people benefiting from the improved sewage system.
Number of people reached with the behavior change component on water usage
and conservation and the benefits of smart meters.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the water supply project will be the Ministry of Energy and Water Resources of the
Republic of Tajikistan.
Timing: The implementation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
4.3. Kjuhand Water Supply Improvement
Programme (Phase III)
Background documents: The description of the project is available at
http://planung.fela.ch/index.php/projects/waste-water/wwtp-khujand,-tajikistan.
Description of the action: The project phase I was completed in 2008 and yielded
promising results. Therefore, a second phase was approved in 2009, which together with
phase 1 have improved the conditions of the water supply systems substantially.
However, the wastewater sectors still proved to be in a bad state. Thus, the Kjuhand
Water Supply Improvement Programme Phase III was approved.
The project consists in the rehabilitation of Waste Water Treatment Plant (WWTP) of
Khujand. The previous WWTP was built in the 1970’s. The mechanical and biological
units were out of operation for more than 10 years. As a result of this project, all electro-
mechanical equipment has either been removed or is completely dilapidated and non-
functional. Expected results after implementation of the project will be a fully functioning
Waste Water Treatment Plant.
Implementation period: 2016-2020
Assumptions: The component of the project leading to GHG emission reductions is the
rehabilitation of the WWTP, which benefits the entire population of Khujand. The
implementation period for the project is 2016-2020, and it is assumed that the impact of
the action will start affecting GHG emissions in the year 2020. During these years, the
population growth is assumed to stay at the same rate of national total population.
The improved sewerage will affect the emission factor for calculating the emissions of
category 4D1 Domestic wastewater in the WOM, which is calculated according to the tier
1 approach for category 4D1 and estimated consistently with the WoM.
Table 93. Reference scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Type of population affected Urban -
Type of treatment or discharge pathway Septic tank -
Population affected Population of Khujand -
Biochemical Oxygen Demand (BOD) 14.6 kg BOD/capital/year
Emission factor sceptic tank 0.3 kg CH4/kg BOD
Degree of utilization sceptic tank 10 %
Emission factor sewer 0.15 kg CH4/kg BOD
Degree of utilization sewer 90 %
Projections of GHG emissions to 2030 in Tajikistan
Table 94. Reduction scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Type of population affected Urban -
Type of treatment or discharge
pathway
Centralized, aerobic treatment
plant -
Population affected Population of Khujand Population
Biochemical Oxygen Demand (BOD) 14.6
kg
BOD/capital/year
Emission factor 0 kg CH4/kg BOD
Degree of utilization 100 %
Results:
Table 95. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 13.70 0.00 13.70
2030 15.23 0.00 15.23
Proposal of monitoring indicator: The implementation of the project has been
finalized, however, the operational aspect of the project will be monitored through the
following indicators:
Liters of wastewater treated by the WWTP of Khujand after the implementation
of the project.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the waste treatment will be the Ministry of Energy and Water Resources of the Republic
of Tajikistan.
Timing: The operation of this action will be monitored on a biannual basis.
Projections of GHG emissions to 2030 in Tajikistan
4.4. Nurek Water and Wastewater Project
Background documents: The description of the project is available at
https://www.ebrd.com/work-with-us/projects/psd/nurek-water-and-wastewater-
project.html.
Description of the action: Supporting the project to modernize and upgrade the water
and wastewater services in the city of Nurek in Tajikistan. The overall objectives of this
project are to rehabilitate the water supply and selected wastewater improvements and
to improve financial and operational management of the Nurek Water Company.
Implementation period: 2015-2017
Assumptions: The intervention leading to GHG emission reduction is the increase in the
population benefitting from access to the wastewater collection system from 20,142 in
2016 to 24,573 by 2019, which means that the project will expand the wastewater
collection system to more than 4 thousand people that not had access previously.
The implementation period for the project is 2014-2017, and it is assumed that the impact
of the action will start affecting GHG emissions in the year 2020. The improved sewerage
will affect the emission factor for calculating the emissions of domestic wastewater for
these population, which will be calculated according to the tier 1 approach for category
4D1 domestic wastewater.
Table 96. Reference scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Type of population affected Urban -
Type of treatment or discharge
pathway
Untreated: discharges to sea, river,
and lake -
Population affected Population of Nurek Population
Biochemical Oxygen Demand (BOD) 14.6
kg
BOD/capital/ye
ar
Emission factor sea, river and lake
discharge 0.06 kg CH4/kg BOD
Degree of utilization sceptic tank 100 %
Table 97. Reduction scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Type of population affected Urban -
Type of treatment or discharge
pathway
Centralized, aerobic treatment
plant -
Projections of GHG emissions to 2030 in Tajikistan
Variable Value Units
Population affected Population of Nurek Population
Biochemical Oxygen Demand (BOD) 14.6
kg
BOD/capital/year
Emission factor 0 kg CH4/kg BOD
Degree of utilization 100 %
Results:
Table 98. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 0.10 0.00 0.10
2030 0.10 0.00 0.10
Proposal of monitoring indicator: The implementation of the project has been
finalized, however, the operational aspect of the project will be monitored through the
following indicators:
Number of modernized and upgraded water and wastewater services.
Liters of water provided by the improved water services.
Liters of wastewater treated by the upgraded wastewater services.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the modernization of the water and wastewater services will be the Ministry of Energy
and Water Resources of the Republic of Tajikistan.
Timing: The operation of this action will be monitored on a biannual basis.
Projections of GHG emissions to 2030 in Tajikistan
4.5. Kulob Water and Wastewater Project
Background documents: The description of the project is available at
https://www.ebrd.com/work-with-us/projects/psd/51436.html.
Description of the action: The project will improve water supply and wastewater
services in the city of Kulob through the rehabilitation of the water network and pump
stations and the rehabilitation and modernization of the wastewater treatment plant. This
will impact the GHG emissions from wastewater occurring in Kulob.
Implementation period: 2020-2024
Assumptions: The implementation period for the project is 2020-2025 and it is assumed
that the impact of the action will star affecting GHG emissions in the year 2025. During
the project, the population growth is assumed to stay at the same rate of the national
total population.
The rehabilitation of the wastewater treatment in Kulob will affect the emission factor for
calculating the emissions of category 4D1 Domestic wastewater in the WoM, which is
calculated according to the tier 1 approach for category 4D1 and estimated consistently
with the WoM.
Table 99. Reference scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Type of population affected Urban -
Type of treatment or discharge pathway Septic tank -
Population affected Total population of Kulob Population
Biochemical Oxygen Demand (BOD) 14.6 kg BOD/capital/year
Emission factor sceptic tank 0.3 kg CH4/kg BOD
Degree of utilization sceptic tank 10 %
Emission factor sewer 0.15 kg CH4/kg BOD
Degree of utilization sewer 90 %
Table 100. Reduction scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Type of population affected Urban -
Type of treatment or discharge
pathway
Centralized, aerobic treatment
plant -
Population affected Total population of Kulob Population
Biochemical Oxygen Demand (BOD) 14.6
kg
BOD/capital/year
Emission factor 0 kg CH4/kg BOD
Projections of GHG emissions to 2030 in Tajikistan
Variable Value Units
Degree of utilization 100 %
Results:
Table 101. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 7.22 0.00 7.22
2030 8.02 0.00 8.02
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Number of rehabilitated pump stations.
Kilometers of rehabilitated water network.
Liters of wastewater treated by the modernized wastewater treatment plant.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the improved water supply and wastewater services will be the Ministry of Energy and
Water Resources of the Republic of Tajikistan.
Timing: The implementation of this action will be monitored on a biannual basis.
Projections of GHG emissions to 2030 in Tajikistan
4.6. Vahdat Solid Waste Project
Background documents: The description of the project is available at
https://www.ebrd.com/work-with-us/projects/psd/vahdat-sw-project-subproject.html.
Description of the action: The objective of this project is to finance construction of a
new sanitary landfill, as well as to upgrade solid waste collection and transportation
systems. The project will result in improved solid waste services and environmental
standards in Vahdat, along other activities.
Implementation period: 2018-2023
Assumptions: By 2023, the solid waste of the population of Vahdat will be treated in a
sanitary landfill. During the period, the population growth is assumed to stay at the same
rate of the national total population.
The reference scenario is the WoM, in which the waste is treated in three different type
of landfills. The impact is calculated in an IPCC 2006 IPCC model.
Table 102. Reference scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Waste treatment
Un-managed shallow (13%); Un-managed deep
(15%);
Managed (72%) -
Methane correction
factor 0.89
wt.
Fraction
Waste per capita 275 kg/cap/yr
% to SWDS 74 %
Waste composition
Food (31%); Garden (13%); Paper (11%); Wood
(0%);
Textile (2%); Nappies (0%); Plastic and other inert
(43%) %
Table 103. Reduction scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Waste treatment Managed semi-anaerobic -
Methane correction
factor 0.5
wt.
Fraction
Waste per capita 275 kg/cap/yr
% to SWDS 74 %
Waste composition
Food (31%); Garden (13%); Paper (11%); Wood
(0%); %
Projections of GHG emissions to 2030 in Tajikistan
Variable Value Units
Textile (2%); Nappies (0%); Plastic and other inert
(43%)
Results:
Table 104. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 7.45 7.00 0.46
2030 8.41 6.92 1.49
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Number of upgraded solid waste collection and transportation systems.
Kilograms of waste treated by the newly constructed sanitary landfill.
Number of people taking part in the community-based stakeholder participation
programme.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the new sanitary landfill will be the Ministry of Industry and New Technologies of the
Republic of Tajikistan.
Timing: The implementation of this action will be monitored on a biannual basis.
Projections of GHG emissions to 2030 in Tajikistan
4.7. Yavan Solid Waste Sub-Project
Background documents: The description of the project is available at
https://www.ebrd.com/work-with-us/projects/psd/yavan-solid-waste-subproject.html.
Description of the action: The project seeks to facilitate critical solid waste investments
for the city of Yavan and their neighboring municipalities. The overall objectives of this
sub-project are to rehabilitate the solid waste infrastructure and to improve financial and
operational management. This will result in a newly constructed sanitary landfill, the
upgrade of collection and transportation services and an improved level of solid waste
services and environmental improvements in the city and the municipalities.
Implementation period: 2017-2021
Assumptions: By 2021, the solid waste of the population of Yavan will be treated in a
sanitary landfill. During the period, the population growth is assumed to stay at the same
rate of the national total population.
The reference scenario is the WoM, in which the waste is treated in three different type
of landfills. The impact is calculated in an IPCC 2006 IPCC model.
Table 105. Reference scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Waste treatment
Un-managed shallow (13%); Un-managed deep
(15%);
Managed (72%) -
Methane correction
factor 0.89
wt.
Fraction
Waste per capita 275 kg/cap/yr
% to SWDS 74 %
Waste composition
Food (31%); Garden (13%); Paper (11%); Wood
(0%);
Textile (2%); Nappies (0%); Plastic and other inert
(43%) %
Table 106. Reduction scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Waste treatment Managed semi-anaerobic -
Methane correction
factor 0.5
wt.
Fraction
Waste per capita 275 kg/cap/yr
% to SWDS 74 %
Projections of GHG emissions to 2030 in Tajikistan
Variable Value Units
Waste composition
Food (31%); Garden (13%); Paper (11%); Wood
(0%);
Textile (2%); Nappies (0%); Plastic and other inert
(43%) %
Results:
Table 107. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 3.75 3.32 0.43
2030 4.23 3.33 0.90
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Number of upgraded solid waste collection and transportation systems.
Kilograms of waste treated by the newly constructed sanitary landfill.
Number of people taking part in the consultation process in form of a community-
based stakeholder participation programme.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the new sanitary landfill will be the Ministry of Industry and New Technologies of the
Republic of Tajikistan.
Timing: The implementation of this action will be monitored on a biannual basis.
Projections of GHG emissions to 2030 in Tajikistan
4.8. Kulob Solid Waste Sub-Project
Background documents: The description of the project is available at
https://www.ebrd.com/work-with-us/projects/psd/kulob-solid-waste-subproject.html.
Description of the action: Current waste practices are such that only 40% of waste is
collected in Kulob using aging equipment and methods. This waste is disposed of to an
old landfill site. The sub-project includes the development of a new sanitary landfill
adjacent to the existing landfill, which will be closed. This would be supported additional
collection points, waste containers, rehabilitation of existing collection points and
equipment as well as improvements to company facilities.
The overall objectives of this sub-project are to rehabilitate the solid waste infrastructure,
which is outdated, and purchase necessary equipment, and to improve financial and
operational management of the municipal solid waste company.
