Accumulative phases for heavy metals in limnic sediments

Data from mechanical concentrates of recent sediments indicate that clay minerals, clay-rich aggregates and heavy minerals are the major carriers of heavy metals in detrital sediment fractions. Hydrous Fe/Mn oxides and carbonates and sulfides, in their specific environments, are the predominant accumulative phases for heavy metals in autochthonous fractions. Sequential chemical extraction techniques permit the estimation of characteristic heavy metal bonding forms: exchangeable metal cations, easily reducible, moderately reducible, organic and residual metal fractions, whereby both diagenetic processes and the potential availability of toxic compounds can be studied. The data from lakes affected by acid precipitation indicate that zinc, cobalt and nickel are mainly released from the easily reducible sediment fractions and cadmium from organic phases. In contrast at pH 4.4, neither lead nor copper seem to be remobilized to any significant extent. Immobilization by carbonate precipitation seems to provide an effective mechanism for the reduction of dissolved inputs 9f metals such as zinc and cadmium in pH-buffered, hard water systems.     

Heavy metals (Cd, Pb, Zn, Ni, Cu and Cr(III)) removal from water in Malaysia: post treatment by high quality limestone

This paper presents the results of research on heavy metals removal from water by filtration using low cost coarse media which could be used as an alternative approach to remove heavy metals from water or selected wastewater. A series of batch studies were conducted using different particle media (particle size 2.36-4.75 mm) shaken with different heavy metal solutions at various pH values to see the removal behaviour for each metal. Each solution of cadmium (Cd), lead (Pb), zinc (Zn), nickel (Ni), copper (Cu) and chromium (Cr(III)) with a concentration of 2 mg/L was shaken with the media. At a final pH of 8.5, limestone has significantly removed more than 90% of most metals followed by 80% and 65% removals using crushed bricks and gravel, respectively. The removal by aeration and settlement methods without solid media was less than 30%. Results indicated that the removal of heavy metals was influenced by the media and not directly by the pH. Investigations on the removal behaviour of these metals indicated that rough solid media with the presence of carbonate were beneficial for the removal process. Adsorption and precipitation as metals oxide and probably as metals carbonate were among the two mechanisms that contributed to the removal of metals from solution.     

Advances in biotreatment of acid mine drainage and biorecovery of metals: 1. Metal precipitation for recovery and recycle

Acid mine drainage (AMD), an acidic metal-bearingwastewater, poses a severe pollution problem attributedto post mining activities. The metals usuallyencountered in AMD and considered of concern for riskassessment are arsenic, cadmium, iron, lead, manganese,zinc, copper and sulfate. The pollution generated byabandoned mining activities in the area of Butte, Montanahas resulted in the designation of the Silver Bow Creek–ButteArea as the largest Superfund (National Priorities List) sitein the U.S. This paper reports the results of bench-scalestudies conducted to develop a resource recovery basedremediation process for the clean up of the Berkeley Pit.The process utilizes selective, sequential precipitation (SSP)of metals as hydroxides and sulfides, such as copper, zinc,aluminum, iron and manganese, from the Berkeley Pit AMDfor their removal from the water in a form suitable foradditional processing into marketable precipitates and pigments.The metal biorecovery and recycle process is based on completeseparation of the biological sulfate reduction step and themetal precipitation step. Hydrogen sulfide produced in the SRBbioreactor systems is used in the precipitation step to forminsoluble metal sulfides. The average metal recoveries usingthe SSP process were as follows: aluminum (as hydroxide) 99.8%,cadmium (as sulfide) 99.7%, cobalt (as sulfide) 99.1% copper(as sulfide) 99.8%, ferrous iron (sulfide) 97.1%, manganese(as sulfide) 87.4%, nickel (as sulfide) 47.8%, and zinc (as sulfide)100%. The average precipitate purity for metals, copper sulfide,ferric hydroxide, zinc sulfide, aluminum hydroxide and manganesesulfide were: 92.4, 81.5, 97.8, 95.6 , 92.1 and 75.0%, respectively.The final produced water contained only calcium and magnesiumand both sulfate and sulfide concentrations were below usablewater limits. Water quality of this agriculturally usable watermet the EPA's gold standard criterion.     

