FEMS Microbiology Letters 121 (1994) 141-146 © 1994 Federation of European Microbiological Societies 0378-1097/94/$07.00 Published by Elsevier 141 FEMSLE 06102 Phosphatase-mediated heavy metal accumulation by a Citrobacter sp. and related enterobacteria L.E. Macaskie *, K.M. B o n t h r o n e and D.A. R o u c h 1 School of Biological Sciences, The Unit,ersity of Birmingham, Edgbaston, Birmingham B15 2T7] UK (Received 6 May 1994; revision received 1 June 1994; accepted 3 June 1994) Abstract: A Citrobacter sp. was reported previously to accumulate heavy metals as cell-bound heavy metal phosphates. Metal uptake is mediated by the activity of a periplasmic acid-type phosphatase that liberates inorganic phosphate to provide the precipitant ligand for heavy metals presented to the cells. Amino acid sequencing of peptide fragments of the purified enzyme revealed significant homology to the phoN product (acid phosphatase) of some other enterobacteria. These organisms, together with Klebsiella pneumoniae, previously reported to produce acid phosphatase, were tested for their ability to remove uranium and lanthanum from challenge solutions supplemented with phosphatase substrate. The coupling of phosphate liberation to metal bioaccumulation was limited to the metal accumulating Citrobacter sp.; therefore the participation of species-specific additional factors in metal bioaccumulation was suggested. Key words: Citrobacter sp.; Salmonella typhimurium; Morganella morganii; Providencia stuartii; Klebsiella pneumoniae; Phosphatase; PhoN; Heavy metal accumulation Introduction A strain of a species of Citrobacter, isolated from metal-polluted soil [1] was resistant to cadmium and accumulated this and other metals as ceil-bound metal phosphates [2-4]. Metal accumulation is mediated by an acid-type phosphatase which liberates inorganic phosphate (HPO42-) from a suitable substrate molecule, with stoichiometric precipitation of metal phosphates as cell- * Corresponding author. Tel: (021) 414-5889; Fax: (021) 4146557. i Present address: New Chemistry Laboratory, The University of Oxford, South Parks Road, Oxford OX1 3QT, UK SSDI 0 3 7 8 - 1 0 9 7 ( 9 4 ) 0 0 2 5 3 - N bound MHPO 4 ([3,4]; M = heavy metal cation). This reaction has been harnessed to the continuous removal of heavy metals from challenge solutions presented to immobilized cells held within a flow-through column [2]; application to the decontamination of metal-laden industrial wastes has been suggested [2]. The insensitivity of the acid-type phosphatase to cadmium [5,6] and some other heavy metals [61, together with the ability of growing cells to accumulate Cd [7], suggests that metal accumulation may have evolved as a resistance mechanism whereby metals are desolubilized away from cellular sensitive sites; indeed, lead was accumulated extensively by another Citrobacter sp. isolated from a metal-contaminated soil [8], while strains 142 of Citrobacter freundii obtained from a culture collection gave only low phosphatase activity and very little metal bioaccumulation (D. Montgomery, A.C.R. Dean and L.E. Macaskie, unpublished). The acid-type phosphatase has been purified to homogeneity [6,9] and extensively characterized [6]. During this earlier study peptide mapping was done, and amino acid sequences of the peptide fragments were obtained [6]. A significant homology was seen with some of the sequences of the phoN product (acid phosphatase) of some other enterobacteria (this investigation). It might be anticipated that these enterobacterial species would also accumulate heavy metals and may find a similar application in metal waste treatment bioprocesses. These organisms, together with Klebsiella pneumoniae (previously Kl. (Aerobacter) aerogenes) with reported acid phosphatase activity [10], were tested for their ability to accumulate uranium and lanthanum from challenge solutions. Materials and Methods Citrobacter sp. strain N14 was isolated from metal-polluted soil [1], and was as described previously [11]. The phosphatase deficient mutant lp4a was as described previously; phosphatase deficiency was confirmed by immunogold labelling experiments [6]. Strains of Salmonella typhimurium were a gift from Dr. J. Stephen (School of Biological Sciences, University of Birmingham). Other enterobacteria ( Klebsiella pneumoniae subsp, pneumoniae NCIMB 8806, Morganella morganii NCIMB 10466 and Providencia rettgeri NCIMB 10457) were from the National Collection of Industrial and Marine Bacteria (Aberdeen, Scotland). The organisms were routinely grown in glycerol-glycerol 2-phosphate minimal medium as described previously [11]; in this case phosphatase activity assists