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Applied and Environmental Microbiology, September 2006, p. 6411-6413, Vol. 72, No. 9
0099-2240/06/$08.00+0     doi:10.1128/AEM.00957-06
Copyright © 2006, American Society for Microbiology. All Rights Reserved.

SHORT REPORT

Organotin Decomposition by Pyochelin, Secreted by Pseudomonas aeruginosa Even in an Iron-Sufficient Environment

Guo-Xin Sun, Wen-Qiang Zhou, and Jian-Jiang Zhong^*

State Key Laboratory of Bioreactor Engineering, East China University of Science and Technology, 130 Meilong Road, Shanghai 200237, People's Republic of China

Received 23 April 2006/ Accepted 20 June 2006

Top Abstract Introduction Chemicals. References

 
A triphenyltin (TPT)-decomposing strain, Pseudomonas aeruginosa CGMCC 1.860, was screened out. It secreted an unknown TPT-decomposing factor into the medium, later shown to be pyochelin, even in the presence of 100 µM iron. To our knowledge, this is the first report of organotin decomposition by pyochelin.

Top Abstract Introduction Chemicals. References

 
Organotin compounds are ubiquitous in the environment and have a wide range of industrial and agricultural applications (7). However, they are toxic and harmful to a variety of nontarget organisms (see, e.g., references 10 and 16). Without a doubt, it is important to remove organotins from the environment.

It has previously been reported that some microalgae were capable of degrading organotin, but their degradation rate was very low (14). Information on the bacterial degradation of organotin compounds is still severely limited (7, 9). This work investigated the decomposition of triphenyltin chloride (TPT) by microorganisms, and interestingly, pyochelin (PCH) [2-(2-o-hydroxy phenyl-2-thiazolin-4-yl)-3-methylthiazolidine-4-carboxylic acid], different from pyoverdine (PVD), was found as a new organotin-decomposing factor.

Top Abstract Introduction Chemicals. References

 
TPT (95%), diphenyltin dichloride (DPT) (98%), and monophenyltin trichloride (MPT) (96%) were purchased from Aldrich Chemical Co.

Seventeen strains belonging to Pseudomonas and Burkholderia genera, obtained from the China General Microbiological Culture Collection Center (Beijing, People's Republic of China), were used for screening for TPT-decomposing bacteria. The TPT decomposition activity was measured by monitoring the decrease of TPT concentrations and the increase of DPT and MPT levels using high-performance liquid chromatography (HPLC) as described previously (12). Shimadzu (Kyoto, Japan) HPLC equipment (LC-10AT_VP) with a UV-Vis detector and a reversed-phase column (Kromasil C₁₈) (250- by 4.6-mm internal diameter, 5 µm) was used. The mobile phase consisted of methanol-acetate acid-water (60:10:30 [vol/vol/vol]) containing 1 mM dithiothreitol. The flow rate was 0.75 ml/min, and the UV detection wavelength was 257 nm. Among all the strains, none of them were able to utilize TPT as a sole carbon source to support growth, but all of them were able to grow in the M9 medium with sodium succinate (4 g/liter) as a carbon source supplemented with 200 µM TPT. Pseudomonas aeruginosa CGMCC 1.860, a fluorescent pseudomonad with the greatest ability to decompose TPT (data not shown), was chosen for the following experiments.

The kinetics of TPT (200 µM) decomposition by P. aeruginosa CGMCC 1.860 are shown in Fig. 1. TPT rapidly decomposed during log-phase growth and reduced to about 40% of the initial amount within 36 h, and it decreased slowly in the stationary phase (Fig. 1). The accumulation of DPT reached a maximal concentration of 50 µM at 24 h and then slowly decreased. The concentration of MPT increased slowly during 96 h of incubation. This strain showed a decomposition ability similar to that of other Pseudomonas strains (7), and it had a relatively higher organotin-decomposing capacity than reported for other strains previously, such as Alteromonas sp. strains (6, 9). Methanol used to dissolve TPT did not inhibit either the growth of bacteria or TPT decomposition with the concentration used (data not shown), and no decomposition occurred in the control (Fig. 1). These facts indicate that the TPT decomposition was done by the microorganism.

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FIG. 1. Decomposition of TPT by P. aeruginosa CGMCC 1.860 in M9 medium supplemented with TPT (200 µM). The concentrations of TPT (), DPT (), and MPT () were determined by HPLC with a UV detector at 257 nm, and the growth () was measured as the optical density at 600 nm (OD600). , TPT level for control without inoculation. There were triplicate samples for each condition.

