INTRODUCTION
Bioremediation processes such as wastewater treatment and decontamination of soils rely on the ability of bacteria to use toxic organic compounds, such as solvents or detergents, as growth substrates. The presence of such toxic compounds is generally a challenge for bacteria and requires energy-consuming protection mechanisms such as efflux pumps (
1) and chaperones (
2). If the toxic compound is the only source of energy and carbon, this challenge is increased because the bacterial cells have to take up and expose their cell membrane and cytosol to these chemicals. Since the energy needed for protection against this chemical stress has to originate from the catabolism of the toxic substrate, this process requires elaborated adaptations for providing a well-balanced regulation of catabolism and protection mechanisms to avoid detrimental cell damage.
Degradation of the anionic detergent sodium dodecyl sulfate (SDS) by
Pseudomonas aeruginosa is a suitable paradigm for studying how bacteria cope to grow with a toxic compound as a carbon and energy source. In the past we have shown that a sufficient energy status of the cells is crucial for survival, e.g., for operating proton-motif-force-dependent efflux-pumps such as MexEF-OprM (
3–5). In addition, we were able to show that cell aggregation serves as a preadaptive survival strategy of
P. aeruginosa for growth with SDS (
6). Cell aggregation is induced via a signal transduction system encoded by
siaABCD and increases the survival rate upon exposure to SDS-related stress several hundredfold compared to suspended single cells (
4,
7). Since the degradation of the toxic compounds also contributes to minimizing the toxic effects, the rapid induction of synthesis of the respective enzymes is crucial. This calls attention to the genetic regulation of the enzymes that initiate SDS degradation in
P. aeruginosa. While the ability of SDS degradation in pseudomonads has been known for many years (
8–12), the regulation of the involved enzymes and stimulus perception is poorly understood.
The initial step in SDS degradation by
P. aeruginosa strain PAO1 starts with the hydrolysis of the sulfate ester group catalyzed by the well-studied alkylsulfatase SdsA1 (PA0740) (
13) (
Fig. 1, left panel). We recently identified the Lao system to be involved in the following oxidation steps of the first intermediate, the long-chain primary alcohol 1-dodecanol, and the emerging aldehyde 1-dodecanal (
14). In particular, LaoA and LaoB (PA0364-65) were found to be responsible but not essential for the 1-dodecanol oxidation. The respective genes are located together with
laoC (PA0366), encoding an aldehyde dehydrogenase, in one gene cluster. In addition, the Lao system has been shown to participate in the oxidation of long-chain alcohols originating from alkane degradation (
14). Thus, the Lao system is apparently disconnected from the initial SDS degradation step not only by its genomic localization but also by its substrate specificity. Accordingly, different regulatory pathways are required to enable the expression of the Lao system in the absence of SDS. Thus far, the LysR-type regulator SdsB for the alkylsulfatase SdsA in
Pseudomonas sp. strain ATCC 19151 has been specified and analyzed. This regulator gene has 54% identity to PA0739 (
15,
16), which is located directly adjacent to
sdsA1 in an opposite direction on the
P. aeruginosa PAO1 genome (
Fig. 1, right panel). In addition, we have already shown that the TetR-type regulator LaoR (formerly PA0367), the gene of which is located directly adjacent to
laoCBA in the opposite direction (
Fig. 1, right panel), regulates the genes encoding the Lao enzymes (
14).
The goal of our study was to study the question how P. aeruginosa copes to grow with SDS as a carbon and energy source from the point of genetic regulation. In particular, we sought to identify the regulator for sdsA1, as well as inducers for expression of the initiating enzymes in the SDS degradation.
DISCUSSION
The goal of this study was to elucidate how the expression of the enzymes catalyzing the initial reactions of SDS degradation, namely, of the alkylsulfatase SdsA1 and the long-chain alcohol-oxidizing enzymes encoded by
laoCBA, in
P. aeruginosa strain PAO1 is regulated. We could show that these reactions are induced in a two-step manner by a consecutive positive and negative regulation. In the first step, the transcription of
sdsA1 encoding the sulfatase converting SDS into sulfate and 1-dodecanol (
13) is activated by the LysR-type regulator SdsB1 (PA0739), which we identified in this study. This activation was caused by SDS, as well as by SLES, another sulfate ester detergent and commonly used alternative for SDS. In the second step, transcription of the
laoCBA operon is induced by a detachment of the TetR-type repressor LaoR from its DNA binding site. Our analysis revealed that long-chain acyl-CoA esters can act as ligands, with dodecanoyl-CoA exhibiting the highest efficiency of LaoR detachment from its DNA-binding site. Thus, derepression of the
laoCBA operon would require basal expression of the encoded enzymes and an as-yet-unknown acyl-CoA-ligase for the formation of this ligand. This two-step induction of SDS degradation could be the outcome of a strategy that ensures rapid inactivation of a toxic sulfate ester detergent, while the degradation of the resulting long-chain alcohol is only induced when it can sufficiently be further converted into a metabolite that signals the availability of an energy-rich substrate for β-oxidation. This derepression of the
laoCBA operon would result in the increased formation of the inductor 1-dodecanoyl-CoA and thus in a positive regulatory feedback loop. Further degradation of the activated fatty acid by β-oxidation then enables both growth and the operation of protection mechanisms against SDS. The latter is particularly important for survival since we have previously concluded that dividing cells are more vulnerable to the damaging effects of SDS (
5). The observation that the
laoR gene is subject to positive autoregulation suggests that the
lao operon can be rapidly repressed again when the inducer is depleted, thereby preventing undue expression. In this respect it is unlikely that SDS, although it caused detachment of LaoR in the EMSAs, is a specific inducer of the
lao operon, which is also required for the degradation of alkanes that are much more abundant in nature than SDS (
16).
