Polyphosphate-degrading enzymes in Acinetobacter spp. and activated sludge

Enzymatic properties of Myxococcus xanthus exopolyphosphatases mxPpx1 and mxPpx2

Myxococcus xanthus possesses two exopolyphosphatases, mxPpx1 and mxPpx2, which belong to the family of Ppx/GppA phosphatases; however, their catalytic properties have not been described. mxPpx1 and mxPpx2 contain 311 and 505 amino acid residues, respectively; mxPpx2 has an additional C-terminal region, which corresponds to the metal-dependent HDc phosphohydrolase domain. mxPpx1 mainly hydrolyzed short-chain polyPs (polyP₃ and polyP₄), whereas mxPpx2 preferred long-chain polyP_60-70 and polyP_700-1000. mxPpx2 was activated by 25-50 mM KCl, but mxPpx1 did not significantly depend on K⁺. In addition, mxPpx1 and mxPpx2 showed weak hydrolysis of ATP and GTP in the absence of K⁺, and mxPpx2 could also hydrolyze guanosine pentaphosphate (pppGpp) in the presence of K⁺. The exopolyphosphatase activity of mxPpx1 toward polyP₃ was inhibited by polyP_700-1000 and that of mxPpx2 toward polyP_60-70 and polyP_700-1000, by pyrophosphate. To clarify the function of the mxPpx2 C-terminal domain, it was fused to mxPpx1 (mxPpx1-2C) and deleted from mxPpx2 (mxPpx2∆C). Compared to wild-type mxPpx2, mxPpx2∆C had significantly reduced exopolyphosphatase activity toward long-chain polyPs (by 90%), whereas that toward polyP₃ and polyP₄ was much less affected; furthermore, the phosphohydrolase activity toward pppGpp, ATP, and GTP was also decreased (by 30-75%). In contrast, mxPpx1-2C had increased hydrolytic activity compared to mxPpx1. Furthermore, mxPpx2∆C lost the requirement for K⁺ characteristic for the wild-type enzyme, whereas mxPpx1-2C acquired it. These results suggest that the C-terminal domain of mxPpx2 is necessary for its maximum hydrolytic activity, especially toward long-chain polyPs, and defines mxPpx2 dependency on K⁺ for activation.

Catalytic activity profile of polyP:AMP phosphotransferase from Myxococcus xanthus

Myxococcus xanthus generates polyphosphates (polyPs) during starvation and forms fruiting bodies through the activity of polyphosphate kinase (Ppk). M. xanthus polyP:AMP phosphotransferase (Pap), a class II Ppk2, catalyzes the transfer of the terminal phosphate from polyP to AMP to yield ADP, but its enzymatic properties have not been investigated in detail. In this study, we found that Pap was activated by Mn²⁺ or Mg²⁺ and required higher concentrations of these ions in reactions with longer polyPs to demonstrate maximum activity. The K_m of Pap for polyP_700-1000 was significantly lower than that for shorter polyPs, but the highest catalytic constant (k_cat) was observed for polyP_60-70. When Pap was incubated with polyP_60-70 and AMP for 3 h, it first generated ADP and then gradually produced ATP, suggesting that M. xanthus Pap also has polyP:ADP phosphotransferase activity similar to that of class III Ppk2 enzymes. During starvation, the specific activity of Pap in M. xanthus was increased by 2.3-2.4-fold at days 1 and 2 of incubation. In addition, recombinant Pap in combination with M. xanthus recombinant enzymes Ppk1 or adenylate kinase (AdkA) could generate ATP from AMP and polyP_60-70. These results suggest a functional role of Pap during M. xanthus starvation, when it might act in cooperation with Ppk1 and/or AdkA to produce ATP from AMP, ADP, and polyP.

