Aquatic surface microlayer contamination in chesapeake bay

The aquatic surface microlayer (SMIC), 50 μm thick, serves as a concentration point for metal and organic contaminants that have low water solubility or are associated with floatable particles. Also, the eggs and larvae of many fish and shellfish species float on, or come in contact with, the water surface throughout their early development. The objectives of this study were (1) to determine the present degree of aquatic surface microlayer pollution at selected sites in Chesapeake Bay, and (2) to provide a preliminary evaluation of sources contributing to any observed contamination.Twelve stations located in urban bays, major rivers, and the north central bay were sampled three times, each at 5-day intervals during May 1986. Samples of 1.4–4.1 each were collected from the upper 30–60-μm water surface (surface microlayer, SMIC) using a Teflon-coated rotating drum microlayer sampler. One sample of subsurface water was collected in the central bay.At all stations, concentrations of metals, alkanes, and aromatic hydrocarbons in the SMIC were high compared with one bulk-water sample and with typical concentrations in water of Chesapeake Bay and elsewhere. SMIC contamination varied greatly among the three sampling times, but high mean contaminant levels (total polycyclic aromatic hydrocarbons, 1.9–6.2 μg 1⁻¹; Pb, 4.9–24 μg 1⁻¹; Cu, 4–16 μg 1⁻¹; and Zn, 34–59 μg 1⁻¹) were found at the upper Potomac and northern bay sites. Three separate areas were identified on the basis of relative concentrations of different aromatic hydrocarbons in SMIC samples - the northern bay, the Potomac River, and the cleaner southern and eastern portions of the sampling area.Suspected sources of surface contamination include gasoline and diesel fuel combustion, coal combustion, and petroleum product releases. Concentrations of metals and hydrocarbons, at approximately half the stations sampled, are sufficient to pose a threat to the reproductive stages of some fish and shellfish. Sampling and analysis of the surface microlayer provides a sensitive tool for source identification and monitoring of potentially harmful aquatic pollution.     

Toxicity of sea-surface microlayer: Effects on herring and turbot embryos

Marine fish eggs, from herring (Clupea harengus) and turbot (Psetta maxima), were used to test the effects of the sea-surface microlayer on embryonic development. The eggs were exposed in static systems to full strength microlayer and 1,10,50% dilutions. Depending on the sampling site (Helgoland harbour, Kiel Förde, Travemünde marina, Elbe Hamburg Port) and time, microlayer contained varying amounts of Zn, Cd, Cu, Ni, Fe, Pb and Co, in concentrations 100 times above those found in subsurface bulk water. Chlorinated hydrocarbon pesticides were not found at concentrations elevated above bulk water, but considerable amounts of petroleum hydrocarbons and phthalate esters were detected. Microlayer displayed differential concentration-dependent toxicity for each species used in the experiments. Effects on hatching time as well as total hatch (%) and number of abnormal larvae were recorded. Herring eggs were most affected by Helgoland microlayer (suspected effect of high metal content) while turbot eggs were most sensitive to Travemünde and Elbe microlayer (suspected effect of high petroleum hydrocarbons). The usefulness of microlayer studies as a tool for environmental assessment is discussed. An impact of microlayer effects on recruitment in sensitive species is deemed possible.     

Influence of point sources on trace metal contamination and distribution in a semi-enclosed industrial embayment: the Ferrol Ria (NW Spain)

Concentrations of heavy metals (Co, Cr, Cu, Fe, Ni, Pb and Zn), particulate organic (POC) and nitrogen (PON), particulate inorganic carbon (PIC) and opal content were measured in 35 surface sediment samples taken in the Ferrol Ria (Galicia, NW Spain). This ria is a semi-enclosed embayment receiving inputs from industrial and urban effluents. The restricted water exchange between the ria and the shelf has led to a significant accumulation of contaminants within the embayment. Two main factors controlled the metal distribution and concentrations in the bay: (1) contamination point sources and (2) distribution of the organic-rich sediments. Zn, Cu and, to a lesser extent Pb, were the metals most contaminated in the bay, with average enrichment factors (AEF)—defined as the mean metal concentration in the bay divided by the background value reported for this ria—of 4.7, 5.5 and 2.7, respectively. The highest concentrations for these metals were observed in the vicinity of the point sources. Values found for Zn, Cu and Pb are comparable to other industrialized coastal areas in the world. For Ni, Fe, Cr and Co a negligible to low contamination was found (AEF = 1–2), with the highest concentrations found in the organic-rich sediments.     

