Department of Health Sciences and Sciences, University of California - Los Angeles, Los Angeles, CA 90024, USA.
Sci Total Environ. 2024 Dec 1;954:176268. doi: 10.1016/j.scitotenv.2024.176268. Epub 2024 Sep 13.
Biosolids and sludge are what remain after the liquid fraction of wastewater is separated during wastewater treatment. These high organic content matrices are known to contain organic contaminants, a few of which are the hazardous and environmentally persistent per- and polyfluoroalkyl substances (PFAS). The current study investigates whether sludge from a treatment facility serving mostly industrial establishments and biosolids from a facility serving mostly domestic dwellings retain these 'forever chemicals' similarly. Using 31 markers covering different classes of PFAS, the sludge was found to contain higher levels of PFAS (869 ± 791 ng/g; 21 of 31) than biosolids (31 ± 7 ng/g, 11 of 31). The most abundant overall was perfluorooctane sulfonic acid (PFOS), mostly in sludge (range: 71-1300 ng/g versus 0-18 ng/g in biosolids). The large PFAS concentration variability in sludge was seasonal and sinusoidal. Sludge, additionally, contained all long chain PFAS, precursors (mostly surfactant ingredients and their transformation byproducts) and short chain PFAS (perhaps because of higher moisture content). By regression, the sludge is shown to consistently contain twice as much PFAS as biosolids when the same amounts are exposed to increasing levels of PFAS. Factors observed to cause differential PFAS retention between sludge and biosolids were moisture (98.6 % and 72.1 %, respectively), chain length, input quality (industrial versus residential) and functional group. Sulfonic acids for instance are one C atom shorter than carboxylates with similar occurrence in sludge and biosolids. More studies are needed to define the roles that organic carbon of sludge/biosolids, water chemistry, temperature and factors not considered here play in partitioning PFAS between the two matrices with respect to inputs. Existing K values could not help in explaining observed trends, but the ratio of biosolids-to-influent concentrations was found to correlate positively with PFAS size. Using influent in the ratio, and not effluent, is novel. SYNOPSIS: Sludge and biosolids are soil amendments; they contain hazardous and persistent PFAS. Methods of decoupling PFAS from these matrices start with understanding matrix-driven PFAS partitioning as shown here.
污水经过废水处理后,液体部分被分离,剩余的物质就是生物固体和污泥。这些高有机物含量的基质中含有有机污染物,其中有一些是危险的、环境持久性的全氟和多氟烷基物质(PFAS)。本研究调查了主要为工业企业服务的处理设施的污泥和主要为住宅服务的设施的生物固体是否同样含有这些“永久性化学物质”。使用涵盖不同 PFAS 类别的 31 种标记物,发现污泥中 PFAS 的含量(869±791ng/g;31 种中有 21 种)高于生物固体(31±7ng/g,31 种中有 11 种)。总体上最丰富的是全氟辛烷磺酸(PFOS),主要存在于污泥中(范围:71-1300ng/g,而生物固体中则为 0-18ng/g)。污泥中 PFAS 的浓度变化很大,呈季节性和正弦波状。此外,污泥中还含有所有长链 PFAS、前体(主要是表面活性剂成分及其转化的副产物)和短链 PFAS(可能是因为水分含量较高)。通过回归分析,当暴露于不断增加的 PFAS 水平时,与生物固体相比,污泥中始终含有两倍多的 PFAS。观察到导致污泥和生物固体中 PFAS 保留差异的因素是水分(分别为 98.6%和 72.1%)、链长、输入质量(工业与住宅)和官能团。例如,磺酸比羧酸少一个碳原子,但在污泥和生物固体中都有类似的存在。需要进一步研究来确定污泥/生物固体中的有机碳、水化学、温度以及此处未考虑的因素在输入方面对 PFAS 在这两种基质之间分配的作用。现有的 K 值无法帮助解释观察到的趋势,但发现生物固体与进水浓度的比值与 PFAS 大小呈正相关。使用进水比例而不是出水比例是一种新颖的方法。摘要:污泥和生物固体是土壤改良剂;它们含有危险且持久的 PFAS。从这里展示的方法开始,了解基质驱动的 PFAS 分配是分离这些基质中 PFAS 的方法之一。