首页 | 本学科首页   官方微博 | 高级检索  
相似文献
 共查询到20条相似文献,搜索用时 31 毫秒
1.
Behavior features of heavy metals in the Haikou Bay waters   总被引:1,自引:0,他引:1  
INThonUCrIONBecause of the discharge of industrial waste water, waste residue, waste gas and acid rain theheavy metals concentration in river and lake and eventually in seawater have been increasing.Therefore many studies on heavy metals innuencing marine ecological environment have beencarried out (Sun et al., 1990; Sunda and Guillard, 1976; Zhu et al., 1992). After entering intothe sea, heavy metals change, transfer and transform, and these processes have gained attentionfrom marine envi…  相似文献   

2.
The application of inverse polarography with anti-adsorption physically coated mercury film electrode to analysis of fishes and benthos is described. The Zn, Cd, Pb and Cu concentrations' of determined marine organisms are 3-212 μg/g, 0.3-7.2 μg/g, 0.1-7.5μg/g, and 0.06-8.8 μg/g respectively.  相似文献   

3.
海水养殖池沉积物中重金属形态和生物酶活性的关系研究   总被引:1,自引:0,他引:1  
以连云港市对虾养殖池表层沉积物为研究对象,采用Tessier连续萃取法,研究了表层沉积物中重金属(Cu、Zn、Pb、Cd、Cr、As、Mn)的赋存形态和酶(脲酶、碱性磷酸酶、过氧化氢酶、转化酶)活性的相关性。结果表明,重金属Cu和Zn以有机-硫化物结合态为主要的赋存形态,Pb以铁锰氧化物态为主要的赋存形态,Cd以可交换态(平均33.47%)和碳酸盐结合态(平均31.16%)为主要存在形态,Cr和As主要以残渣态存在,Mn的铁锰氧化物态比例最高。脲酶的活性范围为0.45—8.96mg/(g·24h),碱性磷酸酶活性范围为2.45—6.69mg/(g·24h),过氧化氢酶活性范围为0.14—2.36m L/(g·min),转化酶活性范围为0.45—10.45mg/(g·24h)。脲酶活性与Cd、As的可交换态、Cd的碳酸盐结合态、Cu、As的铁锰氧化物态、Zn、Pb、Cd、Mn的有机硫化物态之间显著相关;碱性磷酸酶活性与Zn、Cd的铁锰氧化物态显著相关;过氧化氢酶活性与Cd的可交换态、碳酸盐结合态及残渣态、Cu、Cd、As的铁锰氧化物态、Zn、Pb、Cd、Mn的有机硫结合态之间显著相关;转化酶活性与Cu、Cd、As的可交换态、Cd的碳酸盐结合态、Cu、Cd、As的铁锰氧化物态、Zn、Pb、Cd、Mn的有机硫化物态、Cd、As的残渣态之间显著相关。酶活性可以用来指示海水养殖池沉积物中重金属的形态转化过程。  相似文献   

4.
The aim of this work was to monitor levels of Cd, Cu, Pb, Zn and Fe in sediments, mussels (Mytilus edulis chilensis) and limpets (Nacella magellanica) from the Industrial zone (IZ); fuel dock (FD) and Ushuaia Peninsula (UP) on the Beagle Channel. In sediments, seasonal variations showed high values of Cu and Pb in spring and Zn in autumn. Comparing among sites, Cd concentration was superior in UP (2.07 μg/g); while Pb was maximum in FD (41.00 μg/g). In mussels, a higher bioaccumulation in winter was found. Mussels from UP showed the highest bioaccumulation of Cu (5.95 μg/g) and those from FD presented the highest of Zn (170.15 μg/g). A seasonal trend was not found for limpets, while differences among sites were observed for Cd being the highest at IZ (3.02 μg/g). Although pollution level found was low, anthropic activities at the studied sites could result in deterioration, further monitoring is recommended.  相似文献   

5.
This paper explores the accumulations ana distributions of Cd, Pb and Cu in clam Area granosa through determining their contents in Dlood and soft parts. The results show an order of concentration factors for these metals therein as: Cd>Cu>Pb; the values of concentration factors and the patterns of distribution are similar for Cu and Pb but different from Cd. Concentration factors in blood can reflect the enrichement abilities of soft parts. Exposure experiments have indicated that the Pb level in blood is controlled by Pb concentrations in surrouding seawater, changing with time, that the Pb cocentration causing poisoning in the seawater is 1-100 μg/l, and that the Pb content in blood and soft parts of Area granosa increases with that of Pb increasing in seawater. There exist relationships of double logatithmic concentrations for Pb among the three mediums.  相似文献   

