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渤海莱州湾表层沉积物中金属元素分布及环境质量 总被引：3，自引：1，他引：2
利用X-射线荧光光谱仪、等离子质谱仪或原子荧光光度计测定了莱州湾表层沉积物中金属元素的含量,探讨了它们的分布特征、来源及污染程度,结果表明,沉积物中铜、锌、铅、镉、砷、镍、铬、钴、钒、钪、铁、锰的含量由近岸向湾内递减,莱州湾北部海域的含量大于南部的。银含量高的沉积物主要分布在莱州湾中部偏西南的环流中心区。沉积物中砷和镍含量超过ERL值,潜在生态风险较高。富集系数和主成分分析显示,沉积物中铁、铜、锌、镉、砷、铬、镍、钴、锰、钒和钪为无富集,砷为轻度富集,铅和银为中度富集。铁、铜、锌、镉、铬、镍、钴、锰、钒、砷和钪主要来源于自然源,铅既有岩石和土壤风化产物硅酸盐矿物等自然源的贡献,又受到了人为活动的影响,银主要受人为活动的影响。聚类分析表明,可把莱州湾沉积物分为4类,其中黄河口西北缘沉积物中砷和镍污染生态风险最高,其次是莱州湾中部和北部。 相似文献
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于2002年9月在汕头湾采集了13个表层沉积物样品,测定了它们的细粒级组分、总有机质、铝、铁、锰、铜、锌、铅、镉、铬、镍、钴的含量,对其分布特征及其彼此之间相关性进行了分析,并以南海陆架区重金属含量为背景值计算了汕头湾表层沉积物重金属元素的富集系数,结果表明,铁、锰、铜、锌、铅、镉、铬、镍、钴的含量范围分别为2.91%~3.94%,427.85~810.96,24.43~79.49,84.83~248.50,35.56~50.25,0.30~1.75,36.11~74.22,16.99~31.69,8.22~10.87 mg/kg,其分布由汕头湾上游的榕江口至湾口呈波浪状递减(锰除外)。汕头湾表层沉积物中各重金属的富集系数均大于1,其中富集系数从大到小的重金属元素是铜、镉、铅、锌、镍、铬和锰。人为排污、水动力作用、黏土含量、盐度是多数重金属元素分布特征的控制因素。锰的分布特征更多地取决于汕头湾水域的氧化还原条件。 相似文献
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2007年11月在东海泥质区采集了表层沉积物样品,用连续提取法对金属元素的赋存形态进行了分离,测定了各形态中锰、铁和铝的含量。结果表明,锰主要赋存于碳酸盐结合态,含量为0.04～0.19mg/g,平均0.13mg/g;铁主要赋存于易还原态(铁锰氧化物结合态),含量为1.1～2.3μg/g,平均1.5mg/g;大部分站点的铝主要赋存于易还原态,含量为0.4～1.1mg/g,平均0.7mg/g。沉积物主要成分对金属赋存形态产生影响,CARB态、ERO态Mn、Fe和Al分别随沉积物中碳酸钙、水合铁锰氧化物含量的升高而增加,且ERO态金属与水合铁锰氧化物的相关性显著;有机物的含量的对OSM态金属的影响则不明显。非残渣态Fe和Al的含量随水深增加而降低,主要是由于沉积物中ERO态Fe和Al受陆地径流输入和水体中清除作用的影响,导致近岸沉积物中有较多的活性Fe、Al;离岸距离增加则沉积物中活性Fe、Al含量减少。 相似文献
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渤海沉积物重金属环境质量评价及其影响因素 总被引：1，自引：0，他引：1
基于渤海404个站位的沉积物重金属元素含量与分布特征，通过潜在生态风险、地累积指数等指标定量评价了沉积物中重金属的环境质量，利用富集因子和主成分分析法，对影响渤海表层沉积物中重金属元素分布特征的影响因素进行了分析。研究结果显示，渤海湾重金属元素平均含量最高，渤海海峡最低；渤海Cd具有强潜在生态风险，Hg具有中等?强潜在生态风险，总潜在生态风险程度为中等；Cr和Ni的少量站位超过毒性阈值上限，其余重金属污染物含量均低于毒性阈值下限，表明渤海发生沉积物重金属的毒性污染的概率很低。沉积物中粒度效应控制的重金属元素含量对渤海表层沉积物中的重金属元素的分布具有主要影响，人类活动所造成的污染主要是Cd，主要分布于辽东湾的锦州湾和复州湾，其次通过河流进入海洋的Hg对黄河三角洲及莱州湾有重要影响，亟需引起注意。 相似文献
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本文对莱州湾、渤海湾、渤海中央盆地的海洋底质沉积环境进行了研宄,通过对17柱沉积物岩芯样品中Fe,Al,Mn,Ti的测定和分析,论述了四元素在底质表层沉积物中及在岩芯沉积物中的含量和分布规律,用数理统计的方法分析了渤海中央盆地Fe,Al,Mn,Ti的丰度值,为渤海环境背景值及环境背景历史的研究提供了重要参数。 相似文献
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北部湾沉积物中重金属元素的地球化学特征及物源初探 总被引：6，自引：1，他引：5
本文根据北部湾沉积物岩心样调查结果计算了铜、铅、锌、镉、汞、砷等重金属元素的背景值,并分析了其与南海陆架区和南海全海域沉积物背景值、广西土壤背景值之间的差异.对北部湾表层沉积物中重金属含量及近10 a的变化趋势以及岩心样中重金属元素含量近百年以来的变化趋势综合分析结果表明:北部湾近岸海域沉积物中铜、砷、汞、镉重金属元素含量总体呈增长趋势,北部湾中部海域沉积物中重金属元素含量的年际变化有升有降,至湾口处沉积物中重金属元素的含量基本不变.综合评价结果表明,北部湾近岸沉积物中砷、汞、镉等重金属元素的地球化学特征明显受到广西人类活动的影响.北部湾沉积物中的重金属元素主要来源于人类活动影响下的广西沿岸陆源输入,经由琼州海峡的外部海域物质输入也有贡献. 相似文献
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利用1984年夏季的现场调查,作者研究了黄河口及邻近海域表层沉积物中铜的地球化学形式。含量及其分布,分析了铜和有机质、铁、锰、锌及中值粒径之间关系,并指出总铜平均含量为20.4mg/kg.其中残渣部分占55％,有机结合铜为19.4％、Fe-Mn氧化物结合铜为12.1％、碳酸盐结合铜为13.1％,可交换铜的含量小于1％。此外讨论了沉积物中各种形式铜含量与铁、锰、有机质及中值粒径关系。 相似文献
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Soil-sized particulates have been collected on board ship by a mesh technique from the lower troposphere of the North, Equatorial and South Atlantic Ocean, northern and southern Indian Ocean, South and East China Sea and various coastal localities.Spectrographic analysis reveals that, on average, the particulates have concentrations of Mn, Ni, Co, Ga, Cr, V, Ba, and Sr which are of the same order of magnitude as those in average crustal material. In contrast, the average concentrations of Pb, Sn, and Zn are one order of magnitude higher than those in average crustal material.Within this “world-wide” average there are significant geographical variations in the distributions of Pb, Sn, and Zn which may be related to anthropogenic sources.On the basis of trace-element distributions lower tropospheric soil-sized marine particulates have been divided into four genetic components; local, zonal, inter-zonal, and global. The proportions of these components vary geographically, and each component may have both a natural and an anthropogenic fraction. 相似文献
