Department of Civil, Construction and Environmental Engineering, Marquette University, P.O. Box 1881, Milwaukee, WI 53201, USA.
Department of Civil, Construction and Environmental Engineering, Marquette University, P.O. Box 1881, Milwaukee, WI 53201, USA.
J Hazard Mater. 2016 Nov 5;317:579-584. doi: 10.1016/j.jhazmat.2016.05.088. Epub 2016 Jun 1.
Most wastewater treatment processes are not specifically designed to remove micropollutants. Many micropollutants are hydrophobic so they remain in the biosolids and are discharged to the environment through land-application of biosolids. Micropollutants encompass a broad range of organic chemicals, including estrogenic compounds (natural and synthetic) that reside in the environment, a.k.a. environmental estrogens. Public concern over land application of biosolids stemming from the occurrence of micropollutants hampers the value of biosolids which are important to wastewater treatment plants as a valuable by-product. This research evaluated pyrolysis, the partial decomposition of organic material in an oxygen-deprived system under high temperatures, as a biosolids treatment process that could remove estrogenic compounds from solids while producing a less hormonally active biochar for soil amendment. The estrogenicity, measured in estradiol equivalents (EEQ) by the yeast estrogen screen (YES) assay, of pyrolyzed biosolids was compared to primary and anaerobically digested biosolids. The estrogenic responses from primary solids and anaerobically digested solids were not statistically significantly different, but pyrolysis of anaerobically digested solids resulted in a significant reduction in EEQ; increasing pyrolysis temperature from 100°C to 500°C increased the removal of EEQ with greater than 95% removal occurring at or above 400°C. This research demonstrates that biosolids treatment with pyrolysis would substantially decrease (removal>95%) the estrogens associated with this biosolids product. Thus, pyrolysis of biosolids can be used to produce a valuable soil amendment product, biochar, that minimizes discharge of estrogens to the environment.
大多数废水处理工艺并非专门设计用于去除微量污染物。许多微量污染物具有疏水性,因此它们会留在生物固体中,并通过生物固体的土地应用排放到环境中。微量污染物涵盖了广泛的有机化学品,包括环境雌激素,即存在于环境中的雌激素化合物(天然和合成)。公众对生物固体土地应用的担忧源于微量污染物的存在,这阻碍了生物固体作为废水处理厂有价值的副产品的价值。本研究评估了热解,即在缺氧系统中高温下部分分解有机物质,作为一种生物固体处理工艺,可以去除固体中的雌激素化合物,同时生产出一种激素活性较低的生物炭用于土壤改良。通过酵母雌激素筛选(YES)测定法,以雌二醇当量(EEQ)衡量的热解生物固体的雌激素活性,与原固体和厌氧消化生物固体进行了比较。原固体和厌氧消化固体的雌激素反应没有统计学上的显著差异,但厌氧消化固体的热解导致 EEQ 显著减少;将热解温度从 100°C 升高到 500°C,可增加 EEQ 的去除率,超过 95%的去除率发生在 400°C 或以上。本研究表明,采用热解法处理生物固体可大大降低(去除率>95%)与该生物固体产品相关的雌激素。因此,生物固体的热解可用于生产有价值的土壤改良剂生物炭,最大限度地减少雌激素向环境的排放。