Bioaccumulation of nickel by microbially-enhanced chemisorption into polycrystalline hydrogen uranyl phosphate

Summary Ni²⁺ was removed quantitatively from aqueous solution into a microbially-created crystalline deposit of hydrogen uranyl phosphate (HUP). The mechanism of Ni²⁺ removal is an ion-exchange intercalation of Ni²⁺ into the interlayer space of HUP. The Ni²⁺-removing capacity of a column was proportional to the mass of HUP deposited and the Ni/HUP-loaded column was regenerated by washing with uranyl solution containing citrate/MOPS buffer and glycerol-2-phosphate, or with citrate buffer alone. Regeneration in the presence of UO₂ ²⁺ increased the Ni²⁺-removing capacity of the column. A new mechanism for the removal of heavy metals via microbially enhanced chemisorption is proposed.     

Nickel accumulation by immobilized biofilm of Cirobacter sp. containing cell-bound polycrystalline hydrogen uranyl phosphate

Hydrogen uranyl phosphate (HUO2PO4: HUP), deposited enzymatically on Citrobacter N14 cells immobilized as biofilm on ceramic Raschig rings in a flow-through column, removed nickel quantitatively from dilute aqueous solution in the form of nickel uranyl phosphate, via intercalative ion exchange. Nickel-loaded columns were regenerated by washing either with citrate buffer or with buffer containing UO22 and phosphate donor (glycerol 2-phosphate), this giving additional crystalline HUP deposit for subsequent improvement of nickel removal. No uranium release occurred during selective desorption of Ni, proving the integrity of the biofilm within the column. The use of ceramic supports to manufacture an artificial, bioinorganic, ion exchanger is novel and the use of solid matrices overcomes the problems of mechanical stability which limit the applications of gel-immobilized cells for large-scale processes. © Rapid Science Ltd. 1998     

Removal of Pb2+ and Ni2+ by bio-sludge in sequencing batch reactor (SBR) and granular activated carbon-SBR (GAC-SBR) systems

Living bio-sludge from domestic wastewater treatment plant was used as adsorbent of heavy metals (Pb(2+), Ni(2+)) and its adsorption capacity was about 10-30% reduced by autoclaving at 110 degrees C for 10 min. The living bio-sludge acclimatized in synthetic industrial estate wastewater (SIEWW) without heavy metals showed the highest Pb(2+) and Ni(2+) adsorption capacities at 840+/-20 and 720+/-10 mg/g bio-sludge, respectively. The adsorbed Pb(2+) and Ni(2+) were easily eluted (70-77%) from bio-sludge by washing with 0.1 mol/l HNO(3) solution. The heavy metals (Pb(2+), Ni(2+)) removal efficiency of both SBR and GAC-SBR systems were increased with the increase of hydraulic retention time (HRT), or the decrease of organic loading. The SBR system showed higher heavy metals removal efficiency than GAC-SBR system at the same organic loading or HRT. The Pb(2+), Ni(2+), BOD(5), COD and TKN removal efficiencies of GAC-SBR system were 88.6+/-0.9%, 94.6+/-0.1%, 91.3+/-1.0%, 81.9+/-1.0% and 62.9+/-0.5%, respectively with industrial estate wastewater (IEWW) with 410 mg/l glucose, 5 mg/l Pb(2+) and 5 mg/l Ni(2+) under organic loading of 1.25 kg BOD(5)/m(3) d (HRT of 3 days). The bio-sludge quality (sludge volume index: SVI) of the system was less than 80 ml/g. The excess sludge from both SBR and GAC-SBR systems with SIEWW under the organic loading of 1.25-2.50 kg BOD(5)/m(3) d contained Pb(2+) and Ni(2+) at concentrations of 240-250 mg Pb(2+)/g bio-sludge and 180-210 mg Ni(2+)/g bio-sludge, respectively.     

