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Biomass burning in Asia: Annual and seasonal estimates and atmospheric emissions
Open accessAbstract
Estimates of biomass burning in Asia are developed to facilitate the modeling of Asian and global air quality. A survey of national, regional, and international publications on biomass burning is conducted to yield consensus estimates of “typical” (i.e., non‐year‐specific) estimates of open burning (excluding biofuels). We conclude that 730 Tg of biomass are burned in a typical year from both anthropogenic and natural causes. Forest burning comprises 45% of the total, the burning of crop residues in the field comprises 34%, and 20% comes from the burning of grassland and savanna. China contributes 25% of the total, India 18%, Indonesia 13%, and Myanmar 8%. Regionally, forest burning in Southeast Asia dominates. National, annual totals are converted to daily and monthly estimates at 1° × 1° spatial resolution using distributions based on AVHRR fire counts for 1999–2000. Several adjustment schemes are applied to correct for the deficiencies of AVHRR data, including the use of moving averages, normalization, TOMS Aerosol Index, and masks for dust, clouds, landcover, and other fire sources. Good agreement between the national estimates of biomass burning and adjusted fire counts is obtained (R 2 = 0.71–0.78). Biomass burning amounts are converted to atmospheric emissions, yielding the following estimates: 0.37 Tg of SO 2 , 2.8 Tg of NO x , 1100 Tg of CO 2 , 67 Tg of CO, 3.1 Tg of CH 4 , 12 Tg of NMVOC, 0.45 Tg of BC, 3.3 Tg of OC, and 0.92 Tg of NH 3 . Uncertainties in the emission estimates, measured as 95% confidence intervals, range from a low of ±65% for CO 2 emissions in Japan to a high of ±700% for BC emissions in India.
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“A significant amount of particulate emissions and trace gas emissions can be released, including CO 2 , SO 2 , carbon monoxide (CO), methane (CH 4 ), non-methane volatile organic compounds (NMHCs), nitrogen oxides (NO x ), ammonia (NH 3 ), black carbon (BC), and organic carbon (OC), especially for open field burning which is often practiced for residue clearance and biochar production [28,90].”
From Biomass and biofuels in China: Toward bioenergy resource potentials and their impacts on the environment (2018) · cites this paper as [90]
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“As aforementioned, open biomass burning has caused major air pollution in some areas [88,90].”
From Biomass and biofuels in China: Toward bioenergy resource potentials and their impacts on the environment (2018) · cites this paper as [90]
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Sorted by citations
Items 201–300 of 803
Jung, J., Lee, S., Kim, H., Kim, D., Lee, H., & Oh, S. (2014) · Atmospheric Environment · doi:10.1016/j.atmosenv.2014.03.010 · Cited by 81
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Carter, E. M., Archer‐Nicholls, S., Ni, K., Lai, A. M., Niu, H., Secrest, M. H., Sauer, S. M., Schauer, J. J., Ezzati, M., Wiedinmyer, C., et al. (2016) · Environmental Science & Technology · doi:10.1021/acs.est.6b00082 · Cited by 84
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“This agrees with past suggestions that the central provinces of Shandong, Jiangsu, Anhui and Henan (mainly in the North China Plain) are the source areas of most agricultural fire emissions (Huang et al., 2012; Qin and Xie, 2011; Streets et al., 2003).”
ResultPM2.5 emissions and source profiles from open burning of crop residues
Ni, H., Tian, J., Wang, X., Wang, Q., Han, Y., Cao, J., Long, X., Chen, L. ‐. A., Chow, J. C., Watson, J. G., et al. (2017) · Atmospheric Environment · doi:10.1016/j.atmosenv.2017.08.063 · Cited by 79
“Large amounts 56 of gases and particulate matter (PM) (Andreae and Merlet, 2001; Cheng et al., 2013; 57 Li et al., 2014; Streets et al., 2003) are emitted hat affect local and regional air quality, 58 with adverse effects on human health, visibility, and the Earth’s radiation balance 59 (Chow and…”
BackgroundInfluence of biomass burning from South Asia at a high-altitude mountain receptor site in China
Zheng, J., Hu, M., Du, Z., Shang, D., Gong, Z., Qin, Y., Fang, J., Gu, F., Li, M., Peng, J., et al. (2017) · Atmospheric chemistry and physics · doi:10.5194/acp-17-6853-2017 · Cited by 77
“In recent years, studies have presented convincing evidence for the transport route of air pollutants climbing over the Himalayas, especially during the pre-monsoon season, coinciding with the annual intensive fire season in South and Southeast Asia (Streets et al., 2003; Marinoni et al., 2010; Cong et al., 2015b).”
