Differential expression of pathogenicity- and virulence-related genes of Xanthomonas axonopodis pv. citri under copper stress

GENETICS OF MICROORGANISMS

SHORT COMMUNICATION

Differential expression of pathogenicity- and virulence-related genes of Xanthomonas axonopodis pv. citri under copper stress

Ana Carolina Basílio Palmieri^I; Alexandre Morais do Amaral^I,II; Rafael Augusto Homem^I,III; Marcos Antonio Machado^I

^ICentro APTA Citros Sylvio Moreira, Instituto Agronômico de Campinas, Cordeirópolis, SP, Brazil

^IIEmbrapa Recursos Genéticos e Biotecnologia Brasília, DF, Brazil

^IIIInstituto de Biologia, Universidade Estadual de Campinas, Campinas, SP, Brazil

^{Send correspondence to}

ABSTRACT

In this study, we used real-time quantitative PCR (RT-qPCR) to evaluate the expression of 32 genes of Xanthomonas axonopodis pv. citri related to pathogenicity and virulence that are also involved in copper detoxification. Nearly all of the genes were up-regulated, including copA and copB. Two genes homologous to members of the type II secretion system (xcsH and xcsC) and two involved in the degradation of plant cell wall components (pglA and pel) were the most expressed in response to an elevated copper concentration. The type II secretion system (xcs operon) and a few homologues of proteins putatively secreted by this system showed enhanced expression when the bacteria were exposed to a high concentration of copper sulfate. The enhanced expression of the genes of secretion II system during copper stress suggests that this pathway may have an important role in the adaptative response of X. axonopodis pv. citri to toxic compounds. These findings highlight the potential role of these genes in attenuating the toxicity of certain metals and could represent an important means of bacterial resistance against chemicals used to control diseases.

Key words: copper resistance, citrus canker, real-time quantitative PCR.

The genus Xanthomonas includes pathogenic bacteria that are highly damaging to a number of economically important plant hosts, including citrus species. Xanthomonas axonopodispv. citri is the cause of citrus canker, with most commercial citrus varieties being moderately to highly susceptible to this disease. Typical symptoms of citrus canker are circular, necrotic spots with a water-soaked margin surrounded by a yellow halo on leaves and fruits. Heavily affected plants suffer defoliation, dieback and fruit drop.

The main strategies for controlling citrus canker include quarantine measures to prevent the introduction and establishment of bacteria in orchards, and the use of copper compounds to reduce contamination and dissemination of the disease. The use of copper sprays is a major preventive measure in most integrated management programs. The application of copper to young citrus leaves protects against infection, but this protection is quickly lost because of the fast expansion of the leaf surface area. Indeed, copper compounds are less effective in preventing leaf infection than in preventing fruit infection, primarily because of the slower growth rate of the latter.

Copper induces metabolic changes in several plantassociated bacteria, such as Rhizobium leguminosarum, Agrobacterium tumefaciens, Ralstonia solanacearum, Xanthomonas campestris pv. campestris, and Erwinia amylovora, as part of the survival strategy of these microorganisms (Alexander et al., 1999; Colwell, 2000; Grey and Steck, 2001a,b: da Silva et al., 2002). X. axonopodis pv. citri contains homologues to genes (copA, copB, cutC and dsbD) that are closely related to resistance against toxic levels of copper in other xanthomonads and Pseudomonas syringae (Lee at al., 1994; Mellano and Cooksey, 1988; Mills et al., 1993; Voloudakis et al., 2005; Teixeira et al., 2008). Much of the information available on the factors that affect X. axonopodis pv. citri and its response to copper has been deduced from other bacteria (Basim et al., 2005; Voloudakis et al., 2005). However, recently, the operon copAB of X. axonopodis pv. citri was shown to involved in the copper resistance of this species (Teixeira et al., 2008).

We have previously reported the expression of 279 genes of X. axonopodis pv. citri putatively involved in modulating the pathogenicity and virulence of this species, including resistance to toxic compounds (Astua-Monge et al., 2005). To understand the global response of X. axonopodis pv. citri to copper, we used real-time quantitative PCR to examine the profile of 32 of the 279 genes putatively associated with pathogenicity and virulence. Almost all of the genes were up-regulated. Two genes homologous to members of the type II secretion system (xcsH and xcsC) and two involved in the degradation of plant cell wall components (pglA and pel) were the genes most expressed in response to an elevated concentration of copper.

