Pseudomonas aeruginosa PAO1 used a broad range of alkanesulfonic acids as sole sulfur source for growth, with molar growth yields of 2.2 to 2.9 kg protein per mol sulfur. 4-Phenylbutane-1-sulfonate was desulfonated in vivo to yield 4-pheny 1-1-butyric acid quantitatively as the sole product, suggesting that the desulfonation mechanism is the same as when alkanesulfonates serve as a carbon source for growth. This contrasts with aromatic sulfonate utilization in other organisms, where different desulfonation reactions are used to provide carbon and sulfur. Desulfonation of alkanesulfonates to provide sulfur was repressed by sulfate or thiocyanate, and derepressed in their absence. The alkanesulfonatase system is hence controlled as part of the sulfate starvation-induced stimulo

Kertesz, Michael A.

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FEMS Microbiology Letters 137 (1996) 221-225 Desulfonation of aliphatic sulfonates by Pseudomonas aeruginosa PA0 Michael A. Kertesz * Institute of Microbiology, Swiss Federal Institute of Technology, ETH Zentrum, CH-8092 Ziirich, Switzerland Received 14 November 1995; revised 5 February 1996; accepted 9 February 1996 Abstract Pseudomonas aeruginosa PA01 used a broad range of alkanesulfonic acids as sole sulfur source for growth, with molar growth yields of 2.2 to 2.9 kg protein per mol sulfur. 4-Phenylbutane-1-sulfonate was desulfonated in vivo to yield 4-phenyl-1-butyric acid quantitatively as the sole product, suggesting that the desulfonation mechanism is the same as when alkanesulfonates serve as a carbon source for growth. This contrasts with aromatic sulfonate utilization in other organisms, where different desulfonation reactions are used to provide carbon and sulfur. Desulfonation of alkanesulfonates to provide sulfur was repressed by sulfate or thiocyanate, and derepressed in their absence. The alkanesulfonatase system is hence controlled as part of the sulfate starvation-induced stimulon. Keywords: Pseudomonas aeruginosa; Aliphatic sulfonates; Desulfonation; Sulfate limitation 1. Introduction Organosulfonic acids are widespread in nature, both as atylsulfonate xenobiotics (e.g. linear alkyl- benzene sulfonate detergents, sulfonated dyestuffs) and as natural alkanesulfonates such as taurine (2- aminethanesulfonate), sulfonolipids or methanesul- fonate. The alkanesulfonates play an important role in the biogeochemical sulfur cycle; much of the sulfur in forest-floor litter is present not as inorganic sulfate (circa 5%) but in the form of sulfonates ( > 40%) [ 11, and methanesulfonate is the major pho- tochemical oxidation product of dimethylsulfide in the atmosphere, and is deposited in rain and snow [2]. Whereas the biochemistry of aromatic desulfona- * Tel.: +41 (1) 632 3357; Fax: +41 (1) 632 1148; E-mail: kertesz@micro.biol.ethz.ch Federation of European Microbiological Societies SSDI 0378-1097(96)00061-4 tion by bacteria has been studied in detail in recent years [3], less is known about how alkanesulfonates are degraded by microorganisms. Bacteria able to degrade either synthetic alkane- sulfonates CC,-C 12) [4] or taurine [5] as a source of carbon and energy have long been known. Recent studies have also shown that the sulfur in natural alkanesulfonates such as taurine, isethionate and cysteate can also be utilized specifically by a broad range of microorganisms [6-81. Studies with E. coli mutants defective in cysteine biosynthesis howed that uptake of these sulfonates does not involve the sulfate uptake system, and that assimilation of sul- fonate sulfur proceeds via cleavage to yield sulfite, and subsequent incorporation to cysteine 181. Sulfite is also the initial sulfur product from aromatic sul- fonates in both the carbon and sulfur cycles, where dioxygenases and monooxygenases are involved re- 222 M.A. Krrtr.y: / FEMS Mic~rohiolo,q Letter.r lj7 (19961 221-225 spectively [3]. The biochemistry of alkanesulfonate desulfonation in the sulfur cycle has not yet been elucidated. During growth in the absence of sulfate or cys- teine, several bacterial species (including Pseu- domonas