BackgroundHasnain, M. H., Javed, U., Ali, A., & Zafar, M. S. (2020) · Construction and Building Materials · doi:10.1016/j.conbuildmat.2020.121753 · Cited by 77
Michel, C., Liousse, C., Grégoire, J., Tansey, K. J., Carmichael, G. R., & Woo, J. (2005) · Journal of Geophysical Research Atmospheres · doi:10.1029/2004jd005461 · Cited by 77
“5° fire count data of 2001 (NOAA-AVHRR), and the TOMS-AI data as an additional information source [Streets et al., 2003; Woo et al., 2003].”
MethodUncertainties in estimating mercury emissions from coal-fired power plants in China
Wu, Y., Streets, D. G., Wang, S., & Hao, J. (2010) · Atmospheric chemistry and physics · doi:10.5194/acp-10-2937-2010 · Cited by 76
“Since 2003, Tsinghua University and Argonne National Laboratory have been developing a comprehensive multiple-year inventory of Hg emissions from anthropogenic sources in China, following the precedent of the Asian TRACE-P emission inventory (Streets et al., 2003a, 2003b).”
BackgroundInfluentialImpact of crop field burning and mountains on heavy haze in the North China Plain: a case study
Long, X., Tie, X., Cao, J., Huang, R., Feng, T., Li, N., Zhao, S., Tian, J., Li, G., & Zhang, Q. (2016) · Atmospheric chemistry and physics · doi:10.5194/acp-16-9675-2016 · Cited by 76
“The national annual average proportion of CFB to total residues is about 11–25 %(Cao et al., 2008; Hao Published by Copernicus Publications on behalf of the European Geosciences Union. and Liu, 1994; Streets et al., 2003; Wang and Zhang, 2008; Zhao et al., 2010).”
BackgroundMethodResultInfluentialSun, J., Shen, Z., Zhang, Y., Zhang, Q., Wang, F., Wang, T., Chang, X., Lei, Y., Xu, H., Cao, J., et al. (2019) · Fuel · doi:10.1016/j.fuel.2019.02.031 · Cited by 75
Impact of Open Burning of Crop Residues on Air Pollution and Climate Change in Indonesia
Andini, A., Bonnet, S., Rousset, P. L. A., & Hasanudin, U. (2018) · Current Science · doi:10.18520/cs/v115/i12/2259-2266 · Cited by 74
“As mentioned earlier, Streets et al.(5) had assessed emissions from biomass burning in Asia, including Indonesia.”
BackgroundMethodInfluentialJiang, P., Chen, X., Li, Q., Mo, H., & Li, L. (2020) · Journal of Cleaner Production · doi:10.1016/j.jclepro.2020.120806 · Cited by 75
Zhou, X., Gao, J. G., Wang, T., Wu, W.-S., & Wang, W. (2009) · Atmospheric Environment · doi:10.1016/j.atmosenv.2009.04.062 · Cited by 73
Kumar, A., Hakkim, H., Sinha, B., & Sinha, V. (2021) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2021.148064 · Cited by 72
Air pollutant emissions from straw open burning: A case study in Tianjin
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Woo, J., Streets, D. G., Carmichael, G. R., Tang, Y., Yoo, B., Lee, W., Thongboonchoo, N., Pinnock, S., Kurata, G., Uno, I., et al. (2003) · Journal of Geophysical Research Atmospheres · doi:10.1029/2002jd003200 · Cited by 72
“This information was combined into the ACE-Asia and TRACE-P Modeling and Emission Support System (ACESS) to support these field studies [Streets et al., 2003a, 2003b].”
