teri bangalore air quality study

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February 2010 Air quality assessment, emission inventory and source apportionment study for Bangalore city Final report Supported by Indian Oil Corporation Ltd., R&D Centre, Faridabad Hindustan Petroleum Corporation Ltd. Bharat Petroleum Corporation Ltd. Reliance Industries Ltd. & Central Pollution Control Board Project Report No.2004EE28 www.teriin.org The Energy and Resources Institute

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study by TERI on air quality of bangalore

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  • February 2010

    Air quality assessment, emission inventory and source apportionment study for Bangalore city

    Final report

    Supported by Indian Oil Corporation Ltd., R&D Centre, Faridabad

    Hindustan Petroleum Corporation Ltd. Bharat Petroleum Corporation Ltd.

    Reliance Industries Ltd. &

    Central Pollution Control Board

    Project Report No.2004EE28

    w w w . t e r i i n . o r g The Energy and Resources Institute

  • T E R I Report No. 2004EE28

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  • T E R I Report No. 2004EE28

    Project team

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  • T E R I Report No. 2004EE28

    Acknowledgements

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    Annexure - I

  • List of tables

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  • Executive summary

    Background

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  • ii Executive summary

    T E R I Report No. 2004 EE 28

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    Objectives .98

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  • iii Executive summary

    T E R I Report No. 2004 EE 28

    Air quality status

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  • iv Executive summary

    T E R I Report No. 2004 EE 28

    117

    257

    321

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    109

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    9295135

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    95

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    ( g/

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    SPM RSPM PM10 PM2.5

    13 9 13 11 9 10 10

    3177 66

    44 57 5141 33 28 2542 34 40

    12102077 2027 2017 2083

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    Figure 2 Study domain showing the location of the air quality monitoring locations

    Figure 3 Average concentration of SPM, RSPM, PM10, PM2.5 during three seasons

    Figure 4 Average concentration of gaseous pollutants during three seasons

    1

    4

    67

    1. CSB (Kerbside)2. IGICH (Residential)3. Domlur (Residential)4. Victoria (Kerbside)5. Kammanahalli (Residential)6. Peenya (Industrial)7. Kanamangala (Background)

    1

    4

    67

    1. CSB (Kerbside)2. IGICH (Residential)3. Domlur (Residential)4. Victoria (Kerbside)5. Kammanahalli (Residential)6. Peenya (Industrial)7. Kanamangala (Background)

    Vegetation Residential Roads Monitoring station 1. CSB (Kerbside) 2. IGICH (Residential) 3. Domlur (Residential) 4. Victoria (Kerbside) 5. Kammanahalli (Residential) 6. Peenya (Industrial) 7. Kanamangala (Background)

  • v Executive summary

    T E R I Report No. 2004 EE 28

    Emission inventory $%5665&

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  • vi Executive summary

    T E R I Report No. 2004 EE 28

    PM10

    Transport42%

    Road Dust20%

    Domestic 3%

    DG Set7%

    Industry14%

    Hotel0%

    Construction14%

    NOx

    Transport68%

    Domestic 1%

    DG Set23%

    Hotel0%Industry

    8%

    Figure 5 Percentage share of different sources in total PM10 emission loads

    Figure 6 Percentage share of different sources in total NOX emission loads

    Receptor modelling and source apportionment '

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  • vii Executive summary

    T E R I Report No. 2004 EE 28

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    Table 2 Indicative sources based on Factor Analysis for the different sites

    S. No. Site Site description Indicative sources

    1 Silk Board Traffic location Motor vehicle exhaust, secondary particulate matter, construction activities, natural

    soil, road dust

    2 Victoria road Traffic location Motor vehicle exhaust, natural soil, road dust, biomass burning, secondary particle

    formation

    3 Peenya Industrial Road dust, residual oil burning, crustal soil dust, industrial sources, metal industries,

    motor vehicle exhaust, construction activities

    4 Domlur Residential Soil and road dust, secondary particle formation, motor vehicle exhaust, storm water

    drain, biomass burning

    5 Kammanahalli Residential Road dust, coal combustion, vegetative burning, secondary particle formation,

    resuspended soil, motor vehicle exhaust

    6 IGICH Hospital

    /Residential

    Road dust, natural soil, secondary particle formation, construction activities, motor

    vehicle exhaust, incinerator combustion

    7 Kanamangala/

    Background

    Background Natural soil, crustal source, road dust, vehicular sources, biomass burning,

    secondary particle formation

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  • viii Executive summary

    T E R I Report No. 2004 EE 28

    PM10

    Transport 19.0%

    DG sets13.0%

    Paved road & Soil dust

    50.6%

    Secondary8.7%

    Industrial 4.5%

    Domestic4.2%

    PM2.5

    Transport 49.9%

    Paved road & Soil dust

    3.5%Domestic

    5.8%

    DG sets24.7%

    Industrial 3.5%

    Secondary12.7%

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    Figure 7 Comparison of PM10 and PM2.5 source contribution in Bangalore city (average of 3 seasons)

    Dispersion modelling : existing scenario =!*=8%=!=;&

  • ix Executive summary

    T E R I Report No. 2004 EE 28

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    Figure 8 Contours for 24-hourly average PM10 concentration ( g/m3) for first (winter)

    season during 2007

    0 2000 4000 6000 8000 10000 12000 14000 16000 18000 20000 22000 240000

    2000

    4000

    6000

    8000

    10000

    12000

    14000

    16000

    18000

    20000

    22000

    24000

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    0 g/m325 g/m350 g/m375 g/m3100 g/m3125 g/m3150 g/m3175 g/m3200 g/m3225 g/m3250 g/m3275 g/m3300 g/m3325 g/m3350 g/m3375 g/m3400 g/m3425 g/m3450 g/m3

  • x Executive summary

    T E R I Report No. 2004 EE 28

    Figure 9 Contours for 24-hourly averaged NOX concentration ( g/m3) for first (winter)

    season during 2007

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    0 2000 4000 6000 8000 10000 12000 14000 16000 18000 20000 22000 240000

    2000

    4000

    6000

    8000

    10000

    12000

    14000

    16000

    18000

    20000

    22000

    24000

    26000

    0 g/m320 g/m340 g/m360 g/m380 g/m3100 g/m3120 g/m3140 g/m3160 g/m3180 g/m3200 g/m3220 g/m3240 g/m3260 g/m3280 g/m3300 g/m3

  • xi Executive summary

    T E R I Report No. 2004 EE 28

    22.4

    10.9

    1.8 3.67.8

    0.17.7

    54.4

    26.4

    17.2

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    2007 2012 2017

    Table 3 Growth rates of different sectors

    S.No Sector Description of growth

    1 Domestic Population growth rate of 3.1% as listed in Master

    Plan - 2015

    2 Transport Vehicle-wise growth rates were calculated using the

    last five years data (2002-2007). BS-IV norms are

    taken into account from 2010.

    3 Industrial 5.85% as depicted in Industrial development plan

    4 DG sets Based on population growth rates for domestic sets

    and based on energy consumption for commercial

    DG sets.

    5 Construction Based on population growth rates

    6 Road dust Based on increase in VKT ( from transport sector)

    7 Eating joints Based on population growth rates

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  • xii Executive summary

    T E R I Report No. 2004 EE 28

    146.4

    0.0 2.751.0

    17.2 0.2 0.0

    217.4201.4

    0.0 3.2

    93.8

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    2007 2012 2017

    Figure 11 Sectoral and total NOX emission load under BAU scenario during 2007-2017

    Dispersion modelling - BAU Scenarios 2012 and 2017 $K

    $

    ):55

  • xiii Executive summary

    T E R I Report No. 2004 EE 28

    56:3$K):;:

  • xiv Executive summary

    T E R I Report No. 2004 EE 28

    5663*

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    Table 4 Reduction in PM10 emission loads due to various technological interventions in transport sector in Bangalore

    S.No Strategy 2007 2012 2017 % reduction

    2012

    % reduction

    2017

    Remarks

    1 BAU 22.4 26.4 30.4 CAGR 2002-2007, BS-IV from 2010, No bio-

    diesel ,Ethanol, or ban

    2 BS-V 22.4 26.4 30.1 0% -1% BAU + BS -V has been applied from 2015

    3 BS-VI 22.4 26.4 30.0 0% -1% BAU + BS -VI has been applied from 2015

    4 ELECTRIC 22.4 25.8 29.1 -2% -4% BAU + Introduction of electric vehicle as per

    chart provided by CPCB

    5 Hybrid 22.4 26.4 30.4 0% 0% BAU + 1% hybrid cars in 2012 & 2% in 2017

    6 CNG 22.4 25.4 26.6 -4% -12% BAU+ commercial vehicles (Bus/Car/3w)-

    25% conversion in 2012 and 100% in 2017

    7 Ethanol 22.4 26.4 30.4 0% 0% BAU + 10% Ethanol introduced in 2012-2017

    8 Bio-diesel 22.4 26.3 30.2 -0.4% -1% BAU + 5% Biodiesel introduced in 2012 and

    10% in 2017

    9 H2/CNG 22.4 26.4 30.4 0% 0% 10% Vehicles in 2017

    10 Diesel

    oxidation

    catalyst (DOC)

