Catalan Institute for Water Research (ICRA), Carrer Emili Grahit 101, 17003 Girona, Spain; University of Girona, Plaça de Sant Domenec 3, 17003 Girona, Spain.
Catalan Institute for Water Research (ICRA), Carrer Emili Grahit 101, 17003 Girona, Spain; IHE Delft Institute for Water Education, Westvest 7, 2601 DA Delft, the Netherlands.
Environ Int. 2020 Oct;143:105993. doi: 10.1016/j.envint.2020.105993. Epub 2020 Jul 29.
Human consumption of pharmaceuticals leads to high concentrations of pharmaceuticals in wastewater, which is usually not or insufficiently collected and treated before release into freshwater ecosystems. There, pharmaceuticals may pose a threat to aquatic biota. Unfortunately, occurrence data of pharmaceuticals in freshwaters at the global scale is scarce and unevenly distributed, thus preventing the identification of hotspots, the prediction of the impact of Global Change (particularly streamflow and population changes) on their occurrence, and the design of appropriate mitigation actions. Here, we use diclofenac (DCL) as a typical pharmaceutical contaminant, and a global model of DCL chemical fate based on wastewater sanitation, population density and hydrology to estimate current concentrations in the river network, the impact of future changes in runoff and population, and potential mitigation actions in line with the Sustainable Development Goals. Our model is calibrated against measurements available in the literature. We estimate that 2.74 ± 0.63% of global river network length has DCL concentrations exceeding the proposed EU Watch list limit (100 ng L). Furthermore, many rivers downstream from highly populated areas show values beyond 1000 ng L, particularly those associated to megacities in Asia lacking sufficient wastewater treatment. This situation will worsen with Global Change, as streamflow changes and human population growth will increase the proportion of the river network above 100 ng L up to 3.10 ± 0.72%. Given this background, we assessed feasible source and end-of-pipe mitigation actions, including per capita consumption reduction through eco-directed sustainable prescribing (EDSP), the implementation of the United Nations Sustainable Development Goal (SDG) 6 of halving the proportion of population without access to safely managed sanitation services, and improvement of wastewater treatment plants up to the Swiss standards. Among the considered end-of-pipe mitigation actions, implementation of SDG 6 was the most effective, reducing the proportion of the river network above 100 ng L down to 2.95 ± 0.68%. However, EDSP brought this proportion down to 2.80 ± 0.64%. Overall, our findings indicate that the sole implementation of technological improvements will be insufficient to prevent the expected increase in pharmaceuticals concentration, and that technological solution need to be combined with source mitigation actions.
人类对药品的消费导致了废水中高浓度的药品,这些废水通常未经收集或处理就排放到淡水生态系统中。在那里,药品可能对水生生物群构成威胁。不幸的是,全球范围内关于淡水中药品的出现数据稀缺且分布不均,因此无法确定热点地区,无法预测全球变化(特别是径流量和人口变化)对其出现的影响,也无法设计出适当的缓解措施。在这里,我们以双氯芬酸(DCL)为典型的药物污染物,利用基于废水卫生、人口密度和水文学的全球 DCL 化学命运模型来估计当前河网中的浓度、未来径流量和人口变化的影响,以及符合可持续发展目标的潜在缓解措施。我们的模型是根据文献中的测量数据进行校准的。我们估计,全球河网长度的 2.74±0.63% 具有超过建议的欧盟监测名单限值(100ng/L)的 DCL 浓度。此外,许多人口稠密地区下游的河流显示出超过 1000ng/L 的值,特别是亚洲那些缺乏足够废水处理的特大城市。随着全球变化,这种情况将会恶化,因为径流量变化和人口增长将使超过 100ng/L 的河网比例增加到 3.10±0.72%。鉴于这种背景,我们评估了可行的源头和末端缓解措施,包括通过生态导向的可持续处方(EDSP)减少人均消费、实施联合国可持续发展目标(SDG)6,将无法获得安全管理卫生服务的人口比例减半,以及将废水处理厂提高到瑞士标准。在所考虑的末端缓解措施中,实施可持续发展目标 6 是最有效的,将超过 100ng/L 的河网比例降低到 2.95±0.68%。然而,EDSP 将这一比例降低到 2.80±0.64%。总的来说,我们的研究结果表明,仅实施技术改进将不足以防止预期的药品浓度增加,需要将技术解决方案与源头缓解措施相结合。