BackgroundMethodInfluentialZhang, G., Li, J., Li, X. D., Yue, X., Guo, L., Tang, J., Lee, C. S. L., Liu, X., & Chen, Y. (2010) · Environmental Pollution · doi:10.1016/j.envpol.2010.07.036 · Cited by 74
“Eastern and Southern China are the important source region of anthropogenic pollutants, whereas Southeast Asia is an important source region of biomass burning emissions (Streets et al., 2003).”
BackgroundPavuluri, C. M., Kawamura, K., Swaminathan, T., & Tachibana, E. (2011) · Journal of Geophysical Research Atmospheres · doi:10.1029/2011jd015617 · Cited by 71
“In fact, biomass burning starts in January and the atmospheric concentrations of its emissions (e.g., CO) reach to medium level in February and a peak in March in this region [Streets et al., 2003].”
High-Resolution Mapping of Biomass Burning Emissions in Three Tropical Regions
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Long-lived atmospheric trace gases measurements in flask samples from three stations in India
Lin, X., Indira, N. K., Ramonet, M., Delmotte, M., Ciais, P., Bhatt, B. C., Reddy, M. V., Angchuk, D., Balakrishnan, S., Jorphail, S., et al. (2015) · Atmospheric chemistry and physics · doi:10.5194/acp-15-9819-2015 · Cited by 70
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“Emissions from biomass burning in Eastern India reach a maximum in spring (Duncan et al., 2003; Streets et al., 2003).”
BackgroundOn-road vehicle emission inventory and its spatio-temporal variations in North China Plain
Jiang, P., Xi, Z., & Li, L. (2020) · Environmental Pollution · doi:10.1016/j.envpol.2020.115639 · Cited by 69
Xie, M., Zhu, K., Wang, T., Yang, H., Zhuang, B., Li, S., Li, M., Zhu, X., & Ouyang, Y. (2014) · Atmospheric Environment · doi:10.1016/j.atmosenv.2014.10.013 · Cited by 69
Jena, C., Ghude, S. D., Pfister, G. G., Chate, D. M., Kumar, R., Beig, G., Surendran, D. E., Fadnavis, S. S., & Lal, D. M. (2014) · Atmospheric Environment · doi:10.1016/j.atmosenv.2014.10.027 · Cited by 68
Chai, T., Carmichael, G. R., Sandu, A., Tang, Y., & Daescu, D. N. (2006) · Journal of Geophysical Research Atmospheres · doi:10.1029/2005jd005883 · Cited by 68
“The emission inventories implemented here are presented by Streets et al. [2003] and Woo et al. [2003].”
MethodLi, N., Fu, T., Cao, J., Lee, S., Huang, X., He, L., Ho, K., Fu, J. S., & Lam, Y. F. (2012) · Atmospheric Environment · doi:10.1016/j.atmosenv.2012.12.005 · Cited by 67
“Biomass burning emissions of OC and NMVOC precursors for East Asiawere from the 1 1 inventory developed by Streets et al. (2003).”
MethodSeasonal, interannual, and long-term variabilities in biomass burning activity over South Asia
Bhardwaj, P., Naja, M., Kumar, R., & Chandola, H. C. (2015) · Environmental Science and Pollution Research · doi:10.1007/s11356-015-5629-6 · Cited by 69
“Among Asian regions, the highest amount of biomass is burnt in Southeast Asia (about 45 %), majority of which is in the form of forest fires, followed by East Asia (about 25 %) and South Asia (about 23 %) where crop residue burning is dominant (Streets et al. 2003).”
BackgroundModeling black carbon and its potential radiative effects over the Tibetan Plateau
Ji, Z. (2016) · Advances in Climate Change Research · doi:10.1016/j.accre.2016.10.002 · Cited by 66
Zhang, T., Jong, M. C. D., Wooster, M. J., Xu, W., & Wang, L. (2020) · Atmospheric chemistry and physics · doi:10.5194/acp-20-10687-2020 · Cited by 65
“Streets et al. (2003) used a uniform BR of 17 % derived from 1970s data; however, more recent studies often make use of regionally varying fractions.”