Adsorption and Desorption of Nickel(II) Ions from Aqueous Solution by a Lignocellulose/Montmorillonite Nanocomposite

A new and inexpensive lignocellulose/montmorillonite (LNC/MMT) nanocomposite was prepared by a chemical intercalation of LNC into MMT and was subsequently investigated as an adsorbent in batch systems for the adsorption-desorption of Ni(II) ions in an aqueous solution. The optimum conditions for the Ni(II) ion adsorption capacity of the LNC/MMT nanocomposite were studied in detail by varying parameters such as the initial Ni(II) concentration, the solution pH value, the adsorption temperature and time. The results indicated that the maximum adsorption capacity of Ni(II) reached 94.86 mg/g at an initial Ni(II) concentration of 0.0032 mol/L, a solution pH of 6.8, an adsorption temperature of 70°C, and adsorption time of 40 min. The represented adsorption kinetics model exhibited good agreement between the experimental data and the pseudo-second-order kinetic model. The Langmuir isotherm equation best fit the experimental data. The structure of the LNC/MMT nanocomposite was characterized by X-ray diffraction (XRD) and transmission electron microscopy (TEM), whereas the adsorption mechanism was discussed in combination with the results obtained from scanning electron microscopy (SEM), energy-dispersive X-ray spectroscopy (EDX), and Fourier-transform infrared spectroscopy analyses (FTIR). The desorption capacity of the LNC/MMT nanocomposite depended on parameters such as HNO₃ concentration, desorption temperature, and desorption time. The satisfactory desorption capacity of 81.34 mg/g was obtained at a HNO₃ concentration, desorption temperature, and desorption time of 0.2 mol/L, 60 ºC, and 30 min, respectively. The regeneration studies showed that the adsorption capacity of the LNC/MMT nanocomposite was consistent for five cycles without any appreciable loss in the batch process and confirmed that the LNC/MMT nanocomposite was reusable. The overall study revealed that the LNC/MMT nanocomposite functioned as an effective adsorbent in the detoxification of Ni(II)-contaminated wastewater.     

Enterovirus 71 adsorption on metal ion-composite chitosan beads

In this study, we developed composite chitosan beads combining various metal ions, including Ni(2+), Cu(2+), Zn(2+), and Fe(2+), for direct adsorption of enterovirus 71 (EV71). The metal-ion species had significant effects on the adsorption capacity of beads. Among these metal ion-composite chitosan beads, Ni(2+)-chitosan beads exhibited the best adsorption capacity of EV71. Using a concentration of 0.01-M Ni(2+) was found to best provide for bead formation and EV71 adsorption. The adsorption of EV71 for Ni(2+)-chitosan beads at neutral or alkaline pH was favored. Under a competitive condition with albumin proteins, Ni(2+)-chitosan beads exhibited significant capacity of EV71 adsorption in culture media. The adsorption of EV71 on the Ni(2+)-chitosan beads was attributed to the strong binding between Ni(2+) ions chelated to the surface amino acid of EV71 capsids and Ni(2+) ions chelated on the chitosan materials. Moreover, the adsorbed EV71 retained its antigenicity and infectivity after desorption. The Ni(2+)-chitosan beads exhibit a promising application to EV71 adsorption and removal.     

Use of silica-immobilized humin for heavy metal removal from aqueous solution under flow conditions

Humin extracted from Sphagnum peat moss was immobilized in a silica matrix and column experiments were performed in order to evaluate the removal and recovery of metal ions from aqueous solution under flow conditions. These experiments also allowed testing the recycling capacity of the column. Single-element solutions of Cu(II) and Pb(II), and a multi-metal solution containing Cd(II), Cu(II), Pb(II), Ni(II), and Cr(III) were passed through the columns at a flow rate of 2 ml/min. A 0.5 M sodium citrate solution was used as the stripping agent in the metal-ion recovery process. Humin immobilized in the silica matrix exhibited a similar, and in some cases, even a higher capacity than other biosorbents for the removal of metal ions from aqueous solutions under flow conditions. The sodium citrate was effective in removing Cu(II), Pb(II), Cd(II), and Ni(II) from the metal saturated column. The selectivity of the immobilized biomass was as follows: Cr(III)>Pb(II)>Cu(II)>Cd(II)>Ni(II). This investigation provides a new, environmentally friendly and cost-effective possibility to clean up heavy-metal contaminated wastewaters by using the new silica-immobilized humin material.     

