Synergistic toxic effects of zinc pyrithione and copper to three marine species: Implications on setting appropriate water quality criteria

The Swire Institute of Marine Science, Division of Ecology and Biodiversity, School of Biological Sciences, The University of Hong Kong, Pokfulam, Hong Kong, China.
Marine Pollution Bulletin (Impact Factor: 2.99). 12/2008; 57(6-12):616-23. DOI: 10.1016/j.marpolbul.2008.03.041
Source: PubMed


Zinc pyrithione (ZnPT) is widely applied in conjunction with copper (Cu) in antifouling paints as a substitute for tributyltin. The combined effects of ZnPT and Cu on marine organisms, however, have not been fully investigated. This study examined the toxicities of ZnPT alone and in combination with Cu to the diatom Thalassiosira pseudonana, polychaete larvae Hydroides elegans and amphipod Elasmopus rapax. Importantly, ZnPT and Cu resulted in a strong synergistic effect with isobologram interaction parameter lambda>1 for all test species. The combined toxicity of ZnPT and Cu was successfully modelled using the non-parametric response surface and its contour. Such synergistic effects may be partly due to the formation of copper pyrithione. It is, therefore, inadequate to assess the ecological risk of ZnPT to marine organisms solely based on the toxicity data generated from the biocide alone. To better protect precious marine resources, it is advocated to develop appropriate water quality criteria for ZnPT with the consideration of its compelling synergistic effects with Cu at environmentally realistic concentrations.

