Department of Civil Engineering, IIT(BHU), Varanasi 221005, India.
Department of Civil Engineering, IIT(BHU), Varanasi 221005, India.
Sci Total Environ. 2024 Jun 10;928:172358. doi: 10.1016/j.scitotenv.2024.172358. Epub 2024 Apr 12.
Pharmaceuticals are one of the emerging pollutants (EPs) in river waters across the world. Due to their toxic effects on aquatic organisms, they have drawn the global attention of the scientific community concerned with river ecosystems. This paper reviews the existing occurrence data for various pharmaceutical pollutants (PPs) reported in river waters in some part of the world and their ecological impacts. Using algae, macroinvertebrates (MI), and fish as biotic indicator groups in water to reflect river health conditions, an attempt has been made to assess the ecological risk due to the presence of PPs in the water environment. After ascertaining the predicted no-effect concentration (PNEC) of PPs for selected groups of aquatic organisms, the risk quotient (RQ) is estimated based on their measured environmental concentration (MEC). When MEC > PNEC and RQ > 1 for any of the biotic indicator, ecologically it is 'high risk' condition. The determination of PNEC uses a minimum assessment factor (AF) of 10 due to uncertainty in data over the no observed effect level (NOEL) or lowest observed effect level (LOEL). Accordingly, MEC 10 times higher than PNEC, (RQ = 10) represents a threshold risk concentration (RC) beyond which adverse effects may start showing observable manifestations. In the present study, a new classification system of 'high risk' conditions for RQ = 1-10 has been proposed, starting from 'moderately high' to 'severely high'. For RQ > 10, the ecological condition of the river is considered 'impaired'. For river health assessment, in the present study, the whole range of physico-chemical characteristics of river water quality has been divided into three groups based on their ease of measurement and frequency of monitoring. Dissolved oxygen related parameters (DORPs), nutrients (NTs), and EPs. PPs represent EPs in this study. A framework for calculating separate indicator group score (IGS) and the overall river health index (RHI) has been developed to predict indicator group condition (IGC) and river health condition (RHC), respectively. Color-coded hexagonal pictorial forms representing IGC and RHC provide a direct visible perception of the existing aquatic environment and a scientific basis for prioritization of corrective measures in terms of treatment technology selection for river health improvements. The analyses indicate that many rivers across the world are under 'high risk' conditions due to PPs having MEC > PNEC and RQ > 1. Up to RC, (where RQ = 10), the 'high risk' condition varies from 'moderately high' to 'severely high'. In many instances, RQ is found much more higher than 10, indicating that the ecological condition of river may be considered as 'impaired'. Algae is the most frequently affected group of biotic indicators, followed by MI and fish. A review of treatment methods for selection of appropriate technology to reduce the pollution load, especially PPs from the wastewater streams has been summarized. It appears that constructed wetlands (CWs) are at present the most suitable nature-based solutions, particularly for the developing economies of the world, to reduce the concentrations of PPs within limits to minimize the ecological impacts of pharmaceutical compounds on biotic indicators and restore the river health condition. Some suggestive design guidelines for the CWs have also been presented to initiate the process.
药品是世界范围内河流中新兴的污染物(EPs)之一。由于它们对水生生物的毒性作用,已经引起了科学界对河流生态系统的关注。本文综述了世界部分地区河流中各种药品污染物(PPs)的现有出现数据及其生态影响。使用藻类、大型无脊椎动物(MI)和鱼类作为水生生物指示群,反映河流健康状况,试图评估水环境中存在的 PPs 所带来的生态风险。在确定所选水生生物群体的预测无效应浓度(PNEC)后,基于其测量的环境浓度(MEC)估算风险商(RQ)。当任何生物指标的 MEC > PNEC 和 RQ > 1 时,从生态角度来看,这是“高风险”条件。PNEC 的确定使用最小评估因子(AF)为 10,因为在无观察到效应水平(NOEL)或最低观察到效应水平(LOEL)的数据中存在不确定性。因此,MEC 比 PNEC 高 10 倍(RQ = 10)表示可能开始出现不良反应的阈值风险浓度(RC)。在本研究中,提出了一种新的 RQ = 1-10 的“高风险”条件分类系统,从“中度高”到“重度高”。当 RQ > 10 时,河流的生态状况被认为是“受损”的。对于河流健康评估,在本研究中,根据其测量的难易程度和监测的频率,将整个河流水质理化特征分为三组。与溶解氧相关的参数(DORPs)、营养物(NTs)和药品。在本研究中,PPs 代表药品。已经开发了一种计算单独指示组得分(IGS)和整体河流健康指数(RHI)的框架,分别用于预测指示组状况(IGC)和河流健康状况(RHC)。表示 IGC 和 RHC 的彩色六边形图片形式提供了对现有水生环境的直接可见感知,并为基于治疗技术选择的河流健康改善措施的优先级提供了科学依据。分析表明,由于 MEC > PNEC 和 RQ > 1,世界上许多河流都处于“高风险”状态。在 RC 之前(其中 RQ = 10),“高风险”状态从“中度高”到“重度高”不等。在许多情况下,RQ 远高于 10,表明河流的生态状况可能被认为是“受损”的。藻类是受生物指示群影响最频繁的群体,其次是 MI 和鱼类。总结了选择适当技术减少污染负荷,特别是减少废水中药品浓度的处理方法的回顾,以最大限度地减少药品化合物对生物指示物的生态影响并恢复河流健康状况。还提出了一些关于人工湿地(CWs)的设计建议,以启动该过程。