Assessment of copper,cadmium and zinc remobilization in Mediterranean marine coastal sediments

The remobilization of copper, cadmium and zinc in sediments of three selected coastal microenvironments of the Aegean Sea (Eastern Mediterranean) is assessed. Various analytical methods and techniques were employed providing concentrations, profiles and forms of metals and organic matter in sediments and pore waters.     

The chemical composition and nickel,cobalt, copper,zinc and lead contents of Nanao Bay sediments

The contents of major and some of the minor elements, nickel, cobalt, copper, zinc and lead were studied on sediments collected from three inlets of Nanao Bay located at eastern side of Noto Peninsula. Little variation was found on the average contents of silicon, iron, titanium, aluminum, manganese, magnesium and potassium among the sediments of West, South and North Bays in Nanao Bay. Whereas significant difference was found on the contents of calcium, chlorine, sulfur and nitrogen among sediments of three bays.As to the minor elements, the average contents of nickel (20±5 ppm), cobalt (5±1 ppm), copper (18±5 ppm) and lead (17±8 ppm) are relatively low but zinc content is high in these sediments comparing with those of coastal deposit around Japan Island. From the results obtained here, it became clear that no environmental contamination of nickel, cobalt, copper and lead, and a little organic pollution were found in Nanao Bay sediments.     

Trace metal concentrations in brown seaweeds, Cardigan Bay, Wales

Concentrations of zinc, cadmium, copper, manganese, iron, cobalt, nickel and molybdenum are examined in brown algae, Fucus serratus and F. vesiculosus, from Cardigan Bay, Irish Sea, Great Britain. In both species a seasonal variation in metal content was observed. Zinc, cadmium, copper, iron nickel and cobalt concentrations were highest in the spring and lowest in the autumn, probably reflecting levels of metabolic activity and climatic factors. All the studied elements, except nickel, reached highest concentrations in harbour specimens from Aberystwyth and Aberaeron where rivers draining mineralized areas enter the sea. Outside harbours, marked regional variations were observed in most of the studied elements. Zinc values were highest in the Aberystwyth area while copper and manganese were highest in the northeast part of the bay.Trace-element concentrations varied among different species from the same locality and also varied according to position on the shore.Marine algae may be used to monitor coastal-water trace-metal concentrations, provided a careful sampling procedure is adopted.     

Distribution of silver, mercury, lead, copper and cadmium in central puget sound sediments

Distributions of five of the more toxic heavy metals have been assessed for Puget Sound sediments. Twenty-one Kasten cores were collected for the study. Analysis by Zeeman-corrected graphite-furnace atomic absorption spectroscopy has made possible the accurate and precise determination of silver and cadmium in Puget Sound sediment cores for the first time. Data show that Puget Sound is moderately impacted by anthropogenic Ag, Hg, Pb and Cu. No enrichment of Cd was found. The study also indicates that Puget Sound is quite well mixed with respect to the residence time of particle-bound metals. Toxic metal accumulation sites in the central Sound are determined almost exclusively by grain size, rather than proximity to sources. Estimates are made of trace metal fluxes to the sediments as a function of sediment type and areal distribution.     

Recent saltmarsh accretion and sea level fluctuations in the Dyfi Estuary,central Cardigan Bay,Wales, UK

Rates of saltmarsh accretion were determined for the Dyfi Estuary, central Cardigan Bay, Wales, using marker layers and X-ray radiographic laminae counts. A three-month study revealed the amount of sediment that had accumulated, totalling 2.5 mm, equivalent to 10.0 mm/yr. The saltmarsh sediment accretion rate estimated by laminae counts is 11.5 mm/yr. These data, compared with previous published data, indicate that the rate of sediment accretion has decreased since the 1920s. This is cautiously proposed as suggesting that the upward trend of relative sea level in the Dyfi Estuary may have been decreasing over the last 80 years.     

