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Frontiers of Environmental Science & Engineering

ISSN 2095-2201

ISSN 2095-221X(Online)

CN 10-1013/X

邮发代号 80-973

2018 Impact Factor: 3.883

Frontiers of Environmental Science & Engineering  2024, Vol. 18 Issue (11): 132   https://doi.org/10.1007/s11783-024-1892-4
  本期目录
Environmental sources, fate, toxicological effects, and health risks of copper pyrithione: an overview
Can Tang1, Xian Qin2, Wenlong Huang3, Sutapa Debi1, Zonghang Zhang1, Jiahua Guo4, Wenhua Liu1, Jiezhang Mo1()
1. Guangdong Provincial Key Laboratory of Marine Disaster Prediction and Prevention, Shantou University, Shantou 515063, China
2. State Key Laboratory of Marine Pollution, City University of Hong Kong, Hong Kong, China
3. Department of Forensic Medicine, Shantou University Medical College, Shantou 515041, China
4. Shaanxi Key Laboratory of Earth Surface System and Environmental Carrying Capacity, College of Urban and Environmental Sciences, Northwest University, Xi’an 710127, China
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Abstract

● Toxicological effects of copper pyrithione on aquatic organisms were reviewed.

● Copper pyrithione causes copper-induced oxidative stress and cell death.

● Copper pyrithione induces severe deformities in fish.

● Long-term effects and associated risks of copper pyrithione remain unknown.

Copper pyrithione (CuPT) is an alternative to tributyltin that is widely used as an antifoulant and biocide in paint for ship hulls, fishing nets, and other marine environmental facilities. It gradually leaches from antifouling coatings into the aquatic environment, posing health risks to aquatic organisms. In recent years, there have been increasing concerns regarding the impacts of CuPT and its degradation products on organisms, as well as the associated health risks. Although the ecotoxicity of CuPT and its degradation products in various species has been studied, there are no comprehensive reviews in the literature that have collated and interpreted these data. This review provides a comprehensive summary of the ecotoxicological effects of CuPT and its degradation products on microorganisms, plants, invertebrates, fish, and mammals. CuPT and its degradation products can affect the light utilization of plants, thereby altering primary production in ecosystems. It can disrupt cell membranes, antioxidant capacity, and cellular pH gradients in animals, leading to developmental toxicity, deformities, morphological damages, endocrine disruption, reproductive toxicity, hepatotoxicity, and neurotoxicity. Mitochondria are believed to be the primary target of CuPT-induced toxicity in aquatic animals; however, further investigations are warranted to reveal the long-term (e.g., multigenerational and transgenerational) impacts and associated molecular mechanisms of CuPT and its degradation products—particularly at environmentally realistic levels. This will facilitate a more comprehensive understanding of the health effects (both in terms of toxicity and hormesis) and environmental risks of CuPT and its degradation products, facilitating more effective regulation and mitigation.