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    • "In addition, there is a lack of data on the toxicity of this organometallic compound (Bao et al., 2008). ZnP has teratogenic effects on embryos and larvae of teleosts (Goka, 1999; Sánchez-Bayo and Goka, 2005), sea urchins (Kobayashi and Okamura, 2002; Bellas, 2008), crustaceans (Hossain et al., 2004; Koutsaftis and Aoyama, 2007), bivalves (Bellas et al., 2005) and ascidians (Bellas, 2005). "
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    ABSTRACT: New biocides such as the organometallic compound zinc pyrithione (ZnP) have been massively introduced by many countries in formulations of antifouling paints following the ban on tributyltin (TBT). The effects of sublethal concentrations (LC50=82.5μM, i.e., 26.2mg/l) on cultured haemocytes of the ascidian Botryllus schlosseri have been investigated and compared with TBT. The percentage of haemocytes with amoeboid morphology and containing phagocytised yeast cells were significantly (p<0.05) reduced after exposure to 0.1 (31.7μg/l) and 0.5μM (158μg/l), respectively. An antagonistic interaction in inducing cytoskeletal alterations was observed when ZnP and TBT were co-present in the exposure medium. ZnP affected only the actin component. As caused by TBT, ZnP induced apoptosis and inhibited both oxidative phosphorylation and lysosomal activities. In contrast to the case of TBT, a decrement in Ca(2+)-ATPase activity and a decrease in cytosolic Ca(2+) were detected after incubation at the highest concentration (1μM, i.e., 317.7μg/l) used. In comparison with other antifouling compounds, ZnP shows as much toxicity as TBT to cultured haemocytes at extremely low concentrations and interfering with fundamental cell activities. Copyright © 2014. Published by Elsevier Inc.
    Comparative Biochemistry and Physiology Part C Toxicology & Pharmacology 01/2015; 169. DOI:10.1016/j.cbpc.2014.12.007 · 2.30 Impact Factor
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    • "The acute toxicities of CuPT alone and in combination of Cu on the adult copepod were also examined to elucidate the combined toxicity of ZnPT and Cu. Response surface models have proven to be successful to fit all experimental data in a single model and clearly visualizing all combined toxicity data in a three dimensional concentration response surface (Gessner, 1995; Bao et al., 2008, 2013). We applied and compared three different response surface approaches, namely the Loewe parametric response surface (CARS; Greco et al., 1995), response additive response surface (RARS; Bao et al., 2013), and the non-parametric response surface (NPRS; Gessner, 1995; Greco et al., 1995) models to describe and predict the combined acute toxicity of binary mixtures of individual biocides and Cu. "
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    ABSTRACT: Zinc pyrithione (ZnPT) is a widely used booster biocide in combination with copper (Cu) in antifouling paints as a substitute for tributyltin. The co-occurrence of ZnPT and Cu in coastal marine environments is therefore very common, and may pose a higher risk to marine organisms if they can result in synergistic toxicity. This study comprehensively investigated the combined toxicity of ZnPT and Cu, on the marine copepod Tigriopus japonicus, for the first time, based on both 96-h acute toxicity tests using adult copepods and chronic full-life cycle tests (21 d) using nauplii <24-h old. As ZnPT has been reported to be easily trans-chelated to copper pyrithione (CuPT) in the presence of Cu, the acute toxicities of CuPT alone and in combination with Cu on adult copepods were also assessed. Our results showed that ZnPT and Cu exhibited a strong synergistic toxic effect on the copepod in both acute and chronic tests. During the acute test, the mortalities of adult copepods increased dramatically even with an addition of Cu at concentrations as low as 1–2 μg/L compared with those exposed to ZnPT alone. Severe chronic toxicities were further observed in the copepods exposed to ZnPT–Cu mixtures, including a significant increase of naupliar mortality, postponing of development from naupliar to copepodid and from copepodid to adult stage, and a significant decrease of intrinsic population growth when compared with those of copepods exposed to ZnPT or Cu alone. Such synergistic effects might be partly attributable to the formation of CuPT by the trans-chelation of ZnPT and Cu, because CuPT was found to be more toxic than ZnPT based on the acute toxicity results. Mixtures of CuPT and Cu also led to synergistic toxic effects to the copepod, in particular at high Cu concentrations. A novel non-parametric response surface model was applied and it proved to be a powerful method for analysing and predicting the acute binary mixture toxicities of the booster biocides (i.e., ZnPT and CuPT) and Cu on the copepod. To better protect precious marine resources, it is necessary to revise and tighten existing water quality criteria for biocides, such as ZnPT and CuPT, to account for their synergistic effects with Cu at environmentally realistic levels.
    Aquatic Toxicology 12/2014; 157:81-93. DOI:10.1016/j.aquatox.2014.09.013 · 3.45 Impact Factor
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    • "As an active ingredient in antifouling paints and fungicides, TPTCl is a pervasive marine pollutant which is highly toxic to marine organisms and can trigger imposex in neogastropod species like Thais clavigera (Yi et al. 2012). CuPT is a booster biocide which has been increasingly used in Cu-based antifouling paints since the early 1990s to remove Cu-tolerant fouling organisms (Yebra et al. 2004), but it is highly toxic to nontarget marine species (Bao et al. 2008b). "
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    ABSTRACT: We hypothesize that chemical toxicity to marine ectotherms is the lowest at an optimum temperature (OT) and it exacerbates with increasing or decreasing temperature from the OT. This study aimed to verify this hypothetical temperature-dependent chemical toxicity (TDCT) model through laboratory experiments. Acute toxicity over a range of temperatures was tested on four commonly used chemicals to three marine ectotherms. Our results confirmed that toxicities, in terms of 96-h LC50 (median lethal concentration; for the marine medaka fish Oryzias melastigma and the copepod Tigriopus japonicus) and 24-h LC50 (for the rotifer Brachionus koreanus), were highly temperature-dependent, and varied between test species and between study chemicals. The LC50 value of the fish peaked at 20 °C for copper (II) sulphate pentahydrate and triphenyltin chloride, and at 25 °C for dichlorophenyltrichloroethane and copper pyrithione, and decreased with temperature increase or decrease from the peak (i.e., OT). However, LC50 values of the copepod and the rotifer generally showed a negative relationship with temperature across all test chemicals. Both copepod and rotifer entered dormancy at the lowest temperature of 4 °C. Such metabolic depression responses in these zooplanktons could reduce their uptake of the chemical and hence minimize the chemical toxicity at low temperatures. Our TDCT model is supported by the fish data only, whereas a simple linear model fits better to the zooplankton data. Such species-specific TDCT patterns may be jointly ascribed to temperature-mediated changes in (1) the physiological response and susceptibility of the marine ectotherms to the chemical, (2) speciation and bioavailability of the chemical, and (3) toxicokinetics of the chemical in the organisms.
    Ecotoxicology 08/2014; 23(8):1564-1573. DOI:10.1007/s10646-014-1297-4 · 2.71 Impact Factor
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