aeruginosa) produce a set of extra proteins. components of the sulfate starvation-induced stimu- lon. These proteins have been suggested to play a role in scavenging of alternative sulfur sources such as organosulfates and organosulfonates [9]. The fact that utilization of sulfonates is repressed by addition of sulfate [lo] suggests that the desulfonation sys- tems involved are regulated as part of the sulfate starvation-induced stimulon [9]. We have now exam- ined the physiology of alkanesulfonate utilization as sulfur source by a genetically and physiologically well characterized pseudomonad, Pseudomonas aeruginosa PA0 1. 2. Materials and methods 2.1. Bacterial strains, growth media and growth conditions Pseudomonas aeruginosa PA01 [ 1 I] was rou- tinely grown in a sulfur-free succinate minimal medium described previously [9]. Sulfur-containing compounds required for growth (100 to 500 PM) were sterilized by filtration of stock solutions (0.2 pm filters) and added as described in the text. The cultures were grown aerobically at 37°C either with shaking (180 rpm> on an orbital shaker or in vigor- ously stirred flasks with a continuous air supply [ 121. Growth was monitored by measuring optical density at 650 nm, and cultures were harvested when they reached the stationary phase. 2.2. Chemicals 4-Phenylbutane- 1 -sulfonic acid, toluene-ru- sulfonic acid, 1,3-dioxo-2-isoindoline-ethanesulfonic acid, N-phenyltaurine, 4-(3-methyl-4-nitrophenoxy)- I-butanesulfonic acid and n-hexyl sulfate were sup- plied by Aldrich (Steinheim, Germany). All other sulfur-containing compounds, and components of growth media, were obtained from Fluka (Buchs, Switzerland). 2.3. Analytical methods Metabolites of arylalkanesulfonic acids were anal- ysed by reversed-phase high-performance liquid chromatography (HPLC), using a Nucleosil-C ,x col- umn (250 by 4.6 mm; particle size 7 pm). The mobile phase was 10 mM potassium phosphate buffer (pH 2.2 for a-toluenesulfonic acid and its desulfona- tion products, pH 6.7 for all other compounds) con- taining appropriate amounts of methanol (0-807~ (vol/vol>). Elut d e compounds were detected spec- trophotometrically at 200, 210 nm, or 248 nm. For identification purposes, desulfonation products were extracted from stationary-phase culture supernatants (200 ml> after acidification to pH 1.5 with HCl, using an Extract-Clean C ,* column (1 g sorbent; Alltech) and elution with methanol. The product from 4-phenylbutane- 1 sulfonic acid was further pu- rified by reversed-phase HPLC as described above, and analysed by electron impact mass spectrometry (Fisons VG Tribrid; EI + mode; 70 eV>. The sulfate content of all sulfur sources was checked by ion chromatography before use, using a Durasep A-l anion exchange column (Alltech), with a GA-l guard column. Ions were eluted isocratically with 4 mM NaOH/S’% (v/v) methanol, and were detected by conductimetry after chemical suppres- sion. All sulfur sources contained < 0.5% (mol/mol) inorganic sulfate. Total protein in cell suspensions was determined by a modified Lowry method [ 131 using bovine serum albumin as standard. All glassware used in sulfate-limited experiments was washed with 3 M HCI and rinsed thoroughly with distilled water be- fore use. 3. Results and discussion 3.1. Utilization of alkanesulfonates as sulfur sources by P. aeruginosa PAOI P. aeruginosa can utilize a broad range of sulfur sources for growth. Although it cannot desulfonate aromatic sulfonates or thiophenols, it can degrade a broad range of aromatic sulfate esters [ 141, aliphatic sulfate esters and sulfonates, and other sulfur-con- taining compounds [ 151. Desulfonation of simple MA. Kertesz/ FEMS Microbiology Letters 137 (1996) 221-225 223 alkanesulfonates has been difficult to examine in the past, because they lack a chromophore to facilitate their detection, and are used at low concentrations (30-100 PM) when the sulfur in the compound is utilized specifically. We have therefore chosen to analyse a series of alkanesulfonates that carry an aromatic ring, including 4-phenyl- 1 -butanesulfonate, toluene-cr-sulfonate, N-phenyltaurine, 