To examine the gene expression in response to a high concentration of copper in vitro, X. axonopodis pv. citri strain 306 was grown overnight in 200 mL of nutrient broth (5 g of peptone/L and3gof meat extract/L, pH 7.0) and then centrifuged (10,000 x g, 4 ºC, 15 min). The bacteria were harvested and resuspended in 285 mL of M9 minimum medium (Na₂HPO₄ 6 g/L, KH₂PO₄ 3 g/L, NaCl 0.5 g/L and NH₄Cl 1 g/L) to which 0.2 mM CuSO₄ was added after filtration through a 0.45 /m filter; this concentration of CuSO₄ corresponded to the minimum inhibitory concentration (MIC) and was determined by growing bacteria in M9 medium supplemented with 0.04, 0.08, 0.12 and 0.20 mM CuSO₄. Control cultures contained the same medium but without copper. The cultures were incubated at 28 ºC overnight with shaking (100 rpm) and aliquots of 50 mL were harvested after 2, 4, 6, 8, 10 and 12 h, centrifuged and stored at -80 ºC. The six samples were subsequently pooled and used for RNA extraction. All of the experiments were done in triplicate.

Total RNA was extracted by lysing the bacterial cells with lysozyme (0.5 mg/mL in Tris-HCl/EDTA buffer, pH 8.0) followed by incubation with 10% SDS at 64 ºC and treatment with chloroform. The RNA samples were treated with DNase (DNase I Amp Grade, Invitrogen) according to the manufacturers instructions followed by purification with phenol, phenol:chloroform (50:50, v/v) and chloroform. Finally, the RNA samples were precipitated with 3 M sodium acetate and 100% cold ethanol and stored at -80 ºC until required. Contamination by DNA was confirmed by PCR using specific primers for the gene avrXacE1 from X. axonopodis pv. citri.

cDNA was synthesized in random hexamer-primed reactions from approximately 5 /g of DNase I-treated RNA by single-step reverse transcription RT-PCR done according to the protocol provided by Invitrogen for M-MLV. Briefly, to each RNA sample were added 0.5 /L of random primer (3 µg/µL), 1 /L of 10 mM dNTPs and DEPCtreated water to a final volume of 12 µL. The samples were incubated at 68 ºC for 15 min and then immediately placed on ice for 3 min. A second reaction was prepared by using 5X first-strand buffer, 0.1 M DTT, RNase-out and M-MLV reverse transcriptase followed by incubation in a water bath 37 ºC for 1 h.

The level of abundance of the pathogenicity-related genes acvB, avrBs2, avrXacE1, avrXacE2, celD, copA, copB, cutC, egl, gumB, gumG, gumM, hpaA, hrcR, hrcT, hrpB1, hrpG, ostA, pel, pglA, rpfC, rpfE, rpfF, virB8, virD4, virK, xanB, xcsC, xcsH, xpsD, xpsL, and xrvA, and transcripts over time relative to the lrp gene (leucine-responsive regulatory protein gene, used as an internal control) was analyzed by RT-qPCR. Primers for PCR were designed to amplify internal fragments of 100-200 bp in each open reading frame (Table 1) and were tested for amplification specificity and efficiency. Each reaction was done in a total volume of 25 µL that contained 1 µL of cDNA (60 ng/µL), 2.5 mM of each primer and 12.5 µL of SYBR Green PCR Master Mix kit (PE Applied Biosystems, Foster City, CA). The cycling conditions used were 2 min at 50 ºC, 10 min at 95 ºC and 40 cycles of 30 s at 95 ºC and 1 min at 60 ºC, with a final extension of 10 min at 72 ºC. The cDNA was quantified with an ABI Prism 7500 sequence detection system (PE Applied Biosystems). The comparative cycle threshold method was used to analyze the data, as described by the manufacturer (PE Applied Biosystems). The ΔΔCt method was used to calculate the relative amount of specific RNA present in a sample, from which the fold induction of gene transcription was estimated by comparison to the values for control colonies grown in the same minimal medium but with no addition of copper. Each PCR was done in triplicate and the mean data from 2-3 experimental replicates are reported.

