Birch Heidi, Hammershøj Rikke, Comber Mike, Mayer Philipp
Technical University of Denmark, Department of Environmental Engineering, Building 115, 2800 Kgs. Lyngby, Denmark.
Mike Comber Consulting, Bridford, Exeter, UK.
Chemosphere. 2017 Oct;184:400-407. doi: 10.1016/j.chemosphere.2017.05.169. Epub 2017 Jun 2.
Biodegradation is a dominant removal process for many organic pollutants, and biodegradation tests serve as tools for assessing their environmental fate within regulatory risk assessment. In simulation tests, the inoculum is not standardized, varying in microbial quantity and quality, thereby potentially impacting the observed biodegradation kinetics. In this study we investigated the effect of inoculum origin on the biodegradation kinetics of hydrocarbons for five inocula from surface waters varying in urbanization and thus expected pre-exposure to petroleum hydrocarbons. A new biodegradation method for testing mixtures of hydrophobic chemicals at trace concentrations was demonstrated: Aqueous solutions containing 9 hydrocarbons were generated by passive dosing and diluted with surface water resulting in test systems containing native microorganisms exposed to test substances at ng-μg/L levels. Automated Headspace Solid Phase Microextraction coupled to GC-MS was applied directly to these test systems to determine substrate depletion relative to abiotic controls. Lag phases were generally less than 8 days. First order rate constants were within one order of magnitude for each hydrocarbon in four of the five waters but lower in water from a rural lake. The sequence of degradation between the 9 hydrocarbons showed similar patterns in the five waters indicating the potential for using selected hydrocarbons for benchmarking between biodegradation tests. Degradation half-times were shorter than or within one order of magnitude of BioHCwin predictions for 8 of 9 hydrocarbons. These results showed that location choice is important for biodegradation kinetics and can provide a relevant input to aquatic exposure and fate models.
生物降解是许多有机污染物的主要去除过程,生物降解测试是在监管风险评估中评估其环境归宿的工具。在模拟测试中,接种物未标准化,微生物数量和质量各不相同,从而可能影响观察到的生物降解动力学。在本研究中,我们调查了接种物来源对来自不同城市化程度地表水的五种接种物中烃类生物降解动力学的影响,因此预期这些接种物预先接触过石油烃。展示了一种用于测试痕量浓度下疏水性化学品混合物的新生物降解方法:通过被动加样生成含有9种烃类的水溶液,并用地表水稀释,从而得到含有天然微生物的测试系统,这些微生物暴露于纳克/微克/升水平的测试物质中。将自动顶空固相微萃取与气相色谱-质谱联用直接应用于这些测试系统,以确定相对于非生物对照的底物消耗情况。滞后期一般小于8天。五种水中四种水的每种烃的一级速率常数在一个数量级内,但来自农村湖泊的水中的速率常数较低。9种烃类之间的降解顺序在五种水中呈现出相似的模式,这表明有可能使用选定的烃类在生物降解测试之间进行基准比较。9种烃类中有8种的降解半衰期短于BioHCwin预测值或与预测值在一个数量级内。这些结果表明,地点选择对生物降解动力学很重要,并且可以为水生暴露和归宿模型提供相关输入。