Potential for heavy metal (copper and zinc) removal from contaminated marine sediments using microalgae and light emitting diodes

The effects of monochromatic (blue, yellow and red LED) and mixed wavelengths (fluorescent lamp) on the adsorption and absorption of Cu and Zn by Phaeodactylum tricornutum, Nitzschia sp., Skeletonema sp., and Chlorella vulgaris were investigated. In addition, we confirmed the potential of microalgae for phytoremediation of these heavy metals from contaminated marine sediment by using microcosm experiments that incorporated LEDs and semipermeable membrane (SPM) tube containing microalgae. Among the four microalgae, C. vulgaris grown under red LED exhibited the highest Cu and Zn removal with values of 17.5 × 10^-15 g Cu/cell and 38.3 × 10^-15 g Zn/cell, respectively. Thus, C. vulgaris could be a useful species for phytoremediation. In the microcosm experiments with SPM containing C. vulgaris, the highest Cu and Zn removal from sediment and interstitial water showed under red LED. Therefore, phytoremediation using LED and SPM tube containing microalgae could be utilized as an eco-friendly technique for remediating contaminated marine sediment.     

Temporal and spatial distribution of dissolved copper, lead, zinc and cadmium in the Changjiang Estuary and its adjacent waters

Heavy metal concentrations were measured in the Changjiang Estuary and its adjacent waters. Results from a systematic survey in April 2002 to March 2003 indicate that the ranges of the concentrations of dissolved copper, lead, zinc and cadmium in the study waters are 1.01 - 6.86, 0. 10 - 0.39,3.17 - 9.12 and 0.011 - 0. 049 μg/dm^3 , respectively. Similar to zinc, the behavior of dissolved copper was essentially conservative, but high scatter has been observed for high salinity samples, which can be attributed to the decomposition or mineralization of organic matter by bacteria. Dissolved lead may have active behavior with an addition at high salinity. Overall concentrations of dissolved cadmium increase with salinity. The mean values of these dissolved metals calculated for the surface waters were higher than those for the middle and bottom ones. External inputs of dissolved heavy metals to the surface waters were the likely explanation for these higher values. The maximum seasonal average values of dissolved copper and zinc were found in summer, reflecting higher amounts of riverine input in this season. In contrast, the maximum seasonal average values of dissolved lead and copper were found in winter and the lowest ones in summer, respectively, which might be asso- ciated with a combination of low concentration with heterogeneous scavenging. Concentrations of these dissolved metals found for the Changjiang Estuary fall in the range observed for the other estuaries but are noticeably higher than those from uncontaminated rivers, except for cadmium. Compared with observations for the Changjiang Estuary in the last two decades, it is clear that the Changjiang estuarine waters has been contaminated with copper, lead, zinc and cadmium during China＇ s industrialization, but concentrations of them have decreased in the last few years.     

Concentrations of suspended matter and particulate cadmium,copper, lead and zinc in the Indian sector of the antarctic ocean

The concentrations of suspended matter and particulate Cd, Cu, Pb and Zn were determined for 36 samples collected at 6 stations in the Antarctic Ocean during December, 1970 and January, 1971 using membrane filters. The concentration of suspended matter was determined gravimetrically and trace metal levels were determined using anodic stripping voltammetry. For waters deeper than 100 m the concentration of suspended matter was < 100 μg l^?1. Concentrations up to 542 μg l^?1 were recorded between surface and 100 m. Individual concentrations of the metals were scattered with depth. Average concentrations of particulate metals were: Cd, 3.5 ng l^?1; Cu, 100 ng l^?1; Pb, 35 ng l^?1; and Zn, 230 ng ;l^?1 These measurements represent non-steady state conditions of early Antarctic summer as the ice pack disintegrates and biological activity increases.     

Chemical fractionation of zinc versus cadmium among other metals nickel, copper and lead in the northern North Sea

Concentrations of dissolved Ni, Cu, Zn, Cd and Pb were measured in water samples collected during a cruise with R.V Pelagia (29-6/14-7-1993) in the northern North Sea and N.E. Atlantic Ocean. At least six depths (0–90 m) were sampled with modified Go-Flo samplers from a rubber zodiac. In the study area, the first 25 m were well mixed and stratification occurred below this depth. The local bloom of Emiliania huxleyi hardly affected the trace metals concentration, except for some removal of Cd as seen from its correlation with nitrate. The mean dissolved concentrations were for Ni (3.66 nM), Cu (1.61 nM), Zn (4.5 nM), Cd (48 pM) and Pb (108 pM). These concentrations are among the lowest reported for the North Sea and are of similar magnitude to those found in the eastern North Atlantic at the same latitude. Zn was the only exception with values 10 times higher compared to those in the Atlantic Ocean, suggesting external inputs, mainly atmospheric and possibly from surrounding land masses. The observed ratio Zn:Cd in the North Sea and estuaries is in between the high ratio 600–900 for continental sources and the low ratio 5–10 for oceanic waters. Latter low ratio is consistent with the 21-fold stronger inorganic complexation of Cd in seawater which, in combination with the preferential biological uptake of Zn, may lead to the observed about hundredfold fractionation of Zn versus Cd in the marine system. Other processes may play a role but would need further investigation. The dissolved Pb values tend to be lower than found before in the North Sea, indicating decreasing inventories due to reduced anthropogenic emissions.     

