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| 1 | 鸭绿江河口及近岸地区沉积物中重金属分布的影响因素分析显示文摘对鸭绿江河口不同地区沉积物中重金属分布特征和埋藏通量的垂向变化进行了分析;探讨了其独特的动力环境等因素对重金属分布的影响;评价了鸭绿江河口地区重金属污染状况及潜在生态风险程度。结果显示,自1920年代到2000年以来,除了Cu的含量和埋藏通量逐年减小之外,Cr、Ni、Zn、Cd、Pb、As和Hg的浓度和埋藏通量具有逐渐增加的趋势;鸭绿江河口地区重金属总体污染程度为重到严重,其中西水道沉积物的重金属总体污染程度和总潜在生态风险程度均最高,重金属污染已经对鸭绿江河口地区的生态环境构成了严重的危害;粒度控制效应不是鸭绿江河口地区重金属分布的最主要影响因素;Cu和其他几种重金属有着不同的来源;最大浑浊带独特的动力机制是造成中水道重金属(除Cu外)的高值分布区和最大浑浊带内的高悬沙浓度分布区相对应的最主要原因。 | 高建华 李军 王珍岩 汪亚平 白凤龙 程岩 | 2008 | 地球化学2008，37，5： | 44 |
| 2 | 鸭绿江河口及近岸海域沉积物中重矿物组成、分布及其沉积动力学意义显示文摘通过研究鸭绿江河口和近岸海域沉积物的重矿物分布和区域组合特征,同时以重矿物作为示踪物,分析了河口区底部沉积物的运动状况。研究结果表明,研究区的重矿物主要分为两种组合,一是黑云母-普通角闪石-绿帘石组合,二是由不稳定的矿物普通角闪石、较稳定矿物绿帘石和石榴石以及金属矿物(包括磁铁矿、钛铁矿和赤褐铁矿)组成,该组合又可分为四个亚组合。不稳定矿物与稳定矿物含量的比值变化、推移质潮周期输运率和净输运方向计算以及断面的粒度分布特征表明,鸭绿江河口10 m等深线以北地区的底部沉积物主要向上游地区输运。这一结论与以往分析结果有很大不同,这主要是由于鸭绿江流域受到了人类活动,尤其受水利工程和人工挖沙的影响而出现的一种自我调节机制。此外,重矿物分析的初步结果还表明,鸭绿江河口10 m等深线以南的沉积物主要向下游输运,而近岸地区的沉积物可能由东西两端向中间输运,但是由于受到研究资料的限制,以上结论还有待于通过其他研究方法进一步验证。从北黄海东西两个地区的重矿物分布来看,北黄海西部地区的石榴石和电气石等稳定重矿物含量要大于东部地区的,而白云石和云母等不稳定矿物的含量要小于东部的。综合对比北黄海西部与北黄海东部、南黄海北部和南部来看,前者与后三者最大的区别就是沉积物中没有自生黄铁矿。 | 高建华 李军 汪亚平 白风龙 李家胜 程岩 | 2009 | 海洋学报2009，31，3： | 20 |
| 3 | 鸭绿江河口沉积物元素地球化学及其控制因素显示文摘对鸭绿江河口地区的56个站位沉积物的常量元素含量进行了测试,并对测试结果进行了多元统计分析。研究结果表明,多数常量元素含量在鸭绿江西岸潮滩地区和西部海域波动较小,而在上游地区和河口口门地区变动较大,在河口最大浑浊带内出现两个峰值。R型主因子分析结果表明,粒度控制效应对鸭绿江河口地区常量元素的含量分布起着主要作用,贡献方差达76.55%。运用Q型聚类分析将各站位归为两种类型,揭示出沉积动力环境的差异是造成这种常量元素地球化学分区特征的最主要因素。此外,通过与附近河口对比发现鸭绿江河口及近岸地区沉积物中的常量元素含量同朝鲜半岛的河流、中朝准地台花岗岩以及朝鲜半岛花岗岩比较接近,但与长江和黄河有着较大的差异。 | 李家胜 高建华 李军 王珍言 严杰 白凤龙 程岩 | 2010 | 海洋地质与第四纪地质2010，30，1： | 17 |
| 4 | 基于表层沉积物粒度特征的鸭绿江口沉积环境分析显示文摘为了研究鸭绿江河口地区沉积物的来源和沉积环境,对不同断面43个点位表层沉积物进行了采样分析,通过对沉积物的分类和粒度参数的计算,探讨了沉积物类型和粒度参数的分布特征及其指示意义。研究结果表明,鸭绿江河口地区的表层沉积物类型主要为砂、粉砂质砂、砂质粉砂和极少量黏土质粉砂,其中砂的分布范围最广;鸭绿江河口地区表层沉积物来源具有多元性和空间差异性,以河流径流输砂为主体,同时也有浅海表层沉积物的向陆运动,其中鸭绿江下游地区沉积物来源主要为河流输送,中水道、西水道、辽东浅滩的沉积物来源既有河流输送又有浅海表层沉积物的向陆运动;河口不同区域的沉积环境不同,既有河流径流影响又有海洋潮汐和波浪的影响。研究结果可以为鸭绿江河口系统演变提供研究依据。 | 李富祥 张春鹏 王路 刘敬伟 张亮 | 2014 | 海洋科学2014，38，5： | 12 |
| 5 | Distribution and their pollution assessment of heavy metals in the sediments of the Yalu River Estuary and its adjacent coastal waters显示文摘The present paper deals with the distribution patterns of heavy metals and the associated influencing factors in the Yalu River Estuary and its adjacent coastal waters.Based upon the analysis of the surficial and core sediments measurements,the pollution of heavy metal and potential ecological risk were evaluated.The burial flux and contents of heavy metals(except for copper) have been continuously increasing since the 1920s.Therefore,the gross potential ecological risk for the sedi-ments was high or very high,and the study area was endangered by heavy metals contamination.Heavy metals originated mainly from upstream