6.
南海表层水中的溶解态Cu,Pb, Zn,Cd   总被引:9,自引:0,他引:9  
于1998年“南海海洋环境调查”外业工作期间在南海的各个站位,按照严格的防沾污措施采集了106个表层海水样品.采用溶剂萃取-石墨炉原子吸收法对样品中的痕量重金属Cu,Pb,Zn,Cd含量进行了分析测试.测得各重金属的平均值如下:Cu 0.100 μg/dm3,Pb 0.060μg/dm3,Zn 0.086 μg/dm3,Cd 0.007μg/dm3,接近世界大洋水的浓度水平.各重金属的空间分布呈现出海区周边含量高于中央,浓度有自近岸向远海逐渐减小的趋势.相关分析的结果表明各重金属夏季相关性优于冬季,Cu与Cd存在良好的正相关关系,并且首次在南海表层水发现Cu,Cd与营养盐的相关关系.将重金属浓度值作数理统计分析,得到它们在南海的基线值.  相似文献   

7.
The understanding of the distribution of trace heavy metals in the world ocean has greatlyimProved in the past decades. But most of the data are of vertical profiles of certain stations(Bruland, l980; Paul et al., l992; RObert et al., l990) and large--scale study of temporaland spatial variability of trace heaVy metals in the ocean is rather few. In fact, affected by ver-tical mixing by upwelling or convection, biogenic removal, atmospheric fallout and continentalinput frorn rivers, the dist…  相似文献   

8.
海口湾海水重金属的行为特征   总被引:11,自引:2,他引:9  
本文对海口湾溶解态铜、铅、锌、镉进行了测定.铜的变化范围为:0.47~1.16μg/dm3,平均值为0.78μg/dm3;铅的变化范围为:0.94~2.36μg/dm3,平均值为1.36μg/dm3;锌的变化范围为:1.28~4.83μg/dm3,平均值为3.14μg/dm3;镉的变化范围为:0.005~0.072μg/dm3,平均值为0.030μg/dm3,Cu、Zn的溶解态含量在龙昆路生活污水排污沟口、秀英工业排污沟口及海甸溪口的测站相对较高,Pb、Cd溶解态含量较低,湾内各站平面分布较为均匀.它们的溶解态含量垂直变化趋势为:Cu、Pb、Zn底层大于表层,而Cd表层大于底层.对Cu、Pb、Zn、Cd的颗粒态含量也进行了测定,指出海口湾海水中的颗粒物对重金属的净化起一定作用.对铜的溶解态中的强络合态和不稳态铜也进行了研究,强络合态占总溶解态的比例均在85%以上,对生物起毒性作用有关的不稳态铜含量很低,均小于5nmol/dm3,表明目前海口湾海水中的重金属铜不会对生物生长产生影响.  相似文献   

9.
为了更清楚认识洋山海洋倾倒区海域沉积物的污染状况,测定了该海域倾倒前后表层沉积物中酸可挥发性硫化物(AVS)、酸可提取重金属(SEM)的含量,并对AVS、ΣSEM及ΣSEM-AVS差值的平面分布进行了分析。结果表明,该倾倒区及周边海域倾倒前、中、后表层沉积物中AVS含量分别为0.55~2.62,0.83~1.65和0.51~1.23 μmol·g-1,倾倒后AVS含量呈下降态势,倾倒区AVS含量高于周边海域;ΣSEM倾倒前、中、后平均含量分别为2.80,2.79和2.60 μmol·g-1,倾倒后ΣSEM含量略呈下降态势,往倾倒区方向富集;从单个重金属对ΣSEM的贡献率来看,Zn>Cr>Cu>Pb>Cd,SEMZn基本在35%以上,SEMCr基本在20%以上,而SEMCd均在1%以下,ΣSEM分布形态主要受Zn和Cr的控制;ΣSEM-AVS差值均大于0,且在倾倒区其ΣSEM-AVS值低于周边海域,说明倾倒区海域沉积物中重金属对生物可能有一定毒性。  相似文献   

