双台子河与大辽河表层水体微塑料特征与分布研究

李江南, 凌玮, 沈茜, 贺亚楠, 徐新阳, 陈熙, 安立会. 双台子河与大辽河表层水体微塑料特征与分布研究[J]. 生态毒理学报, 2021, 16(3): 192-199. doi: 10.7524/AJE.1673-5897.20201013002
引用本文: 李江南, 凌玮, 沈茜, 贺亚楠, 徐新阳, 陈熙, 安立会. 双台子河与大辽河表层水体微塑料特征与分布研究[J]. 生态毒理学报, 2021, 16(3): 192-199. doi: 10.7524/AJE.1673-5897.20201013002
Li Jiangnan, Ling Wei, Shen Qian, He Yanan, Xu Xinyang, Chen Xi, An Lihui. Characteristics and Distribution of Microplastics in Surface Water from Shuangtaizi River and Daliao River[J]. Asian Journal of Ecotoxicology, 2021, 16(3): 192-199. doi: 10.7524/AJE.1673-5897.20201013002
Citation: Li Jiangnan, Ling Wei, Shen Qian, He Yanan, Xu Xinyang, Chen Xi, An Lihui. Characteristics and Distribution of Microplastics in Surface Water from Shuangtaizi River and Daliao River[J]. Asian Journal of Ecotoxicology, 2021, 16(3): 192-199. doi: 10.7524/AJE.1673-5897.20201013002

双台子河与大辽河表层水体微塑料特征与分布研究

    作者简介: 李江南(1995-),男,硕士,研究方向为微塑料生态风险评价,E-mail:2644460749@qq.com
    通讯作者: 陈熙, E-mail: chenxineu@mail.neu.edu.cn
  • 基金项目:

    国家重点研发计划项目(2016YFC1402206)

  • 中图分类号: X171.5

Characteristics and Distribution of Microplastics in Surface Water from Shuangtaizi River and Daliao River

    Corresponding author: Chen Xi, chenxineu@mail.neu.edu.cn
  • Fund Project:
  • 摘要: 微塑料是全球新兴环境热点问题之一。据估算,80%的海洋微塑料来于陆源输入,而河流被认为是陆源微塑料输入海洋的主要路径之一。为揭示辽河流域水体微塑料污染特征、空间分布及其对渤海微塑料污染的潜在贡献,本文基于密度分离原理并利用傅里叶变换红外光谱方法,研究了双台子河与大辽河下游至入海口(盘锦段)河道表层水体微塑料丰度、材质组成、形态特征与粒径分布特征。结果显示:从材质上分析,2条河流共检出了17种高分子聚合物,其中以聚乙烯占比最高,分别占双台子河和大辽河表层微塑料总量的38%和32%;从形态上分析,碎片微塑料(533.08~674.25 μm)和纤维微塑料(1 054.87~1 450.76 μm)分别占2条河流检出微塑料总量的80%以上,颗粒微塑料(100.26~241.3μm)占比则低于10%,并且没有检出形状规则的塑料微珠;从丰度上分析,双台子河((4.52±0.76)个·L-1)与大辽河((4.74±0.67)个·L-1)表层水体微塑料丰度之间无显著差异(P>0.05),并且各点之间也没有明显的变化趋势(P>0.05)。以上研究结果表明,双台子河与大辽河表层水体微塑料污染特征相似,这为开展渤海微塑料溯源和风险管理提供了直接依据。
  • 加载中
  • Thompson R C, Olsen Y, Mitchell R P, et al. Lost at sea:Where is all the plastic?[J]. Science, 2004, 304(5672):838
    Liu K, Wang X H, Fang T, et al. Source and potential risk assessment of suspended atmospheric microplastics in Shanghai[J]. Science of the Total Environment, 2019, 675:462-471
    Alam F C, Sembiring E, Muntalif B S, et al. Microplastic distribution in surface water and sediment river around slum and industrial area (case study:Ciwalengke River, Majalaya district, Indonesia)[J]. Chemosphere, 2019, 224:637-645
    Su L, Xue Y G, Li L Y, et al. Microplastics in Taihu Lake, China[J]. Environmental Pollution, 2016, 216:711-719
    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):383-396

