浙江省近岸海域表层水体中微塑料分布与组成特征

doi:10.3785/j.issn.1008-9209.2020.08.111

浙江大学学报（农业与生命科学版）

2021, Vol. 47

Issue (3): 371-379 DOI: 10.3785/j.issn.1008-9209.2020.08.111

资源利用与环境保护

浙江省近岸海域表层水体中微塑料分布与组成特征

周筱田^1,²(

),赵雯璐³,李铁军^1,²,吴伟^1,²,郭远明^1,²,杨承虎^1,²(

)

^1.浙江海洋大学海洋与渔业研究所，浙江舟山 316021
^2.浙江省海洋水产研究所/浙江省海洋渔业资源可持续利用技术研究重点实验室，浙江舟山 316021
^3.浙江工商大学环境科学与工程学院，杭州 310018

Distribution and composition characteristics of microplastics in the coastal surface seawaters of Zhejiang Province

Xiaotian ZHOU^1,²(

),Wenlu ZHAO³,Tiejun LI^1,²,Wei WU^1,²,Yuanming GUO^1,²,Chenghu YANG^1,²(

)

^1.Marine and Fisheries Research Institute, Zhejiang Ocean University, Zhoushan 316021, Zhejiang, China
^2.Marine Fisheries Research Institute of Zhejiang/Key Laboratory of Sustainable Utilization of Technology Research for Fisheries Resources of Zhejiang Province, Zhoushan 316021, Zhejiang, China
^3.School of Environmental Science and Engineering, Zhejiang Gongshang University, Hangzhou 310018, China

全文: PDF(2572 KB) HTML

摘要：

2019年9月—10月，在浙江省近岸海域（平湖、岱山、三门、瑞安和苍南海域）采集20个站位的表层水体，对海水中微塑料丰度、化学成分、形状和颜色等特征进行分析。结果表明：浙江省近岸海域所有调查站位表层水体中普遍存在微塑料，且各海域海水中微塑料平均丰度存在差异，其中：三门海域微塑料平均丰度最高，达240个/m³；瑞安海域微塑料平均丰度最低，为70个/m³。所有站位微塑料丰度范围为40～320个/m³，平均丰度为144个/m³；其化学成分主要是聚酯纤维（38.9%）和纤维素（人造丝）（30.6%）；形状多为纤维状（86.1%），其次为碎片状（12.5%）和薄膜状（1.4%）；颜色以灰色（25.0%）、蓝色（23.6%）和白色（19.4%）为主。特征分析显示，浙江省近岸海域表层水体中微塑料主要来源于纺织业、渔业和居民生活污水。同时，受风力、海流、径流和海水稀释的影响，微塑料在近岸海域水体中分布不均。与国内其他采用类似的研究方法的结果相比，浙江省近岸海域微塑料丰度处于一个较低水平。本研究可为浙江省近岸海域中微塑料的迁移及其污染风险评估提供重要的基础数据。

关键词： 浙江省; 近岸海域; 表层海水; 微塑料; 分布

Abstract:

The surface seawater from 20 stations in the coastal waters (e.g. coastal sea areas of Pinghu, Daishan, Sanmen, Rui’an and Cangnan) of Zhejiang Province were collected from September to October in 2019. The abundance, chemical composition, shape and color of microplastics in the surface seawater were analyzed. The results indicated that the microplastics were widely distributed in the coastal surface seawaters of Zhejiang Province, and the average abundance of microplastics in various coastal areas were heterogeneous. The highest abundance of microplastics were recorded at Sanmen coastal area (240 piece/m³), and the Rui’an coastal area had the lowest microplastic abundance (70 piece/m³). The abundance of microplastics in the surface seawaters of all sampling stations ranged from 40 to 320 piece/m³, and the average abundance was 144 piece/m³. The most major chemical compositions of microplastics were polyester (38.9%) and cellulose (30.6%). Fiber, fragment and film were detected as the mainly shapes of microplastics, accounting for 86.1%, 12.5% and 1.4%, respectively. The most common colors were gray, blue and white, accounting for 25.0%, 23.6% and 19.4%, respectively. The characteristic analysis showed that the microplastics in the coastal surface seawaters of Zhejiang Province mainly originated from textile industry, fishery and domestic sewage. The microplastic was unevenly distributed in the nearshore water resulting from the effects of wind power, ocean current, runoff and seawater dilution. Compared with other domestic studies using the similar methods, the abundance of microplastics in the surface seawater of Zhejiang coastal area was at a relatively low level. This study can provide valuable data for the migration and pollution risk assessment of microplastics in coastal waters of Zhejiang Province.

