- Research article
- Open Access
Genetic relationships among Italian and Mexican maize-rhizosphere Burkholderia cepacia complex (BCC) populations belonging to Burkholderia cenocepaciaIIIB and BCC6 group
BMC Microbiology volume 11, Article number: 228 (2011)
A close association between maize roots and Burkholderia cepacia complex (BCC) bacteria has been observed in different locations globally. In this study we investigated by MultiLocus Restriction Typing (MLRT) the genetic diversity and relationships among Burkholderia cenocepacia IIIB and BCC6 populations associated with roots of maize plants cultivated in geographically distant countries (Italy and Mexico), in order to provide new insights into their population structure, evolution and ecology.
The 31 B. cenocepacia IIIB and 65 BCC6 isolates gave rise to 29 and 39 different restriction types (RTs), respectively. Two pairs of isolates of B. cenocepacia IIIB and BCC6, recovered from both Italian and Mexican maize rhizospheres, were found to share the same RT. The eBURST (Based Upon Related Sequence Types) analysis of MLRT data grouped all the B. cenocepacia IIIB isolates into four clonal complexes, with the RT-4-complex including the 42% of them, while the majority of the BCC6 isolates (94%) were grouped into the RT-104-complex. These two main clonal complexes included RTs shared by both Italian and Mexican maize rhizospheres and a clear relationship between grouping and maize variety was also found. Grouping established by eBURST correlated well with the assessment using unweighted-pair group method with arithmetic mean (UPGMA). The standardized index of association values obtained in both B. cenocepacia IIIB and BCC6 suggests an epidemic population structure in which occasional clones emerge and spread.
Taken together our data demonstrate a wide dispersal of certain B. cenocepacia IIIB and BCC6 isolates in Mexican and Italian maize rhizospheres. Despite the clear relationship found between the geographic origin of isolates and grouping, identical RTs and closely related isolates were observed in geographically distant regions. Ecological factors and selective pressure may preferably promote some genotypes within each local microbial population, favouring the spread of a single clone above the rest of the recombinant population.
The Burkholderia cepacia complex (BCC) is an ubiquitous and extremely versatile group of closely related Gram-negative bacteria, currently divided into 17 species [1, 2]. BCC bacteria emerged in the 1980s as opportunistic human pathogens responsible for devastating lung infections in people with cystic fibrosis and chronic granulomatous disease . BCC has also been shown to colonise natural habitats including agricultural soils, plant rhizospheres, and river waters [4–7]. The maize rhizosphere is a favourable niche for BCC bacteria, probably due to their ability to metabolise at high rates maize root exudates  and has also been suggested to represent a natural reservoir of bacterial strains that may exhibit pathogenic traits [9–13]. A close association between maize roots and BCC has been observed in a number of different locations worldwide [6, 14–17]. Studies on BCC populations recovered from Italian maize rhizosphere have shown the presence of several BCC species such as B. cepacia, B. cenocepacia (recA lineage IIIB), B. ambifaria, B. pyrrocinia, and BCC groups such as BCC5 and BCC6 suggesting possible novel plant associated species within the complex [14, 18–20]. In Mexico, where maize has traditionally been cultivated for thousands of years, B. cenocepacia (recA lineage IIIB) and B. vietnamiensis were isolated with other Burkholderia species from the rhizosphere of local and commercial varieties of maize plants cultivated in distant geographical regions [[21, 22], our unpublished data].
The maize rhizosphere is a dynamic and active environment in which many factors may affect the diversity and activity of microbial communities [23, 24]. The distribution of identical clones among BCC populations recovered from geographically disparate Italian maize rhizospheres suggested that bacterial flow may occur among BCC populations of different geographic areas . Therefore, assessing the diversity of maize-rhizosphere associated BCC species in different and distant countries may provide critical insight into the population structure, evolution and ecology of such BCC populations. Indexing allelic variation in sets of housekeeping genes provides a good basis for estimating overall levels of genotypic variation in microbial populations [25, 26]. Methods based on this principle, such as multilocus restriction typing (MLRT), multilocus enzyme electrophoresis (MLEE), and multilocus sequence typing (MLST), provide good insights into the genetic relationships among strains [27–30]. During the last decade, MLST has emerged as a powerful tool in studies of BCC epidemiology and population structure . MLRT has a lower discrimination power than MLST, but acceptable turnaround time and lower cost make it really advantageous, especially for an 'in-house' initial genotype screening of isolates collected in large-scale [32–34]. Furthermore, MLRT has been used to study the global epidemiology and the population structure of B. cenocepacia [26, 32], Streptococcus pneumoniae  and Helicobacter pylori , as well as to determine the genetic relationships among strains of Neisseria meningitidis [25, 36], Staphylococcus aureus , Escherichia coli  and Yersinia enterocolitica biovar 1A . The successful application of MLRT in these studies and the excellent correlation with MLST results [36, 37] demonstrate its wide range of potential applications.