Simultaneous removal of nitrogen and phosphorous by heterotrophic nitrification-aerobic denitrification of a metal resistant bacterium Pseudomonas putida strain NP5

A novel strain NP5 with efficient heterotrophic nitrification, aerobic denitrification and phosphorus accumulation ability was isolated and identified as Pseudomonas putida strain NP5. The removed ammonium and phosphate were mainly converted into intracellular components by assimilation, and negligible nitrification intermediates and N₂O were accumulated during heterotrophic nitrification. In addition, the optimal conditions for nutrient removal were: succinate as carbon source, C/N 10, P/N 0.2, temperature 30 °C, salinity 0% and shaking speed 160 rpm. Besides, strain NP5 possessed an exceptional heavy metal and nanoparticles resistance. Cr⁶⁺ was found to be the most toxic among the tested metals, and it could be removed simultaneously. Moreover, an obvious phosphorus release was observed under anaerobic condition, and repeated exposure to the anaerobic/aerobic conditions could significantly improve the nutrient removal. Furthermore, the successful expression of key enzymes for nitrogen and phosphorous removal provided additional evidence for possibility of simultaneous nitrification, denitrification and phosphorus removal.

Removal of phosphate by Staphylococcus aureus under aerobic and alternating anaerobic-aerobic conditions

Eutrophication of water bodies due to phosphate enrichment is an ecological problem. Phosphate is removed from wastewaters by enhanced biological phosphate removal worldwide by phosphate accumulating organism. In order to understand the process of treatment, the existing microbial community and its metabolism of phosphate removal are studied widely. This study focuses on the isolation of polyphosphate-accumulating bacteria from different environments and studying their phosphate removal capacity with different carbon supplements under varying culture conditions. The total heterotrophic bacterial population from the diverse environments showed the existence of phosphate-accumulating bacteria. Among them, Staphylococcus aureus removed 81% of phosphate in a polyphosphate-accumulating medium with storage of 93 mM polyphosphate internally. Among the different carbon sources provided, glucose induced a net specific growth rate of 0.816/d. S. aureus removed 70% of phosphate with a phosphate uptake rate of 6.29 mg PO₄/g cells and a growth yield of 0.2 g cells/g glucose consumed when 1 g/L glucose was provided. Furthermore, when 2 g/L glucose was provided, 78% of phosphate was removed with a phosphate uptake rate of 13.24 mg PO₄/g cells and a growth yield of 0.4 g cells/g glucose consumed under aerobic condition. S. aureus showed enhanced phosphate removal under aerobic condition in the presence of glucose.

Performance of wastewater biological phosphorus removal under long-term exposure to CuNPs: adapting toxicity via microbial community structure adjustment

Copper nanoparticles (CuNPs) have been used in a wide range of applications, and the released CuNPs entering wastewater treatment plants (WWTP) might pose potential risks to the wastewater biological treatment process, such as phosphorus removal.

Multilevel correlations in the biological phosphorus removal process: From bacterial enrichment to conductivity-based metabolic batch tests and polyphosphatase assays

Enhanced biological phosphorus removal (EBPR) from wastewater relies on the preferential selection of active polyphosphate-accumulating organisms (PAO) in the underlying bacterial community continuum. Efficient management of the bacterial resource requires understanding of population dynamics as well as availability of bioanalytical methods for rapid and regular assessment of relative abundances of active PAOs and their glycogen-accumulating competitors (GAO). A systems approach was adopted here toward the investigation of multilevel correlations from the EBPR bioprocess to the bacterial community, metabolic, and enzymatic levels. Two anaerobic-aerobic sequencing-batch reactors were operated to enrich activated sludge in PAOs and GAOs affiliating with "Candidati Accumulibacter and Competibacter phosphates", respectively. Bacterial selection was optimized by dynamic control of the organic loading rate and the anaerobic contact time. The distinct core bacteriomes mainly comprised populations related to the classes Betaproteobacteria, Cytophagia, and Chloroflexi in the PAO enrichment and of Gammaproteobacteria, Alphaproteobacteria, Acidobacteria, and Sphingobacteria in the GAO enrichment. An anaerobic metabolic batch test based on electrical conductivity evolution and a polyphosphatase enzymatic assay were developed for rapid and low-cost assessment of the active PAO fraction and dephosphatation potential of activated sludge. Linear correlations were obtained between the PAO fraction, biomass specific rate of conductivity increase under anaerobic conditions, and polyphosphate-hydrolyzing activity of PAO/GAO mixtures. The correlations between PAO/GAO ratios, metabolic activities, and conductivity profiles were confirmed by simulations with a mathematical model developed in the aqueous geochemistry software PHREEQC.

