Department of Environmental Science, Aarhus University , Frederiksborgvej 399, 4000 Roskilde, Denmark.
Department of Plant and Environmental Sciences, University of Copenhagen , Thorvaldsensvej 40, 1871 Frederiksberg, Denmark.
Environ Sci Technol. 2017 Apr 4;51(7):3694-3702. doi: 10.1021/acs.est.6b05512. Epub 2017 Mar 23.
Biocides are common additives in building materials. In-can and film preservatives in polymer-resin render and paint, as well as wood preservatives are used to protect facade materials from microbial spoilage. Biocides leach from the facade material with driving rain, leading to highly polluted runoff water (up to several mg L biocides) being infiltrated into the soil surrounding houses. In the present study the degradation rates in soil of 11 biocides used for the protection of building materials were determined in laboratory microcosms. The results show that some biocides are degraded rapidly in soil (e.g., isothiazolinones: T < 10 days) while others displayed higher persistence (e.g., terbutryn, triazoles: T ≫ 120 days). In addition, mass balances of terbutryn and octylisothiazolinone were determined, including nine (terbutryn) and seven (octylisothiazolinone) degradation products, respectively. The terbutryn mass balance could be closed over the entire study period of 120 days and showed that relative persistent metabolites were formed, while the mass balances for octylisothiazolinone could not be closed. Octylisothiazolinone degradation products did not accumulate over time suggesting that the missing fraction was mineralized. Microtox-tests revealed that degradation products were less toxic toward the bacterium Aliivibrio fischeri than their parent compounds. Rain is mobilizing these biocides from the facades and transports them to the surrounding soils; thus, rainfall events control how often new input to the soil occurs. Time intervals between rainfall events in Northern Europe are shorter than degradation half-lives even for many rapidly degraded biocides. Consequently, residues of some biocides are likely to be continuously present due to repeated input and most biocides can be considered as "pseudo-persistent"-contaminants in this context. This was verified by (sub)urban soil screening, where concentrations of up to 0.1 μg g were detected for parent compounds as well as terbutryn degradation products in soils below biocide treated facades.
杀菌剂是建筑材料中常见的添加剂。聚合物树脂中的罐内和薄膜防腐剂以及木材防腐剂用于保护外墙材料免受微生物破坏。杀菌剂随急降雨从外墙材料中渗出,导致受污染的径流水(高达几毫克/升的杀菌剂)渗透到房屋周围的土壤中。在本研究中,在实验室微环境中确定了用于保护建筑材料的 11 种杀菌剂在土壤中的降解速率。结果表明,一些杀菌剂在土壤中迅速降解(例如,异噻唑啉酮:T < 10 天),而其他杀菌剂则显示出更高的持久性(例如,特丁津、三唑:T ≫ 120 天)。此外,还确定了特丁津和辛基异噻唑啉酮的质量平衡,分别包括九个(特丁津)和七个(辛基异噻唑啉酮)降解产物。特丁津的质量平衡可以在整个 120 天的研究期间关闭,并表明形成了相对持久的代谢物,而辛基异噻唑啉酮的质量平衡无法关闭。辛基异噻唑啉酮降解产物不会随时间积累,表明缺失的部分被矿化。Microtox 测试表明,降解产物对细菌 Aliivibrio fischeri 的毒性低于其母体化合物。雨水将这些杀菌剂从外墙中迁移出来并运送到周围的土壤中;因此,降雨事件控制着新输入土壤的频率。北欧的降雨事件之间的时间间隔比许多快速降解的杀菌剂的半衰期还要短。因此,由于重复输入,一些杀菌剂的残留物可能会持续存在,而且在这种情况下,大多数杀菌剂都可以被认为是“准持久性”污染物。这一点通过(城市)郊区土壤筛选得到了验证,在受杀菌剂处理的外墙下方的土壤中,检测到母体化合物以及特丁津降解产物的浓度高达 0.1μg/g。