Implementation period: 2016-2020
Assumptions: By 2020, all solid waste of the population of Yavan will be treated in a
sanitary landfill. During the period 2020-2030, the population is assumed to grow at the
same rate of the national total population.
The reference scenario is the WoM, in which the waste is treated in three different types
of landfills. The impact is calculated in the IPCC 2006 FOD waste model.
Table 108. Reference scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Waste treatment
Un-managed shallow (13%); Un-managed deep
(15%);
Managed (72%) -
Methane correction
factor 0.89
wt.
Fraction
Waste per capita 275 kg/cap/yr
% to SWDS 74 %
Waste composition
Food (31%); Garden (13%); Paper (11%); Wood
(0%);
Textile (2%); Nappies (0%); Plastic and other inert
(43%) %
Table 109. Reduction scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Waste treatment Managed semi-anaerobic -
Projections of GHG emissions to 2030 in Tajikistan
Variable Value Units
Methane correction
factor 0.5
wt.
Fraction
Waste per capita 275 kg/cap/yr
% to SWDS 74 %
Waste composition
Food (31%); Garden (13%); Paper (11%); Wood
(0%);
Textile (2%); Nappies (0%); Plastic and other inert
(43%) %
Results:
Table 110. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 14.30 12.33 1.97
2030 16.14 12.43 3.71
Proposal of monitoring indicator: The implementation of the project has been
finalized, however, the operational aspect of the project will be monitored through the
following indicators:
Number of upgraded solid waste collection and transportation systems.
Kilograms of waste treated by the newly constructed sanitary landfill.
Percentage of waste collected in Kulob.
Number of added collection points and waste containers.
Number of rehabilitated existing collection points.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the rehabilitation of the solid waste infrastructure will be the Ministry of Industry and New
Technologies of the Republic of Tajikistan.
Timing: The operation of this action will be monitored on a biannual basis.
Projections of GHG emissions to 2030 in Tajikistan
4.9. Khujand Solid Waste Sub-Project
Background documents: The description of the project is available at
https://www.ebrd.com/work-with-us/projects/psd/khujand-solid-waste-subproject.html.
Description of the action: The project will construct a modern integrated solid waste
treatment facility, implement further improvements at the city landfill, rehabilitate the
remaining waste collection points in Khujand and procure waste collection containers and
machinery equipment.
By doing so, better service and environmental standards will be reached due to the timely
and reliable waste collection and transportation operations, the reduced landfilling, lower
CO2 and methane emissions and the introduction of appropriate standards for re-use
and recovery of resources.
Implementation period: 2015-2020
Assumptions: By 2020, the solid waste of the population of Khujand will be treated in a
sanitary landfill. During the period, the population growth is assumed to stay at the same
rate of the national total population. The reduced landfilling will lead to further GHG
emission reductions. However, with the information available, it is not possible to foresee
the reduction in landfilling.
The reference scenario is the WoM, in which the waste is treated in three different type
of landfills and the impact is calculated in an IPCC 2006 IPCC model.
Table 111. Reference scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Waste treatment
Un-managed shallow (13%); Un-managed deep
(15%);
Managed (72%) -
Methane correction
factor 0.89
wt.
Fraction
Waste per capita 275 kg/cap/yr
% to SWDS 74 %
Waste composition
Food (31%); Garden (13%); Paper (11%); Wood
(0%);
Textile (2%); Nappies (0%); Plastic and other inert
(43%) %
Table 112. Reduction scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Waste treatment Managed semi-anaerobic -
Projections of GHG emissions to 2030 in Tajikistan
Variable Value Units
Methane correction
factor 0.5
wt.
Fraction
Waste per capita 275 kg/cap/yr
% to SWDS 74 %
Waste composition
Food (31%); Garden (13%); Paper (11%); Wood
(0%);
Textile (2%); Nappies (0%); Plastic and other inert
(43%) %
Results:
Table 113. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 27.14 23.41 3.73
2030 30.64 23.60 7.04
Proposal of monitoring indicator: The implementation of the project has been
finalized, however, the operational aspect of the project will be monitored through the
following indicators:
Kilograms of waste treated by the newly constructed modern integrated solid
waste treatment facility.
Number of rehabilitated existing collection points.
Number of procured waste collection containers and machinery equipment.
Number of introduced standards for re-use and recovery of resources.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the solid waste project will be the Ministry of Industry and New Technologies of the
Republic of Tajikistan.
Timing: The operation of this action will be monitored on a biannual basis.
Projections of GHG emissions to 2030 in Tajikistan
4.10. Rural Water Supply and Sanitation
Project
Background documents: The description of the project is available at
https://projects.worldbank.org/en/projects-operations/project-detail/P162637.
Description of the action: The development objectives of the Rural Water Supply and
Sanitation Project for Tajikistan are to improve access to basic water supply and
sanitation services in selected districts and to strengthen the capacity of institutions in
the water supply and sanitation sector.
Implementation period: 2019-2025
Assumptions: This project does not have direct impact on GHG emission reductions. It
affects the water supply, but not water discharges in a direct way. Therefore, no GHG
emission reductions have been estimated.
Results:
Table 114. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 NA NA NA
2030 NA NA NA
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Number of people with access to basic water supply and sanitation services.
Number of institutions with strengthened capacity in the water supply and
sanitation sector.
Number of people participating in the training and capacity-building activities for
institutional strengthening.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the project will be the Ministry of Industry and New Technologies of the Republic of
Tajikistan.
Timing: The implementation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
4.11. Khorog Solid Waste Sub-Project
Background documents: The description of the project is available at
https://www.ebrd.com/work-with-us/projects/psd/khorog-solid-waste-sub-project.html
and at https://www.ebrd.com/work-with-us/procurement/p-pn-180530a.html.
Description of the action: The project will address urgently needed solid waste
infrastructure rehabilitation needs. The overall objectives of the project are to rehabilitate
the solid waste improvements and to improve financial and operational management.
Furthermore, to further improve solid waste management in Khorog city, the project will
require the procurement of the following goods, works and services:
Construction works for landfill remediation and extension;
Specialized machinery and vehicles for landfill operations; and
Accounting and billing systems.
The project is expected to bring substantial environmental, health and safety benefits to
the City of Khorog and the surrounding communities through the rehabilitation of waste
collection, transportation, and disposal services.
Implementation period: 2015-2019
Assumptions: By 2019, the solid waste of the population of Khorog will be treated in a
sanitary landfill. However, information about the full scope of the project is not available.
During the period, the population growth is assumed to stay at the same rate of the
national total population.
The reference scenario is the WoM, in which the waste is treated in three different type
of landfills and the impact is calculated in an IPCC 2006 IPCC model.
Table 115. Reference scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Waste treatment
Un-managed shallow (13%); Un-managed deep
(15%);
Managed (72%) -
Methane correction
factor 0.89
wt.
Fraction
Waste per capita 275 kg/cap/yr
% to SWDS 74 %
Waste composition
Food (31%); Garden (13%); Paper (11%); Wood
(0%);
Textile (2%); Nappies (0%); Plastic and other inert
(43%) %
Projections of GHG emissions to 2030 in Tajikistan
Table 116. Reduction scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Waste treatment Managed semi-anaerobic -
Methane correction
factor 0.5
wt.
Fraction
Waste per capita 275 kg/cap/yr
% to SWDS 74 %
Waste composition
Food (31%); Garden (13%); Paper (11%); Wood
(0%);
Textile (2%); Nappies (0%); Plastic and other inert
(43%) %
Results:
Table 117. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 4.94 4.78 0.16
2025 5.62 4.72 0.90
2030 6.35 4.79 1.55
Proposal of monitoring indicator: The implementation of the project has been
finalized, however, the operational aspect of the project will be monitored through the
following indicators:
Number of procured constructions works for landfill remediation and extension.
Number of procured specialized machinery and vehicles for landfill operations.
Number of procured accounting and billing systems.
Kilograms of waste treated after the rehabilitation of solid waste activities.
Number of people taking part in the consultation process in form of a community-
based stakeholder participation programme.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the solid waste project will be the Ministry of Industry and New Technologies of the
Republic of Tajikistan.
Timing: The operation of this action will be monitored on a biannual basis.
Projections of GHG emissions to 2030 in Tajikistan
4.12. Tursun-Zade Solid Waste
Background documents: The description of the project is available at
https://www.ebrd.com/work-with-us/projects/psd/tursun-zade-solid-waste.html.
Description of the action: The Project involves the rehabilitation and upgrade of the
existing dumpsite of the City of Tursun-Zade into a controlled landfill as well as the
improvement in waste collection services and transport to the landfill. Municipal waste is
currently disposed of at an existing dumpsite located 7.6 km from the City. The dumpsite
has been in operation since 1968.
A feasibility study conducted for the project considered the option of developing a new
landfill on a new site or upgrading the existing dumpsite. The study determined that the
existing site was suitable for upgrade to an engineered landfill and this is regarded as the
preferred option. The engineered landfill will be constructed in an unused area of the
dumpsite but on land approved by the Land Commission within the existing dumpsite
boundaries. The existing dumping areas will be re-cultivated and closed.
Ultimately, the project will improve landfill sanitary and operating standards and increase
efficiency and coverage of solid waste collection and transportation in Tursun-Zade.
Implementation period: 2015-2019
Assumptions: By 2019, the solid waste of the population of Tursun-Zade will be treated
in a sanitary landfill. During the period, the population growth is assumed to stay at the
same rate of the national total population.
The reference scenario is the WoM, in which the waste is treated in three different type
of landfills and the impact is calculated in an IPCC 2006 IPCC model.
Table 118. Reference scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Waste treatment
Un-managed shallow (13%); Un-managed deep
(15%);
Managed (72%) -
Methane correction
factor 0.89
wt.
Fraction
Waste per capita 275 kg/cap/yr
% to SWDS 74 %
Waste composition
Food (31%); Garden (13%); Paper (11%); Wood
(0%);
Textile (2%); Nappies (0%); Plastic and other inert
(43%) %
Projections of GHG emissions to 2030 in Tajikistan
Table 119. Reduction scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Waste treatment Managed semi-anaerobic -
Methane correction
factor 0.5
wt.
Fraction
Waste per capita 275 kg/cap/yr
% to SWDS 74 %
Waste composition
Food (31%); Garden (13%); Paper (11%); Wood
(0%);
Textile (2%); Nappies (0%); Plastic and other inert
(43%) %
Results:
Table 120. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 6.40 6.19 0.21
2025 7.28 6.12 1.16
2030 8.22 6.20 2.01
Proposal of monitoring indicator: The implementation of the project has been
finalized, however, the operational aspect of the project will be monitored through the
following indicators:
Kilograms of waste treated at the rehabilitated and upgraded dumpsite of the City
of Tursun-Zade into a controlled landfill.
Number of households with improved waste collection services
Number of improved transport methods of waste to the landfill.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the solid waste project will be the Ministry of Industry and New Technologies of the
Republic of Tajikistan.
Timing: The operation of this action will be monitored on a biannual basis.
Projections of GHG emissions to 2030 in Tajikistan
4.13. Kurgan-Tyube Solid Waste
Background documents: The description of the project is available at
https://www.ebrd.com/work-with-us/projects/psd/kurgan-tyube-solid-waste.html.
Description of the action: The project will bring substantial environmental, health and
safety benefits to the city of Kurgan-Tyube and the surrounding communities through the
rehabilitation of the solid waste management services in the city. It aimed at improving
landfill sanitary and operating standards and at increasing efficiency and coverage of
solid waste operations in the city. However, it is not clear if this project has been
implemented.
Implementation period: 2015-2019
Assumptions: By 2019, the solid waste of the population of Kurgan-Tyube will be treated
in a sanitary landfill. During the period, the population growth is assumed to stay at the
same rate of the national total population.
The reference scenario is the WoM, in which the waste is treated in three different type
of landfills and the impact is calculated in an IPCC 2006 IPCC model.
Table 121. Reference scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Waste treatment
Un-managed shallow (13%); Un-managed deep
(15%);
Managed (72%) -
Methane correction
factor 0.89
wt.
Fraction
Waste per capita 275 kg/cap/yr
% to SWDS 74 %
Waste composition
Food (31%); Garden (13%); Paper (11%); Wood
(0%);
Textile (2%); Nappies (0%); Plastic and other inert
(43%) %
Table 122. Reduction scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Waste treatment Managed semi-anaerobic -
Methane correction
factor 0.5
wt.
