Literature DB >> 24147089

Manganese (Mn) oxidation increases intracellular Mn in Pseudomonas putida GB-1.

Andy Banh1, Valarie Chavez, Julia Doi, Allison Nguyen, Sophia Hernandez, Vu Ha, Peter Jimenez, Fernanda Espinoza, Hope A Johnson.   

Abstract

Bacterial manganese (Mn) oxidation plays an important role in the global biogeochemical cycling of Mn and other compounds, and the diversity and prevalence of Mn oxidizers have been well established. Despite many hypotheses of why these bacteria may oxidize Mn, the physiological reasons remain elusive. Intracellular Mn levels were determined for Pseudomonas putida GB-1 grown in the presence or absence of Mn by inductively coupled plasma mass spectrometry (ICP-MS). Mn oxidizing wild type P. putida GB-1 had higher intracellular Mn than non Mn oxidizing mutants grown under the same conditions. P. putida GB-1 had a 5 fold increase in intracellular Mn compared to the non Mn oxidizing mutant P. putida GB-1-007 and a 59 fold increase in intracellular Mn compared to P. putida GB-1 ∆2665 ∆2447. The intracellular Mn is primarily associated with the less than 3 kDa fraction, suggesting it is not bound to protein. Protein oxidation levels in Mn oxidizing and non oxidizing cultures were relatively similar, yet Mn oxidation did increase survival of P. putida GB-1 when oxidatively stressed. This study is the first to link Mn oxidation to Mn homeostasis and oxidative stress protection.

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Year:  2013        PMID: 24147089      PMCID: PMC3798386          DOI: 10.1371/journal.pone.0077835

Source DB:  PubMed          Journal:  PLoS One        ISSN: 1932-6203            Impact factor:   3.240


Introduction

Bacteria and fungi can catalyze manganese (Mn) oxidation and thus play an important role in the biogeochemical cycling of Mn and other elements. Mn oxidizing bacteria are found in marine, freshwater, and terrestrial environments [1]. These widespread bacteria are found in divergent phylogenetic lineages from Proteobacteria to Firmicutes to the more recently noted Bacteroidetes [2-4]. Biogenic Mn oxidation can occur at much greater rates than homogeneous abiotic oxidation [5] and forms some of the most oxidative compounds in nature, Mn (III, IV) oxides [6]. These oxides can oxidize recalcitrant carbon compounds and reduced metals and sulfide, thereby affecting the fate of many compounds in nature [2,7,8]. Despite the prevalence of Mn oxidizing microbes and their important role in biogeochemical cycling, the physiological function of bacterial Mn(II) oxidation remains enigmatic [9]. Pseudomonas putida GB-1 and MnB1, freshwater Gammaproteobacteria, are model Mn(II) oxidizing bacteria that have been used for biochemical and molecular investigations into biogenic Mn oxidation. Mutational studies have revealed several genes in P. putida that can affect Mn oxidation including genes involved in flagellar synthesis [10], protein transport [11,12], two component response regulation [13], cytochrome c biogenesis [14,15], and carbon metabolism [15]. In addition, the oxidizing enzymes, multicopper oxidases, have been identified [16] and partially characterized [17,18]. Yet, the physiological role of Mn oxidation has not been determined. Many hypotheses regarding the potential physiological function or benefit of Mn(II) oxidation have been put forth, but strong evidence to support these hypotheses remains lacking [1,2,19]. By acting as an electron acceptor or oxidizing carbon compounds to bioavailable forms, Mn oxides may help the survival of bacteria by playing a role in energy production [20]. In addition, the oxidation of Mn(II) with molecular oxygen to form Mn oxides is an exergonic process and energy from this reaction could potentially be harvested [21]. Mn oxides form extracellularly as a result of Mn oxidation [19] with cells of Pseudomonas putida GB-1 becoming encrusted with Mn oxide minerals [17]. In these cases, Mn oxides could act as a protective shield against external reactive oxygen species (ROS), UV light, and predation from protists and viruses [1,22,23]. Mn oxides may also form as a detoxification mechanism to reduce the toxicity of Mn(II) or other toxic metals [1]. The potential benefits and physiological roles could be diverse and may vary between different phylogenetic lineages. Intracellular Mn has been shown to play an important role in protection against oxidative stress. Archibald and Fridovich [24] initially showed that Lactobacillus plantarum, which lacks a superoxide dismutase, could survive aerobic conditions as a result of high levels of intracellular Mn. More recently, Daly et al [25] have shown that Deinococcus radiodurans survives high levels of ionizing radiation and oxidative stress as a result of high intracellular Mn and low intracellular iron (Fe). Maintaining Mn homeostasis is an important part of dealing with the dangers of oxidative stress in many different strains of bacteria, and Mn uptake and efflux transporters have been shown to be important in controlling intracellular Mn levels and providing resistance to oxidative stress [26-33]. Here we show that Mn oxidation can increase intracellular Mn and can protect against oxidative stress. We propose that Mn oxidation plays a role in Mn homeostasis.

