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.     

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.     

Microbially enhanced chemisorption of nickel into biologically synthesized hydrogen uranyl phosphate: a novel system for the removal and recovery of metals from aqueous solutions

Ni(2+) was removed quantitatively from aqueous flows by columns loaded with polycrystalline hydrogen uranyl phosphate (HUP) bound to immobilized cells of Citrobacter sp. The columns functioned effectively in Ni uptake/regeneration cycles; five cycles were completed without significant decrease in the Ni-removing capacity of the column. The influence of pH, temperature, and flow rate on the Ni-removing capacity of the columns was examined. The composition of the Ni/HUP cell-bound deposits was confirmed by X-ray diffraction analysis (XRD) and proton-induced X-ray emission (PIXE) spectroscopy following several consecutive metal challenges and is discussed in relation to the mechanism of Ni(2+) removal from solution via ion-exchange intercalation into the interlayer space of HUP. Ni was selectively recovered from the columns using citrate or tartrate. The regenerated columns functioned effectively in Ni removal throughout repeated Ni challenge and desorption cycles. (c) 1997 John Wiley & Sons, Inc. Biotechnol Bioeng 54: 319-328, 1997.     

Phosphate release and heavy metal accumulation by biofilm-immobilized and chemically-coupled cells of a Citrobacter sp. pre-grown in continuous culture

A heavy metal-accumulating Citrobacter sp. was grown in carbon-limiting continuous culture in an air-lift fermentor containing raschig rings as support for biofilm development. Planktonic cells from the culture outflow were immobilized in parallel on raschig rings by chemical coupling (silanization), for quantitative comparison of phosphatase activity and uranyl uptake by both types of immobilized cell. The flow rate giving 50% conversion of substrate to product (phosphate) in flow-through reactors was higher, by 35-40%, for the biofilm-immobilized cells, possibly exploiting a pH-buffering effect of inorganic phosphate species within the extracellular polymeric material. Upon incorporation of uranyl ions (0.2 mM UO22+), both types of cell removed more than 90% of the input UO22+ at slow flow rates, but the chemically-coupled cells performed better at higher flow rates. The deposited material (HUO2PO4) subsequently removed Ni2+ from a second flow via intercalative ion exchange of Ni2+ into the crystalline HUO2PO4.4H2O lattice. This occurred irrespective of the method of coupling of the biomass to the support and suggested that uranyl phosphate accumulated by both types of cell has potential as a bio-inorganic ion exchanger-a potential use for the uranium recoved from primary waste treatment processes.     

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.     

Proton transport inside the biofilm limits electrical current generation by anode-respiring bacteria

Anode-respiring bacteria (ARB) in a biofilm anode carry out an oxidation half-reaction of organic matter, producing an electrical current from renewable biomass, including wastes. At the same time, ARB produce protons, usually one proton for every electron. Our study shows how current density generated by an acclimated ARB biofilm was limited by proton transport out of the biofilm. We determined that, at high current densities, protons were mainly transported out of the biofilm by protonating the conjugate base of the buffer system; the maximum current generation was directly related to the transport of the buffer, mainly by diffusion, into and out of the biofilm. With non-limiting acetate concentrations, the current density increased with higher buffer concentrations, going from 2.21 +/- 0.02 A m(-2) with 12.5-mM phosphate buffer medium to 9.3 +/- 0.4 A m(-2) using a 100-mM phosphate buffer at a constant anode potential of E(anode) = -0.35 V versus Ag/AgCl. Increasing the concentration of sodium chloride in the medium (0-100 mM) increased current density by only 15%, indicating that ion migration was not as important as diffusion of phosphate inside the biofilm. The current density also varied strongly with medium pH as a result of the buffer speciation: The current density was 10.0 +/- 0.8 A m(-2) at pH 8, and the pH giving one-half the maximum rate was 6.5. A j-V curve analysis using 100 mM phosphate buffer showed a maximum current density of 11.5 +/- 0.9 A m(-2) and half-saturation potential of -0.414 V versus Ag/AgCl, a value that deviated only slightly from the standard acetate potential, resulting in small anode-potential losses. We discuss the implications of the proton-transport limitation in the field of microbial fuel cells and microbial electrolytic cells.     

