ARCHE Consulting, Ghent, Belgium.
UK Centre for Ecology and Hydrology (UKCEH), Lancaster, UK.
Environ Toxicol Chem. 2024 Feb;43(2):450-467. doi: 10.1002/etc.5796. Epub 2024 Jan 10.
Chronic copper (Cu) bioavailability models have been successfully implemented in European risk assessment frameworks and compliance evaluations. However, they were developed almost two decades ago, which calls for an update. In the study, we present updated chronic Cu bioavailability models for invertebrates and algae. They consider recent ecotoxicity data sets and use the more recent speciation model Windermere Humic Aqueous Model (WHAM) VII and an optimized model structure (i.e., a generalized bioavailability model [gBAM]). Contrary to the classic biotic ligand model, a gBAM models the effect of pH on Cu toxicity via a log-linear relationship parametrized through the pH slope S . The recalibrated S parameters are -0.208 for invertebrates (Daphnia magna, two clones) and -0.975 for algae (Raphidocelis subcapitata and Chlorella vulgaris). The updated models predict 80% to 100% of the observed effect levels for eight different species within a factor of 2. The only exception was one of the two data sets considering subchronic 7-day mortality to Hyalella azteca: the prediction performance of the updated invertebrate model at pH ≥ 8.3 was poor because the effect of pH on Cu toxicity appeared to be dependent on the pH itself (with a steeper pH slope compared with the updated invertebrate model at pH ≥ 8.1). The prediction performance of the updated Cu bioavailability models was similar to or better than that of the models used for regulatory application in Europe until now, with one exception (i.e., H. azteca). Together with the recently published fish bioavailability model, the models developed in the present study constitute a complete, updated, and consistent bioavailability model set. Overall, the updated chronic Cu bioavailability model set is robust and can be used in regulatory applications. The updated bioavailability model set is currently used under the European Union Registration, Evaluation, Authorisation, and Restriction of Chemicals framework regulation to guide the safe use of Cu. Environ Toxicol Chem 2024;43:450-467. © 2023 The Authors. Environmental Toxicology and Chemistry published by Wiley Periodicals LLC on behalf of SETAC.
慢性铜(Cu)生物可利用性模型已成功应用于欧洲风险评估框架和合规性评估中。然而,这些模型是在大约二十年前开发的,因此需要进行更新。在本研究中,我们提出了更新的无脊椎动物和藻类慢性 Cu 生物可利用性模型。这些模型考虑了最近的生态毒性数据集,并使用了更现代的形态模型 Windermere Humic Aqueous Model (WHAM) VII 和优化的模型结构(即广义生物可利用性模型 [gBAM])。与经典生物配体模型不同,gBAM 通过 pH 斜率 S 参数化的对数线性关系来模拟 Cu 毒性对 pH 的影响。重新校准的 S 参数值为无脊椎动物(大型溞,两个克隆)为-0.208,藻类(栅藻和普通小球藻)为-0.975。更新后的模型预测了八种不同物种的 80%到 100%的观察到的效应水平,误差因子在 2 以内。唯一的例外是考虑到 Hyalella azteca 的亚慢性 7 天死亡率的两个数据集之一:在 pH ≥ 8.3 时,更新后的无脊椎动物模型的预测性能较差,因为 Cu 毒性对 pH 的影响似乎取决于 pH 本身(与 pH ≥ 8.1 时更新后的无脊椎动物模型相比,pH 斜率更陡)。更新后的 Cu 生物可利用性模型的预测性能与迄今为止在欧洲用于监管应用的模型相似或更好,只有一个例外(即 H. azteca)。与最近发表的鱼类生物可利用性模型一起,本研究中开发的模型构成了一套完整、更新和一致的生物可利用性模型集。总的来说,更新后的慢性 Cu 生物可利用性模型集是稳健的,可以用于监管应用。更新后的生物可利用性模型集目前正在欧盟注册、评估、授权和化学品限制框架法规下使用,以指导 Cu 的安全使用。Environ Toxicol Chem 2024;43:450-467. © 2023 The Authors. Environmental Toxicology and Chemistry published by Wiley Periodicals LLC on behalf of SETAC.