Key words: Zhejiang Province coastal sea area surface seawater microplastic distribution

收稿日期: 2020-08-11 出版日期: 2021-06-25

CLC:

X 55

基金资助: 国家自然科学基金青年科学基金(31800430);浙江省舟山市科技计划(2018C31079);浙江省海洋水产研究所项目(2019F104)

通讯作者: 杨承虎 E-mail: 499618504@qq.com;yangchenghu135@126.com

作者简介: 周筱田（https://orcid.org/0000-0003-1346-5475），E-mail：499618504@qq.com

	服务
	把本文推荐给朋友
	加入引用管理器
	E-mail Alert
	RSS
	作者相关文章
	周筱田
	赵雯璐
	李铁军
	吴伟
	郭远明
	杨承虎

引用本文:

周筱田,赵雯璐,李铁军,吴伟,郭远明,杨承虎. 浙江省近岸海域表层水体中微塑料分布与组成特征[J]. 浙江大学学报（农业与生命科学版）, 2021, 47(3): 371-379.

Xiaotian ZHOU,Wenlu ZHAO,Tiejun LI,Wei WU,Yuanming GUO,Chenghu YANG. Distribution and composition characteristics of microplastics in the coastal surface seawaters of Zhejiang Province. Journal of Zhejiang University (Agriculture and Life Sciences), 2021, 47(3): 371-379.

链接本文:

http://www.zjujournals.com/agr/CN/10.3785/j.issn.1008-9209.2020.08.111 或 http://www.zjujournals.com/agr/CN/Y2021/V47/I3/371

表1 浙江省近岸海域表层水体中微塑料调查站位

图1 各站位表层海水中微塑料丰度各站位号表示的含义详见表1注。

表2 不同调查中东海海域水体里微塑料采样方法、网具孔径及丰度

图2 浙江省各近岸海域表层水体中微塑料丰度各站位表示的含义详见表1注。短栅上不同小写字母表示在 P＜0.05水平差异有统计学意义。

图3 部分微塑料样品特征PE：聚乙烯；CE：纤维素（人造丝）；PP：聚丙烯；PET：聚对苯二甲酸乙二醇酯；PS：聚苯乙烯；PES：聚酯纤维。

图4 各站位表层海水中微塑料化学成分比例各站位号表示的含义详见表1注。PP：聚丙烯；PE：聚乙烯；PS：聚苯乙烯；PA：聚酰胺；PET：聚对苯二甲酸乙二醇酯；PMMA：聚甲基丙烯酸甲酯；PES：聚酯纤维；CE：纤维素（人造丝）；TPEE：热塑性聚酯弹性体；PLM：聚甲基丙烯酸月桂酯。