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“It may cause the people suffering from chronic disease related to respiratory system, heart and lung problems, blood, eye, and skin irritation (Singh et al. 2009, 2011; Mittal et al. 2009; Pathak et al. 2010; Long et al. 1998; Treets et al. 2003).”
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“The seasonal variations of emissions for the residential sector were dependent on monthly mean temperatures (Streets et al., 2003b).”
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“Biomass burning emissions of POC (9.8 GgC y 1) and NMVOC (34.0 Gg y 1) were taken from the inventories developed by He et al. (2011) and Streets et al. (2003).”
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Atmospheric Stressors: Challenges and Coping Strategies
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“In Asia, MODIS fire counts and GFED4 CO emissions show strong interannual variations, and high values often coincide with EI Niño years [64].”
BackgroundInfluentialConcrete made with partially substitution corn cob ash: A review
Ahmad, J., Arbili, M. M., Alabduljabbar, H., & Deifalla, A. F. (2023) · Case Studies in Construction Materials · doi:10.1016/j.cscm.2023.e02100 · Cited by 62
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Estimate of radiative forcing of Asian biomass‐burning aerosols during the period of TRACE‐P
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“only on the BC and OC aerosols because of the high emission amount and the tendency to influence and affect the climate [Ferek et al., 1998; Streets et al., 2003b; Reddy et al., 2005].”
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Spatiotemporal variation in nonagricultural open fire emissions in China from 2000 to 2007
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“i Values are derived from results of the Editorial Board of China Agriculture Yearbook [2002, 2003, 2004], Streets et al. [2003] , and Cao et al. [2006]”
BackgroundMethodInfluentialChang, C., Liu, C., & Tseng, P.-Y. (2013) · Aerosol and Air Quality Research · doi:10.4209/aaqr.2012.06.0150 · Cited by 60
“The burning of crop residues in fields is one of the most significant activities of global biomass burning (excluding biofuels; Streets et al. , 2003), and contributes substantially to air pollution.”
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The Spatial–Temporal Variation of Tropospheric NO2 over China during 2005 to 2018
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“The strong increase in NO2 pollution in China, especially over eastern China, is due to an increase in industrial development and traffic [15,16].”
BackgroundSong, W., Liu, X.-Y., Wang, Y., Tong, Y., Bai, Z., & Liu, C. (2019) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2019.134515 · Cited by 60
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Local to global perspectives on forest and land fires in Southeast Asia
Murdiyarso, D., & Lebel, L. (2006) · Mitigation and Adaptation Strategies for Global Change · doi:10.1007/s11027-006-9055-4 · Cited by 63
“Streets et al. (2003) estimated that, for all of Asia, forest burning comprises 45% and crop residues in field 34% of openly burnt biomass.”
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“5 estimated in the above study; this is not an unreasonable proportion as it is estimated that Bangladesh burns at least 37 tons of biomass each year, making it another significant source of PMs (Streets et al., 2003).”
Particle size characteristics of levoglucosan in ambient aerosols from rice straw burning
Lee, J. J., Engling, G., Lung, S. C., & Lee, K.-Y. (2008) · Atmospheric Environment · doi:10.1016/j.atmosenv.2008.07.047 · Cited by 57
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“In addition, a larger amount of biomass is burned from forests in northern Indochina compared with the south (Streets et al. , 2003).”
Tian, J., Ni, H., Han, Y., Shen, Z., Wang, Q., Long, X., Zhang, Y., & Cao, J. (2018) · Atmospheric Environment · doi:10.1016/j.atmosenv.2018.07.031 · Cited by 57
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“[70], the highest emissions that contribute to high particulate matter in the air occur in March.”
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On the sensitivity of radiative forcing from biomass burning aerosols and ozone to emission location
Naïk, V., Mauzerall, D. L., Horowitz, L. W., Schwarzkopf, M. D., Ramaswamy, V., & Oppenheimer, M. (2007) · Geophysical Research Letters · doi:10.1029/2006gl028149 · Cited by 54
“While for most regions the percentage of OC emissions is higher than BC emissions relative to the global total emissions, in India, the BC emissions percentage is higher than OC emissions percentage due to the dominance of agricultural waste burning (Figure 1) [Streets et al., 2003].”