Methods

Bacterial strains, media, and growth conditions

P. putida GB-1, P. putida ∆2665 ∆2447 [16], and P. putida GB-1-007 [10,34], the wild type and non Mn-oxidizing mutants, respectively, were grown in Lept media (0.5 g/L yeast extract, 0.5 g/L casamino acids, 5 mM glucose, 0.48 mM calcium chloride, 0.83 mM magnesium sulfate, 3.7 µM iron (II) chloride, 10 mM HEPES pH 7.5, 0.04 µM copper sulfate, 0.15 µM zinc sulfate, 0.08 µM cobalt chloride, 0.06 µM sodium molybdate) [35] with or without 200 µM MnCl2. 100 ml cultures were grown at room temperature with shaking (250 rpm) to stationary phase, approximately 24 hours, when maximum Mn oxide precipitation occurred.

Preparation of cells for metal analysis

Cells were harvested by centrifugation (11,000g, 20 min, 4° C) using Corning® polypropylene centrifuge tubes and plasticware prewashed in 1 mM EDTA followed by 10% nitric acid. Harvested cells were resuspended in 20 mM ascorbic acid (pH 8) in PBS buffer to reduce manganese oxides with a minimum contact time of 15 minutes. Mn oxides were no longer detected as measured with the Mn oxidation assay (below). Cells were then washed two times in PBS buffer followed by a final wash in 1 mM EDTA in PBS. For ICP-MS analysis, the cell pellet was digested in 1 ml Optima grade nitric acid for 1 hr at 84 °C and then diluted with 34 ml MilliQ water.

Preparation of cell-free extract and protein separation for metal analysis

Cell pellets were prepared as above without digestion. The cells were lysed by freeze thaw and lysozyme as previously described [36] with minor modifications. Briefly, the washed cell pellets were subjected to 3 cycles of freeze thaw followed by resuspension in 10 mM TRIS pH 7.5, 50 mM sucrose containing 8400 U/ml of Ready Lyse (Epicentre®) and incubated for 15 minutes at room temperature. An equal volume of 10 mM TRIS pH 7.5, 50 mM NaCl, 10 mM MgCl2 with 12.5 U/ml of Benzonase was then added and incubated another 15 minutes at room temperature. Cells were centrifuged at 4 ° C, 17,000g for 15 minutes and the soluble fraction was defined as the cell-free extract. Cell-free extract was separated into a greater than 3 kDa fraction and a less than 3 kDa fraction using Amicon micro ultrafiltration with a 3 kDa filter according to the manufacturer’s specifications. Ultrafiltration tubes were rinsed once with 1 mM EDTA followed by three rinses with PBS prior to use.

Survivability assays

Cells were grown in MSTP media modified from [37] containing 20 mM (NH4)2SO4, 0.25 mM MgSO4, 0.4 mM CaCl2, 0.15 mM KH2PO4, 0.25 mM Na2HPO4, 10 mM HEPES, 9 mM sodium pyruvate, 0.01 mM FeCl3, 0.02 mM EDTA, and 1 ml/L Trace elements [35]. The cultures were prepared by inoculating an overnight culture with 250 µL of a frozen culture grown in MSTP media. The culture was grown for 24 hours and then 1.25 ml was inoculated into 25 ml of fresh MSTP media with 0 or 0.1 mM MnCl2. Cultures were grown for approximately 24 hours until stationary phase when Mn(II) had been converted into Mn oxides. 2 ml of cells were then treated with 16.1 mM hydrogen peroxide for 30 minutes to induce oxidative stress and killing after which 286 U/ml catalase was added to remove remaining hydrogen peroxide. Control cultures were treated with water instead of hydrogen peroxide. Most oxides were reduced upon exposure to hydrogen peroxide, but 0.1 mM ascorbic acid was also added to reduce any remaining Mn oxides that may increase cell clumping. The cells were then serially diluted in MSTP without pyruvate and plated onto MSTP solid media in triplicate. Relative survival was determined by dividing the percent survival of cells grown in 0.1 mM MnCl2 (Mn oxidizing) by the percent survival of cells grown without additional Mn added (non oxidizing). Percent survival was calculated as colony forming units (CFUs) of hydrogen peroxide treated cells divided by CFUs of water treated cells. CFUs were averages of triplicates. The one-tailed Student’s T-test was used for statistical analysis.