    22.4 26.1 29.9 -1.0% -1.7% 50% conversion of BS-II buses in 2012, and

    100% in 2017

    11 Diesel

    particulate

    filter (DPF)

    22.4 26.2 30.1 -0.6% -1.2% 50% conversion of BS-III buses in 2012, and

    100% in 2017

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  • xv Executive summary

    T E R I Report No. 2004 EE 28

    0% 0%

    -2%

    0%

    -4%

    0%

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    0%

    -1.0%-0.6%

    -1%-1%

    -4%

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    -12%

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    -14%

    -12%

    -10%

    -8%

    -6%

    -4%

    -2%

    0%

    BS-V BS-VI ELECTRIC Hybrid CNG Ethanol Bio-diesel H2/CNG DOC DPF

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    2012 2017

    Figure 15 Percentage reduction achieved in PM10 emissions by implementing various strategies in the transport sector

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  • xvi Executive summary

    T E R I Report No. 2004 EE 28

    0% 0%

    -2.5%

    -0.02%

    -1%

    -0.1%

    0.1% 0.0% 0.0% 0.0%

    -1.9%

    -3.7%

    -5% -4%-4.9%

    -0.1%

    0.2%0.0% 0.0%

    -0.04%

    -6%

    -5%

    -4%

    -3%

    -2%

    -1%

    0%

    1%

    BS-

    VBS

    -

    VI

    ELEC

    TRIC

    Hybri

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    GEth

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    Bio-die

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    GDO

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    % re

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    2012 2017

    S.No Strategy 2007 2012 2017 % reduction

    2012

    % reduction

    2017

    Description

    7 Ethanol 146.4 201.1 252.6 -0.1% -0.1% BAU + 10% Ethanol introduced in

    2012-2017

    8 Bio-diesel 146.4 201.6 253.4 0.1% 0.2% BAU + 5% Biodiesel introduced in

    2012 and 10% in 2017

    9 H2/CNG 146.4 201.4 240.6 0.0% -4.9% 10% Vehicles in 2017

    10 Diesel

    oxidization

    catalyst

    (DOC)

    146.4 201.4 252.9 0.0% 0.0% 50% conversion of BS-II buses in

    2012, and 100% in 2017

    11 Diesel

    particulate

    filter (DPF)

    146.4 201.4 252.9 0.0% 0.0% 50% conversion of BS-III buses in

    2012, and 100% in 2017

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    Figure 16 Percentage reduction achieved in NOX emissions by implementing various strategies in the transport sector

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  • xviiExecutive summary

    T E R I Report No. 2004 EE 28

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  • Sectors Alternate-I Alternate-II Alternate-III Alternate-IV Description Scenario with certain

    strategies to reduce the air pollution loads across various sectors.

    Stringent scenario with many more strategies to reduce the air pollution load across various sectors as compared to Alternate- I scenario.

    Scenario that contains additional set of measures that are not a part of the common control options as per the chart suggested by CPCB (for example, introduction of fuel efficiency standards, installation of control devices (DOC/DPF) on all diesel vehicles and DG sets).

    Scenario with measures that are more oriented towards meeting the air quality standards in future

    Transport Introduction of BS-V in 2015 Ban on 10 year old

    commercial vehicles in 2012 and 2017

    Introduction of Metro in 2011 Enhancement of public

    transport system based on diesel (shift of PKT from private vehicles to public transport i.e. 10% in 2012 and 20% in 2017)

    Improvement in inspection and maintenance

    Introduction of DOC in BS-II buses and DPF in BS-III buses

    Introduction of BS-VI in 2015 Ban on 10-yr old commercial vehicles and

    15-yr old private vehicles both in 2012 and 2017

    Introduction of Metro in 2011 Enhancement of public transport system

    based on CNG (shift of PKT from private vehicles to public transport i.e. 10 % in 2012 and 20% in 2017)

    Introduction of electric vehicles (12% 2w, 5-10% 3w and taxis, 510% buses in 2012 and 2017, respectively)

    Improvement in inspection and maintenance

    Conversion of public transport (commercial 3 & 4 w) to CNG (25% in 2012 and 100 % in 2017)

    Introduction of BS-VI in 2015 Ban on 15 yr old commercial vehicles in 2012 and 10 yr old

    commercial vehicles in 2017 Introduction of Metro in 2011 Enhancement of public transport system based on diesel (shift

    of PKT from private vehicles to public transport i.e. 10 % in 2012 and 20% in 2017)

    Introduction of electric vehicles (1 2% 2w, 5 - 10% 3w and taxis, 5 10% buses in 2012 and 2017, respectively)

    Improvement in inspection and maintenance Application of DOC/DPF after introduction of BS- IV fuel in 2010

    to: Old Buses and Trucks (pre BS-IV):reduction in PM10 - DOC : 22.5%, DPF : 70% Old Diesel Cars pre BS-IV (about half of PM reduction is

    assumed as compared to that for buses/trucks) : reduction in PM10-DOC: 10%, DPF : 35%

    Introduction of fuel efficiency standards (considering reduction of fuel consumption)

    Light passenger vehicles : 10% between (2012-15) and 15% between (2015-17), Light duty Passenger cars : 20% between (2012-15) and 30% between (2015-17), Heavy duty vehicles : 20% between (2012-15) and 30% between (2015-17)

    Introduction of BS-V in 2015 Ban on 10 yr old commercial vehicles in 2012 and 2017 Introduction of Metro in 2011 Enhancement of public transport system based on CNG

    (shift of PKT from private vehicles to public transport i.e. 10 % in 2012 and 20% in 2017)

    Introduction of electric vehicles (1 2% 2w, 5 - 10% 3w and taxis, 5 10% buses in 2012 and 2017, respectively)

    Improvement in inspection and maintenance Conversion of public transport (commercial 3 & 4 w) to

    CNG (25% in 2012 and 100 % in 2017) By-passing of trucks on the proposed peripheral ring

    road around Bangalore (which is broadly outside the study domain- assumed only 10% truck traffic within the city)

    Industries Ban on any new air polluting industries in city limits

    Ban on any new air polluting industries in city limits

    Shift from solid fuel to liquid fuel (LSHS) in 2012 & NG in 2017 in existing industries

    Ban on any new air polluting industries in city limits Shift from solid fuel to liquid fuel (LSHS) in existing industries in

    both 2012 and 2017

    Ban on any new air polluting industries in city limits Shift from solid fuel to liquid fuel (LSHS) in 2012 and to

    NG in 2017 in existing industries

    DG sets Inspection and maintenance Inspection and maintenance DOC and DPF applied to commercial DG sets (>12 kVA) in

    2010. Reduction in PM10 :DOC : 22.5%, DPF : 70% (reductions taken same as those in the case of buses)

    No power cuts i.e. no usage of DG sets in the city

    Road dust re-suspension

    Wall to wall paving

    Wall to wall paving Wall to wall paving Reduction of road dust re-suspension due to by-passing

    of trucks Construction Better construction practices Better construction practices Better construction practices

  • xix Executive summary

    T E R I Report No. 2004 EE 28

    217

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    Figure 17 Estimated emissions loads for PM10 and NOX under the BAU and four alternate scenarios

  • PM10 emission load

    F8

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  • xxi Executive summary

    T E R I Report No. 2004 EE 28

    56:33IL5

  • xxiiExecutive summary

    T E R I Report No. 2004 EE 28

    Figure 19 Percent reduction of predicted 24-hourly highest PM10 concentration ( g/m3) for Alternate I, Alternate II, Alternate III and Alternate IV scenarios for the years 2012 and 2017

    Concentration contours for alternate scenarios # :65

  • xxiiiExecutive summary

    T E R I Report No. 2004 EE 28

    Figure 20 Contours for 24-hourly average PM10 concentration ( g/m3) for Alternate I scenario in 2017

    Figure 21 Contours for 24-hourly average PM10 concentration ( g/m3) for Alternate - II scenario in 2017

    0 2000 4000 6000 8000 10000 12000 14000 16000 18000 20000 22000 240000

    2000

    4000

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    12000

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  • xxivExecutive summary

    T E R I Report No. 2004 EE 28

    Figure 22 Contours for 24-hourly average PM10 concentration ( g/m3) for Alternate - III scenario in 2017

    Figure 23 Contours for 24-hourly average PM10 concentration ( g/m3) for Alternate - IV scenario in 2017

    0 2000 4000 6000 8000 10000 12000 14000 16000 18000 20000 22000 240000

    2000

    4000

    6000

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    12000

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    0 2000 4000 6000 8000 10000 12000 14000 16000 18000 20000 22000 240000

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  • xxvExecutive summary

    T E R I Report No. 2004 EE 28

    Prioritized list of management/control options $

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  • xxviExecutive summary

    T E R I Report No. 2004 EE 28

    0

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  • xxviiExecutive summary

    T E R I Report No. 2004 EE 28

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    Figure 25 Percent PM10 emission load reduction due to various individual interventions as compared to the

    total pollution load under BAU scenario in the years 2012 & 2017

    0.0

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    Ethanol

    Metro

    BAN (Com. vehicles)

    BAN (Pvt. vehicles)

    CNG (Com. vehicles)

    Electric Vehicles

    I&M (Vehicles)

    Synchronisation_signals

    Enhance PTS (CNG)

    Enhance PTS (Diesel)

    DOC-DPF (BS-II,III Buses)

    DOC-DPF (All diesel vehicles)

    Bye Passing Trucks

    Fuel Efficiency stds.