Fraction
Waste per capita 275 kg/cap/yr
% to SWDS 74 %
Projections of GHG emissions to 2030 in Tajikistan
Variable Value Units
Waste composition
Food (31%); Garden (13%); Paper (11%); Wood
(0%);
Textile (2%); Nappies (0%); Plastic and other inert
(43%) %
Results:
Table 123. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 13.21 12.78 0.43
2025 15.01 12.62 2.40
2030 16.95 12.80 4.15
Proposal of monitoring indicator: The implementation of the project has been
finalized, however, the operational aspect of the project will be monitored through the
following indicators:
Kilograms of waste treated at the landfill with improved sanitary and operating
standards.
Percentage of collected waste in the city.
Number of households participating in the stakeholder participation programme.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the solid waste project will be the Ministry of Industry and New Technologies of the
Republic of Tajikistan.
Timing: The operation of this action will be monitored on a biannual basis.
Projections of GHG emissions to 2030 in Tajikistan
Section 6 - Planned mitigation actions
This section reflects those actions with significant mitigation impact which are planned
to be implemented in the coming future.
1. Energy
The following are the mitigation actions which lead to GHG emission reductions in the
energy sector in Tajikistan.
1.1. Rogun Hydropower Plant
Background documents: The description of the project is available at
https://www.power-technology.com/projects/rogun-hydropower-plant/
Description of the action: The Rogun Hydropower Plant is being constructed on the
upper reaches of the Vakhsh River in the Pamir mountain ranges, Republic of Tajikistan.
The project is being developed by OJSC Rogun Hydropower Plant (HPP) on behalf of
the Government of Tajikistan. The 3,600MW power plant will have an output capacity of
13.1bn kWh, accounting for half of the country’s electrical installed capacity. Part of the
electrical output from the project will be sold to its neighboring countries, especially
Pakistan, conveyed using the Central Asia-South Asia power project (CASA-1000)
transmission line.
The techno-economic assessment study (TEAS) and environmental and social impact
assessment (ESIA) phase for the project was completed in July 2014 with funds provided
by the World Bank.
The above phase was necessitated due to the objections from the Republic of
Uzbekistan, primarily on the initial design of the dam.
The Rogun Hydropower Plant is currently under development. However, this project has
suffered different delays for different reasons20. Given the magnitude of the project and
its uncertainty, the mitigation action was included under the WaM scenario.
Implementation period: The project will be finalized by 202621.
20 https://cabar.asia/en/tajikistan-why-is-rogun-hpp-construction-delayed/
21 https://www.eu4energy.iea.org/countries/tajikistan
Projections of GHG emissions to 2030 in Tajikistan
Assumptions: The estimation of the impact is performed applying the grid emission
factor to the new energy produced using the new generated capacity, with the emissions
of the new hydro plant assumed to be zero. The capacity factor (hours of operation of
the installed capacity) are calculated using current data of electricity produced and
capacity installed.
It is also assumed that in the absence of this action, the energy demand would have
been met using the same energy mix of year 2016 (the last inventory year).
Some of the electricity produced by this plant will be exported to neighboring countries.
However, the estimation made assumes all electricity generated is consumed at national
level, replacing the fossil generation capacity that would be needed to meet the new
energy demand, as modeled in the WoM scenario.
Table 124. Reference scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Grid emission factor 0.0052 Gg CO2-eq / GWh
Table 125. Reduction scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
New capacity 3,600 MW
Capacity factor 3,590 Full time hours
New annual electricity generated 12,924 GWh
Grid emission factor 0.0052 Gg CO2-eq / GWh
Results:
Table 126. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 67.62 0.00 67.62
2030 67.62 0.00 67.62
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
MW of electricity generated by the constructed Rogun Hydropower Plant going
into the Tajikistan electricity grid.
Percentage of renewable energy in the share of the Tajikistan electricity grid.
Hectares of irrigated arid land.
Projections of GHG emissions to 2030 in Tajikistan
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the project will be the Ministry of Industry and New Technologies of the Republic of
Tajikistan.
Timing: The implementation of this action will be monitored on a biannual basis.
1.2. EBRD Sustainable Energy Financing
Facilities
Background documents: The description of the project is available at
https://www.greenclimate.fund/sites/default/files/document/funding-proposal-fp025-
ebrd-armenia-egypt-georgia-jordan-republic-moldova-mongolia-morocco-serbia.pdf.
Description of the action: The project will contribute to achieving a paradigm shift by
creating new and significantly scaling up existing markets for commercial sustainable
energy, energy efficiency and climate resilience financing. By doing so it will contribute
to the aim as stated in the Paris Agreement to “make finance flows consistent with a
pathway towards low greenhouse gas emissions and climate-resilient development”,
through an innovative combination of financial support, capacity building and technology
transfer and supported by a deep level of country ownership.
The project will deliver scale over the next three years by financing, via local PFIs, more
than 20,000 scalable and replicable renewable energy, energy efficiency, and climate
resilience projects across the industrial, commercial, residential, transport, and
agricultural sectors in the Middle East and North Africa, Western and Central Asia and
Southern and Eastern Europe. It will address multiple market barriers along the
technology supply chains and unlock the potential of private sector finance by:
Building the capacity of all actors along the climate technology supply chain, in
particular by encouraging local PFIs to establish and grow climate financing
solutions for RE, EE and CR that currently either do not exist at all, or are
underserved;
Stimulating demand for best-available climate technologies by providing much-
needed long-term finance that more closely matches the financial characteristics
of RE, EE and CR projects; and
Facilitating the creation of new markets by demonstrating the profitability and
enhanced competitiveness of climate technologies and ultimately de-risking
climate investments to leverage a growing level of funding from the private sector
over time.
Implementation period: The project will be finalized by 2032.
Assumptions: The mitigation impact of this action has not been estimated.
Results:
Projections of GHG emissions to 2030 in Tajikistan
Table 127. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 NA NA NA
2030 NA NA NA
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Number of energy efficiency, renewable energy and climate resilience projects
implemented.
MW of electricity installed.
GWh of annual final energy savings through improved energy efficiency.
Number of beneficiaries relative to the total population of Tajikistan.
Tons of carbon dioxide equivalent to be reduces or avoided.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the project will be the Ministry of Energy and Water Resources of the Republic of
Tajikistan.
Timing: The implementation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
1.3. Scaling Up Hydropower Sector Climate
Resilience
Background documents: The description of the project is available at
https://www.greenclimate.fund/sites/default/files/document/funding-proposal-fp040-
ebrd-tajikistan.pdf.
Description of the action: Tajikistan is the most vulnerable country to climate change
in the Europe & Central Asia (ECA) region. Its energy system is dominated by
hydropower and is therefore highly exposed to climate change risks. Hydropower is of
fundamental importance for economic development and living standards in Tajikistan,
and climate change is a hugely important risk amplifier in this already precarious and
challenging context. Strengthened governance and institutions are necessary to improve
the climate resilience of hydropower systems. Additionally, the climate vulnerability of
Tajikistan’s energy systems also has important social and gender dimensions.
In response to these severe challenges, the proposed Project aims to scale up the
adoption of climate resilience practices and technologies in the Tajik hydropower sector.
Enhanced institutional capacities, modern climate resilience technologies and adequate
technical skills are urgently needed in Tajikistan to address the risks associated with
climate change in the fragile and highly climate-vulnerable hydropower system. The
proposed Project will support the transfer of knowledge and technologies for achieving
these vital targets for Tajikistan’s strategically important hydropower sector. This will be
accomplished through a Project structure consisting of three closely inter-related
components linked to three targeted Project Outputs. Project implementation is
structured in two phases. The funds for Phase I have already been committed by EBRD
and the CIF’s Pilot Programme for Climate Resilience (PPCR), as set out in section B.2.
This proposal is for further funding under Phase II. This arrangement will allow for a
smoother, gradual implementation of the overall Project. The phases are intended to be
staggered and to overlap each other in order to ensure smooth implementation and the
effective coordination of project activities. Phase I has now reached a critical stage, with
all the procurement arrangements and engineering services (covering both phases) now
in place, and Phase I physical works about to commence. This means that it is now timely
to plan ahead and secure the funding for Phase II so that the physical works of Phase II
can begin smoothly and without interruption, taking into account the length of time
needed to secure the funding and all necessary approvals.
The proposed Project will be delivered through a structured approach comprising of
technical assistance, policy dialogue and facility upgrades in close partnership with the
Tajik authorities.
The specific objectives of the Project are the following:
1. To increase the adoption of best international practices in the assessment and
management of climate change risks to hydropower operations by Tajik
Projections of GHG emissions to 2030 in Tajikistan
hydropower operators and other associated agencies such as providers of
hydromet services (Phase I+II);
2. To develop institutional capacities and structures needed to ensure effective
transboundary management of hydropower cascades in order to promote the
climate resilience of hydropower operations (Phase II); and
3. To scale up the integration of climate resilience approaches, technologies and
design standards into a strategic hydropower facility with a powerful
demonstration impact (Phase I + II).
Specific benefits will include:
The modernisation of a major hydropower facility taking into account projected
future climate conditions.
The population of Sughd region (approx. 2,400,000 people), in particular women,
to benefit from a more secure and climate-resilient electricity supply.
Implementation period: The project will be finalized in 2057.
Assumptions: The impact of this action is already considered under 1.22. Long-Term
Small Hydro Power Plant Construction Program in Section 5 and under 1.1. Rogan
Hydropower Plant in Section 6. Therefore, its implementation does not involve additional
GHG emission reductions.
Results:
Table 128. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 IE IE IE
2020 IE IE IE
2025 IE IE IE
2030 IE IE IE
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Number of project beneficiaries relative to the total population of Tajikistan.
Number of physical assets made more resilient to climate variability and change.
Number of institutional and regulatory systems that improve incentives for climate
resilience.
Number of households and SMEs with access to climate resilient, sustainable
energy.
Proposal of entity responsible for monitoring: The entities responsible for monitoring
the project will be the Ministry of Energy and Water Resources and the Committee for
Environmental Protection under the Government of the Republic of Tajikistan.
Projections of GHG emissions to 2030 in Tajikistan
Timing: The implementation of this action will be monitored on an annual basis.
1.4. Institutional Development of the State
Agency for Hydrometeorology of Tajikistan
Background documents: The description of the project is available at
https://www.greenclimate.fund/sites/default/files/document/funding-proposal-fp075-adb-
tajikistan.pdf.
Description of the action: Tajikistan already faces recurring climate-related extreme
weather events, particularly flood and landslides. Climate change is expected to
exacerbate these impacts. Districts in the Pyanj River Basin, in particular, are among
poorest and most vulnerable to climate change.
However, low capacity in the country the forecasting of weather, hydrometeorological,
and climatic conditions remain a critical weakness in the country. Disaster risk mitigation
and response in vulnerable communities, as well as broader climate change adaptation
efforts, are thus hampered. The responsible forecasting entity, the State Agency for
Hydrometeorology (Hydromet) is crippled by many of the common problems faced by
post-Soviet institutions including limited budget, decaying infrastructure, and poor staff
retention. Its technical capacity is relatively low, and government and civil society
stakeholders are generally unsatisfied with the forecasting services offered by Hydromet.
Without interventions addressing its underlying weaknesses, Hydromet capacity and
outputs will likely continue to languish.
The subject proposed project will support Hydromet’s development to a sustainable and
well-resourced institution that produces timely and accurate forecasting of extreme
weather events particularly in the PRB. In doing so, the project will address key
institutional weaknesses. The project will (i) modernize Hydromet’s campus and
associated facilities [Component A], (ii) support legal and organizational transformation
and capacity building of Hydromet into a government entity with flexibility to set staff
salaries and retain additional entrepreneurial revenue [Component B], (iii) undertake
capacity building for improve forecasting and warning of extreme weather events
[Component C], and (iv) support development and implementation of a viable business
model through marketing of fee-based services [Component D]. The project’s primary
measurable benefit (indicators) are (i) Hydromet develops and disseminates timely and
accurate forecasts of flood events in the PRB and (ii) Hydromet develops a weather
service product marketed to customers in the PRB.
Implementation period: 2018-2023
Assumptions: The mitigation impact of this action has not been estimated.
Results:
Table 129. GHG emission reduction impact (Gg CO2-eq)
Projections of GHG emissions to 2030 in Tajikistan
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 NA NA NA
2030 NA NA NA
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Number of surveyed government and civil society stakeholders’ beneficiaries
under the project.
Number of purchased equipment for the hydrometeorology institution.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the institutional development will be the Agency for Hydrometeorology of the Committee
for Environmental Protection under the Government of the Republic of Tajikistan.
Timing: The implementation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
2. Industrial Processes and Product Use
In the project no planned mitigation actions and with impact in IPPU emissions have
been identified.
