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Transboundary Air Pollution
Badar Ghauri, Director, SUPARCO
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Whos Air Do We Breathe?
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Introduction
Pollution is a global problem
There are no boundaries
Satellite Remote Sensing is the only way to mapglobal distribution of air pollution
This talk will highlight various tools available to
track global/Transboundary pollution
Regional and intercontinental aerosol pollution willbe discussed
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Country-to-country source-receptor matrix
Source:Foell et.al, December, 1995(Final report submitted to The World Bank)
The columns represent the source country while the rows represent the
receptor country. Shown is the total annual sulfur deposition expressed intones S/yr
Source/Receptor
Bangladesh Bhutan India Nepal Pakistan Sri Lanka
Bangladesh
1.77E+04 1.27E+00 1.64E+04 1.77E+02 2.30E+02
4.34E-03
Bhutan3.83E+02 1.63E+02 8.14E+03 4.37E+02 8.65E+01
5.57E-18
India1.58E+04 7.14E+01 1.06E+06 5.26E+03 1.88E+04
5.49E+02
Nepal3.22E+02 1.78E+00 4.06E+04 2.21E+04 1.04E+03
1.92E-20
Pakistan 0.00E+00 3.46E-09 1.73E+04 3.97E+00 1.16E+05 0.00E+00
Sri Lanka6.72E+00 4.99E-07 2.97E+03 5.70E-01 6.63E-01
8.15E+03
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Countries with Renewable EnergyTargets in the Region
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Strategy on Transboundary AirPollution
Adequacy of data compiled
Pollutants of concern (additional pollutants)
SOx, NOx, Ozone, etc (NOx shows significant increase) Compatibility of information collected
QA/QC issues
Common monitoring protocol (such as EANET technical manual)
Adequacy of monitoring network (strengthening in terms of no. ofstations/ parameters, frequency)
National baseline studies
Integration of Monitoring data on a sub-regional basis
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Strategy on Transboundary AirPollution
Comparison of methodologies used for different pollutants
Aim for a common approach
Use of emission factors
First preference: Local emission factors for various
activities
Else use emission factors such as from WB rapid
emission inventory
Undertake emission factors development (where ever
deemed necessary)
Subsequent refinements/ updating of emission inventories
Transparency in the development of inventory
Capacity Building
Analysis and refinement of National emission inventories
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Strategy on Transboundary AirPollution
Identification of appropriate tools/ models
Model acceptability and ownership - focal centre
Integrated assessment model - effects based approach
Input data compilation -
emissions/meteorology/database on critical loads
Validation: model prediction vs observed data
Capacity Building
Strengthening of regional modeling capabilities
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Strategy on Transboundary AirPollution
Regional cooperation in cleaner energysources (hydel, alternative energies)
Fuel quality improvement (eg., reduced S indiesel)
Improvement in energy efficiency
Sharing of information and cooperation inadoption of clean process technologies as wellas EOP control technologies
Strategies to minimize air pollution
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Strategy on Transboundary AirPollution
Damage to human health
Impacts on crop productivity, forests, etc
Related economic analysis
These would assist in formulating
appropriate policy response
Studies on the impact assessment
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Strategy on Transboundary AirPollution
Involve relevant stakeholders
Industry, NGOs, research institutes, media
Dissemination of tools, methodologies, and data
Information sharing
Stakeholder involvement and information dissemination
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Strategy on Transboundary AirPollution
Policy issues
Financial assistance for tackling TAP:
Multilateral (UNEP/SACEP), National
funds, others
Scientific process to aid policy making :
Leading to signing of Agreement/
Protocol
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Intergovernmental meeting, stakeholders meeting cum
coordination meeting
Participating countries should initiate the process of
understanding issues arising from TAP
Air pollution related initiatives in South Asia need to be
encouraged to participate
National Advisory Committee and National Stakeholders should
coordinate activities at the national and international levels
Regional Cooperation
Male Declaration
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Male declaration on control & prevention of airpollution & its likely transboundary effects
Declaration approved on April 22, 1998
Aims: intergovernmental cooperation to address TAP
and consequential impacts
Sets an institutional framework linking scientific
research and policy formulation
To draw up and implement national and regional
action plan and protocols based on fullerunderstanding of TAP
India, Pakistan, Bangladesh, Nepal, Sri Lanka,
Bhutan, Maldives and Iran
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Development March 1998: Policy Dialogue
April 1998: Adoption of the Declaration
Implementation Phase I: Awareness and preparation of the baseline information
Phase II: Local capacity development for monitoring and analysis
Member states
Male Declaration
Bhutan
Nepal
Bangladesh
Sri Lanka
Iran
Pakistan
India
Maldives
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Strengthen the regional cooperation and stakeholders participation
under the Mal Declaration;
Strengthen the capacity building programmes initiated
Enhance the capacity of NIAs on emission inventory development
and Integrated Assessment Modeling
Enhance the analytical and impact assessment capability at thenational level through integration of findings from local pollution
studies and conducting assessment studies;
Provide decision support information for policy formulation and airpollution prevention ;
Raise awareness for action through targeted dissemination
Objectives (April 1998)
Male Declaration
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Terra
Aqua
Satellite Measurement Capability
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Aerosol Optical Thickness (AOT) is the degree to which aerosols
prevent the transmission of light. Aerosol Optical Thickness alsoreferred to as optical depth or optical thickness depends upon the
physical constitution, the form and concentration of aerosols.
