Review of the Environmental Impact Assessment Report on Gas Supply Project (Afam FDP) by Shell in...
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ReviewoftheEnvironmentalImpactAssessmentReportonGasSupplyProject(AfamFDP)byShellinNigeria
RESEARCH·JULY2015
DOI:10.13140/RG.2.1.3982.4489
1AUTHOR:
AyotundeOlaKolawole
HebrewUniversityofJerusalem
6PUBLICATIONS0CITATIONS
SEEPROFILE
Availablefrom:AyotundeOlaKolawole
Retrievedon:03September2015
Gas Supply Project (Afam FDP), Nigeria
Environmental Impact Assessment Report
By
Ayotunde Kolawole (888404134)
Felix Ogunmokun (888404092)
Course: Ecological Principles in Spatial Conservation Planning
Course Code: 71947
Lecturer: Dr. Yael Mandelik
Department of Environmental Quality Science,
The Robert H. Smith Faculty of Agriculture, Food and Environment,
The Hebrew University of Jerusalem, Israel.
June, 2015
Table of Content Page
Introduction 1
Objective of the Afam Project 3
Environmental Impact Assessment (EIA) Objectives 3
Justification for the Project 4
Economic Aspects in Conservation Planning (Focal Topic) 4
Study Approach (Data Collection) 5
Ecological and Spatial Effect to Address 5
Possible Biases/Limitation 6
New Field Survey 6
Conservation Planning Tool 7
Conclusions and Recommendations 7
Acknowledgement 7
Bibliography 8
Table 1: Endangered (e) and Vulnerable (v) Wildlife (2007) 8
Table 2: Fisheries and Hydrobiology (2007) 8
Figure 1: Map of Nigeria showing the Delta Regions
Figure 2: Map of the Delta Region showing the project location
Summary
The EIA report was carried out for Afam gas supply project in 2008. The ecology of
the region lies between Rainforest, Freshwater swamp and Mangrove. The main
ecological activities in the area are fishing, tree crop cultivation like Oil palm and arable
crop farming. The objective of this review was to evaluate the quality of the work done
in the EIA report with a focus on economic aspects in conservation planning. The EIA
report was done by Shell Petroleum Development Company (SPDC) in accordance
with the requirement of law of the Federal Government of Nigeria. The objective of the
EIA report was to establish site-specific biophysical, health and social baseline
conditions of the project area, integrate all the views of stakeholders, identify
significant potential positive and negative impacts, proffer mitigation strategies and
develop an environmental management plan. Information from existing data sources
and new data were collected for the report. Biophysical variables collected includes
climatic, vegetation and geomorphological features of the area. Socio-economic
variables and environmental/health influencing factors were also collected. Descriptive
statistics, like frequency distribution, microbial count and scoring were used to analyze
data collected. In their findings, conservation was at a risk, as they showed that some
wildlife and aquatic species were endangered and vulnerable, however the name of the
species were not mentioned in the report. Looking at economic aspects in conservation
planning, the focal article (Protecting Biodiversity when Money Matters: Maximizing
Return on Investment) showed that incorporating cost in a return on investment
framework expands priorities to include areas not traditionally highlighted as priorities
based on conventional irreplaceability and vulnerability approaches. In this line of
thought, we find many faults with the EIA conducted for this project. There was no
conservation plan in the approach and also, the methodology applied in the report was
faulty and biased to suit the stakeholders’ agenda. There was no use of proper terms for
conservation report in the whole write-up. After critically examining the report
presented by SPDC, we feel that much could have been done as money was not a
limiting factor for the study and therefore suggest another EIA report be carried out,
and this time with the objective of incorporating conservation plans in the program for
the endangered and vulnerable species. In order to improve on this reports, components
like hotspots, irreplaceability, complementarity, habitat loss, fragmentation and
identification of umbrella species and how the intended development would affect them
should be thoroughly examined.
1
Introduction
The Shell Petroleum Development Company (SPDC) commonly called "Shell", was
originally known as Royal Dutch Shell plc, an Anglo–Dutch multinational oil and gas
company headquartered in the Netherlands and incorporated in the United Kingdom1.
Shell is vertically integrated and is active in every area of the oil and gas industry,
including exploration and production, refining, distribution and marketing,
petrochemicals, power generation and trading. It has minor renewable energy activities
in the form of biofuels and wind2. Nigeria happens to be a suitable location for Shell
among its tentacles in the world. This is due to high comparative advantage and richness
of Nigeria in both renewable and non-renewable resources. Nigeria ranks as Africa's
largest producer of oil and the sixth largest oil producing country in the world 3. Despite
all the natural resources endowed with Nigeria, poor harnessing, mismanagement and
lack of technical know-how were the major problems limiting the exploration and
utilization of these resources. Shell discovered its first commercial oil field in Nigeria
at Oloibiri, Bayelsa State in 1956 and through a sustained exploration and efforts had
since discovered more oil fields that have firmly established Nigeria as one of the
world's major crude oil producers with significant gas potential. One of the gas station
was Afam in Rivers State of Nigeria.