    Yang J J, Xu L, Lu A X, et al. Research progress on the sources and toxicology of micro (nano) plastics in environment[J]. Environmental Chemistry, 2018, 37(3):383-396(in Chinese)

    Victoria R, Banwart S, Black H, et al. Emerging issues in our global environment[R]. Geneva:United Nations Environment Programme, 2012
    Simon-Sánchez L, Grelaud M, Garcia-Orellana J, et al. River Deltas as hotspots of microplastic accumulation:The case study of the Ebro River (NW Mediterranean)[J]. Science of the Total Environment, 2019, 687:1186-1196
    Lebreton L C M, van der Zwet J, Damsteeg J W, et al. River plastic emissions to the world's oceans[J]. Nature Communications, 2017, 8:15611
    Harris P T. The fate of microplastic in marine sedimentary environments:A review and synthesis[J]. Marine Pollution Bulletin, 2020, 158:111398
    Hurley R, Woodward J, Rothwell J J. Microplastic contamination of river beds significantly reduced by catchment-wide flooding[J]. Nature Geoscience, 2018, 11(4):251-257
    夏斌. 2005年夏季环渤海16条主要河流的污染状况及入海通量[D]. 青岛:中国海洋大学, 2007:58-63 Xia B. Contaminative conditions of main sixteen rivers around Bohai Sea and pollutant flux flowing into sea in summer of 2005[D]. Qingdao:Ocean University of China, 2007

    :58-63(in Chinese)

    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(Pt 1):541-548
    韩丽花, 李巧玲, 徐笠, 等. 大辽河沉积物中微塑料的污染特征[J]. 中国环境科学, 2020, 40(4):1649-1658

    Han L H, Li Q L, Xu L, et al. The pollution characteristics of microplastics in Daliao River sediments[J]. China Environmental Science, 2020, 40(4):1649-1658(in Chinese)

    Xu Q J, Gao Y Y, Xu L, et al. Investigation of the microplastics profile in sludge from China's largest water reclamation plant using a feasible isolation device[J]. Journal of Hazardous Materials, 2020, 388:122067
    伍成成. Mike11在盘锦双台子河口感潮段的应用研究[D]. 青岛:中国海洋大学, 2011:50-58 Wu C C. Study on application of Mike11 in tidal river network of Panjin Shuangtaizi Estuary[D]. Qingdao:Ocean University of China, 2011

    :50-58(in Chinese)

    Wang W F, Ndungu A W, Li Z, et al. Microplastics pollution in inland freshwaters of China:A case study in urban surface waters of Wuhan, China[J]. Science of the Total Environment, 2017, 575:1369-1374
    Gallagher A, Rees A, Rowe R, et al. Microplastics in the Solent estuarine complex, UK:An initial assessment[J]. Marine Pollution Bulletin, 2016, 102(2):243-249
    Miller R Z, Watts A J R, Winslow B O, et al. Mountains to the sea:River study of plastic and non-plastic microfiber pollution in the northeast USA[J]. Marine Pollution Bulletin, 2017, 124(1):245-251
    Moore C J, Lattin G L, Zellers A F. Quantity and type of plastic debris flowing from two urban rivers to coastal waters and beaches of Southern California[J]. Revista De Gestão Costeira Integrada, 2011, 11(1):65-73
    中华人民共和国水利部. 中国水利统计年鉴2018[M]. 北京:中国水利水电出版社, 2018:155-156 Ministry of Water Resources of the People's Republic of China. China Water Statistical Yearbook, 2018[M]. Beijing:China Water Resources and Hydropower Press, 2018

    (in Chinese)