Further experiments on TPT decomposition by the screened strain were conducted. First of all, resting cells and cell-free supernatants were prepared to investigate whether the intracellular or extracellular decomposition of TPT occurred. At the beginning, the resting cells were resuspended in Tris-HCl buffer. TPT (200 µM) was added in the resting cells or supernatants on a shaker (120 rpm) for 3 days. There was only a slight decrease in the TPT level (about 6%) in the case of resting cells. In contrast, the supernatant exhibited a much higher capacity for TPT decomposition (at 40%), indicating that there was a TPT-decomposing compound(s) secreted by the bacteria into the medium.

As reported previously, under conditions of iron starvation, P. aeruginosa can secret a low-molecular-weight compound with high iron-binding affinity known as PVD (2, 12). PVD produced by Pseudomonas chlororaphis was demonstrated to decompose TPT (7, 8). In our work, the PVD obtained from the supernatant of P. aeruginosa CGMCC 1.860 by solid-phase extraction (8) could decompose TPT (data not shown).

According to the literature (18), under iron-sufficient conditions (100 µM), the production of PVD would be absolutely inhibited. Initially, it was supposed that PVD was the sole TPT-decomposing factor, and if sufficient ferric ions were added into the medium, the activity of TPT decomposition by the bacterium would decrease or disappear due to the inhibition of PVD production by Fe³⁺. Here, the stock solution of FeCl₃ (20 mM) was sterilized by passage through membrane filters and was added to cooled media just prior to inoculation (4). The production of PVD in the medium in the presence of 100 µM FeCl₃ was detected spectrophotometrically by measuring the A₄₀₀ (11) or by measuring fluorescence at an excitation wavelength of 405 nm and an emission wavelength of 455 nm (3, 11). Although the bacterium grew slightly better in the presence of Fe³⁺ than it did without Fe³⁺, the A₄₀₀ and fluorescence at 455 nm in the medium with Fe³⁺ were very low compared to those in medium without Fe³⁺ (Table 1). The results indicated that PVD production was completely inhibited in the presence of Fe³⁺ in medium, which is in agreement with previous work (17). However, interestingly, the concentration of TPT decreased from 186.8 to 122.8 µM in the presence of 100 µM Fe³⁺. It is obvious that TPT decomposition still occurred during the bacterial growth in the medium containing 100 µM FeCl₃, although PVD production was inhibited (Table 1). The facts suggest that there was another unknown TPT-decomposing factor secreted by P. aeruginosa into the medium that is different from PVD.

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TABLE 1. Optical densities of cell-free supernatants at 600 nm (for growth) and 400 nm (for PVD) and fluorescent valuea

The extract of the cell-free supernatant (16 liters) with ethyl acetate was found to possess high TPT decomposition activity (data not shown), and it was applied onto a Silica Gel G thin-layer chromatography (TLC) plate with chloroform-acetic acid-ethanol (95:5:2.5 [vol/vol/vol]) as the development solvent. Four fractions were eluted with methanol and dried, and their TPT decomposition activities were then detected. Fraction 3 exhibited a relatively higher capacity for TPT decomposition than other fractions (Table 2), suggesting that it contained a TPT-decomposing factor, and this fraction was further purified by thin-layer chromatography with chloroform-acetic acid-ethanol (95:5:5 [vol/vol/vol]). The purity of PCH was over 99.6%, as determined by HPLC with the normalization method. The chemical structure of the finally purified TPT-decomposing factor was identified by mass spectrometry (MS) and nuclear magnetic resonance (NMR) (¹H and ¹³C NMR) (data not shown); its high-resolution electron ionization mass spectrum contained major peaks at 220.0649 (C₁₁H₁₂N₂OS) and 191.0361 (C₁₀H₉NOS), and the high-resolution electrospray ionization mass spectrum showed a molecular ion peak at m/z 325.0659 [M + H] (C₁₂H₁₆N₂O₃S₂). Those data indicate that this new TPT-decomposing factor is PCH, with a molecular weight of 324.1 (Fig. 2), which is a kind of siderophore (6). In addition, investigations on its chemical properties confirmed that it had UV absorption, fluorescent absorption, R_f, and color reactions identical to those of PCH reported previously (1, 4, 5, 19, 20). Furthermore, the purified PCH was used to decompose TPT. In 24 h, the TPT concentration decreased, and the decomposition products DPT and MPT were detected (Table 3). Benzene, another decomposition product, was also detected by HPLC in additional experiments (data not shown). Furthermore, the molecular ion peak of m/z 396.1 [PCH + Sn + Na] in the electrospray ionization-MS spectrum of the reaction mixture (at 24 h) was seen (data not shown), which indicated the formation of the PCH-Sn complex, and the data suggested that PCH could decompose TPT to inorganic tin and chelate the tin. The above-described results confirmed the TPT-decomposing capacity of PCH.