Afam is a small agricultural community located in the Deltas of Nigeria. The ecology
of the region lies between Rainforest, Freshwater swamp and Mangrove. The main
ecological activities in the area are fishing, tree crop cultivation like Oil palm and arable
crop farming. Due to the need to provide more power supply for the increasing
population of Nigeria and her industrial growth, the Federal Government of Nigeria, in
collaboration with Shell, established Afam Power Station in 1962, with the primary
objective of generating electricity from the combustion of natural gas supplied by the
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SPDC and transmitting the electricity generated via the national grid. The Afam Station
was shut down in 1997, since then, SPDC’s 165 Million standard cubic feet per day
(MMscf/d) gas supply facilities have been redundant. Much of the natural gas extracted
in oil wells in the Delta is immediately burned, or flared, into the air at a rate of
approximately 70 million m³per day. This is equivalent to 41% of African natural gas
consumption, and forms the largest single source of greenhouse gas emissions on the
planet. Therefore, rehabilitation of the power station to restore gas consumption will be
beneficial to SPDC and the entire nation.
Fig. 1: Map of Nigeria showing the Delta Regions
Fig. 2: Map of the Delta Region showing the project location
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Objective of the Afam Project
The Shell Petroleum Development Company of Nigeria Limited proposed to develop
Afam Field since the year of moribund. The main objective of this Afam Field
Development Plan (FDP) project is to provide a robust gas supply of 190 MMscf/d to
Afam Power Station where SPDC plans to build and operate a reliable and economic
combined cycle gas turbine (CCGT) power plant that would generate between 600 MW
to 700 MW of electricity by 2008 in support of her license-to-operate commitment.
Specifically, the project is aimed at increasing the operational capacity in Nigeria by
more than 25 percent.
Environmental Impact Assessment (EIA) Objectives
The objectives of the EIA were to:
i. Establish the site-specific biophysical, health and social baseline conditions of
the project area, i.e. receiving environment;
ii. Integrate the opinions and views of all stakeholders, particularly host
communities into the project in order to ensure that the completed project is
both environmentally and socially sustainable;
iii. Identify the significant potential positive and negative impacts of project
activities on the ecological, social and health aspects of the receiving
environment;
iv. Evaluate the potential impacts and proffer cost-effective mitigation measures
for the negative impacts and, where possible, enhance the positive impacts that
will further assure the environmental and social sustainability of the project;
v. Incorporate the recommendations of the EIA process into detailed project
design and decisions; and
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vi. Develop an Environmental Management Plan (EMP) that covers all phases of
the project.
The detailed scope of the baseline data acquisition were 4:
Biophysical: which includes; climate and meteorology, air quality and noise,
vegetation, land use/cover, wildlife, geology and hydrogeology, soil/sediment quality,
aquatic studies, groundwater quality, hydrobiology and fisheries.
Social: includes, demography, socio-cultural conditions of the communities, socio-
economic condition of the communities, socio-political structure/organization,
political/dispute resolution institutions and mechanisms, archaeological and historical
data, infrastructure and services, social needs of the communities and community
perceptions, evaluations and expectations regarding the project.
Health: includes; socio-economics/vital health statistics, individual/family/community
health determinant, health outcomes, environmental health determinants, institutional
health determinants, knowledge, attitudes and practices.
Justification for the Project
Rehabilitation of the power station to restore gas consumption will be of immense
benefit to Shell Petroleum Development Company and the Nation as a whole. Thus, it
is in SPDC overall interest to see gas sales to power company build up to at least its
historical peak level.
Economic Aspects in Conservation Planning (Focal Topic)
According to Underwood et al5, considering the protection of biodiversity when money
matters, it should be noted that, it is not all conservation planning tools that are
environmentally viable are economically feasible. It is increasingly recognized that
accounting for the economic costs of conservation to maximize the greatest return on
investments may result into substantially larger environmental and biological gains6.
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However, minimizing the area protected and spatial efficiency, does not necessarily
translate into cost or economic efficiency. In a world with dearth of conservation funds7,
efficiency would be better measured in terms of conservation return on financial
investment, such as the number of species protected per dollar expended over a fixed
amount of time. It is also important to identify biodiversity hotspots as priorities for
conservation investment, so as to capture dense concentrations of species. Dynamic
return on investment approach to a global biome was compared with three alternate
priority setting approaches and a random allocation of funding in the work of
Underwood et al5 to consider conservation efficiency in terms of species protected per
dollar invested. In this EIA study of Afam Gas Project, we shall be looking at how best
the funds available could be put into use to maximize conservation per dollar invested.
