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水生生物测试指南未能充分控制稀释用水的总有机碳和硬度对阳离子聚合物毒性的影响——改进标准化测试程序的建议。

Aquatic testing guidelines insufficiently control the influence of dilution water toc and hardness on cationic polymer toxicity - A proposal to improve standardized test procedures.

机构信息

Experimental Ecotoxicology, BASF SE, Carl-Bosch-Strasse 38, 67056, Ludwigshafen, Germany.

Experimental Ecotoxicology, BASF SE, Carl-Bosch-Strasse 38, 67056, Ludwigshafen, Germany.

出版信息

Chemosphere. 2020 Nov;259:127473. doi: 10.1016/j.chemosphere.2020.127473. Epub 2020 Jun 20.

DOI:10.1016/j.chemosphere.2020.127473
PMID:32622247
Abstract

Cationic polymers (CPs) are widely used chemicals for wastewater treatment applications and in various "down-the-drain" household products. The aquatic toxicity of CPs results from an electrostatic interaction with negatively charged cell surfaces. These effects are greatly mitigated by the binding affinity of CPs to total organic carbon (TOC) in surface water. Consequently, baseline aquatic toxicity tests of CPs using clean lab water (TOC < 2 mg/L) typically overestimate toxicity and risk which is greatly mitigated at higher environmentally relevant OC levels. However, the point at which mitigation begins is not well defined and low-level TOC in lab water may influence the baseline toxicity outcome. Similarly, divalent cations, quantified as water hardness, may modulate the electrostatic binding between OC and CP. Although standard guidelines define limits for lab water hardness and TOC, the consequences of variability within those limits on test outcome is unknown. We investigated the impact of part-per-billion (ppb) additions of TOC to lab water at different hardness levels on CP acute toxicity to Daphnia magna and Raphidocelis subcapitata. In both species, the acute toxicities of CPs with different molecular weight and charge density varied by > 10-fold in response to slight changes in TOC and water hardness, although parameters were maintained within guideline limits. When determining the baseline aquatic toxicity of CPs, the lab water should be standardized at the lowest biologically tolerable hardness and TOC at a reliably measurable level (>1 - < 2 mg/L) to reduce variability and increase the reliability of the toxicity estimate.

摘要

阳离子聚合物(CPs)广泛应用于废水处理和各种“随水冲走”的家用产品中。CPs 的水生毒性源于与带负电荷的细胞表面的静电相互作用。这些效应因 CPs 与地表水总有机碳(TOC)的结合亲和力而大大减轻。因此,使用清洁实验室水(TOC<2mg/L)的 CPs 的基线水生毒性测试通常会高估毒性和风险,而在更高的环境相关 OC 水平下,毒性和风险会大大降低。然而,缓解开始的点尚未明确定义,实验室水中的低水平 TOC 可能会影响基线毒性结果。同样,二价阳离子,以水硬度的形式量化,可能会调节 OC 和 CP 之间的静电结合。尽管标准指南定义了实验室水硬度和 TOC 的限制,但这些限制内的变异性对测试结果的影响尚不清楚。我们研究了在不同硬度水平下,将实验室水中 TOC 的 ppm 级添加到实验室水中对大型溞和斜生栅藻急性毒性的影响。在这两个物种中,尽管参数保持在指南限制内,但不同分子量和电荷密度的 CPs 的急性毒性在 TOC 和水硬度稍有变化时会变化 10 倍以上。在确定 CPs 的基线水生毒性时,实验室用水应在最低生物可耐受硬度下标准化,TOC 应在可靠可测量的水平(>1-<2mg/L)下标准化,以减少变异性并提高毒性估计的可靠性。

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