    No power cuts

    I&M (DG sets)

    DOC/DPF (DG sets)

    WTW (Road dust)

    Better Construction

    Ban Industries

    Fuel Shift-Ind.(CNG)

    Fuel Shift-Ind.(LSHS)

    % reduction wrt total PM10 BAU load

    w rt BAU 2012 w rt BAU 2017

  • xxviiiExecutive summary

    T E R I Report No. 2004 EE 28

    Table 6 Prioritised list of key interventions in terms of reduction in total PM10 emission loads in 2017

    S.No Strategy % reduction in total

    PM10 emission loads

    in 2017

    1 By-passing of trucks through the proposed peripheral ring road around

    Bangalore

    13.8%

    2 Installation of DOC and DPF devices in all pre-2010 diesel vehicles 13.0%

    3 No power cuts leading to zero usage of DG sets 12.8%

    4 Ban on 10 year old commercial vehicles in 2012 and 2017 12.5%

    5 Ban on any new industries in city limits(6.2%) and fuel shift towards cleaner

    fuel NG (5.3%) in existing industries

    11.5 %

    6 Installation of DOC and DPF devices in DG sets 8.3%

    7 Wall to wall paving for reduction of road dust 6.2%

    8 Better construction practices 5.5%

    9 Conversion of public transport (commercial 3 & 4 w) to CNG (25% in 2012

    and 100 % in 2017)

    4.0%

    10 Improvement in inspection and maintenance for vehicles 2.5%

    11 Inspection and maintenance for DG sets 1.9%

    12 Enhancement of public transport system based on CNG (shift of PKT from

    private vehicles to public transport i.e. 10% in 2012 and 20% in 2017)

    1.7%

    13 Enhancement of public transport system based on diesel (shift of PKT from

    private vehicles to public transport i.e. 10% in 2012 and 20% in 2017)

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  • Action plan S.No Sector Strategy Impact* Responsible Agency / agencies Time frame Remarks 1 Transport Strengthening of Public

    transport system - Metro

    implementation on schedule

    - Enhance share of public mass transport system on diesel

    - Conversion/ enhancement of public transport to CNG

    High

    Govt of India, State Government, BMRCL (Bangalore Metro rail Corporation Ltd.), Transport Department- Bangalore, BMTC (Bangalore Metropolitan Transport Corporation), GAIL

    Medium term Leveraging the JNNURM funding mechanism for public transportation improvement Public-private partnership models to be explored The metro network needs to be progressively expanded. Bangalore currently does not have a CNG network. There are plans to set up such a network in future. ULSD would also be available by April 2010 in Bangalore. Retro-fitted 2-stroke three wheelers on LPG in Bangalore have higher PM emissions compared to OE 2-stroke/ 4-stroke LPG/Petrol. Thus retro-fitment of 2-stroke 3-wheelers is not an effective control option.

    Ban on old commercial vehicles (10 year) in the city

    High Transport department - Bangalore Short-term Fiscal incentives/ subsidies for new vehicle buyers A plan should be devised for gradual phase out with due advance notice. Careful evaluation of socio-economic impact of banning required. In the long run, a ban/ higher tax on private vehicles (> 15 years) could be looked into.

    By-passing of trucks through the proposed peripheral ring road around Bangalore

    High Traffic Police, Transport department Short-term Has high potential in reducing the pollutant load in the city

    Progressive improvement of vehicular emissions norms (BS-V, BS-VI)

    Low MoRTH, MoPNG, Ministry of Heavy Industry and Public Enterprises, MoEF, Oil companies, Automobile manufacturers

    Medium to Long term

    Auto-fuel road map should be developed well in advance to plan the progressive improvement of emissions norms and corresponding fuel quality norms. Though the impact is low, its potential is high in the long term when gradually fleet renewal takes place.

    Installation of pollution control devices (DOC/DPF) in all pre-2010 diesel vehicles

    High Transport department Medium Technical feasibility and implementation plan of this strategy needs to be carefully evaluated, though it has potential for emission load reduction. Retro-fitment of DOC in BS-II buses and DPF in BS-III buses is technically feasible.

    Introduction of fuel efficiency standards

    Low BEE, Ministry of Power, Ministry of Heavy Industry and Public Enterprises, MoRTH, Automobile manufacturers

    Medium Impact is low since it is applied only to new vehicles registered after 2012. However, its potential is high in the long term when gradually fleet renewal takes place.

    Introduction of hybrid vehicles/ electric vehicles

    Low - medium

    Ministry of Finance, Ministry of Heavy Industry and Public Enterprises, Automobile manufacturers, State

    Short-Medium Appropriate fiscal incentives need to provided; Electric vehicles would be especially effective in high pollution zones. Impact determined by the extent of switchover to hybrid/ electric vehicles.

  • xxxExecutive summary

    T E R I Report No. 2004 EE 28

    government, Effective Inspection and

    maintenance regime for vehicles

    Medium Transport Department, Traffic police Short to Medium

    Initial focus could be on commercial vehicles; Capacity development in terms of infrastructure for fully computerized testing/certification and training of personnel. Linkage of all PUC centres for better data capture.

    Alternative fuels such as ethanol, bio-diesel

    Low MNRE, MoRD, MoPNG, MoA, Oil companies,

    ongoing There are operational issues regarding availability and pricing that need to be sorted.

    Reduction in private vehicle usage/ ownership

    Min. of Finance, State Government NGOs General public

    Medium term A pre-requisite for curbing the growth of private vehicles is the provision of an effective mass based transport system. Strategies such as costlier parking, higher excise duties/sales tax on private vehicles, car pooling would be helpful.

    Improve traffic flow Medium Traffic police, Bangalore Development Authority (BDA), Bruhat Bengaluru Mahanagara Palike (BBMP),

    Short Synchronization of signals, one way roads, flyovers, widening of roads, removal of encroachments, staggering of office timings to reduce peak flow and congestion. Application of IT tools for traffic management (Intelligent transport system)

    Fuel adulteration n.a Govt. of India, Oil companies, Food and civil supplies department- Bangalore

    Short Re-assess subsidy on kerosene, strict vigilance and surveillance actions, better infrastructure in terms of testing laboratories

    2 Road dust -Construction of better quality roads -Regular maintenance and cleaning/sweeping of roads

    -Reduction in vehicular fleet and trips

    n.a Bangalore Development Authority (BDA), Bruhat Bengaluru Mahanagara Palike (BBMP), NHAI

    Short - Mediumterm

    Effective enforcement of road quality norms is required. Landscaping/ greening of areas adjacent to roads

    Wall to wall paving for reduction of road dust

    High Bangalore Development Authority (BDA), Bruhat Bengaluru Mahanagara Palike (BBMP)

    Short term Interlocking tiles may be used so that water percolation takes place.

    3 Industries Fuel shift towards cleaner fuels

    High KSPCB, Directorate of Industries and Commerce, Industry associations, GAIL, Oil companies

    Short-Medium term

    Shift from solid fuels to liquid fuels (LSHS) and subsequently to gaseous fuels (CNG)

    Ban on any new air polluting industry in city limits

    High KSPCB, Department of Forest, Ecology and Environment, Department of Industries and Commerce, Karnataka Industrial Area Development Board

    Short term Industrial estates/zones may be developed well outside the city

    Strengthening of enforcement mechanism for pollution control

    n.a KSPCB, Industry associations, Short term This would ensure greater compliance with standards. In addition, cleaner technology options need to be promoted and appropriate incentives to be defined. Voluntary measures such as ISO certifications to be encouraged.

    4 Power/ DG sets

    No power cuts leading to zero usage of DG sets

    High Bangalore Electricity Supply Company, Karnataka Power Corporation Ltd.