The impacts of silver nanoparticles and silver ions on wastewater biological phosphorous removal and the mechanisms

The effects of AgNPs and Ag+ (0-5 mg/L) on wastewater enhanced biological phosphorus removal (EBPR) were investigated. The phosphorus removal efficiency was maintained at 99% no matter what the concentrations of AgNPs were, but it was decreased to 48.8% at Ag+ of 1 mg/L, and no net phosphorus was removed at Ag+ greater than 2 mg/L in the batch tests. The uptake of wastewater carbon source and the anaerobic and aerobic transformations of phosphorus, polyhydoxyalkanoates and glycogen were inhibited by Ag+ other than AgNPs. Ag+ showed stronger toxicity on polyphosphate accumulating organisms (PAOs) than glycogen accumulating organisms (GAOs). Further investigation revealed that the decrease in anaerobic phosphorus release by Ag+ was caused by the inhibition on the activities of adenylate kinase and expolyphosphatase, whereas the decrease in aerobic phosphorus uptake was due to the suppression in energy generation for phosphorus uptake. However, the presence of either AgNPs or Ag+ did not lead to cell leakage and membrane damage.

Impact of Cr(VI) on P removal performance in enhanced biological phosphorus removal (EBPR) system based on the anaerobic and aerobic metabolism

Influence of Cr(VI) on P removal in enhanced biological phosphorus removal (EBPR) system was investigated with respect to the composition of poly-phosphate-accumulating organisms (PAOs) and glycogen accumulating organisms (GAOs), the transformation of poly-β-hydroxyalkanoates (PHA) and glycogen, enzymes' activities, and the intracellular Cr. Whether EBPR system could revive after Cr(VI) shock was also explored. Results showed P removal performance was completely inhibited by Cr(VI) with the concentration more than 5 mg L(-1). PAOs were more sensitive to Cr(VI) than GAOs and the other bacteria were. PHA consumption, glycogen synthesis and adenylate kinase's activity had been inhibited by 5 mg L(-1) Cr(VI). Both adenylate kinase's activity and P removal efficiency were negatively correlated with the intracellular Cr. Recovery experiments revealed that P removal performance with 5 mg L(-1) Cr(VI) shock could revive after a 2-day recovery treatment, while systems with high level Cr(VI) (20 and 60 mg L(-1)) shock could not.

Multiple mechanisms of uranium immobilization by Cellulomonas sp. strain ES6

Removal of hexavalent uranium (U(VI)) from aqueous solution was studied using a Gram-positive facultative anaerobe, Cellulomonas sp. strain ES6, under anaerobic, non-growth conditions in bicarbonate and PIPES buffers. Inorganic phosphate was released by cells during the experiments providing ligands for formation of insoluble U(VI) phosphates. Phosphate release was most probably the result of anaerobic hydrolysis of intracellular polyphosphates accumulated by ES6 during aerobic growth. Microbial reduction of U(VI) to U(IV) was also observed. However, the relative magnitudes of U(VI) removal by abiotic (phosphate-based) precipitation and microbial reduction depended on the buffer chemistry. In bicarbonate buffer, X-ray absorption fine structure (XAFS) spectroscopy showed that U in the solid phase was present primarily as a non-uraninite U(IV) phase, whereas in PIPES buffer, U precipitates consisted primarily of U(VI)-phosphate. In both bicarbonate and PIPES buffer, net release of cellular phosphate was measured to be lower than that observed in U-free controls suggesting simultaneous precipitation of U and PO₄³⁻. In PIPES, U(VI) phosphates formed a significant portion of U precipitates and mass balance estimates of U and P along with XAFS data corroborate this hypothesis. High-resolution transmission electron microscopy (HR-TEM) and energy dispersive X-ray spectroscopy (EDS) of samples from PIPES treatments indeed showed both extracellular and intracellular accumulation of U solids with nanometer sized lath structures that contained U and P. In bicarbonate, however, more phosphate was removed than required to stoichiometrically balance the U(VI)/U(IV) fraction determined by XAFS, suggesting that U(IV) precipitated together with phosphate in this system. When anthraquinone-2,6-disulfonate (AQDS), a known electron shuttle, was added to the experimental reactors, the dominant removal mechanism in both buffers was reduction to a non-uraninite U(IV) phase. Uranium immobilization by abiotic precipitation or microbial reduction has been extensively reported; however, the present work suggests that strain ES6 can remove U(VI) from solution simultaneously through precipitation with phosphate ligands and microbial reduction, depending on the environmental conditions. Cellulomonadaceae are environmentally relevant subsurface bacteria and here, for the first time, the presence of multiple U immobilization mechanisms within one organism is reported using Cellulomonas sp. strain ES6.

