Editorial: Urban runoff of pollutants and their treatment

A. Zanoletti, E. Bontempi
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引用次数: 1

Abstract

Floods are one of the most common natural disasters worldwide. Their increasing incidence in the past years is mainly due to the consequences of climate change coupled with a general trend of the increase of surface impermeabilization in the cities. In particular, the past years’ rapid urbanization and human land use originated environment modification, with consequent surface modification: in the urban area, most of the surface is covered by buildings and impermeable pavements, which strongly limits snowmelt and rainwater infiltration into the subsurface. However, floods are sometimes predictable events (Enríquez et al., 2022). To account for the vulnerability of a territory, due to extreme events, patterns of development coupled with demographic studies are considered. As a result, the score of flood risk is available as a risk index, evaluated by a dedicated committee of the European (European Commission, 2022). The 2022 flood risk is shown in Figure 1. It appears that only a few countries have a relatively low risk (less than 5), and Vietnam and Bangladesh are the countries with the higher flood risk (the index score is 10). Urban runoff is water deriving from rain and outdoor water usage, comprising stormwater and snowmelt, which drains from roofs, roads, car parks sidewalks, driveways, and other surfaces, and does not soak into the ground. It is widely recognised as a major carrier for the pollutants transport and release in the urban environment. Therefore, it also represents a significant contributor to the degradation of surface water bodies (EPA, 2003). As a consequence, urban runoff is one of the key pathways in the transfer of pollutants to the aquatic and marine environment. The contaminants associated with urban runoff can be divided into different categories such as heavy metals, solids, toxic chemicals, biodegradable organic matter (chemical or biochemical oxygen demand COD/BOD), organic micropollutants (among them polycyclic aromatic hydrocarbons PAHs, polychlorinated biphenyls PCBs), pathogenic microorganisms (such as Escherichia Coli), nutrients (nitrogen and phosphorus) and microplastics (Wei et al., 2013; Piñon-Colin et al., 2020). For example, Wang et al. (2022) reveal that the concentrations of microplastics in urban stormwater are much higher than those found in wastewater effluents. The source of pollutants can be natural (soil, leaves and organic debris) or anthropogenic (construction materials, exhausted particles, roadway debris, fertilizers, and so on) (TrujilloGonzález et al., 2019). Generally, the road deposited sediment represents one of the primary contaminants contributors to urban runoff (Piñon-Colin et al., 2020). In the worst cases, when the stormwater collection is in connection with the sanitary sewage system, an accidental release of raw sewage may also happen because of important precipitation events, with the result of dramatic environmental and economic impacts. OPEN ACCESS
社论:城市污染物径流及其处理
洪水是全世界最常见的自然灾害之一。在过去几年中,其发病率的增加主要是由于气候变化的后果,加上城市表面不渗透性的普遍趋势。特别是,过去几年的快速城市化和人类土地利用引发了环境变化,随之而来的是地表变化:在城市地区,大部分地表被建筑物和不透水的人行道覆盖,这大大限制了融雪和雨水渗入地下。然而,洪水有时是可预测的事件(Enríquez等人,2022)。为了说明一个领土因极端事件而变得脆弱,考虑了发展模式和人口研究。因此,洪水风险得分可作为风险指数,由欧盟专门委员会进行评估(欧盟委员会,2022)。2022年洪水风险如图1所示。似乎只有少数国家的洪水风险相对较低(低于5),越南和孟加拉国是洪水风险较高的国家(指数得分为10)。城市径流是雨水和室外用水产生的水,包括雨水和融雪,从屋顶、道路、停车场、人行道、车道和其他表面排出,不会渗入地面。它被广泛认为是城市环境中污染物运输和释放的主要载体。因此,它也是地表水体退化的重要因素(EPA,2003)。因此,城市径流是污染物向水生和海洋环境转移的关键途径之一。与城市径流相关的污染物可分为不同类别,如重金属、固体、有毒化学品、可生物降解的有机物(化学或生化需氧量COD/BOD)、有机微污染物(其中包括多环芳烃PAHs、多氯联苯PCBs)、病原微生物(如大肠杆菌)、,营养素(氮和磷)和微塑料(Wei等人,2013;Piñon-Colin等人,2020)。例如,王等人(2022)揭示了城市雨水中微塑料的浓度远高于废水中的微塑料浓度。污染物的来源可以是自然的(土壤、树叶和有机碎屑),也可以是人为的(建筑材料、废气颗粒、道路碎屑、肥料等)(TrujilloGonzález等人,2019)。一般来说,道路沉积的沉积物是城市径流的主要污染物之一(Piñon-Colin等人,2020)。在最坏的情况下,当雨水收集与生活污水系统相连时,由于重要的降水事件,也可能发生未经处理的污水的意外排放,从而产生巨大的环境和经济影响。开放存取
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