图5 浙江省近岸海域表层水体中微塑料化学成分比例各微塑料表示的含义详见图4注。

图6 浙江省近岸海域表层水体中不同形状微塑料比例

图7 浙江省近岸海域表层水体中微塑料颜色比例

1	PLASTICSEUROPE. Plastics: the Facts2018. the_facts_2018_AF_web.pdf. DOI:10.1145/3184558.3186917 doi: 10.1145/3184558.3186917
2	JAMBECK J R, GEYER R, WILCOX C, et al. Plastic waste inputs from land into the ocean. Science, 2015,347(6223):768-771. DOI:10.1126/science.1260352 doi: 10.1126/science.1260352
3	ARTHUR C, BAKER J, BAMFORD H. Proceedings of the international research workshop on the occurrence, effects, and fate of microplastic marine debris. Tacoma, USA: NOAA Technical Memorandum NOS-OR＆R-30, 2008.
4	COLE M, LINDEQUE P, HALSBAND C, et al. Microplastics as contaminants in the marine environment: a review. Marine Pollution Bulletin, 2011,62(12):2588-2597. DOI:10.1016/j.marpolbul.2011.09.025 doi: 10.1016/j.marpolbul.2011.09.025
5	COYLE R, HARDIMAN G, O’DRISCAOLL K. Micro-plastics in the marine environment: a review of their sources, distribution processes, uptake and exchange in ecosystems. Case Studies in Chemical and Environmental Engineering, 2020,2(4):100010. DOI:10.1016/j.cscee.2020.100010 doi: 10.1016/j.cscee.2020.100010
6	KOLANDHASAMY P, SU L, LI J N, et al. Adherence of microplastics to soft tissue of mussels: a novel way to uptake microplastics beyond ingestion. Science of the Total Environment, 2018,610/611:635-640. DOI:10.1016/j.scitotenv.2017.08.053 doi: 10.1016/j.scitotenv.2017.08.053
7	LITHNER D, LARSSON A, DAVE G. Environmental and health hazard ranking and assessment of plastic polymers based on chemical composition. Science of the Total Envi-ronment, 2011,409(18):3309-3324. DOI:10.1016/j.scitotenv.2011.04.038 doi: 10.1016/j.scitotenv.2011.04.038
8	BABOSA F, ADEYEMI J A, BOCATO M Z, et al. A critical viewpoint on current issues, limitations, and future research needs on micro- and nanoplastic studies: from the detection to the toxicological assessment. Environmental Research, 2019,182:109089. DOI:10.1016/j.envres.2019.109089 doi: 10.1016/j.envres.2019.109089
9	BERGMANN M, KLAGES M. Increase of litter at the Arctic deep-sea observatory HAUSGARTEN. Marine Pollution Bulletin, 2012,64(12):2734-2741. DOI:10.1016/j.marpolbul.2012.09.018 doi: 10.1016/j.marpolbul.2012.09.018
10	CAUWENBERGHE L VAN, VANREUSEL A, MEES J, et al. Microplastic pollution in deep-sea sediments. Environ-mental Pollution, 2013,182:495-499. DOI:10.1016/j.envpol.2013.08.013 doi: 10.1016/j.envpol.2013.08.013
11	ZHANG W W, ZHANG S F, WANG J Y, et al. Microplastic pollution in the surface waters of the Bohai Sea, China. Environmental Pollution, 2017,231(1):541-548. DOI:10.1016/j.envpol.2017.08.058 doi: 10.1016/j.envpol.2017.08.058
12	ZHU L, BAI H Y, CHEN B J, et al. Microplastic pollution in North Yellow Sea, China: observations on occurrence, distribution and identification. Science of the Total Environ-ment, 2018,636:20-29. DOI:10.1016/j.scitotenv.2018.04.182 doi: 10.1016/j.scitotenv.2018.04.182
13	ZHAO S Y, ZHU L X, WANG T, et al. Suspended microplastics in the surface water of the Yangtze estuary system, China: first observations on occurrence, distribution. Marine Pollution Bulletin, 2014,86(1/2):562-568. DOI:10.1016/j.marpolbul.2014.06.032 doi: 10
