BASF SE, Experimental Toxicology and Ecology, Ludwigshafen, Germany.
Altern Lab Anim. 2011 Jul;39(3):273-95. doi: 10.1177/026119291103900311.
Acute oral toxicity testing is still required for the classification and labelling of chemicals, agrochemicals and related formulations. There have been increasing efforts over the last two decades to reduce the number of animals needed for this testing, according to the Three Rs concept. To evaluate the utility of an in vitro cytotoxicity test in our routine testing for acute oral toxicity, we have implemented in our laboratory the neutral red uptake (NRU) method, with Balb/c 3T3 fibroblasts after a 48-hour exposure, which was recommended in ICCVAM Report 07-4519, 2006. Initially, we tested 16 substances that had existing in vivo and in vitro data available, to prove our technical proficiency with the in vitro test. Then, testing was performed with 187 test substances, including a broad variety of chemicals, agrochemicals and formulations. The starting dose for acute oral systemic toxicity assays in rats (LD50) was estimated by using the prediction model presented in the ICCVAM validation study, and subsequently compared to the results obtained by in vivo testing performed according to, or similar to, OECD Test Guideline 423. Comparison of all of the 203 predicted LD50 values that were deduced from the in vitro IC50 values, with the in vivo results from oral toxicity studies in rats, resulted in a low overall concordance of 35%. The in vitro cytotoxicity assay achieved a good concordance of 74%, only for the weakly toxic substances (EU-GHS Cat. 4). However, it must be noted that 71% of the substances tested (i.e. 145/203) were classified as being weakly toxic in vitro. We further analysed the utility of the in vitro test for predicting the starting dose for an in vivo study, and the potential reduction in animal usage that this would engender. In this regard, the prediction by the cytotoxicity test was useful for 59% of the substances. However, the use of a standard starting dose of 300 mg/kg bw by default (without previous cytotoxicity testing) would have been almost as useful (50%). In contrast, the prediction by an experienced toxicologist was correct for 95% of the substances. However, this was only performed for 40% of the substances, mainly those of no to low toxicity. Calculating the theoretical animal numbers needed in several scenarios supported these results. The additional analysis, considering some physicochemical data (solubility, molecular weight, log POW), substance class and mode of action, revealed no specific applicability domains. In summary, the use of the 3T3 NRU cytotoxicity data alone did not sufficiently contribute to refinement and reduction in the acute oral toxicity testing of the substance portfolio tested routinely in our laboratory.
急性口服毒性测试仍然是化学品、农药和相关制剂分类和标签所必需的。根据“3R”概念,在过去的二十年中,人们一直在努力减少进行这项测试所需的动物数量。为了评估我们常规急性口服毒性测试中体外细胞毒性测试的效用,我们在实验室中实施了 ICCVAM 报告 07-4519(2006 年)中推荐的 48 小时接触后用 Balb/c 3T3 成纤维细胞进行的中性红摄取(NRU)方法。最初,我们测试了 16 种具有现有体内和体外数据的物质,以证明我们在体外测试方面的技术能力。然后,我们用 187 种测试物质进行了测试,这些物质包括广泛的化学品、农药和制剂。大鼠急性口服全身毒性测定(LD50)的起始剂量是通过使用 ICCVAM 验证研究中提出的预测模型来估计的,随后将其与根据 OECD 测试指南 423 或与之类似的体内测试结果进行比较。将从体外 IC50 值推断出的 203 个预测 LD50 值与大鼠口服毒性研究的体内结果进行比较,结果总体一致性低,仅为 35%。体外细胞毒性测定对于弱毒性物质(EU-GHS 类别 4)的一致性为 74%。然而,需要注意的是,测试的物质中有 71%(即 145/203)被分类为体外弱毒性。我们进一步分析了体外测试预测体内研究起始剂量的效用,以及这将带来的动物使用量的潜在减少。在这方面,细胞毒性测试的预测对 59%的物质有用。然而,默认情况下使用 300mg/kg bw 的标准起始剂量(不进行先前的细胞毒性测试)几乎同样有用(50%)。相比之下,经验丰富的毒理学家的预测对 95%的物质是正确的。然而,这仅对 40%的物质进行了评估,主要是那些无毒性或低毒性的物质。在几种情况下计算所需的理论动物数量支持了这些结果。考虑到一些物理化学数据(溶解度、分子量、log POW)、物质类别和作用方式的额外分析没有揭示出特定的适用性域。总之,仅使用 3T3 NRU 细胞毒性数据并不能充分促进我们实验室常规测试的物质组合的急性口服毒性测试的改进和减少。