The ultrastructural localisation of cadmium.

A modified technique for the ultrastructural localisation of heavy metals is described in this paper. The method involves precipitation of heavy metals as sulphides in the tissue by using (NH4)2 S after brief fixation in glutaraldehyde. The sulphides are, in the presence of a physical developer, then used to catalyse the reduction of silver ions into visible molecular silver. This latter step of physical development has been normally carried out after embedding and sectioning. However, when we followed this method we found that the dark metal sulphide was lost from the tissue during the embedding in epoxy resin. Hence the method was unsuitable for our proposed experiment on the ultrastructural localisation of cadmium. We subsequently modified the technique primarily by treating very thin tissue slices with the developer before dehydration and embedding, thus eliminating any problem from sulphide loss. This modified technique was used to investigate the ultrastructural localisation of cadmium in the kidneys of mice which had been exposed to 50 ppm cadmium in their drinking water for up to eight months. The molecular silver was found to be located mainly in the proximal tubule cells, either as dense clumps in apical vesicles and lysosomes or diffuse grains throughout the cytoplasm of the cells particularly in the basal region. We interpret these results as indicating that cadmium is found in the apical vesicles, lysosomes and cytoplasm of proximal tubule cells.     

EPR studies of cytochrome aa3 from Sulfolobus acidocaldarius. Evidence for a binuclear center in archaebacterial terminal oxidase.

The purified cytochrome aa3-type oxidase from Sulfolobus acidocaldarius (DSM 639) consists of a single subunit, containing one low-spin and one high-spin A-type hemes and copper [Anemüller, S. and Sch?fer, G. (1990) Eur. J. Biochem. 191, 297-305]. The enzyme metal centers were investigated by electron paramagnetic resonance spectroscopy (EPR), coupled to redox potentiometry. The low-spin heme EPR signal has the following g-values: gz = 3.02, gy = 2.23 and gx = 1.45 and the high-spin heme exhibits an almost axial spectrum (gy = 6.03 and gx = 5.97, E/D < 0.002). In the enzyme as isolated the low-spin resonance corresponds to 95 +/- 10% of the enzyme concentration, while the high-spin signal accounts for only 40 +/- 5%. However, taking into account the redox potential dependence of the high-spin heme signal, this value also rises to 95 +/- 10%. The high-spin heme signal of the Sulfolobus enzyme shows spectral characteristics distinct from those of the Paracoccus denitrificans one: it shows a smaller rhombicity (gy = 6.1 and gx = 5.9, E/D = 0.004 for the P. denitrificans enzyme) and it is easier to saturate, having a half saturation power of 148 mW compared to 360 mW for the P. denitrificans protein, both at 10 K. The EPR spectrum of an extensively dialyzed and active enzyme sample containing only one copper atom/enzyme molecule does not display CuA-like resonances, indicating that this enzyme contains only a CUB-type center. The EPR-redox titration of the high-spin heme signal, which is assigned to cytochrome a3, gives a bell shaped curve, which was simulated by a non-interactive two step redox process, with reduction potentials of 200 +/- 10 mV and 370 +/- 10 mV at pH = 7.4. The decrease of the signal amplitude at high redox potentials is proposed to be due to oxidation of a CUB(I) center, which in the CUB(II) state is tightly spin-coupled to the heme a3 center. The reduction potential of the low-spin resonance was determined using the same model as 305 +/- 10 mV at pH = 7.4 by EPR redox titration. Addition of azide to the enzyme affects only the high-spin heme signal, consistent with the assignment of this resonance to heme a3. The results are discussed in the context of the redox center composition of quinol and cytochrome c oxidases.     