1,3-dioxo-2- isoindoline-1-ethanesulfonate, and 4-(3-methyl-4- nitrophenoxy)- 1-butanesulfonate. The molar growth yields obtained for P. aeruginosa with these com- pounds (2.2-2.8 kg protein/mol S> and with simple aliphatic sulfonates such as taurine or pentane- l- sulfonate (2.8 kg/mol S> were found to be very similar to the growth yields obtained when other sulfur sources such as sulfate, cysteine, or methion- ine were utilized for growth (2.6-2.9 kg/mol S), and these values also corresponded well to values previously obtained with Pseudomonas putida grown with aromatic sulfonates [16]. We therefore con- cluded that the sulfur contained in aliphatic sul- fonates was assimilated essentially quantitatively into cell material by the cells during growth. After identi- fication of the desulfonation product (see below) it was possible to complete quantification of the desul- fonation mass balance, since > 90% of the desul- fonated carbon moiety was also released uring the desulfonation reaction (Fig. 1). This organic product was not subsequently further degraded, and was not 120 350 0 0 0 5 10 15 20 25 time (ix) Fig. 1. Growth of P. aenrginosu PA01 in succinate-salts medium with 4-phenylbutanesulfonate as sole sulfur source. The cells were grown aerobically at 37”C, and samples were removed periodi- cally for analysis of total protein content (A) by a modified Lowry assay, and of 4-phenylbutanesulfonate (0) and 4-phenyl- butyric acid ( n ) by HPLC. utilized as a carbon source by P. aeruginosa in the absence of succinate ither (not shown). 3.2. Identification of the products of alkanesulfonate desulfonation by P. aeruginosa PA01 During growth of pseudomonads with aliphatic sulfonates as sole source of carbon and energy, the first product to be released is the carboxylic acid derived from cr-hydroxylation, desulfonation to an aldehyde and subsequent oxidation [4]. To determine whether this was also the case when the sulfonate was supplied as a source of sulfur we examined degradation of 4-phenylbutane- 1 -sulfonate, reasoning that this would best approximate desulfonation of simple n-alkanesulfonates. The aromatic product produced from desulfonation was extracted from growth supematants, and purified by reversed-phase HPLC. Electron-impact mass spectrometry of the resulting compound gave the following spectrum: WI/Z: 164 CM+), 104 (M+-CH3~00H), 91 (M+- CH,CH,COOH) allowing its identification as 4- phenylbutyric acid. This was then confirmed by co- chromatography of the product in growth medium with authentic 4-phenylbutyric acid. When toluene- a-sulfonate was supplied as sole sulfur source the corresponding benzoic acid was identified as product (co-chromatography; not shown), and benzaldehyde could not be detected by HPLC at any point in the growth curve (not shown). Sulfonate disappearance and carboxylate appearance occurred simultaneously, without any lag phase to suggest release of an inter- mediate compound or the presence of significant intracellular pools of either sulfonate or products (Fig. 1). The carbo xy rc acid therefore probably arises 1’ by oxidation of a putative intermediate aldehyde within the cell, as is known for aromatic sidechain oxidation, where toluenesulfonate monooxygenase is co-induced with its cognate aldehyde dehydrogenase [17]. The sulfur cycle enzyme therefore proceeds by a similar mechanism to that observed under carbon limitation [4]. This contrasts with the situation ob- served for degradation of aromatic sulfonates, where the carbon cycle enzymes are predominantly dioxy- genases, and the sulfur cycle enzymes are monooxy- genases [ 16,181, and for dibenzothiophene desulfur- ization, where two pathways also exist [19]. 