Section 3: Emission Sources and Estimates
 
  This section presents the existing information regarding pollution sources and estimates of emission from these sources. In developing countries like Bangladesh, data on sources, locations and emission is extremely limited. The information presented in this section is compiled from various primary and secondary sources which include studies on air pollutants at Bangladesh University of Engineering and Technology, Bangladesh Atomic Energy Commission, Department of Environment of Bangladesh as well as studies carried out abroad such as Stockholm Environment Institute (SEI). 3.1 Energy Consumption Statistics: From 1972 to 1980, per capita consumption of commercial energy increased from 24 kilogram to 32.8 kilogram oil equivalent.(KOE) It grew to 41.3 KOE in 1985 and 56 KOE in 19889-90.(The Third Five Year Plan, 1985-90, Fourth Five Year Plan 1990-1995). The total energy consumption of Bangladesh in 1989-90 stood at 164 KOE of per capita i.e. commercial energy accounts for 34.6 percent of the total energy used in the country. The rest coming from the non-commercial resources like agriculture waste, fuelwood, cowdung, etc. with regard to mix between different types of primary energy.
 
 
Table 3.1: Percent share of different fuel consumed in Bangladesh
Year
Consumption in Mtoe
Coal
Petroleum
Natural Gas
Electricity
1984-85*
3.02652
2.25
44.13
45.46
8.16
1985-86*
3.4524
2.99
40.58
48.18
8.25
1986-87
3.67668
4.39
40.03
47.43
8.16
1987-88
3.40704
1988-89
4.37472
0.86
41.65
48.27
9.22
1989-90
4.8006
8.14
37.38
46.09
8.40
1990-91
4.282
2.92
36.81
50.49
9.79
1991-92
4.502
2.60
35.54
50.36
11.51
1992-93
4.919
0.89
35.39
53.65
10.06
1993-94
5.31859
0.77
33.94
55.35
9.94
1994-95
6.09197
0
35.97
54.24
9.79

*Source: Statistical Yearbook ’87,BSS

A Compendium of Environmental Statistics, December ‘94, BSS

Figure 3.1 : Trend of percent share of fuel type consumed in Bangladesh

A. Stationary sources:

Table: 3.1(a) Sector wise energy consumption (in Mtoe)
 
Year
Domestic
Industrial
Commercial
Transport
Other energy use
Non-energy use
Total
1996-97 1.09116 1.03572 0.14112 1.2222 0.4788 1.95048 6.019499

Source: Monthly Statistical Bulletin-April 1999, Bangladesh Bureau of Statistics

B. Mobile Sources:

Table: 3.1(b) Energy Consumption-Mobile Sources(per day)
 
Vehicle Category
Number of Vehicles ('000)
Average hours/ Day
Vehicle hours Traveled
Energy Consumptio-n (Liters of fuel)
Fuel Consump-tion (Ton)
Energy Consum-ption (Mtoe)
Motor Cycle (2 & 4 Stroke)
179611
0.7
125728
295091
218
225
Gasoline Cars & light trucks (Average of all engine capacity)
135169
1
135169
1288748
954
984
Heavy Trucks (predominantly diesel)
72128
0.5
36064
1101166
958
955
Mini-Buses (Diesel)
26732
8
213857
8265832
7191
7171
Motorized Three Wheelers (Auto Rickshaw)
92381
3
277144
970057
718
740

Estimates/Projection on the basis of BBS-97, DUTP Report

3.2 Sulphur Dioxide:

3.2.1 Sources:

In Bangladesh, major Sulfur Dioxides emitting sources are tailpipe emissions of vehicles, brick kilns where coal are extensively burnt, paper and pulp industries, oil refineries, sulfuric acid production plants. In our country we don’t have any specific study to identify the sources of Sulfur Dioxides.

3.2.2 Emission Factors of Sulphur Dioxide

Table 3.3.1: Emission Factors of Sulphur Dioxide ((g/km)
Category
SO2
Light duty cars
0.053
Taxis
0.08
Minibus
0.4
Trucks
1.127
3-wheeler 2 stroke
0.19
2-wheeler 2 stroke
0.19
4-stroke motor cycles
0.25

Source: Rahman Shiply, "Training Workshop on Environmental Impact of Air Pollution", Bangladesh Country Report, Institute of Fuel Research & Development (IFRD), Bangladesh Council of Scientific & Industrial Research (BCSIR), Dhaka, Bangladesh, 19-24 July, 1999.