14	TANG G W, LIU M Y, ZHOU Q, et al. Microplastics and polycyclic aromatic hydrocarbons (PAHs) in Xiamen coastal areas: implications for anthropogenic impacts. Science of the Total Environment, 2018,634:811-820. DOI:10.1016/j.scitotenv.2018.03.336 doi: 10.1016/j.scitotenv.2018.03.336
15	BROWNE M A, CRUMP P, NIVEN S J, et al. Accumulation of microplastic on shorelines worldwide: sources and sinks. Environmental Science & Technology, 2011,45(21):9175-9179. DOI:10.1021/es201811s doi: 10.1021/es201811s
16	ZHAO W L, HUANG W, YIN M C, et al. Tributary inflows enhance the microplastic load in the estuary: a case from the Qiantang River. Marine Pollution Bulletin, 2020,156:111152. DOI:10.1016/j.marpolbul.2020.111152 doi: 10.1016/j.marpolbul.2020.111152
17	ZHAO S Y, ZHU L X, LI D J. Microplastic in three urban estuaries, China. Environmental Pollution, 2015,206:597-604. DOI:10.1016/j.envpol.2015.08.027 doi: 10.1016/j.envpol.2015.08.027
18	刘涛,孙晓霞,朱明亮,等.东海表层海水中微塑料分布与组成.海洋与湖沼,2018,49(1):62-69. DOI:10.11693/hyhz20170100021 LIU T, SUN X X, ZHU M L, et al. Distribution and composition of microplastics in the surface water of the East China Sea. Oceanology and Limnology, 2018,49(1):62-69. (in Chinese with English abstract) doi: 10.11693/hyhz20170100021
19	YAN M T, NIE H Y, XU K H, et al. Microplastic abundance, distribution and composition in the Pearl River along Guangzhou City and Pearl River estuary, China. Chemo-sphere, 2019,217:879-886. DOI:10.1016/j.chemosphere.2018.11.093 doi: 10.1016/j.chemosphere.2018.11.093
20	XU P, PENG G Y, SU L, et al. Microplastic risk assessment in surface waters: a case study in the Changjiang estuary, China. Marine Pollution Bulletin, 2018,133:647-654. DOI:10.1016/j.marpolbul.2018.06.020 doi: 10.1016/j.marpolbul.2018.06.020
21	WANG T, HU M H, SONG L L, et al. Coastal zone use influences the spatial distribution of microplastics in Hangzhou Bay, China. Environmental Pollution, 2020,266:115137. DOI:10.1016/j.envpol.2020.115137 doi: 10.1016/j.envpol.2020.115137
22	DI MAURO R, KUPCHIK M J, BENFIELD M C. Abundant plankton-sized microplastic particles in shelf waters of the northern Gulf of Mexico. Environmental Pollution, 2017,230:798-809. DOI:10.1016/j.envpol.2017.07.030 doi: 10.1016/j.envpol.2017.07.030
23	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. Water Research, 2019,161:560-569. DOI:10.1016/j.watres.2019.06.019 doi: 10.1016/j.watres.2019.06.019
24	LUO W Y, SU L, CRAIG N J, et al. Comparison of microplastic pollution in different water bodies from urban creeks to coastal waters. Environmental Pollution, 2019,246:174-182. DOI:10.1016/j.envpol.2018.11.081 doi: 10.1016/j.envpol.2018.11.081
25	CAI M G, HE H X, LIU M Y, et al. Lost but can’t be neglected: huge quantities of small microplastics hide in the South China Sea. Science of the Total Environment, 2018,633:1206-1216. DOI:10.1016/j.scitotenv.2018.03.197 doi: 10.1016/j.scitotenv.2018.03.197
26	DAI Z F, ZHANG H B, ZHOU Q, et al. Occurrence of microplastics in the water column and sediment in an inland sea affected by intensive anthropogenic activities. Environ-mental Pollution, 2018,242(Pt B):1557-1565. DOI:10.1016/j.envpol.2018.07.131 doi: 10.1016/j.envpol.2018.07.131