In the current study, we investigated the genetic relationships in B. cenocepacia IIIB and BCC6 populations associated with roots of maize plants cultivated in two distant countries (Italy and Mexico). Assessment was carried out by applying the MLRT scheme specifically developed for B. cenocepacia  also to BCC6 group, since it includes bacteria previously assigned to B. cenocepacia by means of recA polymorphism based tests [19, 20]. We focused on B. cenocepacia IIIB as it is widely spread in both Italian and Mexican rhizospheres [[20, 22], our unpublished data], besides its importance as an opportunistic pathogen in patients with cystic fibrosis , and on the underappreciated BCC6 group as it has only been isolated from Italian maize rhizosphere , although its real distribution has most likely been masked by B. cenocepacia IIIB. As the maize historically originates from Mexico, we have chosen to compare representatives isolates of our Italian B. cenocepacia IIIB and BCC6 collections with Mexican ones in order to provide new insights into maize-rhizosphere bacterial populations. In particular, we aimed to (i) describe the genetic structure of bacterial populations by evaluating the extent of linkage equilibrium between the different loci, (ii) assess whether the geographic origin of isolated bacteria influences the extent of their genetic diversity, and (iii) individuate the genetic similarities among the restriction types of B. cenocepacia IIIB and BCC6 group.
RTs distribution among maize-rhizosphere BCC populations
For each of the five loci (recA, gyrB, fliC, cepIR and dsbA), amplified products of the expected size were obtained in each of the 96 BCC isolates (Tables 1 and 2). The number of different alleles present per locus in the B. cenocepacia IIIB population included: 4 (recA), 6 (gyrB), 6 (fliC), 7 (cepIR), and 2 (dsbA). While in the BCC6 population this differed slightly: 1 (recA), 7 (gyrB), 6 (fliC), 7 (cepIR), and 2 (dsbA). The frequency of each allele within each bacterial population is shown in Figure 1. In the B. cenocepacia IIIB population, gyrB and cepIR loci showed the highest diversity (h = 0.8108 and h = 0.8000, respectively), while dsbA and recA loci showed the lowest diversity (h = 0.4903 and h = 0.5140, respectively); in the BCC6 population, cepIR and gyrB loci showed a high diversity (h = 0.7702 and h = 0.7582, respectively), while no polymorphism was observed within recA locus (h = 0.0000). The mean genetic diversity (H mean ) was 0.6576 ± 0.0680 for all B. cenocepacia IIIB isolates and 0.4918 ± 0.1427 for all BCC6 isolates (Table 3).
A restriction type (RT) for each isolate was generated by combining information for each of the five loci. MLRT divided the 31 B. cenocepacia IIIB and the 65 BCC6 isolates into 29 and 39 different RTs, respectively (Tables 1 and 2). Some BCC isolates from Mexico and Italy were found to share identical RTs; i.e., RT-21 was shared by two B. cenocepacia IIIB isolates (MDIII-P378 and MexII-864) and RT-55 was shared by two BCC6 isolates (MDIII-T18 and MexII-829). Many RTs were found to type more than one isolate within the Italian BCC6 population (RT 26, RT 34, RT 35, RT 37, RT 79, RT 81, RT 82, RT 95, RT 98, RT 104, RT 106) and the Mexican BCC6 population (RT 59, RT 60) (Table 2). This was also seen in the case of one RT in the B. cenocepacia IIIB population (RT 7) (Table 1).
Genetic relationships among isolates
Using the eBURST algorithm, clonal complexes or closely related RTs were defined as groups in which each isolate is identical to at least one other isolate at four of the five loci. In addition, within each major clonal complex, the putative ancestral genotype was defined as the RT that differs from the largest number of other RTs at only a single locus, and the single-locus variants (SLVs) as the RTs that differ from the ancestral genotype at only one locus. RTs which differ from all other RTs at more than two loci were designated as singleton RTs.
Within the B. cenocepacia IIIB population, 19 isolates (61%) were distinguished by 15 RTs and grouped into four clonal complexes, while the remaining 12 isolates (8 Italian and 4 Mexican) were characterized as singleton RTs. RT-4-complex, with RT4 (typing one Mexican isolate) as its putative ancestral genotype, represented the major clonal complex since it included 42% of isolates (11 Mexican and 2 Italian isolates), with RT 115 (one Italian isolate), RT 21 (one Mexican and one Italian isolates), RT 31 (one Mexican isolate), and RT 6 (one Mexican isolate) as SLVs of the predicted primary founder. The other three clonal complexes included few isolates and then may be considered as doublets of RTs (Table 1 and Figure 2). As far as the BCC6 group is concerned, the eBURST algorithm grouped most of the BCC6 isolates (94%) into one clonal complex, designated RT-104-complex, with RT104 (typing two Italian isolates) as putative ancestral genotype, while four isolates (two Italian and two Mexican) were branded as four singleton RTs. The RT-104-complex included 35 RTs (typing 51 Italian and 10 Mexican isolates), with RT54 (typing one Mexican isolate) and RT 37, RT 82, RT85, RT98, RT106 and RT116 (typing Italian isolates) as SLVs of the predicted primary founder (Table 2 and Figure 2).
The genetic relationships among isolates belonging to the major complexes of B. cenocepacia IIIB and BCC6 populations (RT-4-complex and RT-104-complex, respectively) as well as to the other minor complexes and singletons are shown in Figure 3. The dendrogram constructed using the UPGMA algorithm in BioNumerics revealed that all isolates were grouped in two main clusters, corresponding to the major eBURST clonal complexes. The major cluster (I) included the BCC6 RT-104 clonal complex, while the cluster II comprised the B. cenocepacia IIIB RT-4 clonal complex. Interestingly, within the cluster I, which mostly comprised the BCC6 isolates, the B. cenocepacia IIIB eBURST groups 1 and 2 were also present, while two BCC6 isolates (MDIII-T258 and MexII-992) belonging to the RT-104 clonal complex fell within the cluster II which mostly included B. cenocepacia IIIB isolates.