BackgroundLutsch, E., Strong, K., Jones, D. B. A., Blumenstock, T., Conway, S., Fisher, J. A., Hannigan, J. W., Hase, F., Kasai, Y. J., Mahieu, E., et al. (2020) · Atmospheric chemistry and physics · doi:10.5194/acp-20-12813-2020 · Cited by 65
“The springtime enhancements of HCN are due to the earlier onset of East and Southeast Asian biomass burning, which occurs annually from March to May (Streets et al., 2003).”
BackgroundInfluentialAir pollution from biomass burning in India
Tripathi, S. N., Yadav, S., & Sharma, K. (2024) · Environmental Research Letters · doi:10.1088/1748-9326/ad4a90 · Cited by 70
“(Streets et al 2003, Taylor 2010).”
BackgroundChemical characterization of aerosols at the summit of Mountain Tai in Central East China
Deng, C., Zhuang, G., Huang, K., Li, J., Zhang, R., Wang, Q., Liu, T., Sun, Y., Guo, Z., Fu, J. S., et al. (2011) · Atmospheric chemistry and physics · doi:10.5194/acp-11-7319-2011 · Cited by 54
“Biomass burning includes those from grassland, forest, and crop residue, among which more than 60 % are from crop residue burning in the world (Streets et al., 2003).”
BackgroundAromatic acids as biomass-burning tracers in atmospheric aerosols and ice cores: A review
Wan, X., Kawamura, K., Ram, K., Kang, S., Loewen, M., Gao, S., Wu, G., Fu, P., Zhang, Y., Bhattarai, H., et al. (2019) · Environmental Pollution · doi:10.1016/j.envpol.2019.01.028 · Cited by 54
“However, BB is found to be a significant source of organic particles, accounting for up to 20e60% (by mass) of atmospheric aerosols (Streets et al., 2003; Titos et al., 2017; Zhang et al., 2017).”
BackgroundTropospheric ozone pollution in India: effects on crop yield and product quality
Singh, A. A., & Agrawal, S. B. (2016) · Environmental Science and Pollution Research · doi:10.1007/s11356-016-8178-8 · Cited by 52
“According to Garg et al. (2001), NOx emissions over the Indian region were growing at an annual rate of 5.5% year−1, while Streets et al. (2003) found an increase rate of 6.5% year−1, displaying an increasing trend.”
BackgroundInfluentialRejoinder to Comments on Minasny et al., 2017 Soil carbon 4 per mille Geoderma 292, 59–86
Minasny, B., Arrouays, D., McBratney, A. B., Angers, D. A., Chambers, A., Chaplot, V. A. M., Chen, Z., Cheng, K., Das, B. S., Field, D. J., et al. (2017) · Geoderma · doi:10.1016/j.geoderma.2017.05.026 · Cited by 53
Rabiei‐Dastjerdi, H., Mohammadi, S., Saber, M., Amini, S., & McArdle, G. (2022) · Remote Sensing · doi:10.3390/rs14071725 · Cited by 51
“A severe increase in NO2 pollution is because of the growing number of industrial sites and traffic volume [15].”
BackgroundWang, J., Xi, F., Liu, Z., Bing, L., Alsaedi, A., Hayat, T., Ahmad, B., & Guan, D. (2018) · Journal of Cleaner Production · doi:10.1016/j.jclepro.2018.01.206 · Cited by 51
“Streets et al. (2003) estimated that CO2 and CH4 emissions from biomass 109 open burning were approximately 300 Mt CO2-eq.”