Geochemistry of suspended matter from the Baltic Sea 2. Results of bulk trace metal analysis by AAS

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 (K_d) 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.     

Accumulation of sediments,trace metals (Pb,Cu) and total hydrocarbons in Narragansett Bay,Rhode Island

The accumulation of sediments, trace metals and hydrocarbons has been estimated from the analysis of the sediment from six coring sites in Narragansett Bay. Radionuclides (²³⁴Th_xs, ²¹⁰Pb_xs, ^239,240Pu) with known input functions and trace metals (Cu, Pb) were used. We estimate that 6·9 × 10⁴ tons of sediments, 51–90 tons of Pb, 72–100 tons of Cu and 400–1000 tons of total hydrocarbons accumulate annually under present conditions in the bay. This represents 64–117% (Pb), 89–123% (Cu) and 23–58% (hydrocarbons), respectively, of present day inputs to the bay. Furthermore, close to 100% of the particle-reactive radionuclides ²¹⁰Pb and ^239,240Pu accumulate in the bay. Present day inputs to the bay were calculated independently as 77–80 tons Pb and 81 tons of Cu. Sewage effluents were the dominant source of Cu, whereas atmospheric deposition and urban runoff were most important for Pb. Dredging activities by the U.S. Army Corps of Engineers between 1946 and 1971 removed more sediments from the bay than would have accumulated during the same time in the undredged areas of the bay. Copper smelting and coal mining on the shores of the upper bay during 1866–1880 left an imprint in the sediments which is still evident. Model derived accumulation rates of Pb, Cu and coal during that time were 3–4 times present-day inputs.     

Accumulation of Phosphorus and Heavy Metals in the Peel-Harvey Estuary in Western Australia: Results of a Preliminary Study

Concentrations of P and of heavy metals (Zn, Cd, Pb, Cu) were determined in sediment cores from the Peel-Harvey Estuary in Western Australia. Two cores were extracted, each representing one of the two basins of the estuary. Sediments were dated by surplus²¹⁰Pb, by¹³⁷Cs and by changes in the Fe/S ratio. Increasing exports of P from the mainly agricultural catchments have resulted in more than a doubling of both total P and acid extractable inorganic P in sediments of the estuary. Accumulation of P in the estuary is less than expected for complete retention of inputs of P from the major tributaries. Historical data show that since 1950 average concentrations of dissolved inorganic P have approximately doubled in the Peel Inlet and increased by times seven in the Harvey Estuary. Increases in concentrations in surface sediments of acid extractable Zn, Cd, Pb and Cu are noticeable in the Peel Inlet, and of Zn and Cd in the Harvey Estuary. The greatest increase, relative to background, is shown by Zn. Concentrations of extractable Zn and Cd in surface sediments are similar to those estimated from average concentrations in the water column for equilibrium adsorption to organic matter in sediments. Extractable Pb is greater than estimated for equilibrium adsorption to sediments. Extractable Cu is of the order of what can be expected for equilibrium adsorption to sediments in the Peel Inlet, but is less than expected in the Harvey Estuary.     

泉州大港湾海水、沉积物及水产生物体内重金属的含量分布

根据1997年7月大港湾海域环境调查资料,着重分析了大港湾海水、表层沉积物及水产生物体内重金属的含量及分布。结果表明：大港湾海水中Cu,Pb,Cd,Zn的含量均低于渔业水质标准,大港湾湾顶水域,海水和表层沉积物中Cu,Pb,Cd,Zn的含最明显高于湾口水域：湾南部水域高于北部水域。文中还根据《海洋沉积物质量》、《无公害食品》、《食品中锌限量卫生标准》、《海洋生物质量》标准对表层沉积物和6种水产生物的重金属污染程度进行评价,结果大港湾的水产生物体内的重金属含量均未超标,但沉积物中的Cd含量已超标。     