Standardized index of association () and population structure
Evidence for recombination and clonality in B. cenocepacia IIIB and BCC6 rhizosphere populations was assessed using standardized index of association (). A value differing from zero characterizes clonal population (linkage disequilibrium), while a value close to zero characterizes freely recombining population (linkage equilibrium). values including all rhizosphere isolates or single representatives of each RT were calculated separately to put in evidence bias due to epidemic structure for (i) the entire B. cenocepacia IIIB population, (ii) the Italian B. cenocepacia IIIB population, (iii) the Mexican B. cenocepacia IIIB population, (iv) the entire BCC6 population, (v) the Italian BCC6 population, and (vi) the Mexican BCC6 population (Table 3). In the B. cenocepacia IIIB population, the value of calculated considering all 31 isolates differed significantly from zero (; P = 0.0187) indicating a high level of linkage disequilibrium and a non-random association among alleles at different loci. decreased when only single representatives of each RT were included (; P = 0.127), suggesting a random association between alleles in some subgroups (linkage equilibrium). In the BCC6 population, the value calculated including all 65 isolates was 0.0296 (P = 0.025), indicating a linkage disequilibrium which disappeared when the analysis was repeated with each RT treated as an individual (P > 0.05), suggesting a possible epidemic population structure in which occasional clones emerge and spread.
Considering each bacterial population according to its geographic origin, a random association among the alleles (linkage equilibrium) within the Italian B. cenocepacia IIIB population was found either when all isolates or each RT treated as an individual were considered (P > 0.05); conversely, the Mexican B. cenocepacia IIIB population showed linkage disequilibrium at both levels (Table 3). Linkage disequilibrium was also observed within the Italian BCC6 population when all 53 isolates were considered (; P = 0.0002); conversely, when the analysis was restricted to RTs taken as units, linkage equilibrium was found (; P > 0.05). Within the Mexican BCC6 maize rhizosphere population, linkage equilibrium was found either when all isolates or RTs taken as units were considered (P > 0.05).
In this study, 96 isolates belonging to the species B. cenocepacia IIIB and the BCC6 group, recovered from maize rhizosphere in Italy and Mexico, were characterized by using MLRT, in order to investigate the genetic diversity and relationships of bacteria associated with maize cultivated in geographically distant locations. Despite the clear relationship found between the geographic origin of isolates and grouping, identical RTs and closely related isolates were observed in geographically distant regions (Mexico and Italy). Two main complexes were identified following eBURST analysis, namely RT-4 for B. cenocepacia IIIB and RT-104 for BCC6. These two main clonal complexes included RTs shared by both Italian and Mexican maize rhizospheres, suggesting some mixing of the genotypes between the two continental regions and excluding the possibility of any kind of geographic subspeciation in the formation of these two complexes. At the genus and species level, many prokaryotes have a cosmopolitan distribution in their respective habitats and the same genotypes have often been identified in similar habitats in different geographic areas . The wide geographic distribution and substantial capability of Burkholderia spp. to colonize diverse host plants was observed in distantly separated environments [21, 24], as well as genetic identity between BCC isolates of clinical and environmental origins recovered from different countries has been proved . Grouping isolates by eBURST analysis is useful to better evaluate the RTs distribution in natural population where highly similar RTs are found, i.e. to elucidate the meaning of the presence of closely related strains in geographically separated maize rhizospheres in respect to niche specificity and adaptation. Our finding that the majority of BCC6 isolates are part of RT-104-complex suggests that large networks of closely related BCC6 isolates colonize the maize rhizosphere of plants cultivated in Italy and Mexico. On the other hand, the presence of four clonal complexes and 12 singletons within the B. cenocepacia IIIB population suggests that maize rhizosphere is commonly colonized by well adapted B. cenocepacia IIIB clones rather than large networks of closely related isolates.
In spite of its lower discriminatory power in respect to MLST (restriction fragments vs sequences), MLRT provides useful data for typing and structure population investigations [26, 28, 32, 35]. Previous MLST analyses performed on 26 Italian BCC isolates examined in the present work indicate a good correspondence between RTs and sequence types (STs) for certain isolates: i.e., three BCC6 isolates, typed by RT 34, had ST 127, and four isolates, typed by RT 81, had ST132 . Conversely, MLST and MLRT data do not always match and the same ST for different RTs as well as different STs for the same RT were occasionally found . Considering that MLRT and MLST do not rely on the same loci, we cannot strictly correlate our MLRT results with the MLST sequence database. Indeed, a previous study on S. aureus isolates  revealed that MLRT performed on the same seven loci used in MLST captures about 95% of the discrimination power of MLST, and demonstrated that MLRT approach represents a convenient alternative to MLST. The analyses of MLRT data using tools developed for MLST permit to assess clonality/recombination in our maize-rhizosphere populations. This is an important feature when assessing the risks for human health posed by opportunistic pathogens present in the natural environment. Bacterial population structures can vary from the extremes of strictly clonal to panmictic, with most populations occupying a middle ground where recombination is significant in the evolution but the emergence of epidemic clonal lineages can also occur [41–44]. The difference in the values between complete and corrected data sets (when the RTs are taken as units) suggests that both B. cenocepacia and BCC6 group have an epidemic population structure in which occasional clones emerge and spread. Both populations are recombining in the long term but a few RTs have recently become abundant and widespread [20, 42]. Similar "epidemic" population structure has been observed in global collections of B. cenocepacia , and may occur continuously in microbial populations not affected by the severe selective constraints imposed by human activity . The values calculated on a subset of isolates chosen on the basis of geographical origin evidenced a population structure different from that obtained considering the entire dataset. Concerning the BCC6 group, the Italian population behaved like the whole BCC6 population, showing linkage equilibrium only when RTs were taken as units (epidemic structure), while the Mexican population showed linkage equilibrium at all levels (freely recombining population structure). Regarding the B. cenocepacia IIIB populations, the Italian one was freely recombining, while the Mexican one had a clonal structure. Nevertheless, the values of the Mexican population are quite low, which may indicate that some recombination occurs. Recombination has had an important role in the long-term evolution of B. cenocepacia and it was also found among strains from different locations [20, 32]. Most likely, the efficiency of genetic exchange mechanisms, due to BCC inherent genomic plasticity, together with ecological factors, play a crucial role.