                            Table: 3.2.2 Emission Factors-Sulphur Dioxide
Vehicle Category
SOx
Average ppm
Average gm/l
Average gm/Minute
Average gm/km
Average gm/pass-km or Ton-km
Motor Cycle (2&4 Stroke)
6.16
4.76
0.1862
0.2164
0.1665
Gasoline Cars & light trucks (Average of all engine capacity)
3.69
2.852
0.4532
0.4074
0.1852
Heavy Trucks (predominantly diesel)
7.74
5.9822
3.0443
4.273
0.5341
Mini-Buses (Diesel)
3.49
2.6944
1.7357
1.0778
0.0337
Buses (Diesel)
4.88
3.77
1.92
3.144
0.037
Motorized Three Wheelers (Auto Rickshaw)
4.66
3.5998
0.21
0.2
0.0909

Source : Environmental Impact of Improved Bus Services in Dhaka city, M. Sc Thesis, Dept. of Civil Engineering, BUET, 1998

3.2.3 Current Sulfur Emission Estimate:

In Bangladesh, we don’t have any sectoral data or region-wise data of sulphur emission.

3.2.4 Trends in Emissions:

Bangladesh doesn’t has any sulphur emission trends. So in this regard there should be specific study, which will guide our national and as well as regional action plan.
 
 

3.3 Nitrogen Oxides:

3.3.1 Sources:

The main emitting sources of Nitrogen Oxides are Energy Use, Industrial Process, and Agriculture (Source: ALGAS Report). The breakdown of these sources is given below:

(i) All Energy Use

Energy and Transformation Industries

Industry

Transport

Commercial Institutional

Residential

Traditional Biomass Burned for Energy

(ii) Industrial Process Metal (Iron & Steel) (iii) Agriculture Field Burning of Agricultural Residues
 
Table 3.3.1: NOx Emitted from different source in 1990
 
Source and Sink
N2O (Gg)
NOx (Gg)
Total (net) National Emissions
4.51
203
1. All Energy(Fuel combustion +Fugitive)
4.4
200
Fuel Combustion
1. Energy and Transformation Industries
40
2. Industry
0.44
16
3. Transport
1.5
4. Commercial Institutional 
0.01
0.2
5. Agriculture
6. Residential
1.75
63
7. Others
8. Traditional Biomass Burned for Energy
2.20
79
2. Industrial Process
A. Cement Production
B. Others
1. Ammonia Production
2. Metal (Iron & Steel)
0.01
3. Agriculture
0.11
3.84
Field Burning of Agricultural Residues
0.11
3.84

Source: ALGAS Report,Table1-2,Page 7
 

Table 3.3.2: NOx Emitted from Energy Sector in Gg in 1996

Detailed Technology Based Approach
 
GHGs Source
N2O
NOx
Energy and Transformation Industries
Petroleum Refining
0.8
Electricity Generation
Gas-Steam Turbine
13.4
Gas Turbine
21.6
Gas-Combined Cycle
1.3
Oil
3.4
Total
40.5
Industry
Iron and Steel+
Pulp and Paper
Fertilizer+
Cement+
Brickmaking
0.03*
1.5*
Others
0.01*
0.3*
Total
0.04*
1.8*
Transportation
Cars +2-wheelers+3-wheelers
1.5
Buses
Trucks
Rail
Water
Air
Total
1.5
Small Combustion
Residential
63.0*
Commercial
0.01*
0.2*
Small/Cottage
0.40*
14.3*
Agriculture
Other
0.5
Fugitive Emissions
Oil
Grand Total
2.20
120

Source: Rahman Shiply, "Training Workshop on Environmental Impact of Air Pollution", Bangladesh Country Report, Institute of Fuel Research & Development (IFRD), Bangladesh Council of Scientific & Industrial Research (BCSIR), Dhaka, Bangladesh, 19-24 July, 1999.

+ Emissions from energy use only. Emission from the processes are accounted for in Industrial Processes.

