University of York, Environment Department, Heslington, York YO10 5NG, UK.
University of York, Environment Department, Heslington, York YO10 5NG, UK.
Ecotoxicol Environ Saf. 2022 Mar 1;232:113231. doi: 10.1016/j.ecoenv.2022.113231. Epub 2022 Jan 29.
A major limitation of dietary toxicity studies on rodents is that food consumption often differs between treatments. The control treatment serves as a reference of how animals would have grown if not for the toxicant in their diet, but this comparison unavoidably conflates the effects of toxicity and feeding rate on body weight over time. A key advantage of toxicity models based on dynamic energy budget theory (DEB) is that chemical stress and food consumption are separate model inputs, so their effects on growth rate can be separated. To reduce data requirements, DEB convention is to derive a simplified feeding input, f, from food availability; its value ranges from zero (starvation) to one (food available ad libitum). Observed food consumption in dietary toxicity studies shows that, even in the control treatment, rats limit their food consumption, contradicting DEB assumptions regarding feeding rate. Relatively little work has focused on addressing this mismatch, but accurately modelling the effects of food intake on growth rate is essential for the effects of toxicity to be isolated. This can provide greater insight into the results of chronic toxicity studies and allows accurate extrapolation of toxic effects from laboratory data. Here we trial a new method for calculating f, based on the observed relationships between food consumption and body size in laboratory rats. We compare model results with those of the conventional DEB method and a previous effort to calculate f using observed food consumption data. Our results showed that the new method improved model accuracy while modelled reserve dynamics closely followed observed body fat percentage over time. The new method assumes that digestive efficiency increases with body size Verifying this relationship through data collection would strengthen the basis of DEB theory and support the case for its use in ecological risk assessment.
啮齿动物饮食毒性研究的一个主要局限性是,不同处理组之间的食物消耗往往存在差异。对照处理是一种参考,它说明了如果动物的饮食中没有毒物,它们会如何生长,但这种比较不可避免地混淆了毒性和喂养率对体重随时间的影响。基于动态能量预算理论 (DEB) 的毒性模型的一个主要优势是,化学应激和食物消耗是单独的模型输入,因此它们对生长率的影响可以分开。为了减少数据需求,DEB 惯例是从食物供应中得出简化的喂养输入 f;其值范围从零(饥饿)到一(可自由获取食物)。饮食毒性研究中的观察到的食物消耗表明,即使在对照处理中,大鼠也会限制食物消耗,这与 DEB 关于喂养率的假设相矛盾。相对较少的工作集中在解决这种不匹配上,但准确模拟食物摄入对生长率的影响对于隔离毒性的影响至关重要。这可以更深入地了解慢性毒性研究的结果,并允许从实验室数据准确推断毒性效应。在这里,我们尝试了一种新的方法来计算 f,该方法基于实验室大鼠中观察到的食物消耗与体型之间的关系。我们将模型结果与传统 DEB 方法和之前使用观察到的食物消耗数据计算 f 的方法进行了比较。我们的结果表明,新方法提高了模型的准确性,同时模型储备动态在整个时间内与观察到的体脂肪百分比密切相关。新方法假设消化效率随体型增加而增加通过数据收集验证这种关系将加强 DEB 理论的基础,并支持在生态风险评估中使用它的理由。