不同人为干扰程度云贵高原湖泊表层水中微塑料分布差异性及成因分析
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西南林业大学云南省高原湿地保护修复与生态服务重点实验室

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Analysis of differences and causes of microplastic distribution in surface water of plateau lakes under varying human disturbance intensities
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1.Key Laboratory of Plateau Wetland Conservation, Restoration and Ecological Services, Southwest Forestry University;2.Key Laboratory of Wetland Conservation and Restoration and Ecological Services in Yunnan Province, Southwest Forestry University

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    摘要:

    为了揭示不同人为干扰程度高原湖泊表层水体中微塑料(MPs)分布规律和成因,本研究选取人为干扰较弱的属都湖、干扰较强的星云湖为研究区,通过样品采集以及MPs分离、提取和鉴定等,对比分析两个湖泊表层水体中MPs分布特征和来源差异,为不同高原湖泊MPs防控和保护修复提供理论依据。结果表明:(1)MPs平均丰度属都湖1.82个/m3、星云湖2.14±1.25个/m3,平均数量属都湖478±57个/条、星云湖558±314个/条,随着人为干扰强度的增强,两个高原湖泊表层水体中MPs平均丰度和平均数量均呈现逐步增大趋势。(2)属都湖以黑色、蓝色为主(平均数量合计为295±12个/条),星云湖以蓝色、黑色为主(平均数量合计为403±106个/条)。星云湖和属都湖MPs形状都以线条状为主,线条状平均数量属都湖462个/条、星云湖481±239个/条。MPs尺寸≤200 μm的平均数量属都湖86±30个/条、星云湖280±167个/条。主要聚合物类型属都湖有4种(人造丝(RY)、聚丙烯(PP)、聚乙烯(PE)、聚对苯二甲酸乙二醇酯(PET)),星云湖有7种(RY、PE、PET、低密度苯乙烯-丁二烯-苯乙烯(SBS)、环氧氯丙烷改性聚乙烯亚胺(PEM)、聚酯(PES)、聚乙烯醇(PVA)),属都湖少于星云湖,说明星云湖MPs来源更广泛。随着人为干扰强度的增强,两个高原湖泊表层水体中MPs主要颜色(黑色和蓝色)、主要形状(线条状)、尺寸范围(≤200 μm)的平均数量均呈现逐步增大以及主要聚合物类型种类数呈现逐步增多的趋势。(3)属都湖为贫营养,人为干扰较弱,MPs污染主要成因有旅游活动、放牧活动和大气沉降;星云湖为轻度富营养,人为干扰较强,MPs污染主要成因有生活污水、农田耕种、交通运输、鱼类养殖、鱼类捕捞、工业生产、旅游活动、大气沉降、放牧活动等。两个高原湖泊表层水体中MPs分布和来源存在一定的差异性,人为干扰状况是决定MPs多寡的关键因素。

    Abstract:

    In order to reveal the distribution patterns and causes of microplastics (MPs) in the surface water of plateau lakes with different degrees of human interference, this study selected Shudu Lake, which has relatively weak human interference, and Xingyun Lake, which has relatively strong human interference, as the research areas. Through sample collection and the separation, extraction, and identification of MPs, the distribution characteristics and source differences of MPs in the surface water of the two lakes were compared and analyzed, providing a theoretical basis for the prevention and protection restoration of MPs in different plateau lakes. The results indicate that: (1) The average abundance of MPs was 1.82 particles/m3 in Shudu Lake and 2.14 ± 1.25 particles/m3 in Xingyun Lake. The average number of MPs was 478 ± 57 particles/individual in Shudu Lake and 558 ± 314 particles/individual in Xingyun Lake. As the intensity of human disturbance increases, both the average abundance and average count of MPs in the surface waters of these two plateau lakes show a gradual upward trend. (2) The MPs in Shudu Lake are mainly black and blue (with an average total count of 295 ± 12 particles/individual), while those in Xingyun Lake are mainly blue and black (with an average total count of 403 ± 106 particles/individual). The shapes of MPs in both Xingyun Lake and Shudu Lake are mainly line, with an average number of 462 particles/individual in Shudu Lake and 481 ± 239 particles/individual in Xingyun Lake. The average number of MPs with a size of ≤ 200 μm is 86 ± 30 particles/individual in Shudu Lake and 280 ± 167 particles/individual in Xingyun Lake. The main polymer types in Shudu Lake are 4 types (rayon (RY), polypropylene (PP), polyethylene (PE), and polyethylene terephthalate (PET)), while in Xingyun Lake there are 7 types (RY, PE, PET, low-density styrene-butadiene-styrene (SBS), polyethylenimine ephchlorohydrin modified (PEM), polyester (PES), and polyvinyl alcohol (PVA)). Shudu Lake has fewer polymer types than Xingyun Lake, indicating that the sources of MPs in Xingyun Lake are more diverse. With the increase in the intensity of human interference, the average quantities of the main colors (black and blue), main shapes (line), and size range (≤ 200 μm) of MPs in the surface water of the two plateau lakes have all shown a gradual increase trend, and the number of main polymer types has also shown a gradual increase trend. (3) Shudu Lake is oligotrophic and subject to limited anthropogenic disturbance; the main sources of microplastic pollution are tourism activities, grazing, and atmospheric deposition. Xingyun Lake is mildly eutrophic and experiences stronger human interference; MPs pollution originates from domestic sewage, agricultural cultivation, transportation, fish farming, fishing operations, industrial production, tourism activities, atmospheric deposition, and grazing activities. The distribution and sources of MPs in the surface waters of the two plateau lakes differ, and the level of anthropogenic disturbance is the key factor determining MPs abundance.

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  • 收稿日期:2025-10-28
  • 最后修改日期:2026-02-02
  • 录用日期:2026-02-02
  • 在线发布日期: 2026-04-08
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