in the utilization of glycerol 2-phosphate as the sole phosphorus source. The growth temperature was 30°C (Citrobacter sp., M. morganii, P. rettgeri, KI. pneumoniae) or 37°C (S. typhimurium, Kl. pneumoniae); with the latter strain similar results were obtained at both temperatures. M. morganii and some strains of S. typhimurium grew poorly in the minimal medium; yeast extract (Difco) was routinely incorporated to 0.1% (wt/vol), as appropriate. For determination of phosphatase activity, samples were removed from mid-logarithmic phase cultures (after 3-4 generations: OD at 600 nm (OD600) = 0.30.4) or from overnight cultures, as specified, and the phosphatase activity was determined by the liberation of p-nitrophenol from p-nitrophenyl phosphate, as described previously [11]. Although the pH optimum of acid phosphatase is typically in the region of 5.0-6.5 [6], this is extended to pH 7.0 in whole cells [12]; phosphatase activity was assayed at the latter pH since this is the pH of maximum metal accumulation [12]. The Citrobacter phosphatase was purified to homogeneity via ammonium sulphate fractionation, ion exchange chromatography (SP-Sephadex C50 cation exchange and QAE Sephadex A-50 anion exchange), hydroxyapatite separation and chromatography using phenyl sepharose as described previously [6,9]. Enzyme purity was confirmed by sodium dodecyl sulphate-polyacrylamide gel electrophoresis, and immunoblotting [6]. Amino acid sequencing of peptide fragments was done commercially (Department of Biochemistry, University of Oxford, UK) using an Applied Biosystems (ABI) 470 A protein sequencer with on-line analysis (PTH analyser) using the standard 03CPTH program from Applied Biosystems. Data analysis utilized 'Export Ease' software from Millipore (UK) Ltd. For evaluation of the metal uptake capacity of the Citrobacter sp. and other enterobacteria, cultures were harvested as for the phosphatase assay, washed in isotonic saline (8.5 g / l of NaC1) and resuspended at an OD60o of 0.3-0.4 in metal challenge solution (2 mM citrate buffer/20 mM MOPS (3-[morpholino]propanesulfonic acid)NaOH buffer, pH 7, supplemented with either 1 mM uranyl nitrate or lanthanum nitrate (B.D.H. Ltd.)). The suspensions were shaken gently for 6 h or 18-24 h as specified, and the residual metal in the supernatant of centrifuged samples was determined by assay. Uranyl ion (UO 2+) and lanthanum were assayed using arsenazo III by a modification of the 143 method of Fritz and Bradford [13]. A saturated solution of arsenazo I I I was p r e p a r e d by the addition of 0.038 g of arsenazo I I I (B.D.H. Ltd.) to 25 ml of distilled water (1 h, with stirring) and filtration through W h a t m a n No 1 filter paper. Metal challenge solution or spent supernatant was diluted 20-fold (uranyl ion) or 10-fold (lanthanum) in metal-unsupplemented challenge solution to a total volume of 2 ml. The samples were acidified (0.3 ml of 0.75 M HC1), 0.1 ml of arsenazo III solution was added and the bluemauve metal-arsenazo III complex was visualized and quantified at A652. Metal removal was expressed as a percentage of the initial metal in the challenge solution. Some experiments utilized immobilized cells. Five g wet weight of Citrobacter sp. N14 or P. rettgeri N C I M B 10457 was immobilized in polyacrylamide gel as described previously [9,12]. Each preparation provided material for five replicate columns of volume 25 ml (approx). The columns were challenged with metal-supplemented flows (composition as above) with metal removal determined by assay and comparison with the input solution. Strains of Morganella, Providencia and Salmonella were obtained and examined for phosphatase activity and metal bioaccumulation. A strain of Klebsiella pneumoniae was also tested. Although not apparently containing nueleotide sequences that hybridize to phoN [16], substantial biochemical evidence was found for acid phosphatase activity in this species [10]. Conversely, the Citrobacter sp. N14 clearly contains a PhoN-type phosphatase (Fig. 1), but no evidence for hybridization of Salmonella phoN fragments to D N A from the related C. freundii was found [16]. Various enterobacteria were screened for phosphatase activity and ability to accumulate La 3+ and U O 2+ as shown in Table 1. As reported previously [11] the phosphatase activity of Citrobacter sp. N14 was highly variable. T h r e e high-activity cultures removed most of the presented metals, while the phosphatase-deficient mutant lp4a removed no UOzz÷ but some La 3+. This control established that at least some of the lanthanum uptake was attributable to non-specific binding, or to precipitation on the cells. Low-activity