Loading…
Speciated PM10 Emission Inventory for Delhi, India
Emission inventories can serve as a basis for air quality management programs. The focus has been mainly on building inventories for criteria pollutants including particulate matter (PM). Control efforts in developing countries are mostly limited to total suspended particles (TSP) and/or PM 10 . Sin...
Saved in:
Published in: | Aerosol and air quality research 2014, Vol.14 (5), p.1515-1526 |
---|---|
Main Authors: | , , , |
Format: | Article |
Language: | English |
Citations: | Items that cite this one |
Online Access: | Get full text |
Tags: |
Add Tag
No Tags, Be the first to tag this record!
|
Summary: | Emission inventories can serve as a basis for air quality management programs. The focus has been mainly on building inventories for criteria pollutants including particulate matter (PM). Control efforts in developing countries are mostly limited to total suspended particles (TSP) and/or PM
10
. Since the adverse effects of PM
10
depend on its chemical composition, it is important to control emissions of toxic species. The first step is to identify key pollution sources and estimate quantities of various chemical species in emissions. This paper presents a speciated PM
10
emission inventory for Delhi, the capital and one of the most polluted cities in India. An established PM
10
inventory for Delhi in conjunction with source profiles was used to estimate emissions of major PM
10
components including organic and elemental carbon (OC and EC, respectively), sulphates (SO
4
2–
), and nitrates (NO
3
–
), as well as selected toxic trace metals (i.e., Pb, Ni, V, As, and Hg), some of which are subject to India’s National Ambient Air Quality Standards (NAAQS). For the base year of 2007, emission estimates for PM
10
mass, OC, EC, SO
4
2–
, and NO
3
–
are 140, 22, 6.4, 2.8, and 2.1 tonnes/day (TPD; 1 tonne = 1000 kg), respectively. Emissions of Pb, Ni, V, As, and Hg are estimated to be 203, 43, 37, 26, and 9.4 kg/day, respectively. This inventory underestimated Pb and Hg emissions because sources of PM
10
from unorganized secondary lead smelters are not specifically identified and gas-to-particle conversion of Hg is not accounted for. |
---|---|
ISSN: | 1680-8584 2071-1409 |
DOI: | 10.4209/aaqr.2013.02.0047 |