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Frontiers of Earth Science

ISSN 2095-0195

ISSN 2095-0209(Online)

CN 11-5982/P

Postal Subscription Code 80-963

2018 Impact Factor: 1.205

Front Earth Sci    2013, Vol. 7 Issue (3) : 351-360    https://doi.org/10.1007/s11707-013-0366-y
RESEARCH ARTICLE
Impacts of river impoundment on the riverine water chemistry composition and their response to chemical weathering rate
Yang GAO1, Baoli WANG2, Xiaolong LIU3, Yuchun WANG4, Jing ZHANG1, Yanxing JIANG1, Fushun WANG1()
1. School of Environmental and Chemical Engineering, Shanghai University, Shanghai 200444, China; 2. Institute of Geochemistry, Chinese Academy of Science, Guiyang 550002, China; 3. Tianjin Normal University, Tianjin 300387, China; 4. Department of Water Environment, China Institute of Water Resources and Hydroelectric Power Research (IWHR), Beijing 100038, China
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Abstract

Currently, most rivers worldwide have been intensively impounded. River damming becomes a big problem, not only in inducing the physical obstruction between upstream and downstream, but also in destroying the natural continuity of river. But the discontinuity of water quality was often neglected, which presents a challenge to traditional river geochemistry research. To understand the changes in basic chemistry of water upstream and downstream of the dam, we investigated the Miaotiao River reservoirs in series in the Wujiang River Basin, and the Hongjiadu, Dongfeng Reservoir on the upper reaches of the Wujiang River. Chemical weathering rates were calculated using the water chemistry data of the reservoir surface and downstream of the dam, in each reservoir, respectively. The results showed that the difference between the chemical weathering rates calculated from reservoir surface water and water downstream of the dam was greater in reservoirs with a longer water retention time. In Hongjiadu Reservoir with the longest water retention time among the studied reservoirs, this difference reaches 9%. As a result, the influence of river damming, especially the influence of reservoirs in series, should be taken into account when calculating the chemical weathering rate of a river basin.

Keywords reservoirs in series      chemical weathering rate      Wujiang     
Corresponding Author(s): WANG Fushun,Email:fswang@shu.edu.cn   
Issue Date: 05 September 2013
 Cite this article:   
Baoli WANG,Xiaolong LIU,Yuchun WANG, et al. Impacts of river impoundment on the riverine water chemistry composition and their response to chemical weathering rate[J]. Front Earth Sci, 2013, 7(3): 351-360.
 URL:  
https://academic.hep.com.cn/fesci/EN/10.1007/s11707-013-0366-y
https://academic.hep.com.cn/fesci/EN/Y2013/V7/I3/351
ReservoirDrainagearea/km2Average flow/(m3·s-1)Average annual precipitation/mmTotal volume/ (108m3)Year of constructionHeight of dam/(m-1)Residence time/d
Hongfeng155130.21584.956.01196054230.3
Baihua1832381362.41.8219745055.4
Xiuwen208441.21230.70.1141961493.2
Hongyan275249.211080.3041971607.2
Hongjiadu99001551191.449.472000182568.5
Dongfeng181613431118.38.64198416254.35
Suofengying218623951061.22.01220011134.9
Wujiangdu277904831124.723197016582.5
Tab.1  Main features of studied reservoirs
Fig.1  Geographic location of study area and sampling sites
HF-1HF-2BH-1BH-2XW-1XW-2HY-1HY-2HJD-1HJD-2DF-1DF-2SFY-1SFY-2WJD-1WJD-2
pH8.467.428.377.347.967.468.327.668.127.568.277.7387.788.347.57
DO/%93.6846.5998.947.6274.8646.58126.7253.5485.3864.7799.8464.1895.9573.79116.0887.2
TDS/(mg·L-1)279.95308.2337.14380.51364.15363.83330.45342.33280.17302.97316.88306.93314.93311.56333.55327.99
K+ /(mmol·L-1)0.0680.0670.0810.0760.080.0930.0810.0730.0350.0380.0370.0390.0420.0430.0480.045
Ca2+/ (mmol·L-1)1.1981.3651.411.4941.5741.4671.3261.371.3591.5091.4851.5051.5141.5081.5631.583
Na+/(mmol·L-1)0.2220.2240.3820.3180.3460.4830.3720.3430.150.1470.2590.1940.2090.2130.220.208
Mg2+ /(mmol·L-1)0.6660.5730.60.5880.5510.5890.6490.5820.3630.360.3860.3780.4180.4070.4830.454
Cl-/(mmol·L-1)0.1740.1630.2010.1780.1690.2210.1920.1760.0720.0730.0910.0820.090.0880.120.099
SO42-/(mmol·L-1)0.9010.9431.121.1031.1091.1710.9910.9560.6810.7020.9360.8160.8580.8460.9370.905
NO3-/(mmol·L-1)0.0870.0820.0680.0950.1320.1250.1130.110.2420.2530.2040.230.2110.2160.1790.2
HCO3-/(mmol·L-1)1.8062.1422.2212.9222.5622.4312.3152.5892.122.3512.2142.2332.2842.2482.4122.368
Si/(mmol·L-1)0.0070.0180.0180.020.0240.0230.0220.0280.0410.0670.0540.0640.0580.0590.0290.058
TZ+/(meq·L-1)4.0184.1694.4834.5594.6764.6874.4034.3213.6293.9244.03944.1134.0874.3614.326
TZ-/(meq·L-1)3.874.2734.7315.4015.085.1194.6014.7873.7974.0814.3814.1764.34.2444.5864.477
NICB0.037-0.025-0.055-0.185-0.086-0.092-0.045-0.108-0.046-0.04-0.085-0.044-0.046-0.038-0.052-0.035
CRWsil/(t·(km2·yr)-1)3.13.827.76.537.449.916.756.473.464.226.955.975.735.954.235.32
CRWcarb/(t·(km2·yr)-1)52.7355.2947.2654.6953.5942.1445.6547.3547.954.2748.1757.9455.1754.8355.0956.36
CRWevap/(t·(km2·yr)-1)74.477.59100.3298.2694.14100.5476.5473.5743.4944.9474.4464.565.1664.2268.966.07
Tab.2  Water chemistry data of the samples and the CWR of the reservoirs
Fig.2  The anion and cation ternary diagrams
Fig.3  Relationship between water residence time and changes of CWR (a-XW, b-HY, c-SFY, d-DF; e-WJD, f-BH, g-HF, h-HJD). (The residence times are in Table 1).
Fig.4  Water temperature above and below the dam for 12 months (these reservoirs are arranged in axes by residence time from short to long)
Fig.5  pH, DO, Ca, and Si (annual average value) above and below the dam (these reservoirs are arranged in axes by residence time from short to long)
Fig.6  Ca, Si concentration and DO, pH (annual average value) profiles in reservoir
Fig.7  CaCOsaturation index variation (The black triangle for the site of the dam)
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