Export of dissolved carbonaceous and nitrogenous substances in rivers of the “Water Tower of Asia”
Graphical abstract
Introduction
As the “Water Tower of Asia,” the Tibetan Plateau feeds quite a few large rivers (e.g., the Yangtze River, the Yellow River, the Brahmaputra, the Mekong) in Asia (Immerzeel et al., 2010). There are more than 100 catchments with a drainage area > 2000 km2 on the plateau, among which twenty have drainage areas larger than 10,000 km2 (MWR, 2015). The outflow area of the rivers on the Tibetan Plateau is 1.2 × 106 km2, accounting for more than half of the entire land surface of the plateau (Cao et al., 2006). The Tibetan Plateau is also referred to as the “Third Pole” of the earth due to its extensive glacial and snow area (~ 100,000 km2) covering the vast high-altitude region (Wang et al., 2000, Yao et al., 2012). Snow and glacial melt water are important sources of rivers on the plateau, making up a contribution of 8%–27% to the regional river water flow (Lutz et al., 2014). Precipitation is another essential source for the Tibetan rivers. It was estimated that over 50% of total water flowing on the plateau was from local precipitation (Lutz et al., 2014). With global warming, the climate-sensitive glaciers on the Tibetan Plateau have shrunk ~ 10% during the years of 1970 to 2000 (Kang et al., 2010, Zhang et al., 2012a). In addition, the melting of glaciers can promote evapotranspiration and positively affect local precipitation (Du and Ma, 2004). Therefore, with the increasing glacier melt and precipitation, more runoff from rivers on the Tibetan Plateau can be expected in the future (Zhang et al., 2012b).
Considering the hydrologic and geochemical processes related to the outflows of the rivers, there could be some amount of carbon (C) and nitrogen (N) loss from the land surface of the Tibetan Plateau. Currently, most of the studies on the rivers of the Tibetan Plateau are related to water circulation and water quality, in consideration of its major role as a water resource for millions of people in both local and surrounding areas (Huang et al., 2009, Immerzeel et al., 2010, Li et al., 2011, Qu et al., 2015). However, data on the dissolved carbon and nitrogen substances in rivers of the Tibetan Plateau are still limited, despite their potential interactions with the regional carbon and nitrogen cycle in this area (Tong et al., 2016, Yang et al., 2014). Dissolved carbon (dissolved inorganic/organic carbon, DIC/DOC) and nitrogen (dissolved inorganic/organic nitrogen, DIN/DON) in rivers are critical components to the carbon and nitrogen cycle at both regional and global scales (IPCC, 2013). It has been proposed that concentrations of dissolved carbon and nitrogen in the global river systems have experienced a significant change due to human activity and global warming during the past hundred years (Evans et al., 2005, Howarth et al., 1996, Sillanpää, 2014, Valinia et al., 2015). Since the last century, the hydrologic processes on the Tibetan Plateau have been affected greatly by climate change (Immerzeel et al., 2010, Wang et al., 2013). Also, with increasing agricultural and industrial activities on the plateau, the local nitrogen cycles have been substantially altered in the preceding decades (Tong et al., 2016). Here we present the dissolved carbon and nitrogen concentrations from ten watersheds on the Tibetan Plateau, and the potential impact factors for the riverine carbon and nitrogen cycles in this ecologically fragile region are also discussed.
Section snippets
Field sampling
Water samples from 29 sites in nine large rivers on the Tibetan Plateau were collected during the monsoon season (July and August) from 2013 to 2015 (Fig. 1). The sampling work was conducted in three water systems: (1) In the Indian Ocean water system (IOWS), samples were collected in the Yarlung Tsangpo, Nu Jiang and Shiquan He, which are the upper reaches of the Brahmaputra River, the Salween River and the Indus, respectively. (2) In the Pacific Ocean water system (POWS), the sampling sites
Results and discussion
Riverine C and N characteristics are jointly affected by comprehensive factors, such as geological (e.g., topographical, soil/rock weathering), meteorological (e.g., temperature, precipitation), hydrological (e.g., runoff), land vegetation conditions, biota (e.g., microorganisms) and anthropogenic disturbances (e.g., agricultural and industrial activities) (Grabs et al., 2012, Meybeck, 1982, Tank et al., 2012). It was demonstrated that the riverine C and N features varied greatly in the
Conclusions
This study investigated the export of riverine C and N in ten large rivers on the Tibetan Plateau. It was shown that the concentrations of riverine C and N were affected notably by the hydrological conditions (e.g., runoff) within the catchments. Vegetation coverage in the river basins also has an important influence on the dissolved carbon and nitrogen on the Tibetan Plateau. DIC concentrations in rivers of the Tibetan Plateau (average DIC, 30.7 mg/L) were much higher than the world average due
Acknowledgments
This work was supported by the National Natural Science Foundation of China (Nos. 41675130, 41271015, 41225002), the Academy of Finland (decision number: 268170), and the State Key Laboratory of Cryospheric Science (SKLCS-ZZ-2008-01 and SKLCS-OP-2014-05). Dr. Shaopeng Gao and Dr. Xiaoqing Cui are thanked for their assistance with the measurement of C and N with the TOC analyzer, Dr. Zhiyong Wang is thanked for his sharing of the runoff data and Dr. Wei Yan is thanked for his assistance with the
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