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TABLE 2. TPT decomposition by extract fractions of TLCa

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FIG. 2. Structure of a novel TPT-degrading factor, which was identified as PCH by MS and NMR.

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TABLE 3. TPT decomposition by PCHa

In supplementary experiments, 100 µM Fe³⁺ and 200 µM TPT were added alone or together into the culture medium to investigate their effects on PCH biosynthesis by P. aeruginosa CGMCC 1.860 (data not shown). The PCH production titer was 24.76 µM for the control (without both Fe³⁺ and TPT), and it was decreased to 0.83 µM with the sole addition of Fe³⁺. It is apparent that Fe³⁺ remarkably inhibited the PCH synthesis. This is in agreement with a previous report, where the PCH production was significantly (but not completely) repressed in the presence of Fe³⁺ (19). However, it is different from other reports, which claimed a complete repression of PCH synthesis by P. aeruginosa PAO1 at 10 µM Fe³⁺ (4, 20). The reason for this may be related to the different physiologies of different strains. In the case with the sole addition of TPT, the PCH level detected was 29.69 µM, slightly higher than that of the control. This indicates that TPT had a slight effect on PCH production. When both Fe³⁺ and TPT were added into the culture medium, the PCH titer reached 3.29 µM, fourfold more than that with only Fe³⁺ added, suggesting that the addition of TPT significantly enhanced PCH biosynthesis under iron-rich conditions. It seems that TPT could have an iron-limiting effect on P. aeruginosa, which could have caused the increase of PCH accumulation. Similarly, other researchers also claimed that lead could stimulate the siderophore yield under conditions of an excess of iron (13), although the mechanism is yet unclear. Given that the TPT level was slightly reduced (about 6%) in resting cells, a small amount of TPT might be taken up by the cells and might affect cellular physiology and metabolism. As reported previously, in the presence of iron, the ferric uptake regulator (Fur) binds to the promoter of pvdS for PVD and pchR for PCH, which leads to the repression of PVD and PCH biosynthesis (15). We speculate that a certain amount of TPT absorbed into the cells might bind to Fur and reduce its affinity for pchR but not for pvdS, which accordingly would result in the increased synthesis of PCH but not of PVD.

In conclusion, this work demonstrated that P. aeruginosa CGMCC 1.860 could decompose TPT and that it secreted a new TPT-decomposing factor identified as PCH when it was grown in medium containing 100 µM Fe³⁺, in contrast to data reported previously (7). To the best of our knowledge, there have been no reports on the decomposition function of PCH and specifically the decomposition capacity of organometallic compounds. Further work on the decomposition mechanism is under way in our laboratory.

 
Financial support from the National Natural Science Foundation of China (NSFC project no. 20225619) is acknowledged.

We also thank Zhong Li of the Shanghai Key Laboratory of Chemical Biology, ECUST, for his advice on chemical structure analyses.

 
* Corresponding author. Mailing address: State Key Laboratory of Bioreactor Engineering, East China University of Science and Technology, 130 Meilong Road, Shanghai 200237, People's Republic of China. Phone: 86-21-6425-2091. Fax: 86-21-6425-2250. E-mail: jjzhong{at}ecust.edu.cn.

Top Abstract Introduction Chemicals. References

 

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Applied and Environmental Microbiology, September 2006, p. 6411-6413, Vol. 72, No. 9
0099-2240/06/$08.00+0     doi:10.1128/AEM.00957-06
Copyright © 2006, American Society for Microbiology. All Rights Reserved.

This article has been cited by other articles:

• Sun, G.-X., Zhong, J.-J. (2006). Mechanism of Augmentation of Organotin Decomposition by Ferripyochelin: Formation of Hydroxyl Radical and Organotin-Pyochelin-Iron Ternary Complex. Appl. Environ. Microbiol. 72: 7264-7269 [Abstract] [Full Text]  

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