The transmissivity, which is the ratio of amount of solar radiation
incident on the surface of the earth to the amount of solar
radiation incident at the top of the atmosphere, has a value
between 0 and 1, is an indication of Aerosol optical thickness.
The smaller the transmissivity, the larger the aerosol optical
thickness. When the transmissivity is 0 the atmosphere is
perfectly opaque, and when the transmissivity is 1 the
atmosphere is perfectly transparent.
Aerosol Optical Thickness
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From AOT to Air Quality
Using satellite AOT to assess air quality categories
IndexValues
Category Cautionary StatementsPM2.5
(ug/m3)PM10
(ug/m3)
0-50 Good 0-15.4 0-54
51-100 ModerateUnusually sensitive peopleshould consider reducing
prolonged or heavy exertion
15.5-40.4 55-154
101-150
Unhealthyfor
SensitiveGroups
Sensitive groups should reduceprolonged or heavy exertion
40.5-65.4 155-254
151-200 Unhealthy
Sensitive groups should avoid
prolonged or heavy exertion;everyone else should reduceprolonged or heavy exertion
65.5-150.4 255-354
201-300VeryUnhealth
y
Sensitive groups should avoidall physical activity outdoors;
everyone else should avoid
prolonged or heavy exertion
150.5-250.4 355-424
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Northern India, Pakistan,Nepal, and Bangladesh Air
Quality Event
Case Study 1:
Map of the Air Quality Event Region
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Map of the Air Quality Event RegionNorthern India, Pakistan, Nepal, and Bangladesh
(http://worldatlas.com/webimage/countrys/asia/lgcolor/incolor.htm)
Region of Air
Quality Event
MODIS-Aqua True Color Image
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MODIS-Aqua True Color ImageNorthern India, Pakistan, Nepal, and Bangladesh
February 5, 2006(http://rapidfire.sci.gsfc.nasa.gov/gallery/?2006036-0205)
A l O ti l D th (AOD) I
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Aerosol Optical Depth (AOD) ImageNorthern India, Pakistan, Nepal, and Bangladesh
(Prepared by Battelle from MODIS-Aqua data using ArcView GIS processing software)
The AOD scale in this image is similar to the U.S. EPA Air Quality Index (AQI)
scale, such that red-colored regions indicate unhealthy air.
T C l d AOD I A il bl
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True Color and AOD Images Available onthe Internet
True Color Images
MODIS instrument:http://rapidfire.sci.gsfc.nasa.gov/subsets/
Click on region of interest. Click on the display alternate dates available for this subset link. Select date of interest (dates are in Julian date format).
Repeat for all overlapping regions of interest.
True Color and AOD Images
MODIS instrument:http://ladsweb.nascom.nasa.gov/browse_images/l2_browser.html
Select Terra or Aqua satellite Select appropriate month,day, and year. Select parameter from pull-down menu; RGB = true color images
Parasol satellite:http://www-icare.univ-lille1.fr/parasol/browse/ Click the box next to Aerosol Optical Thickness over land to view aerosol images.
AOD Images
OMI instrument:http://toms.gsfc.nasa.gov/aerosols/aerosols_v8.html
Scroll to the bottom of the page to select images. Select global image from Choose output pull-down menu. Select OMI: 8/17/2004 Present from coverage satellite pull-down menu. Select appropriate Date to be studied.
http://rapidfire.sci.gsfc.nasa.gov/subsets/http://ladsweb.nascom.nasa.gov/browse_images/l2_browser.htmlhttp://www-icare.univ-lille1.fr/parasol/browse/http://toms.gsfc.nasa.gov/aerosols/aerosols_v8.htmlhttp://toms.gsfc.nasa.gov/aerosols/aerosols_v8.htmlhttp://www-icare.univ-lille1.fr/parasol/browse/http://www-icare.univ-lille1.fr/parasol/browse/http://www-icare.univ-lille1.fr/parasol/browse/http://www-icare.univ-lille1.fr/parasol/browse/http://www-icare.univ-lille1.fr/parasol/browse/http://ladsweb.nascom.nasa.gov/browse_images/l2_browser.htmlhttp://rapidfire.sci.gsfc.nasa.gov/subsets/7/29/2019 Trans Air Pollution in Quetta
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Meteorological Information Availableon the Internet
Hourly Weather Observations (temperature,winds, visibility, etc.)