    Medium term Adequate tie-ups need to be ensured

  • xxxiExecutive summary

    T E R I Report No. 2004 EE 28

    Installation of pollution control devices (DOC/DPF) in DG sets

    High KSPCB, DG set manufacturers Medium Technical feasibility and implementation plan of this strategy needs to be carefully evaluated, though it has potential for emission load reduction

    Effective Inspection and maintenance regime for large DG sets

    Medium KSPCB, Chief Electrical inspectorate Short to Medium

    5 Construction Better enforcement of construction guidelines (which should reflect Green Building concepts)

    High KSPCB, SEAC (State expert appraisal committee), Bruhat Bengaluru Mahanagara Palike (BBMP),

    Short term

    6 Other sectors

    Integrated land-use development of Bangalore taking environmental factors into consideration

    n.a. Bangalore Metropolitan Region Development Authority, Bangalore Development Authority, Bruhat Bengaluru Mahanagara Palike (BBMP)

    Medium term Holistic development of the entire region including peripheral areas.

    Open burning/ Waste burning to be discouraged

    n.a Bruhat Bengaluru Mahanagara Palike (BBMP), KSPCB

    Short term Organic matter could be used for compost formation and methane gas generation

    Domestic sector biomass burning to be reduced

    Low Food and civil supplies department, Oil companies

    Medium Rural areas should be encouraged to shift to cleaner fuels

    Virtual mobility- using ICT information and communication technology

    n.a Department of Information Technology& Biotechnology, Government of Karnataka;

    Short-Medium term

    Reduced number of trips.

    Strengthening of air quality monitoring mechanism in terms of number of stations as well as pollutants monitored. Capacity building of KSPCB staff.

    n.a KSPCB Short Good quality data is an important input in assessing the change in air quality and the impact of policy interventions. Continuous monitoring stations to be promoted.

    Environmental education and awareness activities

    n.a Education department, Schools/Colleges, CBOs, NGOs

    Short Also, sensitization programmes for policy makers.

    * Impact is determined in terms of percent reduction in total emission load for PM10 for the study period upto 2017 subject to the assumptions listed in chapter 6 (High impact > 5% reduction; medium impact 1-5% reduction; low impact < 1% reduction; n.a = not quantified or not quantifiable). Time frame: Short (upto 2012), Medium (2012-2017)

  • T E R I Report No. 2004EE28

    CHAPTER 1 Introduction

    1.1 Background of the study

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  • Air quality assessment, emission inventory and source apportionment study

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  • Air quality assessment, emission inventory and source apportionment study

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  • Air quality assessment, emission inventory and source apportionment study

    T E R I Report No. 2004EE28

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    12O5603.21 N 77 O3630.01 E Elevation 2991 ft

    12O5703.65 N 77 O3604.58 E Elevation 2920 ft

    12O5641.23 N 77 O3502.02 E Elevation 2996 ft

    12O5541.09 N 77 O3528.52 E Elevation 3016 ft

    N

    Figure 2.5 Sampling location at IGICH

    R

  • Air Quality Status

    T E R I Report No. 2004EE28

    13

    Peenya Industrial Area (Industrial location namely I) )

    +

    79 78:88

    !! 9 8? 88;@

    @::>

    4

    /"

    4

    7:>!>&

    7?>

    #&77>

    ;

    )++5C

    Figure 2.6 Sampling location at Peenya Industrial Area

    13O0128.15 N 77 O3039.92 E Elevation 2975 ft

    13O0107.97 N 77 O3122.61 E Elevation 2991

    13O0210.68 N 77 O3058.95 E Elevation 2969 ft

    13O0148.47 N 77 O2957.69 E Elevation 2955 ft

    13O0045.75 N 77 O3020.03 E Elevation 3014 ft

    N

  • Air quality assessment, emission inventory and source apportionment study

    T E R I Report No. 2004EE28

    14

    Kanamangala, Whitefield (Background location namely B) 2

    9

    79 8 988

    !! ?@8 88;!

  • Air Quality Status

    T E R I Report No. 2004EE28

    15

    Table 2.1 Summary descriptions of the seven sampling sites in terms of the predominant activities

    S.No Site Site Description Predominant activity levels

    1 Domlur Residential - High and medium income category population

    - Shops, showrooms and IT companies

    - Number of restaurants, bakeries and few big hotels

    - Vehicular distribution shows 47% 2-wheelers, 34% cars, 16% auto-rickshaws and

    3% heavy vehicles.

    2 Kammanahalli Residential - Low and medium income category population

    - Shops of medium scale

    - Restaurants, bakeries, dhabas and hotels

    - Vehicular distribution shows 57% 2-wheelers, 18% cars, 20% auto-rickshaws and

    5% heavy vehicles.

    3 Victoria Road Kerbside - Medium and low income category population

    - Heavy commercial activity zone, many commercial complexes

    - Restaurants, bakeries, and number of big hotels.

    - Vehicular distribution shows 47% 2-wheelers, 29% cars, 19% auto-rickshaws and

    5% heavy vehicles.

    4 CSB Kerbside - Mixed Population of all income groups

    - Shops and IT companies

    - Few, restaurants, bakeries and eating joints

    - High volume of heavy-duty diesel (HDD) vehicles

    - Vehicular distribution shows 46% 2-wheelers, 27% cars, 13% auto-rickshaws and

    14% heavy vehicles.

    5 IGICH Hospital

    (Residential)

    - Mixed Population of all income groups

    - Many hospitals and educational institutions

    - Shops of small and medium scale

    - Vehicular distribution shows 53% 2-wheelers, 22% cars, 19% auto-rickshaws and

    6% heavy vehicles.

    6 Peenya Industrial - Only one residential colony with medium and low income group population

    - Industries falling in the region include engineering, machine tools, metal smelting,

    chemical, and pharmaceuticals

    - High volume of heavy-duty diesel (HDD) vehicles

    - Vehicular distribution shows 57% 2-wheelers, 14% cars, 11% auto-rickshaws and

    18% heavy vehicles.

    7 Kanamangala,

    Whitefield

    Background - Plantation in 70% area of zone of influence

    - 10 % of area covered by about 200 medium income group houses.

    - Some bio-fuels usage for cooking

    - Movements of tractors and plying of very few public transport buses and HDD

    vehicles.

  • Air quality assessment, emission inventory and source apportionment study

    T E R I Report No. 2004EE28

    16

    Monitoring Parameters & Framework *D'

    2

    Table 2.2a Sampling and analytical protocol for source apportionment study being conducted at Bangalore

    Particulars Parameters

    SPM

    RSPM

    PM10 PM 2.5 NO2 SO2 CO

    OC/EC

    Ions VOC (Benzene and 1,3 Butadiene, Alkanes)

    O3

    Aldehyde

    NMHC

    HC

    PAHs (Included in

    organic Markers)

    Sampling Instrument

    High Volume Sampler

    Respirable Dust

    Sampler (High

    Volume Sampler)

    Multichannel (3 channel) Speciation Sampler

    FRM Partisol (PM2.5) sampler

    Impingers attached to RDS

    Impingers attached to

    RDS

    Online CO analyzer/Low

    volume sampling

    pump connected to Tedler bags

    PM10 Sampler

    Particulate collected on Quartz filter

    PM10 Sampler Particulate

    collected on Teflon filter

    Low volume sampling

    pump connected to Adsorption

    Tube

    Automatic analyser

    Impingers attached to HVS / RDS

    Low volume sampling

    pump connected to Tedlar bags

    Low volume sampling

    pump connected to Tedlar bags

    PM 10 Sampler

    Sampling Principle

    Filtration of aerodynamic

    sizes

    Filtration of aerodynamic

    sizes

    Filtration of aerodynamic sizes with a size cut by impaction

    Filtration of aerodynamic sizes with a size cut by impaction

    followed by cyclone

    separation

    Chemical absorption in suitable

    media

    Chemical absorption in

    suitable media

    Suction by Pump As per

    instrument specification

    Filtration of aerodynamic sizes with a size cut by

    impaction

    Filtration of aerodynamic sizes with a size cut by impaction

    Active pressurised sampling / Adsorption

    Suction by Pump

    Chemical Absorption

    Or Active

    pressurised sampling

    Suction by Pump

    Auto suction by pump

    Filtration of aerodynami

    c sizes

    Flow rate 0.8-1.2 m3/min

    0.8-1.2 m3/min

    16.7 LPM

    16.7 LPM 0.5 LPM/ 1 LPM

    0.5 LPM/ 1 LPM

    1.3 LPM 16.7 LPM

    16.7 LPM 0.2 - 0.5 LPM 0.7 LPM 0.5 LPM 0.2 lpm 0.2 lpm 16.7 LPM

    Sampling Period

    8 hourly change of

    filter, 24 Hourly Reporting

    8 hourly change of

    filter, 24 Hourly Reporting

    24 hourly 24 hourly 8 hourly/4 hourly

    change of absorbing media, 24

    Hourly Reporting

    8 hourly/4 hourly

    change of absorbing media, 24

    Hourly Reporting

    Continuous sampling

    24 hourly 24 hourly 8 Hourly sampling and

    24 Hourly Reporting

    One week continuous

    8 Hourly sampling and 24 Hourly

    Reporting

    Intermittent sampling in

    24 hour

    Intermittent sampling in

    24 hour

    Weekly composite of left over Quartz filter after OC/Ec

    analysis

  • Air Quality Status

    T E R I Report No. 2004EE28

    17

    Particulars Parameters

    SPM

    RSPM

    PM10 PM 2.5 NO2 SO2 CO

    OC/EC

    Ions VOC (Benzene and 1,3 Butadiene, Alkanes)

    O3

    Aldehyde

    NMHC

    HC

    PAHs (Included in

    organic Markers)

    Sampling frequency

    20 Days continuous in each season,

    for three seasons at

    One location only

    20 Days continuous in each season,

    for three seasons

    20 Days continuous in

    each season, for

    three seasons

    One week continuous.