Metal ion binding to human hemopexin

Binding of divalent metal ions to human hemopexin (Hx) purified by a new protocol has been characterized by metal ion affinity chromatography and potentiometric titration in the presence and absence of bound protoheme IX. ApoHx was retained by variously charged metal affinity chelate resins in the following order: Ni(2+) > Cu(2+) > Co(2+) > Zn(2+) > Mn(2+). The Hx-heme complex exhibited similar behavior except the order of retention of the complex on Zn(2+)- and Co(2+)-charged columns was reversed. One-dimensional (1)H NMR of apoHx in the presence of Ni(2+) implicates at least two His residues and possibly an Asp, Glu, or Met residue in Ni(2+) binding. Potentiometric titrations establish that apoHx possesses more than two metal ion binding sites and that the capacity and/or affinity for metal ion binding is diminished when heme binds. For most metal ions that have been studied, potentiometric data did not fit to binding isotherms that assume one or two independent binding sites. For Mn(2+), however, these data were consistent with a high-affinity site [K(A) = (15 +/- 3) x 10(6) M(-)(1)] and a low-affinity site (K(A) 相似文献   

Accumulation of zirconium phosphate by a <Emphasis Type="Italic">Serratia</Emphasis> sp.: a benign system for the removal of radionuclides from aqueous flows

Metal phosphate deposited enzymatically on Serratia sp. has been used successfully for the removal of radionuclides from aqueous flows. Previous studies using biogenic hydrogen uranyl phosphate (HUP) on Serratia sp. biofilm showed removal of 100% of ⁹⁰Sr, ¹³⁷Cs, and ⁶⁰Co via their intercalation into biogenic HUP crystals. Zirconium phosphates (ZrP) offer a potential non-toxic and non-radioactive alternative to HUP for water decontamination. A method was developed for biomanufacturing ZrP. Biogenic ZrP removed ca. 100% of Sr²⁺ and Co²⁺ (0.5 mM) from solutions to a molar ratio at saturation of ca. 1:0.6 for both Zr:Sr and Zr:Co. The potential for drinking water decontamination via bio-ZrP is discussed with respect to bio-HUP and also other commercially available materials.     

The influence of phototrophic benthic biofilms on Cd, Cu, Ni, and Pb transport in permeable sediments

The effect of phototrophic biofilm activity on advective transport of cadmium (Cd), copper (Cu), nickel (Ni), and lead (Pb) in sandy sediments was examined using percolated columns. Cd and Ni in the effluent exhibited clear diel cycles in biofilm-containing columns, with concentrations at the end of dark periods exceeding those during illumination by up to 4.5- and 10-fold for Ni and Cd, respectively. Similar cycles were not observed for Pb or Cu. Breakthrough of the latter metals was greatly retarded and incomplete relative to Cd and Ni, and trends in biofilm treatments did not differ greatly from those in control columns. Inhibition of photosystem II by DCMU (3-(3,4-dichlorophenyl)-1,1-dimethylurea) proved that diel cycles of Cd and Ni were controlled by oxygenic photosynthesis, and microsensor measurements showed that metal cycles closely matched metabolic activity-driven pH variations. The sorption edge pH for the sand/biofilm substrate followed the order Ni > Cd > Cu > Pb, and for Ni and Cd, was within the pH 7?C10 range observed in the biofilm-containing column. Adsorption dynamics over the light periods matched pH increases, but desorption during dark periods was incomplete and slower than the rate of change of pH. Over a diel cycle, desorption was less than adsorption, resulting in net binding of dissolved metals due to the biofilm metabolic activity. Extraction with selective reagents indicated that the adsorbed metals were readily exchangeable, and potentially bioavailable. Thus, phototrophic benthic biofilms can control the transport of some metals across the sand?Cwater interface, and processes in this very thin surficial layer should be considered when evaluating chemical fluxes in permeable sediments.     