The use of a common MLRT scheme for both B. cenocepacia IIIB and BCC6 group allowed to compare their genetic variability, relatedness, and population structure also at interspecific level. B. cenocepacia IIIB and BCC6 populations shared identical alleles but not the same RTs. In the UPGMA tree, where the genetic similarities between the restriction profiles of both B. cenocepacia IIIB and BCC6 group were represented, the isolates were grouped into two main clusters (clusters I and II) corresponding to their taxonomic status and eBURST clonal complexes; i.e., cluster I for B. cenocepacia IIIB and RT-4-complex, and cluster II for BCC6 group and RT-104-complex. Within each cluster, the occasional presence of few isolates belonging to the other BCC species is not surprising since BCC6 and B. cenocepacia IIIB are closely related, and indeed BCC6 was previously included in the B. cenocepacia species. UPGMA performed with only the isolates included in the RT-4 and RT-104 clonal complexes gave rise to a dendrogram showing two clusters exactly corresponding to them (data not shown), confirming the correspondence between eBURST and UPGMA grouping. Finally, the finding of a clear relationship between grouping and maize cultivar suggests that maize cultivars could influence rhizosphere bacterial diversity probably due to the different chemical composition of root exudates. In fact, it is well known that plant root bacterial communities are very sensitive to environmental conditions and are more strongly influenced by plant species and different cultivars rather than by other environmental factors such as soil type and agricultural practices [46–49].
In conclusion, our data demonstrate a wide dispersal of certain B. cenocepacia IIIB and BCC6 isolates in Mexican and Italian maize rhizospheres. Despite the clear relationship found between the geographic origin of isolates and grouping, identical RTs and closely related isolates were observed in geographically distant regions. The differences in rhizosphere habitats and/or maize varieties between Italy and Mexico may result in certain selective pressure which may preferably promote some genotypes within each local microbial population, favouring the spread of a single clone above the rest of the recombinant population. Investigation of other important population genetic forces, such as gene flow and natural selection, with more extensive and/or focused sampling, would provide more insight into the spatial and temporal dynamics of BCC populations.
A total of 31 B. cenocepacia recA lineage IIIB isolates (13 from Italian and 18 from Mexican maize-rhizosphere) and 65 BCC6 isolates (53 from Italian and 12 from Mexican maize-rhizosphere) were analysed.
Italian B. cenocepacia IIIB and BCC6 isolates investigated in this work represent a subsample of BCC populations recovered over a 8-year period (1995-2002) from the rhizosphere of different modern commercial varieties of maize cultivated in three fields located in different regions: S. Maria di Galeria, Rome (MC population), Pieve d'Olmi, Cremona (MVP population) and Dragoni, Caserta (MD population). Each bacterial population included distinct sub-populations recovered from the rhizosphere of different maize cultivars: MCII/MCIII in MC population, recovered in 1995 and 1997 from Fir and Pactol cultivars, respectively; MVPC1/MVPC2 in MVP population, recovered in 1996 from Airone and Goldiane cultivars, respectively; MDII/MDIII in MD population, recovered in 1996 and 2002 from Doge and Eleonora cultivars, respectively [[49–53], our unpublished data]. The majority of isolates were recovered by using the semi-selective PCAT medium , while MDIII isolates were selected from three different media (PCAT, TB-T or BAc, as indicated by the letters P, T or B, respectively) [21, 53].
Mexican B. cenocepacia IIIB and BCC6 isolates investigated in this work belong to Burkholderia populations recovered in 2002 from the rhizosphere of maize plants cultivated in two sites located in the State of Morelos: Tetecala (MexII isolates from 57 to 264), where the modern commercial variety named Costeño mejorado was planted, and Amatlipac (MexII isolates from 815 to 1011), where the traditional maize variety named Criollo was planted. After 90-110 days of growth, 16 maize plants were randomly harvested in each site at a distance of 10 m between each other. Roots were excised from plants and loosely adhering soil was removed. The excised roots were randomly grouped into four samples, each comprising four root systems. Afterwards, each root sample was cut into small pieces (0.2-0.7 cm) and mixed thoroughly. Five grams of each mixture were suspended in 10 ml of potassium phosphate buffer (PPB 0.02 M, pH 6.8) added with 50 μl of Tween 80. Each root suspension was shaken by vortexing for 3 min at maximum speed. Samples were serially diluted in PBB and 100 μl of serial dilutions were plated on PCAT medium amended with 100 μg ml-1 of cycloheximide (Sigma) to inhibit fungal growth. Plates were incubated at 29°C for 48 h. Single small colonies (diameter, about 1-2 mm), white or pale yellow with well-defined margins, were randomly picked up from the same dilution of root slurry sample, i.e. 1000-fold dilution from plates containing approximately 50-100 colonies. Isolates were subjected to single-colony isolation on the same medium and cryopreserved at -80°C in 30% glycerol until use.