Projections of GHG emissions to 2030 in Tajikistan
3. AFOLU
The following are the mitigation actions which lead to GHG emission reductions in the
AFOLU sector in Tajikistan.
3.1. Forest Sector Development Strategy for
2016-2030
Background documents: The description of the proposed Strategy is available at
https://www.landuse-ca.org/wp-content/uploads/2019/11/Forest-Sector-Development-
Strategy-for-Tajikistan-RU.pdf.
Description of the action: The forest sector development strategy for 2016-2030
(hereinafter referred to as the Strategy) is aimed at the sustainable development of the
forest sector of the Republic of Tajikistan to ensure a balance of ecological, economic
and social functions of the forest, the implementation of which contributes to addressing
important aspects of Tajikistan's forest reform and is consistent with the main priorities
of the National Strategy the development of the Republic of Tajikistan.
The main objectives of the Strategy are:
conservation of forest biodiversity, restoration and conservation of forests,
increase in their area and productivity;
improving the quality and quantity of ecosystem services provided under climate
change;
promoting the development of the economy by attracting entrepreneurs to the
forest sector and increasing the efficiency of forestry;
improving the welfare of the local population by involving them in forestry and
providing forest products based on sustainable forest use.
strengthening the participation of civil society, in particular women, in forest policy
issues at the national and local levels;
strengthening the role of forests of the Republic of Tajikistan in fulfilling
international obligations and global programs for sustainable forest development
and for mitigating and adapting to climate change.
One of the indicators of the strategy, which will be used to estimate the potential
mitigation GHG impact is the "planting of 10 thousand hectares new forests adapted to
the terrain in the face of climate change". More specifically, according to the strategy:
new forests will be planted in the amount of not less than 1 thousand ha per year,
degraded forests in the amount of not less than 2 thousand ha per year will be
restored, and
assistance will be provided in the natural restoration of degraded forests in the
amount of not less than 8 thousand ha per year
Projections of GHG emissions to 2030 in Tajikistan
The "Forest Sector Development Strategy 2016-2030" was prepared in 2015, however it
has not been approved by the Government, yet. The planned duration of the Strategy is
up to 2030.
Assumptions: According to the strategy:
new forests will be planted in the amount of not less than 1 thousand ha per year;
degraded forests in the amount of not less than 2 thousand ha per year will be
restored; and
assistance will be provided in the natural restoration of degraded forests in the
amount of not less than 8 thousand ha per year.
Implementation Period: 2021-2030
Mitigation effect of new forests of 1 thousand ha per year, starting in 2021.
Table 130. General assumptions for the estimation of the potential GHG
mitigation effect of new forests of 1 thousand ha per year, starting in 2021.
Variable Value Units Source
Afforested land 1000 ha
Average annual above-ground
biomass growth, Gw 6 t dm/(ha yr)
2006 IPCC GLs,
subtropical steppe
Ratio of below-ground biomass
to above-ground biomass, R 0.56 2006 IPCC GLs
Average annual biomass growth
above- and below-ground,
Gtotal
9.36 t dm/(ha yr)
Carbon fraction of dry matter,
CF 0.49 tC / t dm 2006 IPCC GLs
Annual increase in biomass
carbon stocks due to biomass
growth ΔCG
4586.4 tC/yr
Annual loss of carbon ΔCL 10%
Mitigation effect 15.14 ktCO2/year
Mitigation effect of restoration of degraded forests, starting in 2021.
According to the national inventory, the average annual above-ground biomass growth
(Gw) of forests in Tajikistan is 0.8 t dm/(ha yr). We assume that this annual growth of
biomass will be restored to degraded forests.
Table 131. General assumptions for the estimation of the potential GHG
mitigation effect of restoration of degraded forests.
Variable Value Units Source
Restored forest land 10,000 ha
Projections of GHG emissions to 2030 in Tajikistan
Variable Value Units Source
Average annual above-ground
biomass growth, Gw 0.8 t dm/(ha yr) National inventory
Ratio of below-ground biomass to
above-ground biomass, R 0.56 National inventory
Average annual biomass growth
above- and below-ground, Gtotal 1.248 t dm/(ha yr)
Carbon fraction of dry matter, CF 0.49 tC / t dm National inventory
Annual increase in biomass
carbon stocks due to biomass
growth ΔCG
6115.2 tC/yr
Annual loss of carbon CL 10%
Mitigation effect 20.18 ktCO2/year
Results:
Table 132. GHG emission reduction impact (Gg CO2-eq)
Year Impact of Mitigation
action
2016 NA
2020 NA
2025 176.58
2030 353.15
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Hectares of newly planted forests.
Hectares of degraded forests which is restored.
Hectares of national restoration of degraded forests.
Number of people involved in forest policy issues at national and local levels.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the forest sector development will be the Forestry Agency under the Government of the
Republic of Tajikistan.
Timing: The implementation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
3.2. Climate Adaptation and Mitigation Program
for the Aral Sea Basin
Background documents: The description of the project is available at
https://www.greenclimate.fund/sites/default/files/document/funding-proposal-fp014-
world-bank-tajikistan-and-uzbekistan.pdf.
Description of the action: The proposed GCF financing of US$19 million would scale
up the first phase of the World Bank Group (WBG) supported Climate Adaptation and
Mitigation Program for Aral Sea Basin (CAMP4ASB), which focuses on Tajikistan and
Uzbekistan (while future phases of the Program, under preparation, will progressively
cover the remaining Central Asian countries: Kazakhstan, Kyrgyz Republic, and
Turkmenistan). A further allocation of US$27 million from GCF will be requested for the
remaining Central Asian countries, for which GCF’s funding approval will be issued upon
WB submission of program details for those countries.
CAMP4ASB seeks to help Central Asian countries build upon the benefits of regional
cooperation to address the mounting challenges from climate change, which often
transcend borders.
The WBG-supported program lays the foundation for an institutional platform for regional
cooperation on climate change across a broad range of sectors. This will be the first such
platform in Central Asia that will provide access to improved climate change knowledge
services for climate change assessment and decision-making and to increased financing
and technical assistance, on a demand-driven basis, for climate investments in priority
areas common to Central Asian countries.
While the associated WBG program will provide financing via sub-loans primarily to
farmers (Dekhan and commercial farmers), resource user groups (e.g., water user
associations), village communities, and private companies for climate investments
(resilience or mitigation), GCF financing will provide investment support via sub-grants
to the most vulnerable communities for climate resilient measures in priority areas,
including to the poorest populations residing on fringe/risk-prone areas and marginalized
groups such as women. Successfully building climate change resilience in Tajikistan and
Uzbekistan will require increasing engagement with those most adversely affected by
climate change, and community facilitation support and capacity building will accompany
investments and be designed to reach those who are marginalized and most vulnerable.
The combination of WBG and GCF financing will allow CAMP4ASB to pilot certain
climate-smart activities that could not have otherwise been implemented at this scale,
and double the Project’s expected benefits. In particular, GCF-financed activities will
strengthen the climate resilience of those most vulnerable to climate change, by
supporting the adoption of climate-smart rural production and landscape management
investments that aim to achieve multiple benefits (e.g., climate resilience, food security,
increased well-being of beneficiaries, including gender and social inclusion).
Projections of GHG emissions to 2030 in Tajikistan
The primary measurable benefits will be monitored against indicators such as (i) number
of direct project beneficiaries (disaggregated by gender) (205,000 in total), (ii) number of
hectares covered by effective agricultural, land and water management practices suited
to local agro-ecological conditions and climate change resilience (35,000 hectares), and
(iii) lessons from climate change knowledge services and climate-smart investments
financed under CAMP4ASB informing country planning processes, including through
scaled-up sectoral programs for climate smart development (3 plans and programs that
draw on Project’s climate knowledge services).
Implementation period: 2016-2022
Assumptions: The mitigation impact of this action has not been estimated.
Results:
Table 133. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 NA NA NA
2030 NA NA NA
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Number of project beneficiaries relative to the total population of Tajikistan.
Hectares covered by effective agriculture, land, and water management
practices.
Tons of carbon dioxide equivalent to be reduces or avoided.
Proposal of entity responsible for monitoring: The entities responsible for monitoring
the adaptation and mitigation program will be the Ministry of Agriculture, the Ministry of
Energy and Water Resources and the Committee for Environmental Protection under the
Government of the Republic of Tajikistan.
Timing: The implementation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
3.3. Building Climate Resilience of Vulnerable
and Food Insecure Communities through
Capacity Strengthening and Livelihood
Diversification in Mountainous Regions of
Tajikistan
Background documents: The description of the project is available at
https://www.greenclimate.fund/sites/default/files/document/funding-proposal-fp067-wfp-
tajikistan.pdf.
Description of the action: The project “Building climate resilience of vulnerable and
food insecure communities through capacity strengthening and livelihood diversification
in mountainous regions of Tajikistan” will increase the adaptive capacities of the most
vulnerable and food insecure communities residing in Rasht valley, Khatlon and
GornoBadakhshan Autonomous Region (GBAO) regions. Due to their location, these
communities are vulnerable to the negative impacts of climate change, particularly from
rainfall variability resulting in adverse livelihood impacts, increasing temperatures with
glacial melting and sudden onset extreme events causing loss and damage, in addition
to high levels of malnutrition and poverty (See Annex 1.3). The proposed project
intervention takes a transformative approach to ensure food security and support
communities to adapt to climate change through two key components:
i. Capacity strengthening and awareness raising of food insecure climate
vulnerable communities and national actors for enhanced rural resilience and
food security; and
ii. Resilience building at household and community level through diversification of
livelihoods and improved market access.
A key element of this approach will be addressing institutional capacity needs at both
national and sub-national levels to better understand needs and support vulnerable
communities develop effective responses to prepare for and manage climate risks.
Interventions of the project will reach 50,000 direct beneficiaries among the estimated
270,000 vulnerable individuals residing in climate vulnerable areas, and up to 70,000
indirect beneficiaries, who live in the proposed project locations. The proposed project
contributes to climate-resilient development pathways in Tajikistan through the sustained
impact of project measures that have high potential for replicability and scale. Overall,
many of these measures can be scaled to reach 100% of national coverage. The project
stimulates a demand-based model for climate information and use of ICT/mobile
platforms to enable public and private sector participation, innovation, and market
development. It contributes to key policies in the country and supports efforts to
mainstream gender-responsive climate change adaptation into development plans. It
institutionalizes knowledge generation and learning through the incorporation of climate
change and food security in national and district level planning processes. At the
Projections of GHG emissions to 2030 in Tajikistan
community level, the project introduces new technologies such as renewables,
rehabilitates dilapidated assets that take into account the diverse needs and capacities
of women and men and that strengthens community resilience through tailored social
and behavioural change interventions.
Implementation period: 2018-2022
Assumptions: The mitigation impact of this action has not been estimated.
Results:
Table 134. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 NA NA NA
2030 NA NA NA
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Number of project beneficiaries relative to the total population of Tajikistan.
Number of farmers with better understanding and knowledge regarding climate
change.
Number of greenhouses, storage facilities and renewable energy based systems
established.
Number of natural and physical livelihood assets created and improved for
increased community and household resilience.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the project will be the Committee for Environmental Protection under the Government of
the Republic of Tajikistan.
Timing: The implementation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
4. Waste
In the project no planned mitigation actions and with impact in waste emissions have
been identified.
Projections of GHG emissions to 2030 in Tajikistan
Section 7 - Mitigation Options
The following are the list of mitigation options identified by the working team based on
their mitigation potential for reducing GHG emissions in the country. The mitigation
options are considered under the WaM scenario (further information is available in
section 10 below).
1. Energy
The following are the mitigation actions which lead to GHG emission reductions in the
energy sector in Tajikistan.
1.1. Energy efficiency in the
residential/commercial/institutional sector
Background documents: NA
Description of the action: Replacement of coal boilers and stoves by efficient electric
devices.
Assumptions: The total terajoules (TJ) of anthracite consumed are calculated in the
national GHG emissions inventory and the WoM scenario for the residential, commercial,
and institutional sectors and considered as the reference scenario for the estimation of
impact of this action. This TJ will be replaced by electric devices for an equivalent
amount. It is assumed that all anthracite consumption is replaced by electricity
consumption by 2030.
Implementation Period: the mitigation option starts in 2022 and is implemented lineally
up to 2030.