The ultrastructural localisation of cadmium

Summary A modified technique for the ultrastructural localisation of heavy metals is described in this paper. The method involves precipitation of heavy metals as sulphides in the tissue by using (NH₄)₂S after brief fixation in glutaraldehyde. The sulphides are, in the presence of a physical developer, then used to catalyse the reduction of silver ions into visible molecular silver. This latter step of physical development has been normally carried out after embedding and sectioning. However, when we followed this method we found that the dark metal sulphide was lost from the tissue during the embedding in epoxy resin. Hence the method was unsuitable for our porposed experiment on the ultrastructural localisation of cadmium. We subsequently modified the technique primarily by treating very thin tissue slices with the developer before dehydration and embedding, thus eliminating any problem from sulphide loss. This modified technique was used to investigate the ultrastructural localisation of cadmium in the kidneys of mice which had been exposed to 50 ppm cadmium in their drinking water for up to eight months. The molecular silver was found to be located mainly in the proximal tubule cells, either as dense clumps in apical vesicles and lysosomes or diffuse grains throughout the cytoplasm of the cells particularly in the basal region. We interpret these results as indicating that cadmium is found in the apical vesicles, lysosomes and cytoplasm of proximal tubule cells.     

Immobilization of cadmium in soil by microbially induced carbonate precipitation with Exiguobacterium undae at low temperature

Microbially induced carbonate precipitation (MICP) is an advanced biological treatment technology to immobilize heavy metals in form of carbonate salts. In this MICP study, ureolytic Exiguobacterium undae was employed for immobilization of cadmium in contaminated soil at low temperature (10 °C). The sequential extraction test revealed conversion of more than 90% of cadmium in the tested soil from the soluble-exchangeable fraction to carbonate-bound fraction in 14 days of treatment. The cadmium may be precipitated in a separate CdCO₃ phase or be co-precipitated in calcite crystals. Activities of urease and dehydrogenase were enhanced during MICP, which were not affected by the testing temperatures. MICP with E. undae is a biological approach that may be worth investigating further to immobilize cadmium in soils of cold regimes.     

Geochemical, Microbiological, and Geophysical Assessments of Anaerobic Immobilization of Heavy Metals

Bioremediation methods that precipitate contaminants in situ as solid (mineral) phases can provide cost-effective options for removing dissolved metals in contaminated groundwater. The current field-scale experiments demonstrate that indigenous bacteria can be stimulated to remove metals by injection of electron-donating substrates and nutrients into a contaminated aquifer. Groundwater at the investigation site is aerobic and contains high levels of lead, cadmium, zinc, copper, and sulfuric acid (pH = 3.1) derived from a car-battery recycling plant. During the experiments, lead, cadmium, zinc, and copper were almost completely removed by precipitation of solid sulfide phases, as pH increased from 3 to ∼ 5 and Eh dropped from +400 mV to -150 mV. X-ray and transmission electron microscopy (TEM) analyses of filtered material from the treated groundwater indicated the presence of newly formed nanocrystalline metal sulfides. Genetic sequencing indicated that the principal species of sulfate-reducing bacteria involved in the bioremediation process was Desulfosporosinus orientis. Geochemical modeling shows that oxidation of added substrates and subsequent bacterial sulfate reduction produced desired geochemical conditions (i.e., decreasing Eh and increasing pH) for the precipitation and sorption of metal sulfides. Geophysical survey results suggest that bioremediation lowers electrical conductance of groundwater and possibly increases the magnetic susceptibility of porous media. This study demonstrates that integrated geochemical, geophysical, and microbiological analyses, combined with theoretical modeling, can successfully track and predict the progress of subsurface bioremediation.     

Selective removal of transition metals from acidic mine waters by novel consortia of acidophilic sulfidogenic bacteria

Two continuous‐flow bench‐scale bioreactor systems populated by mixed communities of acidophilic sulfate‐reducing bacteria were constructed and tested for their abilities to promote the selective precipitation of transition metals (as sulfides) present in synthetic mine waters, using glycerol as electron donor. The objective with the first system (selective precipitation of copper from acidic mine water containing a variety of soluble metals) was achieved by maintaining a bioreactor pH of ～2.2–2.5. The second system was fed with acidic (pH 2.5) synthetic mine water containing 3 mM of both zinc and ferrous iron, and varying concentrations (0.5–30 mM) of aluminium. Selective precipitation of zinc sulfide was possible by operating the bioreactor at pH 4.0 and supplementing the synthetic mine water with 4 mM glycerol. Analysis of the microbial populations in the bioreactors showed that they changed with varying operational parameters, and novel acidophilic bacteria (including one sulfidogen) were isolated from the bioreactors. The acidophilic sulfidogenic bioreactors provided ‘proof of principle’ that segregation of metals present in mine waters is possible using simple online systems within which controlled pH conditions are maintained. The modular units are versatile and robust, and involve minimum engineering complexity.     

