Anthropogenic disturbances on distribution and sources of pharmaceuticals and personal care products throughout the Jinsha River Basin, China
Introduction
Pharmaceutical and personal care products (PPCPs) are a group of emerging contaminants that include prescription, nonprescription, and veterinary drugs as well as chemical ingredients of personal health and cleaning products (Boxall et al., 2012; Daughton, 2016). PPCPs have increasingly raised concerns since they are extensively used and continuously released into river ecosystems, and consequently cause a series of adverse effects including endocrine disruption, antibiotic resistance and even decline of biodiversity (Rosi-Marshall and Royer, 2012; Tijani et al., 2016). To assess and mitigate the human health and ecological risks of PPCPs, their sources and distribution patterns in river systems have been documented globally since the 1990s (Daughton, 2016). PPCPs enter river water primarily through wastewater treatment plants, and their contamination of river water is ubiquitous, with levels ranging from nano-to micrograms per liter (Aus et al., 2016; Burns et al., 2018; Wu et al., 2014). Despite some PPCPs are not inherently persistent in the environment, PPCPs are regarded as “pseudo-persistent” contaminants due to their sustained discharge and partial metabolism (Ellis, 2006; Ternes et al., 2004). These ubiquitous chemicals may lead to severe aquatic pollution worldwide with chronic exposure even at a low concentration (Peng et al., 2018; Santos et al., 2010; Wilkinson et al., 2017).
Anthropogenic activities play a critical role in PPCP contamination in the environment. Previous investigations indicated that the PPCP contamination was mainly associated with anthropogenic activities including the treatment and discharge of municipal sewage and industrial wastewater, livestock breeding, aquaculture, and landfill, leading to the presence of PPCPs in an aquatic environment (Xu et al., 2019; Yang et al., 2020). Meanwhile, different PPCP categories are variously related to different anthropogenic activities. For instance, therapeutic PPCPs have been generally considered to be related to the medical treatment level, and the elevated concentrations have been detected in the receiving water nearby hospitals (Spongberg et al., 2011). The agricultural activities, such as pesticide application, livestock rearing, and manure application, have been reported to release agricultural herbicides and pesticides into the aquatic environment (Fairbairn et al., 2015). However, most of previous studies have focused on a single class of PPCPs and associated anthropogenic activities, a comprehensive investigation was lack to establish the link between large class of PPCP categories with multiple anthropogenic activities, especially at large-scale watershed.
The Jinsha River is the upper reach of the Yangtze River in southwestern China. Most areas along this river are less urbanized, and it therefore serves as an important ecological barrier in China (Jun et al., 2013). Pollution in the Jinsha River deteriorates the downstream water quality of the Yangtze River and threatens both public health and ecosystems (Wang et al., 2015b). Since the Jinsha River Basin is large and located in a mountainous region (Zhou et al., 2018), sample collection is difficult, and its pollution condition has consequently been poorly investigated. Previous studies have revealed only heavy metal contamination, nutrients, and polycyclic aromatic hydrocarbon in some parts of the Jinsha River (Jun et al., 2003; Teng et al., 2011). However, the distribution of large PPCP classes along the entire Jinsha River Basin has not been explored. The Jinsha River has been subject to increasing anthropogenic activities, especially human habitation and dam construction, which may be regarded as potential sources of PPCPs. The Jinsha River originates in a pristine area and flows through the famous “Hu Huanyong line”, which delineates the striking difference in the distribution of China's population. With increasing human habitation, more PPCPs may be discharged into the river. The operation and management activities of hydropower stations might serve as another source of PPCPs, since these contaminants enter the environment through the activities of the staff in hydropower management station (Olsen et al., 2009). However, the influence of anthropogenic activities on PPCP distribution and sources along the Jinsha River remains unclear.
Land use patterns (including agricultural, urban, grassland and other land use) provides strong evidence of anthropogenic conditions along rivers, and land use can affect aquatic ecosystems via erosive processes (Likens and Bormann, 1974). As different PPCPs are discharged into rivers via multiple anthropogenic pathways (Liu and Wong, 2013), land use patterns may reflect the influence of multiple anthropogenic activities on PPCP composition, and may indicate potential PPCP sources in the river. Therefore, it is hypothesized that PPCP distribution and sources may be associated with land use patterns at large-scale watershed.
To test this hypothesis and address the abovementioned gap in knowledge, this study aimed to (1) provide an overview of the occurrence and concentrations of different PPCP categories in the surface water of the entire Jinsha River, (2) determine the impact of anthropogenic activities on PPCP distribution along the river, and (3) investigate PPCP sources (focusing on land use patterns) based on a statistical approach.
Section snippets
Study area and field sampling procedure
The Jinsha River is the upper reach of the Yangtze River and has a total length of 2316 km and an area of 340000 km2 (Zhou et al., 2018). The northern part of the river basin forms part of the Qinghai–Tibet Plateau (Tongtian River), and the southern part forms the western margin of the Sichuan Basin (Yinbin City). The Hu Huanyong line divides the Jinsha River into two parts along the midstream area of the river and is primarily based on the level of human habitation (Hu et al., 2016). The
Land use conditions of the Jinsha River
The land use conditions of the Jinsha River are listed in Table S1. The elevation gradually decreased from the source of the river (N1, 3552 m) to the end of the river (YBD, 330 m), and the land use condition was gradually changed along the river. In the upstream area of the Jinsha River, grass land (49.57%) and forest (42.86%) were the major land use types. Cultivated land gradually expanded in the mid- and downstream areas, accounting for 19.36 and 33.49% of land use, respectively. Artificial
Overview of PPCP occurrence and concentration in the Jinsha River
China is a large country with high PPCP productions and usage volumes, which may result in promoted PPCP levels in aquatic environments (Liu and Wong, 2013). Most investigations have been carried out in highly developed river basins, such as the Pearl, Yangtze, and Haihe River Basins because of their dense population and rapid socioeconomic development. However, the extent of PPCP contamination in the less developed areas of the Jinsha River Basin remains unclear. In this study, a large group
Conclusions
The present study showed that the PPCP concentrations were magnitudes lower in the Jinsha River than in other major rivers in China and globally. Nonetheless, the distribution of PPCPs in the Jinsha River was widespread, and some compounds could threaten ecosystems and human health. PPCP distribution differed significantly between the two sides of the Hu Huanyong line, indicating that human habitation significantly influenced PPCP distribution. Dam construction both intercepted PPCPs and served
Credit author statement
Sheng Liu: Conceptualization, Methodology, Software, Investigation, Writing – original draft, Visualization. Chao Wang: Conceptualization, Writing – review & editing. Peifang Wang: Conceptualization, Writing – review & editing. Juan Chen: Investigation, Resources. Xun Wang: Investigation, Resources. Qiusheng Yuan: Investigation, Resources.
Declaration of competing interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgments
This work was supported by the National Key Plan for Research and Development of China (2016YFC0502203), the Key Program of National Natural Science Foundation of China (No. 91647206), and the National Science Funds for Creative Research Groups of China (No.51421006).
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