Nickel resistance of Alcaligenes denitrificans strain 4a-2 is chromosomally coded

Single and combined effects of nickel (Ni(II)) and cobalt (Co(II)) ions on activated sludge and on other aerobic microorganisms: a review

Nickel (N(II)) and cobalt (Co(II)) are often encountered in wastewaters. As conventional wastewater treatment may only partially remove nickel and cobalt, a large fraction of the above metals is released to the aquatic environment. Both metals have been identified as micronutrients, at trace concentrations; however, they are both microbial growth inhibitors, at relatively high concentrations. On the other hand, the combined effects (e.g.: growth stimulation or toxicity) of the above metals have been found to differ from the summation of the effects which occur when the metals are applied individually. Moreover, a number of environmental factors (e.g.: pH, biomedium composition, biomass concentration, presence of other heavy metals) can affect the microbial toxicity of the above metallic species. The present review discusses, in a systematic way, the individual and joint effects of the above heavy metals to the growth of microorganisms grown under aerobic conditions, with focus on the growth of activated sludge. Data on multi-metal toxicity are particularly useful in establishing criteria for heavy metal tolerance levels in the environment.

Extracytoplasmic storage as the nickel resistance mechanism in a natural isolate of Pseudomonas putida S4

Metal resistances in microbes are important to study not only to understand metal homeostasis but also to use such organisms further in environmental bioremediation. Nickel (Ni2+) is an important micronutrient, which at higher concentration becomes toxic. Many Ni2+-resistant organisms are known, which resist metal by active efflux. Pseudomonas putida S4, a natural isolate from India, is reported to show a multi-metal resistance profile. In the present study, the Ni2+-resistance mechanism in strain S4 was examined. Wild-type cells gradually accumulated Ni2+ but kept it preferentially in the periplasmic space in a bound form. In Ni2+-sensitive mutants, periplasmic storage was disturbed and more metal accumulated cytoplasmically, producing toxicity. Sodium dodecyl sulphate-polyacrylamide gel electrophoresis analysis of periplasmic proteins revealed a band of approximately 18 kDa, which appeared only in Ni2+-exposed wild-type cells, and which was absent from cells not exposed to Ni2+ as well as from Ni2+-sensitive mutants. On the basis of these observations, we propose a Ni2+-resistance mechanism in P. putida S4 based on sequestration of metal in the periplasmic space. This is the first study of sequestration-based Ni2+ resistance.

Amplified rDNA restriction analysis and further genotypic characterisation of metal-resistant soil bacteria and related facultative hydrogenotrophs

The level of genotypic relationship between czc+ soil bacteria mainly resistant to zinc (but also to various other metals), and related facultative hydrogenotrophs previously assigned to the genera Alcaligenes, Ralstonia, and Burkholderia was evaluated using ARDRA (Amplified Ribosomal DNA Restriction Analysis). The analysis included 44 strains isolated from harsh industrial environments in sediments, soils and wastes with high content of heavy metals. These strains were selected by their ability to grow in the presence of high concentrations of multiple heavy metals and to hybridise with czc or ncc probes. The czc operon confers resistance to cadmium, zinc and cobalt in strain Ralstonia eutropha CH34. The ncc operon confers resistance to nickel, cobalt and cadmium in strain 31A known as Alcaligenes xylosoxidans. The analysis showed a close phylogenetic clustering of the czc+ strains inside the Ralstonia genus despite of their different origins and that the Ralstonia genus contained also the hydrogenotrophs and some catabolic strains assigned to the genus Ralstonia eutropha, strains up to now registrated as CDC IV c-2 strains as well as reference strains belonging to Ralstonia solanacearum and Ralstonia pickettii. The ncc+ strains are phylogenetically less related to each other compared to the czc+ strains. This suggests that the tested czc+ strains and some of the ncc+ strains may be considered as belonging to the genus Ralstonia. Inside this major Ralstonia cluster, a subcluster gathers most of the czc+ isolates maybe giving a clue to define a new species. Besides, from 30 tested strains, 15 metal resistant strains of this subcluster proved to display the unusual mutator phenotype characteristic of the representative strain CH34.