The effect of ageing on the accumulation of uranium by a biofilm bioreactor,and promotion of uranium deposition in stored biofilms

Summary Biofilm-immobilised cells of aCitrobacter sp. accumulated uranyl ion when challenged in a flow-through bioreactor. Uranyl ion deposition and activity of the mediating phosphatase were adversely affected by pre-storage of the biofilm at 4°C for 5–6 months. Pre-exposure to uranyl ion statically enabled recovery from the deleterious effect of storage and promoted subsequent bioreactor performance.     

Purification of a functional gene therapy vector derived from Moloney murine leukaemia virus using membrane filtration and ceramic hydroxyapatite chromatography

The ability of membrane ultra- and diafiltration and two chromatography media, Matrex Cellufine Sulfate (Millipore) and Macro-Prep ceramic hydroxyapatite (Bio-Rad), to adsorb, elute, and purify gene therapy vectors based on Moloney murine leukaemia virus (MoMuLV) carrying the 4070A amphotropic envelope protein was studied. Membrane ultra- and diafiltration provided virus concentration up to 160-fold with an average recovery of infectious viruses of 77 +/- 14%. In batch experiments, Macro-Prep ceramic hydroxyapatite (type 2, particle size 40 microm) proved superior to Matrex Cellufine Sulfate for MoMuLV vector particle adsorption. Furthermore, functional vector particles could be eluted using phosphate buffer pH 6.8 (highest titres from >or=300 mM phosphate) from the Macro-Prep adsorbent, with higher specific titres (cfu/mg protein) than the starting material. Similar results were obtained when this ceramic hydroxyapatite was packed into a column and used in a liquid chromatography system. Recovery of transduction-competent virus was between 18 and 31% for column experiments and 32 and 46% for batch experiments.     

Ion exchange/complexation of the uranyl ion by Rhizopus biosorbent

Nonliving biomass of nine Rhizopus species effectively sequestered the uranyl ion from solution, taking up 150-250 mg U/g dry cells at 300 ppm U equilibrium concentration in solution, and 100-160 mg U/g dry cells with 100 ppm U in solution. The affinity of this biosorbent for the uranyl ion was found to be affected by timing of harvesting and medium composition. Uptake of the uranyl ion by nonliving biomass of Rhizopus oligosporus was due to ion exchange or complexation, since binding was reversed by the addition of complexing ligands or the reduction of pH to a value less than 2. Uptake isotherms were interpreted in terms of a model of multiple equilibria. At pH 相似文献   

Uranyl Precipitation by Pseudomonas aeruginosa via Controlled Polyphosphate Metabolism

The polyphosphate kinase gene from Pseudomonas aeruginosa was overexpressed in its native host, resulting in the accumulation of 100 times the polyphosphate seen with control strains. Degradation of this polyphosphate was induced by carbon starvation conditions, resulting in phosphate release into the medium. The mechanism of polyphosphate degradation is not clearly understood, but it appears to be associated with glycogen degradation. Upon suspension of the cells in 1 mM uranyl nitrate, nearly all polyphosphate that had accumulated was degraded within 48 h, resulting in the removal of nearly 80% of the uranyl ion and >95% of lesser-concentrated solutions. Electron microscopy, energy-dispersive X-ray spectroscopy, and time-resolved laser-induced fluorescence spectroscopy (TRLFS) suggest that this removal was due to the precipitation of uranyl phosphate at the cell membrane. TRLFS also indicated that uranyl was initially sorbed to the cell as uranyl hydroxide and was then precipitated as uranyl phosphate as phosphate was released from the cell. Lethal doses of radiation did not halt phosphate secretion from polyphosphate-filled cells under carbon starvation conditions.     

