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中国东部主要河流稀土元素地球化学特征 被引量:22
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作者 周国华 孙彬彬 +3 位作者 刘占元 魏华玲 曾道明 张必敏 《现代地质》 CAS CSCD 北大核心 2012年第5期1028-1042,共15页
在2007年底至2008年初的枯水期间,系统采集了中国东部流域面积和径流量较大的33条河流沉积物、悬浮颗粒物和水样,采用等离子质谱法、X荧光光谱法等方法测定了14种稀土元素含量以及常量组分和水体pH值等理化指标。研究发现中国河流稀土... 在2007年底至2008年初的枯水期间,系统采集了中国东部流域面积和径流量较大的33条河流沉积物、悬浮颗粒物和水样,采用等离子质谱法、X荧光光谱法等方法测定了14种稀土元素含量以及常量组分和水体pH值等理化指标。研究发现中国河流稀土元素浓度总体高于世界均值,且南方河流沉积物、悬浮物稀土元素含量高于北方河流,南方河流悬浮物态中稀土、重稀土呈现一定程度的相对富集,与我国上地壳稀土丰度和稀土矿产种类的南北分异相吻合。展示了以中国东部泥质岩稀土元素丰度标准化后的稀土配分模式及Ce、Eu异常特征,发现河流沉积物的中、重稀土元素相对富集,悬浮物轻稀土相对富集,溶解相重稀土富集的特征;北方河流溶解相稀土元素浓度明显大于南方河流,且除小清河外,溶解相Eu不同于沉积物与悬浮物而呈强烈的正异常,主要与河水理化性质影响下的稀土分异有关。研究发现小清河等少数河流沉积物中稀土元素为异常高值,经Al标准化处理、计算拟合剩余值后,认为小清河等河流稀土元素已受人为污染的影响。 展开更多
关键词 稀土元素浓度 稀土配分模式与异常 水粒分配系数 沉积物 悬浮物 溶解相 人为污染 中国东部河流
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中国东部主要入海河流As元素分布、来源及影响因素分析 被引量:16
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作者 柳青青 杨忠芳 +4 位作者 周国华 夏学齐 侯青叶 余涛 翟大兴 《现代地质》 CAS CSCD 北大核心 2012年第1期114-124,共11页
为查明中国河流中As等重金属元素的分布规律,于2007—2008年分丰水期和枯水期对中国东部30余条入海河流水体、悬浮物统一进行采样分析。结果表明:东部河流中As元素溶解态含量均值为3.1μg/L,同世界河流相比,明显偏高;且频率分布直方图... 为查明中国河流中As等重金属元素的分布规律,于2007—2008年分丰水期和枯水期对中国东部30余条入海河流水体、悬浮物统一进行采样分析。结果表明:东部河流中As元素溶解态含量均值为3.1μg/L,同世界河流相比,明显偏高;且频率分布直方图具有多个峰值,反映出明显的人为污染。利用富集系数的研究表明,悬浮物同样受到较明显的人为污染。As在河水中的迁移形式以溶解态为主,pH值和温度对As的迁移形式有明显影响。流域内岩石类型对河流中As含量影响显著,火山岩、火山碎屑岩类广泛分布的流域河水中As含量明显偏高,花岗岩及中、深变质岩广泛分布的流域河流中As含量则偏小。利用生活、工业污水作为As元素人为来源端元,对海河、黄河、长江、珠江等河流人为源进行了估算,分别为46.7%、18.7%、13.5%、8.3%。 展开更多
关键词 砷元素 分布 来源 人为污染 中国东部河流
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Sources of dissolved inorganic carbon in rivers from the Changbaishan area, an active volcanic zone in North Eastern China 被引量:2
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作者 Xue Bai Benjamin Chetelat Yilong Song 《Acta Geochimica》 EI CAS CSCD 2017年第3期410-415,共6页
Major elements and carbon isotopes of dissolved inorganic carbon(DIC)have been measured in the waters of Changbaishan mountain,a volcanic area in northeastern China,between June and September 2016 to decipher the orig... Major elements and carbon isotopes of dissolved inorganic carbon(DIC)have been measured in the waters of Changbaishan mountain,a volcanic area in northeastern China,between June and September 2016 to decipher the origin of the CO_2 involved in chemical weathering reactions.Spatial variations of major elements ratios measured in water samples can be explained by a change of the chemical composition of the volcanic rocks between the volcanic cone(trachytes)and the basaltic shield as evidenced by the variations in the composition of these rocks.Hence,DIC results from the neutralization of CO_2 by silicate rocks.DIC concentrations vary from 0.3 to 2.5 mmol/L and carbon isotopic compositions of DIC measured in rivers vary from-14.2‰to 3.5‰.At a first order,the DIC transported by rivers is derived from the chemical weathering’s consumption of CO_2 with a magmatic origin,enriched in^(13)C(-5%)and biogenic soil CO_2 with lower isotopic compositions.The highest δ^(13)C values likely result from C isotopes fractionation during CO_2 degassing in rivers.A mass balance based on carbon isotopes suggest that the contribution of magmatic CO_2 varied from less than 20%to more than 70%.Uncertainties in this calculation associated with CO_2 degassing in rivers are difficult to quantify,and the consequence of CO_2 degassing would be an overestimation of the contribution of DIC derived from the neutralization of magmatic CO_2 by silicate rocks. 展开更多
关键词 Carbon isotopes Dissolved inorganic carbon RIVERS Chemical weathering CHANGBAISHAN Active volcanic zone
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Response of Stream Pollution Characteristics to Catchment Land Cover in Cao-E River Basin, China 被引量:13
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作者 SHEN Ye-Na LUE Jun +1 位作者 CHEN Ding-Jiang SHI Yi-Ming 《Pedosphere》 SCIE CAS CSCD 2011年第1期115-123,共9页
This study addressed the relationship of river water pollution characteristics to land covers and human activities in the catchments in a complete river system named Cao-E River in eastern China.Based on the hydrogeoc... This study addressed the relationship of river water pollution characteristics to land covers and human activities in the catchments in a complete river system named Cao-E River in eastern China.Based on the hydrogeochemical data collected monthly over a period of 3 years,cluster analysis(CA) and principal component analysis(PCA) were adopted to categorize the river reaches and reveal their pollution characteristics.According to the differences of water quality in the river reaches and land use patterns and average population densities in their catchments,the whole river system could be categorized into three groups of river reaches,i.e.,non-point sources pollution reaches(NPSPR),urban reaches(UR) and mixed sources pollution reaches(MSPR).In UR and MSPR,the water quality was mainly impacted by nutrient and organic pollution,while in NPSPR nutrient pollution was the main cause.The nitrate was the main nitrogen form in NPSPR and particulate phosphorus was the main phosphorus form in MSPR.There were no apparent trends for the variations of pollutant concentrations with increasing river flows in NPSPR and MSPR,while in UR the pollutant concentrations decreased with increasing river flows.Thus dry season was the critical period for water pollution control in UR.Therefore,catchment land covers and human activities had significant impact on river reach water pollution type,nutrient forms and water quality responses to hydrological conditions,which might be crucial for developing strategies to combat water pollution in watershed scale. 展开更多
关键词 cluster analysis hydrological conditions pollution factors principle component analysis water quality
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