Impacts of land use and landscape pattern on water quality at multiple spatial scales in a subtropical large river

Ecohydrology ◽  
2021 ◽  
Author(s):  
Xiao Shu ◽  
Weibo Wang ◽  
Mingyong Zhu ◽  
Jilei Xu ◽  
Xiang Tan ◽  
...  
2021 ◽  
Author(s):  
Xiao Shu ◽  
Weibo Wang ◽  
Mingyong Zhu ◽  
Jilei Xu ◽  
Xiang Tan ◽  
...  

Abstract The coupling between land use/landscape pattern and water quality in river system varies across different spatial and temporal scales. It is important to understand the association between water quality and land use/landscape pattern across different spatial and temporal scales for the protection of water resources. Here, we measured seasonal water quality at 12 sub-basins in the upper reaches of the Han River (UHR) between 2010 and 2018. We conducted factor analysis and redundancy analysis to determine the links between land use and water quality at multiple spatial scales and to identify the main factors influencing water quality. We found that the concentration of nutrients, including total nitrogen, total phosphorus, nitrate-N, and ammonium-N were higher during the wet season than the dry season. Total nitrogen was identified as the main driver of nutrient pollution of UHR, whereas total phosphorus was identified as another potential nutrient pollutant. We also found that water quality parameters had a stronger related to land use types over the wet season than the dry season. Croplands and urban lands increased phosphorus concentrations of river water, whereas forest and grass lands decreased the nitrogen concentrations of river water at the sub-basins scale. Land use at riparian zone scales better explained variations in water quality than land use at sub-basin scales. The explained variations in landscape metrics were generally higher over the dry season compared to that over the wet season. The largest patch index and Shannon's diversity index were the main predictors of river water quality in UHR.


2015 ◽  
Vol 48 ◽  
pp. 417-427 ◽  
Author(s):  
Zhenyao Shen ◽  
Xiaoshu Hou ◽  
Wen Li ◽  
Guzhanuer Aini ◽  
Lei Chen ◽  
...  

2013 ◽  
Vol 28 (20) ◽  
pp. 5259-5272 ◽  
Author(s):  
Guoqiang Wang ◽  
Yinglan A ◽  
Zongxue Xu ◽  
Shurong Zhang

2005 ◽  
Vol 62 (6) ◽  
pp. 1309-1319 ◽  
Author(s):  
Geneviève M Carr ◽  
Patricia A Chambers ◽  
Antoine Morin

The ability of land use to replace water quality variables in predictive models of periphyton chlorophyll a was tested with a 21-year data set for Alberta rivers. Nutrients (total dissolved P and NO2 + NO3) explained 23%–24% of the variability in seasonal chlorophyll a, whereas land use (human population density) explained 25%–28% of the variability. The best models included the combination of total dissolved P and population density, explaining 32%–34% of periphyton chlorophyll a variability. However, analysis of variance of chlorophyll a by ecoregions and ecozones explained about as much variability (28%–30%), and the inclusion of an ecoregion term into the regression models showed a diminished importance of land use as a predictor of chlorophyll a, with best models based on the combination of nutrients and ecoregion and explaining up to 43%–44% of periphyton chlorophyll a variability. Within ecoregions, land use was sometimes a good surrogate for nutrient data in predicting chlorophyll a concentrations. Overall, land use is a suitable surrogate for nutrients in regression models for chlorophyll a, but its inclusion in general models may reflect regional differences in nutrient–chlorophyll relationships rather than true land use effects on chlorophyll a.


2018 ◽  
Vol 38 (7) ◽  
Author(s):  
范敏 FAN Min ◽  
彭羽 PENG Yu ◽  
王庆慧 WANG Qinghui ◽  
米凯 MI Kai ◽  
卿凤婷 QING Fengting

2018 ◽  
Vol 38 (3) ◽  
Author(s):  
项颂 XIANG Song ◽  
庞燕 PANG Yan ◽  
窦嘉顺 DOU Jiashun ◽  
吕兴菊 LÜ Xingju ◽  
薛力强 XUE Liqiang ◽  
...  

2014 ◽  
Vol 43 (12) ◽  
pp. 1616-1622 ◽  
Author(s):  
Ying Cai ◽  
Dehua Zhao ◽  
Delin Xu ◽  
Hao Jiang ◽  
Mengqiu Yu ◽  
...  

2012 ◽  
Vol 51 (3) ◽  
pp. 555-570 ◽  
Author(s):  
Ge Zhang ◽  
Subhro Guhathakurta ◽  
Gang Dai ◽  
Lingying Wu ◽  
Lijiao Yan

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