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[Emission Characteristics of Wind-Eroded Dust from Concrete Batching Plants in Beijing].
Li, Bei-Bei; Han, Kai-Li; Qin, Jian-Ping; Wang, Xin; Song, Bo; Huang, Yu-Hu; Zhang, Chun-Lai.
Afiliação
  • Li BB; College of Resource Environment and Tourism, Capital Normal University, Beijing 100048, China.
  • Han KL; National Engineering Research Center of Urban Environmental Pollution Control, Beijing Municipal Research Institute of Environmental Protection, Beijing 100037, China.
  • Qin JP; National Engineering Research Center of Urban Environmental Pollution Control, Beijing Municipal Research Institute of Environmental Protection, Beijing 100037, China.
  • Wang X; Hebei Sailhero Environmental Protection Hi-tech Co., Ltd., Shijiazhuang 050035, China.
  • Song B; National Engineering Research Center of Urban Environmental Pollution Control, Beijing Municipal Research Institute of Environmental Protection, Beijing 100037, China.
  • Huang YH; China National Environmental Monitoring Centre, Beijing 100012, China.
  • Zhang CL; College of Resource Environment and Tourism, Capital Normal University, Beijing 100048, China.
Huan Jing Ke Xue ; 39(9): 4078-4085, 2018 Sep 08.
Article em Zh | MEDLINE | ID: mdl-30188048
Concrete batching plants are a typical source of fugitive dust in Beijing. In this study, two concrete batching plants in Beijing were used to test wind erosion of dust with a Portable In-suit Wind Erosion Laboratory (PI-SWERL) designed by the Desert Research Institute (DRI). Sand and aggregate storage piles and paved roads in concrete batching plants were tested to determine the emission characteristics of wind eroded dust. Combining the frequencies of disturbance of storage piles and paved road surface with local meteorological data, localized wind erosion dust emission factors of PM2.5 were established. Results demonstrate that:①There are small differences in daily average emission factors for PM2.5 between the aggregate warehouse entrance area, concrete loading area, social road import area, and concrete batching plant entrance area, with these being 0.45, 0.41, 0.31, and 0.30 kg·(hm2·d)-1, respectively. ②Daily average emission factors for PM2.5 of coarse stone, fine stone, coarse sand, and fine sand storage piles are 0.10, 0.12, 0.26, and 2.02 kg·(hm2·d)-1, respectively. Emission factors of fine sand storage piles are 20.5, 16.8, and 7.7 times greater than those of coarse stone, fine stone, and coarse sand, respectively, and spring emission factors are 6.4, 3.4, and 1.3 times greater than those of summer, autumn, and winter, respectively. ③Daily average emission factors for PM2.5 of storage piles and paved roads are 1.13 and 0.37 kg·(hm2·d)-1, respectively 3.9 and 1.3 times higher than the wind erosion factor from storage piles from AP-42 files (c11s12 concrete batching, 1995); the uncertainty range of the emission factor is 34%-92%. ④It is recommended to strengthen watering, sweeping, and cleaning of paved roads, and to ensure fully enclosed storage and use of spray water to reduce wind erosion of dust from storage piles, especially from fine sand piles.
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Texto completo: 1 Base de dados: MEDLINE Idioma: Zh Ano de publicação: 2018 Tipo de documento: Article

Texto completo: 1 Base de dados: MEDLINE Idioma: Zh Ano de publicação: 2018 Tipo de documento: Article