Although a number of X. axonopodis pv. citri genes have been implicated in processes related to detoxification (da Silva et al., 2002), little is known about the regulation of the copper stress response in this species. A better understanding of the pathways involved in resistance to copper could be useful in identifying potential target genes for further studies. In this work, we used qPCR to examine the response of X. axonopodis pv. citri after exposure to an elevated concentration of copper sulfate for up to 12 h. The genes investigated here were chosen based on the results of a previous study that used DNA macroarrays (Astua-Monge et al., 2005) (Table 1).

The level of gene expression was estimated based on the cycle threshold (Ct) values and the use of standard curves. In all cases, the data were normalized relative to the constitutively expressed lrp gene. The lrp gene encodes a major transcriptional regulatory protein involved in the control of at least 75 genes in E. coli (Newman et al., 1992), and Lrp homologues are involved in the regulation of amino acid metabolism (Brinkman et al., 2003). This gene was chosen as an internal control because previous experiments had shown that its transcript levels were not significantly altered compared to those of other genes (pthA, rpo, nuoB, petC and 16S rRNA). In addition, this gene is universally present in Xanthomonas spp. and has been used to assess the phylogenetic relationships within this genus (Cubero and Graham, 2004, 2005).

In the present study, some of the operons chosen for analysis were clusters from which the initial, central and terminal genes were used to monitor transcription. Overall, gene expression in the presence of copper was up-regulated by 0.03-5.72 fold (Table 1).

RT-qPCR indicated that the transcripts of two transporters (xcsC and xcsH) and a protein involved in the degradation of plant cell wall components (pel) were nearly five-fold higher in medium containing copper compared to that without copper. In addition, the expression of pglA,another homologous protein involved in the degradation of plant cell wall components, was approximately two-fold higher in the presence of copper. The copA and copB genes, which are directly associated with copper resistance (Russel, 1998), also showed enhanced expression in the presence of copper, but at a lower level than for transporter (xcsH and xcsC) and exoenzyme (pglA and pel) genes.

The homologue genes xcsH and xcsC (OK) encode putative transport proteins of the type II secretory apparatus involved in the translocation of exoproteins from the cytoplasm to the periplasm. Interestingly, all of the other homologous proteins, i.e., those involved in degrading plant cell wall components, that showed higher expression during copper stress may also be translocated by the type II secretion systems (Russel, 1998; Jha et al., 2005; Johnson et al., 2006).

Although most of the genes examined here were only slightly up-regulated, a set of four genes related to pathogenicity and virulence showed markedly enhanced expression, including two type II secretion system components and two genes involved in degrading components of plant cell walls. These genes are associated with pathogenicity and virulence-related genes of X. axonopodis pv. citri identified in hrp-inducing medium (XVM2) (Astua-Monge et al., 2005). Since it is not feasible to reproduce in vitro the restrictive environmental conditions required to identify all of the X. axonopodis pv. citri genes involved in plant colonization there is a need for individual analysis of the key virulence factors involved in this process.

The type II secretion system is used by various Gram-positive bacteria to transport a large number of secreted proteins, including major virulence factors (such as pectate lyases, cellulases, proteases, toxins and alkaline phosphatases) and other proteins associated with the induction of plant defense responses, from the periplasmic space to the extracellular environment (Russel, 1998; Jha et al., 2005; Johnson et al., 2006). Interestingly, X. axonopodis pv. citri contains two copies (xps and xcs operons) of this machinery, but there is no homology between the two clusters. Although X. axonopodis pv. citri harbors two type II secretion systems (xps and xcs), only xcs was expressed to a significant extent. These two systems are probably involved in the secretion of different exoproteins, as in Pseudomonas aeruginosa, which has two functional type II systems (Filloux et al., 1998; Ball et al., 2002). Despite the fact that bacterial secretion systems are important for host-pathogen interactions, in many bacteria the type II secretion system is responsible for the transport of a number of virulence-associated proteins (Iwobi et al., 2003; Arrieta et al., 2004; Rossier et al., 2004; Soderberg et al., 2004).