Weather Underground:http://www.wunderground.com/
Type India in the box at the top of the page, and hitenter.
Scroll down to the list of cities and click on Patna.
Select the date of interest under History andAlmanac.
Repeat for Lahore Pakistan
Repeat for Kolkata (Calcutta), India.
Repeat for Dhaka Bangladesh.
http://www.wunderground.com/http://www.wunderground.com/7/29/2019 Trans Air Pollution in Quetta
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Ground-Based Particulate Measurements
Indian National Air Quality Monitoring Programme (NAMP)
Central Pollution Control Board:http://www.cpcb.nic.in/index.php
Click on Air in the menu on the left side of the page.
Learn about Indian air quality monitoring by clicking on the different links in theAir section.
Currently, no data are archived for 2006, but you can get an idea of the trends inIndian air quality.
Nepal Ministry of Environment, Science and TechnologyAir Quality Monitoring Results:http://www.ncit.gov.np/pollution/pollution.php
24-hour average PM10 concentrations in mg m-3 for 6 sites in Nepal
Click on General Search in menu on right-hand side of screen to search archived
data.
Pak EPA Environmental Monitoring Program (EMS)
http://www.cpcb.nic.in/index.phphttp://www.ncit.gov.np/pollution/pollution.phphttp://www.ncit.gov.np/pollution/pollution.phphttp://www.cpcb.nic.in/index.php7/29/2019 Trans Air Pollution in Quetta
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Long-Range Transportation of ParticulateMatter (PM) and Trajectory
PM10 and PM2.5 can travel over 100 to 1000
kilometers downwind depending on themeteorological condition
This long-range transported PM always mixes
with the local emissions and affects ambient air
PM10 and PM2.5 levels
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A trajectory is the time integration of the position of a
parcel of air as it is transported by the wind.
The parcel's passive transport by the wind is
computed/reconstructed by the Hybrid Single ParticleLagrangian Integrated Trajectory (HYSPLIT) modelwhere the velocity vectors used are interpolated in both
space and time. (Draxler, R.R. and Rolph, G.D., 2003)
Trajectories may be integrated both forward andbackward in time
What is a trajectory?
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HYSPLIT Back Trajectory
Backward trajectories are commonly used to identifyair pollution source regions and specific sources byback computation starting from the receptor
This long-range transported PM always mixes with thelocal emissions and affects ambient air PM10 andPM2.5 levels
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Sources of Satellite Data and Imagery
Moderate Resolution Imaging Spectroradiometer (MODIS) description: http://modis-
atmos.gsfc.nasa.gov/
MODIS Rapid Response System: http://rapidfire.sci.gsfc.nasa.gov/
MODIS direct broadcast site: http://eosdb.ssec.wisc.edu/modisdirect/
MODIS Level 2 LAADS data browser:
http://ladsweb.nascom.nasa.gov/browse_images/l2_browser.html
The Smog Blog: http://alg.umbc.edu/usaq/NASA Earth Observatory: http://earthobservatory.nasa.gov/
NASA Visible Earth: http://visibleearth.nasa.gov/
NASA Giovanni: http://daac.gsfc.nasa.gov/techlab/giovanni
European Space Agency (ESA) Observing the Earth: http://www.esa.int/esaEO/index.html
Tropospheric Emission Monitoring Internet Service (European): http://www.temis.nl/
Satellite Products for Europe (German Remote Sensing Data Center):
http://www.dlr.de/caf/en/desktopdefault.aspx/tabid-2683/4049_read-6052/
India Meteorological Department Satellite Images and Products (INSAT satellite):
http://www.imd.ernet.in/section/satmet/dynamic/insat.htm
EUMETSAT Image Gallery (Europe and Africa):http://www.eumetsat.int/Home/Main/Image_Gallery/Real-time_Images/index.htm
True color 05-02-2006