威海双岛湾海域重金属的分布特征及生态风险评价

根据2012年双岛湾海域环境调查资料,研究了海水和表层沉积物中重金属的分布特征以及生态风险。结果显示,双岛湾海域海水中的重金属Cu和Pb在湾中部和湾底的部分站位含量较高,Zn和Cr含量在湾底最高、湾外最低,Cd和Hg在湾底和湾外的含量均高于湾中部,As的分布比较均匀;除Zn和Pb外,其余重金属含量均高于周边其他海域。双岛湾海域沉积物中重金属含量较低,与区域背景值相近,其中重金属Hg和Cd在湾内沉积作用明显,而Cu、Pb和Cr在湾外沉积作用比较明显。相关性分析表明,有机碳含量对双岛湾沉积物中的重金属分布影响不大。生态风险评价结果表明,双岛湾海域海水未受到重金属的污染;表层沉积物中重金属存在中低度的生态风险,具有潜在的不利生物毒性效应,重金属毒性大小依次为Pb>As>Cu>Hg>Cr=Cd>Zn。     

The sea-surface microlayer of puget sound: Part I. Toxic effects on fish eggs and larvae

The sea surface is an important habitat for the developmental stages (eggs and larvae) of many fish and invertebrates; it is also a concentration point for anthropogenic contaminants entering the sea. Studies were conducted to determine the extent to which the sea surface of Puget Sound was toxic to the early life history stages of fish. Three urban bays with suspected contamination, a rural reference bay, and a Central Sound site were compared. Surface-dwelling eggs and organisms (zooneuston) were collected with a surface-skimming neuston net and their densities enumerated. Sand sole (Psettichthys melanostictus) embryos were exposed in the field and laboratory to the sea-surface microlayer. To develop a useful year-round approach to monitoring sea-surface toxicity, larval development of anchovies, kelp bass, and sea urchins was also evaluated as an indication of sea-surface microlayer toxicity.During the spawning season (February and March), urban boys in Puget Sound had lower concentrations of sand sole eggs and neustonic organisms on the sea surface than did the rural bayor Central Sound reference sites. Compared to the reference sites, laboratory exposure to surface microlayer samples collected from urban bay sites generally resulted in more chromsomal aberrations in developing sole embryos, reduced hatching success of sole larvae, and reduced growth in trout cell cultures. In situ hatching success of sole eggs was reduced by half or more in urban bays compared to reference sites.Toxicity was associated with visible surface slicks and, in urban bays, increased with increasing surface pressure (dynes cm⁻¹). Results to be reported separately (Part II) indicate that toxicity is strongly correlated with the presence of high concentrations of polycyclic aromatic hydrocarbons and metals in the sea-surface microlayer. The toxicity of SMIC samples was similar when evaluated by sole, anchovy, kelp bass, or sea urchin tests. A sea-surface monitoring program could use sea urchin embryos to evaluate site-specific sea-surface toxicity throughout the year.     

Can the Movements of Barramundi in the Fly River Region, Papua New Guinea be Traced in their Otoliths?

To determine whether the concentrations of heavy metals in fish otoliths could be used to infer the fish's movement into water contaminated by heavy metals, we collected barramundi Lates calcarifer from two sites below the outfall from a large copper mine. It was first demonstrated that otolith Sr concentration could be used to separate the marine and freshwater life phases. Twelve elements were then examined (in particular Cu, Mn, Zn, Cd and Pb) in the otoliths by laser-ablation inductively coupled plasma mass spectrometry (LA-ICPMS). Cadmium concentrations were rarely above the detection level of the instrument. There were low concentrations of Cu in the otoliths of most fish during the freshwater phase of their life history. Three fish out of 10 had higher levels of Cu at some ablations, coinciding with higher concentrations of both Zn and Pb. However, further analysis found no correlation between the Cu concentration of replicate ablations in the same growth zone to those with initially higher Cu values. Copper concentration in the otoliths did not rise during the period the fish were in freshwater, despite the concentration of dissolved Cu in the water being several times greater than in the lower estuary and adjacent coast.These results and other data from recent studies of heavy metals in fish tissues suggest that very little of the dissolved Cu in the Fly River is in the form of free ions that can be adsorbed across the gills and into the blood and the otoliths. It can be concluded that otoliths are not a good indicator of the history of barramundi movements into water contaminated with heavy metals. Our data support recent studies that suggest that the concentration of many elements, such as Cu, may vary in the endolymph around the otolith and thus may be attached to the calcium-binding proteins that form the matrix around the aragonite. Hence, high concentrations of heavy metals in some ablations may be related to the relative amount of aragonite and protein in each ablation rather than reflect environmental differences.     