    Sutton R, Sedlak M. Microplastic monitoring and science strategy for San Francisco Bay[R]. California:SFEI Contribution, 2017
    Shahul Hamid F, Bhatti M S, Anuar N, et al. Worldwide distribution and abundance of microplastic:How dire is the situation?[J]. Waste Management & Research, 2018, 36(10):873-897
    Di M X, Wang J. Microplastics in surface waters and sediments of the Three Gorges Reservoir, China[J]. Science of the Total Environment, 2018, 616-617:1620-1627
    Koelmans A A, Mohamed Nor N H, Hermsen E, et al. Microplastics in freshwaters and drinking water:Critical review and assessment of data quality[J]. Water Research, 2019, 155:410-422
    Scircle A, Cizdziel J V, Tisinger L, et al. Occurrence of microplastic pollution at oyster reefs and other coastal sites in the Mississippi Sound, USA:Impacts of freshwater inflows from flooding[J]. Toxics, 2020, 8(2):E35
    Eriksen M, Lebreton L C M, Carson H S, et al. Plastic pollution in the world's oceans:More than 5 trillion plastic pieces weighing over 250, 000 tons afloat at sea[J]. PLoS One, 2014, 9(12):e111913
    Zhao S Y, Zhu L X, Li D J. Microplastic in three urban estuaries, China[J]. Environmental Pollution, 2015, 206:597-604
    Zhao S Y, Wang T, Zhu L X, et al. Analysis of suspended microplastics in the Changjiang Estuary:Implications for riverine plastic load to the ocean[J]. Water Research, 2019, 161:560-569
    Wang W F, Yuan W K, Chen Y L, et al. Microplastics in surface waters of Dongting Lake and Hong Lake, China[J]. Science of the Total Environment, 2018, 633:539-545
    Wagner M, Scherer C, Alvarez-Muñoz D, et al. Microplastics in freshwater ecosystems:What we know and what we need to know[J]. Environmental Sciences Europe, 2014, 26(1):12
    Zhang D D, Cui Y Z, Zhou H H, et al. Microplastic pollution in water, sediment, and fish from artificial reefs around the Ma'an Archipelago, Shengsi, China[J]. Science of the Total Environment, 2020, 703:134768
    Han M, Niu X R, Tang M, et al. Distribution of microplastics in surface water of the lower Yellow River near estuary[J]. Science of the Total Environment, 2020, 707:135601
    Kooi M, Nes E H V, Scheffer M, et al. Ups and Downs in the ocean:Effects of biofouling on vertical transport of microplastics[J]. Environmental Science & Technology, 2017, 51(14):7963-7971
    Browne M A, Crump P, Niven S J, et al. Accumulation of microplastic on shorelines woldwide:Sources and sinks[J]. Environmental Science & Technology, 2011, 45(21):9175-9179
  • 加载中
计量
  • 文章访问数:  2168
  • HTML全文浏览数:  2168
  • PDF下载数:  74
  • 施引文献:  0
出版历程
  • 收稿日期:  2020-10-13

双台子河与大辽河表层水体微塑料特征与分布研究

    通讯作者: 陈熙, E-mail: chenxineu@mail.neu.edu.cn
    作者简介: 李江南(1995-),男,硕士,研究方向为微塑料生态风险评价,E-mail:2644460749@qq.com
  • 1. 东北大学资源与土木工程学院, 沈阳 110004;
  • 2. 中国环境科学研究院, 国家环境基准与风险评估重点实验室, 北京 100012
基金项目:

国家重点研发计划项目(2016YFC1402206)

摘要: 微塑料是全球新兴环境热点问题之一。据估算,80%的海洋微塑料来于陆源输入,而河流被认为是陆源微塑料输入海洋的主要路径之一。为揭示辽河流域水体微塑料污染特征、空间分布及其对渤海微塑料污染的潜在贡献,本文基于密度分离原理并利用傅里叶变换红外光谱方法,研究了双台子河与大辽河下游至入海口(盘锦段)河道表层水体微塑料丰度、材质组成、形态特征与粒径分布特征。结果显示:从材质上分析,2条河流共检出了17种高分子聚合物,其中以聚乙烯占比最高,分别占双台子河和大辽河表层微塑料总量的38%和32%;从形态上分析,碎片微塑料(533.08~674.25 μm)和纤维微塑料(1 054.87~1 450.76 μm)分别占2条河流检出微塑料总量的80%以上,颗粒微塑料(100.26~241.3μm)占比则低于10%,并且没有检出形状规则的塑料微珠;从丰度上分析,双台子河((4.52±0.76)个·L-1)与大辽河((4.74±0.67)个·L-1)表层水体微塑料丰度之间无显著差异(P>0.05),并且各点之间也没有明显的变化趋势(P>0.05)。以上研究结果表明,双台子河与大辽河表层水体微塑料污染特征相似,这为开展渤海微塑料溯源和风险管理提供了直接依据。

English Abstract

参考文献 (34)

目录

/

返回文章
返回