Quantification of Tinto River sediment microbial communities: importance of sulfate-reducing bacteria and their role in attenuating acid mine drainage

Tinto River (Huelva, Spain) is a natural acidic rock drainage (ARD) environment produced by the bio-oxidation of metallic sulfides from the Iberian Pyritic Belt. This study quantified the abundance of diverse microbial populations inhabiting ARD-related sediments from two physicochemically contrasting sampling sites (SN and JL dams). Depth profiles of total cell numbers differed greatly between the two sites yet were consistent in decreasing sharply at greater depths. Although catalyzed reporter deposition fluorescence in situ hybridization with domain-specific probes showed that Bacteria (>98%) dominated over Archaea (<2%) at both sites, important differences were detected at the class and genus levels, reflecting differences in pH, redox potential, and heavy metal concentrations. At SN, where the pH and redox potential are similar to that of the water column (pH 2.5 and +400 mV), the most abundant organisms were identified as iron-reducing bacteria: Acidithiobacillus spp. and Acidiphilium spp., probably related to the higher iron solubility at low pH. At the JL dam, characterized by a banded sediment with higher pH (4.2 to 6.2), more reducing redox potential (-210 mV to 50 mV), and a lower solubility of iron, members of sulfate-reducing genera Syntrophobacter, Desulfosporosinus, and Desulfurella were dominant. The latter was quantified with a newly designed CARD-FISH probe. In layers where sulfate-reducing bacteria were abundant, pH was higher and redox potential and levels of dissolved metals and iron were lower. These results suggest that the attenuation of ARD characteristics is biologically driven by sulfate reducers and the consequent precipitation of metals and iron as sulfides.     

Accumulation of metal-binding peptides in fission yeast requires hmt2+

The fission yeast Schizosaccharomyces pombe detoxifies cadmium by synthesizing phytochelatins, peptides of the structure (gamma-GluCys)nGly, which bind cadmium and mediate its sequestration into the vacuole. The fission yeast protein HMT2, a mitochondrial enzyme that can oxidize sulphide, appears to be essential for tolerance to multiple forms of stress, including exposure to cadmium. We found that the hmt2- mutant is unable to accumulate normal levels of phytochelatins in response to cadmium, although the cells possess a phytochelatin synthase that is active in vitro. Radioactive pulse-chase experiments demonstrated that the defect lies in two steps: the synthesis of phytochelations and the upregulation of glutathione production. Phytochelatins, once formed, are stable. hmt2- cells accumulate high levels of sulphide and, when exposed to cadmium, display bright fluorescent bodies consistent with cadmium sulphide. We propose that the precipitation of free cadmium blocks phytochelatin synthesis in vivo, by preventing upregulation of glutathione production and formation of the cadmium-glutathione thiolate required as a substrate by phytochelatin synthase. Thus, although sulphide is required for phytochelatin-mediated metal tolerance, aberrantly high sulphide levels can inhibit this pathway. Precise regulation of sulphur metabolism, mediated in part by HMT2, is essential for metal tolerance in fission yeast.     

Effects of copper and cadmium on heavy metal polluted waterbody restoration by duckweed (Lemna minor).

Aquatic plants have been identified as a potentially useful group for accumulating and bioconcentrating heavy metals. In the study, we investigated changes in the contents of soluble protein and photosynthetic pigments as well as the activity of antioxidant enzymes caused by copper sulfate and cadmium dichloride, respectively in duckweed (Lemna minor) during concentration-dependent exposure (0.05-20 mg l(-1)) to metal salt. The results demonstrated that exposure to high concentration heavy metals (Cu>10 mg l(-1), Cd>0.5 mg l(-1)) could result the disintegration of antioxidant system in duckweed. Also, the significant decrease of contents of soluble protein and photosynthetic pigments was observed to high-level metal stress. Additionally, cadmium was found to be more toxic than copper on plants. The outcome of this study corroborate that Lemna minor is a suitable candidate for the phytoremediation of low-level copper and cadmium contaminated waterbody.     