A novel ATP regeneration system using polyphosphate-AMP phosphotransferase and polyphosphate kinase

Polyphosphate-AMP phosphotransferase (PAP) and polyphosphate kinase (PPK) were used for designing a novel ATP regeneration system, named the PAP-PPK ATP regeneration system. PAP is an enzyme that catalyzes the phospho-conversion of AMP to ADP, and PPK catalyzes ATP formation from ADP. Both enzymes use inorganic polyphosphate [poly(P)] as a phosphate donor. In the PAP-PPK ATP regeneration system, ATP was continuously synthesized from AMP by the coupling reaction of PAP and PPK using poly(P). Poly(P) is a cheap material compared to acetyl phosphate, phosphoenol pyruvate and creatine phosphate, which are phosphate donors used for conventional ATP regeneration systems. To achieve efficient synthesis of ATP from AMP, an excessive amount of poly(P) should be added to the reaction solution because both PAP and PPK consume poly(P) as a phosphate donor. Using this ATP generation reaction, we constructed the PAP-PPK ATP regeneration system with acetyl-CoA synthase and succeeded in synthesizing acetyl-CoA from CoA, acetate and AMP. Since too much poly(P) may chelate MG2+ and inhibit enzyme activity, the Mg2+ concentration was optimized to 24 mM in the presence of 30 mM poly(P) in the reaction. In this reaction, ATP was regenerated 39.8 times from AMP, and 99.5% of CoA was converted to acetyl-CoA. In addition, since the PAP-PPK ATP regeneration system can regenerate GTP from GMP, it could also be used as a GTP regeneration system.

Polyphosphate synthetic activity of polyphosphate:AMP phosphotransferase in Acinetobacter johnsonii 210A

Polyphosphate:AMP phosphotransferase (PAP) has been identified as an enzyme that catalyzes the phosphorylation of AMP with inorganic polyphosphates [poly(P)] as phosphate donors. We found that the purified PAP of Acinetobacter johnsonii 210A has poly(P) synthetic activity. The PAP catalyzes the dephosphorylation of ADP and processively synthesizes poly(P) of 200 to 700 residues. Comparatively lower concentrations of MgCl(2) (20 mM) were required to obtain optimum poly(P) synthetic activity, whereas higher concentrations of MgCl(2) (100 mM) were necessary for optimum PAP activity. ADP is preferred over GDP as a phosphate donor for poly(P) synthesis. The K(m) and V(max) values for ADP in the poly(P) synthetic activity of PAP were 8.3 mM and 55 micromol min(-1) mg(-1), respectively. We concluded that the PAP of A. johnsonii 210A is a novel type of poly(P) kinase that uses ADP and GDP as substrates.

The microbiology of biological phosphorus removal in activated sludge systems

Activated sludge systems are designed and operated globally to remove phosphorus microbiologically, a process called enhanced biological phosphorus removal (EBPR). Yet little is still known about the ecology of EBPR processes, the microbes involved, their functions there and the possible reasons why they often perform unreliably. The application of rRNA-based methods to analyze EBPR community structure has changed dramatically our understanding of the microbial populations responsible for EBPR, but many substantial gaps in our knowledge of the population dynamics of EBPR and its underlying mechanisms remain. This review critically examines what we once thought we knew about the microbial ecology of EBPR, what we think we now know, and what still needs to be elucidated before these processes can be operated and controlled more reliably than is currently possible. It looks at the history of EBPR, the currently available biochemical models, the structure of the microbial communities found in EBPR systems, possible identities of the bacteria responsible, and the evidence why these systems might operate suboptimally. The review stresses the need to extend what have been predominantly laboratory-based studies to full-scale operating plants. It aims to encourage microbiologists and process engineers to collaborate more closely and to bring an interdisciplinary approach to bear on this complex ecosystem.

