Department of Chemistry, University of Bath, Bath BA2 7AY, UK; Water Innovation & Research Centre (WIRC), University of Bath, Bath BA2 7AY, UK; School of Pharmacy and Life Sciences, Robert Gordon University, Aberdeen AB10 7GJ, UK.
Department of Chemistry, University of Bath, Bath BA2 7AY, UK; Centre for Doctoral Training in Sustainable Chemical Technologies, University of Bath, Bath BA2 7AY, UK.
Sci Total Environ. 2018 Jul 15;630:648-657. doi: 10.1016/j.scitotenv.2018.02.242. Epub 2018 Feb 27.
The distribution of micropollutants in biotic phases of horizontal sub-surface flow (HSSF) constructed wetlands was investigated. 88 diverse micropollutants (personal care products, pharmaceuticals and illicit drugs) were monitored for in full-scale HSSF steel slag and gravel beds to assess their fate and behaviour during tertiary wastewater treatment. Of the studied micropollutants 54 were found in receiving and treated wastewaters. Treatment reduced concentrations of several micropollutants by >50% (removal range -112% to 98%) and resulted in changes to the stereo-isomeric composition of chiral species. For example, stereo-selective changes were observed for 3,4-methylenedioxymethamphetamine (MDMA) and atenolol during HSSF constructed wetland treatment for the first time. Analysis of sludge present within the HSSF beds found 37 micropollutants to be present. However, concentrations for the majority of these micropollutants were not considered high enough to suggest partitioning into sludge was a contributing mechanism of removal. Nevertheless the preservative methylparaben was found at 2772mgbed. Its daily removal from wastewater of 3.4mgd indicates partitioning and accumulation in sludge contributes to its removal. Other micropollutants found at high levels in sludge (relative to their overall removals) were the antidepressants sertraline and fluoxetine, and the metabolite desmethylcitalopram. Furthermore, process balances indicated uptake and metabolism by Phragmites australis (Cav.) Trin. ex Steud did not contribute significantly to micropollutant removal. However analysis of plant tissues evidenced uptake, metabolism and accumulation of recalcitrant micropollutants such as ketamine and carbamazepine. It is considered that the rate of uptake was too slow to have a notable impact on removal at the 14h hydraulic retention time. Despite evidence of other removal mechanisms at play (e.g., partitioning into sludge and plant uptake), findings indicate biodegradation is the dominant mechanism of micropollutant removal in HSSF constructed wetlands.
本研究调查了水平潜流(HSSF)人工湿地生物相中微污染物的分布情况。在全尺寸 HSSF 钢渣和砾石床中监测了 88 种不同的微污染物(个人护理产品、药物和非法药物),以评估它们在三级废水处理过程中的归宿和行为。在所研究的微污染物中,有 54 种在接收和处理废水中被发现。处理将几种微污染物的浓度降低了>50%(去除范围为-112%至 98%),并导致手性物质的立体异构体组成发生变化。例如,在 HSSF 人工湿地处理过程中,首次观察到 3,4-亚甲二氧基甲基苯丙胺(MDMA)和阿替洛尔的立体选择性变化。对 HSSF 床内存在的污泥进行分析,发现有 37 种微污染物存在。然而,由于大多数微污染物的浓度没有高到足以表明分配到污泥是去除的一个贡献机制,因此没有考虑它们的浓度。然而,防腐剂甲基对羟基苯甲酸酯被发现存在于 2772mgbed 中。它每天从废水中去除 3.4mgd,表明分配和积累在污泥中有助于其去除。在污泥中含量较高(相对于其整体去除率)的其他微污染物是抗抑郁药舍曲林和氟西汀,以及代谢物去甲基西酞普兰。此外,过程平衡表明,湿地植物芦苇(Cav.)Trin. ex Steud 的吸收和代谢对微污染物的去除没有显著贡献。然而,对植物组织的分析表明,一些难降解的微污染物,如氯胺酮和卡马西平,被吸收、代谢和积累。考虑到吸收的速度太慢,在 14 小时水力停留时间内对去除没有显著影响。尽管有证据表明存在其他去除机制(例如,分配到污泥和植物吸收),但研究结果表明,生物降解是 HSSF 人工湿地去除微污染物的主要机制。