Trace metal distribution in different chemical fractions of nearshore marine sediments

The major objective of this study was to carry out sequential chemical extractions for the partitioning of particulate trace metals in sediment samples, collected from False Bay. Eight metals, Cd, Cu, Cr, Fe, Mn, Ni, Pb and Zn, were examined in each of 65 samples. Three chemical fractions of the sediments were separated and the concentrations of the trace metals were determined in each, by atomic absorption techniques. The three different leaches used were hydroxylamine hydrochloride-acetic acid, hydrogen peroxide, and nitricperchloric acids. Fe and Pb were concentrated mainly in the fraction extracted by nitric-perchloric acid, while Cu, Zn and Ni were found mainly in the peroxide fraction. Most of the metals in the peroxide phase were found in the finer sediments in the central area of the bay, where the concentration of organic meterial was high. The metal concentrations (except for Pb) correlated well with the organic content of the sediments.     

Distribution and cycling of dimethylsulfide in surface microlayer and subsurface seawater

Laboratory experiments, along with in situ investigation in Funka Bay, Japan, were conducted to determine the enrichment factor (EF) of dimethylsulfide (DMS) in the sea surface microlayer, as well as its the production and consumption rates. The EF of DMS in the microlayer was largely affected by various factors including sampling methods, sampling thickness, temperature, salinity, and DMS concentration in bulk water. In all cases but the sealed system, a part of DMS in the microlayer was always unavoidably lost during sampling. High temperature, great wind speed, and slow sampling would increase the extent of loss of DMS due to volatilization. In the field, the screen-collected samples usually exhibited greater microlayer enrichment for DMS than the plate-collected samples, showing that the screen sampler might be more effective for collecting the in situ microlayer DMS. The production and consumption rates of DMS in the surface microlayer were higher than those in the bulk water and these two rates were significantly correlated with the microlayer DMS concentrations. Moreover, the EF of DMS appeared to be related to the microlayer production rate of DMS, providing evidence supporting the observed DMS enrichment in the microlayer. The DMS production and consumption rates were not directly related to its concentrations in the bulk water, suggesting that the processes of production and consumption of DMS were very complex. In the surface microlayer, the biological turnover time of DMS varied from 0.4 to 1.9 days, with an average of 0.9 days, which was about 540-fold greater than the mean DMS sea–air turnover time (2.4 min). Thus, the biological process occurring within the microlayer can be neglected when we consider the sea–air exchange of DMS. Considering the microlayer production rate of DMS (an average of 9.7 nM day⁻¹) to be too small to counteract the sea-to-air removal of DMS, the main source of DMS in the microlayer appears to be through vertical transport by turbulent diffusion from the underlying water.     

Processes affecting particulate trace metals in the sea surface microlayer

Concentrations of particulate Fe, Mn, Ni, Cu, Zn, Cd and Pb have been measured in surface microlayer and subsurface seawater samples collected in the North Sea adjacent to the East Anglian coast, in an area subject to a considerable fluvial input of clay minerals. The results are interpreted by estimating the magnitudes of different processes affecting particulate matter in the microlayer: atmospheric deposition, Brownian diffusion, gravitational settling, bubble flotation and mixing. Both Fe and Mn are strongly depleted in the microlayer, evidently as a result of gravitational settling of Fe- and Mn-bearing mineral particles out of the microlayer. These particles are mixed into the surface region from the water column beneath. Microlayer enrichment of Cu, Zn and Pb was also observed and probably results from flotation of particles attached to rising bubbles. In one set of samples, however, the marked enrichment of these elements, as well as Ni, may result instead from deposition of particles from the atmosphere directly onto the water surface.     

