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1.
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   

2.
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   

3.
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   

4.
Dissolved concentrations of Cu, Pb, Zn, and Cd were measured in the Changjiang estuary and its adjacent waters. The results indicate that the ranges of dissolved heavy metals in the studied waters are as follows: Cu = 1.0−6.9 μg/L, Pb = 0.10−0.39 μg/L, Zn = 3.2−9.1 μg/L, and Cd = 0.011−0.049 μg/L. The behavior of the dissolved Cu was essentially conservative, but a high scatter was observed for the high salinity samples, and it is the same with Zn and Pb. The overall concentrations of dissolved Cd increase with the salinity. There were no differences between the surface, middle, and bottom layer for Cu, Pb, Zn, and Cd. Seasonal changes of their averages were not obvious on the whole. River discharges, sedimentary dynamics, and biological processes might determine the profiles of heavy metals. The text was submitted by the authors in English.  相似文献   

5.
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   

6.
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   

7.
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   

8.
The forms distribution of Zn, Cd, Pb and Cu in waters of the Northwest Bohai Gulf is investigated by inverse polarography of anti-adsorption physically coated mercury film electrode, the higher content of most forms of trace metals is in polluted estuary water, and unstable Zn and Pb are in anomalous distribution. The average concentrations read ΣZn 20.0μg/1 (14.5-36.6 μg/l, ΣCd 0.11pg/1 (0.080-0.14μg/1), ΣPb 1.0μg/1 (0.58-1.6 μg/1), and ΣCu 5.2μg/1) (2.37-8.43 μ/1) respectively.  相似文献   

9.
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   

10.
The concentrations of the trace metals Cd, Cu, Fe, Ni, Pb and Zn in the Göta River estuary have been investigated. The following metal fractions have been determined: acid-leachable, dissolved, labile and particulate.The estuary represents a salt wedge type estuary and is situated in a densely populated region of Sweden. The metal concentrations found for the dissolved fraction is in the range of what can be considered as background levels for freshwater. It is difficult to evaluate any estuarine processes other than conservative mixing for Cd, Cu, Ni and Zn. The dissolved levels in the freshwater end member are Cd, 9–25 ngl?1; Cu, 1·1–1·4 μgl?1; Fe, 20–75 μg l?1: Ni, 0·7–0·9 μg l?1: Pb 0·09–0·2 μg l?1; and Zn, 6–7 μg l?1:The results from the acid-leachable fraction show that at high suspended load the particles sediment in the river mouth. The trace metal levels in this fraction are subject to large variations.  相似文献   

11.
Some of the results about vertical profile of heavy metals of seawater to the south of Japan in Oct. 1990 are presented and discussed in relation to the concentration of dissolved Cu, Cd and Ni to biogeochemical environments. It points out that the distribution of dissolved Cu is higher in surface water than that in/upper 500 m layer, and maxima value attains the 8. 2 n mol/dm3 in depth of 4 000 m. The concentrations of dissolved Ni ranges from 3. 4 n mol/dm3 in surface seawater to 8. 5 n mol/dm3 in the deep to the south of Japan. The highest values are observed in the colder waters. This paper shows also that the vertical profile of dissolved Cd is perfect nutrient-type distribution. And dissolved Cd and Phosphate are linearly correlated by the regression equation. The ·Cd : ·N : ·P atomic ratio is 3. 5 × 10-4 : 14 : 1.  相似文献   

12.
The pathway and fate of heavy metals were studied in 10m3 enclosures at Xiamen Bay in 1985. The dissolved metals added are removed rather quickly during the first days, and their half-removal times ( t1/2) (d) are as follows: Pb 5. 4-5. 8, Hg 6. 7-14, Zn 11-22, Cu 16 - 29, and Cd 30-89. Zinc is transferred biologically to particles during phytoplankton bloom. The main Fate of added metals after 27 days is as follows; over 80% Cd and 60% Cu remain in dissolved phase, more than 60% Pb and 50% Hg transfer to settling settlement, while Zn is equally distributed in dissolved phase and settling settlement. The wall uptake is less than 2% of the total metals added. Organic materials play an essential role in the partition and the transfer of heavy metals in water column. Terrigenous and autochthonous particles show different affinities to different metals. Most heavy metals associate weakly with zooplankton. The Binding of Cd, Pb, Zn and Cu to the particles shows distinctive features related to the diagenetic  相似文献   