27	许海超.三门湾三门海域海洋环境污染原因分析及防治对策探讨.海岸工程,2017,36(2):79-84. DOI:10.3969/j.issn.1002-3682.2017.02.010 XU H C. Analysis of cause and discussion of prevention and treatment for the sea environmental pollution in the Sanmen Bay. Coastal Engineering, 2017,36(2):79-84. (in Chinese with English abstract) doi: 10.3969/j.issn.1002-3682.2017.02.010
28	白濛雨,赵世烨,彭谷雨,等.城市污水处理过程中微塑料赋存特征.中国环境科学,2018,38(5):1734-1743. DOI:10.19674/j.cnki.issn1000-6923.2018.020 BAI M Y, ZHAO S Y, PENG G Y, et al. Occurrence, characteristics of microplastic during urban sewage treatment process. China Environmental Science, 2018,38(5):1734-1743. (in Chinese with English abstract) doi: 10.19674/j.cnki.issn1000-6923.2018.020
29	WANG T, LI B J, ZOU X Q, et al. Emission of primary microplastics in mainland China: invisible but not negligible. Water Research, 2019,162:214-224. DOI:10.1016/j.watres.2019.06.042 doi: 10.1016/j.watres.2019.06.042
30	浙江省统计局.浙江统计年鉴.北京:中国统计出版社, 2019. Statistics Bureau of Zhejiang Province. Zhejiang Statistical Yearbook. Beijing: China Statistics Press, 2019. (in Chinese)
31	ZHANG C F, ZHOU H H, CUI Y Z, et al. Microplastics in offshore sediment in the Yellow Sea and East China Sea, China. Environmental Pollution, 2019,244:827-833. DOI:10.1016/j.envpol.2018.10.102 doi: 10
32	GEYER R, JAMBECK J R, LAW K L. Production, use, and fate of all plastics ever made. Science Advances, 2017,3(7):e1700782. DOI:10.1126/sciadv.1700782 doi: 10.1126/sciadv.1700782
33	张建耀,刘春阳.汽车用聚丙烯树脂的开发及国内应用现状.中国塑料,2018,32(2):19-26. DOI:10.19491/j.issn.1001-9278.2018.02.003 ZHANG J Y, LIU C Y. Development of polypropylene resins for automobiles and their application situation in China. China Plastics, 2018,32(2):19-26. (in Chinese with English abstract) doi: 10.19491/j.issn.1001-9278.2018.02.003
34	平湖市统计局.平湖市国民经济和社会发展统计公报.浙江,嘉兴:平湖市统计局,2018. Pinghu Municipal Bureau of Statistics. Pinghu City National Economic and Social Development Statistics Bulletin. Jiaxing, Zhejiang: Pinghu Municipal Bureau of Statistics, 2018. (in Chinese)
35	LI Y B, LU Z B, ZHENG H Y, et al. Microplastics in surface water and sediments of Chongming Island in the Yangtze estuary, China. Environmental Sciences Europe, 2020,32(1):1-12. DOI:10.1186/s12302-020-0297-7 doi: 10.1186/s12302-020-0297-7
36	NAPPER I E, THOMPSON R C. Release of synthetic microplastic plastic fibers from domestic washing machines: effects of fabric type and washing conditions. Marine Pollution Bulletin, 2016,112(1/2):39-45. DOI:10.1016/j.mar polbul.2016.09.025 doi: 10.1016/j.mar
37	ABAYOMI O A, RANGE P, AL-GHOUTI M A, et al. Microplastics in coastal environments of the Arabian Gulf. Marine Pollution Bulletin, 2017,124(1):181-188. DOI:10.1016/j.marpolbul.2017.07.011 doi: 10.1016/j.marpolbul.2017.07.011
38	SHAW D G, DAY R H. Colour- and form-dependent loss of plastic micro-debris from the North Pacific Ocean. Marine Pollution Bulletin, 1994,28(1):39-43. DOI:10.1016/0025-326X(94)90184-8 doi: 10.1016/0025-326X(94)90184-8
39	SANTOS R G, ANDRADES R, FARDIM L M, et al. Marine debris ingestion and Thayer’s law: the importance of plastic color. Environmental Pollution, 2016,214:585-588. DOI:10.1016/j.envpol.2016.04.024 doi: 10