Table 135. Reference scenario for the estimation of the potential GHG mitigation
impact
Variable
Valu
e
Unit
s
TJ of Anthracite consumption in the WoM for the residential, commercial
and institutional sectors - -
Table 136. Reduction scenario for the estimation of the potential GHG mitigation
impact
Projections of GHG emissions to 2030 in Tajikistan
Variable Value Units
Grid emission factor 0.0052 Gg CO2-eq / GWh
Conversion factor from TJ to GWh 0.28 TJ/GWh
Results:
Table 137. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 0.00 0.00 0.00
2020 0.00 0.00 0.00
2025 1454.05 817.28 636.77
2030 1957.51 28.70 1928.81
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Number of coal boilers and stoves replaced by efficient electric devices.
Total TJ of anthracite replaced by electricity consumption.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the energy efficiency will be the Ministry of Energy and Water Resources of the Republic
of Tajikistan.
Timing: The implementation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
1.2. Reduction of electricity consumption in
aluminium production
Background documents: NA
Description of the action: Aluminium production is highly energy-intensive, with
electricity making up a large share of the energy consumed. Aluminium production is one
of the key industries operating in Tajikistan. The reduction of energy intensities of
aluminium production would have a significative GHG emission reduction potential. An
increasing share of secondary production will be the primary catalyst of energy intensity
improvements. Primary production is approximately ten times more energy intensive than
secondary production.
Assumptions: all electricity used by the industry has been assumed to be consumed by
the aluminium industry. This consumption has been projected applying the evolution of
the GDP series. Through an improvement in the recycling and sorting of material, 50%
of national production of aluminium will be secondary. It is also assumed that primary
production is approximately ten times more energy intensive than secondary production
(https://www.iea.org/reports/tracking-industry/aluminium ).
Implementation Period: the mitigation option starts in 2022 and is implemented lineally
up to 2030.
Table 138. Reference scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
GHG emissions of the WoM
Grid emission factor 0.0052 Gg CO2-eq / GWh
Table 139. Reduction scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Secondary aluminium production 50 %
Energy efficiency improvements 90 %
Results:
Table 140. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
Projections of GHG emissions to 2030 in Tajikistan
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Percentage of secondary production used as the primary catalyst of energy.
MW of electricity consumed after the implementation of secondary production.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the reduction of electricity consumption will be the Ministry of Energy and Water
Resources of the Republic of Tajikistan.
Timing: The implementation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
2. Industrial Processes and Product Use
The following are the mitigation actions which lead to GHG emission reductions in the
IPPU sector in Tajikistan.
2.1. Reduction of clinker content of cement
Background documents: NA
Description of the action: The emissions of cement production occur in the production
of clinker. By reducing the clinker content of cement, the emissions of the process are
reduced significantly
Assumptions: National total cement production is calculated from clinker production,
assuming it contains a 95% of clinker.
The reduction scenario is calculated assuming a clinker content in the cement of 70 %,
in a slag-modified Portland. All clinker is assumed to be produced in Tajikistan
Implementation Period: the mitigation option starts in 2022 and is implemented lineally
up to 2030.
Table 141. Reference scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Content of clinker in cement 95% %
Emission factor 0.52 Tonnes CO2 / tonne clinker
Table 142. Reduction scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Content of clinker in cement 70% %
Emission factor 0.52 Tonnes CO2 / tonne clinker
Results:
Table 143. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 1517.34 1339.87 177.47
Projections of GHG emissions to 2030 in Tajikistan
2030 1936.55 1426.93 509.62
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Percentage of clinker content in cement.
Kilograms of cement produced in Tajikistan.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the reduction of clinker content will be the Ministry of Energy and Water Resources of
the Republic of Tajikistan.
Timing: The implementation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
2.2. Phase down of F-gases
Background documents: NA
Description of the action: F-gases consumed in refrigeration, air conditioning, fire
extinguishers and aerosols are replaced by low carbon refrigerants.
Assumptions: It is assumed that 50% of the market is replaced by low carbon
alternatives by 2030. The estimate made in the WoM scenario is assumed to be reduced
by a 50%.
Implementation Period: the mitigation option starts in 2022 and is implemented lineally
up to 2030.
Results:
Table 144. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 372.58 289.78 82.80
2030 414.28 207.14 207.14
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Number of refrigeration, air conditioning, fire extinguishers, and aerosols using
low carbon refrigerants.
Number of refrigeration, air conditioning, fire extinguishers, and aerosols
consuming F-gases.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the mitigation option will be the Ministry of Energy and Water Resources of the Republic
of Tajikistan.
Timing: The implementation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
3. AFOLU
The following are the mitigation actions which lead to GHG emission reductions in the
AFOLU sector in Tajikistan.
3.1. Enhancing removals by creating new fruit
orchards and vineyards
Background documents: NA
Description of the action: Horticulture and viticulture is one of the key agricultural
sectors of the Republic of Tajikistan, able to provide the country's domestic market with
food, increase the export potential of the republic and provide the population with
permanent work.
According to the "Horticulture and Viticulture Development Program in the Republic of
Tajikistan for 2016 – 2020", there is a shortage of fruits to ensure the physiological needs
of the country's population and to ensure food security. On the other hand, the plantation
of new high-yielding fruit orchards will increase woody biomass carbon sequestration.
This mitigation option is associated to the plantation of new fruit orchards and vineyards,
in addition to those referred in the "Horticulture and Viticulture Development Program in
the Republic of Tajikistan for 2016 – 2020".
Assumptions: The mitigation impact was calculated by considering that the baseline
emissions are those as included in the inventory. Since the IPCC Tier 1 method was
applied for the inventory, the same method was applied to estimate the mitigation impact.
Woody fruit trees in orchards and vineyards can store significant carbon in long-lived
biomass, the amount depending on species type and cultivar, density, growth rates, and
harvesting and pruning practices.
The mitigation potential that is associated to the plantation of new orchards and vineyards
on an area of 20 thousand hectares for the 5 years period up to 2025 is estimated (10%
vineyards and 90% fruit orchards).
It was assumed that these plantations accumulate biomass linearly until they reach
maturity, assumed to be at half the replacement cycle. During maturity biomass increases
are offset by losses from pruning - in order the tree to be retained to the desired form -
and natural mortality, and hence changes in living biomass are assumed to be zero. The
annual growth rate (GW), during the growth period, is derived thus by dividing biomass
stock at maturity by the time from crop establishment to maturity reach.
Implementation Period: 2026-2030
Projections of GHG emissions to 2030 in Tajikistan
Table 145. General assumptions for the estimation of the Increase of above
ground biomass C stock due to new woody plantations (orchards and vineyards)
Tree crops
Average
Aboveground
fresh biomass
stock
Biomass
moisture
Average
Aboveground
biomass stock
Carbon
fraction of
dry matter
Average
aboveground
biomass C
stock
Harvest
cycle
Annual C
uptake from
crop growth
t fresh b/ha % t dm/ha t C/t dm t C/ha yr t C/ha yr
Vineyards 20 40 12 0.5 6 26 0.46153846
Fruit trees 80 40 48 0.5 24 26 1.84615385
Land of new woody plantations 20,000 Ha
Land of vineyards 2,000 Ha
Land of fruit plantations 18,000 Ha
Mitigation effect 125.23 ktCO2/year
Results:
Table 146. GHG emission reduction impact (Gg CO2-eq)
Year Impact of Mitigation
action
2016 NA
2020 NA
2025 NA
2030 125.23
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Hectares of newly planted fruit orchards
Hectares of newly planted vineyards.
Hectares of newly planted woody plantations.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the plantation will be the Ministry of Agriculture of the Republic of Tajikistan.
Timing: The implementation of this action will be monitored on a biannual basis.
Projections of GHG emissions to 2030 in Tajikistan
3.2. Agroforestry and / or silvo-pastoral systems
Background documents: NA
Description of the action: Agroforestry and silvo-pastoral systems is the production of
livestock or food crops on land that also grows trees for timber, firewood, or other tree
products. It includes shelter belts and riparian zones/buffer strips with woody species.
The standing stock of carbon above ground is usually higher than the equivalent land
use without trees, and planting trees may also increase soil carbon sequestration.
Planting shrubs and trees in pastures or alleys interspersed with food crops to provide
additional sources of high-quality forage and improve animal nutrition.
Trees planted for silvo-pastoral systems can result in increased carbon stocks in living
biomass. They also systems provide more wood, reduce demand/pressure on wood
removals from forest, which cause forest degradation. The quality of forage improves,
and soil organic matter is maintained.
This mitigation option is associated to the improving agroforestry and/or silvo-pastoral
systems by planting shrubs and trees in pastures and agricultural land.
Assumptions: According to national statistics, the sown area of agricultural crops for
2018 in Tajikistan is 826,705 ha. The mitigation option of setting under agro-forestry a
20% of agricultural land up to 2025. will be estimated. In addition, the mitigation option
of setting under silvo-pastoral systems a 5% of pastures will be estimated (3,847,522 ha)
up to 2025.
The mitigation impact will be calculated by using the guidance from the WGII of the 4th
AR of IPCC related to Agriculture (Smith et al 2007)22.
Implementation Period: 2026-2030
Table 147. General assumptions for the estimation of the potential GHG
mitigation effect of agro-forestry practices
Variable Value Units
Total sown area of agricultural crops for 2018 826,705 ha
Percentage of land under agroforestry 20%
Annual mitigation potentials 0.35 tCO2eq/ha/yr
Mitigation impact 57.87 ktCO2/yr
22 Smith, P., D. Martino, Z. Cai, D. Gwary, H. Janzen, P. Kumar, B. McCarl, S. Ogle, F. O’Mara, C. Rice, B. Scholes, O. Sirotenko, 2007: Agriculture. In Climate Change 2007: Mitigation. Contribution of Working Group III to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change [B. Metz, O.R. Davidson, P.R. Bosch, R. Dave, L.A. Meyer (eds)], Cambridge University Press, Cambridge, United Kingdom and New York, NY, USA.
Projections of GHG emissions to 2030 in Tajikistan
Table 148. General assumptions for the estimation of the potential GHG
mitigation effect of silvo-pastoral systems
Variable Value Units
Total area of pastures 3,847,522 ha
Percentage of land under agroforestry 5%
Annual mitigation potentials 0.35 tCO2eq/ha/yr
mitigation impact 67.33 ktCO2/yr
Results:
Table 149. GHG emission reduction impact (Gg CO2-eq)
Year Impact of Mitigation
action
2016 NA
2020 NA
2025 NA
2030 125.20
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Hectares of agricultural land planted with shrubs and trees.
Hectares of pastures planted with shrubs and trees.
Total hectares of created agroforestry and/or silvo-pastoral systems.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the plantation will be the Ministry of Agriculture of the Republic of Tajikistan.
Timing: The implementation of this action will be monitored on a biannual basis.
Projections of GHG emissions to 2030 in Tajikistan
3.3. Minimal or no tillage/residue management
Background documents: NA
Description of the action: Advances in weed control methods and farm machinery now
allow many crops to be grown with minimal tillage (reduced tillage) or without tillage (no-
till). Since soil disturbance tends to stimulate soil carbon losses through enhanced
decomposition and erosion, reduced- or no-till agriculture often results in soil carbon gain.
Further, no-tillage systems can reduce CO2 emissions from energy use. Systems that
retain crop residues also tend to increase soil carbon because these residues are the
precursors for soil organic matter, the main carbon store in soil. Avoiding the burning of
residues also avoids emissions of aerosols and GHGs generated from fire, although CO2
emissions from fuel use may increase.
Switching to no-till or conservation tillage agriculture has the following effects that are
related to potential mitigation potential:
Soils are less disturbed or undisturbed; crop residues are not incorporated or are
less incorporated
Organic matter decomposition is slowed compared to disturbed soils (due to
reduced aeration and oxidation)
Soil organic carbon content increases; soil quality and resilience is enhanced;
formation of more stable humus is increase
Fossil fuel consumption decreases
This mitigation option is associated to switching to no-till or conservation tillage
agriculture. Currently, according to the monitoring of the "Agriculture Reform Programme
of the Republic of Tajikistan for 2012-2020", minimal or zero tillage (mulching) is carried
out on 5% of the total area of arable land.
Assumptions: According to national statistics, the sown area of agricultural crops for
2018 in Tajikistan is 826,705 ha. Currently, minimal or zero tillage (mulching) is carried
out on 5% of the total area of arable land in Tajikistan. The potential GHG mitigation
effect of the option of increasing the no-till or conservation tillage agriculture to 15% up
to 2025 will be estimated.
The mitigation impact will be calculated by using the guidance from the WGII of the 4th
AR of IPCC related to Agriculture (Smith et al 2007)23.
