Johnson M S, Paulus H I, Salice C J, Checkai R T, Simini M
United States Army Center for Health Promotion and Preventive Medicine, 5158 Blackhawk Rd., Toxicology Directorate, Aberdeen Proving Ground, Maryland 21010-5403, USA.
Arch Environ Contam Toxicol. 2004 Nov;47(4):496-501. doi: 10.1007/s00244-004-3242-7.
Red-backed salamanders (Plethodon cinereus) were exposed to four different concentrations of 1,3,5-trinitrohexahydro-1,3,5-triazine (RDX) in soil under controlled laboratory conditions for 28 days. Wild-caught P. cinereus (N = 20/treatment) were exposed to target concentrations of 5,000, 1000, 100, 10, and 0 mg RDX/kg soil (dry wt) using a microcosm design. Animals were fed 5 to 10 uncontaminated mutant Drosophila flies every 3 days and monitored daily. Animals were weighed 1 day before being placed in treatment and weekly thereafter. RDX concentrations in soil were analytically determined after the compound was added and mixed at the beginning, the midpoint, and the end of exposure. RDX soil concentrations were relatively stable throughout the exposure period. Signs of overt toxicity were observed primarily in the highest exposure group. Salamanders exposed to 5,000 mg RDX/kg soil exhibited signs of neuromuscular effects (lethargy, gaping, hypersensitivity, tremors) and exhibited significant weight loss. A single moribund animal from this group lost >20% of its original body weight and was killed. Animals in this exposure group also lost weight relative to animals in other treatments. Histopathologic evaluations, including an evaluation of melanomacrophage parameters, indicated no strong treatment-related findings. This study provided information regarding the effects from subchronic dermal exposure of a terrestrial amphibian species to RDX in soil and provides a microcosm approach to the evaluation of toxicity of contaminants in soil to a terrestrial vertebrate.
在实验室控制条件下,将红背蝾螈(Plethodon cinereus)暴露于土壤中四种不同浓度的1,3,5-三硝基六氢-1,3,5-三嗪(RDX)中,持续28天。使用微观生态系统设计,将野外捕获的红背蝾螈(每组N = 20)暴露于目标浓度为5000、1000、100、10和0 mg RDX/kg土壤(干重)的环境中。每隔3天给动物喂食5到10只未受污染的突变果蝇,并每天进行监测。在放入处理组前1天对动物称重,此后每周称重一次。在添加并混合化合物后,于暴露开始、中期和结束时分别分析测定土壤中的RDX浓度。在整个暴露期间,土壤中的RDX浓度相对稳定。明显的毒性迹象主要在最高暴露组中观察到。暴露于5000 mg RDX/kg土壤的蝾螈表现出神经肌肉效应的迹象(嗜睡、张口、过敏、震颤),并出现显著体重减轻。该组中有一只濒死动物体重减轻超过其原始体重的20%,随后被处死。与其他处理组的动物相比,该暴露组的动物体重也有所减轻。组织病理学评估,包括对黑素巨噬细胞参数的评估,未发现与处理相关的明显结果。本研究提供了关于陆生两栖动物亚慢性皮肤暴露于土壤中RDX的影响的信息,并提供了一种微观生态系统方法来评估土壤中污染物对陆生脊椎动物的毒性。