Uranyl precipitation by Pseudomonas aeruginosa via controlled polyphosphate metabolism

The polyphosphate kinase gene from Pseudomonas aeruginosa was overexpressed in its native host, resulting in the accumulation of 100 times the polyphosphate seen with control strains. Degradation of this polyphosphate was induced by carbon starvation conditions, resulting in phosphate release into the medium. The mechanism of polyphosphate degradation is not clearly understood, but it appears to be associated with glycogen degradation. Upon suspension of the cells in 1 mM uranyl nitrate, nearly all polyphosphate that had accumulated was degraded within 48 h, resulting in the removal of nearly 80% of the uranyl ion and >95% of lesser-concentrated solutions. Electron microscopy, energy-dispersive X-ray spectroscopy, and time-resolved laser-induced fluorescence spectroscopy (TRLFS) suggest that this removal was due to the precipitation of uranyl phosphate at the cell membrane. TRLFS also indicated that uranyl was initially sorbed to the cell as uranyl hydroxide and was then precipitated as uranyl phosphate as phosphate was released from the cell. Lethal doses of radiation did not halt phosphate secretion from polyphosphate-filled cells under carbon starvation conditions.     

Electron Dense Artefactual Deposits in Tissue Sections: The Role of Ethanol, Uranyl Acetate and Phosphate Buffer

The occurrence of electron dense deposits in sections of aldehyde-fixed tissue prepared for transmission electron microscopy has been attributed to a number of conflicting factors. In an attempt to clarify this, the precipitating effect of different combinations of phosphate or cacodylate buffer, glutaraldehyde, ethanol and uranyl acetate was investigated in test tubes. As a preliminary investigation the combination of phosphate buffer, ethanol and uranyl acetate was investigated in heart and kidney tissue fixed in glutaraldehyde with or without postosmication. The essential factors in the formation of electron dense deposits in these tissues appear to be phosphate buffer, ethanol, and uranyl acetate, although glutaraldehyde may contribute in some way. The nature and intensity of the deposits seem to vary with the sequence of combination of these factors. Osmium did not appear to be an essential factor in the reaction since deposits were observed in both osmicated and unosmicated tissue. To avoid such deposits, a postosmication distilled water wash for 20 to 30 min followed by en bloc staining with aqueous uranyl acetate is advised if phosphate buffer is used as a fixative vehicle or buffer wash after the primary fixative.     

Electron dense artefactual deposits in tissue sections: the role of ethanol, uranyl acetate and phosphate buffer.

The occurrence of electron dense deposits in sections of aldehyde-fixed tissue prepared for transmission electron microscopy has been attributed to a number of conflicting factors. In an attempt to clarify this, the precipitating effect of different combinations of phosphate or cacodylate buffer, glutaraldehyde, ethanol and uranyl acetate was investigated in test tubes. As a preliminary investigation the combination of phosphate buffer, ethanol and uranyl acetate was investigated in heart and kidney tissue fixed in glutaraldehyde with or without postosmication. The essential factors in the formation of electron dense deposits in these tissues appear to be phosphate buffer, ethanol, and uranyl acetate, although glutaraldehyde may contribute in some way. The nature and intensity of the deposits seem to vary with the sequence of combination of these factors. Osmium did not appear to be an essential factor in the reaction since deposits were observed in both osmicated and unosmicated tissue. To avoid such deposits, a postosmication distilled water wash for 20 to 30 min followed by en bloc staining with aqueous uranyl acetate is advised if phosphate buffer is used as a fixative vehicle or buffer wash after the primary fixative.     