A selenomethionine-containing azurin from an auxotroph of Pseudomonas aeruginosa

The production and spectroscopic properties of an L-selenomethionine-containing homolog of Pseudomonas aeruginosa azurin are described. The amino acid substitution was carried out by developing an L-methionine-dependent bacterial strain from a fully functional ATCC culture. Uptake studies monitored using L-[75Se]methionine indicated that L-selenomethionine was incorporated into the protein synthetic pathway of Pseudomonas bacteria in a manner analogous to L-methionine. Several batches of bacteria were grown, and one sample of isolated and purified selenoazurin (azurin in which methionine was substituted by selenomethionine) was found (by neutron activation analysis) to contain 5.2 +/- 0.8 seleniums/copper. Correspondingly, a residual 0.35 methionines, relative to 6.0 in the native protein, were found by amino acid analysis in this azurin sample. The redox potential and extinction coefficient of this selenoazurin were found to be 333 +/- 1 mV (pH 7.0, I = 0.22) and 5855 +/- 160 M-1 cm-1 at 626 +/- 1 nm, respectively. Visible electronic, CD, and EPR spectra are reported and Gaussian curve fitting to the former spectrum allowed assignment of the selenomethionine Se----Cu(II) transition to a band found at 18034 cm-1, based upon an observed 450 cm-1 shift to the red from the analogous band position in the native protein. The data are consistent with a relatively more covalent copper site stabilizing the reduced, Cu(I), form in the selenoprotein. A role for the methionine as a modulator of the blue copper site redox potential by metal----ligand back bonding from Cu(I) is discussed in terms of a ligand sphere which limits the valence change at copper to much less than 1 during a redox cycle.     

Zinc and copper modulate differentially the P2X4 receptor

The rat ATP P2X4 receptor was expressed in Xenopus laevis oocytes to assess the effect of zinc and copper as possible regulators of purinergic mechanisms. ATP applied for 20 s evoked an inward cationic current with a median effective concentration (EC50) of 21.4+/-2.8 microM and a Hill coefficient (nH) of 1.5+/-0.1. Coapplication of ATP plus 10 microM zinc displaced leftward, in a parallel fashion, the ATP concentration-response curve, reducing the EC50 to 8.4+/-1.8 microM (p < 0.01) without altering the receptor nH. The zinc potentiation was fast in onset, easily reversible, and voltage-independent and did not require metal preexposure. The zinc EC50 was 2-5 microM, with a bell-shaped curve. At concentrations of 100-300 microM, zinc produced less potentiation, and at 1 mM, it inhibited 50% the ATP current. The effect of zinc was mimicked by cadmium. In contrast, copper inhibited the ATP-evoked currents in a time- and concentration-dependent fashion, reducing the maximal current (Imax) without altering the EC50. The copper-induced inhibition was slow in onset, slowly reversible, and voltage-independent. Whereas coapplication of 300 microM copper plus ATP reduced Imax to 36.2+/-5%, the coapplication of, or 60-s preexposure by, 10 microM copper reduced Imax to 79+/-9.2% (p < 0.05) and 39.6+/-8.7% (p < 0.01), respectively. The inhibition was noncompetitive in nature and mimicked by mercury. Cobalt, barium, and manganese did not modify significantly the ATP-evoked current, demonstrating metal specificity. The simultaneous 1-min preapplication of both metals revealed that the 10 microM zinc-induced potentiation was obliterated by 10 microM copper, whereas 30 microM copper not only reduced the potentiation, but inhibited the ATP response. Following coapplication of both metals for 20 s with ATP, at least 100 microM copper was required to counteract the 10 microM zinc-induced potentiation. The simultaneous preincubation with both metals provided evidence for a noncompetitive interaction. We hypothesize the existence of metal binding site(s), which are most likely localized in the extracellular domain of the P2X4 receptor structure. These sites are selective and accessible to extracellular metal applications and bind micromolar concentrations of metals. The present results are compatible with the working hypothesis that trace metals, such as copper and zinc, are physiological modulators of the P2X4 receptor. The modulation of brain purinergic transmission by physiologically and toxicologically relevant trace metal cations is highlighted.     