* Emissions from Biomass
 

3.3.1(a) Mobile Sources:

Table 3.3.3: (a): Number of Vehicle for the year 1996

Year
Truck
Jeep
Car
Taxi
Bus
Micro-bus
Motorcycle
Auto-rickshaw
Tractor
Trawler
Others
1996
48734
30597
98854
2863
30428
10724
196012
79293
3834
2385
4059

Table 3.3.3 (b): Number of Train for the year 1995-96

Year
Trains (diesel)
1995-96
272

Source: A Compendium of Environment Statistics December 1994

Table: 3.3.4: Emission Factors of Nitrogen Oxide
 
Vehicle Category
NOx
Average ppm
Average gm/l
Average gm/Minute
Average gm/km
Average gm/pass-km or Ton-km
Motor Cycle (2&4 Stroke)
4.36
2.42
0.0947
0.11
0.0846
Gasoline Cars & light trucks (Average of all engine capacity)
18.72
10.39
1.6515
1.4848
0.6749
Heavy Trucks (predominantly diesel)
57
31.648
16.1053
22.6056
2.8257
Mini-Buses (Diesel)
34
18.88
5.9691
7.55
0.236
Buses (Diesel)
44.24
24.56
12.5
20.469
0.2408
Motorized Three Wheelers (Auto Rickshaw)
4.32
2.3986
0.1399
0.1333
0.0606

Source : Environmental Impact of Improved Bus Services in Dhaka city, M. Sc Thesis, Dept. of Civil Engineering, BUET, 1998
 

Table 3.3.5: Relative Air Pollution Contribution of Different Vehicles
 
Category
Percent share of pollutants (NOx) Annual growth (%)
Truck
59.67
7.77
Bus
18.54
2.48
Mini bus
6.50
6.83
Utility
2.84
10.22
Car / Taxi
6.16
9.39
Auto / Tempo
5.99
31.00
M. Cycle
0.29
8.12

Table 3.3.6: NOx Emission from Biomass Burning in 1990 in Gg
 
Source
N2O
NOx
Industry    
Brick Making
0.03
1.5
Other
0.01
0.3
Total
0.04
1.8
Small Combustion    
Residential
1.75
63.0
Commercial
0.01
0.2
Small/Cottage
0.4
14.3
Total
2.20
79.3

Source: Rahman Shiply, "Training Workshop on Environmental Impact of Air Pollution", Bangladesh Country Report, Institute of Fuel Research & Development (IFRD), Bangladesh Council of Scientific & Industrial Research (BCSIR), Dhaka, Bangladesh, 19-24 July, 1999.
 
 

3.4 Ammonia:

3.4.1 Source:

Ammonia effluent comes from the Urea fertilizer plants. A concentration of 1.2 to 3 ppms of Ammonia is considered toxic even to strong fish. Ammonia effluent if discharged in winter or if the factories go suddenly out of operation, concentration level can reach 30 ppms or above. The Chittagong Urea Fertilizer Factory is the only plant, which controls Ammonia through vaporization. The other fertilizer factories must take necessary steps to control their Ammonia disposal. Concentration of ammonia in the total effluent from a Urea factory can be as high as 100 to 400 ppms.
 
3.4.2 Emission Estimate: In Bangladesh, we don’t have any specific study on emission estimate of Ammonia. 3.4.3 Trends in Emissions: In Bangladesh the trends of emission is not given because we don’t have national annual emission data of Ammonia.
 
3.5 Suspended Particulate Matter:

3.5.1 Sources of SPM:

Natural sources of particulate matter include strong winds blowing over dry soil, and pollen from trees and flowers. Combustion of fuels for power generation in industrial processes and for powering motor vehicle also generates particulate. Particulates containing lead compounds are emitted from the exhausts of vehicles that use leaded gasoline. In Bangladesh another sources of SPM is different construction and development works. 3.5.2 Emission Factors of Particulate Matters

Table 3.5.1: Emission Factors of Particulate Matters (g/km)
 
Category
PM10
Light duty cars
0.181
Taxis
0.181
Minibus
0.1
Trucks
0.45
3-wheeler 2 stroke
0.75
2-wheeler 2 stroke
0.75
4-stroke motor cycles
0.048

Source: Rahman Shiply, "Training Workshop on Environmental Impact of Air Pollution", Bangladesh Country Report, Institute of Fuel Research & Development (IFRD), Bangladesh Council of Scientific & Industrial Research (BCSIR), Dhaka, Bangladesh, 19-24 July, 1999.

3.5.3 Emission Estimates:

In Bangladesh, we don’t have any specific study on emission estimate of SPM. Relative Air Pollution Contribution of Different Vehicles is given in table 3.5.2. Table 3.5.2: Relative Air Pollution Contribution of Different Vehicles
 
Category
Percent share of pollutants PM
Annual growth (%)
Truck
47.45
7.77
Bus
29.38
2.48
Mini bus
19.09
6.83
Utility
0.70
10.22
Car / Taxi
1.22
9.39
Auto / Tempo
1.19
31.00
M. Cycle
0.98
8.12

 

                                        3.5.4 Trends in Emission:

In Bangladesh the trends of emission is not given because we don’t have national annual emission data of SPM.