The determination of weakly and strongly bound copper,lead and cadmium in oslofjord samples

Weakly and strongly bound copper, lead and cadmium have been determined in the dissolved and particulate fractions of water samples from Oslofjord. The differentiation was made possible by using different sequences of filtration, acidification and digestion. The quantitative measurements were done by differential pulse anodic stripping voltammetry. Lead was found to be associated mostly with particulate matter, while cadmium was present only in the dissolved fraction. A strong digestion was needed for the determination of total metal. The advantage of pretreating sample bottles and filters with a conditioning solution is illustrated.     

Analytical fractionation of dissolved copper, lead and cadmium in coastal seawater

The speciation of dissolved Cu, Pb and Cd in twelve seawater samples from the Inner Oslofjord, Norway, has been examined by an operational scheme which involves ultrafiltration followed by determination of labile, acid soluble and total Cu, Pb and Cd by differential pulse anodic stripping voltammetry (DPASV). The techniques employed are discussed and evaluated. It was found that Cd was present entirely in low molecular weight (LMW) labile species; Pb was mainly in non-labile LMW species, with half of the total Pb probably occurring in LMW organo-metallic compounds; Cu distribution was irregular, with extensive organic and colloidal association.     

Sulfide control of cadmium and copper concentrations in anaerobic estuarine sediments

Equilibrium concentrations of the toxic trace metals copper and cadmium were calculated for the physico-chemical conditions characterizing pore waters of anaerobic estuarine sediments using available thermodynamic data and assuming simple sulfide minerals control solubilities. Polysulfide complexes are responsible for the solubility of copper in the cuprous (Cu(I)) oxidation state. Predicated copper concentrations, assuming covellite (CuS) is the controlling solid phase, are in reasonable agreement with copper analyses in a wide range of sulfidic waters and sediment pore waters. In the absence of thermodynamic data, no account could be taken of possible polysulfide complexes of cadmium. However, bisulfide complexes appear to account satisfactorily for observed solubilities assuming the existence of greenockite (CdS) as the controlling solid phase. Anaerobic estuarine sediments may act as a sink for copper and cadmium in the common situation in which free sulfide concentrations are controlled by the coexistence of iron sulfide and iron oxide minerals. However, where free sulfides reach high concentrations of 10^?3 M or more, the concomitant increase in concentration of bisulfide and polysulfide complexes may result in the sediments acting as a source of copper and cadmium.     

Determination of the chemical forms of dissolved cadmium, lead and copper in seawater

The chemical forms of Cd, Pb and Cu in seawater have been examined using a novel scheme which permits the quantification of up to seven different species of one metal. The concentration of each species was calculated from measurements using anodic stripping voltammetry of labile and total metal in samples which were (a) untreated, (b) UV irradiated, (c) passed through a chelating resin column, and (d) UV irradiated then passed through a chelating resin column. In the sample studied, the major proportion of Cd, Pb and Cu was found to be associated with organic and inorganic colloidal species. Less than half of the bound Pb and Cu was readily exchangeable with added ²¹⁰Pb and ⁶⁴Cu.     

Determination of cadmium,lead and copper in interstitial water by anodic stripping voltammetry

This paper gives the results of determination of cadmium, lead and copper in interstitial water of the coastal sediment, Seto Inland Sea, Japan by using anodic stripping voltammetry. An aliquot of 4–5 ml interstitial water separated from 30–70 ml of sediment is used for the simultaneous determination of ionic cadmium, lead and copper. No significant differences were observed on the content of trace metals between surface water and interstitial water of the top of the sediment.     