http://modis-atmos.gsfc.nasa.gov/http://modis-atmos.gsfc.nasa.gov/http://rapidfire.sci.gsfc.nasa.gov/http://eosdb.ssec.wisc.edu/modisdirect/http://ladsweb.nascom.nasa.gov/browse_images/l2_browser.htmlhttp://alg.umbc.edu/usaq/http://earthobservatory.nasa.gov/http://visibleearth.nasa.gov/http://daac.gsfc.nasa.gov/techlab/giovannihttp://www.esa.int/esaEO/index.htmlhttp://www.temis.nl/http://www.dlr.de/caf/en/desktopdefault.aspx/tabid-2683/4049_read-6052/http://www.imd.ernet.in/section/satmet/dynamic/insat.htmhttp://www.eumetsat.int/Home/Main/Image_Gallery/Real-time_Images/index.htmhttp://www.eumetsat.int/Home/Main/Image_Gallery/Real-time_Images/index.htmhttp://www.eumetsat.int/Home/Main/Image_Gallery/Real-time_Images/index.htmhttp://www.eumetsat.int/Home/Main/Image_Gallery/Real-time_Images/index.htmhttp://www.imd.ernet.in/section/satmet/dynamic/insat.htmhttp://www.dlr.de/caf/en/desktopdefault.aspx/tabid-2683/4049_read-6052/http://www.dlr.de/caf/en/desktopdefault.aspx/tabid-2683/4049_read-6052/http://www.dlr.de/caf/en/desktopdefault.aspx/tabid-2683/4049_read-6052/http://www.dlr.de/caf/en/desktopdefault.aspx/tabid-2683/4049_read-6052/http://www.dlr.de/caf/en/desktopdefault.aspx/tabid-2683/4049_read-6052/http://www.temis.nl/http://www.esa.int/esaEO/index.htmlhttp://daac.gsfc.nasa.gov/techlab/giovannihttp://visibleearth.nasa.gov/http://earthobservatory.nasa.gov/http://alg.umbc.edu/usaq/http://ladsweb.nascom.nasa.gov/browse_images/l2_browser.htmlhttp://eosdb.ssec.wisc.edu/modisdirect/http://rapidfire.sci.gsfc.nasa.gov/http://modis-atmos.gsfc.nasa.gov/http://modis-atmos.gsfc.nasa.gov/http://modis-atmos.gsfc.nasa.gov/7/29/2019 Trans Air Pollution in Quetta
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True color 05-02-2006
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AOT, 05-02-2006
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MODIS Terra 28-01-2007
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Transboundary fog
In winter season widespread fog and often thick fog occursin eastern India and northeastern Pakistan (especially theLahore Region)
The wide spread nature of the fog can be seen using
remote sensing satellite data
Fog extends approximately an area of 1500-2000 sq.kmextending from eastern India to northeastern Pakistan.
During the fog visibility reduces to ~100 m.
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Transboundary fog
India ranks fourth among countries producing SO2emissions
This part is the most industrialized part of subcontinent
During winter this region is generally in the influence ofhigh pressure system resulting in dry seasons and low windspeeds
Analysis of the aerosols samples were performed in 1999onwards
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METEOSAT IMAGE SHOWING FOG OVER INDIAAND NORTHERN PAKISTAN
INDIAPAKISTAN
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Major Thermal Power Plants inIndia
According to CentralElectricity Authority ofIndia, there are 83 coalfired thermal powerplants
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Experimental Methods
The aerosol samples are collected on Whatman 41 filterpapers using high volume samplers.
The samples are collected at Lahore from 8 A.M to 8 PM
and from 8 PM to 8 A.M
The flow rate was controlled with Sieria mass flowcontroller at a rate of 0.7 m3/min.
An aliquot of the filter was extracted in double distilled
deionized water and analyzed for SO42- NO3- by ion-chromatograph using a Dionex Model 500 equipped withPeaknet software
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SO42-
NO3-
Se x 103
As x 103
Sb x 103
No. of Days
Concentrations in ug/m3 of SO42- , NO3
- , Se, As, and
Sb in 12 hour samples at Lahore, Pakistan.
1 2 3 4 5 610
40
70
100
35
20
50
6
10
14
5
15
25
0
20
40
60
Sb x 103
FogClear
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As x 103
NO3-
SO4-2
Se x 103
SO4-2/Se
No. of Days
Concentrations in ug/m3 of SO4 2, NO
3
-, Se and SO4
- 2/Se ratios inaerosol samples at Lahore, Pakistan.
FogFog Clear
Concentrationg/m3
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The SO4-2 / Se ratios were suggestive of long-range
transport from several hundred kms away inneighbouring India.
Such high concentrations pose a serious health
risk and require a more detailed study on long-termbasis.
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The SO4-2 concentration varied from 7.29 ug/m3 to 41.89
ug/m3
with an average 18.98 ug/m3
for the period. Se concentration varied from below the detection limit (