3.6 Lead:

  Lead is one of the vital pollutants, which is polluting the air of Bangladesh. Mainly lead comes from auto exhaust. Lead exists as Tetra Ethyl Lead [(C2H5)4 Pb] in leaded gasoline. Lead comes in air, when this leaded gasoline is burnt. This Tetra Ethyl Lead is used in gasoline as anti-knocking agent and it facilitates the burning of fuel, beside it increases the octane number of gasoline. Part of this lead comes in air as process loss at the time of Tetra Ethyl Lead processing. Some leads emitted in the air from fuel tank or carburetor emission. Blow gas from old engines also emits lead.

Leads content (as Pb) in motor Gasoline available in Bangladesh:

Motor Gasoline Premium Max 0.84 g/liter

Motor Gasoline Regular Max 0.5 g/ liter
 

Table 3.6.1: Lead content in ambient air of different places of Dhaka city.

Date
Place
Lead Nanogram/m3
Height of data collection
February 3-8, 1996 Lalmatia Housing Estate 
1.26
3 meters above from surface 
February 4-8, 1996 Farm gate Police Box
126.03
1 meters above from surface
March 2-7, 1996 Mirpur Road (near Fire Service )
50.01
1 meters above from surface
April 1-7, 1996 Mohakhali Rail Crossing
44.01
1 meters above from surface
November 19-25, 1996 Farm gate Police Box
175.43
1 meters above from surface
November 19-25, 1996 Bangladesh Beverage Ltd. (Tejgaon)
30.02
3 meters above from surface
February 18-22, 1997 Bangladesh Beverage Ltd. (Tejgaon)
75.73
1 meters above from surface
February 19-22, 1997 Farm gate Police Box
251.84
1 meters above from surface
March 18-20, 1997 Bangladesh Beverage Ltd. (Tejgaon)
61.18
1 meters above from surface
March 20-24, 1997 Farm gate Police Box
122.78
1 meters above from surface

Source DoE

Lead affects circulatory, reproductive, nervous, and kidney systems; suspected of causing hyperactivity and lowered learning ability in children; hazardous even after exposure ends. Lead is ingested through the lungs and the gastrointestinal tract. Young children from one to five years old are particularly sensitive to lead exposure.

Besides posing and immediate health risks through inhalation, vehicular lead emissions also accumulate in soil, enter the food chain, contributing to exposure through ingestion over long period of time. Food sold in the open air along city streets has been found to contain high level of lead.

Currently, the World Health Organization suggests that a level of 20 microgram of metal per deciliter of blood (20 micro gram/dl) is the maximum acceptable concentration. Other studies consider that the detrimental effects of exposure to lead appear at concentration of between 10 and 15 micro gram/ dl. The body tends to accumulate lead over a lifetime and can release it only slowly. Hence even exposure to small concentrations of lead over a long period can produce harm. It is the total body burden of lead that is related to adverse effects.

Bangladesh Atomic Energy Commission recently expresses their alarming study finding that the quantity of lead in air of Dhaka city is 463 nanogram per cubic meter. Available information from similar research work in other parts of the world would have found lead concentrations of 383 nanogram in Mexico city, 360 nanogram in Bombay, 333 nanogram in Sydney, 230 nanogram in Santiago, 70 nanogram in Los Angles whilst in Kyoto the presence of lead in air is at 40 nanogram, the lowest. So the lead pollution of Dhaka city has passed even the Mexico City which is considered to be the most polluted city in the world. According to an estimate made by BAEC, 50 tons of lead is emitted in Dhaka air annually and emission reaches its highest level in the dry season, from November to January.

Department of Environment has also conducted a study for lead level in three different areas of Dhaka city form November '96 to March '97 and found 122.78 to 251.84 nanogram /cu meter at Farmgate area. At the same time it was 61.18 to 75.73 nanogram /cu.m in Tejgaon Industrial Area and 1.26 nanogram /cu.m in Lalmatia Housing Area. Though the accepted level of lead for Bangladesh has not yet been settled but result is very alarming (Ref: Report on Air pollution in Dhaka city by Department of Environment '98).

In a study conducted to determine the level of lead in water, soil and fish of Dhanmondi lake of Dhaka city found average total aqueous lead concentration varies from 151 to 210 m g/l during dry season and 30 to 120 m g /l during wet season. Lead concentration in aqueous media was found to be much higher than that specified by Environmental Quality Standard in Bangladesh (EQS) for fishing and drinking (50 m g /l), industrial (100 m g /l) and irrigation (100 m g /l) purposes. Significant amount of lead was also found in various tissues of fish of Dhanmondi Lake, located at the central part of the Dhaka City.