Microbially-enhanced chemisorption of Ni2+ ions into biologically-synthesised hydrogen uranyl phosphate (HUP) and selective recovery of concentrated Ni2+ using citrate or chloride ion

Hydrogen uranyl phosphate (HUP) deposited enzymatically on Citrobacter N14 immobilized in polyacrylamide gel removed nickel ions from solution via intercalative ion-exchange into the HUP lattice. Using flow-through columns containing 100 mg dry weight of biomass and 200–250 mg loaded uranium column saturation and breakthrough of Ni²⁺ occurred after ca. 600 ml, with a total of 30 mg Ni²⁺ loaded per column, corresponding to a molar ratio of U:Ni of 2:1, in accordance with the identity of the material as Ni(UO₂PO₄)₂, identified previously. Ni²⁺ was selectively desorbed using 100 mM sodium citrate-citric acid buffer over 140 ml or a short pulse (5 ml) of 500 mM citrate buffer followed by a water wash, giving a total recovery volume of 80 ml, with a total citrate concentration of 30 mM in the wash solution of the latter. As an alternative eluant which gives no residual BOD NaCl (0.6 M) or seawater gave comparable recovery of Ni²⁺ to the 0.5 M citrate pulse, but with a Ni²⁺ recovery volume of 40–50 ml. The concentration ratio of Ni²⁺-deposition:desorption (vol:vol) was 3–4 fold better with chloride ion than with 100 mM citrate.     

Construction and characterization of a photosynthetic bacterium genetically engineered for Hg2+ uptake

A recombinant photosynthetic bacterium, Rhodopseudomonas palustris, was constructed to simultaneously express mercury transport system and metallothionein for Hg(2+) removal from heavy metal wastewater. The effects of essential process parameters, including pH, ionic strength and presence of co-ions on Hg(2+) uptake were evaluated. The results showed that compared with wild type R. palustris, recombinant strain displayed stronger resistance to toxic Hg(2+), and its Hg(2+) binding capacity was enhanced threefolds. In the range of pH 4-10, recombinant R. palustris maintained effective accumulation of Hg(2+). The presence of 10 mg L(-1) Mg(2+), Ca(2+), Zn(2+) or Ni(2+) did not significantly influence Hg(2+) bioaccumulation by recombinant R. palustris from solutions containing 0.2 mg L(-1) Hg(2+), while Na(+) and Cd(2+) posed serious adverse effect on Hg(2+) uptake. Furthermore, EDTA treatment experiment confirmed that different from wild type R. palustris that mainly absorbed Hg(2+) on the cell surface, recombinant R. palustris transported most of the bound Hg(2+) into the cells.     

Preparation of ethylenediamine-anchored cellulose and determination of thermochemical data for the interaction between cations and basic centers at the solid/liquid interface

Cellulose was first modified with thionyl chloride, giving 99% substitution at C6, and then reacted with ethylene-1,2-diamine to produce 6-(2'-aminoethylamino)-6-deoxy-cellulose. From the 8.5% of nitrogen incorporated in the polysaccharide backbone, the amount of ethylene-1,2-diamine anchored per gram of modified cellulose was determined to be 3.03+/-0.01mmol. This chemically immobilized surface was characterized by FTIR, TG, (13)C NMR, and SEM techniques. The available basic nitrogen centers covalently bonded to the biopolymer skeleton were studied for copper, cobalt, nickel, and zinc adsorption from aqueous solutions and the respective thermal adsorption effects were determined by calorimetric titration. The ability to adsorb cations gave a capacity order of Co(2+)>Cu(2+)>Zn(2+)>Ni(2+) with affinities of 1.91+/-0.07, 1.32+/-0.07, 1.31+/-0.02, and 1.08+/-0.04mmol/g, respectively. The net thermal effects obtained from calorimetric titration measurements were adjusted to a modified Langmuir equation and the enthalpy of the interaction was calculated to give the following exothermic values: -20.8+/-0.05, -11.72+/-0.03, -7.32+/-0.01, and -6.27+/-0.02kJ/mol for Co(2+), Cu(2+), Zn(2+), and Ni(2+), respectively. With the exception of the entropic value for copper, the other thermodynamic data for these systems are favorable for cation adsorption from aqueous solutions at the solid/liquid interface, suggesting the use of this anchored biopolymer for cation removal from the environment.     