Heavy metals removal by the microalga Scenedesmus incrassatulus in continuous cultures

The microalga Scenedesmus incrassatulus was grown under continuous regime in the presence of chromium(VI), cadmium(II) and copper(II), as single metal species and as mixtures of two or three metals, in a laboratory scale system. We used an artificial wastewater with low free ion activities (as determined by MINEQL+) due to the presence of EDTA (a strong chelating agent) but with total concentrations not suitable for acceptable environments. Chromium(VI) and cadmium(II) had positive interaction that increased the removal percentages of both these metals; we could not, however, detect any interaction with copper(II). S. incrassatulus was able to remove all the tested metals to some extent (25-78%), but bivalent metals were not removed as efficiently as reported in batch cultures, probably due to the high pH values there recorded. Chromium(VI) was more efficiently removed in continuous cultures than in batch culture, because the uptake of chromate could be favored by actively growing algae.     

Effect of pH and organic matter on the toxicity of heavy metals to growth of some fungi

Increasing the pH from 5 to 9 decreased the toxicity of mercuric chloride, zinc sulfate, lead nitrate, copper sulfate and nickel chloride toward the growth ofAspergillus flavus, Penicillium chrysogenum, Cunninghamella echinulata, Myrothecium verrucaria andPhoma humicola. On the other hand, the toxicity of cadmium chloride was increased by the increasing pH. Also increasing the concentration of organic matter (peptone and yeast extract) from 0.5 to 1.5% induced a significant reduction in the toxicity of all heavy metals toward the growth of all test fungi.     

The Rieske FeS center from the gram-positive bacterium PS3 and its interaction with the menaquinone pool studied by EPR.

The Rieske 2Fe2S center from Bacillus PS3, a Gram-positive thermophilic eubacterium, has been studied by EPR spectroscopy. Its redox midpoint potential at pH 7.0 was determined to be +165 +/- 10 mV and was found to decrease with an apparent slope of -80 mV/pH unit above pH 7.9. The Qo-site inhibitor stigmatellin induced spectral changes analogous to those reported for Rieske centers from mitochondria and chloroplasts. The redox midpoint potential of the PS3 Rieske cluster was not affected by stigmatellin. The orientation of the g tensor was similar to other Rieske centers (gz and gy are oriented parallel, gx is oriented perpendicular to the membrane plane). The shape of the EPR spectrum of the Rieske cluster from PS3 changed as a function of the redox state of the menaquinone (MK) pool. This permitted the redox midpoint potential of the MK pool to be determined in the membrane. Values of -60 +/- 20 mV at pH 7.0 and of -130 +/- 20 mV at pH 8.0 were obtained. The results are compared with already published data from other Rieske centers. It is proposed that all Rieske centers that function in electron transport chains using MK as pool quinone show common features that distinguish them from Rieske centers operating in ubiquinone- or plastoquinone-based electron transfer chains.     

Plant responses to abiotic stresses: heavy metal-induced oxidative stress and protection by mycorrhization

