我国沿海机动车轮胎磨损橡胶微粒释放量初步估算

凌玮, 陈熙, 高翊尧, 沈茜, 田静毅, 安立会. 我国沿海机动车轮胎磨损橡胶微粒释放量初步估算[J]. 生态毒理学报, 2020, 15(1): 265-273. doi: 10.7524/AJE.1673-5897.20190418001
引用本文: 凌玮, 陈熙, 高翊尧, 沈茜, 田静毅, 安立会. 我国沿海机动车轮胎磨损橡胶微粒释放量初步估算[J]. 生态毒理学报, 2020, 15(1): 265-273. doi: 10.7524/AJE.1673-5897.20190418001
Ling Wei, Chen Xi, Gao Yiyao, Shen Qian, Tian Jingyi, An Lihui. Preliminary Estimates of Microplastics Emission from Vehicle Tires along the Coast in China[J]. Asian Journal of Ecotoxicology, 2020, 15(1): 265-273. doi: 10.7524/AJE.1673-5897.20190418001
Citation: Ling Wei, Chen Xi, Gao Yiyao, Shen Qian, Tian Jingyi, An Lihui. Preliminary Estimates of Microplastics Emission from Vehicle Tires along the Coast in China[J]. Asian Journal of Ecotoxicology, 2020, 15(1): 265-273. doi: 10.7524/AJE.1673-5897.20190418001

我国沿海机动车轮胎磨损橡胶微粒释放量初步估算

    作者简介: 凌玮(1994-),男,硕士研究生,研究方向为环境科学,E-mail:772077773@qq.com
  • 基金项目:

    国家科技重大专项(2018ZX07111006);国家自然科学基金资助项目(21577137)

  • 中图分类号: X171.5

Preliminary Estimates of Microplastics Emission from Vehicle Tires along the Coast in China

  • Fund Project:
  • 摘要: 环境微塑料是当前环境领域关注热点,并被列为环境与生态科学研究领域的关键科学问题。机动车轮胎因与路面摩擦而向环境不断释放橡胶微粒,因此,机动车轮胎经摩擦释放的橡胶微粒被认为是环境微塑料主要初生源之一。基于我国公路总里程位居世界首位和机动车保有量占世界第二的实际情况,以2016年为基准年,采用经验公式方法估算了我国沿海地区机动车轮胎释放的橡胶微粒水平。结果表明,我国沿海机动车轮胎摩擦释放橡胶微粒量为189 965.91 t,其中广东省释放量最高,占全国沿海省(市)释放总量的24.09%以上,而广西省释放量最小,占比为1.41%。另外,土壤是轮胎橡胶微粒的主要释放去向,橡胶微粒对土壤环境产生的潜在影响需及早引起关注。
  • 加载中
  • Jabeen K, Su L, Li J, et al. Microplastics and mesoplastics in fish from coastal and fresh waters of China[J]. Environmental Pollution, 2017, 221:141-149
    Cózar A, Echevarría F, González-Gordillo J I, et al. From the Cover:Plastic debris in the open ocean[J]. Proceedings of the National Academy of Sciences of the United States of America, 2014, 111(28):10239-10244
    Wu W M, Yang J, Criddle C S. Microplastics pollution and reduction strategies[J]. Frontiers of Environmental Science and Engineering, 2017, 11:6
    Qian X Y. Characteristics of secondary salinization of vegetable soil in plastic film greenhouse[J]. Soil and Fertilizer Sciences in China, 2017(2):73-79
    Farrell P, Nelson K. Trophic level transfer of microplastic:Mytilus edulis (L.) to Carcinus maenas (L.)[J]. Environmental Pollution, 2013, 177:1-3
    United Nations Environment Programme (UNEP). Resolution of marine waste and microplastics in the Third UN Environment Conference[R]. Nairobi:UNEP, 2018
    Masura J, Baker J, Foster G, et al. Laboratory methods for the analysis of microplastics in the marine environment:Recommendations for quantifying synthetic particles in waters and sediments[R]. Washington D C:U.S. Department of Commerce, 2015
    王彤,胡献刚,周启星.环境中微塑料的迁移分布、生物效应及分析方法的研究进展[J].科学通报, 2018, 63(4):385-395

    Wang T, Hu X G, Zhou Q X. The research progress in migration, distribution, biological effects and analytical methods of microplastics[J]. Chinese Science Bulletin, 2018, 63(4):385-395(in Chinese)

    Hartmann B N, Hüffer T, Thompson C R. Are we speaking the same language?Recommendations for a definition and categorization framework for plastic debris[J]. Environmental Science and Technology, 2019, 53(3):1039-1047
    Siegfried M, Koelmans A A, Besseling E, et al. Export of microplastics from land to sea. A modelling approach[J]. Water Research, 2017, 127:249-257
    Sundt P, Syversen F, Skogesal O, et al. Primary microplastic pollution:Measures and reduction potentials in Norway[R]. Trondheim:Norwegian Environment Agency, 2016
    Kole P J, Löhr A J, van Belleghem F, et al. Wear and tear of tyres:A stealthy source of microplastics in the environment[J]. International Journal of Environmental Research and Public Health, 2017, 14(1265):1-31
    中国橡胶工业协会.中国橡胶工业年鉴[M].北京:中国商业出版社, 2017:79-96
    丁玉华.建议完善和加强轮胎产品标准[J].中国橡胶, 2017, 33(6):7
    国家海洋局.中国海洋统计年鉴[M].北京:中国统计出版社, 2016:27-43 State Oceanic Administration. China Marine Statistical Yearbook[M]. Beijing:China Statistics Press, 2016:27

