Kuperman Roman G, Checkai Ronald T, Simini Michael, Phillips Carlton T, Kolakowski Jan E, Kurnas Carl W
U.S. Army Edgewood Chemical Biological Center, 5183 Blackhawk Road, Aberdeen Proving Ground, Maryland 21010-5424, USA.
Environ Toxicol Chem. 2006 May;25(5):1368-75. doi: 10.1897/05-475r1.1.
Scientifically based ecological soil-screening levels are needed to identify concentrations of contaminant energetic materials (EMs) in soil that present an acceptable ecological risk at a wide range of military installations. Insufficient information regarding the toxicity of 2,4-dinitrotoluene (2,4-DNT), 2,6-dinitrotoluene (2,6-DNT), and 1,3,5-trinitrobenzene (TNB) to soil invertebrates necessitated toxicity testing. We adapted the standardized Enchytraeid Reproduction Test (International Standardization Organization 16387:2003) and selected Enchytraeus crypticus for these studies. Tests were conducted in Sassafras sandy loam soil, which supports relatively high bioavailability of nitroaromatic EMs. Weathering and aging procedures for EMs amended to test soil were incorporated into the study design to produce toxicity data that better reflect the soil exposure conditions in the field compared with toxicity in freshly amended soils. This included exposing hydrated, EM-amended soils in open glass containers in the greenhouse to alternating wetting and drying cycles. Definitive tests established that the order of EM toxicity to E. crypticus based on the median effect concentration values for juvenile production in either freshly amended or weathered and aged treatments was (from the greatest to least toxicity) TNB > 2,4-DNT > 2,6-DNT. Toxicity to E. crypticus juvenile production was significantly increased in 2,6-DNT weathered and aged soil treatments compared with toxicity in freshly amended soil, based on 95% confidence intervals. This result shows that future investigations should include a weathering and aging component to generate toxicity data that provide more complete information regarding ecotoxicological effects of energetic contaminants in soil.
需要基于科学的生态土壤筛选水平来确定在众多军事设施中,土壤中污染物高能材料(EMs)的浓度,这些浓度所呈现的生态风险是可接受的。关于2,4 -二硝基甲苯(2,4 - DNT)、2,6 -二硝基甲苯(2,6 - DNT)和1,3,5 -三硝基苯(TNB)对土壤无脊椎动物毒性的信息不足,因此需要进行毒性测试。我们采用了标准化的蚯蚓繁殖试验(国际标准化组织16387:2003),并选择了隐尾蚓进行这些研究。试验在黄樟砂壤土中进行,这种土壤能使硝基芳香族EMs具有相对较高的生物利用度。将添加到测试土壤中的EMs的风化和老化程序纳入研究设计,以生成毒性数据,与新添加土壤中的毒性相比,这些数据能更好地反映田间土壤的暴露条件。这包括将添加了EMs的湿润土壤置于温室中的敞口玻璃容器内,使其经历交替的干湿循环。确定性试验表明,基于新添加或风化老化处理中幼体生产的半数效应浓度值,EMs对隐尾蚓的毒性顺序为(从毒性最大到最小)TNB > 2,4 - DNT > 2,6 - DNT。基于95%置信区间,与新添加土壤中的毒性相比,在2,6 - DNT风化老化土壤处理中,对隐尾蚓幼体生产的毒性显著增加。这一结果表明,未来的研究应包括风化和老化部分,以生成毒性数据,从而提供关于土壤中高能污染物生态毒理效应的更完整信息。