China PAH Emission Inventory
China National Emission [xls]
China Provincal Emission [xls]
China County Emission [xls]
China 1kmx1km Emission [Arcraster]
The emission factors for indoor straw combustion are a major data gap for estimating
the polycyclic aromatic hydrocarbon (PAH) emissions in China. The emission factors
for open-fire straw burning were borrowed from our previous study and a rough estimate
has been developed. As one of the most important emission sources in China, Q1
the emission factors for indoor straw combustion needed to be determined and revised
accurately. In this study, a representative straw in rural China was collected and burned
in similar conditions with those used by countryside families. The smoke producedwas
sampled and the PAH concentrations were analyzed by gas chromatography¨Cmass selective
detection (GC-MSD), andmuch higher emission factorswere found. Based on the
newlymeasured emission factors, the emission amount from indoor straw combustion
was updated. In addition, recently published emission factors were compiled in a comprehensive
database and some new sources were included. Additionally, the emission
inventory was extended to cover the period from 1950 to 2005 and upgraded to a scale
resolution of one kilometer. In the updated inventory, the total quantity of 16 PAHs emitted
from Chinawas 116,000 tons in 2003, with indoor strawand firewood combustions as
themost important sources. Although vehicular emission contributed a relatively small
percentage of the total emission, it was still one of the major sources in the urban areas
of China. The total PAHemission increased continuously for four decades, starting from
1950, but fluctuated since 1990 due to variations in coke production.
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Global PAH Emission Inventory
Global Emission [xls]
Global 1degx1deg Emission [rar]
The global atmospheric emissions of the 16 polycyclic aromatic hydrocarbons (PAHs) listed as the US EPA
priority pollutants were estimated using reported emission activity and emission factor data for the
reference year 2004. A database for emission factors was compiled, and their geometric means and
frequency distributions applied for emission calculation and uncertainty analysis, respectively. The
results for 37 countries were compared with other PAH emission inventories. It was estimated that the
total global atmospheric emission of these 16 PAHs in 2004 was 520 giga grams per year (Gg/y) with
biofuel (56.7%), wildfire (17.0%) and consumer product usage (6.9%) as the major sources, and China
(114 Gg/y), India (90 Gg/y) and United States (32 Gg/y) were the top three countries with the
highest PAH emissions. The PAH sources in the individual countries varied remarkably. For example,
biofuel burning was the dominant PAH source in India, wildfire emissions were the dominant PAH source
in Brazil, while consumer products were the major PAH emission source in the United States. In China, in
addition to biomass combustion, coke ovens were a significant source of PAHs. Globally, benzo(a)pyrene
accounted for 0.05% to 2.08% of the total PAH emission, with developing countries accounting for
the higher percentages. The PAH emission density varied dramatically from 0.0013 kg km2/y in the
Falkland Islands to 360 kg km2/y in Singapore with a global mean value of 3.98 kg km2/y. The atmospheric
emission of PAHs was positively correlated to the country¡¯s gross domestic product and negatively
correlated with average income. Finally, a linear bivariate regression model was developed to
explain the global PAH emission data.
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