Ducrot Virginie, Askem Clare, Azam Didier, Brettschneider Denise, Brown Rebecca, Charles Sandrine, Coke Maïra, Collinet Marc, Delignette-Muller Marie-Laure, Forfait-Dubuc Carole, Holbech Henrik, Hutchinson Thomas, Jach Arne, Kinnberg Karin L, Lacoste Cédric, Le Page Gareth, Matthiessen Peter, Oehlmann Jörg, Rice Lynsey, Roberts Edward, Ruppert Katharina, Davis Jessica Elphinstone, Veauvy Clemence, Weltje Lennart, Wortham Ruth, Lagadic Laurent
INRA, UMR 0985 Ecologie et Santé des Ecosystèmes, Equipe Ecotoxicologie et Qualité des Milieux Aquatiques, 65 rue de Saint-Brieuc, CS 84215, F-35042 Rennes Cedex, France.
CEFAS Lowestoft Laboratory, Pakefield Road, Lowestoft NR33 0HT, United Kingdom.
Regul Toxicol Pharmacol. 2014 Dec;70(3):605-14. doi: 10.1016/j.yrtph.2014.09.004. Epub 2014 Sep 16.
The OECD test guideline development program has been extended in 2011 to establish a partial life-cycle protocol for assessing the reproductive toxicity of chemicals to several mollusk species, including the great pond snail Lymnaea stagnalis. In this paper, we summarize the standard draft protocol for a reproduction test with this species, and present inter-comparison results obtained in a 56-day prevalidation ring-test using this protocol. Seven European laboratories performed semi-static tests with cultured snails of the strain Renilys® exposed to nominal concentrations of cadmium chloride (from 53 to 608μgCdL(-1)). Cd concentrations in test solutions were analytically determined to confirm accuracy in the metal exposure concentrations in all laboratories. Physico-chemical and biological validity criteria (namely dissolved oxygen content >60% ASV, water temperature 20±1°C, control snail survival >80% and control snail fecundity >8 egg-masses per snail over the test period) were met in all laboratories which consistently demonstrated the reproductive toxicity of Cd in snails using the proposed draft protocol. Effect concentrations for fecundity after 56days were reproducible between laboratories (68<EC50-56d<124μgL(-1)) and were consistent with literature data. EC50-56d and EC10-56d values were comprised within a factor of 1.8 and 3.6, respectively, which is in the range of acceptable variation defined for reference chemicals in OECD test guidelines for invertebrates. The inter-laboratory reproducibility coefficient of variation (CV) for the Cd LC50-56d values was 8.19%. The inter-laboratory comparison of fecundity within the controls gave a CV of 29.12%, while exposure to Cd gave a CV of 25.49% based on the EC50-56d values. The OECD has acknowledged the success of this prevalidation exercise and a validation ring-test involving 14 laboratories in Europe, North- and South-America is currently being implemented using four chemicals (Cd, prochloraz, trenbolone and tributyltin).
经济合作与发展组织(OECD)的测试指南制定计划于2011年得到扩展,以建立一个部分生命周期协议,用于评估化学品对包括大瓶螺(Lymnaea stagnalis)在内的几种软体动物物种的生殖毒性。在本文中,我们总结了针对该物种进行繁殖试验的标准草案协议,并展示了使用该协议在为期56天的预验证环试中获得的相互比较结果。七个欧洲实验室对Renilys®品系的养殖蜗牛进行了半静态试验,使其暴露于标称浓度的氯化镉(53至608μgCdL(-1))中。通过分析确定测试溶液中的镉浓度,以确认所有实验室中金属暴露浓度的准确性。所有实验室均满足物理化学和生物学有效性标准(即溶解氧含量>60%空气饱和值、水温20±1°C、对照蜗牛存活率>80%以及在测试期间对照蜗牛繁殖力>每只蜗牛8个卵块),这些实验室一致证明了使用拟议的草案协议时镉对蜗牛具有生殖毒性。各实验室之间56天后繁殖力的效应浓度具有可重复性(68<EC50 - 56d<124μgL(-1)),并且与文献数据一致。EC50 - 56d和EC10 - 56d值分别在1.8倍和3.6倍的范围内,这处于OECD无脊椎动物测试指南中为参考化学品定义的可接受变化范围内。镉LC50 - 56d值的实验室间再现性变异系数(CV)为8.19%。对照内繁殖力的实验室间比较得出的CV为29.12%,而基于EC50 - 56d值,镉暴露的CV为25.49%。OECD已认可此次预验证工作的成功,目前正在开展一项涉及欧洲、北美洲和南美洲14个实验室的验证环试,使用四种化学品(镉、咪鲜胺、群勃龙和三丁基锡)。