cultures of strain N14 removed more than 85% of the presented La 3+ and 2 5 - 5 0 % of the UO22+ after 18-24 h. None of the other entero- Results The amino acid sequence of five peptide fragments of purified Citrobacter sp. N14 acid phosphatase was c o m p a r e d with known polypeptide sequences using the ' S W E E P ' program [14] to search the O W L composite database, release 17.0 [14]. Highly significant alignments were seen between two of the fragments (1 and 3) with the phoN product of Morganella morganii, Providencia stuartii [16] and Salmonella typhimurium [17] (Fig. 1). These strong similarities indicate the Citrobacter enzyme to be a class PhoN phosphatase; the low similarities of fragments 2, 4 and 5 are consistent with the expected evolutionary divergence among these enzymes. The PhoN protein of S. typhimurium was identified as a nonspecific acid phosphatase of subunit molecular mass of 26 k D a [17,18], which is similar to the the subunit molecular mass of the Citrobacter phosphatase h o m o t e t r a m e r (27 kDa; [6]). c i t r o b a c t e r sp. NI4 [FI] M. morganii P. stuartii S. typhimurium Consensus C i t r o b a c t e r sp. NI4 [F2) M. morganii P. stuartii S. typhimuriu2n Consensus c i t r o b a c r e r sp. NI4 IF4] M. morganii P. stuartii S. typhimurium Consensus AR~'PDFY%q~KEAQSXDSLSIdSPPPPAVDSIDI'U~D 25 G N D A % ~ g K P D L ~ E Q A X D S L K I , L p p I ~ E U G S Z Q I m . A I D 63 25 GNDV'I"~KPDLY'~51~SQAIDSIJ~Id~PPPPEVGSILI~ID 63 15 A K Y T S A E T V Q P F H S P E E ~ / N S Q F Y L P P P P G N D D P A Y R Y D 53 ............ S---LPPPP ........ D LVGAAZVAI~ 185 A N Q D A I L E R 193 185 E N Q D K I L K R 193 175 E R A Q E L A ~ 183 ..... R DVTTTPDFYYLK 225 T L H S D P A I Q A Q L 225 T L H S N ~ E F Q K Q L 215 R L Q T I P A F Q K S L .... P-F . . VICGYHW0SD%'TAG [F3) 202 V I C G ~ S ~ 215 202 VICGYHW0SD~DAA215 192 V X C G A H W O B D V D A O 205 V I C G -H W Q S D V - A [F5] 236 236 226 . . . . QAYNDAQIYGD 242 K E D H P K L N Y . . . . 250 Fig. 1. Amino acid sequences were determined as described in the text, and compared to the OWL database using 'SWEEP' [14]; OWL file names for M. morganii, P. stuartii and S. typhimurium were S19187, PHON-PROST and PHONSALTY, respectively. The homologous sequences found, the PhoN products of M. morganii, P. stuartff and S. typhimurium, were aligned with PILEUP [15], and the most likely probable match for each of the peptide fragments to the alignment was determined with PROFILEGAP [15]. Homologous residues (residues identical between the Citrobacter and other sequences) are in boldface and positional identity among all four sequences is shown in the consensus lines. 144 b a c t e r i a gave c o m p a r a b l e m e t a l r e m o v a l . In general, a l t h o u g h p h o s p h a t a s e activity was g e n e r a l l y only a b o u t 3 0 - 5 0 % of th e lowest activity s h o w n by strain N14, significant r e m o v a l o f l a n t h a n u m was given only by P. rettgeri a n d S. typhimurium (strain 11027). T h e l a t t e r illustrates t h a t m e t a l r e m o v a l is strain-specific. I n d e e d , S. typhimurium strain M206 gave n o L a 3 + r e m o v a l b u t r e m o v e d 5 - 6 % o f t h e U O 2+. Kl. pneumoniae gave a simi- lar result. O v e r a l l P. rettgeri s h o w e d p r o m i s e , r e m o v i n g b o t h metals, a l t h o u g h uranyl r e m o v a l was similarly low ( T a b l e 1). C o l u m n s c o n t a i n i n g p o l y a c r y l a m i d e gel-imm o b i l i z e d cells w e r e t e s t e d at flow r at es o f 15 to 230 m l / h with c h a l l e n g e solution s u p p l e m e n t e d with 1 m M uranyl ion. E v e n at t h e slowest flow rate (15 m l / h ) b r e a k t h r o u g h o f UO22÷ was alm o s t i m m e d i a t e with P. rettgeri-supplemented Table 1 Phosphatase activity and metal uptake by Citrobacter sp. N14 and other enterobacteria Organism Batch Phosphatase specific activity (nmol product/min/mg protein) Percentage of challenge metal removed La (6 h) La (18 h) U (18-24 h) Citrobacter sp. I II III IV V 65.6 60.4 550.O 596.0 938.7 NT NT 26 48 100 100 85 92 NT NT NT N14 100 96 97 98 Citrobacter sp. I 1.7 0 NT 0 lp4a II 2.0 14 NT NT IC1.pneumoniae I II III IV V VI 9.6 (30°C) 49.3 (37°C) 29.6 (30°C) 37.6 (37°C) 51.9 (30°C) 20.8 (37°C) NT NT NT NT NT NT 0 0 6 0 0 4 7 7 7 8 3 4 I II 25.6 24.9 NT NT 72 76 5 4 I II 26.7 29.7 NT NT NT 0 2 1 8.1 NCIMB 8066 P. rettgeri NCIMB 10457 M. rnorganii NCIMB 10466 S. typhimurium M206 thax 1 II III IV V VI 10.0 9.5 6.O 2.6 9.5 NT NT NT NT NT NT NT 0 0 0 0 0 4 14 5 0 5 I 21.7 20.7 NT NT 0 2 0 1 7.6 14.6 NT NT 1 1 II 0 1 I II 24.6 35.9 NT NT 86 93 2 1 I II LT7 11027 I 6 The micro-organisms were grown to the mid-logarithmic phase as described in Materials and Methods. Samples were assayed for phosphatase activity or challenged with lanthanum or uranyl solution for times as shown. Metal removal is expressed as percentage of the initial metal removed. NT: not tested. 