Polyphosphate kinase from activated sludge performing enhanced biological phosphorus removal

A novel polyphosphate kinase (PPK) was retrieved from an uncultivated organism in activated sludge carrying out enhanced biological phosphorus removal (EBPR). Acetate-fed laboratory-scale sequencing batch reactors were used to maintain sludge with a high phosphorus content (approximately 11% of the biomass). PCR-based clone libraries of small subunit rRNA genes and fluorescent in situ hybridization (FISH) were used to verify that the sludge was enriched in Rhodocyclus-like beta-Proteobacteria known to be associated with sludges carrying out EBPR. These organisms comprised approximately 80% of total bacteria in the sludge, as assessed by FISH. Degenerate PCR primers were designed to retrieve fragments of putative ppk genes from a pure culture of Rhodocyclus tenuis and from organisms in the sludge. Four novel ppk homologs were found in the sludge, and two of these (types I and II) shared a high degree of amino acid similarity with R. tenuis PPK (86 and 87% similarity, respectively). Dot blot analysis of total RNA extracted from sludge demonstrated that the Type I ppk mRNA was present, indicating that this gene is expressed during EBPR. Inverse PCR was used to obtain the full Type I sequence from sludge DNA, and a full-length PPK was cloned, overexpressed, and purified to near homogeneity. The purified PPK has a specific activity comparable to that of other PPKs, has a requirement for Mg(2+), and does not appear to operate in reverse. PPK activity was found mainly in the particulate fraction of lysed sludge microorganisms.

In vitro ATP regeneration from polyphosphate and AMP by polyphosphate:AMP phosphotransferase and adenylate kinase from Acinetobacter johnsonii 210A

In vitro enzyme-based ATP regeneration systems are important for improving yields of ATP-dependent enzymatic reactions for preparative organic synthesis and biocatalysis. Several enzymatic ATP regeneration systems have been described but have some disadvantages. We report here on the use of polyphosphate:AMP phosphotransferase (PPT) from Acinetobacter johnsonii strain 210A in an ATP regeneration system based on the use of polyphosphate (polyP) and AMP as substrates. We have examined the substrate specificity of PPT and demonstrated ATP regeneration from AMP and polyP using firefly luciferase and hexokinase as model ATP-requiring enzymes. PPT catalyzes the reaction polyP(n) + AMP --> ADP + polyP(n-1). The ADP can be converted to ATP by adenylate kinase (AdK). Substrate specificity with nucleoside and 2'-deoxynucleoside monophosphates was examined using partially purified PPT by measuring the formation of nucleoside diphosphates with high-pressure liquid chromatography. AMP and 2'-dAMP were efficiently phosphorylated to ADP and 2'-dADP, respectively. GMP, UMP, CMP, and IMP were not converted to the corresponding diphosphates at significant rates. Sufficient AdK and PPT activity in A. johnsonii 210A cell extract allowed demonstration of polyP-dependent ATP regeneration using a firefly luciferase-based ATP assay. Bioluminescence from the luciferase reaction, which normally decays very rapidly, was sustained in the presence of A. johnsonii 210A cell extract, MgCl(2), polyP(n=35), and AMP. Similar reaction mixtures containing strain 210A cell extract or partially purified PPT, polyP, AMP, glucose, and hexokinase formed glucose 6-phosphate. The results indicate that PPT from A. johnsonii is specific for AMP and 2'-dAMP and catalyzes a key reaction in the cell-free regeneration of ATP from AMP and polyP. The PPT/AdK system provides an alternative to existing enzymatic ATP regeneration systems in which phosphoenolpyruvate and acetylphosphate serve as phosphoryl donors and has the advantage that AMP and polyP are stabile, inexpensive substrates.

Regulation of polyphosphate kinase gene expression in Acinetobacter baumannii 252

A strain of Acinetobacter baumannii cultured in butyric acid media was found to take up phosphate following a period of phosphate release. PCR was used to clone the polyphosphate kinase (ppk) gene from the strain. The promoter for the ppk gene was functional in the heterologous Escherichia coli host. Using RT-PCR, transcription of the ppk gene was found to be regulated by phosphate concentration.