Biotransference and biomagnification of selenium copper,cadmium, zinc,arsenic and lead in a temperate seagrass ecosystem from Lake Macquarie Estuary,NSW, Australia

In this study the biotransference of selenium copper, cadmium, zinc, arsenic and lead was measured in a contaminated seagrass ecosystem in Lake Macquarie, NSW, Australia, to determine if biomagnification of these trace metals is occurring and if they reach concentrations that pose a threat to the resident organisms or human consumers. Selenium was found to biomagnify, exceeding maximum permitted concentrations for human consumption within carnivorous fish tissue, the highest trophic level examined. Selenium concentrations measured within carnivorous fish were also above those shown to elicit sub-lethal effects in freshwater fish. As comparisons are made to selenium concentrations known to effect freshwater fish, inferences must be made with caution. There was no evidence of copper, cadmium, zinc or lead biomagnification within the food web examined. Copper, cadmium, zinc and lead concentrations were below concentrations shown to elicit adverse responses in biota. Copper concentrations within crustaceans M. bennettae and P. palagicus were found to exceed maximum permitted concentrations for human consumption. It is likely that copper concentrations within these species were accumulated due to the essential nature of this trace metal for many species of molluscs and crustaceans. Arsenic showed some evidence of biomagnification. Total arsenic concentrations are similar to those found in other uncontaminated marine ecosystems, thus arsenic concentrations are unlikely to cause adverse effects to aquatic organisms. Inorganic arsenic concentrations are below maximum permitted concentrations for human consumption.     

Concentrations of cadmium,copper, lead and zinc in surface waters of the Northwest Atlantic Ocean — A comparison of Go-flo and teflon water samplers

The concentrations of cadmium, copper, lead and zinc were measured at two locations in surface waters of the western North Atlantic. Samples were collected upstream of the research vessel in 1-1 teflon bottles, and in a 30-1 teflon-coated Go-flo bottle. Surface mixed-layer samples were also collected at each location by ship cast using this same Go-flo sampler. A comparison of the three sampling modes shows that all the samples taken with the Go-flo sampler possessed much higher concentrations of zinc (7–10-fold) and lead (2–3-fold) than those collected directly in teflon bottles. No apparent differences were noted at each station in the concentrations of either copper or cadmium among the samples collected by the three different procedures. The measured values for copper and cadmium in these waters are in good agreement with recent reports for the western North Atlantic.     

Chemical forms of copper and zinc in the surficial sediments of Borollos Lake, Egypt

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东海陆扰海域铜、铅、锌、镉重金属排海通量及海洋环境容量估算

汇总并分析了20世纪80年代初以来东海陆扰海域重金属排海通量年变化规律及主要来源,应用多介质海洋环境中重金属迁移-转化模型,估算了东海陆扰海域重金属海洋环境容量。20世纪80年代初以来,东海陆扰海域铜、铅、锌、镉排海总量整体上呈不对称的倒"U"形变化趋势,基本符合"环境库兹涅茨曲线",20世纪90年代达到最大值,当前排海总量仍高于20世纪80年代初期的水平。东海陆扰海域铜、铅、锌、镉污染物主要来源于以河流为主的陆源排放,其中88.0%左右来源于河流排放,7.5%左右来源于排污口,只有4.5%左右来源于大气沉降。长江流域排海通量占东海陆扰海域排海总量的比例最大,平均为92.4%左右,钱塘江流域平均只有3.9%左右,闽江流域平均只有3.7%左右。东海陆扰海域铜、铅、锌、镉污染物海洋环境容量分别约为17.0,4.7,113.1,0.71 kt/a。当前铅、锌、镉污染物排海总量没有超过东海陆扰海域海洋环境容量,但铜的排海总量超过其海洋环境容量大约8%。     

Cadmium,cobalt, copper,iron, lead,nickel and zinc in Indian Ocean water

Results of trace-metal analyses of water samples obtained during a cruise with the Soviet R.V. “Akademik Kurchatov” in the Indian Ocean are presented. The determinations were performed on board with atomic absorption spectrophotometry after a two-stage dithiocarbamate—Freon extraction procedure. Trace-metal concentrations found are in the same range as those found recently for similar open-ocean areas by other workers. The values for lead and zinc are probably high due to contamination. Vertical profiles indicate biogenic processes as controlling factors for the increase of cadmium, copper and nickel concentrations with depth. Iron shows an irregular depth distribution as a result of large random variations in concentration.