Uranyl precipitation by biomass from an enhanced biological phosphorus removal reactor

Heavy metal and radionuclide contamination presents a significant environmental problem worldwide. Precipitation of heavy metals on membranes of cells that secrete phosphate has been shown to be an effective method of reducing the volume of these wastes, thus reducing the cost of disposal. A consortium of organisms, some of which secrete large quantities of phosphate, was enriched in a laboratory-scale sequencing batch reactor performing Enhanced Biological Phosphorus Removal, a treatment process widely used for removing phosphorus. Organisms collected after the aerobic phase of this process secreted phosphate and precipitated greater than 98% of the uranyl from a 1.5 mM uranyl nitrate solution when supplemented with an organic acid as a carbon source under anaerobic conditions. Transmission electron microscopy, energy dispersive x-ray spectroscopy, and fluorescence spectroscopy were used to identify the precipitate as membrane-associated uranyl phosphate, UO₂HPO₄.     

A Stopped-Flow Method for the Determination of Ascorbic Acid in Orange Juice Containing Triose Reductone

The adsorption of uranium by chitin phosphate and chitosan phosphate was investigated to obtain information on uranium recovery from aqueous systems, especially sea water and uranium mine waste water. The adsorption of uranium by chitin phosphate and chitosan phosphate was much greater than copper, cadmium, manganese, zinc, cobalt, nickel, magnesium and calcium. The adsorption of uranium was very rapid during the first 10 min and was affected by pH of the solution, temperature, granule radius and the co-existence of carbonate ion. The amounts of uranium adsorbed on the adsorbents increased linearly as the external uranium concentration increased. Uranium adsorbed on chitin phosphate easily desorbed with diluted sodium carbonate solution. On the other hand, uranyl and cobalt ions were separated from each other by using chitin phosphate.     

Radiotolerance of phosphatases of a Serratia sp.: potential for the use of this organism in the biomineralization of wastes containing radionuclides

Aqueous wastes from nuclear fuel reprocessing present special problems of radiotoxicity of the active species. Cells of Serratia sp. were found previously to accumulate high levels of hydrogen uranyl phosphate (HUP) via the activity of a phosphatase enzyme. Uranium is of relatively low radiotoxicity whereas radionuclide fission products such as (90)Sr and (137)Cs are highly radiotoxic. These radionuclides can be co-crystallized, held within the bio-HUP "host" lattice on the bacterial cells and thereby removed from contaminated solution, depending on continued phosphatase activity. Radiostability tests using a commercial (60)Co γ-source showed that while cell viability and activity of purified phosphatase were lost within a few hours on irradiation, whole-cell phosphatase retained 80% of the initial activity, even after loss of cell culturability, which was increased to 100% by the incorporation of mercaptoethanol as an example radioprotectant, beyond an accumulated dose of >1.3 MGy. Using this co-crystallization approach (without mercaptoethanol) (137)Cs(+) and (85)Sr(2+) were removed from a simulated waste selectively against a 33-fold excess of Na(+).     

The use of Escherichia coli bearing a phoN gene for the removal of uranium and nickel from aqueous flows

A Citrobacter sp. originally isolated from metal-polluted soil accumulates heavy metals via metal-phosphate deposition utilizing inorganic phosphate liberated via PhoN phosphatase activity. Further strain development was limited by the non-transformability of this environmental isolate. Recombinant Escherichia coli DH5α bearing cloned phoN or the related phoC acquired metal-accumulating ability, which was compared with that of the Citrobacter sp. with respect to removal of uranyl ion (UO₂ ²⁺) from dilute aqueous flows and its deposition in the form of polycrystalline hydrogen uranyl phosphate (HUO₂PO₄). Subsequently, HUO₂PO₄-laden cells removed Ni²⁺ from dilute aqueous flows via intercalation of Ni²⁺ into the HUO₂PO₄ lattice. Despite comparable acid phosphatase activity in all three strains, the E. coli DH5α (phoN) construct was superior to Citrobacter N14 in both uranyl and nickel accumulation, while the E. coli DH5α (phoC) construct was greatly inferior in both respects. Expression of phosphatase activity alone is not the only factor that permits efficient and prolonged metal phosphate accumulation, and the data highlight possible differences in the PhoN and PhoC phosphatases, which are otherwise considered to be related in many respects. Received: 30 December 1997 / Received revision: 25 March 1998 / Accepted: 26 March 1998     