Study Approach (Data Collection)
The EIA study was based on existing information on this area, site-specific fieldwork,
laboratory analysis of samples, consultations (with host communities and other
stakeholders) and a number of workshops involving consultants and other stakeholders
including regulatory agencies.
Ecological and Spatial Effect of the Project
Specifically, the ecological and spatial effect of the project include: loss of farmland
and associated income, changes in traditional occupation, potential increase in road
traffic volume, increase in noise levels, loss of flora and fauna, potential increase in
erosion, changes in local population, increase in social vices, soil degradation, loss of
biodiversity, blockage of natural drainages, changes in aesthetic quality of the
environment, potential for falls into exposed trenches (by animals, unsuspecting
passers-by), threat to health of workers (snake bites, insect stings, injuries etc.), increase
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in dust generation and potential for community unrest (from employment, pollution and
resistance to dismantling of equipment).
Possible Biases/Limitation
The EIA document has been prepared by drawing conclusions from site visits, primary
data and secondary information, therefore, intrinsic randomness of human behavior and
unreliable data sources may forfeit the overall objective of the EIA study. From their
findings (Table 1 & 2) there was a big gap between what their wildlife team found and
what the local people reported to exist in the environment. They saw less than what was
there, and this indicates that their exploration was not thorough. Further still, in their
findings (Table 1 & 2), some wildlife and aquatic organisms were reported to be
endangered and vulnerable, but these organisms were not named. This is however an
incomplete information, and cannot serve as a basis for conservation planning. This
could also be due to lack of expertise among wildlife team to identify these organisms.
Yet again, all through their report, there was no plan for conserving the endangered and
vulnerable species they found in the area. Also, the mitigation measures and other
recommendations they provided in their report are prepared at the level of conceptual
design and implementation framework and may not address the significant impact of
the final work on the environment.
New Field Survey
Although, some steps taken in the EIA report are inevitable, but to improve upon the
report we are going to do the following;
Develop a baseline survey for the project boundary,
Identify all potential environmental impacts due to the project,
Propose for a conservation plan that efficiently utilize the available funds,
Estimating externalities both in the short-run and long-run,
Propose mitigation measures for avoidance of significant negative impact(s),
Evaluate the relevant legislative requirements,
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Evaluate project alternative scenarios,
Formulate an environmental monitoring plan.
Conservation Planning Tool
The following will be considered for the new EIA reports we suggest; components like
the hotspots, irreplaceability, complementarity, habitat loss, fragmentation and
identification of umbrella species in the study area and the impact the development will
have on them.
Conclusions and Recommendations
The project should be committed to implement an environmental conservation, social
management and monitoring plan, which will ensure that the construction and the
operation of the Afam Gas Power Plant involves full implementation of all proposed
mitigation measures and complies with high environmental standards, the requirements
of the environmental legislation and guidance notes as applicable in Nigeria and
international guidelines. Monitoring data should be analyzed and reviewed at regular
intervals and compare with the relevant standards so that any necessary corrective
actions can be taken into account.
In conclusion, this project should be executed, but modified to make it realistic,
accountable, compensatory and conservative, rather than tailoring its findings towards
the interest of stakeholders at the expense of its ecological and environmental
consequences. Conserving vulnerable and endangered species should be of major
priority, while the problem of likely pollution should also be ironed out, especially as
it affects the aquatic animals and subsequently fishes. Finally, incorporating some
economic estimators to account for both negative and positive externalities
accompanied by the project in the short-run and long-run respectively is germane.
Acknowledgment
Our appreciation goes to Dr. Yael Mandelik for giving detailed knowledge about this important course.
8
Bibliography
(1) http://www.shell.com/global/aboutshell/at-a-glance.html
(2) Webb, Tim (17 March 2009). "Shell dumps wind, solar and hydro power in favour
of biofuels". London: The Guardian. Retrieved 17 March 2013.
(3) Nigerian National Petroleum Company (2015).
www.nnpcgroup.com/nnpcbusiness/upstreamventures/oilproduction.aspx
(4) The Shell Petroleum Development Company of Nigeria (2007). Environmental
impact assessment for Afam FDP (gas supply) project in Nigeria.
(5) Underwood EC, Shaw MR, Wilson KA, Kareiva P, Klausmeyer KR, et al (2008)
Protecting biodiversity when money matters: Maximizing return on investment. PLoS
ONE 3(1): e1515. doi:10.1371/journal.pone.0001515.
(6) Naidoo R, Balmford A, Ferraro PJ, Polasky S, Ricketts TH, et al. (2006) Integrating
economic costs into conservation planning. Trends in Ecology and Evolution 21: 681–
686.
(7) James A, Gaston KJ, Balmford A (1999) Balancing the Earth’s accounts. Nature
401: 323–324.
Table 1: Endangered (e) and Vulnerable (v) Wildlife (SPDC, 2007)
Table 2: Fisheries and Hydrobiology (SPDC, 2007)