Oxidative stress for protein carbonylation assay

Following growth to stationary phase, a 100 ml culture of P. putida GB-1 grown on Lept media was stressed with 0.6 mM H2O2 or 5 mM paraquat for 30 minutes at room temperature. A lower concentration of hydrogen peroxide was used in protein carbonylation assays as opposed to survival assays to decrease death by oxidative stress. After 30 minutes, any remaining Mn oxides in the cultures were reduced with 1 mM ascorbic acid and cells were harvested by centrifugation at 11,000g, 4° C, 10 minutes. The pellets were resuspended in 3 ml 50 mM HEPES pH 7.75. Cells were disrupted by 4 passages through a French press at 18,000 psi and clarified by centrifugation for 20 minutes at 20,000g, 4° C. The extent of protein carbonylation was determined with the OxyBlot (Millipore) kit according to the manufacturer’s specifications.

Protein quantification

Protein was determined using the commercial Coomassie Plus Assay reagent (Pierce) with bovine serum albumin as the standard.

Mn oxidation assay

Oxidized Mn was measured as previously described using leucoberbelin blue with potassium permanganate as the standard [38].

Inductively coupled plasma mass spectrometry (ICP-MS)

All samples for ICP-MS analysis were acidified with Optima grade nitric acid and analyzed at IIRMES, California State University Long Beach. Triplicate blank samples were prepared in the same manner as all samples for analysis and the average concentration of the various metals in the blanks was subtracted from all samples.

Chemicals and reagents

All chemicals were reagent grade and purchased from Fisher or Sigma-Aldrich. Milli-Q water was used for the preparation of all solutions.

Results and Discussion

Intracellular Mn increases under Mn oxidizing conditions

To determine whether Mn(II) oxidation can play a role in Mn homeostasis, intracellular metal concentrations were determined for P. putida GB-1 and two non Mn oxidizing mutants of P. putida GB-1 (GB-1-007 and ∆2665 ∆2447). P. putida GB-1-007 was previously thought to have a mutation in the multicopper oxidase cumA gene which prevented Mn oxidation [34], but has since been found to have an additional mutation in a two component regulatory system sensor kinase which causes the non-oxidizing phenotype [13]. This two component system may regulate more genes than those involved in Mn oxidation as its regulon is currently unknown. P. putida ∆2665 ∆2447 is a double mutant with mutations in the mnxG and mcoA multicopper oxidase genes which are directly involved in catalyzing Mn oxidation [16]. All strains were grown on rich media commonly used for studying Mn oxidizers with and without added Mn (200 µM) for oxidizing and non-oxidizing conditions, respectively. The complex Lept media in the absence of additional Mn contained approximately 1 µM Mn as measured by ICP-MS. Cells were harvested during stationary phase when Mn oxides were most abundant. Mn, Fe, cobalt, copper, nickel, and zinc were determined by ICP-MS. Cobalt concentrations were below or just at the detection level (~0.01 nmoles/mg) in all strains and conditions. P. putida GB-1 showed a significant and greater than 1000 fold increase in intracellular Mn when grown in the presence of Mn (Table 1). There was also an increase in the intracellular concentrations of Fe, copper, nickel and zinc. When grown in the absence of added Mn, P. putida GB-1 had similar levels of Mn as P. putida KT2440 [25], but Fe levels were much higher (32.7 nmol/mg protein vs 6.8 nmol/mg protein). Although the non-oxidizing mutants also showed an increase in intracellular Mn when grown in media for Mn oxidation, the intracellular Mn concentration was significantly less than the wild type strain (1/5 for the GB-1-007 strain and 1/59 for the ∆2665 ∆2447 strain). Iron, copper, nickel, and zinc were largely unchanged in the mutant strains when grown in the presence or absence of Mn.
Table 1

Intracellular metal concentration.

