Pollution Characteristics and Emission Coefficients for Volatile Organic Compounds from the Synthetic Leather Industry in Zhejiang Province

被引:3
|
作者
Xu J.-Q. [1 ]
Wang Z.-M. [2 ]
Song S. [1 ]
Xu Z.-R. [2 ]
Yao Y. [2 ]
机构
[1] College of Environment, Zhejiang University of Technology, Hangzhou
[2] Zhejiang Province Academy of Environmental Science, Hangzhou
来源
Huanjing Kexue/Environmental Science | 2019年 / 40卷 / 08期
关键词
Emission characteristics; Emission coefficient; Material balance; Synthetic leather; Volatile organic compounds(VOCs);
D O I
10.13227/j.hjkx.201812214
中图分类号
学科分类号
摘要
Based on the survey of 175 synthetic leather enterprises in Zhejiang Province, China, in 2014, this paper analyzes the control of volatile organic compounds (VOCs) and, ultimately, screened 161 key enterprises for further research. The results showed that most enterprises take measures to control waste gas; however, there is a distinct problem with the efficiency of exhaust gas collection. The industry used Solvent-based materials. The main VOC pollutants were DMF, toluene, methyl acetate, acetone, ethylacetate, and butanone. The VOC emission coefficient of the synthetic leather industry in Zhejiang was 0.168 kg•m-2. The industry includes polyurethane and polyvinyl chloride processes, for which VOC emission coefficients were 0.170 kg•m-2 and 0.142 kg•m-2, respectively. In addition, the emission coefficient of polyurethane wet processes was 0.191 kg•m-2 and that of dry processes was 0.179 kg•m-2. The emission coefficient for VOCs in post-treatment processes was 0.120 kg•m-2. © 2019, Science Press. All right reserved.
引用
收藏
页码:3463 / 3469
页数:6
相关论文
共 20 条
  • [1] Chen J.S., The development of regenerative catalytic combustion technology and it's treatment of VOCs from synthetic leather industry, pp. 5-6, (2017)
  • [2] Zhou H.F., The study of DMF pollution monitoring and assessment and comprehensive renovation of synthetic leather industries of some region in Zhejiang, pp. 18-29, (2011)
  • [3] Moorman W.J., Ahlers H.W., Chapin R.E., Et al., Prioritization of NTP reproductive toxicants for field studies, Reproductive Toxicology, 14, 4, pp. 293-301, (2000)
  • [4] Li L.M., Wang M.L., Sun X.L., Et al., Study on the relationship between the level of urinary monomethylfomamide and the injury of liver and kidney in workers exposed to dimethylfomamide, Chinese Journal of Industrial Hygiene and Occupational Diseases, 22, 4, pp. 270-271, (2004)
  • [5] Xia Y.T., Chen X.D., Wang C.S., Et al., Toxicity of N, N-dimethylformamide: a review of recent studies, Journal of Environment and Health, 28, 9, pp. 842-845, (2011)
  • [6] Senoh H., Aiso S., Arito H., Et al., Carcinogenicity and chronic toxicity after inhalation exposure of rats and mice to N, N-dimethylformamide, Journal of Occupational Health, 46, 6, pp. 429-439, (2004)
  • [7] Tong Z.M., Ding X.F., Shi J., Et al., Cross-sectional survey on dimethylfomamide occupational hazards in Kunshan city, Journal of Environmental & Occupational Medicine, 31, 8, pp. 621-623, (2014)
  • [8] Boeglin M.L., Wessels D., Henshel D., An investigation of the relationship between air emissions of volatile organic compounds and the incidence of cancer in Indiana counties, Environmental Research, 100, 2, pp. 242-254, (2006)
  • [9] Bo Y., Cai H., Xie S.D., Spatial and temporal variation of historical anthropogenic NMVOCs emission inventories in China, Atmospheric Chemistry and Physics, 8, 23, pp. 7297-7316, (2008)
  • [10] Jiang Y.Y., Sun M., Wu L., Environmental impacts of polyurethane synthetic leather production process, Guangdong Chemical Industry, 38, 7, (2011)