Environmental Simulation and Pollution Control State Key Joint Laboratory, State Environmental Protection Key Laboratory of Microorganism Application and Risk Control (SMARC), School of Environment, Tsinghua University, Beijing 100084, China; Key Laboratory of Microorganism Application and Risk Control of Shenzhen, Graduate School at Shenzhen, Tsinghua University, Shenzhen 518055, China.
Key Laboratory of Microorganism Application and Risk Control of Shenzhen, Graduate School at Shenzhen, Tsinghua University, Shenzhen 518055, China.
J Environ Sci (China). 2017 Aug;58:51-63. doi: 10.1016/j.jes.2017.01.013. Epub 2017 Feb 10.
Chlorination is essential to the safety of reclaimed water; however, this process leads to concern regarding the formation of disinfection byproducts (DBPs) and toxicity. This study reviewed the formation and control strategies for DBPs and toxicity in reclaimed water during chlorination. Both regulated and emerging DBPs have been frequently detected in reclaimed water during chlorination at a higher level than those in drinking water, indicating they pose a greater risk to humans. Luminescent bacteria and Daphnia magna acute toxicity, anti-estrogenic activity and cytotoxicity generally increased after chlorination because of the formation of DBPs. Genotoxicity by umu-test and estrogenic activity were decreased after chlorination because of destruction of toxic chemicals. During chlorination, water quality significantly impacted changes in toxicity. Ammonium tended to attenuate toxicity changes by reacting with chlorine to form chloramine, while bromide tended to aggravate toxicity changes by forming hypobromous acid. During pretreatment by ozonation and coagulation, disinfection byproduct formation potential (DBPFP) and toxicity formation potential (TFP) occasionally increase, which is accompanied by DOC removal; thus, the decrease of DOC was limited to indicate the decrease of DBPFP and TFP. It is more important to eliminate the key fraction of precursors such as hydrophobic acid and hydrophilic neutrals. During chlorination, toxicities can increase with the increasing chlorine dose and contact time. To control the excessive toxicity formation, a relatively low chlorine dose and short contact time were required. Quenching chlorine residual with reductive reagents also effectively abated the formation of toxic compounds.
氯化是再生水安全处理的必要步骤,但这一过程会引起人们对消毒副产物(DBPs)和毒性形成的担忧。本研究综述了氯化过程中再生水中 DBPs 和毒性的形成和控制策略。在氯化过程中,经常会在再生水中检测到受管制和新兴的 DBPs,其浓度水平高于饮用水,表明它们对人类构成了更大的风险。发光细菌和大型蚤急性毒性、抗雌激素活性和细胞毒性通常会因 DBPs 的形成而在氯化后增加。由于有毒化学物质的破坏,umu 试验的遗传毒性和雌激素活性在氯化后降低。在氯化过程中,水质对毒性变化有显著影响。氨倾向于通过与氯反应形成氯胺来减弱毒性变化,而溴化物则倾向于通过形成次溴酸来加剧毒性变化。在臭氧预处理和混凝预处理过程中,消毒副产物生成潜力(DBPFP)和毒性生成潜力(TFP)偶尔会增加,同时伴随着 DOC 的去除;因此,DOC 的减少被限制在指示 DBPFP 和 TFP 的减少范围内。消除疏水性酸和亲水性中性等关键前体物质更为重要。在氯化过程中,随着氯剂量和接触时间的增加,毒性可能会增加。为了控制过度的毒性形成,需要使用相对较低的氯剂量和较短的接触时间。用还原性试剂淬灭余氯也能有效地减少有毒化合物的形成。