Recently a descriptive cross sectional study have been conducted by a researcher of Department of Occupational and Environmental Health of NIPSOM on Rickshaw pullers, Baby-taxi drivers, Traffic police, Tempo assistants, Petrol pump operators and motor vehicles serving men of some selected areas of Dhaka city. In this study it was found that, the mean blood lead levels of Rickshaw pullers was 248 m g /dl (range 154-344 m g /dl), of Baby Taxi drivers 287 m g /dl (range 161-372 m g /dl), Traffic polices 272 m g /dl (range 152-32 m g /dl). Tempo assistants 255 m g /dl (mean 177-49.9 m g /dl), petrol pump operators 249 m g /dl (mean 177-314 m g /dl) and Motor vehicles serving men was 264 (mean 207-342 m g /dl). The mean blood lead level on of among all these risk group was found to be higher than the accepted value. The traffic police group was the worst affected. The study also noted that blood lead levels increased with the duration of exposure. It was also observed that there was a relationship between increased blood lead levels with some signs and symptoms of respondents exposed.

Countries around the world are at various stages of tackling the problem of human exposure to traffic related emission. Lead has been totally phased out from gasoline in several countries including Australia, Austria, Brazil, Canada, Japan, Sweden, Thailand and the USA.

Various technological options are available to increase use of octane gasoline without using lead by modifying the petroleum refining process. The use of oxygenates, as well as isomerisation and alkyation are ways of substituting lead. As in Dhaka City two strokes engine vehicles are the major culprits of emission of lead. Government of Bangladesh has already imposed ban on importing two stroke engine. In the road signals posts it is observed that the drivers of the motor vehicles do not stop their vehicles. In the developed countries it is a common practice to stop the vehicle deadly in the signal posts. When the post gives the yellow signals drivers start their engine and getting green signal they run. These should be practiced in our country also. This will reduce environmental pollution and even accident.

People should be motivated to compressed natural gas and lead free fuel. Motor Vehicles Ordinance '83 and Environment Protection Act '93 should properly enforced. Lastly People's awareness should be increased about environment pollution and to move against lead poisoning through motor vehicle emission.
 
 

3.7 Volatile Organic Compounds (VOCs):
  Volatile Organic Compounds (VOCs) are substances that originate in plant matter and evaporate readily at ordinary pressures and temperatures. By far the greatest source of VOCs in B.C. is vegetation, but the greatest source from human activity is from transportation. Hydrocarbons, which form part of this group of chemicals, are solely made up of carbon and hydrogen and are a prime component of such fuels as methane, propane, natural gas, gasoline and kerosene.

VOCs contribute to the formation of ground-level ozone, with the deleterious effects noted above. A number of VOC's are also toxic and are described under Hazardous Air Pollutants.

Automobile exhaust fills the air in Dhaka City with Volatile Organic Compounds beyond tolerable limits, with some of the compounds causing cancer.

Recently, Prof. Abul Hussam of George Mason University, Virginia USA, detected 200 organic compounds and identified 35 of those by analyzing four air samples collected from the Shewrapara of the city. It was the first such advance analysis of air quality ever done in Bangladesh. The air samples were analyzed at the time of installing ultramodern equipment at a privately setup research, development and technology center in the area on August 18 and 19, 1998. The test showed that the exhaust of auto rickshaw contain VOCs, four to more than seven times beyond the allowable limit. The ambient air in Shewrapara contains these compounds close to threshold limit, the test revealed.

Prof. Hussam said the analysis of exhausts of auto-rickshaw showed the presence of toluene, a cancer causing agent, up to 200,000 micrograms per cubic meter as against the threshold limit of 2000 micrograms per cubic meter. The 35 volatile organic compounds identified included cancer causing agents: benzene, toluene, octane, ethylbenzene, 1-isocyanato-3-methoxybenzene, p-xylene, propylbenzene, trimethylbenzene and butylbenzene. The test, however, were conducted at a less vehicular traffic congested area in the metropolis. Prof. Alauddin said that a much higher concentration of air pollutants would be found if tests were carried out at heavily automobile congested areas like Hatkhola, Shapla crossing, Sonargaon crossing and Farm Gate. Prof. Hussam, said that apart form automobile exhausts, natural gas (if cookers are on), chemical processing plants, and biogenic sources contribute to the extremely bad VOC pollution of Dhaka’s air.