BackgroundMethodAlberto, M. C., Waßmann, R., Gummert, M., Buresh, R. J., Quilty, J. R., Correa, T. Q., Centeno, C. A. R., & Oca, G. M. (2015) · Field Crops Research · doi:10.1016/j.fcr.2015.10.004 · Cited by 50
Suthawaree, J., Kato, S., Okuzawa, K., Kanaya, Y., Pochanart, P., Akimoto, H., Wang, Z., & Kajii, Y. (2010) · Atmospheric chemistry and physics · doi:10.5194/acp-10-1269-2010 · Cited by 50
Nguyen, T. N. T., Pham, H. V., Lasko, K., Bui, M. T., Laffly, D., Jourdan, A., & Bui, Q. H. (2019) · Environmental Pollution · doi:10.1016/j.envpol.2019.113106 · Cited by 50
Vongruang, P., & Pimonsree, S. (2020) · Atmospheric Environment · doi:10.1016/j.atmosenv.2020.117414 · Cited by 50
Identification of NO2 and SO2 Pollution Hotspots and Sources in Jiangsu Province of China
Wang, Y., Ali, M. A., Bilal, M., Qiu, Z., Mhawish, A., Almazroui, M., Shahid, S., Islam, M. N., Zhang, Y., & Haque, M. N. (2021) · Remote Sensing · doi:10.3390/rs13183742 · Cited by 49
“A significant increase in industrial development and traffic over eastern China is another important reason for increasing NO2 [74,75].”
Biomass burning sources and their contributions to the local air quality in Hong Kong
Chan, K. L. (2017) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2017.04.091 · Cited by 49
Li, X., Jiang, L., Bai, Y., Yang, Y., Liu, S., Chen, X., Xu, J. X., Liu, Y., Wang, Y., Guo, X., et al. (2018) · Atmospheric Research · doi:10.1016/j.atmosres.2018.10.010 · Cited by 49
“of sugars, but also the sources of EC, PAHs, CO, NOx and VOCs (Duan et al. 2004; Streets et al. 2003).”
BackgroundSaccharides as Particulate Matter Tracers of Biomass Burning: A Review
Vincenti, B., Paris, E., Carnevale, M., Palma, A., Guerriero, E., Borello, D., Paolini, V., & Gallucci, F. (2022) · International Journal of Environmental Research and Public Health · doi:10.3390/ijerph19074387 · Cited by 48
“Accounting for 18–38% of the fine OA [16], biomass burning significantly contributes to the emission of gases and toxic compounds in the atmosphere [17,18], and it has been identified as a biofuel that may contribute to the worsening of both outdoor and indoor air quality [19].”
BackgroundTang, H., Liu, G., Zhu, J., Han, Y. M., & Kobayashi, K. (2012) · Atmospheric Research · doi:10.1016/j.atmosres.2012.10.030 · Cited by 48
Xing, X., Zhou, Y. C., Lang, J., Chen, D., Cheng, S., Han, L., Huang, D., & Zhang, Y. (2018) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2018.01.048 · Cited by 48
Kalita, G., Kunchala, R. K., Fadnavis, S. S., & Kaskaoutis, D. G. (2020) · Atmospheric Research · doi:10.1016/j.atmosres.2020.105064 · Cited by 48
Tang, Y., Carmichael, G. R., Horowitz, L. W., Uno, I., Woo, J., Streets, D. G., Dabdub, D., Kurata, G., Sandu, A., Allan, J. D., et al. (2004) · Journal of Geophysical Research Atmospheres · doi:10.1029/2004jd004513 · Cited by 48
“The portion of emissions from gasoline in Asia is generally smaller than that in the United States [Streets et al., 2003a].”