145 columns, confirming negligible retention. In accordance with previous results [2,20,21] in excess of 90% of the input UO 2+ was removed by the Citrobacter-supplemented columns, at flow rates up to 200 m l / h (10 columns volumes/h). Discussion A survey of some enterobacteria having acid phosphatase activity has given no evidence for a role for the enzyme alone in heavy metal resistance via phosphatase-mediated metal bioaccumulation. Although some lanthanum uptake was observed by several strains, the significance of this is questionable, being observed also with the phosphatase-deficient mutant Citrobacter sp. lp4a; indeed, other experiments using the chemically similar yttrium have shown that yttrium removal was largely attributable to rapid precipitation on the cells (K. Bonthrone and L.E. Macaskie, unpublished). In contrast to lanthanum the uranyl ion is highly toxic to both cell growth [19] and phosphatase activity [20], although phosphate production by the enzyme confers a resistance effect [20]. No evidence for extensive UO 2+ removal was seen with any strain other than the metal-accumulating Citrobacter sp. although several strains did produce significant levels of phosphatase. The presence of phoN was not sought in the strains tested; indeed, this may not be a prerequisite for acid phosphatase activity (see above) but was taken as an indication of which enterobacterial genera might display metal bioaccumulation. Acid phosphatase activity was found in all the strains examined (Table 1), while other studies have shown that of 150 Salmonella strains, representing 28 serotypes, 98% had phosphatase activity [16]. Evidence obtained from other studies has also suggested that the presence of acid phosphatase per se is not sufficient to confer metal bioaccumulation properties [21]; current evidence indicates that it is the juxtaposition of phosphate release to suitable nucleation sites on the cell surface which permits initiation of uptake (nucleation) prior to sustained metal phosphate crystal growth [21]. These findings suggest that the metal accumulating Citrobacter sp., if not unique, is highly unusual; the appropriate combination of phosphatase overproduction and cell surface architecture (nucleation sites) may have been selected during prolonged stress in the metal-polluted environment. It is worth noting that no phoN sequences have been found in Citrobacter freundii [16]; Groisman et al. [16] point out that Salmonella and related enterobacteria (Escherichia, Citrobacter) have a high DNA G + C content, while Morganella and Providencia are of low G + C content and were proposed to have split from the Salmonella and Citrobacter groups early in the evolution of the enterobacteriaceae. The phoN sequences are of low G + C content and it was proposed that phoN was passed by lateral transfer early in the evolutionary sequence, and retained chromosomally [16]. By this argument, the Citrobacter strain N14 is atypical of the genus; indeed, attempts to classify the organism further in the laboratory using the API 20E system (L.E. Macaskie, unpublished), and commercially (Torry Research Station, Aberdeen, UK) have failed to resolve the strain identity to beyond genus level. Acknowledgements The comparative evaluation of Citrobacter sp. N14 and Providencia rettgeri for the removal of uranyl ion was supported by a grant from the European Community (No. BE-5350). DAR was supported by MRC grant G9025236CB to N.L. Brown. The authors are indebted to B.C. Jeong and A. Willis (Dept. of Biochemistry, University of Oxford) for the provision of purified phosphatase and amino acid sequencing, respectively. For software support they thank staff of both the University of Birmingham, Academic Computing Service, and the Science and Engineering Research Council SEQNET facility at Daresbury. References 1 Macaskie, L.E. and Dean, A.C.R. (1982) Cadmium removal by micro-organisms.Environ.Technol. Lett. 3, 4956. 146 2 Macaskie, L.E. (1990) An immobilized cell bioprocess for the removal of heavy metals from aqueous flows. J. Chem. Technol. Biotechnol. 49, 357-379. 3 Macaskie, L.E., Dean, A.C.R., Cheetham, A.K., Jakeman, R.J.B. and Skarnulis, A.J. (1987). Cadmium accumulation by a Citrobacter sp.: the chemical nature of the accumulated metal precipitate and its location on the bacterial cells. J. Gen. 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