13.
Between 1980 and 1984 extensive studies were carried out in the Baltic Sea on trace metals (Cd, Co, Cu, Fe, Hg, Mn, Ni, Pb and Zn) in water, suspended matter and sediments. The results enabled the influence of different factors on metal distribution patterns to be considered. The vertical profiles of dissolved and particulate metals in waters of the central deep basins reflect influences caused by oxygen deficiency and anoxic conditions in near-bottom water layers. Peculiarities at Station BY15 in the Gotland Deep included high dissolved Fe, Mn and Co concentrations and remarkable enrichment of Zn (0.64%), Cd (51 μg g−1) and Cu (0.15%) in particulate matter from the anoxic zone. Manganese-rich particles were accumulated above this layer.In fine-grained soft sediments below anoxic deep waters, maximum contents of Cd, Cu and Zn were observed, relative to other coring sites, between Bothnian Bay and Lübeck Bight. The Hg content in sediments probably reflects the joint flocculation with organic matter. Land-based sources seem to play the leading part for maximum lead contents.  相似文献   

14.
The distribution, partitioning and concentrations of trace metals (Cd, Cr, Cu, Fe, Mn, Pb and Zn) in seawater, including dissolved and particulate phases, and in copepods in the ocean outfall area off the northern coast of Taiwan were investigated. Normalization of metal concentrations to the background metal concentration to yield relative enrichment factors (EF), which were used to evaluate the contamination of dissolved and particulate trace metals in seawater around the ocean outfall. The EF results indicated that the outfall area was significantly contaminated by dissolved Fe and Zn, and by particulate Fe, Cr, Cu, Pb and Zn. In addition, most trace metals were chiefly in the particulate phase. The average percentage of total metal concentrations (dissolved plus particulate phases) bound by suspended particulate matter followed the sequence Al(95%) = Mn(95%) > Pb(88%) > Cu(86%) > Fe(72%) > Zn(32%) > Cr(17.5%) > Cd(3.4%). Therefore, metal contamination is better evaluated in solid phase than in the dissolved phase. The concentration ranges of trace metals in the copepods, Temora turbinata, Oncaea venusta and Euchaeta rimana, near the outfall were: Cd, 0.23-1.81 microg g(-1); Cr, 16.5-195 microg g(-1); Cu, 14-160 microg g(-1); Fe, 256-7255 microg g(-1); Mn, 5.5-80.8 microg g(-1); Pb, 2.6-56.2 microg g(-1); Zn, 132-3891 microg g(-1); and Al, 0.21-1.13%. Aluminum, and probably Fe, seemed to be the major elements in copepods. The concentrations of trace metals in copepods, especially Temora turbinata, near the outfall were generally higher than those obtained in the background station. The mean increase in bioconcentration factor of metals in copepods ranged from 4 to 7 and followed the sequence Al(6.4) > Cu(6.2) > Fe(6.0) > Zn(5.7) > Pb(5.6) > Cr(5.5) > Cd(5.1) > Mn(4.7). Therefore, marine copepods in the waters of northern Taiwan can accumulate trace metals over background concentrations and act as contamination indicators.  相似文献   

15.
An investigation of trace metal distributions in the Western Mediterranean Sea was carried out during the RRS Discovery cruise (July 1993) in which a transect from the Strait of Gibraltar to the Strait of Sicily was conducted. Organically complexed dissolved trace metals and their total concentrations were measured to investigate the end-members and to predict the environmental capacity of the Mediterranean for potential toxic metals. The distribution of trace metals can be accounted for by the mixing of several end-members and by some atmospheric inputs to the surface water. For Pb and Fe, the effects of the atmospheric inputs are more pronounced than for the other metals. Due to the rapid exchange of water masses, the Western Mediterranean may have the ability to assimilate the increased external inputs for some trace metals such as Cu, Cd, Ni and Zn. But the external inputs for Pb and Fe exceed the removal capacity of the Western Mediterranean and these elements may accumulate in the water column of the western basin. The C18 Sep-Pak technique and direct determination by DPASV were used to determine the amount of trace metal–organic complexes. The C18 Sep-Pak column isolates only a small fraction of trace metals except for Cu. The maximum hydrophobic fractions for the studied trace metals, except for Cd and Pb, which are not detectable, were found in the subsurface layer at all stations. This maximum may well be linked to picoplankton activity and the picoplankton, prochlorophytes may have an important role in the speciation of dissolved Cu as well as Synechococcus. These organic ligands for Cu were produced at the maximum of biological activity in the Western Mediterranean basin and seem to be accumulated at halocline level by Mediterranean hydrodynamic characteristics. However, direct determination by DPASV showed that the major part of Cu, Cd and Pb, complexed by organic materials, was not isolated by C18 Sep-Pak technique.  相似文献   