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Tautog, Tautoga onitis, is an abundant species of fish in estuaries of the northeastern United States. Planktonic tautog larvae are abundant in summer in these estuaries, but there is little information on rates of growth of tautog larvae feeding on natural assemblages of food in the plankton. We examined abundance and growth of larval tautog and environmental factors during weekly sampling at three sites along a nearshore‐to‐offshore transect in Buzzards Bay, Massachusetts, USA during summer 1994. This is the first study of a robust sample size (336 larvae) to estimate growth rates of field‐caught planktonic tautog larvae feeding on natural diets, using the otolith daily‐growth‐increment method. The study was over the entire summer period when tautog larvae were in the plankton. The sampling sites contrasted in several environmental variables including temperature, dissolved oxygen (DO), and chlorophyll a concentration. There was a temporal progression in the abundance of tautog larvae over the summer, in relation to location and temperature. Tautog larvae were first present nearshore, with a pronounced peak in abundance occurring at the nearshore sites during the last 2 weeks in June. Larvae were absent at this time further offshore. From late June through August, larval abundance progressively decreased nearshore, but increased offshore although never approaching the abundance levels observed at the nearshore sites. The distribution and abundance of tautog larvae appeared to be related to a nearshore‐to‐offshore seasonal warming trend and a nearshore decrease in DO. Otoliths from 336 larvae ranging from 2.3 to 7.7 mm standard length had otolith increment counts ranging from 0 to 19 increments. Growth of larval tautog was estimated at 0.23 mm·day?1, and length of larvae prior to first increment formation was estimated at 2.8 mm indicating that first increment formation occurs 3–4 days after hatching at 2.2 mm. Despite spatial and temporal differences in environmental factors, there were no significant differences in growth rates at any of three given sites over time, or between sites. Because larval presence only occurred at a narrow range of temperature (17–23.5 °C) and DO (6.5–9.3 mg·l?1), in situ differences in growth did not appear to be because of differences in larval distribution and abundance patterns relative to these parameters. 相似文献
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Klaus Kremling 《Marine Chemistry》1983,13(2):87-108
In June 1981, dissolved Zn, Cd, Cu, Ni, Co, Fe, and Mn were determined from two detailed profiles in anoxic Baltic waters (with extra data for Fe and Mn from August 1979). Dramatic changes across the O2H2S interface occur in the abundances of Cu, Co, Fe, and Mn (by factors of ?100). The concentrations of Zn, Cd, and Ni at the redox front decrease by factors between 3 to 5.Equilibrium calculations are presented for varying concentrations of hydrogen sulfide and compared with the field data. The study strongly supports the assumption that the solubility of Zn, Cd, Cu, and Ni is greatly enhanced and controlled by the formation of bisulfide and(or) polysulfide complexes. Differences between predicted and measured concentrations of these elements are mainly evident at lower ΣH2S concentrations.Cobalt proved to be very mobile in anoxic regions, and the results indicate that the concentrations are limited by CoS precipitation. The iron (Fe2+) and manganese (Mn2+) distribution in sulfide-containing waters is controlled by total flux from sediment-water interfaces rather than by equilibrium concentrations of their solid phases (FeS and MnCO3). The concentrations of these metals are therefore expected to increase with prolonged stagnation periods in the basin. 相似文献
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P.N. Froelich L.W. Kaul J.T. Byrd M.O. Andreae K.K. Roe 《Estuarine, Coastal and Shelf Science》1985,20(3):239-264