Nickel resistance in Escherichia coli V38 is dependent on the concentration used for induction

Strain Escherichia coli V38 resistant to 4 mM NiCl2 was isolated from the city sewage sludge. It showed low nickel accumulation by cells and nickel ion efflux. Cells were pregrown (induced) overnight in the presence of Ni2+, then the culture was kept on ice for 20-30 min and transferred to 37 degrees C for further incubation. When the Ni2+ concentration during growth was the same as during incubation, there was no noticeable accumulation of Ni2+. When the Ni2+ concentration during incubation was higher than that used for induction, uptake of 63Ni2+ and delayed efflux were seen. The uptake and delay of both efflux and growth were directly proportional to the difference between the concentrations used for induction and incubation. Active nickel ion uptake was seen in cells taken from cultures in the delayed efflux period.

Aluminum detoxication mechanism in Pseudomonas fluorescens is dependent on iron

The soil microbe Pseudomonas fluorescens has been shown to detoxify aluminum by the elaboration of a soluble metabolite where the trivalent metal is sequestered [Appanna and St. Pierre, FEMS Microbiol. Lett. 24 (1994) 327-332]. The inclusion of 5 mM iron in the growth medium elicited an entirely disparate detoxification strategy. In this instance, the two trivalent metals were immobilized in a gelatinous lipid-rich residue. Dialysis and ultracentrifugation studies indicated that the test metals were being transformed from early stages of growth and were associated with phosphatidylethanolamine. However, at 45 h of cellular multiplication, most of the metals were deposited as an insoluble residue. X-ray fluorescence analyses identified the constituents of this mineral essentially as aluminum, iron and phosphorus. Scanning electron microscopy and energy dispersive X-ray microanalysis of the dialysate, isolated at 35 h of microbial growth, revealed thread-like structures associated with nodule-like bodies that were rich in the two test metals. Transmission electron microscopic studies aided in the visualization of iron and aluminum inclusions within the bacterial cells.

Nickel-resistant bacteria from anthropogenically nickel-polluted and naturally nickel-percolated ecosystems

DNA fragments harboring the nickel resistance determinants from bacteria isolated from anthropogenically polluted ecosystems in Europe and Zaire were compared with those harboring the nickel resistance determinants from bacteria isolated from naturally nickel-percolated soils from New Caledonia by DNA-DNA hybridization. The biotinylated DNA probes were derived from the previously described Alcaligenes eutrophus CH34, Alcaligenes xylosoxidans 31A, Alcaligenes denitrificans 4a-2, and Klebsiella oxytoca CCUG 15788 and four new nickel resistance-determining fragments cloned from strains isolated from soils under nickel-hyperaccumulating trees. Nine probes were hybridized with endonuclease-cleaved plasmid and total DNA samples from 56 nickel-resistant strains. Some of the New Caledonian strains were tentatively identified as Acinetobacter, Pseudomonas mendocina, Comamonas, Hafnia alvei, Burkholderia, Arthrobacter aurescens, and Arthrobacter ramosus strains. The DNA of most strains showed homologies to one or several of the following nickel resistance determinants: the cnr and ncc operons of the strains A. eutrophus CH34 and A. xylosoxidans 31A, respectively, the nre operon of strain 31A, and the nickel resistance determinants of K. oxytoca. On the basis of their hybridization reactions the nickel resistance determinants of the strains could be assigned to four groups: (i) cnr/ncc type, (ii) cnr/ncc/nre type, (iii) K. oxytoca type, and (iv) others. The majority of the strains were assigned to the known groups. Among the strains from Belgium and Zaire, exclusively the cnr/ncc and the cnr/ncc/nre types were found. Among the New Caledonian strains all four types were represented. Homologies to the nre operon were found only in combination with the cnr/ncc operon. The homologies to the cnr/ncc operon were the most abundant and were detected alone or together with homologies to the nre operon. Only the DNA of the strains isolated from soil in Scotland and the United States and that of five of the New Caledonian strains did not show any detectable homologies to any of our probes. The nickel resistance fragment isolated from Burkholderia strain 32W-2 was studied in some detail. This 15-kb BamHI fragment conferred resistance to 1 to 5 mM NiCl(inf2) to Escherichia coli and resistance to up to 25 mM NiCl(inf2) to A. eutrophus. It showed strong homologies to both the cnr/ncc operon and the nre operon and conferred strictly regulated (inducible) nickel resistance to A. eutrophus.