EMSA analyses revealed that SdsB1 possesses an atypical DNA-binding site within the first 40-bp DNA fragment upstream of
sdsB1, which is located in the intergenic region between
sdsB1 and
sdsA1 (
Fig. 3B). LysR-type regulators often bind to an RBS and a distinct activation binding site (
18). The RBS generally has a recognized LTTR (LysR-type transcriptional regulator) box with the conserved palindromic sequence T-N
11-A (
18,
22) that was not identified within the fragment bound by SdsB1. Instead, we identified two IRs, gcat-N
16-atgc and aatg-N
13-catt, which partly overlap within the bound DNA fragment (
Fig. 3). An
in silico protein domain analysis (Interpro) (
23) of SdsB1 exhibited a conserved CysB-like substrate binding domain (IPR 000847). Interestingly, complex DNA-binding with multiple overlapping DNA binding sites is also described for CysB from
Salmonella enterica serovar Typhimurium (
24,
25). Moreover, the binding site of the master regulator CysB from
P. aeruginosa (
26–28) contains two inverted repeats, which partly overlap (
28). However, an alignment of SdsB1 and CysB from
P. aeruginosa, as well as
S. Typhimurium, revealed only 24% identity in each case (BLASTP) (
29). Nevertheless, both CysB regulators share their involvement in metabolism of organic sulfur compounds with SdsB1 (
30,
31). In addition, a recent study identified sulfate ions captured within the cleft of the crystallized C-terminal regulatory domain (substrate binding domain) of CysB from
P. aeruginosa, pointing toward sulfate ions as potential ligands influencing the function of this regulator (
27). Since sulfate was the sulfur source for
P. aeruginosa in our experiments, it is unlikely to be the inducer for SdsB1. The expression of
sdsA1 via SdsB1 was induced only by substrates of SdsA1, namely, SDS and SLES, but not by the structural analogue dodecyl sulfonate, which cannot be cleaved by SdsA1. Thus, a sulfate group attached to a long-chain alcohol is apparently a decisive structural element for a ligand of SdsB1, thereby supporting the similarities between SdsB1 and CysB.
A typical DNA-binding site was identified to be occupied by the TetR-type regulator LaoR. Ligands of TetR-type regulators comprise a remarkable variety of compounds, including antibiotics, bile acids, cell-cell signaling molecules, proteins, metal ions, or fatty acids (
19,
32). Also, acyl-CoA esters such as oleoyl-CoA and palmitoyl-CoA for the regulator DesT, which is involved in lipid metabolism of
P. aeruginosa, are known as ligands (
33). One example very similar to our proposed model for the positive-feedback regulation for LaoR is the TetR regulator AlkX from
Dietzia sp. strain DQ12-45-1b (
34). This regulator controls the expression of genes involved in the degradation of alkanes and binds long-chain fatty acids derived from alkane degradation as ligands. The relatively high concentration of dodecanoyl-CoA required for the detachment of LaoR from its DNA-binding site might indicate that a threshold concentration is required for inducing the postulated positive-feedback regulation. However, since acyl-CoA esters are already unstable in aqueous solution at neutral pH values, the actual concentration of this ligand might have been overestimated in the respective experiments.
The finding that SLES serves as an inducer for the SdsB1-mediated
sdsA1 transcription prompted us to test whether this sulfate ester detergent could also serve as a carbon and energy source. To the best of our knowledge, the growth of
P. aeruginosa strain PAO1 with SLES has not yet been described. This milder detergent often replaces SDS in cosmetic and hygienic products due to its reduced skin irritation properties (
35–37). Since SLES also induced cell aggregation in
P. aeruginosa, this sulfate ester detergent apparently also activates the Sia system, indicating that it presumably has toxic effects similar to those of SDS. Generally, SLES degradation has been observed in other pseudomonads, but the degradation pathway is not completely understood. Metabolite analysis in
Pseudomonas sp. strain Des1 (
38,
39),
Pseudomonas sp. strain SC25A (
40), and
P. nitroreducens (
41) revealed that degradation starts with cleavage of the ether bonds, but cleavage of the sulfate ester bond has also been shown to occur concomitantly to ether cleavage in some of these strains (
41,
42). However, in strain PAO1, the
sdsB1 deletion mutant, which does not express the alkylsulfatase SdsA1, could not no longer grow with SLES, indicating that SLES degradation is compulsively initiated by sulfate ester hydrolysis. This conclusion is supported by the fact that the stains-all assay (see Materials and Methods) used to quantify sulfate ester detergents did not indicate a decrease in SLES concentration. While SdsA1 apparently had an essential role in SLES metabolism, the Lao system is clearly involved but not essential. The reduced growth rate of the PAO1
ΔlaoA strain with SLES could plausibly be explained by the presumptive formation of 1-dodecanol after cleavage of the ethoxy units from the SLES molecule. There are many different ether-cleaving reactions known among bacteria (
43), but they are unknown for
P. aeruginosa and are therefore under investigation in our laboratory.
In conclusion, our study is a further step toward the understanding of how P. aeruginosa copes to grow with toxic detergent SDS as a carbon and energy source. The next steps for pursuing this research question further involve analysis of how expression of the metabolic pathway and the protection mechanisms, especially cell aggregation and efflux pumps, are coordinated.