Isolates were identified by means of HaeIII recA restriction fragment length polymorphism (RFLP) and species-specific PCRs as previously reported . RFLP profiles were compared with those of published reference strains as appropriate. All Italian isolates have been identified at the species level in previous works [19, 20, 22, 52, 53]. Fourteen Mexican isolates characterized by recA RFLP profile J' were identified as B. cenocepacia IIIB, while 12 Mexican isolates showing the recA RFLP profile AD were assigned to BCC6 group (present study). Two Mexican isolates with the RFLP profile I (which gave uncertain identification) and two Mexican isolates with RFLP profiles which were never recovered among BCC reference strains examined were assigned to B. cenocepacia IIIB by MLST analysis (Table 1) .
MLRT characterization and data analysis
DNA preparation, PCR amplification of nearly complete sequence of five open reading frames of recA, gyrB, fliC, cepIR and dsbA genes, enzymatic restriction digests and separation of the resulting restriction fragments were performed as described previously . Gel images were digitalized using GelDoc 2000 (Bio-Rad) and stored as TIFF files. Different restriction patterns for each locus were considered to represent separate alleles, and an arbitrary number was assigned to each allele. The different combinations of alleles for the five loci represented different allelic profiles. An arbitrary number [restriction type (RT)] was assigned to each allelic profile. The different restriction patterns found at each locus were analysed with DNA START-2 (Sequence Type Analysis and Recombination Test, version 2) software package http://pubmlst.org/software/analysis/start2/. RT data sets were also analyzed using the eBURST (Based Upon Related Sequence Types) algorithm v3 http://eburst.mlst.net/. MLRT profiles were also analyzed by means of BioNumerics (Applied Maths) software 6.0. Cluster analysis was carried out on data defined as character type data. A similarity matrix was created by using the unweighted pair group method with arithmetic means algorithm (UPGMA) in order to assess the genetic relationships between the restriction profiles. The cophenetic correlation coefficient was used as a statistical method to estimate the error associated with dendrogram branches, while the Cluster Cutoff method was applied to define the most reliable clusters.
Linkage disequilibrium analysis
The genetic diversity at individual loci (h), the mean genetic diversity (H mean ) and the standardized index of association () were calculated using the LIAN version 3.5 software program (Department of Biotechnology and Bioinformatics University of Applied Sciences Weihenstephan; http://adenine.biz.fh-weihenstephan.de/cgi-bin/lian/lian.cgi.pl) . The , that is independent on the number of loci considered, was calculated as , where VD is the observed variance, Ve is the variance expected for linkage equilibrium, and L is the number of loci analysed. The significance of linkage disequilibrium was tested by a parametric method  as implemented in LIAN 3.5.
Vandamme P, Dawyndt P: Classification and identification of the Burkholderia cepacia complex: Past, present and future. Syst Appl Microbiol. 2011, 34: 87-95. 10.1016/j.syapm.2010.10.002.
Chiarini L, Bevivino A, Dalmastri C, Tabacchioni S, Visca P: Burkholderia cepacia complex species: health hazards and biotechnological potential. Trends Microbiol. 2006, 14: 277-286. 10.1016/j.tim.2006.04.006.
Mahenthiralingam E, Urban TA, Goldberg JB: The multifarious, multireplicon Burkholderia cepacia complex. Nat Rev Microbiol. 2005, 3: 144-156. 10.1038/nrmicro1085.
Coenye T, Vandamme P: Diversity and significance of Burkholderia species occupying diverse ecological niches. Environ Microbiol. 2003, 5: 719-729. 10.1046/j.1462-2920.2003.00471.x.
Miller SCM, LiPuma JJ, Parke JL: Culture-based and non-growth-dependent detection of the Burkholderia cepacia complex in soil environments. Appl Environ Microbiol. 2002, 68: 3750-3758. 10.1128/AEM.68.8.3750-3758.2002.
Balandreau J, Viallard V, Cournoyer B, Coenye T, Laevens S, Vandamme P: Burkholderia cepacia genomovar III is a common plant-associated bacterium. Appl Environ Microbiol. 2001, 67: 982-985. 10.1128/AEM.67.2.982-985.2001.
Vermis K, Brachkova M, Vandamme P, Nelis H: Isolation of Burkholderia cepacia complex genomovars from waters. Syst Appl Microbiol. 2003, 26: 595-600. 10.1078/072320203770865909.
Alisi C, Lasinio GJ, Dalmastri C, Sprocati A, Tabacchioni S, Bevivino A, Chiarini L: Metabolic profiling of Burkholderia cenocepacia, Burkholderia ambifaria, and Burkholderia pyrrocinia isolates from maize rhizosphere. Microbiol Ecol. 2005, 50: 385-395. 10.1007/s00248-005-0223-y.
