WEEK 10 OVERVIEW ON WASTEWATER
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Transcript of WEEK 10 OVERVIEW ON WASTEWATER
CEW 542 WATER AND
WASTEWATER ENGINEERING
INFRASTRUCTURE
TOPIC 4
WASTEWATER
TREATMENT
INFRASTRUCTURE
-overview of ww -
LECTURER: MDM SALINA BINTI ALIAS
ROOM: 5.23 PERDANA BLOCK
LESSON OUTCOME
Able to explain the source of wastewater
and differentiate the types of wastewater
Able to determine the population
equivalent (PE) and what it represent for.
Able to estimate the quantity and quality
of wastewater based on PE
SOURCES
Domestic or sanitary wastewater
- refers to liquid discharge from residences, business buildings and institutions.
Industrial wastewater
- is the liquids discharge from manufacturing plants.
Municipal wastewater
- liquid collected in sanitary sewers and treated in a municipal plant
Infiltration
- flow of groundwater into sanitary sewers
Inflow
- storm water flows into sanitary sewers
DOMESTIC WASTEWATER
Volume – varies depending on sewer uses. - normally 50 – 250 gal per capita per day
Quantity and strength of ww from schools, offices factories and other commercial establishments depend on hours of operation and available eating facilities.
In selection of data for design, the quantity of organic strength of wastewater should be based on actual measurements taken throughout the year to account for variations resulting from seasonal climatic changes and other forces.
The organic matter contributed per person per day in domestic ww is approximately 11 g of suspended solid and 90 g of BOD in communities where a substantial portion of the household kitchen wastes is discharged to the sewer system.
INDUSTRIAL WASTEWATER Ordinarily discharge their wastewater to the city’s sewer system after
pretreatment.
Pretreatment at the industrial site must be considered for wastewater having strength or characteristics significantly different from sanitary wastewater
The majority of manufacturing wastes are more amenable to biological
treatment after dilution with domestic wastewater.
It characteristics vary from industry to industry, treatment process also vary.
- food processing wastes - contains sufficient nitrogen and phosphorus for biological treatment but discharge from chemical and materials industries is deficient in growth of nutrients.
- petroleum, handling animal fats and plant oils – contains lot of grease. - metal finishing, battery manufacturing plants and electroplating
processes – contains toxic chemicals, such as cyanide, lead, oil, chromium and other heavy metal.
Industrial wastewater expressed it quantity of flow and pound of BOD
(quantity and strength) related to the number of persons that would be required to contribute an equivalent quantity of wastewater.
MUNICIPAL WASTEWATER
The flow in sanitary sewers is a composite of domestic and industrial wastewater, infiltration and inflow, and from intercepted flow from combined sewers (Figure 4.1 shown a schematic system of municipal wastewater).
Design criteria
– pipe must be sized to carry peak flow.
- waste strength ( organic matter) greatest during workday.
- at night – amount of organic matter is reduce – slow velocities in pipes permit settling of solids.
- quantity and it characteristics of ww fluctuate with season of the year and between weekdays and holidays.
Infiltration
groundwater entering sewers and building connections through defective joint – broken or cracked pipe/manhole.
depends on
- condition of pipe and pipe joints,
- groundwater level and
- permeability of the soil.
Inflow water discharge into sewer pipes or
service connection from
- foundation drains,
- roof leaders,
- cooling water from air conditioner and
- yard area drain.
Main Composition of Pollutants in
Wastewater
Although wastewater can be polluted by many materials, the most common contaminations found that cause damage to natural watercourses or create human health problems are:
- organic materials - organic loading (BOD, COD)
- nitrogen (N)
- phosphorus (P)
- suspended solids, SS (dissolved/suspended & biodegradable)
- pathogenic organisms (bacteria, viruses etc)
Table 5.1 (from pg 209) gives the sources of municipal
wastewater along with their contaminants.
The composition of wastewater
from a given collection system
may change depend on:
* season,
* dilution,
* fluctuation in quality.
Factors Affect the Flowrate of
Wastewater
1. Amount of water supplied
2. Population
3. Leakage
4. Type of sewer
5. Loss of water
6. Season
7. Socio-economy and religion
PURPOSE OF WASTEWATER TREATMENT
Prevent pollution at the receiving water
Prevention of disease, protecting the health and
well-being of community
To obtain permissible/allowable quality of effluent
(final quality of wastewater after treatment) which
meet with Standard A or Standard B.
GUIDELINES
Malaysian Standard MS 1228:1991. Code of
Practice For Design And Installation of
Sewerage Systems
Malaysian Sewerage Industry Guidelines by
SPAN
i. Volume III ( Sewer Networks and Pumps Stations)
ii. Volume IV ( Sewage Treatment Plants)
iii. Volume V (Septic Tanks )
Says, influent quality is 280mg/L BOD dan 360mg/L SS.