Anaerobic phosphate release from activated sludge with enhanced biological phosphorus removal. A possible mechanism of intracellular pH control

The biochemical mechanisms of the wastewater treatment process known as enhanced biological phosphorus removal (EBPR) are presently described in a metabolic model. We investigated details of the EBPR model to determine the nature of the anaerobic phosphate release and how this may be metabolically associated with polyhydroxyalkanoate (PHA) formation. Iodoacetate, an inhibitor of glycolysis, was found to inhibit the anaerobic formation of PHA and phosphate release, supporting the pathways proposed in the EBPR metabolic model. In the metabolic model, it is proposed that polyphosphate degradation provides energy for the microorganisms in anaerobic regions of these treatment systems. Other investigations have shown that anaerobic phosphate release depends on the extracellular pH. We observed that when the intracellular pH of EBPR sludge was raised, substantial anaerobic phosphate release was caused without volatile fatty acid (VFA) uptake. Acidification of the sludge inhibited anaerobic phosphate release even in the presence of VFA. From these observations, we postulate that an additional possible role of anaerobic polyphosphate degradation in EBPR is for intracellular pH control. Intracellular pH control may be a metabolic feature of EBPR, not previously considered, that could have some use in the control and optimisation of EBPR. Copyright 1999 John Wiley & Sons, Inc.

New aspects of inorganic polyphosphate metabolism and function

The review analyzes the results of recent studies on the biochemistry of high-molecular inorganic poly-phosphates (PolyPs). The data obtained lead to the following main conclusions. PolyPs are polyfunctional compounds. The main role of PolyPs is their participation in the regulation of metabolism both at the genetic and metabolic levels. Among the functions of PolyPs known at present, the most important are the following: phosphate and energy storage; regulation of the levels of ATP and other nucleotide and nucleoside-containing coenzymes; participation in the regulation of homeostasis and storage of inorganic cations and other positively charged solutes in an osmotically inert form; participation in membrane transport processes mediated by poly-beta-Ca2+-hydroxybutyrate complexes; participation in the formation and functions of cell surface structures; control of gene activity; and regulation of activities of the enzymes and enzyme assemblies involved in the metabolism of nucleic acids and other acid biopolymers. However, the functions of PolyPs vary among organisms of different evolutionary levels. The metabolism and functions of PolyPs in each cellular compartment of procaryotes (cell wall, plasma membrane, cytosol) and eucaryotes (nuclei, vacuoles, mitochondria, plasma membrane, cell wall, mitochondria, cytosol) are unique. The synthesis and degradation of PolyPs in the organelles of eucaryotic cells are possibly mediated by different sets of enzymes. This is consistent with of the endosymbiotic hypothesis of eucaryotic cell origin. Some aspects of the biochemistry of high-molecular PolyPs are considered to be of great significance to the approach to biotechnological, ecological and medical problems.

Biology of polyphosphate-accumulating bacteria involved in enhanced biological phosphorus removal

Recent research on the process of biological phosphorus removal in lab-scale treatment systems has indicated that: (i) the development of an actively polyP-accumulating bacterial community after the introduction of an anaerobic period may take at least 4 months; (ii) up to 80% of all aerobic bacteria isolated from these communities are able to accumulate polyP; (iii) polyP synthesized by the bacterial communities of lab-scale treatment systems is probably mainly low polymeric, not exceeding 20 P-residues, and this polyP is rapidly degraded during the anaerobic period; (iv) the enzymatic hydrolysis of polyP under anaerobic conditions is accompanied by PHB formation from exogenous acetate, reducing equivalents are provided by the degradation of carbohydrates; and (v) nitric oxide inhibits the release of phosphate under anaerobic conditions in Renpho and F&D sludges. Bacteria belonging to the genus Acinetobacter occur in a wide variety of activated sludges in which enhanced biological phosphate removal is observed. A. johnsonii 210A was studied in detail with respect to the elemental composition of polyP granules, the enzymatic synthesis and degradation of polyP, the regulation of polyP metabolism, and the transport of phosphate. A. johnsonii 210A reflects activated sludge in a number of ways as far as polyP metabolism is concerned but its polyP is highly polymeric and the phosphate efflux rate under anaerobic conditions is relatively low and not increased by exogenous acetate. In addition to Acinetobacter, other polyP-accumulating microorganisms may be involved in biological phosphorus removal. The isolation of polyP-accumulating denitrifying bacteria may well have interesting implications for a new process design in wastewater treatment systems. Further studies on the enzymes involved in polyP biosynthesis and on the uptake and efflux systems of phosphate, potassium, magnesium and lower fatty acids in pure cultures will enlarge our insight in the energetics of the metabolism of polyP. In addition, the regulation of the metabolism of polyP-accumulating organisms needs to be studied in more detail.