The pathway and fate of the heavy metal mixture in Xiamen marine experiment enclosures

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     

辽东湾西北部海域沉积物重金属含量分析及污染评价

为了解辽东湾西北部海域沉积物重金属的分布特征及污染程度,文章基于2017年3月辽东湾西北部12个采样站位表层沉积物7种重金属含量(Hg、Cu、Pb、Cd、Zn、Cr、As)的测定,对辽东湾西北部海洋沉积物中的重金属进行了研究。SPSS用于沉积物中重金属含量统计分析并通过地累积指数和潜在生态风险指数的方法评估重金属污染和生态危害的程度。结果显示:(1)辽东湾西北部沉积物重金属含量平均值只有Cd符合海洋沉积物一类标准,变异程度由高到低依次为Hg、Cd、As、Zn、Pb、Cu,汞和镉受人为来源控制最高;(2)地累积指数法评价结果表明重金属元素污染程度由大到小依次为Hg、Cd、Zn、As、Cu、Pb;(3)潜在生态风险指数法评价结果表明,单因子潜在生态风险系数由高到低依次为Hg、Cd、As、Cu、Pb、Zn、Cr,Hg具有很强的生态风险,综合生态风险指数在233.77~4785.15,平均1224.12,处于很强的生态风险水平。文章揭示了辽东湾西北部海域沉积物重金属的分布特征,为该海域的生态环境建设提供依据。     

Cesium-137, metals and organic carbon in the sediments of the James River estuary,Virginia

A wide variety of sedimentary subenvironments are found within a 10-km stretch of James River including a flood dominated channel (Rocklanding Channel) and its bank (Rocklanding Shoal), a shoal with a water depth of 1 m separating two channels (Point of Shoals), an ebb-dominated channel (Burwell Bay Channel) and its bank (Burwell Bay Bank) and a tributary (Warwick River). The concentrations of Cs-137, Cu, Pb, Zn and organic carbon in the fine-grained sediments (i.e. < 63 μm) and the amount of fine-grained sediments in eight cores covering these subenvironments were determined. The sedimentation rates, estimated by Cs-137 geochronology, range from 0·4 to > 3 cm year^?1. The sedimentation rates in the Burwell Bay region are two or more, times those in the Point of Shoals and in the Rocklanding Channel and Shoal, reflecting the weaker currents in the Burwell Bay region. These sedimentation rates agree well with those obtained independently by measuring changes in the bathymetry of this area between 1873 and 1943. The concentrations of Cs-137, Cu, Pb, Zn and organic carbon in surface sediments vary by a factor of two to three. The concentrations are higher in the Burwell Bay region, probably as a result of the higher rates of accumulation of recently formed sediments in these subenvironments. The inventories of fine-grained sediments and of Cs-137, Cu, Pb, Zn and organic carbon accumulated since 1954 are also up to an order of magnitude higher in the Burwell Bay region. Although the concentrations of fine-grained sediments in three cores obtained in this region are similar, the inventories still vary by a factor of two to three. The inventories of Cs-137, Cu, Pb, Zn, organic carbon and fine-grained sediments correlate well with each other indicating that Cs-137 can be a useful tracer for studying the fate of these metals and organic carbon in estuarine environments. The inhomogeneity of the concentrations and inventories of the different elements along a 10-km segment of a river suggests that a closely-spaced sampling programme is essential for characterizing the sedimentary provinces within an estuary. The concentrations of Cs-137, metals and organic carbon in the coarse-grained sediments (i.e. > 63 μm) are considerably lower than those in fine-grained sediments. Thus, the contribution of coarse-grained sediments to the total inventory of these elements is small.     