If Standard B is needed, thus the effluent value for BOD dan SS must be <50mg/L dan <100mg/L
Therefore engineer must design suitable wastewater treatment plant
Residential
Area
Wastewater
treatment
plant
BOD5 = 280mg/l
SS = 360 mg/l
Standard A
<20 ?
<50 ?
River
Volumetric Flowrate (Q) vs
Population Equivalents (PE)
Volumetric flow rate is the main parameter to
design sewage treatment plants, sewerage
network or sewer system and pump stations.
Thus volumetric flow rate must be estimated.
Population Equivalents (PE) is one of the
method to estimate flowrate
Type of Establishment Population Equivalent
Residential 5 per house
Commercial : Includes offices, shopping complex,
entertainment / recreational centres, restaurants, cafeteria and theatres
3 per 100m2 gross area
School / Educational Institutions : - Day schools / Institutions
- Fully residential - Partial residential
0.2 per student 1 per student
0.2 per non-residential student 1 per residential student
Hospitals 4 per bed
Hotel with dining and laundry facilities 4 per room
Factories, excluding process water 0.3 per staff
Market (Wet Type) 3 per stall
Market (Dry Type) 1 per stall
Petrol kiosks / Service stations 15 per toilet
Bus Terminal 4 per bus bay
Taxi Terminal 4 per taxi bay
Mosque / Church / Temple 0.2 per person
Stadium 0.2 per person
Swimming Pool or Sports Complex 0.5 per person
Public Toilet 15 per toilet
Airport 0.2 per passenger/day
0.3 per employee
Laundry 10 per machine
Prison 1 per person
Golf Course 20 per hole
The PE may be converted to a flow rate using a simple formula such as set out in Malaysian Standards 1228 (MS1228).
Exercise1 Determine the population equivalent from
the following data.
i. Shopping complex and commercial building each
with 2 blocks of buildings and floor area of 10
000 m2/floor and a height of 3 storeys.
ii. Two primary school with 400 students of each
school
iii. A secondary school with 1200 students
iv. A bus station with 20 public toilets and 30 bus
bays
v. Residential with 2500 houses
vi. Hospital with 300 beds
MS 1228
Flowrate (𝑚3/𝑑𝑎𝑦) =𝑃𝐸 𝑥 1000 𝑥 0.077 𝐵𝑂𝐷 𝑘𝑔/ 𝑑𝑎𝑦 /𝑝𝑒𝑟𝑠𝑜𝑛
𝐵𝑂𝐷 𝑐𝑜𝑛𝑐𝑒𝑛𝑡𝑟𝑎𝑡𝑖𝑜𝑛, 𝑚𝑔/𝐿
PE =𝐵𝑂𝐷 𝑐𝑜𝑛𝑐𝑒𝑛𝑡𝑟𝑎𝑡𝑖𝑜𝑛, 𝑚𝑔/𝐿
0.17𝐵𝑂𝐷/ 𝑑𝑎𝑦 /𝑝𝑒𝑟𝑠𝑜𝑛
PE =𝑂𝑟𝑔𝑎𝑛𝑖𝑐 𝑙𝑜𝑎𝑑 𝑓𝑟𝑜𝑚 𝑝𝑟𝑒𝑚𝑖𝑠𝑒𝑠 , 𝑚𝑔/𝐿
𝑜𝑟𝑔𝑎𝑛𝑖𝑐 𝑙𝑜𝑎𝑑 𝑓𝑟𝑜𝑚 𝑜𝑛𝑒 𝑝𝑒𝑟𝑠𝑜𝑛
Organic loading
Organic loading = Q(m3/capita.day) X BOD(gram/m3)
Organic Loading = 𝐹𝑙𝑜𝑤𝑟𝑎𝑡𝑒, 𝑄 𝑥 𝐵𝑂𝐷
Calculate the organic loading of
wastewater if the BOD5 concentration is
300 mg/L and quantity of water is 200
L/unit
Exercise 2
If the organic loading for a sewage is 60
gram/day and has a flowrate of 182
liter/capita.day, calculate
a) BOD concentration
b) BOD if the flowrate is 100 liter/capita.day
c) Comment?
Solution 2
Organic loading = (300 x 10-3)(200)
= 60 g/unit
a) BOD concentration = (60)/182
= 0.3297 g/L/capita
= 329.7 mg/L/capita
b) BOD concentration = (60)/100
= 600 mg/L
Exercise 3
If an industry has a flow of 1500 liter/day and
BOD 2000 mg/L, convert into PE. Assume
organic loading BOD for one person is 70
gram/day.