23 Smith, P., D. Martino, Z. Cai, D. Gwary, H. Janzen, P. Kumar, B. McCarl, S. Ogle, F. O’Mara, C. Rice, B. Scholes, O. Sirotenko, 2007: Agriculture. In Climate Change 2007: Mitigation. Contribution of Working Group III to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change [B. Metz, O.R. Davidson, P.R. Bosch, R. Dave, L.A. Meyer (eds)], Cambridge University Press, Cambridge, United Kingdom and New York, NY, USA.
Projections of GHG emissions to 2030 in Tajikistan
Implementation Period: 2026-2030
Table 150. General assumptions for the estimation of the potential GHG
mitigation effect
Variable Value Units
Total sown area of agricultural crops for 2018 826,705 ha
Additional percentage of land under no-till or
conservation tillage agriculture 10%
Annual mitigation potentials 0.35 tCO2eq/ha/yr
Mitigation impact 28.93 ktCO2/yr
Results:
Table 151. GHG emission reduction impact (Gg CO2-eq)
Year Impact of Mitigation
action
2016 NA
2020 NA
2025 NA
2030 28.93
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Hectares of agricultural land switched to no-till agriculture.
Hectares of agricultural land switched to conservation tillage agriculture.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the switch will be the Ministry of Agriculture of the Republic of Tajikistan.
Timing: The implementation of this action will be monitored on a biannual basis.
Projections of GHG emissions to 2030 in Tajikistan
3.4. Improved agronomic practices through the
continuation of the Development Program for
Seed Production of the Republic of Tajikistan
Background documents: NA
Description of the action: The main objective of the Program was the promotion of
selection and seed-growing with a view of formation of this sector of the national economy
capable of the functioning in compliance with international norms and standards.
Selection and seed-growing must be aimed at the promotion of plant varieties,
introduction, testing and registration of plant varieties, use of different seed-growing
methods for the extension of crop cultivation through application of new technologies,
and also commercial production, reproduction, processing, certification and marketing of
high quality seeds for internal market and export. In particular, this Program is oriented
towards introduction of new high-yielding cotton varieties and production of high-quality
cotton seeds.
This mitigation option refers to the continuation of the "Development Program for Seed
Production of the Republic of Tajikistan for 2016 - 2020" up to 2025. The potential
mitigation effect will be estimated by assuming that the continuation of the Programme
would result in an additional use of arable area under elite seeds.
Assumptions: The potential GHG mitigation impact will be related to an additional
increase in the area under elite seeds. We assume that elite seeds will be used for an
additional 10% of agricultural land up to 2025, which is used for the following agricultural
crops: cotton, cereals, legumes, potatoes and fodder crops. The mitigation potential will
be correlated to the improved agronomic practices that increase yields and generate
higher inputs of carbon residue and by this way can lead to increased soil carbon storage.
The type of improved agronomic practice is the use of improved crop varieties.
The mitigation impact will be calculated by using the guidance from the WGII of the 4th
AR of IPCC related to Agriculture (Smith et al 2007)24.
Implementation Period: 2026-2030
24 Smith, P., D. Martino, Z. Cai, D. Gwary, H. Janzen, P. Kumar, B. McCarl, S. Ogle, F. O’Mara, C. Rice, B. Scholes, O. Sirotenko, 2007: Agriculture. In Climate Change 2007: Mitigation. Contribution of Working Group III to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change [B. Metz, O.R. Davidson, P.R. Bosch, R. Dave, L.A. Meyer (eds)], Cambridge University Press, Cambridge, United Kingdom and New York, NY, USA
Projections of GHG emissions to 2030 in Tajikistan
Table 152. Arable area per crop25
Crop Area Units
Cotton 254,830 ha
Cereals 384,940 ha
Legumes 11,790 ha
Potatoes 29,750 ha
Fodder crops 166,490 ha
Table 153. General assumptions for the estimation of the potential GHG
mitigation impact
Variable Value Units
Total area of cotton, cereals,
legumes, potatoes and fodder
crops
847,800 ha
Percentage of land under
improved agronomy practices 10%
Annual mitigation potentials 0.39 tCO2eq/ha/yr
Mitigation impact 33.06 ktCO2/yr
Results:
Table 154. GHG emission reduction impact (Gg CO2-eq)
Year Impact of Mitigation
action
2016 NA
2020 NA
2025 NA
2030 33.06
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Number of newly used high-yielding seed-growing methods
Hectares of land used to plant elite seeds such as cotton, cereals, legumes,
potatoes, and fodder crops.
25 Source: STATE OF PLANT GENETIC RESOURCES FOR FOOD AND AGRICULTURE (PGRFA) IN THE REPUBLIC OF TAJIKISTAN, COUNTRY REPORT BY PROF. DR. HAFIZ MUMINJANOV, DUSHANBE 2008
Projections of GHG emissions to 2030 in Tajikistan
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the seed development will be the Ministry of Agriculture of the Republic of Tajikistan.
Timing: The implementation of this action will be monitored on a biannual basis.
Projections of GHG emissions to 2030 in Tajikistan
3.5. Livestock Management through the
continuation of the Comprehensive livestock
development program
Background documents: NA
Description of the action: Integrated Program of Livestock Sector Development in the
Republic of Tajikistan for the period of 2018-2022 is a cross-sectoral policy document
envisaging the development of the livestock sector, which covers a range of zootechnical,
biotechnological and economic measures aimed at growing, preserving and increasing
the number of cattle, poultry, bees, fish, and their breeds in the country, as well as the
breeding of new high-yielding breeds. At the same time, ensuring the development of
livestock breeding industries within the framework of measures aimed at organizing and
conducting selection and breeding works, improving growing technology and feeding
standards for livestock, poultry, fish and bees, and increasing productivity of pastures by
indigenous and surface methods with the use of modern achievements. For further
development of the livestock sector, it is very important to provide a stable fodder supply
and it is expedient to create enterprises for the production of mixed fodder.
This mitigation option refers to the continuation of the "Comprehensive livestock
development program for 2018 - 2022" up to 2027. The potential mitigation effect will be
estimated by assuming that the continuation of the Programme would affect the 40% of
cattle population.
Assumptions: The estimation of the mitigation impacts are consistent with the data and
methods applied in the National Inventory of Tajikistan.
The mitigation impact will be calculated by using the guidance from the WGII of the 4th
AR of IPCC related to Agriculture (Smith et al 2007).26
The affected livestock population from the continuation of the Programme is assumed to
be 40% of cattle population.
Implementation period: 2028-2030
Table 155. General assumptions for the estimation of the potential GHG
mitigation effect
26 Smith, P., D. Martino, Z. Cai, D. Gwary, H. Janzen, P. Kumar, B. McCarl, S. Ogle, F. O’Mara, C. Rice, B. Scholes, O. Sirotenko, 2007: Agriculture. In Climate Change 2007: Mitigation. Contribution of Working Group III to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change [B. Metz, O.R. Davidson, P.R. Bosch, R. Dave, L.A. Meyer (eds)], Cambridge University Press, Cambridge, United Kingdom and New York, NY, USA.
Projections of GHG emissions to 2030 in Tajikistan
Variable Value Units Source
Total Cattle in 2016 2,278,072 heads National inventory
Percentage of cattle affected by
the programme 40% % Assumption
Enteric methane production in
2016 132 kt CH4 National inventory
GWP of CH4 25 4AR IPCC
Enteric methane production in
2016 2763.747 kt CO2 eq National inventory
Technical reduction potential
(proportion of an animal’s enteric
methane production) for enteric
methane emissions due to longer
term structural/management
change and animal breeding
2% IPCC 2007
Efficiency of the programme 80% % Assumption
Mitigation effect 13.27 kt CO2 eq/year Calculation
Results:
Table 156. GHG emission reduction impact (Gg CO2-eq)
Year Impact of Mitigation
action
2016 NA
2020 NA
2025 NA
2030 15.79
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Percentage of the cattle population affected by the newly high-yielding breeds.
Percentage of the cattle population affected by the newly introduced modern
technologies.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the cattle population under the project will be the Ministry of Agriculture of the Republic
of Tajikistan.
Timing: The implementation of this action will be monitored on a biannual basis.
Projections of GHG emissions to 2030 in Tajikistan
3.6. Fat supplementation in ruminants’ diets
Background documents: NA
Description of the action: Fat supplementation is one of various feeding practices
aiming to reduce GHG emission from livestock operations (others include, for example,
reduced protein content of the diet and feed supplements). This measure is based on
increasing some of the commonly used feed ingredients in the diet. A traditional ruminant
diet, depending on whether the animal is mostly grazing or fed a high proportion of
concentrates (non-forage feeds high in energy and/or protein content, e.g. a mixture of
grains, soybean meal, beet pulp, etc.) contains 1.5-3 dry matter % (DM%) fat. Increasing
the fat content reduces enteric CH4 emissions from the rumen via biological processes
in the digestive system. The CH4 reduction is proportional to the fat content, but, due to
potential health issues and practical aspects, a limit of 5-6 DM% total fat content is
necessary. Various supplementary fat sources exist: whole seeds (e.g. rapeseed,
linseed, soybean), plant oils (e.g. sunflower oil, rapeseed oil, palm oil, coconut oil), and
special products (e.g. Energy Booster, Megalac). Alternative sources can be the high-oil
by-products of the biofuel industries. Some farmers with high-productivity herds are
already supplementing fat to their animals, to boost the energy content of the diet.
However, even for those animals the total fat content might be below 5-6 DM%. The
additional uptake potential is even higher in those herds which are currently not receiving
fat supplementation, though the incorporation of fat in the diet for animals mainly fed on
forages (i.e. grazing and cut grass) might not be practical.
Assumptions: The mitigation impact will be calculated by using the guidance from the
following reference:
MacLeod, M. et al. (2015-08-01), “Cost-Effectiveness of Greenhouse Gas Mitigation
Measures for Agriculture: A Literature Review”, OECD Food, Agriculture and Fisheries
Papers, No. 89, OECD Publishing, Paris.
With every 1% fat added, CH4 emissions are reduced by approximately 4% across all
ruminants. We assume that fat supplementation may be performed to 10% of cattle
population.
Implementation period: 2025-2030
Table 157. General assumptions for the estimation of the potential GHG
mitigation effect
Variable Value Units Source
Total Cattle in 2016 2,278,072 heads National inventory
Percentage of cattle affected by
the mitigation option 10% % Assumption
Enteric methane production in
2016 132 kt CH4 National inventory
Projections of GHG emissions to 2030 in Tajikistan
Variable Value Units Source
GWP of CH4 25 - 4AR IPCC
Enteric methane production in
2016 2763.747 kt CO2 eq National inventory
Fat added to animal feed 2 %DM fat added Assumption
1% fat added 4% Reduction in CH4 Assumption
Mitigation effect 22.11 kt CO2 eq/year Calculation
Results:
Table 158. GHG emission reduction impact (Gg CO2-eq)
Year Impact of Mitigation
action
2016 NA
2020 NA
2025 26.32
2030 26.32
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Percentage of dietary fat contents of the cattle population.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the cattle’s diet will be the Ministry of Agriculture of the Republic of Tajikistan.
Timing: The implementation of this action will be monitored on a biannual basis.
Projections of GHG emissions to 2030 in Tajikistan
3.7. Rice cultivation management
Background documents: NA
Description of the action: Cultivated wetland rice soils emit significant quantities of
methane. Emissions during the growing season can be reduced by various practices.
For example, draining wetland rice once or several times during the growing season
reduces CH4 emissions. Rice cultivars with low exudation rates could offer an important
methane mitigation option. In the off-rice season, methane emissions can be reduced by
improved water management, especially by keeping the soil as dry as possible and
avoiding water logging. Increasing rice production can also enhance soil organic carbon
stocks. Methane emissions can be reduced by adjusting the timing of organic residue
additions (e.g., incorporating organic materials in the dry period rather than in flooded
periods; by composting the residues before incorporation, or by producing biogas for use
as fuel for energy production.
According to the national GHG inventory, the rice straw is incorporated shortly (<30days)
before cultivation. There is a GHG mitigation potential in the case of a long fallow after
rice straw incorporation: CH4 emissions in the ensuing rice-growing season will be less
than the case that rice straw is incorporated just before rice transplanting. This mitigation
option refers to the above-mentioned mitigation potential.
Assumptions: The estimation of the mitigation impacts are consistent with the data and
methods applied in the National Inventory of Tajikistan. The mitigation impact was
calculated by considering that the baseline emissions are those as included in the
inventory. Since the IPCC Tier 1 method was applied for the inventory, the same method
was applied to estimate the mitigation impact.
