Environmental Laboratory, US Army Engineer Research and Development Center, Vicksburg, Mississippi, USA.
Department of Civil, Environmental, and Construction Engineering, Texas Tech University, Lubbock, Texas, USA.
Environ Toxicol Chem. 2022 Aug;41(8):1885-1902. doi: 10.1002/etc.5356. Epub 2022 Jun 22.
We evaluated the precision and accuracy of multilaboratory measurements for determining freely dissolved concentrations (C ) of polycyclic aromatic hydrocarbons (PAHs) and polychlorinated biphenyls (PCBs) in sediment porewater using polydimethylsiloxane (PDMS) and low-density polyethylene (LDPE) polymeric samplers. Four laboratories exposed performance reference compound (PRC) preloaded polymers to actively mixed and static ex situ sediment for approximately 1 month; two laboratories had longer exposures (2 and 3 months). For C results, intralaboratory precision was high for single compounds (coefficient of variation 50% or less), and for most PAHs and PCBs interlaboratory variability was low (magnitude of difference was a factor of 2 or less) across polymers and exposure methods. Variability was higher for the most hydrophobic PAHs and PCBs, which were present at low concentrations and required larger PRC-based corrections, and also for naphthalene, likely due to differential volatilization losses between laboratories. Overall, intra- and interlaboratory variability between methods (PDMS vs. LDPE, actively mixed vs. static exposures) was low. The results that showed C polymer equilibrium was achieved in approximately 1 month during active exposures, suggesting that the use of PRCs may be avoided for ex situ analysis using comparable active exposure; however, such ex situ testing may not reflect field conditions. Polymer-derived C concentrations for most PCBs and PAHs were on average within a factor of 2 compared with concentrations in isolated porewater, which were directly measured by one laboratory; difference factors of up to 6 were observed for naphthalene and the most hydrophobic PAHs and PCBs. The C results were similar for academic and private sector laboratories. The accuracy and precision that we demonstrate for determination of C using polymer sampling are anticipated to increase regulatory acceptance and confidence in use of the method. Environ Toxicol Chem 2022;41:1885-1902. © 2022 The Authors. Environmental Toxicology and Chemistry published by Wiley Periodicals LLC on behalf of SETAC. This article has been contributed to by U.S. Government employees and their work is in the public domain in the USA.
我们评估了使用聚二甲基硅氧烷(PDMS)和低密度聚乙烯(LDPE)聚合物采样器测定沉积物孔隙水中多环芳烃(PAHs)和多氯联苯(PCBs)游离溶解浓度(C)的多实验室测量的精度和准确性。四个实验室将预先加载有性能参考化合物(PRC)的聚合物暴露于主动混合和静态现场沉积物中约 1 个月;两个实验室的暴露时间更长(2 个月和 3 个月)。对于 C 的结果,单个化合物的实验室内精密度很高(变异系数为 50%或更低),并且对于大多数 PAHs 和 PCB,跨聚合物和暴露方法的实验室间变异性较低(差异幅度为 2 倍或更小)。最疏水的 PAHs 和 PCBs 的变异性更高,这些化合物的浓度较低,需要更大的基于 PRC 的校正,萘的变异性也更高,可能是由于实验室之间的挥发性损失不同。总体而言,方法之间(PDMS 与 LDPE、主动混合与静态暴露)的实验室内和实验室间变异性较低。结果表明,在主动暴露期间,大约 1 个月即可达到聚合物平衡,这表明在使用可比主动暴露进行现场分析时,可以避免使用 PRC;然而,这种现场测试可能无法反映现场条件。对于大多数 PCB 和 PAHs,聚合物衍生的 C 浓度与一个实验室直接测量的孤立孔隙水中的浓度平均相差 2 倍;对于萘和最疏水的 PAHs 和 PCBs,观察到的差异因子高达 6。学术和私营部门实验室的 C 结果相似。我们展示的使用聚合物采样测定 C 的准确性和精密度预计将提高监管机构对该方法的接受度和信心。环境毒理化学 2022;41:1885-1902。©2022 作者。环境毒理化学由 Wiley 期刊出版公司代表 SETAC 出版。本文由美国政府雇员做出贡献,其工作在美国属于公有领域。