Berg G, Eberl L, Hartmann A: The rhizosphere as a reservoir for opportunistic human pathogenic bacteria. Environ Microbiol. 2005, 7: 1673-1685. 10.1111/j.1462-2920.2005.00891.x.
LiPuma JJ, Spilker T, Coenye T, Gonzalez CF: An epidemic Burkholderia cepacia complex strain identified in soil. Lancet. 2002, 359: 2002-2003. 10.1016/S0140-6736(02)08836-0.
Payne GW, Vandamme P, Morgan SH, LiPuma JJ, Coenye T, Weightman AJ, Jones TH, Mahenthiralingam E: Development of a recA gene-based identification approach for the entire Burkholderia genus. Appl Environ Microbiol. 2005, 7: 3917-3927.
Baldwin A, Mahenthiralingam E, Drevinek P, Vandamme P, Govan JR, Waine DJ, LiPuma JJ, Chiarini L, Dalmastri C, Henry DA, Speert DP, Honeybourne D, Maiden MCJ, Dowson CG: Environmental Burkholderia cepacia complex isolates in human infections. Emerg Infect Dis. 2007, 13: 458-461. 10.3201/eid1303.060403.
Mahenthiralingam E, Baldwin A, Dowson CG: Burkholderia cepacia complex bacteria: opportunistic pathogens with important natural biology. J Appl Microbiol. 2008, 104: 1539-1551. 10.1111/j.1365-2672.2007.03706.x.
Fiore A, Laevens S, Bevivino A, Dalmastri C, Tabacchioni S, Vandamme P, Chiarini L: Burkholderia cepacia complex: distribution of genomovars among isolates from the maize rhizosphere in Italy. Environ Microbiol. 2001, 3: 137-143. 10.1046/j.1462-2920.2001.00175.x.
Ramette A, LiPuma JJ, Tiedje JM: Species abundance and diversity of Burkholderia cepacia complex in the environment. Appl Environ Microbiol. 2005, 71: 1193-1201. 10.1128/AEM.71.3.1193-1201.2005.
Payne GW, Ramette A, Rose HL, Weightman AJ, Jones TH, Tiedje JM, Mahenthiralingam E: Application of a recA gene-based identification approach to the maize rhizosphere reveals novel diversity in Burkholderia species. FEMS Microbiol Lett. 2006, 259: 126-132. 10.1111/j.1574-6968.2006.00257.x.
Zhang L, Xie G: Diversity and distribution of Burkholderia cepacia complex in the rhizosphere of rice and maize. FEMS Microbiol Lett. 2007, 266: 231-235. 10.1111/j.1574-6968.2006.00530.x.
Dalmastri C, Fiore A, Alisi C, Bevivino A, Tabacchioni S, Giuliano G, Sprocati A, Segre L, Mahenthiralingam E, Chiarini L, Vandamme P: A rhizospheric Burkholderia cepacia complex population: genotypic and phenotypic diversity of Burkholderia cenocepacia and Burkholderia ambifaria. FEMS Microbiol Ecol. 2003, 46: 179-187. 10.1016/S0168-6496(03)00211-3.
Dalmastri C, Pirone L, Tabacchioni S, Bevivino A, Chiarini L: Efficacy of species-specific recA PCR tests in the identification of Burkholderia cepacia complex environmental isolates. FEMS Microbiol Lett. 2005, 246: 39-45. 10.1016/j.femsle.2005.03.041.
Dalmastri C, Baldwin A, Tabacchioni S, Bevivino A, Mahenthiralingam E, Chiarini L, Dowson CG: Investigating Burkholderia cepacia complex populations recovered from Italian maize rhizosphere by multilocus sequence typing. Environ Microbiol. 2007, 9: 1632-1639. 10.1111/j.1462-2920.2007.01273.x.
Estrada-de los Santos P, Bustillos-Cristales R, Caballero-Mellado J: Burkholderia, a genus rich in plant-associated nitrogen fixers with wide environmental and geographic distribution. Appl Environ Microbiol. 2001, 67: 2790-2798. 10.1128/AEM.67.6.2790-2798.2001.
Cesarini S, Bevivino A, Tabacchioni S, Chiarini L, Dalmastri C: RecA gene sequence and multilocus sequence typing for species-level resolution of Burkholderia cepacia complex isolates. Lett Appl Microbiol. 2009, 49: 580-588. 10.1111/j.1472-765X.2009.02709.x.
Garbeva P, Van Elsas JD, Van Veen JA: Rhizosphere microbial community and its response to plant species and soil history. Plant Soil. 2008, 302: 19-32. 10.1007/s11104-007-9432-0.
Compant S, Nowak J, Coenye T, Clement C, Ait Barka E: Diversity and occurrence of Burkholderia spp. in the natural environment. FEMS Microbiol Rev. 2008, 32: 607-626. 10.1111/j.1574-6976.2008.00113.x.
Bennet DE, Cafferkey MT: Multilocus restriction typing: a tool for Neisseria meningitidis strain discrimination. J Med Microbiol. 2003, 52: 781-787. 10.1099/jmm.0.05225-0.
Coenye T, LiPuma JJ: Multilocus restriction typing: a novel tool for studying global epidemiology of Burkholderia cepacia complex infection in cystic fibrosis. J Infect Dis. 2002, 185: 1454-1462. 10.1086/340279.