10.
The resuspension of 65 marine sediments was simulated in the laboratory with elutriates from 30 different sites from the north coast of Spain. The partitioning of Cu, Pb and Zn between sediment and elutriate was studied as a function of different physicochemical characteristics of the sediment: organic matter (OM), fine fraction (FF), redox potential and acid volatile sulfides (AVS). Mean remobilization factors (RF) -calculated as metal concentration in the elutriate (μg/L) divided by metal concentration in the sediment (μg/g dry weight)- were 0.072 for Cu, 0.012 for Pb and 0.071 for Zn. Remobilization of Pb was significantly lower than that of Cu and Zn. Although AVS, OM and FF presented a strong intercorrelation, OM explained great part of the variability on Cu and Pb remobilization while AVS did it for Zn. A multiple regression model considering both OM and AVS explained slightly better the remobilization of Pb and Cu, but not that of Zn.  相似文献   

11.
Bioaccumulation of Cd, Co, Cu, Ni, Pb and Zn in Antarctic gammaridean amphipod collectives, Orchomene plebs (Hurley, 1965), was investigated during a cruise of RV "Polarstern" to the Wedell Sea. With the sole exception of Cd the organisms accumulated metals during exposure and depurated them in uncontaminated seawater. Four independent toxicokinetic experiments and one field study were modelled simultaneously to calculate the following size-dependent bioconcentration factors for organisms with body length 10 mm (BCF(10 mm)): 130 (Co), 4030 (Cu), 190 (Ni), 2900 (Pb), and 5210 (Zn). On the time scale of our experiments the data suggest an increased metal uptake by previously exposed test organisms. The collectives investigated may be regarded as potentially suitable biomonitors for Co, Cu, Ni, Pb and Zn but not for Cd. An approach to evaluate the sensitivity of Orchomene plebs as a biomonitor of waterborne metals in the field indicates minimal increments of the ambient exposure concentrations of 0.01 microg Co l(-1), 0.2 microg Cu l(-1), 0.4 microg Ni l(-1), 0.6 microg Pb l(-1) and 0.3 microg Zn l(-1).  相似文献   

12.
The acute effects of many individual, seawater-solubilized metals on meiobenthic copepods and nematodes are well known. In sediments, however, metals most often occur as mixtures, and it is not known whether such mixtures exhibit simple additive toxicity to meiobenthos. The estuarine meiobenthic copepod Amphiascus tenuiremis was tested in four acute (96-h) sediment bioassays to determine sediment and pore-water LC50s for single-metal exposures to copper (Cu), lead (Pb), nickel (Ni) and zinc (Zn). Laboratory-cultured copepods were exposed to clean 98% silt:clay sediments spiked with metal chloride solutions to yield five exposure concentrations plus a control. Trimmed Spearman-Karber analysis gave sediment 96-h LC50 values of 4.4 mumole Cu/g, 5.7 mumole Ni/g, 11.9 mumole Pb/g, 10.3 mumole Zn/g, and pore-water 96-h LC50 values of 2 mumole/l, 11.7 mumole/l, and 5.7 mumole/l for Cu, Ni, and Zn, respectively. Male survival after exposure to Cu, Pb, and Ni was significantly less than female survival (alpha = 0.05). Toxicity of a combined USEPA priority metal mixture to A. tenuiremis was assessed using sediment spiked equitoxically with Cd, Cu, Ni, Pb, and Zn. The sum toxic unit that produced a median lethal dose was 0.72. The mixture had a significantly greater than additive effect on A. tenuiremis survival, with the mixture being 1.4x more toxic than that expected by simple additivity.  相似文献   

13.
4种重金属离子对海洋三角褐指藻生长影响的研究   总被引:23,自引:0,他引:23  
于1993年4月-1993年5月以Zn^2+,Cd^2+,Pb^2+,Cu^2+不同浓度的海水对三角褐指藻进行生长影响的研究。实验表明,Cu^2+对三角褐指藻生长的毒性最大,其96hEC50为0.017mg/L。Pb^2+的毒性最小,其96hEC50为0.468mg/L。4种重金属离子的毒性顺序是Cu^2+>Cd^2+>Zn^2+>Pb^2+,除Cd^2+外,其他3种金属离子对该单细胞藻的生长安全  相似文献   