Microalgal-luffa sponge immobilized disc: a new efficient biosorbent for the removal of Ni(II) from aqueous solution

AIMS: The aim was to develop a new, efficient and cost-effective biosorbent for the removal of heavy metals from aqueous solution. METHODS AND RESULTS: A new biosorbent was developed by immobilizing a unicellular green microalga Chlorella sorokiniana within luffa sponge discs and used for the removal of metal ions from aqueous solution. Microalgal-luffa sponge immobilized discs (MLIDs) removed Ni(II) very rapidly, with 97% of equilibrium loading being reached in 5 min. MLIDs were tested for their potential to remove Ni(II) from aqueous solution in fixed-bed column bioreactor. The regenerated MLIDs retained 92.9% of the initial binding capacity for Ni(II) up to five cycles of reuse. CONCLUSIONS: In this study for the first time, C. sorokiniana biomass immobilized within luffa sponge disc was successfully used as a metal biosorbent for the removal of Ni(II). It appears that MLIDs can be used as an effective biosorbent for efficient removal of Ni(II) or other metals from aqueous solution. SIGNIFICANCE AND IMPACT OF THE STUDY: MLIDs biosorption system was shown to have good biosorption properties with respect to Ni(II). Efficient metal removal ability of MLIDs, low cost and simplicity of the technique used for the preparation of MILDs could provide an attractive strategy for developing high-affinity biosorption system for heavy metal removal.     

The nickel site of Bacillus pasteurii UreE, a urease metallo-chaperone, as revealed by metal-binding studies and X-ray absorption spectroscopy

UreE is a homodimeric metallo-chaperone that assists the insertion of Ni(2+) ions in the active site of urease. The crystal structures of UreE from Bacillus pasteurii and Klebsiella aerogenes have been determined, but the details of the nickel-binding site were not elucidated due to solid-state effects that caused disorder in a key portion of the protein. A complementary approach to this problem is described here. Titrations of wild-type Bacillus pasteurii UreE (BpUreE) with Ni(2+), followed by metal ion quantitative analysis using inductively coupled plasma optical emission spectrometry (ICP-OES), established the binding of 2 Ni(2+) ions to the functional dimer, with an overall dissociation constant K(D) = 35 microM. To establish the nature, the number, and the geometry of the ligands around the Ni(2+) ions in BpUreE-Ni(2), X-ray absorption spectroscopy data were collected and analyzed using an approach that combines ab initio extended X-ray absorption fine structure (EXAFS) calculations with a systematic search of several possible coordination geometries, using the Simplex algorithm. This analysis indicated the presence of Ni(2+) ions in octahedral coordination geometry and an average of two histidine residues and four O/N ligands bound to each metal ion. The fit improved significantly with the incorporation, in the model, of a Ni-O-Ni moiety, suggesting the presence of a hydroxide-bridged dinuclear cluster in the Ni-loaded BpUreE. These results were interpreted using two possible models. One model involves the presence of two identical metal sites binding Ni(2+) with negative cooperativity, with each metal ion bound to the conserved His(100) as well as to either His(145) or His(147) from each monomer, residues found largely conserved at the C-terminal. The alternative model comprises the presence of two different binding sites featuring different affinity for Ni(2+). This latter model would involve the presence of a dinuclear metallic core, with one Ni(2+) ion bound to one His(100) from each monomer, and the second Ni(2+) ion bound to a pair of either His(145) or His(147). The arguments in favor of one model as compared to the other are discussed on the basis of the available biochemical data.     