pollutant input,correlation analysis showed that chromium,nickel,zinc,cadmium,lead,arsenic,and mercury in the sediments of the middle and west channels as well as the sea area of the western Yalu River Estuary concentrations were most probably derived from similar sources.In contrast,the metal of copper most probably originated from sources different from the other metals.Preliminary studies indicate that copper contamination was most likely the result of emission from mining activities situated at the upstream of the river.The contents of heavy metals in the sediments of estuarine turbidity maximum zone of Yalu River were larger than those of any other areas in the middle channel.With large portion of fine sediments,weaker hydrodynamics,and richer sources of heavy metals,the sediments of the west channel,were even more enriched with heavy metals than those of the middle channel. | GAO Jianhua LI Jun Wang Harry V WANG Yaping WANG Zhenyan BAI Fenglong GAO Shu CHENG Yan | 2009 | Acta Oceanologica Sinica2009，28，6： | 4 |
| 6 | The response of sedimentary record to catchment changes induced by human activities in the western intertidal flat of Yalu River Estuary,China显示文摘The response to the catchment changes of the sedimentary environment of the western intertidal flat of Yalu River Estuary was investigated by analyzing the vertical variations of the grain size of sediment cores,along with the hydrologic data and human activities in the catchment.The results demonstrated a stepwise decreasing trend for the variations of both the sediment load and water discharge into the sea,which could be divided into three stages as 1958–1970,1971–1990 and 1991–2009.Reservoir construction and the changes of catchment vegetation coverage turned out to be the two predominant contributors to the changes.There are four periods for the variation of the sensitive components of the sediment cores from 1940 to 2010,i.e.,1940–1950,1951–1980,1981–1990 and 1991–2010.The vertical distribution of grain size in the cores mainly varied with the changes of vegetation coverage in the catchment and reservoir construction from 1960 to 1980,whereas it varied depending on the intensity of water and soil erosion in the catchment from 1980 to 1990.Despite the further reduction of the water and sediment input into the sea from 1990 to 2009,this period was characterized by coarsening trends for the grain size of sediment in the estuarine intertidal flat and correspondingly,the significantly increased silt contents of the sensitive component. | SHI Yong LIU Zhishuai GAO Jianhua YANG Yang WANG Yaping | 2017 | Acta Oceanologica Sinica2017，36，4： | 0 |
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