新关注的废水衍生污染物:模拟灌溉情景下土壤溶液中的浓度

Evyatar Ben Mordechay , Moshe Shenker , Jorge Tarchitzky , Vered Mordehay , Yoni Elisar , Yehoshua Maor , Jose Julio Ortega-Calvo , Dieter Hennecke , Tamara Polubesova , Benny Chefetz
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引用次数: 0

摘要

为了应对自然水源的减少,处理后的废水已被引入水循环,作为一种新的灌溉水源。然而,这种做法使农业环境暴露在各种新出现的令人担忧的污染物之下。为了更好地了解它们在土壤中的命运,并有效地预测它们在植物吸收中的生物利用度,需要量化它们在土壤溶液中的浓度。在这项研究中,我们检测了经处理的废水的浓度​在三种情况下,土壤解决方案中新出现的令人担忧的污染物:(1)从淡水灌溉转向经处理的废水(FW→TWW情景),(2)用处理过的废水进行长期连续灌溉(TWW→TWW情景),以及(3)用处理过的废水和淡水进行长期灌溉(TWW→FW场景)。新出现的令人担忧的污染物,包括卡马西平、1H-苯并三唑、拉莫三嗪、文拉法辛和噻苯唑,在处理过的废水中普遍存在(平均浓度为1259451803630和90​ng/L)和灌溉土壤。有趣的是,它们在土壤溶液中的浓度与灌溉水中的相应浓度不同(更高或更低)。在淡水至废水(FW→TWW)和处理后的废水转化为淡水(TWW→FW)灌溉情景中,与延长处理后的废水灌溉情景(TWW→TWW),表明在单个灌溉季节之后没有达到稳定状态条件。例如,Nir-Oz土壤溶液中1H-苯并三唑的浓度分别为638、310和1577​ng/L。此外​TWW中土壤溶液中的污染物浓度略低→FW灌溉方案与TWW的比较→TWW场景。我们的数据表明,雨水灌溉的作物也暴露在经过处理的废水衍生污染物中,这些污染物从吸附相释放到土壤溶液中,引起了人们的关注。土壤溶液中容易获得的污染物浓度取决于分子的物理化学性质、灌溉用水类型和灌溉历史、灌溉水中的污染物浓度和土壤特性。
本文章由计算机程序翻译,如有差异,请以英文原文为准。

Wastewater-derived contaminants of emerging concern: Concentrations in soil solution under simulated irrigation scenarios

Wastewater-derived contaminants of emerging concern: Concentrations in soil solution under simulated irrigation scenarios

In response to declineing natural water sources, treated wastewater has been introduced into the water cycle as a new water source for irrigation. However, this practice exposes the agricultural environment to various contaminants of emerging concern. To better understand their fate in the soil and to effectively predict their bioavailability for plant uptake, there is a need to quantify their concentrations in soil solutions. In this study, we examined the concentrations of treated wastewater-derived ​contaminants of emerging concern in soil solutions under three scenarios: (1) shifting from irrigation with freshwater to treated wastewater (FW→TWW scenario), (2) long-term continuous irrigation with treated wastewater (TWW→TWW scenario), and (3) prolonged irrigation with treated wastewater followed by freshwater (TWW→FW scenario). Contaminants of emerging concern including carbamazepine, 1H-benzotriazole, lamotrigine, venlafaxine, and thiabendazole were ubiquitous in the treated wastewater (mean concentrations of 125, 945, 180, 3630, and 90 ​ng/L, respectively) and irrigated soils. Interestingly, their concentrations in the soil solutions were different (higher or lower) from the corresponding concentrations in the irrigation water. In both the freshwater to wastewater (FW→TWW) and treated wastewater to freshwater (TWW→FW) irrigation scenarios, lower contaminant concentrations were observed in soil solutions compared to the prolong treated wastewater irrigation scenario (TWW→TWW), indicating that a steady state condition was not achieved after a single irrigation season. For example, the concentrations of 1H-benzotriazole in Nir Oz soil solutions were 638, 310, and 1577 ​ng/L for the three irrigation scenarios, respectively. Moreover, the ​contaminants concentrations in soil solutions were slightly lower in the TWW→FW irrigation scenario compared to the TWW→TWW scenario. Our data suggest that rain-fed crops are also exposed to treated wastewater-derived contaminants of emerging concern released from the adsorbed phase into the soil solution. The readily-available contaminants concentration in soil solution depends on the physicochemical properties of the molecule, the water type used for irrigation and the irrigation history, the contaminant concentration in the irrigation water, and soil characteristics.

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