Implementation period: 2021-2030
Table 159. General assumptions for the estimation of the potential GHG
mitigation effect
Variable Value Units Source
Conversion factor
(CFOA) for the case that straw is
incorporated shortly (<30 days)
before cultivation
1 - 2006 IPCC GLs
Conversion factor
(CFOA) for the case that straw is
incorporated long (>30 days) before
cultivation
0.29 - 2006 IPCC GLs
Adjusted daily EF for a particular
harvested area (straw is
incorporated shortly)
3.71796 kgCH4/ha/day 2006 IPCC GLs +
National inventory
Projections of GHG emissions to 2030 in Tajikistan
Variable Value Units Source
Adjusted daily EF for a particular
harvested area (straw is
incorporated long)
2.87042 kgCH4/ha/day 2006 IPCC GLs +
National inventory
Area of rice cultivation 20,501 ha National inventory
Cultivation period 135 days National inventory
GWP of CH4 25 - 4AR IPCC
Mitigation effect 49.26 kt CO2 eq/year Calculation
Results:
Table 160. GHG emission reduction impact (Gg CO2-eq)
Year Impact of Mitigation
action
2016 NA
2020 NA
2025 58.64
2030 58.64
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Number of days the rice straw is incorporated before cultivation.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the rice cultivation management will be the Ministry of Agriculture of the Republic of
Tajikistan.
Timing: The implementation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
3.8. Continuation of the Pasture Development
Programme after 2020
Background documents: NA
Description of the action: Improving the condition of pastures has a special place in
ensuring the food security of the country and reducing poverty. At the same time, it
should be noted that in recent years, most of the pastures have been degraded,
especially pastures located near settlements and some of them are turning into a desert
zone. In many pastures, water supply facilities are unsuitable for exploitation. Due to the
lack of cattle drive roads and bridges, watering and feeding areas, about 1 million
hectares of pastures are partially used, and some areas are not used at all. As a result
of mudflow rains, hail, fires and other natural and anthropogenic factors, more than a
thousand hectares of pastures annually undergo degradation and erosion. At the same
time, according to statistics, in comparison with 1991, the livestock population increased.
Due to the lack of grazing feed in the winter, livestock loss of small livestock from 10 to
25 percent occurs.
Failure to prevent this unfavorable situation can lead to dangerous irretrievable
consequences. For the development of animal husbandry, it is necessary to create a
solid fodder base. Based on this, improvement of quality, productivity, appropriate and
rational regulation and use of pastures are the main factors in the development of
agriculture production. Please to the link:
http://extwprlegs1.fao.org/docs/pdf/taj170827.pdf for more details about the Programme.
This mitigation option refers to the continuation of the Pasture Development Program of
the Republic of Tajikistan up to 2025, covering an area of pastures of 20,000 ha.
Assumptions: The estimation of the mitigation impacts are consistent with the data and
methods applied in the National Inventory of Tajikistan. The mitigation impact was
calculated by considering that the baseline emissions are those as included in the
inventory. Since the IPCC Tier 1 method was applied for the inventory, the same method
was applied to estimate the mitigation impact.
The mitigation effect does not reflect any potential positive impact to livestock productivity
associated to increased availability of fodder and grass from pastures.
Implementation period: 2026-2030
Table 161. General assumptions for the estimation of the soil carbon stock
increment due to pastures’ improvement
Land-use
category
Reference
soil
carbon
stock
Stock change factors
Representative
soil carbon
stock
Parameter
s source
Projections of GHG emissions to 2030 in Tajikistan
SOCref
(tC/ha) F(LU) F(MG) F(I) SOC (tC/ha)
Grassland
(pasture)
before
LPDP
4 1 0.9 1 3.6 National
inventory
Grassland-
improved
pasture
after LPDP
4 1 1.14 1 4.56
National
inventory
& 2006
IPCC GLs
Pasture land improved 20000 Ha
Transition period for soils 20 years
Mitigation effect 3.52 ktCO2/year
Results:
Table 162. GHG emission reduction impact (Gg CO2-eq)
Year Impact of Mitigation
action
2016 NA
2020 NA
2025 NA
2030 3.52
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Stocks of pasture vegetation after the continuation of the Pasture Development
Programme.
Hectares of improved pastures.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the Pasture Development Programme will be the Ministry of Agriculture of the Republic
of Tajikistan.
Timing: The implementation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
4. Waste
The following are the mitigation actions which lead to GHG emission reductions in the
waste sector in Tajikistan.
4.1. Reduction of open burning
Background documents: NA
Description of the action: In line with national efforts to improve solid waste practices,
the national waste management system could be extended to rural areas, reducing the
GHG emissions that occur in the open burning of waste. This mitigation option assumes
that all wastes generated by rural population are treated in solid waste disposal sites.
Assumptions: GHG emissions from open burning of waste will be eliminated and will be
replaced by those occurring in landfills.
GHG emissions from landfills in rural areas are calculated in the 2006 IPCC waste model
using the same parameters used for urban population emissions calculated in the WoM.
Implementation Period: the mitigation option starts in 2022 and is implemented lineally
up to 2030.
Table 163. Reference scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Open burning GHG emissions per capita 0.07595 GHG emissions/thousand inhabitants
Table 164. Reduction scenario for the estimation of the potential GHG mitigation
impact
Variable Value Units
Waste treatment Managed semi-anaerobic -
Methane correction
factor 0.5
wt.
Fraction
Waste per capita 275 kg/cap/yr
% to SWDS 74 %
Waste composition
Food (31%); Garden (13%); Paper (11%); Wood
(0%);
Textile (2%); Nappies (0%); Plastic and other inert
(43%) %
Results:
Projections of GHG emissions to 2030 in Tajikistan
Table 165. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 581.72 390.19 191.54
2030 648.59 319.81 328.78
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Percentage of generated waste by rural population collected.
Percentage of generated waste by rural population treated in open burning waste
locations.
Percentage of generated waste by rural population treated in landfills.
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the reduction of open burning will be the Ministry of Industry and New Technologies of
the Republic of Tajikistan.
Timing: The implementation of this action will be monitored on an annual basis.
Projections of GHG emissions to 2030 in Tajikistan
4.2. Improved wastewater management practices
Background documents: NA
Description of the action: In line with national efforts to improve wastewater
management practices, this mitigation option assumes that the wastewater generation of
all population is discharged and treated in advanced wastewater treatment plants
Assumptions: The mitigation actions W2, W3, W4 and W5 address a change in
practices in wastewater treatment. Following the same methodology, this mitigation
action estimates the impact of the improvement of wastewater systems for all population.
The same methodology of the WoM (tier 1 IPCC 2006) is applied for the reference
scenario
For the reduction scenario, we assumed the treatment type "Centralized, aerobic
treatment plant ". For the urban areas, we chose the option "Not well managed.
Overloaded". For rural areas, we selected the option "well managed" from Table 6.3 of
IPCC 2006.
As the EF for well managed aerobic plants is zero in 2006 IPCC Guidelines, we assumed
the alternative for rural areas have certain level of emissions, represented in an emission
factor slightly higher than zero
Implementation Period: the mitigation option starts in 2025 and is implemented lineally
up to 2030.
Table 166. Reference scenario
Variable Value Units
Type of population affected Urban and rural -
Type of treatment or
discharge pathway
Septic tank, sewer and latrines, at
different % in urban and rural areas -
Population affected
Total population (except population
covered in actions W2, W3, W4 and
W5) Population
Biochemical Oxygen Demand (BOD) 14.6
kg
BOD/capita/year
Emission factor Septic tank 0.3 kg CH4/kg BOD
Degree of utilisation septic tank in urban
areas 10% Percentage
Degree of utilisation septic tank in rural
areas 30% Percentage
Emission factor Sewer 0.15 kg CH4/kg BOD
Degree of utilisation Sewer in urban areas 90% Percentage
Degree of utilisation Sewer in rural areas 60% Percentage
Emission factor latrines 0.06 kg CH4/kg BOD
Projections of GHG emissions to 2030 in Tajikistan
Variable Value Units
Degree of utilisation latrines in urban
areas 0 Percentage
Degree of utilisation latrines in rural areas 10% Percentage
Table 167. Reduction scenario
Variable Value Units
Type of population affected Urban -
Type of treatment or
discharge pathway Centralized, aerobic treatment plant -
Population affected
Total population (except population
covered in actions W2, W3, W4 and
W5) Population
Biochemical Oxygen Demand (BOD) 14.6
kg
BOD/capita/year
Emission factor urban areas 0 kg CH4/kg BOD
Emission factor rural areas 0.18 kg CH4/kg BOD
Degree of utilisation 100% Percentage
Results:
Table 168. GHG emission reduction impact (Gg CO2-eq)
Year Emissions in the
reference option
Emissions in the
reduction option
Impact of Mitigation
action
2016 NA NA NA
2020 NA NA NA
2025 659.40 484.82 174.58
2030 733.29 539.53 193.76
Proposal of monitoring indicator: The implementation of this project will be monitored
through the following indicators:
Percentage of wastewater of all population treated by "Centralized, aerobic
treatment plant".
Percentage of wastewater of rural population treated "Not well managed.
Overloaded".
Percentage of wastewater of urban population treated "Well managed".
Proposal of entity responsible for monitoring: The entity responsible for monitoring
the wastewater management will be the Ministry Energy and Water Resources of the
Republic of Tajikistan.
Timing: The implementation of this action will be monitored on a biannual basis.
Projections of GHG emissions to 2030 in Tajikistan
Section 8- With Existing Measures
Scenario
The With Existing Measures (WeM) scenario is calculated from the WoM scenario by
subtracting the estimated mitigation impact of the actions under implementation since
2015. This includes mitigation actions that were adopted after 2015 but their
implementation is not yet finalized. Detailed information about these actions and their
mitigation impact is provided under section 5 of this report.
The WeM scenario can be seen as Business as Usual Scenario, representing a forecast
which assumes no further changes in the current circumstances. Under this scenario,
Tajikistan would not take additional climate change actions in the future. However, the
future mitigation impact of the mitigation actions which have been implemented or are
under implementation since 2015 are taken into account.
The following figure shows the WeM scenario compared to the WoM scenario, noting
that the differences between scenarios are only due to the impact of the mentioned
mitigation actions.
Figure 4. GHG emission projections in the WeM and WoM scenarios (Gg CO2-eq)
As illustrated in the previous figure, the mitigation impact of the policies under
implementation after 2015 in the country does not produce a significant change in the
GHG emission pathway of the country. With the current mitigation actions, Tajikistan will
not meet its conditional NDC target, which is defined as 65-75% reduction in the GHG
emissions levels of 1990 by 2030.
Tajikistan counts with a sectoral policy framework which form the foundation for the
future low carbon development of the country. Nevertheless, the objectives and strategic
lines defined in these policy frameworks are not always translated into mitigation actions
Projections of GHG emissions to 2030 in Tajikistan
with real GHG emission reductions. This is in fact the reason for the limited GHG
emission reduction impact of the mitigation actions implemented in Tajikistan.
Streamlining climate change in the existent policy instruments should be a priority to
achieve a low carbon development pathway in Tajikistan.
Projections of GHG emissions to 2030 in Tajikistan
Section 9 - With Additional Measures
Scenario
The With Additional Measures (WaM) scenario is calculated from the WeM scenario by
subtracting the estimated mitigation impact of additional actions planned to be
implemented in the country (described in section 6) as well as the impact of the most
significant mitigation options identified by the working team (described in section 7).
The WaM scenario represent a GHG emission profile for the country in which all actions
planned to be implemented in the future are undertaken, and all the key mitigation
possibilities for the country are also implemented. This scenario could be seen as the
GHG emissions profile that the country could achieve if appropriate national and
international resources are mobilized.
The conditional NDC target is by far achieved under this scenario, as shown in the
following figure.
Figure 5. GHG emissions in the WaM scenario (Gg CO2-eq)
Analysis of the future GHG emission profile
and mitigation options available
In the energy sector, the greatest mitigation potential is found in the energy industries
and in the residential, commercial and institutional sectors, the areas producing the
largest GHG emissions in both the historical and projected (i.e. in the WoM) periods
within this sector.
Projections of GHG emissions to 2030 in Tajikistan
In energy industries, the high levels of installed hydroelectric capacity limits the current
GHG emissions of the electricity sector. Future GHG emissions in energy industries
depend on the finalization of the Rogun Hydropower plant. This power plant will
represent an addition of 3,600 MW to the electricity generation capacity of the country,
limiting the need of fossil fuel generation for meeting national electricity demand.
Conversely, if this plant is not finally commissioned, additional fossil generation capacity
will be needed to avoid shortages in the winter period. This will also involve significantly
higher GHG emissions in the energy sector (as represented in the WoM scenario).