    4 days Teflon, 3

    days quartz

    20 Days continuous in each season, for three seasons

    20 Days continuous in each season,

    for three seasons

    One week continuous during 20 days of

    monitoring in each season

    20 Days continuous

    in each season, for

    three seasons

    20 Days continuous in each season,

    for three seasons

    Once during 20 days of

    monitoring in each season

    One week continuous during 20 days of

    monitoring in each season

    Once in 20 days of

    monitoring in each season

    One week continuous during 20 days of

    monitoring in each season

    One week continuous during 20 days of

    monitoring in each season

    03 weekly composite samples

    per season

    Analytical instrument

    Electronic Balance

    Electronic Balance

    Electronic Balance

    Electronic Micro

    Balance

    Spectrophotometer

    Spectrophoto-meter

    NDIR based continuous analyser

    OC/EC Analyser

    Ion Chromatograph

    GC-FID Automatic analyser

    Spectrophotometer

    GC - FID with Methaniser

    GC - FID with

    Methaniser

    GC-MS

    Analytical method

    Gravimetric Gravimetric Gravimetric Gravimetric Colorimetric

    Improved Jacob&Hochheiser method

    Colorimetric Modified

    west&Gake method

    IR absorption according to

    Beer & Lamberts law

    TOR Method

    Ion Chromatograph

    y

    USEPA method TO-1/ TO-2 / TO-4 /

    TO-10 / TO-14

    UV-Photometry

    Colorimetric (MBTH method)

    FID Analysis FID Analysis GC-MS

    Minimum Reportable

    value

    5 g/m3 5 g/m3 5 g/m3 5 g/m3 9 g/m3 4 g/m3 0.05 ppm 0.5 cm2 punch

    0.1 ppb 2 ppb

    1.0 g/m3

    0.05 ppm 0.05 ppm 1 ng/m3

    Notes: 1. Benzene & 1,3 Butadiene being done by Charcoal adsorption followed by desorbtion in CS2 and GC-FID Analysis. 2. Methodology for molecular marker has been provided separately

    3. To suitably split background monitoring into 3 periods so as to correspond to monitoring at other sites 4. CO and O3 monitoring for about 1 week per season

    Table 2.2b Target physical and chemical components (groups) for characterization of particulate matter for source apportionment studies at Bangalore

    Components Required filter matrix Analytical methods PM10 / PM2.5 Teflon filter paper. Pre and post exposure

    conditioning of filter paper is mandatory Gravimetric

    Elements (Na, Mg, Al, Si, P, S, Cl, Ca, Br, V, Mn, Fe, Co, Ni, Cu, Zn, As, Ti, Ga, Rb, Y, Zr, Pd, Ag, In, Sn, La Se, Sr, Mo, Cr, Cd, Sb, Ba, Hg, and Pb)

    Teflon filter paper Flame AAS and GT-AAS and Hydride generation for As and Hg, ICP-MS

    Ions (F-, Cl-, Br-, NO2-, NO3-, SO4-2, K+, NH4+, Na+, Ca++, Mg++) Teflon filter paper Ion chromatography with conductivity detector

  • Air quality assessment, emission inventory and source apportionment study

    T E R I Report No. 2004EE28

    18

    Components Required filter matrix Analytical methods Carbon Analysis (OC, EC and Total Carbon) Quartz filter. Prebaking of quartz filter

    paper at 600 C is essential TOR method

    Molecular markers* The left over quartz filter paper after OC/EC analysis. Pool of 20 days sample as the dust concentration in the filters at some locations were very low.

    Extraction, followed by GC-MS/ GC-FID analysis with and without derivatization

    Alkanes n- Hentriacontane n-Tritriacontane n- Pentatriacontane

    Hopanes 22, 29, 30 Trisnorneohopane 17(H), 21(H)-29 Norhopane 17(H), 21(H) Norhopane

    Alkanoic acid

    Hexadecanamide Octadecanamide

    PAHs Benzo[b]fluoranthene Benzo[k]fluoranthene Benzo[e]pyrene Indeno[1,2,3-cd]fluoranthene Indeno[1,2,3-cd]pyrene Phenylenepyrene Picene Coronene

    Others Stigmasterol Levoglucosan

    * Few molecular markers such as Indeno[1,2,3-cd]fluoranthene, Picene, Hopanes(above 3), Hexadecanamide could not be analysed. 17(H), 21(H)-Hopane was analysed instead.

    Table 2.2c Other pollutants and their methods of analysis

    Pollutants Methods SO2 Spectrophotometric measurement, Improved West & Gaeke Method NO2 Spectrophotometric measurement, Jacobs & Hochheiser Method CO GC FID with methaniser / NDIR based continuous analyzer O3 Automatic Analyzer, UV Photometric Method Aldehydes Spectrophotometric measurement Benzene Active sampling in charcoal adsorption, desorption in CS2 and GC-FID

    determination 1,3 Butadiene GC - FID Method with suitable sorbent HC Sampling in Tedlar Bag followed by GC - FID NMHC By difference THC Methane by GC FID with methaniser

  • T E R I Report No. 2004EE28

    2.3 QA/QC (Calibration, coding, quality checks, etc.)

    Development of standard operating procedures and QA/QC plan )5$

    07 $ @1

    4

    ((

    Quality Assurance and Quality Control #''

    '(E

    '0(-,-=--9%=

    +=

    41'

    =(-,-

    -

    =4

    35

    4

    @

    -=-4

    =-

    0771F3-

    '

    -44

    /

    3

    (;*E

    G0

    1

    H059 1

    #5

    (

    %=7

    -

    *

  • 20 Air quality assessment, emission inventory and source apportionment study

    T E R I Report No. 2004EE28

    2

    7

    +

    $

    ;

    2I#BI=

    =)=7

    J !

    (29

    Table 2.3 Difference (mg) in post and pre-weights of lab blanks for different batches of filters used in the 1st season

    S.No Lab blanks

    1 0.00027

    2 0.00086

    3 0.00431

    4 0.00078

    5 0.00037

    6 0.01057

    7 0.01013

    8 0.00234

    9 0.00107

    +

  • 21 Air Quality Status

    T E R I Report No. 2004EE28

    2.4 Monitoring results *

    Domlur (Residential) ;:()*()*)*

    /()*B()*

    (-,-

    =-

    -9=)=

    01=--9

    Kammanahalli (Residential) ()*()*

    )*

    (-

    ,-

    =-

    -9

    =)=D

    =--9

    ;A

    CSB (Kerbside) #;7 ()*()*)*

    ()*

    #()*

    )*=)=

    (-

    ,-

    =-

    -9

    =)=

    =--9

    Victoria road (Kerbside) ()*()*

    )*

    =)=

  • 22 Air quality assessment, emission inventory and source apportionment study

    T E R I Report No. 2004EE28

    (-

    ,-

    =-

    -9

    =)=

    =--9

    ;77

    IGICH (Hospital/ Residential) ;7()*

    /

    0()*()*)*1

    (-

    ,-

    =-

    #-9

    01#

    =)==--9

    Peenya (Industrial) ()*

    ()*?

    '

    )*

    (-

    ,-

    =-

    -9

    -9

    =--9

    ;79

    Kanamangala(Background)

    #;7?()*()*)*

    (-

    ,-

    =-

    -9

    =--9

  • 23 Air Quality Status

    T E R I Report No. 2004EE28

    * NO2 reported as NOx

    For uniform depiction purpose 8-hourly O3 values are averaged for each day

    126

    67 69

    25

    7293

    25

    71

    24

    63

    19

    152

    0

    40

    80

    120

    160

    200

    SPM RSPM PM10 (avg.) PM2.5

    Conc

    entra

    tion

    ( g/

    m)

    Ist IInd IIIrd

    050

    100150200250300350400

    18.1

    2.06

    21.1

    2.06

    24.1

    2.06

    27.1

    2.06

    30.1

    2.06

    2.01

    .07

    5.1.

    078.

    1.07

    11.4

    .07

    14.4

    .07

    17.4

    .07

    20.4

    .07

    23.4

    .07

    26.4

    .07

    29.4

    .07

    2.5.

    075.

    5.07

    24.6

    .07

    27.6

    .07

    30.6

    .07

    3.7.

    076.

    7.07

    9.7.

