Water use patterns of dominant species of riparian wetlands in arid areas
Lei Wang
College of Geography and Environment Science, Northwest Normal University, Lanzhou, Gansu, China
Shiyang River Ecological Environment Observation Station, Northwest Normal University, Lanzhou, Gansu, China
Search for more papers by this authorCorresponding Author
Guofeng Zhu
College of Geography and Environment Science, Northwest Normal University, Lanzhou, Gansu, China
Shiyang River Ecological Environment Observation Station, Northwest Normal University, Lanzhou, Gansu, China
Correspondence
Guofeng Zhu, College of Geography and Environment Science, Northwest Normal University, 967 East Road, Lanzhou, Gansu 730000, China.
Email: [email protected]
Search for more papers by this authorXinrui Lin
College of Geography and Environment Science, Northwest Normal University, Lanzhou, Gansu, China
Shiyang River Ecological Environment Observation Station, Northwest Normal University, Lanzhou, Gansu, China
Search for more papers by this authorYuwei Liu
College of Geography and Environment Science, Northwest Normal University, Lanzhou, Gansu, China
Shiyang River Ecological Environment Observation Station, Northwest Normal University, Lanzhou, Gansu, China
Search for more papers by this authorKailiang Zhao
College of Geography and Environment Science, Northwest Normal University, Lanzhou, Gansu, China
Shiyang River Ecological Environment Observation Station, Northwest Normal University, Lanzhou, Gansu, China
Search for more papers by this authorLiyuan Sang
College of Geography and Environment Science, Northwest Normal University, Lanzhou, Gansu, China
Shiyang River Ecological Environment Observation Station, Northwest Normal University, Lanzhou, Gansu, China
Search for more papers by this authorWenhao Zhang
College of Geography and Environment Science, Northwest Normal University, Lanzhou, Gansu, China
Shiyang River Ecological Environment Observation Station, Northwest Normal University, Lanzhou, Gansu, China
Search for more papers by this authorDongdong Qiu
College of Geography and Environment Science, Northwest Normal University, Lanzhou, Gansu, China
Shiyang River Ecological Environment Observation Station, Northwest Normal University, Lanzhou, Gansu, China
Search for more papers by this authorZhuanxia Zhang
College of Geography and Environment Science, Northwest Normal University, Lanzhou, Gansu, China
Shiyang River Ecological Environment Observation Station, Northwest Normal University, Lanzhou, Gansu, China
Search for more papers by this authorZhigang Sun
College of Geography and Environment Science, Northwest Normal University, Lanzhou, Gansu, China
Shiyang River Ecological Environment Observation Station, Northwest Normal University, Lanzhou, Gansu, China
Search for more papers by this authorLei Wang
College of Geography and Environment Science, Northwest Normal University, Lanzhou, Gansu, China
Shiyang River Ecological Environment Observation Station, Northwest Normal University, Lanzhou, Gansu, China
Search for more papers by this authorCorresponding Author
Guofeng Zhu
College of Geography and Environment Science, Northwest Normal University, Lanzhou, Gansu, China
Shiyang River Ecological Environment Observation Station, Northwest Normal University, Lanzhou, Gansu, China
Correspondence
Guofeng Zhu, College of Geography and Environment Science, Northwest Normal University, 967 East Road, Lanzhou, Gansu 730000, China.
Email: [email protected]
Search for more papers by this authorXinrui Lin
College of Geography and Environment Science, Northwest Normal University, Lanzhou, Gansu, China
Shiyang River Ecological Environment Observation Station, Northwest Normal University, Lanzhou, Gansu, China
Search for more papers by this authorYuwei Liu
College of Geography and Environment Science, Northwest Normal University, Lanzhou, Gansu, China
Shiyang River Ecological Environment Observation Station, Northwest Normal University, Lanzhou, Gansu, China
Search for more papers by this authorKailiang Zhao
College of Geography and Environment Science, Northwest Normal University, Lanzhou, Gansu, China
Shiyang River Ecological Environment Observation Station, Northwest Normal University, Lanzhou, Gansu, China
Search for more papers by this authorLiyuan Sang
College of Geography and Environment Science, Northwest Normal University, Lanzhou, Gansu, China
Shiyang River Ecological Environment Observation Station, Northwest Normal University, Lanzhou, Gansu, China
Search for more papers by this authorWenhao Zhang
College of Geography and Environment Science, Northwest Normal University, Lanzhou, Gansu, China
Shiyang River Ecological Environment Observation Station, Northwest Normal University, Lanzhou, Gansu, China
Search for more papers by this authorDongdong Qiu
College of Geography and Environment Science, Northwest Normal University, Lanzhou, Gansu, China
Shiyang River Ecological Environment Observation Station, Northwest Normal University, Lanzhou, Gansu, China
Search for more papers by this authorZhuanxia Zhang
College of Geography and Environment Science, Northwest Normal University, Lanzhou, Gansu, China
Shiyang River Ecological Environment Observation Station, Northwest Normal University, Lanzhou, Gansu, China
Search for more papers by this authorZhigang Sun
College of Geography and Environment Science, Northwest Normal University, Lanzhou, Gansu, China
Shiyang River Ecological Environment Observation Station, Northwest Normal University, Lanzhou, Gansu, China
Search for more papers by this authorAbstract
Water resource shortage in arid areas is the main cause of ecological problems. Understanding plant water use patterns is essential for understanding soil–plant interactions and assessing the adaptability of plants in ecosystems with limited water resources. Riparian wetlands are functional transition areas connecting aquatic ecosystems and terrestrial ecosystems. Wetland vegetation restoration is of great significance to water conservation and ecological balance. Using isotope tracing method, our study clarified the water use patterns of dominant plants in typical riparian wetlands in arid areas. The results showed that the dominant herbal species of Salsola affinis mainly used 0–60 cm soil water (48.96%). Salsola affinis, which continuously obtains water from shallow soil, may be difficult to survive in extreme drought conditions. If it withered significantly aged in the dry season, it would have a negative ecological impact. The dominant tree species of Salix matsudana Koidz mainly used 20–100 cm soil water (43.99%) and groundwater (23.16%). With increasing water stress, S. matsudana Koidz had a greater degree of ecological plasticity and can use water from deeper soils. However, S. matsudana Koidz can continuously obtained water from deep soil and groundwater, which may weaken the water and soil conservation capacity of the wetland. In addition, the lc-excess value of soil water showed that the soil evaporation intensity of grassland was higher than that of forest land, and the surface evaporation depth reached 60 cm. Our findings will help better understand the impact of vegetation restoration plan (artificial forest land and natural grassland) on the hydrological process of riparian wetland in arid areas, and provide reference for plant species selection and water resources management.
Open Research
DATA AVAILABILITY STATEMENT
The data that support the findings of this study are available on request from the corresponding author. Stable isotope data are not publicly available due to privacy.
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