14.
In this paper, a comparison viral made between the two results of determining Pb, Cd, Cu and Zn in seawater by direct current (tripping voltammetry (DCS) with rotating glass carbon electrode and by differential pulse stripping voltammetry (DPS) with hanging mercury drop electrode (HMDE). By DCS, the range of linear calibration curves obtained was 4×10-3 M-2×10-7M for Cu, Zn and Cd, and 4× 10-9M-2×10-3M for Pb. By using DPS, the range of linear calibration curve was as follows: Cu 0.65-1.9 ppb; Pb 1.0-10 ppb; Zn 0.65-2.0 ppb; Cd 0.02-0.14 ppb. It was found that DCS could be used for determining Pb, Cu, Zn in coastal waters, but it is necessary to add gallium ion to it to eliminate the interference of Cu-Zn inter-metallic compound for determining Zn. The DPS is better for determinig Cd.  相似文献   

15.
Dissolved, weakly and strongly bound particulates Cu, Pb, Zn, Cd, Co, Ni and Fe have been measured in the surface water sampled from eleven stations in Xiamen Harbor by clean laboratory methods and GFAAS. The average concentrations found in dissolved fractions are Cu: 0.41±0.12; Pb: 0.014±0.008; Zn: 0.084±0.043; Cd: 0.022±0.004; Co: 0.009±0.004; Ni: 0.15±0.02; and Fe: 0.15± 0.02 μg/kg, which make up 62%, 6%, 12%, 85%, 5%, 25% and <1% of the total metals in the surface water respectively. The results are mucn lower than those reported previously in the coastal waters of China. Industrial sources of trace metal contamination are likely responsible for the distribution of trace metals.  相似文献   

16.
兴化湾表层海水和沉积物中重金属含量的时空变化特征   总被引:1,自引:0,他引:1  
蔡榕硕  白娅舒 《台湾海峡》2011,30(3):316-323
根据福建兴化湾2006年12月(冬季)和2007年4月(春季)表层海水以及2007年3月表层沉积物的监测资料,分析了该海域表层海水和沉积物中重金属Cu、Pb、zn、Cd、Hg和As含量的时空变化特征,评价了该海域重金属的污染程度.结果表明:冬季,调查海域表层海水中cu、Pb、zn、cd、Hg、As的含量范围分别为〈0.20~2.42、〈0.03~1.08、〈3.1~16.5、〈0.010—0.043、〈0.007~0.170、0.82~4.00肌g/dm’;春季其含量范围分别为0.91~3.80、0.18~3.40、8.7~36.0、〈0.Ol~0.22、〈0.007~0.063、0.63~1.58~g/dm’.这两季表层海水重金属的测值均低于《海水水质标准(GB3097—1997)》第二类标准值,其中春季cu、Pb、zn、cd含量的均值高于冬季,可能与陆源重金属污染物入海的影响有关.兴化湾表层沉积物中cu、Ph、zn、Cd、Hg和As的含量范围分别为7.60~22.oo、22.4~39.1、54.2~114.0、0.045~0.082、0.020~0.066、5.00~10.20mg/kg,均低于《海洋沉积物质量(GB18668_2002)》的第一类标准值.该湾表层海水和沉积物中重金属含量的平面分布特征呈近岸海域较高.此外,对其历年来监测结果的比较表明,兴化湾表层海水和沉积物中cu和Ph含量的多次监测值较接近,但重金属zn含量的监测值存在着波动现象.  相似文献   

17.
Ag, Al, Ca, Cd, Cu, Fe, Mg, Mn, Pb and Zn concentrations and 210Po and 210Pb activities were measured in 26 specimens of the squid Nototodarus gouldi taken from the waters of Bass Strait in one jigging operation. All the elements show wide ranges in concentrations in specimens apparently subject to the same environmental conditions. Copper concentration was 27-1 200 μg/g, and 210Po activity 4·8–24·2 Bq/g. The animal wet weights, the elements Ag, Al, Cd, Fe and Zn, and the radionuclide 210Po have coefficients of variation in the range 40–60%; Ca, Mg and Mn show the smallest variability (CV = < 30%), and Cu the greatest (CV = 12%). Significant correlations (p < 0·001) were found between the following pairs of elements: Cd-Zn, Cd-Cu, Zn-Cu, Mg-Mn, Fe-Mn, Ca-Mg and Fe-210Po.  相似文献   