Strain Growth Condition Mn (nmol/mg protein) Fe (nmol/mg protein) Cu (nmol/mg protein) Ni (nmol/mg protein) Zn (nmol/mg protein)
P. putida GB-1+ Mn27.6 (±11.6)43.1 (±5.56)0.427 (±0.054)0.054 (±0.008)2.02 (±0.154)
P. putida GB-1- Mn0.010 (±0.001)32.7 (±3.95)0.164 (±0.009)0.015 (±001)1.28 (±0.113)
P. putida ∆2665 ∆2447+ Mn0.466 (±0.041)16.4 (±1.11)0.178 (±0.003)BD1.20 (±0.018)
P. putida ∆2665 ∆2447- MnBD21.5 (±1.48)0.215 (±0.004)BD1.31 (±0.025)
P. putida GB-1-007+ Mn5.19 (±2.77)17.7 (±3.03)0.210 (±0.022)0.022 (±0.005)1.81 (±0.381)
P. putida GB-1-007- Mn0.052 (±0.031)22.8 (±3.72)0.169 (±0.012)0.017 (±0.006)1.43 (±0.108)

Standard deviation of three biological replicates in parentheses. BD = below detection.

Standard deviation of three biological replicates in parentheses. BD = below detection. The increase in Fe levels of wild type cells grown in Mn added conditions may be from Mn interfering with Fe requiring metabolism causing the cell to perceive Fe starvation. This is in line with other studies where high levels of Mn derepress Fe acquisition genes and repress Fe storage protein genes [29,39]. These findings suggest that when Mn levels are high, cells either need additional Fe or interpret high Mn as a low Fe condition. Alternatively, if Mn transporters are upregulated in response to Mn oxidation, transport of other divalent metals may also occur as many divalent transporters can have broad substrate specificity [40-42]. The increase in intracellular Mn also led to an increase in the intracellular Mn/Fe ratio (Table 2). This ratio may serve as an indicator of how well a cell may survive oxidative stress as Mn can potentially protect cells against oxidative stress and Fe can increase oxidative stress. Although intracellular Fe also increased in the presence of added Mn, it was to a much lesser extent than the increase in intracellular Mn. The increased Mn/Fe ratio was not as high as that found in Deinococcus radiodurans [25] (Table 2) which is known to have high intracellular Mn and low Fe, but the increase was significant.
Table 2

Intracellular Mn/Fe Ratios.

Strain (Growth media) Mn/Fe Reference
P. putida GB-1 (Lept + Mn)0.64This work
P. putida GB-1 (Lept – Mn)0.0003This work
P. putida ∆2665 ∆2447 (Lept + Mn)0.028This work
P. putida ∆2665 ∆2447 (Lept – Mn)BDThis work
P. putida GB1-007 (Lept + Mn)0.29This work
P. putida GB1-007 (Lept – Mn)0.002This work
P. putida KT2440 (complex media)<0.0001[25]
Deinococcus radiodurans (2.5 µM Mn in minimal media)2.5[25]
Deinococcus radiodurans (complex media)0.24[25]
Deinococcus geothermalis (complex media)0.46[25]

BD = Below Detection

BD = Below Detection Although the data illustrated that Mn oxidation can increase intracellular Mn, the mechanism is unknown. Mn oxidation may decrease efflux of Mn from the cell or it could be directly linked to uptake. Mn uptake transporters include NRAMP type MntH transporters, SitABC ABC-type transporters, and MntX transporters [43-45]. Although Mn transporters have not been experimentally identified in P. putida GB-1, there are candidate ABC type divalent metal transporters including PputGB1_2113-2115 and PputGB1_0132-0135. Coupling oxidation with transport has been demonstrated for Fe transport in yeast whereby the oxidation of Fe(II) to Fe(III) occurs using the multicopper oxidase Fet3p and ferric uptake transporter, Ftr1p [46,47]. Another possibility is that Mn uptake by the cell may occur as Mn(III). Mn oxides have been shown to accumulate extracellularly in P. putida GB-1 [17], thus Mn(III) uptake may compete with oxidation to Mn(IV) and could serve as a mechanism to decrease precipitation on the cell surface.