224 M.A. Kerre.r/ FEMS Microbiology Letters 137 (19%) 221-225 3.3. Regulation ofdesulfonation actMy by the sulfur supply to the cell Aromatic desulfonation activity in P. putida S-3 I3 has been shown to be controlled by the sulfur sources present during growth, with the arylsulfonatase sys- tem apparently repressed in the presence of sulfate. cysteine or thiocyanate, and derepressed during growth with other sulfur sources [ 16,18,20]. Regula- tion of aliphatic sulfonate desulfonation was studied in vivo in P. aeruginosa by measuring desulfonation of 4-phenylbutanesulfonate (100 PM) during growth of the cells in the presence of an excess (500 FM) of a second sulfur source (Fig. 2). No desulfonation reaction was observed in the presence of sulfate or thiocyanate, but the alkanesulfonate was converted to its carboxylic acid product in the presence of methio- nine, aryl- or alkyl-sulfate esters, or cyclamate. Transformation of 4-phenylbutanesulfonate also oc- curred in the presence of pentanesulfonate, though the rate was reduced, presumably due to competition between the two sulfonates for the same enzyme. The alkanesulfonatase system of P. aeruginosa is hence regulated in the sulfur cycle as part of the sulfate starvation-induced stimulon [9], i.e. synthesis 40 35 r Fig. 2. Desulfonation of 4-phenylbutanesulfonate by P. aerugi- nosa PA01 during 24 h growth in succinate-salts medium contain- ing 4-phenylbutanesulfonate (100 PM) together with a second sulfur source (500 FM). Desulfonation was quantified for each experiment both as 4-phenylbutanesulfonate disappearance and as production of 4-phenylbutyric acid, and the results are the mean of 2-4 independent experiments. In the absence of a second sulfur source, complete desulfonation was observed (100 PM). NCS - 4-nitrocatechol sulfate. of the enzyme is repressed in the presence of pre- ferred sulfur sources, and derepressed in their ab- sence. In several organisms, these preferred sulfur sources have been shown to include sulfate, cysteine, and thiocyanate [6,9,10,2 l], though the mechanism of assimilation of the last of these is not yet clear. Our data, however, (Fig. 2, and [15]) suggest that the situation may be more complex in P. aeruginosa than has been observed in other species, since desul- fonation of 4-phenylbutanesulfonate was also ob- served in the presence of cysteine, though this com- pound acts to repress arylsulfonate desulfonation in P. putida, and also represses synthesis of both aryl- sulfatase and other sulfate starvation-induced pro- teins in P. aeruginosa [15]. The regulatory pattern observed for desulfonation activity also explains the previously observed loss of carbon-limited desul- fonation activity by an isolate which retained the ability to use alkanesulfonates as sulfur source [6]. Two isoenzymes catalyzing the same reaction may well be present in the cell, since cells utilizing sulfonates as source of carbon will necessarily re- lease excess sulfur and repress synthesis of the sulfur cycle enzyme. Loss of the carbon cycle enzyme therefore does not need to involve loss of sulfur-de- pendent desulfonation, although exact quantification of this will require purification and characterization of the enzymes involved. Acknowledgements My thanks are due to T. Leisinger for generous support and to A.M. Cook for useful discussions and critical reading of the manuscript. This work was supported in part by Swiss National Foundation grant no. 31-41873.94. References [ll Dl [31 Autry, A.R. and Fitzgerald, J.W. (1990) Sulfonate S - a major form of forest soil organic sulfur. Biol. Fertil. Soils 10, 50-56. Baker, S.C., Kelly, D.P. and Murrell, J.C. (1991) Microbial degradation of methanesulfonic acid - a missing link in the biogeochemical sulfur cycle. Nature 350, 627-628. Kertesz, M.A., Cook, A.M. and Leisinger, T. (1994) Micro- bial metabolism of sulfur- and phosphorus-containing xeno- biotic% FEMS Microbial. Rev. 15, 195-215. 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(1995) The assimilation of sulfur from multiple sources and its regulation as part of the sulfate starvation-induced stimulon in Pseudomonas putida S-313. Microbiology (U.K.), in press. [21] Roberts, R.B., Abelson, P.H., Cowie, D.B., Bolton, E.T. and Britten, R.J. (1955) Studies of biosynthesis in Escherichia coli. Carnegie Institution, Washington. 

Desulfonation of aliphatic sulfonates by Pseudomonas aeruginosa PAO

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