Characterization of two phosphate transport systems in Acinetobacter johnsonii 210A

The transport of P(i) was characterized in Acinetobacter johnsonii 210A, which is able to accumulate an excessive amount of phosphate as polyphosphate (polyP) under aerobic conditions. P(i) is taken up against a concentration gradient by energy-dependent, carrier-mediated processes. A. johnsonii 210A, grown under P(i) limitation, contains two uptake systems with Kt values of 0.7 +/- 0.2 microM and 9 +/- 1 microM. P(i) uptake via the high-affinity component is drastically reduced by N,N'-dicyclohexylcarbodiimide, an inhibitor of H(+)-ATPase, and by osmotic shock. Together with the presence of P(i)-binding activity in concentrated periplasmic protein fractions, these results suggest that the high-affinity transport system belongs to the group of ATP-driven, binding-protein-dependent transport systems. Induction of this transport system upon transfer of cells grown in the presence of excess P(i) to P(i)-free medium results in a 6- to 10-fold stimulation of the P(i) uptake rate. The constitutive low-affinity uptake system for P(i) is inhibited by uncouplers and can mediate counterflow of P(i), indicating its reversible, secondary nature. The presence of an inducible high-affinity uptake system for P(i) and the ability to decrease the free internal P(i) pool by forming polyP enable A. johnsonii 210A to reduce the P(i) concentration in the aerobic environment to micromolar levels. Under anaerobic conditions, polyP is degraded again and P(i) is released via the low-affinity secondary transport system.

Properties of polyphosphatase of Acinetobacter johnsonii 210A

Polyphosphatase, an enzyme which hydrolyses highly polymeric polyphosphates to Pi, was purified 77-fold from Acinetobacter johnsonii 210A by Q-Sepharose, hydroxylapatite and Mono-Q column chromatography. The native molecular mass estimated by gel filtration and native gel electrophoresis was 55 kDa. SDS-polyacrylamide gel electrophoresis indicated that polyphosphatase of Acinetobacter johnsonii 210A is a monomer. The enzyme was specific for highly polymeric polyphosphates and showed no activity towards pyrophosphate and organic phosphate esters. The enzyme was inhibited by iodoacetamide and in the presence of 10 mM Mg2+ by pyro- and triphosphate. The apparent Km-value for polyphosphate with an average chain length of 64 residues was 5.9 microM and for tetraphosphate 1.2 mM. Polyphosphate chains were degraded to short chain polymers by a processive mechanism. Polyphosphatase activity was maximal in the presence of Mg2+ and K+.

Properties of polyphosphate: AMP phosphotransferase of Acinetobacter strain 210A

Polyphosphate:AMP phosphotransferase, an enzyme which catalyzes the phosphorylation of AMP to ADP at the expense of polyphosphate, was purified more than 1,500-fold from Acinetobacter strain 210A by streptomycin sulfate precipitation and by Mono-Q, Phenyl Superose, and Superose column chromatography. Streptomycin sulfate precipitation appeared to be an effective step in the purification procedure. During the following chromatographic steps, there was a 29-fold increase in specific activity but the yield was low (0.3%). Kinetic studies showed apparent Km values of 0.26 mM for AMP and 0.8 microM for polyphosphate with an average chain length of 35 phosphate groups. The highest activities were found with polyphosphate molecules of 18 to 44 phosphate residues. The polyphosphate chain was degraded completely to ADP. The mechanism of degradation is processive. No activity was obtained with ortho-, pyro-, tri-, and tetraphosphate. The enzyme was inhibited by pyro-, tri-, and tetraphosphate. The inhibition by tri- and tetraphosphate was mixed with polyphosphate as a substrate. The inhibition constants for the dissociation of the enzyme-inhibitor complex and for the enzyme-inhibitor-substrate complex were 0.9 and 6.5 mM, respectively, for triphosphate and 0.7 and 1.5 mM, respectively, for tetraphosphate.