Fate of intracellular Mn

Because the significant increase in intracellular Mn may affect metallation of proteins, the association of Mn with cellular protein was determined. Mn has been shown to bind apoferritin [48], and proteins such as bacterioferritin may also bind Mn. The P. putida GB-1 genome does contain putative bacterioferritin encoding genes. High levels of Mn may also cause a conversion from Fe based metabolism to Mn based metabolism leading to additional Mn being associated with cellular protein, as such substitutions of Mn for Fe can protect enzymes with solvent exposed Fe cofactors from oxidative stress [49]. To address this, soluble cell free extract from Mn oxidizing cultures was separated into a greater than 3 kDa and a less than 3 kDa fraction. Proteins were retained in the greater than 3 kDa fraction. No protein was detected in the less than 3 kDa fraction. Approximately 10% of the Mn was present with the protein (Table 3). The majority of the Mn was present in the small molecule fraction, suggesting it was not associated with protein although it could be associated with small peptides or may have been released by especially labile proteins during sample preparation. In contrast, a significant amount of the iron was associated with the protein fraction. This suggests that the increased intracellular Mn is free aqueous Mn2+ (Mn(H2O)6 2+) or complexed with small molecules such as phosphates, small peptides, nucleotides, or organic acids. Nucleotides are one of the most abundant metabolites detected in a metabolite screen of closely related P. putida S12 [50]. In addition, organic acids were also detected [50], suggesting the P. putida GB-1 is likely to have small molecules available to complex Mn. The Mn levels determined for P. putida GB-1 were lower in cell extract compared to whole cells, and this is likely due to the oxidation and precipitation of Mn resulting from in vitro Mn oxidation [17] once the cells are broken.
Table 3

Intracellular Mn and Fe in total cell-free extracts, < 3K cell extract fraction, and > 3K cell extract fraction.

Mn Fe
Soluble cell-free extract4.95 ± 1.25 µM19.3 ± 1.78 µM
> 3K cell extract fraction0.54 ±0.15 µM7.62 ±0.96 µM
< 3K cell extract fraction4.11 ±1.13 µM6.13 ± 1.58 µM

± standard deviations from 3 biological replicates

± standard deviations from 3 biological replicates

Mn(II) oxidation protects cells

Mn(II) and Mn oxides have been shown to react with and scavenge both hydrogen peroxide and superoxide [51-54]. Several studies have identified an increase in protection against reactive oxygen species when cells have high intracellular Mn [55]. Two well-known examples would be Deinococcus radiodurans which uses Mn in combination with phosphate and peptides to protect protein from oxidative stress [25,56] and Lactobacillus plantarum which can functionally substitute high intracellular manganese for superoxide dismutase activity [57]. Therefore, the extent of oxidative stress under Mn oxidizing and non-oxidizing conditions was determined by examining cell survival and the level of protein carbonylation. Only hydrogen peroxide was used for oxidative stress survival studies as the superoxide generator paraquat can be metabolized by a P. putida strain [58], may not induce genes involved in oxidative protection [59], and did not kill the cells (data not shown). P. putida GB-1 was grown under Mn oxidizing (+100 µM Mn) and non-oxidizing conditions (no Mn addition) and then stressed with hydrogen peroxide. MSTP media was used to avoid the cell clumping common with the complex Lept media that led to poor reproducibility of CFU counts. P. putida GB-1 grown in the presence of Mn, produced Mn oxides, had higher intracellular Mn concentrations, and had survival levels greater than the Mn oxidizing mutants P. putida GB-1-007 and P. putida ∆2665 ∆2447 (Figure 1) when grown in the same Mn(II) containing media. The increase in survival correlates with the presence of Mn oxides and is not related to Mn(II) as the same extent of increased survival was not found with P. putida GB-1-007 and P. putida ∆2665 ∆2447. The increase in survival in the presence of Mn oxides may be related to the ability of Mn oxides to react with hydrogen peroxide [51] as Mn oxides were reduced upon the addition of hydrogen peroxide (data not shown).
Figure 1

Survival of P. putida following hydrogen peroxide stress.