Maiden MCJ, Bygraves JA, Feil E, Morelli G, Russell JE, Urwin R, Zhang Q, Zhou J, Zurth K, Caugant DA, Feavers IM, Achtman M, Spratt BG: Multilocus sequence typing: a portable approach to the identification of clones within populations of pathogenic microorganisms. Proc Natl Acad Sci USA. 1998, 95: 3140-3145. 10.1073/pnas.95.6.3140.
Muller-Graf CDM, Whatmore AM, King SJ, Trzcinski K, Pickerill AP, Doherty N, Paul J, Griffiths D, Crook D, Dowson CG: Population biology of Streptococcus pneumoniae isolated from oropharyngeal carriage and invasive disease. Microbiology. 1999, 145: 3283-3293.
Musser JM: Molecular population genetic analysis of emerged bacterial pathogens: selected insights. Emerg Infect Dis. 1996, 2: 1-17. 10.3201/eid0201.960101.
Mallik S, Virdi JS: Genetic relationships between clinical and non-clinical strains of Yersinia enterocolitica biovar 1A as revealed by multilocus enzyme electrophoresis and multilocus restriction typing. BMC Microbiol. 2010, 10: 158-10.1186/1471-2180-10-158.
Baldwin A, Mahenthiralingam E, Thickett KM, Honeybourne D, Maiden MCJ, Govan JR, Speert DP, LiPuma JJ, Vandamme P, Dowson CG: Multilocus sequence typing scheme that provides both species and strain differentiation for the Burkholderia cepacia complex. J Clin Microbiol. 2005, 43: 4665-4673. 10.1128/JCM.43.9.4665-4673.2005.
Coenye T, LiPuma JJ: Population structure analysis of Burkholderia cepacia genomovar III: varying degrees of genetic recombination characterize major clonal complexes. Microbiology. 2003, 149: 77-88. 10.1099/mic.0.25850-0.
Hookey JV, Arnold C: A comparison of multilocus sequence typing and fluorescent fragment-length polymorphism analysis genotyping of clone complex and other strains of Neisseria meningitidis. J Med Microbiol. 2001, 50: 991-995.
Olive DM, Bean P: Principles and applications of methods for DNA-based typing of microbial organisms. J Clin Microbiol. 1999, 37: 1661-1669.
Han S-R, Zschausch H-CE, Meyer H-GW, Schneider T, Loos M, Bhakdi S, Maeurer MJ: Helicobacter pylori: clonal population structure and restricted transmission within families revealed by molecular typing. J Clin Microbiol. 2000, 38: 3646-3651.
Dyet KH, Simmonds RS, Martin DR: Multilocus restriction typing method to predict the sequence type of Meningococci. J Clin Microbiol. 2004, 42: 1742-1745. 10.1128/JCM.42.4.1742-1745.2004.
Diep B, Perdreau-Remington F, Sensabaugh GF: Clonal characterization of Staphylococcus aureus by multilocus restriction fragment typing, a rapid screening approach for molecular epidemiology. J Clin Microbiol. 2003, 41: 4559-4564. 10.1128/JCM.41.10.4559-4564.2003.
Helgerson AF, Sharma V, Dow AM, Schroeder R, Post K, Cornick NA: Edema disease caused by a clone of Escherichia coli O147. J Clin Microbiol. 2006, 44: 3074-3077. 10.1128/JCM.00617-06.
Drevinek P, Mahenthiralingam E: Burkholderia cenocepacia in cystic fibrosis: epidemiology and molecular mechanims of virulence. Clin Microbiol Infect. 2010, 16: 821-830. 10.1111/j.1469-0691.2010.03237.x.
Ramette A, Tiedje JM: Biogeography: An emerging cornerstone for understanding prokaryotic diversity, ecology, and evolution. Microbial Ecol. 2007, 53: 197-207. 10.1007/s00248-005-5010-2.
Feil EJ, Spratt BG: Recombination and the population structures of bacterial pathogens. Annu Rev Microbiol. 2001, 55: 561-590. 10.1146/annurev.micro.55.1.561.
Maynard Smith J, Smith NH, O'Rourke M, Spratt BG: How clonal are bacteria?. Proc Natl Acad Sci USA. 1993, 90: 4384-4388. 10.1073/pnas.90.10.4384.
Posada D, Crandall KA, Holmes EC: Recombination in evolutionary genomics. Annu Rev Genet. 2002, 36: 75-97. 10.1146/annurev.genet.36.040202.111115.
Spratt BG, Maiden MCJ: Bacterial population genetics, evolution and epidemiology. Philos Trans R Soc Lond B Biol Sci. 1999, 354: 701-710. 10.1098/rstb.1999.0423.
Whitaker RJ, Grogan DW, Taylor JW: Recombination shapes the natural population structure of the hyperthermophilic archaeon Sulfolobus islandicus. Mol Biol Evol. 2005, 22: 2354-2361. 10.1093/molbev/msi233.
Gomes NCM, Heuer H, Schönfeld J, Costa R, Medonça-Hagler L, Smalla K: Bacterial diversity of the rhizosphere of maize (Zea mays) grown in tropical soil studied by temperature gradient gel electrophoresis. Plant Soil. 2001, 232: 167-180. 10.1023/A:1010350406708.