    -43(in Chinese)

    中华人民共和国国家标准化管理委员会. GB/T3730. 1-2001汽车和挂车类型的术语和定义[S].北京:中国标准出版社, 2001 Standardization Administration of the People's Republic of China. GB/T3730.1-2001

    Motor vehicles and trailers-Types-Terms and definitions[S]. Beijing:Standards Press of China, 2001(in Chinese)

    中华人民共和国公安部. GA802-2014机动车类型术语和定义[S].北京:中国标准出版社, 2014 Ministry of Public Security of the People's Republic of China. GA802-2014 Types of motor vehicle-Terms and definitions[S]. Beijing:Standards Press of China, 2014

    (in Chinese)

    Verschoor A, de Poorter L, Dröge R, et al. Emission of microplastics and potential mitigation measures:Abrasive cleaning agents, paints and tyre wear[R]. Bilthoven:National Institute for Public Health and the Environment, 2016:1-73
    前瞻产业研究院. 2015-2020年中国成品油行业市场调研与投资预测分析报告[R].北京:前瞻产业研究院, 2015
    He D F, Luo Y M, Lu S B, et al. Microplastics in soils:Analytical methods, pollution characteristics and ecological risks[J]. Trends in Analytical Chemistry, 2018, 109:163-172
    United Nations Environment Programme (UNEP). Marine plastic debris and microplastics-Global lessons and research to inspire action and guide policy change[R]. Nairobi:UNEP, 2016
    Zhang W W, Zhang S F, Wang J Y, et al. Microplastic pollution in the surface waters of the Bohai Sea, China[J]. Environmental Pollution, 2017, 231(1):541-548
    Zhao J M, Ran W, Teng J, et al. Microplastic pollution in sediments from the Bohai Sea and the Yellow Sea, China[J]. Science of the Total Environment, 2018, 640-641:637-645
    Zhu L, Bai H, Chen B, et al. Microplastic pollution in North Yellow Sea, China:Observations on occurrence, distribution and identification[J]. Science of the Total Environment, 2018, 636:20-29
    Zhang C, Zhou H, Cui Y, et al. Microplastics in offshore sediment in the Yellow Sea and East China Sea, China[J]. Environment Pollution, 2019, 244:827-833
    刘涛,孙晓霞,朱明亮,等.东海表层海水中微塑料分布与组成[J].海洋与湖沼, 2018, 49(1):62-69

    Liu T, Sun X X, Zhu M L, et al. Distribution and composition of microplastics in the surface water of the east China sea[J]. Oceanologia et Limnologia Sinica, 2018, 49(1):62-69(in Chinese)

    Cai M, He H, Liu M, et al. Lost but can't be neglected:Huge quantities of small microplastics hide in the South China Sea[J]. Science of the Total Environment, 2018, 633:1206-1216
    Li R, Zhang L, Xue B, et al. Abundance and characteristics of microplastics in the mangrove sediment of the semi-enclosed Maowei Sea of the South China Sea:New implications for location, rhizosphere, and sediment compositions[J]. Environmental Pollution, 2019, 244:685-692
    Sommer F, Dietze V, Baum A, et al. Tire abrasion as a major source of microplastics in the environment[J]. Aerosol and Air Quality Research, 2018, 18(8):2014-2028
    杨婧婧,徐笠,陆安祥,等.环境中微(纳米)塑料的来源及毒理学研究进展[J].环境化学, 2018, 37(3):13-26

    Yang J J, Xu L, Lu A X, et al. Research progress on the sources and toxicology of micro (nano) plastics in environment[J]. Environment Chemistry, 2018, 37(3):13-26(in Chinese)

  • 加载中
计量
  • 文章访问数:  1879
  • HTML全文浏览数:  1879
  • PDF下载数:  84
  • 施引文献:  0
出版历程
  • 收稿日期:  2019-04-18

我国沿海机动车轮胎磨损橡胶微粒释放量初步估算

    作者简介: 凌玮(1994-),男,硕士研究生,研究方向为环境科学,E-mail:772077773@qq.com
  • 1. 东北大学资源与土木工程学院, 沈阳 110819;
  • 2. 东北大学秦皇岛分校资源与材料学院, 秦皇岛 066004;
  • 3. 中国环境科学研究院, 环境基准与风险评估国家重点实验室, 北京 100012
基金项目:

国家科技重大专项(2018ZX07111006);国家自然科学基金资助项目(21577137)

摘要: 环境微塑料是当前环境领域关注热点,并被列为环境与生态科学研究领域的关键科学问题。机动车轮胎因与路面摩擦而向环境不断释放橡胶微粒,因此,机动车轮胎经摩擦释放的橡胶微粒被认为是环境微塑料主要初生源之一。基于我国公路总里程位居世界首位和机动车保有量占世界第二的实际情况,以2016年为基准年,采用经验公式方法估算了我国沿海地区机动车轮胎释放的橡胶微粒水平。结果表明,我国沿海机动车轮胎摩擦释放橡胶微粒量为189 965.91 t,其中广东省释放量最高,占全国沿海省(市)释放总量的24.09%以上,而广西省释放量最小,占比为1.41%。另外,土壤是轮胎橡胶微粒的主要释放去向,橡胶微粒对土壤环境产生的潜在影响需及早引起关注。

English Abstract

参考文献 (30)

目录

/

返回文章
返回