Concentrations of dissolved nutrients (NO3, PO4, Si), germanium species, arsenic species, tin, barium, dimethylsulfide and related parameters were measured along the salinity gradient in Charlotte Harbor. Phosphate enrichment from the phosphate industry on the Peace River promotes a productive diatom bloom near the river mouth where NO3 and Si are completely consumed. Inorganic germanium is completely depleted in this bloom by uptake into biogenic opal. The ratio taken up by diatoms is about 0·7 × 10?6, the same as that provided by the river flux, confirming that siliceous organisms incorporate germanium as an accidental trace replacement for silica. Monomethylgermanium and dimethylgermanium concentrations are undetectable in the Peace River, and increase linearly with increasing salinity to the seawater end of the bay, suggesting that these organogermanium species behave conservatively in estuaries, and are neither produced nor consumed during estuarine biogenic opal formation or dissolution. Inorganic arsenic displays slight removal in the bloom. Monomethylarsenic is produced both in the bloom and in mid-estuary, while dimethylarsenic is conservative in the bloom but produced in mid-estuary. The total production of methylarsenicals within the bay approximately balances the removal of inorganic arsenic, suggesting that most biological arsenic uptake in the estuary is biomethylated and released to the water column. Dimethylsulfide increases with increasing salinity in the estuary and shows evidence of removal, probably both by degassing and by microbial consumption. An input of DMS is observed in the central estuary. The behavior of total dissolvable tin shows no biological activity in the bloom or in mid-estuary, but does display a low-salinity input signal that parallels dissolved organic material, perhaps suggesting an association between tin and DOM. Barium displays dramatic input behavior at mid-salinities, probably due to slow release from clays deposited in the harbor after catastrophic phosphate slime spills into the Peace River. 相似文献
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Linjie Zheng Tomoharu Minami Shotaro Takano Hideki Minami Yoshiki Sohrin 《Journal of Oceanography》2017,73(5):669-685
A central theme of the ongoing GEOTRACES program is to improve the understanding of processes occurring at ocean interfaces with continents, sediments, and ocean crust. In this context, we studied the distributions of Al, Mn, Fe, Co, Ni, Cu, Zn, Cd, and Pb around the Juan de Fuca Ridge (JdFR) in total dissolvable (td), dissolved (d), and labile particulate (lp) fractions, which represent a fraction in unfiltered samples, filtered samples through an AcroPak capsule filter, and the difference between td and d, respectively. Al and Fe were dominated by lp-species, while Ni, Zn, and Cd were dominated by d-species with undetectable amounts of lp-species. Major findings in this study are as follows: (1) The continental margin (CM) provided large sources of Al, Mn, Fe, and Co from the surface to ~2000 m in depth. The supply from CM caused high surface concentrations of dMn and dCo, a subsurface (100–300 m depth) maximum of dCo, and intermediate (500–2000 m depth) maxima of lpAl and lpFe. The supply of dFe from CM was ~10 times that from the high-temperature hydrothermal activity at station BD21, which is located at ~3 km from the Middle Valley venting site and ~ 200 km from Vancouver Island. (2) DPb was maximum at the top layer of North Pacific Intermediate Water, probably owing to isopycnal transport of anthropogenic Pb via advection of subducted surface waters. Although dCo and dPb had different sources in the upper water, they showed a strong linearity below 300 m (r 2 = 0.95, n = 38), indicating concurrent scavenging. (3) A high-temperature hydrothermal plume occurred at a depth of 2300 m at BD21, accounting for maxima of dAl, dMn, dFe, lpCu, and lpPb and a minimum of dCu. (4) Strong bottom maxima of lpAl, lpMn, lpFe, lpCo, and lpPb occurred above the abyssal plain at the western foot of the JdFR, indicating resuspension of sediments. However, bottom maxima of d-species were apparent only for dAl and dCu. 相似文献