18.
2007年6月(夏季)和2008年1月(冬季)分别对广东红海湾的汕尾港周边海域35个站位进行了表层海水的采样,在实验室内使用XGY-1011A型原子荧光光度计和HY-1F型多功能极谱仪获得了海水中重金属Hg、Cu、Pb、Zn、Cd的含量,研究了其时空变化特征,并采用综合指数法(WQI)评价其污染程度.结果显示:Hg、Cu、Pb、Zn、Cd的含量范围分别为0.009~0.050、0.9~4.3、0.4~1.4、1.6~19.0、0.1~0.7μg/dm3,平均含量分别为0.025、2.4、0.8、9.4、0.2μg/dm3.该海域表层海水各重金属含量的平面分布总体上呈现以品清湖向汕尾港递减的变化趋势.各站位重金属元素的单项污染指数和综合污染指数(WQI)均小于1,海水受重金属的污染程度较轻微,符合国家二类海水水质标准值的要求.2008年1月(冬季)重金属综合污染指数的平均值(0.17)略大于2007年6月(夏季)的平均值(0.14),海水中重金属污染程度略有加重的趋势.采用多元线性回归方法分析重金属元素含量与环境要素测值的相关程度,相关系数按从大到小的排列顺序大致为:Zn>Cd>Cu>Hg>Pb.  相似文献   

19.
Based on the survey of surface sediment in Xiamen Bay in October 2011, the speciation, distribution, and potential ecological risk assessment of heavy metals (Cu, Pb, Zn, Cd, and Cr) in this area were studied us-ing the sequential extraction method and ecological risk assessment method. The results indicated:(1) the total concentrations of these heavy metals were influenced by runoff, industrial wastewater, and sewage, and were all higher in the coastal area than the offshore area while the highest area of Pb was a little far-ther away from the coastal water due to atmosphere deposition;(2) sequential extractions suggested that Cu was mainly composed with residual and Fe/Mn-oxide bound fractions, Pb was bound to Fe/Mn-oxide, Zn and Cr were dominated by residual, and Cd bound to exchangeable and carbonate fractions; (3) the order of migration and transformation sequence was Cd&gt;Pb&gt;Cu&gt;Zn&gt;Cr and the degree of pollution was Cd&gt;Pb&gt;Cu&gt;Zn&gt;Cr;and (4) the ratios of the secondary and primary phases showed that Zn and Cr were both clean, Cu may be polluted, Pb was moderately polluted, while Cd was heavily polluted.  相似文献   

20.
城市道路沉积物重金属风险评价是表征城市环境质量的有效途径。采用重金属化学形态和生物可利用性来评估其生态风险更合理,越来越受到人们的关注。本文采集山东省青岛市崂山区10条次干道沉积物样品,分析不同粒径沉积物中Zn、Cd、Cu、Pb的含量、化学形态和生物可利用性,采用地累积指数(Igeo)和改进的生态风险指数(RIm)评价细粒径(小于75μm)沉积物中重金属污染水平和生态风险。结果表明:(1)沉积物粒径越小,重金属含量则越多。当粒径小于75μm时,Zn、Cd、Cu和Pb平均含量分别为山东省土壤元素背景值的10.63、6.07、3.39、2.70倍。(2)随粒径的减小,生物可利用性增大。小于75μm粒径的Zn、Cd、Cu和Pb的生物可利用态百分比为74%、78%、66%和55%。(3)评价结果显示,Zn、Cd、Cu和Pb的值分别为2.83、2.01、2.22和2.05,结果均为偏重度污染。(4)评价结果为较高生态风险,其中Cd属于极高风险,Cu和Pb属于中等风险,Zn属于低风险,Cd对的贡献高达75%。以重金属污染水平、迁移率、生物可利用性和生态风险为评价依据,认为Zn、Cd、Cu、Pb的风险均较大。该研究可为青岛市道路重金属污染防控提供指导。  相似文献   

设为首页 | 免责声明 | 关于勤云 | 加入收藏

Copyright©北京勤云科技发展有限公司  京ICP备09084417号