16.
红海湾底质重金属分布与背景值探讨   总被引：3，自引：0，他引：3  
红海湾表层沉积物中Zn,Cd,Cu,Pb含量呈湾顶高于湾中部和湾口的分布特征,在河口潮间带形成污染区。根据背景区沉积物重金属平均含量和2倍标准差,提出用红海湾表层沉积物中Zn,Cd,Cu,Pb,Ni,Cr的背景上限（分别为90,0.65,20,55,30,45mg·kg~-1干重）作为背景参考值。红海湾表层沉积物中Zn,Cd,Cu,Pb呈显著的正相关关系,推测四者具有相似的来源。  相似文献   

17.
2009年夏季,九龙江口表层水COD、DO、PO4-P、DIN、TN、TP含量的变化范围分别为0.81～4.37、3.74～5.76、0.025～0.046、0.53～1.89、0.68～2.65、0.046～0.253 mg/dm3,平均值分别为2.38、5.09、0.04、1.30、1.70、0.10 mg/dm3;而Cu、Pb、Zn、Cd、Cr、Hg、As、Oil含量的变化范围分别为0.92～2.09、0.005～1.431、0.77～4.05、0.006 4～0.054 2、0.073～0.622、0.010～0.038、0.9～5.7、8.5～17.2μg/dm3,平均值分别为1.45、0.26、1.84、0.03、0.26、0.02、2.3、12.0μg/dm3.与1992年厦门海域水质调查结果比较分析表明:影响九龙江口海水质量的环境因子主要是DIN、PO4-P含量.应用主成分分析(PCA)方法对其污染来源进行分析表明:14个变量的全部信息可由4个主成分反映(特征值:7.24+2.06+1.63+1.25=12.18个变量),总贡献率达87.01%.第一主成分的贡献率为51.74%,主要体现了水体中营养要素氮、磷和COD的影响,其中COD、PO4-P、TN、DIN含量之间的相关系数介于0.778(COD～PO4-P)至0.971(TN～DIN)之间.第二主成分的贡献率是14.72%,在As、TP、Pb上的载荷分别为0.938、0.814、0.731,它主要反映表层水中重金属As的影响.第三主成分的主要特征是在Cr、Zn、Cu含量上有较高的载荷,分别为0.929、0.915、0.757.第四主成分的主要特征是在Hg、Cd含量上有较高载荷,且它们之间的相关系数为0.627.第三、四主成分分析结果表明九龙江口表层水受部分重金属元素的污染.通过PCA聚类分析调查站位间污染状况的相似性及远近关系,及对九龙江河口区主要化学要素污染来源的分析,结果表明其表层水污染来源可能是上游生活污水、生活垃圾未能很好处理就排入河流以及农业化肥污染和上游工业点源废水排放等.  相似文献   