Combined nickel-cobalt-cadmium resistance encoded by the ncc locus of Alcaligenes xylosoxidans 31A

The nickel-cobalt-cadmium resistance genes carried by plasmid pTOM9 of Alcaligenes xylosoxidans 31A are located on a 14.5-kb BamHI fragment. By random Tn5 insertion mutagenesis, the fragment was shown to contain two distinct nickel resistance loci, ncc and nre. The ncc locus causes a high-level combined nickel, cobalt, and cadmium resistance in strain AE104, which is a cured derivative of the metal-resistant bacterium Alcaligenes eutrophus CH34. ncc is not expressed in Escherichia coli. The nre locus causes low-level nickel resistance in both Alcaligenes and E. coli strains. The nucleotide sequence of the ncc locus revealed seven open reading frames designated nccYXHCBAN. The corresponding predicted proteins share strong similarities with proteins encoded by the metal resistance loci cnr (cnrYXHCBA) and czc (czcRCBAD) of A. eutrophus CH34. When different DNA fragments carrying ncc genes were heterologously expressed under the control of the bacteriophage T7 promoter, five protein bands representing NccA (116 kDa), NccB (40 kDa), NccC (46 kDa), NccN (23.5 kDa), and NccX (16.5 kDa) were detected.

Use of DNA probes and plasmid capture in a search for new interesting environmental genes

Adaptation to a stressed environment leads to organisms bearing DNA, encoding defense mechanisms. These mechanisms can be heavy metal resistance, catabolism of organic xenobiotics or stress reactions. Genes responsible for these mechanisms can be used for monitoring changing environments and therefore it can be important to store such bacteria in a bank. DNA-probing will be presented by the use of DNA fragments (of Alcaligenes eutrophus) coding for heavy metal resistance or xenobiotic degradation. Some strains do not grow on petri dishes and accordingly cannot be isolated from soils. In order to isolate plasmids from such strains, coding for heavy metal resistances or xenobiotic degradations, an exogenous plasmid isolation method was developed. In this method, the endogenous population is conjugated with Pseudomonas or Alcaligenes strains bearing a retrotransfer plasmid like RP4. In that way new plasmids from various sources including non-culturable strains could be obtained. With these methods, a large number of specimens adapted to stressed situations can be isolated or constructed (in the case of the exogenous plasmid isolation method). They form a source of interesting genetic material that can be used to restore polluted areas in natural areas, if necessary with the aid of genetic engineering (in vitro or in vivo techniques). Full knowledge of such bacteria and their resistance mechanisms or degradation pathways, can lead to new constructions able to attack recalcitrant mixtures of different organics and to resist heavy metals.

Characterization of the inducible nickel and cobalt resistance determinant cnr from pMOL28 of Alcaligenes eutrophus CH34

From pMOL28, one of the two heavy metal resistance plasmids of Alcaligenes eutrophus strain CH34, we cloned an EcoRI-PstI fragment into plasmid pVDZ'2. This hybrid plasmid conferred inducible nickel and cobalt resistance (cnr) in two distinct plasmid-free A. eutrophus hosts, strains AE104 and H16. Resistances were not expressed in Escherichia coli. The nucleotide sequence of the 8.5-kb EcoRI-PstI fragment (8,528 bp) revealed seven open reading frames; two of these, cnrB and cnrA, were assigned with respect to size and location to polypeptides expressed in E. coli under the control of the bacteriophage T7 promoter. The genes cnrC (44 kDa), cnrB (40 kDa), and cnrA (115.5 kDa) are probably structural genes; the gene loci cnrH (11.6 kDa), cnrR (tentatively assigned to open reading frame 1 [ORF]; 15.5 kDa), and cnrY (tentatively assigned to ORF0ab; ORF0a, 11.0 kDa; ORF0b, 10.3 kDa) are probably involved in the regulation of expression. ORF0ab and ORF1 exhibit a codon usage that is not typical for A. eutrophus. The 8.5-kb EcoRI-PstI fragment was mapped by Tn5 transposon insertion mutagenesis. Among 72 insertion mutants, the majority were nickel sensitive. The mutations located upstream of cnrC resulted in various phenotypic changes: (i) each mutation in one of the gene loci cnrYRH caused constitutivity, (ii) a mutation in cnrH resulted in different expression of cobalt and nickel resistance in the hosts H16 and AE104, and (iii) mutations in cnrY resulted in two- to fivefold-increased nickel resistance in both hosts. These genes are considered to be involved in the regulation of cnr. Comparison of cnr of pMOL28 with czc of pMOL30, the other large plasmid of CH34, revealed that the structural genes are arranged in the same order and determine proteins of similar molecular weights. The largest protein CnrA shares 46% amino acid similarity with CzcA (the largest protein of the czc operon). The other putative gene products, CnrB and CnrC, share 28 and 30% similarity, respectively, with the corresponding proteins of czc.