Different pH Optima in the Two Steps of an Indirect Fluorescent Antibody Reaction for Clostridium botulinum Type E

Quantitative measurements of the effects of ions on fluorescent antibody reactions have not been reported in the literature. Data in this report show the effects of ranges of H(+), phosphate, Mg(2+), and Ca(2+) molarities on antigen-antibody coupling during an indirect fluorescent antibody (IFA) reaction for Clostridium botulinum type E. These effects were quantified in two ways: (i) by microphotometric measurement of cell fluorescence intensity; and (ii) by visual estimation of cell fluorescence intensity on long glass strips treated with antibody in ion gradients. Optimal pH for the first part of the reaction (coupling of rabbit antibody to cells) was 7.25, and optimum in the second part (coupling of tracer globulin to the rabbit globulin) was pH 7.37. Running the reaction as little as 0.10 to 0.15 pH units off from the optima considerably reduced fluorescence intensity. Sodium phosphate buffer up to 0.1 M did not significantly affect either portion of the reaction. Ca(2+) and Mg(2+) showed no effect on the first part of the reaction. These results support the use of higher-strength phosphate buffer and indicate for the first time that IFA reactions may have two independent, narrow pH optima.     

Antigen retrieval trial for post-embedding immunoelectron microscopy by heating with several unmasking solutions.

A novel antigen retrieval procedure was carried out in the post-embedding immunogold electron microscopy method to improve the stainability of the samples. This was done by weakly fixing cultured Helicobacter pylori (ATCC43504) and embedding in Lowicryl K4M. Before staining with the anti-H. pylori antibody, the ultrathin sections were mounted on a nickel grid and heated at 121C for 15 min, 99C for 40 min, and 65C for 24 hr in distilled water, 0.1 M phosphate buffer (pH 7.4), 0.01 M EDTA (pH 7.2), 0.05 M Tris buffer (pH 10.0), 0.8 M urea (pH 7.2), 0.01 M citric acid (pH 6.0), or a commercially available target unmasking fluid (S1699; pH 6.0). Antigen retrieval in the Tris buffer solution generally showed better stainability than the classical post-embedding method without any antigen retrieval. At 65C for 24 hr, better stainability of the ultrasections was observed for each of the solutions used except for the phosphate buffer compared to the control. We suggest that the antigen retrieval method should be applied for routine use even by in post-embedding immunogold electron microscopy.     

Subcellular localization of the inducible Chlorella HUP1 monosaccharide-H+ symporter and cloning of a Co-induced galactose-H+ symporter.

The unicellular green alga Chlorella kessleri can induce monosaccharide-H+ symport catalyzing the energy-dependent transport of D-glucose (D-Glc) and several other pentoses and hexoses across the plasmalemma. The gene coding for the inducible HUP1 monosaccharide-H+ symporter has been cloned and the protein has been characterized previously. The data presented in this paper demonstrate that the presence of the HUP1 gene product alone is not sufficient to cover the broad substrate specificity of monosaccharide transport in induced Chlorella cells. Two other HUP genes are shown to be co-induced in Chlorella in response to D-Glc in the medium. The cloning of HUP2 and HUP3 cDNA and genomic sequences is described, both being very homologous to HUP1. Modification of the 5' untranslated sequences of full-length cDNA clones of HUP2 and HUP3 allowed the functional expression of both transporters in Schizosaccharomyces pombe. HUP2 was shown to be a galactose-H+ symporter, whereas the substrate specificity of the HUP3 gene product is very similar to that of the HUP1 protein. However, HUP3 does not seem to be induced to high levels in Glc-treated Chlorella cells. Results are also presented proving that the product of the HUP1 gene is localized in the plasmalemma of D-Glc-induced Chlorella cells and is absent in plasma membranes of noninduced cells. Incubation of thin sections of Chlorella cells with anti-HUP1 antibodies and a fluorescence-labeled, second antibody yielded a ring of fluorescence on the surface of Glc-induced Chlorella cells.