    0712

    .7.0

    7

    Conc

    entra

    tion

    ( g/

    m)

    SPM RSPM PM10 PM2.5

    9

    4626

    586

    2955

    1492

    15 2243

    15

    1551

    1

    10

    100

    1000

    10000

    SO2 NOx O3 (ppb) CO

    Conc

    entra

    tion

    ( g/

    m)

    Ist IInd IIIrd

    0

    500

    1000

    1500

    2000

    2500

    3000

    3500

    12/1

    /200

    713

    /1/2

    007

    14/1

    /200

    715

    /1/2

    007

    16/1

    /200

    717

    /1/2

    007

    18/1

    /200

    720

    /1/2

    007

    21/1

    /200

    722

    /1/2

    007

    23/1

    /200

    724

    /1/2

    007

    25/1

    /200

    726

    /1/2

    007

    27/1

    /200

    728

    /1/2

    007

    25/6

    /200

    726

    /6/2

    007

    27/6

    /200

    728

    /6/2

    007

    29/6

    /200

    730

    /6/2

    007

    1/7/

    2007

    2/7/

    2007

    CO co

    nce

    ntr

    atio

    n (

    g/m

    )

    Figure 2.8 : Air quality monitoring results for Domlur (Residential)

    First Second Third

    1

    10

    100

    1000

    10000

    18.1

    2.06

    21.1

    2.06

    24.1

    2.06

    27.1

    2.06

    30.1

    2.06

    2.01

    .07

    5.1.

    078.

    1.07

    11.4

    .07

    14.4

    .07

    17.4

    .07

    20.4

    .07

    23.4

    .07

    26.4

    .07

    29.4

    .07

    2.5.

    075.

    5.07

    24.6

    .07

    27.6

    .07

    30.6

    .07

    3.7.

    076.

    7.07

    9.7.

    0712

    .7.0

    7

    Conc

    entra

    tion

    ( g/

    m)

    SO2 NOx CO O3 (ppb)

    First Second Third

    First Second Third

    15

    2

    13

    30

    12

    1

    11

    31

    11

    2

    915

    05

    101520253035

    THC (ppm) Methane (ppm) NMHC (ppm) Aldehydes(ug/m)

    Conc

    entra

    tion

    Ist IInd IIIrd

    1.6

    0.4

    0.0

    0.4 0.4

    1.21.5

    0.90.4 0.3

    28.3

    0.4 0.5

    25.7

    1.3

    0.4

    1.7 1.2

    28.0

    0.40.40.1

    1.0

    10.0

    100.0

    Metha

    neEth

    aneBut

    ane

    Pentan

    e

    Hexan

    e

    Benzen

    e (ppb)

    1-3 Bu

    tadien

    e (ppb)

    Conc

    entra

    tion

    (ppm

    )

    Ist IInd IIIrd

    0

    20

    40

    60

    80

    100

    120

    12/23

    /2006

    12/24

    /2006

    12/26

    /2006

    12/27

    /2006

    12/28

    /2006

    12/29

    /2006

    12/31

    /2006

    26/4/0

    7

    27/4/0

    7

    28/4/0

    7

    30/4/0

    7

    1/5/20

    07

    2/5/20

    07

    3/5/20

    07

    8/7/20

    07

    10/7/2

    007

    11/7/2

    007

    12/7/2

    007

    13/7/0

    7

    Ozo

    ne (p

    pb)

    First Second Third

  • 24 Air quality assessment, emission inventory and source apportionment study

    T E R I Report No. 2004EE28

    * NO2 reported as NOx

    010203040506070

    1/31

    /07

    2/3/

    072/

    4/07

    2/4/

    072/

    5/07

    2/6/

    072/

    6/07

    5/11

    /07

    5/13

    /07

    5/14

    /07

    5/15

    /07

    5/17

    /07

    8/11

    /07

    8/13

    /07

    8/14

    /07

    8/14

    /07

    8/15

    /07

    8/16

    /07

    8/17

    /07

    8/18

    /07O

    zone

    Con

    cent

    ratio

    n (p

    pb)

    12

    2

    10 10

    15

    3

    1214

    17

    3

    13 14

    0

    5

    10

    15

    20

    THC (ppm) Methane (ppm) NMHC (ppm) Aldehydes(ug/m)

    Conc

    entra

    tion

    Ist IInd IIIrd

    3.41.8 1.2

    0.7 0.5

    63.1

    3.92.71.5

    0.6 0.6

    59.7

    1.90.9

    0.9

    3.3

    0.8 0.5

    66.1

    3.93.1

    0.1

    1.0

    10.0

    100.0

    Metha

    neEth

    aneBut

    ane

    Pentan

    e

    Hexan

    e

    Benzen

    e (ppb)

    1-3 Bu

    tadien

    e (ppb)

    Conc

    entra

    tion

    (ppm

    )

    Ist IInd IIIrd

    First Second Third

    0

    100

    200

    300

    400

    50013

    .01.

    0716

    .01.

    0719

    .01.

    0722

    .01.

    0725

    .01.

    0728

    .01.

    0731

    .01.

    0703

    .02.

    0706

    .02.

    07

    6.5.

    079.

    5.07

    12.5

    .07

    15.5

    .07

    18.5

    .07

    21.5

    .07

    24.5

    .07

    10/8

    /200

    713

    /8/2

    007

    16/8

    /200

    719

    /8/2

    007

    22/8

    /200

    725

    /8/2

    007

    28/8

    /200

    731

    /8/2

    007

    Conc

    entra

    tion

    ( g/

    m)

    SPM RSPM PM10 PM2.5

    First Second Third

    1

    10

    100

    1000

    10000

    13.0

    1.07

    16.0

    1.07

    19.0

    1.07

    22.0

    1.07

    25.0

    1.07

    28.0

    1.07

    31.0

    1.07

    03.0

    2.07

    06.0

    2.07

    6.5.

    079.

    5.07

    12.5

    .07

    15.5

    .07

    18.5

    .07

    21.5

    .07

    24.5

    .07

    10/8

    /200

    713

    /8/2

    007

    16/8

    /200

    719

    /8/2

    007

    22/8

    /200

    725

    /8/2

    007

    28/8

    /200

    731

    /8/2

    007C

    once

    ntra

    tion

    ( g/

    m)

    SO2 NOx CO O3 (ppb)

    First Second Third

    Figure 2.9: Air quality monitoring results for Kammanahalli (Residential)

    294

    115133

    34

    109 92

    41

    177

    61 5329

    301

    050

    100150200250300350

    SPM RSPM PM10 (avg.) PM2.5

    Conc

    entra

    tion

    ( g/

    m)

    Ist IInd IIIrd

    5

    26 18

    1220

    1942

    3322

    11

    49 39

    10

    1689

    1

    10

    100

    1000

    10000

    SO2 NOx O3 (ppb) COCo

    ncen

    tratio

    n (

    g/m

    )

    Ist IInd IIIrd

    01000200030004000500060007000

    31/0

    1/20

    07

    1/2/

    07

    3/2/

    07

    4/2/

    07

    5/2/

    07

    7/2/

    07

    12/8

    /07

    13/0

    8/07

    15/0

    8/07

    17/0

    8/07

    18/0

    8/07

    19/0

    8/07CO

    Con

    cent

    ratio

    n (

    g/m

    )

    First Third

    For uniform depiction purpose 8-hourly O3 values are averaged for each day

    Second season continuous data for CO not available

  • 25 Air Quality Status

    T E R I Report No. 2004EE28

    * NO2 reported as NOx

    Second season continuous data for CO not available

    2.8 1.80.9 0.9

    0.7

    2.3 2.01.1

    0.7

    65.7

    1.81.0

    3.1

    76.9

    2.81.1

    3.4 3.4

    80.0

    0.7

    0.9

    0.1

    1.0

    10.0

    100.0

    Metha

    neEth

    aneBut

    anePen

    tane

    Hexan

    e

    Benzen

    e (ppb)

    1-3 Bu

    tadien

    e (ppb)

    Conc

    entra

    tion

    (ppm

    )

    Ist IInd IIIrd

    181

    91 986276

    96

    31

    411

    10273

    38

    191

    0

    100

    200

    300

    400

    500

    SPM RSPM PM10 (avg.) PM2.5

    Conc

    entra

    tion

    ( g/

    m)

    Ist IInd IIIrd

    14

    3

    11

    35

    14

    2

    12

    36

    16

    3

    12

    34

    0

    10

    20

    30

    40

    THC (ppm) Methane (ppm) NMHC (ppm) Aldehydes(ug/m)

    Conc

    entra

    tion

    Ist IInd IIIrd

    Figure 2.10: Air quality monitoring results for CSB (Kerbside)

    10

    94

    12

    1180

    5827

    3636

    10

    47 3714

    1234

    1

    10

    100

    1000

    10000

    SO2 NOx O3 (ppb) CO

    Conc

    entra

    tion

    ( g/

    m)

    Ist IInd IIIrd

    0100200300400500600

    15.1

    2.06

    18.1

    2.06

    21.1

    2.06

    24.1

    2.06

    27.1

    2.06

    30.1

    2.06

    02.0

    1.07

    05.0

    1.07

    08.0

    1.07

    13.4

    .07

    16.4

    .07

    19.4

    .07

    22.4

    .07

    25.4

    .07

    28.4

    .07

    1.5.