Influence of Ni(2+) concentration on biohydrogen production

In this paper, the effect of Ni(2+) concentration ranging from 0 to 50mg/L on fermentative hydrogen production by mixed cultures was investigated in batch test. The results showed that at 35 degrees C and initial pH 7.0, Ni(2+) was able to enhance the hydrogen production rate with increasing Ni(2+) concentration from 0 to 0.2mg/L, and enhance the hydrogen production potential and hydrogen yield with increasing Ni(2+) concentration from 0 to 0.1mg/L. The maximum hydrogen production potential of 288.6mL and the maximum hydrogen yield of 296.1mL/g glucose were obtained at the Ni(2+) concentration of 0.1mg/L. In all tests, the major soluble metabolites produced by mixed cultures were ethanol, acetic acid and butyric acid, without propionic acid. Ni(2+) had little effect on the substrate degradation efficiency with increasing concentration from 0 to 50mg/L. Ni(2+) was able to enhance the biomass production yield with increasing Ni(2+) concentration from 0 to 0.1mg/L. The maximum biomass production yield of 232.5mg/g glucose was obtained at the Ni(2+) concentration of 0.1mg/L. In all tests, the final pH after fermentative hydrogen production was lower than the initial pH.     

Interaction of adenine nucleotides with multiple binding sites on beef heart mitochondrial adenosine triphosphatase.

Beef heart mitochondrial ATPase (F1) contained 2 mol of ADP and 1 mol of ATP/mol of enzyme, which resisted removal by Sephadex chromatography with dilute buffers or repeated precipitation with ammonium sulfate. The native enzyme also contained two apparently equivalent binding sites, which participated in readily reversible binding of adenyl-5'-ylimidodiphosphate (AMP-P(NH)P), with a Kd of 1.3 mum. The failure of AMP-P(NH)P to compete effectively with ADP for binding sites on F1 may be related to the failure of the analog to inhibit oxidative phosphorylation. Virtually complete removal of all adenine nucleotides from F1 occurred when the enzyme was chromatographed on columns of Sephadex equilibrated with 50% glycerol. No loss in ATPase activity was observed following removal of nucleotides from the enzyme, which was then capable of binding more than 4 mol of ADP and almost 5 mol of AMP-P(NH)P/mol of protein. Subsequent chromatography on columns of Sephadex equilibrated with dilute buffers containing Mg2+ removed only 1.5 mol of ADP and no AMP-P(NH)P from the enzyme. Reconstitution of F1 with ADP or with almost 5 mol of AMP-P(NH)P resulted in preparations that exhibited an undiminished capacity to restore oxidative phosphorylation in F1-deficient submitochondrial particles.     

Properties of a reconstituted eukaryotic hexose/proton symporter solubilized by structurally related non-ionic detergents: specific requirement of phosphatidylcholine for permease stability

Overexpression of the hexose/proton symporter HUP1 from Chlorella kessleri in S. cerevisiae permits a one-step purification via a biotinylation domain. Milligram amounts of the protein are obtained starting from 2 l of yeast culture. The HUP1 protein is used as a model eukaryotic membrane protein of the 'major facilitator superfamily' (MFS) to study specific lipid requirements for activity and stability. Testing two series of detergents revealed that n-nonyl-beta-D-glucoside (NG) and n-octyl-beta-D-glucoside (OG) solubilize the HUP1 protein efficiently. Only the use of NG resulted in long-term stabilization of the HUP1 protein in the absence of external lipids. When affinity purified protein was extracted with organic solvents, a stoichiometric amount of phosphatidyl choline, phosphatidyl ethanolamine and ergosterol in the ratio of close to 2:1 was detected. These lipids were only observed, however, when the protein purification was carried out in the presence of NG; no lipids were copurified with the HUP1 protein in the presence of OG. Of the three lipids copurified, phosphatidyl choline showed a crucial role in ensuring maximal HUP1 permease activity and stability when added back to the OG-protein. The requirement of phosphatidylcholine documents a specific effect of lipids on vectorial transport mediated by a eukaryotic membrane protein of the MFS family.     