In X. axonopodis pv. citri the copAB operon is specifically induced by copper (Teixeira et al., 2008). We also observed up-regulation of copA and copB, but to a lower extent than for genes associated with secretion systems. Neither of the transcripts was detected in incubations without copper but showed enhanced expression in the presence of this metal (Table 1). Since X. axonopodis pv. citri is copper-sensitive, the apparent difference in the expression of copA and copB may be related to the method of transcript detection (northern blot versus RT-qPCR) or to the activity of copper in the medium. In our experiments, the MIC was estimated in inorganic medium (M9) that lacked chelating agents usually present in organic media such as TSA (1% trypone, 1% sucrose and 0.1% sodium glutamate) or nutrient broth (see Material and Methods). On the other hand, there could be a direct relationship between the external concentration of copper and expression of the copAB operon. Since the MIC values obtained using different culture media cannot be compared, the corresponding levels of gene expression are also not directly comparable. Despite the absence of copC and copD in the cop operon of X. axonopodis pv. citri, the bacteria were apparently able to detoxify copper at low concentrations that affected growth but did not kill the cells.

Although a lack of growth in the presence of high levels of copper is generally considered to be indicative of cell death, this absence of growth could also result from the cells entering the viable but non-culturable (VBNC) state (Grey and Steck, 2001b). This state is defined as one in which cells are viable but do not undergo sufficient division to allow visible growth in non-selective media (Colwell, 2000). After exposure to a high concentration of copper sulfate, E. amylovora cells in the VBNC state regained their ability to grow and their pathogenicity (Ordax et al., 2006). Our results indicate that copper may cause X. axonopodis pv. citri to enter the VBNC state.

In contrast to Cupriavidus metallidurans, a model organism remarkable for its copper-resistance in which exposure to elevated Cu(II) concentrations results in gene inductions of 2-to 1159-fold (Monchy et al., 2006), the copper-resistance genes of X. axonopodis pv citri were only slighly up-regulated by exposure to copper. In E. amylovora, another bacterial plant pathogen, the MIC of copper sulfate in solid medium was 3.5 mM Cu²⁺, which was 70 times higher than the highest copper concentration (0.05 mM Cu²⁺) used in the survival experiments (Ordax et al., 2006). In Xanthomonas campestris pv. juglandis, the expression of all four ORFs (copABCD) that showed homology with the operons for tolerance against copper was increased following exposure to copper; this enhanced expression was required for full resistance to this metal (Lee et al., 1994).

In some organisms, the cop operon is induced by copper, which allows growth in the presence of high levels of copper compounds (up to 5 mM) used for disease control in agricultural crops. In C. metallidurans, a bacterial species with a notorious resistance to metals, resistance to copper is represented by two gene clusters that putatively encode periplasmic resistance (copSRABCD and copVTMKNSRABCDIJGFLQHE), with maximal expression at 0.4 mM Cu (Monchy et al., 2006).

In conclusion, the results described here indicate that exposure to copper induces the differential expression of several pathogenicity-related genes in X. axonopodis pv. citri. The most highly induced genes (such as the xcs operon, pel and pglA) are related to high levels of copper and transport, whereas the genes involved in other activities showed a lower level of induction. The responsive genes xcsC and xcsH are members of the type II secretion system, which confirms the importance of this system in the response to copper compounds in X. axonopodis pv. citri. Whether the enhanced expression of these genes in response to a high copper concentration is associated with a mechanism of detoxification or is simply a response to the presence of copper as a co-factor remains to be determined. The identification of a type II secretion system as a component involved in the response of X. axonopodis pv. citri is an essential step towards a more comprehensive understanding of the role of these genes in bacterial adaptation to copper-induced stress.

Acknowledgments

The authors thank PRODETAB and FAPESP for financial support. AMA and MAM are supported by research fellowships from CNPq.

Received: February 2, 2009; Accepted: October 14, 2009.

Associate Editor: Luis Carlos de Souza Ferreira

License information: This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

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Publication Dates

• Publication in this collection
  02 Apr 2010
• Date of issue
  2010

History

• Received
  02 Feb 2009
• Accepted
  14 Oct 2009