18.
Dissolved and particulate trace metals (Cu, Cd, Pb, Zn, Ni, Fe and Mn) measured at six stations along the Scheldt estuary in October/November 1978 are compared with more recent data. Based on Ca content in the suspended matter, three distinct geochemical regions could be distinguished: the upper estuary (salinity 1–7) dominated by fluvial mud, mid-estuary (salinity 7–17) where the composition of the suspended matter remained relatively constant, and the lower estuary where marine mud prevailed. Re-suspension of sediments is the major factor controlling the composition of the particles in the upstream region. Anoxic conditions prevailed in the upper part of the estuary extending to a salinity of 15 in 1978, while at present the seaward boundary of the anoxic water body is located at less saline waters. Furthermore, the present-day metal load is much lower than in 1978. As a consequence of the changed situation, maxima in dissolved concentrations of redox-sensitive metals in the mid/lower estuary have moved as well, which affects the trace metal re-distribution pattern. In the anoxic zone, exchange processes between dissolved and particulate metal fractions were strongly redox regulated, with Fe and Mn as excellent examples. Iron was removed from the dissolved phase in the early stages of mixing resulting in an increase in the suspended particulate matter of the leachable ‘non-residual' Fe fraction from 2 to 3.5%. Due to its slower kinetics, removal of Mn from solution occurred in mid-estuary where oxygen concentrations increased. Cu, Cd and Zn on the contrary were mobilised from the suspended particles during estuarine mixing. External inputs of Pb, and to a lesser extent of Cu, in the lower estuary resulted in the increase of their particulate and the dissolved concentrations. Calculated Kd (distribution coefficient) values were used to assess the redistribution between the dissolved and particulate phase of the investigated metals. Due to the existence of the anoxic water body in the upper estuary, the importance of redox processes in determining the Kd values could be demonstrated. The sequence of Kd values in the upper estuary (Fe, Cd, Zn, Pb > Cu > Ni, Mn) is significantly different from that in the lower estuary (Fe > Mn > Pb, Ni, Zn, Cu, Cd). Thus, in such a dynamic estuary single metal-specific Kd values cannot be used to describe redistribution processes.  相似文献   

19.
In 1984, on a transect covering the whole Baltic Sea and parts of the adjacent North Sea, 160 water samples were taken and analysed for their concentrations of particulate and dissolved metals. In addition, the suspended materials were investigated for their elemental bulk composition.The particulate fractions represented from about 5% (Cd, Cu and Ni) to 50% (Fe and Pb) of the total (particulate plus dissolved) concentrations. For some elements (Ba, Cd, Cu, Pb and Zn), the particulate matter from the surface microlayer was enriched with respect to those suspended materials taken from 0.2 m depth. This could reflect the atmospheric input of metal-rich aerosols. In anoxic deep waters, maximum contents of Zn (6400 μg g−1), Cu (1330 μg g−1) and Cd (12 μg g−1) were observed in the particulate matter, indicating sulphidic forms. On the other hand, under oxic conditions the distribution coefficients (Kd) decreased with the water depth (Cd, Fe and Pb).Relative to global background levels, the particulate matter contained metal “excesses” amounting to more than 90% of the total contents (Cd, Mn, Pb and Zn). Automated electron probe X-ray microanalysis (EPXMA) revealed that the elemental composition of sediments is mainly governed by post-depositional processes of early diagenesis and is only weakly related to the composition of suspended matter in the overlying water body. For instance, in relation to surface mud sediments of the central Baltic net-sedimentation basins, Zn, Cd, Cu and Mn had 30–100% higher levels in the suspended materials. The general pattern of metal contents of particulate matter taken from 10 m depth on a transect between the Bothnian Bay and the North Sea were—possibly as a result of anthropogenic inputs—rather similar for Pb, Zn and Cu. For Fe and Mn, the distribution patterns along the transect were probably governed by the natural loading characteristics and by the biogeochemistry of those elements.  相似文献   

20.
研究了条纹小环藻（Cyclotella striata）对Cu2＋和Zn2＋的耐受力、吸附率和吸附量的作用规律.结果表明：Cu2＋和Zn2＋对条纹小环藻的生长影响显著（p〈0.05）,随着Cu2＋、Zn2＋含量的升高,其对条纹小环藻生长的抑制作用增大;当Cu2＋和Zn2＋的含量分别高于4.00×10-3、0.01 mg/dm3时,其对条纹小环藻的生长几乎没有影响;Cu2＋和Zn2＋对条纹小环藻生长的半抑制含量分别为0.26、11.17 mg/dm3.Cu2＋含量为1.00 mg/dm3和Zn2＋含量为50.00 mg/dm3的组合,对条纹小环藻生长的抑制率达72.28%,Cu2＋对条纹小环藻的毒性大于Zn2＋.条纹小环藻对Cu2＋、Zn2＋吸附效果良好,当藻细胞含量为2.45×107cells/dm3时,对Cu2＋的吸附率为63.00%;当藻细胞含量为1.75×107cells/dm3时,对Zn2＋的吸附率为60.52%;条纹小环藻对Cu2＋和Zn2＋的吸附量分别为9.26 mg/g（21.30×10-9mg/cell）和20.06 mg/g（46.15×10-9mg/cell）时,Cu2＋和Zn2＋对条纹小环藻不会产生明显毒性.  相似文献   

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