Removal of Pb2+ from aqueous system by live Oscillatoria laete-virens (Crouan and Crouan) Gomont isolated from industrial effluents

Cyanobacteria have been found to be potential biosorbents of metal ions from waste water. The Pb(2+) removal capacity of growing cells of indigenous cyanobacterium Oscillatoria laete-virens (Crouan and Crouan) Gomont was studied under batch experiments and it was found capable of removing Pb(2+) of lower concentrations (below 100?mg L(-1)). The effects of different concentrations of Pb(2+), on the growth rate of alga were also evaluated. The research parameters include the pH of the solution, contact time, initial concentration of Pb(2+), and culture density. Of the parameters studied, the pH of the solution was found to be the most crucial. The removal of Pb(2+) peaked at an initial pH of 5. The data obtained from the equilibrium experiments were found well fitting with the Langmuir isotherm with a maximum sorptive capacity (q (max)) of 20.36?mg?g(-1), indicating a good biosorbtive potential of growing cells. This was confirmed using scanning electron microscope and energy dispersive X-ray analysis, which showed the adsorption of lead on the surface of the cell. The species could tolerate a concentration as high as 60?mg L(-1) of Pb(2+). It was observed that the removal obeyed the pseudo-second-order kinetics. The percentage removal was found to decrease with increasing metal concentration, from 10 to 100?mg L(-1). FTIR analysis indicates the involvement of amino, carboxylic and amide groups in the sorption process. Among the desorbing agents evaluated, an efficient recovery of 90.2?% was achieved by HCl, in 24?h. Thus Oscillatoria laete-virens (Crouan and Crouan) Gomont seems to be a promising metal biosorbent for the treatment of Pb(2+), in waste waters.     

Ni2+ enhances Fe2+/peroxide-induced oxidation of arachidonic acid and formation of geno/cytotoxic 4-hydroxynonenal: a possible contributory mechanism in nickel toxicity and allergenicity

Ni(2+), a toxic, carcinogenic and allergenic agent, affected both the kinetic and chemical courses of the Fe(2+)-induced oxidation of arachidonic acid (AA) in 0.05 M phosphate buffer (pH 7.4) and at 37 degrees C. At 10 microM concentration, Ni(2+) decreased the rate of oxidation of peroxide-free AA (200 microM) promoted by 50 microM Fe(2+), as determined by measurement of thiobarbituric acid reactive species (TBARS) and 1H NMR analysis. However, in the presence of low levels of peroxides (e.g. 2%), Ni(2+) exerted a significant stimulatory effect on Fe(2+)-induced AA oxidation and TBARS formation. 1H NMR analysis showed that Ni(2+) (10 microM) enhanced formation of genotoxic alkenals including 4-hydroxy-2-nonenal (4-HNE, GC/MS evidence) by Fe(2+)-promoted degradation of both AA and 15-hydroperoxy-5,8,11,13-eicosatetraenoic acid (15-HPETE) methyl esters. The observed stimulatory effects of Ni(2+) on peroxide breakdown and cytotoxic aldehyde formation provide an attractive explanation to the enhanced sensitization capacity of nickel in inflammatory states compared to normal states.     

Sorption of heavy metals from electroplating effluent using immobilized biomass Trichoderma viride in a continuous packed-bed column

The sorption of heavy metals ions by immobilized Trichoderma viride biomass in a packed-bed column was studied. Fungal biomass T. viride was immobilized to Ca-alginate used for removal of Cr(VI), Ni(II) and Zn(II) ions from synthetic solutions and electroplating effluent. The experiments were conducted to study the effect of important design parameters such as bed height, flow rate and initial concentration of metal ions. The maximum sorption capacity was observed at flow rate 5 ml/min, bed height 20 cm and metal ions concentration 50 mg/L with immobilized biomass. Whereas, breakthrough time and saturation time decreased with increase flow rate and metal ions concentration and an inverse condition was found in bed height. The bed depth service time (BDST) Adams-Bohart model was used to analyze the experimental data. The regeneration efficiency was observed 40.1%, 75% and 53% for Cr(VI), Ni(II) and Zn(II) without any significant alteration in sorption capacity after 5th sorption-desorption cycles.