BackgroundAnalysis of source regions for smoke events in Singapore for the 2009 El Nino burning season
Atwood, S. A., Reid, J. S., Kreidenweis, S. M., Yu, L. E., Salinas, S. V., Chew, B. N., & Balasubramanian, R. (2013) · Atmospheric Environment · doi:10.1016/j.atmosenv.2013.04.047 · Cited by 47
Chi, K. H., Lin, C., Yang, C.-F. O., Wang, J., Lin, N. H., Sheu, G., & Lee, C.-T. (2010) · Environmental Science & Technology · doi:10.1021/es1000984 · Cited by 47
Zhu, J., Xia, X., Wang, J., Zhang, J., Wiedinmyer, C., Fisher, J. A., & Keller, C. A. (2017) · Journal of Geophysical Research Atmospheres · doi:10.1002/2016jd025793 · Cited by 47
Zhang, S., Deng, M., Shan, M., Zhou, C., Liu, W., Xu, X., & Yang, X. (2019) · Energy Policy · doi:10.1016/j.enpol.2019.01.038 · Cited by 47
Yao, W., Zhao, Y., Chen, R., Wang, M., Song, W.-W., & Yu, D. (2023) · Processes · doi:10.3390/pr11030853 · Cited by 50
Satellite and surface-based remote sensing of Southeast Asian aerosols and their radiative effects
Feng, N., & Christopher, S. A. (2012) · Atmospheric Research · doi:10.1016/j.atmosres.2012.02.018 · Cited by 46
Harvest season, high polluted season in East China
Huang, X., Song, Y., Li, M., Li, J., & Zhu, T. (2012) · Environmental Research Letters · doi:10.1088/1748-9326/7/4/044033 · Cited by 46
Mehmood, K., Wu, Y., Wang, L., Yu, S., Li, P., Chen, X., Li, Z., Zhang, Y., Li, M., Liu, W., et al. (2020) · Atmospheric chemistry and physics · doi:10.5194/acp-20-2419-2020 · Cited by 46
Zhang, Y., Zhang, Z., Chan, C., Engling, G., Sang, X.-F., Shi, S., & Wang, X. (2011) · Environmental Science and Pollution Research · doi:10.1007/s11356-011-0548-7 · Cited by 46
“biofuels, including crop residues, wood, and domestic waste, are the major sources of aerosol particles in this region and specific chemical species, such as carbon monoxide, nitrogen oxides, black carbon, and organic carbon (OC) (Streets et al. 2003; Duncan et al. 2003).”
BackgroundThe Extent and Management of Crop Stubble
Kumar, P., Kumar, S., & Joshi, L. (2014) · SpringerBriefs in environmental science · doi:10.1007/978-81-322-2014-5_2 · Cited by 45
Tanimoto, H., Sawa, Y., Yonemura, S., Yumimoto, K., Matsueda, H., Uno, I., Hayasaka, T., Mukai, H., Tohjima, Y., Tsuboi, K., et al. (2008) · Atmospheric chemistry and physics · doi:10.5194/acp-8-3867-2008 · Cited by 45
“As already mentioned, Streets et al. (2006) have recently updated their previous estimates (Streets et al., 2003a) for Chinese anthropogenic emissions to 142 Tg, resulting in a total emission (including biomass burning) of 158 Tg for the year 2001.”
Background
Metadata
- Authors
- Streets, D. G., Yarber, K. F., Woo, J. ‐., & Carmichael, G. R.
- Affiliations
- Argonne National Laboratory (US)
- University of Iowa (US)
- Venue
- Global Biogeochemical Cycles
- Publisher
- American Geophysical Union (AGU)
- Published
- 2003-10-15
- Volume
- 17
- Issue
- 4
- ISSN
- 0886-6236 (ISSN-L)
- 1944-9224
- OpenAlex
- W2084089284
- Cited by
- 807
- References
- 32
- Citations by year
- 2026: 19 · 2025: 21 · 2024: 44 · 2023: 43 · 2022: 60 · 2021: 50 · 2020: 57 · 2019: 53 · 2018: 54 · 2017: 52 · 2016: 41 · 2015: 44 · 2014: 44 · 2013: 34 · 2012: 39
- FWCI
- 13.32
- Type
- journal article
- Language
- en
- Open access
- bronze
- doi.org
- Locations
- Global Biogeochemical Cycles (publishedVersion)
- NCHU Institutional Repository CRIS (submittedVersion)
- Funders
- U.S. Department of Energy
- National Aeronautics and Space Administration
- University of Chicago
- Argonne National Laboratory
- Topics
- Physical Sciences › Environmental Science › Global and Planetary Change › Fire effects on ecosystems
- Physical Sciences › Earth and Planetary Sciences › Atmospheric Science › Atmospheric chemistry and aerosols
- Physical Sciences › Environmental Science › Global and Planetary Change › Atmospheric aerosols and clouds
- Keywords
- biomass burning, forest burning, crop residue burning, emission estimates, TOMS aerosol index, black carbon, organic carbon, sulfur dioxide, nitrogen oxides, methane, non-methane volatile organic compounds, air quality modeling, emission uncertainty, seasonal and spatial distribution
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