    07

    19/7

    /200

    722

    /7/2

    007

    25/7

    /200

    728

    /7/2

    007

    31/7

    /200

    73/

    8/20

    076/

    8/20

    079/

    8/20

    0712

    /8/2

    007

    Conc

    entra

    tion

    ( g/

    m)

    SPM RSPM PM10 PM2.5

    First Second Third

    1

    10

    100

    1000

    10000

    15.1

    2.06

    18.1

    2.06

    21.1

    2.06

    24.1

    2.06

    27.1

    2.06

    30.1

    2.06

    02.0

    1.07

    05.0

    1.07

    08.0

    1.07

    13.4

    .07

    16.4

    .07

    19.4

    .07

    22.4

    .07

    25.4

    .07

    28.4

    .07

    1.5.

    07

    19/7

    /200

    722

    /7/2

    007

    25/7

    /200

    728

    /7/2

    007

    31/7

    /200

    73/

    8/20

    076/

    8/20

    079/

    8/20

    0712

    /8/2

    007

    Conc

    entra

    tion

    ( g/

    m)

    SO2 NOx CO O3 (ppb)

    First Second Third

    010203040506070

    12/2

    7/06

    12/2

    8/06

    12/2

    8/06

    12/2

    9/06

    12/3

    0/06

    12/3

    1/06

    1/1/

    071/

    2/07

    4/26

    /07

    4/27

    /07

    4/28

    /07

    4/29

    /07

    4/29

    /07

    4/30

    /07

    5/1/

    075/

    2/07

    7/31

    /07

    8/1/

    078/

    1/07

    8/2/

    078/

    3/07

    8/4/

    078/

    5/07

    8/6/

    078/

    6/07O

    zone

    Con

    cent

    ratio

    n (p

    pb)

    First Second Third

    01000200030004000500060007000

    29/1

    2/06

    31/1

    2/06

    1/1/

    07

    3/1/

    07

    4/1/

    07

    6/1/

    07

    7/1/

    07

    31/7

    /07

    2/8/

    07

    3/8/

    07

    5/8/

    07

    6/8/

    07

    CO C

    once

    ntra

    tion

    ( g/

    m)

    First Third

    For uniform depiction purpose 8-hourly O3 values are averaged for each day

  • 26 Air quality assessment, emission inventory and source apportionment study

    T E R I Report No. 2004EE28

    * NO2 reported as NOx

    First Second Third

    For uniform depiction purpose 8-hourly O3 values are averaged for each day

    0100200300400500600

    2/16

    /07

    2/19

    /07

    2/22

    /07

    2/25

    /07

    2/28

    /07

    3/3/

    073/

    6/07

    3/9/

    073/

    12/0

    73/

    15/0

    73/

    18/0

    718

    .6.0

    721

    .6.0

    724

    .6.0

    727

    .6.0

    730

    .6.0

    73.

    7.07

    6.7.

    079.

    7.07

    3/9/

    076/

    9/07

    9/9/

    0712

    /9/0

    715

    /9/2

    007

    18/9

    /200

    721

    /9/2

    007

    Conc

    entra

    tion

    ( g/

    m)

    SPM RSPM PM10 PM2.5

    306

    191 199

    64

    115

    184

    43

    369

    100 109

    27

    287

    050

    100150200250300350400

    SPM RSPM PM10 (avg.) PM2.5

    Conc

    entra

    tion

    ( g/

    m)

    Ist IInd IIIrd

    1

    10

    100

    1000

    10000

    2/16

    /07

    2/19

    /07

    2/22

    /07

    2/25

    /07

    2/28

    /07

    3/3/

    073/

    6/07

    3/9/

    073/

    12/0

    73/

    15/0

    73/

    18/0

    718

    .6.0

    721

    .6.0

    724

    .6.0

    727

    .6.0

    730

    .6.0

    73.

    7.07

    6.7.

    079.

    7.07

    3/9/

    076/

    9/07

    9/9/

    0712

    /9/0

    715

    /9/2

    007

    18/9

    /200

    721

    /9/2

    007

    Conc

    entra

    tion

    ( g/

    m)

    SO2 NOx CO O3 (ppb)

    7

    60

    12

    3338

    10535

    1183

    12

    6637

    19

    1560

    1

    10

    100

    1000

    10000

    SO2 NOx O3 (ppb) CO

    Conc

    entra

    tion

    ( g/

    m)

    Ist IInd IIIrd

    020406080

    100120

    3/12

    /07

    3/13

    /07

    3/14

    /07

    3/15

    /07

    3/16

    /07

    3/17

    /07

    3/18

    /07

    3/19

    /07

    7/5/

    077/

    6/07

    7/7/

    077/

    8/07

    7/9/

    077/

    10/0

    77/

    11/0

    7

    9/4/

    079/

    5/07

    9/6/

    079/

    7/07

    9/8/

    07

    Ozo

    ne C

    once

    ntra

    tion

    (ppb

    )

    0

    5000

    10000

    15000

    20000

    5/3/

    077/

    3/07

    8/3/

    0710

    /3/0

    712

    /3/0

    7

    4/7/

    075/

    7/07

    7/7/

    078/

    7/07

    4/9/

    075/

    9/07

    7/9/

    079/

    9/07C

    O Co

    ncen

    tratio

    n (

    g/m

    )

    12

    210

    1711

    39

    36

    13

    2

    11

    37

    0

    10

    20

    30

    40

    THC (ppm) Methane(ppm)

    NMHC (ppm) Aldehydes(ug/m)

    Conc

    entra

    tion

    Ist IInd IIIrd

    2.11.2 1.2

    0.6 0.5

    0.01.82.7 1.3

    0.6 0.5

    15.6

    1.3 1.2 1.61.12.5 1.9

    12.6

    0.50.60.1

    1.0

    10.0

    100.0

    Metha

    neEth

    aneBut

    anePen

    tane

    Hexan

    e

    Benzen

    e (ppb)

    1-3 Bu

    tadien

    e (ppb)

    Conc

    entra

    tion

    (ppm

    )

    Ist IInd IIIrd

    Figure 2.11: Air quality monitoring results for Victoria Road (Kerbside)

    First Second Third

    First Second Third

    First Second Third First Second Third

  • 27 Air Quality Status

    T E R I Report No. 2004EE28

    * NO2 reported as NOx

    For uniform depiction purpose 8-hourly O3 values are averaged for each day

    0

    50

    100

    150

    200

    250

    3002.

    3.07

    8.3.

    0711

    .3.0

    714

    .3.0

    717

    .3.0

    720

    .3.0

    723

    .3.0

    7

    4/16

    /07

    4/19

    /07

    4/22

    /07

    28.5

    .07

    31.5

    .07

    3.6.

    076.

    6.07

    9.6.

    712

    .6.0

    715

    .6.0

    7

    10/8

    /07

    13/8

    /200

    716

    /8/2

    007

    19/8

    /200

    722

    /8/2

    007

    25/8

    /200

    728

    /8/2

    007

    31/0

    8/07

    Conc

    entra

    tion

    ( g/

    m)

    SPM RSPM PM10 PM2.5

    197

    81 85

    3623 34 15

    79

    3769

    2252

    0

    50

    100

    150

    200

    250

    SPM RSPM PM10 (avg.) PM2.5

    Conc

    entra

    tion

    ( g/

    m)

    Ist IInd IIIrd

    1

    10

    100

    1000

    10000

    2.3.

    078.

    3.07

    11.3

    .07

    14.3

    .07

    17.3

    .07

    20.3

    .07

    23.3

    .07

    4/16

    /07

    4/19

    /07

    4/22

    /07

    28.5

    .07

    31.5

    .07

    3.6.

    076.

    6.07

    9.6.