大辽河口溶解态重金属的变化特征及影响因素研究

分别于2009年7月和2010年4月在大辽河口采集表层水样,测定了水体中溶解态Cu、Pb、Zn、Cd和Cr的含量,并对其分布特征及影响因素进行探讨。结果表明:除2010年4月Cu,及个别站位Pb、Zn含量较高外,表层水重金属含量均达到国家一类海水水质标准。2010年4月表层水中Cu、Pb、Zn、Cr的浓度大于2009年7月,2航次Cu、Cd、Cr的含量由河向海呈逐渐上升趋势,2010年4月Pb、Zn的含量表现为河口段高于口外海滨。重金属的含量和分布主要受径流量、潮汐作用以及风浪扰动的影响。     

Cadmium,lead, copper,and zinc in Elminius modestus Darwin (Crustacea,Cirripedia) from Waitemata and Manukau Harbours,Auckland, New Zealand

Abstract

Concentrations of cadmium (Cd), lead (Pb), copper (Cu), and zinc (Zn) were measured in adult barnacles (Elminius modestus Darwin) from Waitemata and Manukau Harbours in the Auckland area, New Zealand. As in studies on sediments reported in the literature, it was possible to identify areas of likely anthropogenic influence, e.g., around the Auckland Harbour Bridge for Pb, Cu, and Zn. Groups of individuals with highest concentrations for these metals showed 19.8–23.8 mg Pb kg^?1, 198–266 mg Cu kg^?1, and 4460–6530 mg Zn kg^?1 (95% confidence limits, dry weight basis). Cd concentrations found for all barnacles from the Auckland area ranged from 0.8 to 3.1 mg kg^?1. Two samples from Omaha Beach, 60 km north of Auckland, were used as a reference. Accordingly, groups of individuals with lowest concentrations for Pb, Cu, and Zn could be allocated to this site using the Student‐Newman‐Keuls Multiple Range Test (0.5–1.3 mg Pb kg^?1, 8–10 mg Cu kg^?1, and 144–214 mg Zn kg^?1 ; 95% confidence limits). Only Cd concentrations were highest at Omaha Beach (8.6–12.1 mg Cd kg^?1 ). This result may have arisen from “naturally” increased bio‐availabilities of certain metals in mangrove systems which are reported in the literature. Generally, metal concentrations in barnacles from the Auckland Harbour area and from Omaha Beach were within the wider range for E. modestus as well as other barnacle species reported in the international literature.     

Seasonal and vertical variations in the elemental composition of suspended and settling particulate matter in Puget Sound,Washington

The distributions of C, Al, Si, P, Cr, Mn, Fe, Ni, Cu, Zn and Pb in suspended and settling particulate matter from Puget Sound were studied to investigate the processes affecting the uptake of trace metals by particulate phases. Particulate material was collected by water filtration procedures and sequentially-sampling sediment traps during approximately bimonthly surveys from December 1980 through December 1981 at a station located in the center of the main basin of Puget Sound. The samples were selectively extracted for trace metals associated with oxide, organic, and residual phases and analysed by graphite furnace atomic absorption spectrophotometry and X-ray energy spectrometry. The results show that for Mn, Fe, Zn and Pb, residual and oxide phases were the most important phases controlling the vertical flux; whereas residual and organic phases controlled the vertical flux of Cu. The average annual flux data were used along with dissolved metal profiles to compute scavenging residence times for several trace metals in Puget Sound. Relatively short scavenging residence times (i.e. < 30 days) were calculated for those metals that were significantly enriched in oxide phases, such as Fe, Mn and Pb. In contrast, longer scavenging residence times (> 100 days) were calculated for metals enriched in organic phases, such as Cu.     

Arsenic and heavy metals in the bottom sediments of the Balaklava Bay (Black Sea)

We present the results of investigation of the contents of metals (As, Cr, Co, Cu, Ni, Pb, Zn, V, Sr, Mn, Ti, and Fe) in the bottom sediments of the Balaklava Bay (Black Sea) carried out in July 2005. It is shown that the pollution of the bottom sediments with metals has a polyelemental character. We establish the specific features of changes in the contents of the analyzed elements and localize the sources of their appearance in the ecosystem. On the basis of the results of evaluation of the intensity of technogenic action upon the marine medium, we determine a group of toxic elements (As, Cr, Cu, Pb, and Zn) accumulated in the bottom sediments of the bay in amounts significantly exceeding the background values typical of sediments of the Black Sea shelf. The comparative analysis of the degrees of pollution of the bay and some other coastal water areas with metals is performed.