Resistance to cadmium, cobalt, zinc, and nickel in microbes

The divalent cations of cobalt, zinc, and nickel are essential nutrients for bacteria, required as trace elements at nanomolar concentrations. However, at micro- or millimolar concentrations, Co2+, Zn2+, and Ni2+ (and "bad ions" without nutritional roles such as Cd2+) are toxic. These cations are transported into the cell by constitutively expressed divalent cation uptake systems of broad specificity, i.e., basically Mg2+ transport systems. Therefore, in case of a heavy metal stress, uptake of the toxic ions cannot be reduced by a simple down-regulation of the transport activity. As a response to the resulting metal toxicity, metal resistance determinants evolved which are mostly plasmid-encoded in bacteria. In contrast to that of the cation Hg2+, chemical reduction of Co2+, Zn2+, Ni2+, and Cd2+ by the cell is not possible or sensible. Therefore, other than mutations limiting the ion range of the uptake system, only two basic mechanisms of resistance to these ions are possible (and were developed by evolution): intracellular complexation of the toxic metal ion is mainly used in eucaryotes; the cadmium-binding components are phytochelatins in plant and yeast cells and metallothioneins in animals, plants, and yeasts. In contrast, reduced accumulation based on an active efflux of the cation is the primary mechanism developed in procaryotes and perhaps in Saccharomyces cerevisiae. All bacterial cation efflux systems characterized to date are plasmid-encoded and inducible but differ in energy-coupling and in the number and types of proteins involved in metal transport and in regulation. In the gram-positive multiple-metal-resistant bacterium Staphylococcus aureus, Cd2+ (and probably Zn2+) efflux is catalyzed by the membrane-bound CadA protein, a P-type ATPase. However, a second protein (CadC) is required for full resistance and a third one (CadR) is hypothesized for regulation of the resistance determinant. The czc determinant from the gram-negative multiple-metal-resistant bacterium Alcaligenes eutrophus encodes proteins required for Co2+, Zn2+, and Cd2+ efflux (CzcA, CzcB, and CzcC) and regulation of the czc determinant (CzcD). In the current working model CzcA works as a cation-proton antiporter, CzcB as a cation-binding subunit, and CzcC as a modifier protein required to change the substrate specificity of the system from Zn2+ only to Co2+, Zn2+, and Cd2+.

High-Level Nickel Resistance in Alcaligenes xylosoxydans 31A and Alcaligenes eutrophus KTO2

Two new nickel-resistant strains of Alcaligenes species were selected from a large number (about 400) of strains isolated from ecosystems polluted by heavy metals and were studied on the physiological and molecular level. Alcaligenes xylosoxydans 31A is a heterotrophic bacterium, and Alcaligenes eutrophus KTO2 is an autotrophic aerobic hydrogen-oxidizing bacterium. Both strains carry—among other plasmids—a megaplasmid determining resistance to 20 to 50 mM NiCl 2 and 20 mM CoCl 2 (when growing in defined Tris-buffered media). Megaplasmids pTOM8, pTOM9 from strain 31A, and pGOE2 from strain KTO2 confer nickel resistance to the same degree to transconjugants of all strains of A. eutrophus tested but were not transferred to Escherichia coli. However, DNA fragments carrying the nickel resistance genes, cloned into broad-hostrange vector pVDZ'2, confer resistance to A. eutrophus derivatives as well as E. coli. The DNA fragments of both bacteria, TBA8, TBA9, and GBA (14.5-kb Bam HI fragments), appear to be identical. They share equal size, restriction maps, and strong DNA homology but are largely different from fragment HKI of nickel-cobalt resistance plasmid pMOL28 of A. eutrophus CH34.