    712

    .6.0

    715

    .6.0

    7

    10/8

    /07

    13/8

    /200

    716

    /8/2

    007

    19/8

    /200

    722

    /8/2

    007

    25/8

    /200

    728

    /8/2

    007

    31/0

    8/07

    Conc

    entra

    tion

    ( g/

    m)

    SO2 NOx CO O3 (ppb)

    6

    23 37

    3750

    1851

    483

    8

    9037

    13

    2016

    1

    10

    100

    1000

    10000

    SO2 NOx O3 (ppb) CO

    Conc

    entra

    tion

    ( g/

    m)

    Ist IInd IIIrd

    020406080

    100120

    4/13

    /07

    4/15

    /07

    4/17

    /07

    4/18

    /07

    4/19

    /07

    4/20

    /07

    4/21

    /07

    4/22

    /07

    6/1/

    076/

    3/07

    6/3/

    076/

    4/07

    6/5/

    076/

    6/07

    6/7/

    07

    8/21

    /07

    8/22

    /07

    8/23

    /07

    8/24

    /07

    Ozo

    ne C

    once

    ntra

    tion

    (ppb

    )

    02000400060008000

    100001200014000

    15/0

    3/07

    17/0

    3/07

    18/0

    3/07

    20/0

    3/07

    21/0

    3/07

    31/0

    5/07

    1/6/

    073/

    6/07

    4/6/

    076/

    6/07

    7/6/

    07

    24/0

    8/07

    26/0

    8/07

    27/0

    8/07C

    O Co

    ncen

    tratio

    n (

    g/m

    )

    11

    2

    10

    16

    11

    1

    108

    13

    1

    12

    7

    0

    5

    10

    15

    20

    THC (ppm) Methane (ppm) NMHC (ppm) Aldehydes(ug/m)

    Conc

    entra

    tion

    Ist IInd IIIrd

    0.4 0.5

    0.9

    0.2 0.2

    2.0

    0.6 0.60.2 0.3

    23.1

    0.50.8

    18.8

    0.8

    1.2

    0.2 0.3

    19.6

    2.1

    0.50.1

    1.0

    10.0

    100.0

    Metha

    neEth

    aneBut

    ane

    Penta

    ne

    Hexan

    e

    Benzen

    e (ppb)

    1-3 Bu

    tadien

    e (ppb)

    Conc

    entra

    tion

    (ppm

    )

    Ist IInd IIIrd

    Figure 2.12: Air quality monitoring results for IGICH (Hospital/Residential)

    First Second Third

    First Second Third First Second Third

    First Second Third

  • 28 Air quality assessment, emission inventory and source apportionment study

    T E R I Report No. 2004EE28

    * NO2 reported as NOx

    0

    100

    200

    300

    400

    500

    2/14

    /07

    2/17

    /07

    2/20

    /07

    2/23

    /07

    2/26

    /07

    3/1/

    073/

    4/07

    3/7/

    07

    3/24

    /07

    3/27

    /07

    5.5.

    078.

    5.07

    11.5

    .07

    14.5

    .07

    17.5

    .07

    20.5

    .07

    23.5

    .07

    18/7

    /200

    721

    /7/2

    007

    24/7

    /200

    727

    /7/2

    007

    30/7

    /200

    72/

    8/07

    5/8/

    07

    Conc

    entra

    tion

    ( g/

    m)

    SPM RSPM PM10 PM2.5

    262

    143171

    30

    84

    171

    21

    171

    58 69

    22

    245

    0

    50

    100

    150

    200

    250

    300

    SPM RSPM PM10 (avg.) PM2.5

    Conc

    entra

    tion

    ( g/

    m)

    Ist IInd IIIrd

    1

    10

    100

    1000

    10000

    2/14

    /07

    2/17

    /07

    2/20

    /07

    2/23

    /07

    2/26

    /07

    3/1/

    073/

    4/07

    3/7/

    07

    3/24

    /07

    3/27

    /07

    5.5.

    078.

    5.07

    11.5

    .07

    14.5

    .07

    17.5

    .07

    20.5

    .07

    23.5

    .07

    18/7

    /200

    721

    /7/2

    007

    24/7

    /200

    727

    /7/2

    007

    30/7

    /200

    72/

    8/07

    5/8/

    07

    Conc

    entra

    tion

    ( g/

    m)

    SO2 NOx CO O3 (ppb)

    9

    5326

    1780

    30 39

    4411

    10

    8936

    10

    3373

    1

    10

    100

    1000

    10000

    SO2 NOx O3 (ppb) CO

    Conc

    entra

    tion

    ( g/

    m)

    Ist IInd IIIrd

    0

    20

    40

    60

    80

    3/21

    /07

    3/22

    /07

    3/23

    /07

    3/24

    /07

    3/25

    /07

    3/26

    /07

    3/27

    /07

    3/28

    /07

    5/19

    /07

    5/21

    /07

    5/22

    /07

    5/24

    /07

    7/17

    /07

    7/18

    /07

    7/19

    /07

    7/20

    /07

    7/21

    /07

    7/22

    /07

    7/23

    /07

    Ozo

    ne C

    once

    ntra

    tion

    (ppb

    )

    0300060009000

    1200015000

    24/0

    2/07

    26/0

    2/20

    07

    27/0

    2/07

    1/3/

    07

    2/3/

    07

    4/3/

    07

    5/3/

    07

    17/0

    7/20

    07

    19/0

    7/20

    07

    20/0

    7/07

    22/0

    7/07

    24/0

    7/07CO

    Con

    cent

    ratio

    n (

    g/m

    )

    12

    2

    9

    22

    15

    3

    12

    1919

    4

    1518

    05

    10152025

    THC (ppm) Methane (ppm) NMHC (ppm) Aldehydes(ug/m)

    Conc

    entra

    tion

    Ist IInd IIIrd

    3.11.6 1.3

    0.7 0.5

    3.33.51.7

    0.9 0.6

    61.7

    1.8 1.1

    66.0

    3.21.1

    3.7 3.4

    66.1

    0.70.80.1

    1.0

    10.0

    100.0

    Metha

    neEth

    aneBut

    ane

    Pentan

    e

    Hexan

    e

    Benzen

    e (ppb)

    1-3 Bu

    tadien

    e (ppb)

    Conc

    entra

    tion

    (ppm

    )

    Ist IInd IIIrd

    Figure 2.13: Air quality monitoring results for Peenya (Industrial)

    First Second Third First Third

    First Second Third

    First Second Third

    For uniform depiction purpose 8-hourly O3 values are averaged for each day

    Second season continuous data for CO not available

  • 29 Air Quality Status

    T E R I Report No. 2004EE28

    * N

    O2

    reported

    as N

    Ox

    110

    5147

    2732

    105

    23

    83

    31

    66

    27

    82

    0 40 80

    120

    160

    200

    SP

    MR

    SP

    MP

    M10

    (avg.)P

    M2.5

    Concentration (g/m)

    IstIInd

    IIIrd

    For uniform depiction purpose 8-hourly O

    3 values are averaged for each day

    12

    2

    119

    7

    0

    76

    8

    0

    88

    0 5 10 15

    THC (ppm)

    Methane

    (ppm)

    NMHC (ppm

    )Aldehydes

    (ug/m)

    Concentration

    IstIInd

    IIIrd

    0.30.2

    0.0

    0.10.0

    3.6

    0.50.3

    0.10.1

    0.1

    0.0

    0.20.1

    0.10.3

    0.10.1

    3.3

    0.40.2

    0.0

    0.1

    1.0

    10.0MethaneEthane

    Butane

    Pentane

    HexaneBenzene (ppb)

    1-3 Butadiene (ppb)

    Concentration (ppm)

    IstIInd

    IIIrd

    Figu

    re 2

    .14: A

    ir q

    uality

    mo

    nitoring

    results fo

    r K

    anam

    angala

    (Backg

    rou

    nd)

    618

    21

    925

    4554

    1723

    9

    9144

    14

    1399

    1 10

    100

    1000

    10000

    SO2

    NOx

    O3 (ppb)

    CO

    Concentration (g/m)

    IstIInd

    IIIrd

    1 10

    100

    1000

    10000

    12/15/200612/25/2006

    1/4/20071/14/20071/24/20072/3/2007

    2/13/20072/23/20073/5/2007

    3/15/20073/25/2007

    16/04/200726/04/200706/05/200716/05/200726/05/20075/06/2007

    15/06/200725/06/20075/07/2007

    28/6/078/7/2007

    18/7/200728/7/20077/8/2007

    17/8/200727/8/20076/9/2007

    16/9/2007

    Concentration (g/m)

    SO2

    NOx

    COO

    3 (ppb) First

    S

    econd

    Third

    0 50100150200250300

    12/15/200612/25/2006

    1/4/20071/14/20071/24/20072/3/2007

    2/13/20072/23/20073/5/2007

    3/15/20073/25/2007

    16/04/200726/04/200706/05/200716/05/200726/05/2007

    5/06/200715/06/200725/06/2007

    5/07/200728/6/07

    8/7/200718/7/200728/7/20077/8/2007

    17/8/200727/8/20076/9/2007

    16/9/200726/9/2007

    Concentration (g/m)

    SPMRSPM

    PM10

    PM2.5

    First

    S

    econd

    Third

    0 20 40 60 80100

    1/19/071/20/071/21/071/22/071/23/071/24/071/25/071/26/071/27/07

    5/4/075/5/075/6/075/7/075/8/075/9/075/10/07

    9/12/079/13/079/15/079/16/079/17/079/18/079/19/079/20/079/21/079/22/079/23/079/24/07

    Ozone Concentration (ppb)

    First

    S

    econd

    Third

    0

    3000

    6000

    9000

    12