Key wordsCopper pyrithione    Ecotoxicity    Environmental fate    Ecological risk assessment    Review
收稿日期: 2024-04-04      出版日期: 2024-08-06
Corresponding Author(s): Jiezhang Mo   
 引用本文:   
. [J]. Frontiers of Environmental Science & Engineering, 2024, 18(11): 132.
Can Tang, Xian Qin, Wenlong Huang, Sutapa Debi, Zonghang Zhang, Jiahua Guo, Wenhua Liu, Jiezhang Mo. Environmental sources, fate, toxicological effects, and health risks of copper pyrithione: an overview. Front. Environ. Sci. Eng., 2024, 18(11): 132.
 链接本文:  
https://academic.hep.com.cn/fese/CN/10.1007/s11783-024-1892-4
https://academic.hep.com.cn/fese/CN/Y2024/V18/I11/132
Fig.1  
Fig.2  
Taxa Species Duration (h) EC50 or IC50 (μg/L) NOEC (μg/L) References
Cyanophyceae Svnechococcus sp. 96 22 Bao etal. (2011)
Bacillariophyceae Skeletonema costatum 72 1.5 0.7 Onduka etal. (2010)
Skeletonema marinoi 96 1.16 Dupraz etal. (2018)
Halamphora coffeaeformis 96 50 Mochida and Fuji (2009)
Chaetocerus caleitrans 72 3.2 2.0 Onduka etal. (2010)
Amphora coffeaeformis 96 50 Turley etal. (2005)
Nitzschia pungens 96 4.908 0.677 Jung etal. (2017)
Phaeodactylum tricornutum 96 10 Avelelas etal. (2017)
Chlorophyceae Dunaliella tertiolecta 72 7.3 3.5 Onduka etal. (2010)
Selenastrum capricornutum 72 33 Okamura etal. (2003)
Coscinodiscophyceae Thalassiosira pseudonana 96 0.7 Bao etal. (2011)
Prasinophyceae Tetaselmis tetrathele. 72 12 5 Onduka etal. (2010)
Pyrocystis lnula 24 23 Bao etal. (2011)
Tetraselmis suecica 72 24 Okamura etal. (2003)
96 18.0 Dupraz etal. (2018)
Tetraselmis chuii 96 280 Avelelas etal. (2017)
Haptophyta Tisochrysis lutea 96 1.21 Dupraz etal. (2018)
Monocotyledon Lemna gibba G3 168 700 Okamura etal. (2003)
Lemna minor 1769 168 360
Dicotyledoneae Lactuca sativa 120 4300
Tab.1  
Fig.3  
Taxa Species Stages Duration (h) EC50 or LC50 (μg/L) NOEC (μg/L) References
Shrimp Hertacarpus funilirostirls 96 2.5 Mochida et al. (2006)
Mysidacea Neomysis awatschensis Larvae 96 0.441 0.00124 Lee etal. (2023)
Neomysis awatschensis Adults 96 0.785 0.034
Barnacle Balanus amphitrite Larvae 24 4.0–6.1 Romano etal. (2010)
Amphibalanus amphitrite Larvae 24 30 Piazza etal. (2014)
Bryozoan Bugula neritina Larvae 72 50–190 Gutner-Hoch etal. (2018)
Amphipoda Elasmopus rapax Juveniles 96; 168 11.5; 4.0–9.9 Bao etal. (2012)
Elasmopus rapax Juveniles 96 11 Bao etal. (2011)
Anostraca Artemia salina Larvae 24 830 Koutsaftis and Aoyama (2007)
Artemia salina 48 249.529–555.914 Lavtizar etal. (2018)
Artemia salina 4580 Gutner-Hoch etal. (2019)
Artemia franciscana 24 900 Koutsaftis and Aoyama, 2008
Decapoda Heptacarpus futilirostris 96 2.5 Mochida etal. (2006)
Penaeus japonicus 96 43.6 Yamada (2007)
Cirripedia Balanus amphitrite Larvae 24 63 Bao etal. (2011)
Copepoda Tigriopus joponicus 96 32.7 Bao etal. (2014)
Tigriopus joponicus Larvae 24 23 Onduka etal. (2010)
Tigriopus joponicus 24 31 Yamada (2007)
Tigriopus joponicus 24 41 Yamada (2007)
Cnidaria Acropora tumida Larvae 24 28 Bao etal. (2011)
Polychaete Perinereis nuntia. 96; 336 80; 60 Mochida etal. (2011)
Hydroides elegans Larvae 48 5.7 Bao etal. (2011)
Echinoidea Strongylocentrotus intermedius Embryos 50 10.401 Wang etal. (2011)
Paracentrotus lividus Embryos 11 Gutner-Hoch etal. (2019)
Anthocidaris crassispina Embryos 27; 32 2.2×10−3; 1×10−11 Okamura etal. (2006); Kobayashi and Okamura (2002)
Lytechinus variegatus Embryos 3.5 0.53 Okamura etal. (2006)
Strongylocentrotus intermedius Embryos 50 10.4 Wang etal. (2011)
Mussel Mytilus galloprovincialis 96 2612.162 Marcheselli etal. (2010)
Diplostraca Daphnia magna 48 22 Yamada (2007)
Tab.2  
Taxa Species Stages Duration (h) EC50 or LC50 (μg/L) NOEC (μg/L) References
Pereiformes Pagrus major Juveniles 96 22 Mochida etal. (2006)
Pagrus major Juveniles 96 7.67 Yamada (2007)
Rainbow trout Oncorhynchus mykiss Juveniles 168 7.6 –––– Okamura etal. (2002)
336 3.0
504 1.7
672 1.3
Chinook salmon Oncorhynchus tshawytscha Embryos 24 100 Okamura etal. (2002)
Beloniformes Oryzias javanicus Adults 96 16580 Mohamat-Yusuff etal. (2018)
Oryzias melastigma Larvae 96 3.0 (13 °C) –––––– Li etal. (2014)
3.1 (15 °C)
5.1 (20 °C)
5.7 (25 °C)
1.3 (28 °C)
0.3 (32 °C)
Oryzias melastigma Larvae 96 8.2 Bao etal. (2011)
Diplostraca Daphnia magna 48 22 Yamada (2007)
Mummichog Fundulus heteroclitus Larvae 96 2.9–8.4 0.24 Mochida etal. (2008)
Fundulus heteroclitus Juveniles 96 5.0–17.8 Mochida etal. (2008)
Cypriniformes Pimephakes promelas 96 8.2 Yamada (2007)
Tab.3  
Fig.4  
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