[1]	盛威, 莫亚鹰, 胡忠健, 茹雅璐, 吴玉环. 杭州市树附生苔藓植物分布特征及其与环境的关系[J]. 浙江大学学报（农业与生命科学版）, 2018, 44(6): 711-721.
[2]	朱红雪, 田忠玲, 蔡瑞杭, 李晓琳, 郑经武. 朝鲜孢囊线虫--浙江省孢囊线虫新记录种[J]. 浙江大学学报(农业与生命科学版), 2017, 43(1): 81-88.
[3]	王志明, 吕彭民, 陈霓, 马广. 水稻籽粒连接力分布频谱分析及联合收割机差速脱粒装置研究[J]. 浙江大学学报(农业与生命科学版), 2017, 43(1): 120-127.
[4]	刘西, 陈贤兴. 浙江省植物分布5个新记录种[J]. 浙江大学学报(农业与生命科学版), 2017, 43(1): 33-36.
[5]	施小平，袁森，李新华，邢桂培. 小檗科黄芦木和安徽小檗的叶片特征及其地理分布[J]. 浙江大学学报(农业与生命科学版), 2016, 42(6): 687-693.
[6]	陈丽春,陈征海,马丹丹,林海伦,李修鹏,李根有. 浙江省6种新记录植物[J]. 浙江大学学报(农业与生命科学版), 2016, 42(5): 551-.
[7]	陆叶强, 史云斌, 孙在, 宋熠金, 楼晓春. 基于光散射法柴油发动机尾气颗粒测试分析[J]. 浙江大学学报(农业与生命科学版), 2016, 42(3): 378-384.
[8]	屠艳拉，肖芳，张敬泽，卢启强，汪乐福. 发生在铁皮石斛栽培田中的2种“黏菌病”[J]. 浙江大学学报(农业与生命科学版), 2016, 42(2): 137-142.
[9]	孔樟良. 浙西北茶园土壤固碳能力及其不同形态有机碳的积累特点[J]. 浙江大学学报(农业与生命科学版), 2016, 42(2): 209-219.
[10]	周庄，吴棣飞，陈贤兴，陶正明，熊先华，杨燕萍，丁炳扬. 浙江省植物分布2个新记录属和4个新记录种[J]. 浙江大学学报(农业与生命科学版), 2015, 41(2): 201-204.
[11]	洪春桃, 缪丽华, 季梦成. 浙江省苔藓植物分布新记录[J]. 浙江大学学报(农业与生命科学版), 2015, 41(03): 320-322.
[12]	熊先华1，吴庆玲2，陈贤兴3，胡仁勇3，吴玉南3，丁炳扬3. 浙江省植物分布2新记录属和5新记录种(英文)*[J]. 浙江大学学报(农业与生命科学版), 2013, 39(6): 695-698.
[13]	董旭1，陈秀芝2，娄玉霞1，郭水良1. 外来入侵植物草胡椒在我国的潜分布范围预测*[J]. 浙江大学学报(农业与生命科学版), 2013, 39(6): 621-628.
[14]	徐秋桐1, 常跃畅1，章明奎1,2. 浙江省土壤中细菌对抗生素耐药性的生态分布特征*[J]. 浙江大学学报(农业与生命科学版), 2013, 39(5): 537-544.
[15]	吴家森1，2，张金池1，黄坚钦2，童志鹏3，叶晶2，顾光同4. 浙江省临安市山核桃产区林地土壤有机碳分布特征*[J]. 浙江大学学报(农业与生命科学版), 2013, 39(4): 413-420.

Viewed

Full text

Abstract

Cited

Shared

Discussed