P. putida GB-1, GB-1-007, and ∆2665 ∆2447 strains were exposed to 16.1 mM hydrogen peroxide for 30 minutes. Relative survival was calculated as the log10 of the percent survival rate of the oxidizing (+ Mn) culture divided by the percent survival rate of the non-oxidizing (-Mn) culture. The horizontal lines represent the mean value of the data sets. The mean relative survival of P. putida GB-1 is significantly higher than the mean relative survival of P. putida GB-1-007 and P. putida ∆2665 ∆2447 (P < 0.05, n=5) as determined by the Student’s t-test. Although the relative survival varied by experiment, P. putida GB1 consistently showed greater relative survival than the non-oxidizing mutants.

Survival of P. putida following hydrogen peroxide stress.

P. putida GB-1, GB-1-007, and ∆2665 ∆2447 strains were exposed to 16.1 mM hydrogen peroxide for 30 minutes. Relative survival was calculated as the log10 of the percent survival rate of the oxidizing (+ Mn) culture divided by the percent survival rate of the non-oxidizing (-Mn) culture. The horizontal lines represent the mean value of the data sets. The mean relative survival of P. putida GB-1 is significantly higher than the mean relative survival of P. putida GB-1-007 and P. putida ∆2665 ∆2447 (P < 0.05, n=5) as determined by the Student’s t-test. Although the relative survival varied by experiment, P. putida GB1 consistently showed greater relative survival than the non-oxidizing mutants. Protein carbonylation, an indicator of cellular oxidative damage, was determined for cells grown under Mn oxidizing (+Mn) and non oxidizing (-Mn) conditions. Protein was analyzed from stationary phase P. putida GB-1 in the absence of oxidative stress and following exposure to hydrogen peroxide and paraquat. In the absence of oxidative stress, protein from stationary phase cells grown under Mn oxidizing conditions had a slight decrease in protein carbonylation compared to non-oxidizing cultures (data not shown). But, there was no discernable difference in the amount of protein oxidation between Mn oxidizing (+Mn) and non-oxidizing (-Mn) conditions when cells were oxidatively stressed with hydrogen peroxide (0.6 mM) (Figure 2) or paraquat (5 mM). Higher concentrations of hydrogen peroxide (6mM, 60 mM) did not increase the extent of protein carbonylation.
Figure 2

Protein carbonylation following oxidative stress.

A) Oxyblot and B) Coomassie stained SDS-PAGE of hydrogen peroxide treated P. putida GB-1 grown under oxidizing (+Mn) and non-oxidizing (-Mn) conditions. Stationary phase cells were treated with 0.6 mM hydrogen peroxide for 30 minutes. The extent of protein carbonylation in cells oxidatively stressed in the presence or absence of Mn oxides was equivalent. Lane 1: negative control for non-oxidizing conditions; Lane 2,3: non-oxidizing conditions; Lane 4: Mn oxidizing negative control; Lane 5,6: Mn oxidizing conditions; Lane 7: Protein standard. The negative control was not derivatized with dinitrophenylhydrazine.

Protein carbonylation following oxidative stress.

A) Oxyblot and B) Coomassie stained SDS-PAGE of hydrogen peroxide treated P. putida GB-1 grown under oxidizing (+Mn) and non-oxidizing (-Mn) conditions. Stationary phase cells were treated with 0.6 mM hydrogen peroxide for 30 minutes. The extent of protein carbonylation in cells oxidatively stressed in the presence or absence of Mn oxides was equivalent. Lane 1: negative control for non-oxidizing conditions; Lane 2,3: non-oxidizing conditions; Lane 4: Mn oxidizing negative control; Lane 5,6: Mn oxidizing conditions; Lane 7: Protein standard. The negative control was not derivatized with dinitrophenylhydrazine. The lack of protein protection against ROS in Mn oxidizing cultures is somewhat unexpected, but there are several reasons why this may occur. The intracellular concentration of Mn may not be as important as the presence of specific ligands to complex Mn inside the cell [53,55-57,60-66]. The increase in intracellular Mn in Mn oxidizing P. putida GB-1 is also accompanied by an increase in intracellular Fe that can produce additional oxidative damage through Fenton chemistry. In addition, oxidative stress resistance or other regulatory and signaling pathways may be up or down regulated during Mn oxidation and increased intracellular Mn [65,67]. Thus, the survival benefit may not be related to intracellular Mn concentrations, but to the external reaction of Mn oxides with hydrogen peroxide. In summary, we have found an intriguing link between Mn oxidation and intracellular Mn levels. Our data suggests that Mn oxidation can affect Mn homeostasis and enhances the survival of cells experiencing hydrogen peroxide stress.
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