Notwithstanding the foregoing, the greatest mitigation opportunity identified for the
energy sector is in the residential, commercial, and institutional sector. The use of coal
(anthracite) in these sectors is one of the biggest emission sources of the inventory. The
replacement of boilers, kitchens and stoves using coal for equivalent electric appliances
will significantly reduce the emissions of these emission sources. Complementarily,
energy efficiency measures to reduce energy consumption could be also considered to
reduce the contribution of these sector to national GHG emissions.
Aluminium production is one of the key industries operating in Tajikistan and is highly
energy intensive. The reduction of the energy intensity in the production of aluminum
through the incentive of secondary aluminum production practices is another possibility
to reduce the GHG emissions of the energy sector significantly. The promotion of Best
Available Techniques27 in the industry will reduce the energy consumption requirements
of the industry, limiting its GHG emissions. Tajikistan should consider addressing this
issue in the framework of its Strategy for the development of industry in the Republic of
Tajikistan, by including specific actions for future implementation.
The transport sector has a limited contribution to energy sector GHG emissions.
However, the transport sector is an essential sector for the development of the country,
and it should be considered in the core of the mitigation strategy of the country.
Continuing the renovation of the public transport infrastructure and providing incentives
to stimulate its use should be a priority for the climate change action of the country in the
future.
Industrial processes and product use emissions (IPPU) are dominated by the
contribution of the cement industry, in which the recent commissioning of cement plants
sharply increased its emissions. Measures to promote the reduction of the clinker content
of cement will reduce largely the emissions of the IPPU sector and have been identified
as a key mitigation potential alternative for the country.
Additionally, the refrigeration and air conditioning market of Tajikistan is increasingly
using F-gases to replace CFC and HCFC. These gases have a very high global warming
potential, affecting the GHG emission profile of the country. The future replacement of
27 https://eippcb.jrc.ec.europa.eu/reference
Projections of GHG emissions to 2030 in Tajikistan
F-gases for climate friendly alternatives will also have a representative mitigation
potential.
In the waste sector, Tajikistan is making substantial efforts to improve its solid waste and
wastewater management practices, in line with the national policy framework. The
expansion of the solid waste management practices and the reduction of open burning
of wastes in the rural areas is identified as a key opportunity for reducing GHG emissions
with outstanding co-benefits in terms of health and air quality. Furthermore, continuing
with the renovation of wastewater treatment plants have been also identified as a
relevant mitigation opportunity for the country.
Projections of GHG emissions to 2030 in Tajikistan
Section 10 – Summary of results
The following figure illustrate the GHG emission projections of Tajikistan up to 2030
under the WoM, WeM and WaM scenarios. These GHG emission projections are in line
with the macroeconomic framework projected in the National Development Strategy to
2030 for the industrial scenario28.
Figure 6. GHG emission projections by scenario and NDC targets of Tajikistan
(Gg CO2-eq)
The GHG emissions of the WoM will growth an average of 3.3 per cent by year in the
period 2016-2030, compared to the 6 per cent annual growth of GDP and the 2.1 per
cent annual growth of population. The projection of the WoM has been developed at
category level, considering the different determinant of each emission source.
The GHG emission projections estimated in the WoM are below the unconditional
mitigation target set in the NDC for 2030, without considering the impact of any mitigation
action. The unconditional NDC objective is defined as 80-90% of the 1990 emission
levels, i.e. 20,400 Gg emissions of CO2-eq for year 2020.
28 Three scenarios are considered in the National Development Strategy, an inertial scenario, an industrial scenario and an innovative scenario. The inertial scenario is not relevant for this type of exercise. The innovative scenario assumes a structural change in the economy which is not feasible with the existent policy framework. The industrial scenario assumes that the economy reduces the weight of agriculture, shifting to a more industrial intensive economy. This is in line with national policies and programmes, such as the “Strategy for the development of industry in the Republic of Tajikistan”. For this reason, the industrial scenario has been chosen as a core for this GHG emissions projections.
Projections of GHG emissions to 2030 in Tajikistan
However, WoM emissions are above the conditional mitigation target defined in the NDC,
which is defined as a 65-75% of the 1990 level by 2030, ie. 16,575 Gg emissions of CO2-
eq for the lower range.
The absolute levels for the NDC targets mentioned in the previous paragraph are
calculations which considered that the emissions of year 1990 were 25,500 Gg CO2-eq
. Nevertheless, the GHG emissions of year 1990 have not been re-calculated with the
methodology used in this exercise, so the absolute value for the NDC target can only be
seen as an approximate value. For this reason, it would be recommendable that
Tajikistan either recalculates its 1990 emissions or sets a new NDC target using a more
recent year (for instance, 2010 or 2015).
Considering the effect of the main projects and programmes implemented or adopted in
the country, Tajikistan will not meet its conditional NDC target, as these mitigation actions
have a limited mitigation impact in terms of GHG emissions. The mitigation actions which
showed higher mitigation impact in the country are the following:
Horticulture and Grapevine Development Program. The estimated mitigation impact
for this action in 2030 is 122 Gg CO2-eq.
Second public employment for sustainable agriculture and water resources
management project. The estimated mitigation impact for this action in 2030 is 92
Gg CO2-eq.
Climate Adaptation through Sustainable Forestry in Important River Catchment
Areas in Tajikistan (CAFT). The estimated mitigation impact for this action in 2030
is 90 Gg CO2-eq.
The aggregated impact of all implemented or adopted actions is 507 Gg CO2-eq by 2030.
The impact of these actions is shown in the WeM scenario.
Given the modest mitigation impact of these actions, Tajikistan will require to implement
additional mitigation actions for achieving its conditional NDC target.
Tajikistan is already making efforts to further reduce its GHG emissions in the future and
is planning the future implementation of substantial mitigation initiatives. This is the case
of the Forest Sector Development Strategy, which is not yet adopted, but has an
estimated mitigation impact of 353 Gg CO2-eq by 2030. This is also the case for the
commissioning of the Rogun Hydroelectricity power plant, which is undergoing and is
expected to finalised by 2026. The effect of this strategy and the commissioning of the
Rogun Hydroelectricity power plant are included in the WaM scenario, together with
additional mitigation actions with potential to reduce GHG emission which have been
identified in the framework of this project.
Projections of GHG emissions to 2030 in Tajikistan
Section 11 – Sensitivity of the estimates
This section includes an assessment of the sensitivity of the estimates related to the
possible development pathways which can occur in the country, specifically related to
the different trends of GDP and population growth, which are the key proxies defining
the national macro and socioeconomic framework of the country.
Different scenarios were defined for the analysis of the sensitiveness of results, as shown
in the following table.
Table 169. Sensitivity scenarios
Sensitivity scenario Average annual
GDP Growth
Average annual
population Growth
Sensitivity scenario 1 6-7% 2.1%
Sensitivity Scenario 2 5% 2.1%
Sensitivity Scenario 3 2% 0.5%
The scenario 1 was chosen as the central scenario for projections, as it is in line with
the National Development Strategy. The other two scenarios represent alternative
macro and socio-economic frameworks which could be feasible in view of the current
international framework.
The results of the differences GHG emission pathways differ significatively, especially
in sensitivity scenario 3. The differences obtained in the central scenario of projections
i.e. the WeM scenario, are illustrated in the following figure:
Projections of GHG emissions to 2030 in Tajikistan
Figure 7. WeM emissions in different sensitivity scenarios (Gg CO2-eq)
Figure 8. Results obtained in sensitivity scenario 1 (Gg CO2-eq)
Projections of GHG emissions to 2030 in Tajikistan
Figure 9. Results obtained in sensitivity scenario 2 (Gg CO2-eq)
Figure 10. Results obtained in sensitivity scenario 3 (Gg CO2-eq)
As shown in previous figures, the main conclusion derived from the sensitivity analysis
is that in sensitivity scenario 2 and 3, under lower prospects of economic and population
growth, Tajikistan would achieve both its conditional and non-conditional NDC targets
without additional efforts.
This analysis also indicated that Tajikistan has room to increase its mitigation ambition
under different circumstances, providing a useful insight for the revision of the NDC.
Projections of GHG emissions to 2030 in Tajikistan
Section 12 - Conclusions
This project involved the estimation of impact of all mitigation actions implemented and
planned in Tajikistan and has identified and approximated the GHG emission reduction
impact of additional mitigation options for the country. Different scenarios have been
estimated illustrating the possible mitigation pathways of Tajikistan.
The results of this exercise show that Tajikistan needs to implement additional mitigation
actions for meeting its conditional NDC target, set at 65% of 1990 GHG emission levels
by year 2030. The impact of the actions under implementation since 2015 is thus not
sufficient to achieve the conditional NDC target. As shown in the sensitivity analysis,
under lower prospects of economic and population growth, Tajikistan would achieve both
its conditional and non-conditional NDC targets without additional efforts.
The assessment of progress towards the achievement of the NDC targets made in this
report can only be seen as an approximation, as these targets refer to the GHG
emissions of year 1990, which were calculated following a different methodology (IPCC
Good Practice guidelines were used) than the one used in the latest GHG emission
inventory and also this exercise, so the differences between reference year emissions
(i.e. 1990), emissions of year 2016 and year 2030 are partially explained by the different
methodologies used. For this reason, it would be recommendable to either
recalculating the GHG emissions of year 1990 using consistently 2006 IPCC
Guidelines or updating the NDC target using the results of this exercise, i.e. the
GHG emissions of the period 2004-2030 which are calculated using the same
methodology.
Tajikistan counts with a sectoral policy framework which form the foundation for the
future low carbon development of the country. Nevertheless, the objectives and strategic
lines defined in these policy frameworks are not always translated into mitigation actions
with real GHG emission reductions. This is in fact the reason for the limited GHG
emission reduction impact of the mitigation actions implemented in Tajikistan.
Streamlining climate change in the existent policy instruments and including
specific a roadmap of specific mitigation actions should be a priority to achieve a
low carbon development pathway in Tajikistan.
The GHG emissions and mitigation profile of Tajikistan are strongly driven by the
contribution of the Agriculture, Forestry and Other Land Use sector, with over 40% of
national total emissions attributable to this sector in the historical and projected period in
both the WoM and the WeM scenarios. Given its impact in national total GHG emissions
and its prospects, the AFOLU sector should be prioritized within the mitigation
efforts of the country. In particular, the implementation of the Forest Sector
Development Strategy for 2016-2030 and the continuation of the Comprehensive
livestock development program, Pasture Development Programme after 2020 and
Development Program for Seed Production of the Republic of Tajikistan, are key for the
low carbon development of the country.
Projections of GHG emissions to 2030 in Tajikistan
Apart from the AFOLU sector, the future GHG emission profile of Tajikistan is highly
dependent on the finalization of the Rogun Hydropower plant. This power plant will
represent an addition of 3,600 MW to the electricity generation capacity of the country,
limiting the need of fossil fuel generation for meeting national electricity demand.
The mitigation options with the greatest potential to reduce future GHG emissions
have been identified under this assignment, and include:
Replacement of anthracite consumption by electricity in the residential,
commercial and institutional sectors. This action has the higher estimated
mitigation potential, with 1,929 Gg CO2-eq by 2030.
Incentivise the reduction of the clinker content of the cement produced in the
country. The reduction of clinker production in national cement production plants
has an estimated mitigation potential of 510 Gg CO2-eq by 2030.
Improving solid waste management practices. In line with national efforts to
improve solid waste practices, the waste management system could be extended
to rural areas, reducing the GHG emissions that occur in the open burning of
waste. This mitigation action has an estimated mitigation potential of 328 Gg
CO2-eq by 2030.
Enhancing removals by creating new fruit orchards and vineyards in addition to
those referred in the "Horticulture and Viticulture Development Program in the
Republic of Tajikistan for 2016 – 2020". This mitigation action has an estimated
mitigation potential of 125 Gg CO2-eq by 2030.
Agroforestry and / or silvo-pastoral systems. This mitigation option is associated
to the improving agroforestry and/or silvo-pastoral systems by planting shrubs
and trees in pastures and agricultural land. This mitigation action has an
estimated mitigation potential of 125 Gg CO2-eq by 2030.
The implementation of the forestry Sector Development Strategy for 2016-2030, the
continuation of the key programmes in the AFOLU sector, the finalization of the Rogun
Hydropower plant and the implementation of the key mitigation options identified will
allow Tajikistan to reduce its GHG emissions well below its conditional NDC target,
contributing to achieve the objectives of the Paris Agreements and the United Nations
Convention of Climate Change.