Heuer H, Kroppenstedt RM, Lottmann J, Berg G, Smalla K: Effects of T4 lysozyme release from transgenic potato roots on bacterial rhizosphere communities are negligible relative to natural factors. Appl Environ Microbiol. 2002, 68: 1325-1335. 10.1128/AEM.68.3.1325-1335.2002.
Chiarini L, Bevivino A, Dalmastri C, Nacamulli C, Tabacchioni S: Influence of plant development, cultivar and soil type on microbial colonization of maize roots. Appl Soil Ecol. 1998, 8: 11-18. 10.1016/S0929-1393(97)00071-1.
Di Cello F, Bevivino A, Chiarini L, Fani R, Paffetti D, Tabacchioni S, Dalmastri C: Biodiversity of a Burkholderia cepacia population isolated from the maize rhizosphere at different plant growth stages. Appl Environ Microbiol. 1997, 63: 4485-4493.
Bevivino A, Sarrocco S, Dalmastri C, Tabacchioni S, Cantale C, Chiarini L: Characterization of a free-living maize-rhizosphere population of Burkholderia cepacia: effect of seed treatment on disease suppression and growth promotion of maize. FEMS Microbiol Ecol. 1998, 27: 225-237. 10.1111/j.1574-6941.1998.tb00539.x.
Dalmastri C, Chiarini L, Cantale C, Bevivino A, Tabacchioni S: Soil type and maize cultivar affect the genetic diversity of maize root-associated Burkholderia cepacia populations. Microbiol Ecol. 1999, 38: 274-283.
Bevivino A, Peggion V, Chiarini L, Tabacchioni S, Cantale C, Dalmastri C: Effect of Fusarium verticillioides on maize-root-associated Burkholderia cenocepacia populations. Res Microbiol. 2005, 156: 974-983. 10.1016/j.resmic.2005.05.007.
Pirone L, Chiarini L, Dalmastri C, Bevivino A, Tabacchioni S: Detection of cultured and uncultured Burkholderia cepacia complex bacteria naturally occurring in the maize rhizosphere. Environ Microbiol. 2005, 7: 1734-1742. 10.1111/j.1462-2920.2005.00897.x.
Burbage DA, Sasser M, Lumsden RD: A medium selective for Pseudomonas cepacia [abstract]. Phytopathology. 1992, 72: 706-
Mahenthiralingam E, Bischof J, Byrne SK, Radomski C, Davies JE, Av-Gay Y, Vandamme P: DNA-Based diagnostic approaches for identification of Burkholderia cepacia complex, Burkholderia vietnamiensis, Burkholderia multivorans, Burkholderia stabilis, and Burkholderia cepacia genomovars I and III. J Clin Microbiol. 2000, 38: 3165-3173.
Jolley KA, Feil EJ, Chan MS, Maiden MCJ: Sequence type analysis and recombinational tests (START). Bioinformatics. 2001, 17: 1230-1231. 10.1093/bioinformatics/17.12.1230.
Haubold H, Hudson RR: LIAN 3.0: detecting linkage disequilibrium in multilocus data. Bioinformatics. 2000, 16: 847-848. 10.1093/bioinformatics/16.9.847.
Haubold B, Travisano M, Rainey PB, Hudson RR: Detecting linkage disequilibrium in bacterial populations. Genetics. 1998, 150: 1341-1348.
Acknowledgements and funding
We are grateful to Lourdes Martínez-Aguilar for technical assistance in the isolation of Mexican BCC strains and Claudio Ferrelli for technical informatics assistance. We also thank Alessandra Pasquo, Silvia Dalmastri, and Ryan Robert (UCC Biomerit Research Centre) for critical revision of the manuscript. We are also very grateful to the editor and the two anonymous reviewers for their suggestions in improving the manuscript. This research was partially funded by grant DGAPA-UNAM IN229005 and grant N.29 of the Italian Ministry of Foreign Affairs (Italian-Mexican Scientific Cooperation 2003-2005).
We dedicate the present study to the memory of the late Dr Jesus Caballero-Mellado (Centro de Ciencias Genómicas, Universidad Nacional Autónoma de México, Cuernavaca, Morelos, Mexico). He greatly contributed to the design of this study as well as he was involved in the discussion of data and manuscript preparation. With Jesus's death, we lost an excellent scientist, a loyal and generous friend, a marvelous speaker, a charming person of the highest sensitivity and nobility. His physical absence will be impossible to overcome, but his memory will live in all of us who were honored with his friendship.
The authors declare that they have no competing interests.
AB conceived and coordinated the study, and drafted the manuscript. BC carried out MLRT and linkage disequilibrium analyses. CC performed UPGMA analysis and prepared the manuscript's figures. SC performed eBURST analysis. LC participated in the design of the study and discussion of data. ST revised the manuscript. JCM contributed to the study design as well as was involved in the discussion of data and manuscript preparation. CD participated in discussion of data, in drafting and revising the manuscript. All authors read and approved the final manuscript.
About this article
Cite this article
Bevivino, A., Costa, B., Cantale, C. et al. Genetic relationships among Italian and Mexican maize-rhizosphere Burkholderia cepacia complex (BCC) populations belonging to Burkholderia cenocepaciaIIIB and BCC6 group. BMC Microbiol 11, 228 (2011). https://doi.org/10.1186/1471-2180-11-228
- Clonal Complex
- Restriction Type
- Burkholderia Cepacia Complex
- Restriction Fragment Length Polymorphism Profile
- Italian Isolate