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生态学杂志 ›› 2021, Vol. 40 ›› Issue (12): 4069-4080.doi: 10.13292/j.1000-4890.202112.024

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水相及沉积物固相污染物作用下摇蚊幼虫口器畸形研究进展

田文龙,侯桂林,张瑗玲,杨佳,潘钰琛,曹艳敏*   

  1. (中南民族大学资源与环境学院资源转化与污染控制国家民委重点实验室, 武汉 430074)
  • 出版日期:2021-12-10 发布日期:2022-05-10

Research progress in morphological deformities of chironomid larvae induced by contaminants in water and sediments.

TIAN Wen-long, HOU Gui-lin, ZHANG Yuan-ling, YANG Jia, PAN Yu-chen, CAO Yan-min*   

  1. (Key Laboratory of Resources Conversion and Pollution Control of the State Ethnic Affairs Commission, College of Resources and Environmental Science, SouthCentral University for Nationalities, Wuhan 430074, China).
  • Online:2021-12-10 Published:2022-05-10

摘要: 水体及底泥污染物对底栖动物具有致畸作用。双翅目摇蚊科(Diptera: Chironomidae)幼虫对水体环境变化高度敏感,其口器形态畸变被视为水体底泥质量监测及环境压力评估研究中最具潜力的生物标志物之一。文章综述了摇蚊口器畸形的发现和畸变形态、致畸污染物及可能的致畸机理,并指出目前畸形研究中存在的困难及尚待解决的问题。本领域研究进展大致可归纳为三个方面:(1)广布性:污染水体中摇蚊口器畸变普遍存在,目前不同属种幼虫畸变形态的描述已较为详尽;(2)区域差异性:不同研究报道的畸形率差异较大,识别及标准的不统一可能是导致畸形率高估或低估的主要原因;(3)因果效应非线性:重金属和有机污染物对摇蚊幼虫的致畸作用明显,其致畸效应的生物测试实验已在全球范围开展,但单一污染物与幼虫畸形间的剂量效应关系仍不明确,污染物致畸过程及机理尚不明晰。未来,基于摇蚊畸形的水环境监测及污染物毒性评估分析应重点关注以下四个方面:(1)明确单一污染物与摇蚊畸形间剂量效果关系;(2)统一畸形表征参数;(3)制定规范的生物测试实验室控制规程;(4)国内污染水体摇蚊畸形现象鲜见报道,迫切需要野外调查及室内生物测试研究联合开展,以找到适合本土水体质量评估的有效生物指标及污染物生态效应的早期预警信号。

关键词: 重金属污染, 有机污染, 摇蚊, 口器畸形, 水环境监测

Abstract: Contaminants in water and sediments have the potential to exert teratogenic effects on benthos. Larvae of Chironomid (Diptera: Chironomidae) are highly sensitive to environmental changes in water. Morphological deformities in the mouthparts of chironomid larvae have been proposed as potential biomarkers in the assessment of sediment quality and environmental stress. Here, we reviewed the discovery, morphology, and types of mouthpart deformity in chironomids, showed the potential teratogenic contaminants and mechanisms, and explained the challenges of such research. Current progress on chironomid mouthpart deformities could be summarized into three aspects: (1) ubiquitous: mouthpart deformities in chironomid larvae commonly exist in polluted water, and abnormal morphologies in different taxa and different parts of the mouthpart have been well described; (2) regional variability: there are large discrepancies in deformity frequency among reports on different polluted waters, which might stem from the inconsistency of standards for deformity analysis and calculation of deformity incidence; and (3) causal nonlinearity: both trace metals and organic contaminants are found to have significant teratogenic effects on chironomid larvae, and series of bioassays on teratogenic effects of specific pollutants have been conducted globally, but the dose-effect relationship between specific contaminants and morphological abnormality is still ambiguous and the teratogenic processes and mechanisms should be demonstrated. Future studies using chironomid deformity in water quality monitoring and toxicity assessment of contaminants should focus on the following four issues: (1) establish clear dose-effect relationship between specific pollutants and chironomid deformity; (2) develop unambiguous indices to represent deformity occurrence; (3) establish laboratory protocols of standardized chironomid deformation assay; and (4) carry out domestic studies on mouthpart deformity in chironomid larvae through field investigation and laboratory bioassays, because related studies are scarcely conducted in China, to develop effective bioindicators suitable for local water quality assessment and early warning signals for the ecological effects of pollutants.

Key words: heavy metal pollution, organic pollution, chironomids, mouthpart deformity, water quality monitoring.