The aim of this review is to assess the mode of action and role of antioxidants as protection from heavy metal stress in roots, mycorrhizal fungi and mycorrhizae. Based on their chemical and physical properties three different molecular mechanisms of heavy metal toxicity can be distinguished: (a) production of reactive oxygen species by autoxidation and Fenton reaction; this reaction is typical for transition metals such as iron or copper, (b) blocking of essential functional groups in biomolecules, this reaction has mainly been reported for non-redox-reactive heavy metals such as cadmium and mercury, (c) displacement of essential metal ions from biomolecules; the latter reaction occurs with different kinds of heavy metals. Transition metals cause oxidative injury in plant tissue, but a literature survey did not provide evidence that this stress could be alleviated by increased levels of antioxidative systems. The reason may be that transition metals initiate hydroxyl radical production, which can not be controlled by antioxidants. Exposure of plants to non-redox reactive metals also resulted in oxidative stress as indicated by lipid peroxidation, H(2)O(2) accumulation, and an oxidative burst. Cadmium and some other metals caused a transient depletion of GSH and an inhibition of antioxidative enzymes, especially of glutathione reductase. Assessment of antioxidative capacities by metabolic modelling suggested that the reported diminution of antioxidants was sufficient to cause H(2)O(2) accumulation. The depletion of GSH is apparently a critical step in cadmium sensitivity since plants with improved capacities for GSH synthesis displayed higher Cd tolerance. Available data suggest that cadmium, when not detoxified rapidly enough, may trigger, via the disturbance of the redox control of the cell, a sequence of reactions leading to growth inhibition, stimulation of secondary metabolism, lignification, and finally cell death. This view is in contrast to the idea that cadmium results in unspecific necrosis. Plants in certain mycorrhizal associations are less sensitive to cadmium stress than non-mycorrhizal plants. Data about antioxidative systems in mycorrhizal fungi in pure culture and in symbiosis are scarce. The present results indicate that mycorrhization stimulated the phenolic defence system in the Paxillus-Pinus mycorrhizal symbiosis. Cadmium-induced changes in mycorrhizal roots were absent or smaller than those in non-mycorrhizal roots. These observations suggest that although changes in rhizospheric conditions were perceived by the root part of the symbiosis, the typical Cd-induced stress responses of phenolics were buffered. It is not known whether mycorrhization protected roots from Cd-induced injury by preventing access of cadmium to sensitive extra- or intracellular sites, or by excreted or intrinsic metal-chelators, or by other defence systems. It is possible that mycorrhizal fungi provide protection via GSH since higher concentrations of this thiol were found in pure cultures of the fungi than in bare roots. The development of stress-tolerant plant-mycorrhizal associations may be a promising new strategy for phytoremediation and soil amelioration measures.     

The oxidizing power of the glutathione thiyl radical as measured by its electrode potential at physiological pH

The oxidizing power of the thiyl radical (GS*) produced on oxidation of glutathione (GSH) was determined as the mid-point electrode potential (reduction potential) of the one-electron couple E(m)(GS*,H+/GSH) in water, as a function of pH over the physiological range. The method involved measuring the equilibrium constants for electron-transfer equilibria with aniline or phenothiazine redox indicators of known electrode potential. Thiyl and indicator radicals were generated in microseconds by pulse radiolysis, and the position of equilibrium measured by fast kinetic spectrophotometry. The electrode potential E(m)(GS*,H+/GSH) showed the expected decrease by approximately 0.06 V/pH as pH was increased from approximately 6 to 8, reflecting thiol/thiolate dissociation and yielding a value of the reduction potential of GS*=0.92+/-0.03 V at pH 7.4. An apparently almost invariant potential between pH approximately 3 and 6, with potentials significantly lower than expected, is ascribed at least in part to errors arising from radical decay during the approach to the redox equilibrium and slow electron transfer of thiol compared to thiolate.     

Removal characteristics of metal ions using degreased coffee beans: adsorption equilibrium of cadmium(II)

The feasibility of using coffee beans after being dripped and degreased (DCB) as an adsorbent for base metals such as copper(II), zinc(II), lead(II), iron(III) and cadmium(II) were examined. The compositions of the DCB were characterized by Fourier transform infrared spectroscopy, scanning electronic micrograph and fluorescent X-ray. It was found that DCB contain sulfur and calcium from the analysis using fluorescent X-ray. The plant cell wall in DCB has the porous structure from the scanning electron microscopy (SEM) analysis, and the specific surface area was determined to be 1.2 m2/g using the specific surface area analyzer. Batch adsorption experiments on DCB were carried out at various pHs in order to elucidate the selectivity of metal ions. All metals were adsorbed at low pH region (3.0-5.0). Of particular interest was the adsorption characteristics of cadmium(II) on DCB. The adsorption isotherm for cadmium(II) at pH 8 fitted with a Langmuir equation to yield an adsorption equilibrium constant of 55.2 mmol dm(-3) and an adsorption capacity of 5.98 x 10(-2) mmol g(-1). The desorption of cadmium(II) was easily achieved over 90% by a single batchwise treatment with an aqueous solution of hydrochloric acid or nitric acid at more than 0.01 mol dm(-3). These results suggested that DCB behaves as a cation exchanger.