Chlamydial disease control is increasingly utilised as a management tool to stabilise declining koala populations, and yet we have a limited understanding of the factors that contribute to disease progression. To examine the impact of host and pathogen genetics, we selected two geographically separated south east Queensland koala populations, differentially affected by chlamydial disease, and analysed koala major histocompatibility complex (MHC) genes, circulating strains of Chlamydia pecorum and koala retrovirus (KoRV) subtypes in longitudinally sampled, well-defined clinical groups. We found that koala immunogenetics and chlamydial genotypes differed between the populations. Disease progression was associated with specific MHC alleles, and we identified two putative susceptibility (DCb 03, DBb 04) and protective (DAb 10, UC 01:01) variants. Chlamydial genotypes belonging to both Multi-Locus Sequence Typing sequence type (ST) 69 and ompA genotype F were associated with disease progression, whereas ST 281 was associated with the absence of disease. We also detected different ompA genotypes, but not different STs, when long-term infections were monitored over time. By comparison, KoRV profiles were not significantly associated with disease progression. These findings suggest that chlamydial genotypes vary in pathogenicity and that koala immunogenetics and chlamydial strains are more directly involved in disease progression than KoRV subtypes.
Chlamydial disease is a significant contributing factor affecting population viability in some declining northern Australian koala populations1. Chlamydia pecorum is endemic in almost all koala populations, however, in northern koala populations, it is highly prevalent and causes more severe disease2. In south east Queensland (SE Qld), a population prevalence for chlamydial infection and disease of up to 73% and 53%, respectively, has been reported3,4. Chlamydial infections predominantly cause inflammatory and fibrotic disease in the eyes and urogenital tract of susceptible koalas5,6,7, and can result in blindness, infertility and death2. Consequently, population management programs that incorporate chlamydial disease control, as well as manage concurrent threats, can reverse the extinction trajectory of these declining populations1,8. The success of these management interventions relies on a thorough understanding of chlamydial epidemiology in koalas, however this understanding has been limited by a lack of comprehensive, longitudinal population studies9 and the complexity of host–pathogen interactions.
Chlamydial disease progression in koalas is likely multifactorial, and associations with the chlamydial strain and infection load, co-infection with koala retrovirus (KoRV) and variation in koala immune genes have been identified as contributing factors. Chlamydial strain typing in one SE Qld population, using a fragment of the ompA gene, found that koalas with genotype F/F´ infections at their urogenital tract site and genotype E´ infections at their ocular site were significantly more likely to progress to disease9. Conversely, koalas with genotype G infections generally did not progress to disease10 and Victorian (Vic) koalas with genotype B infections only displayed mild signs of disease11. Further, chlamydial strain typing in a New South Wales (NSW) population, using Multi-Locus Sequence Typing (MLST), suggested that increased disease expression in the population may have been due to the introduction of a novel chlamydial strain12. Another identified predictor of disease progression in koalas is the load of chlamydial organisms in the urogenital tract13. A longitudinal study in SE Qld found a significant correlation between higher urogenital tract infection loads and progression to disease9. In addition, significantly higher infection loads were detected in the eyes and urogenital tract of hospitalised SE Qld koalas with active disease14. Co-infection with particular KoRV subtypes has also been linked to disease progression, with KoRV-B infection linked to chlamydial disease in SE Qld koalas15 and KoRV-A infection linked to ‘wet bottom’ in Vic koalas16. Finally, Class II major histocompatibility complex genes (MHC) have been associated with chlamydial disease in koalas, with the absence of DBb allele 0313 and the presence of DAb allele 10 and DBb allele 0417 linked to disease. The contrasting pattern of chlamydial disease prevalence and severity between northern and southern koala populations may be due to regional differentiation of these host and pathogen genotypes4,18,19.
Several suggested biogeographical barriers have been identified on the eastern coast of Australia, where climate-driven habitat fragmentation in the late Pleistocene era is thought to have contributed to the genetic divergence of some species20,21,22. One of these biogeographical barriers, the Brisbane Valley barrier (BVB), might have impacted the phylogeography of the koala23. Although a recent large-scale analysis of mitochondrial DNA control regions (CR) in koalas supported historical genetic connectivity across their range, it did identify four weakly differentiated lineages in SE Qld24. These occurred in three geographic clusters, with two northern lineages separated from a central lineage by the BVB24. These lineages were also supported by a study using single nucleotide polymorphisms (SNPs) mapped to the koala genome23. As ongoing habitat fragmentation continues to drive genetic divergence in these lineages, both the koala and its key infectious agents, C. pecorum and KoRV, are likely to be affected. This divergence provides a unique opportunity to study the impact of specific genetic variants on chlamydial disease outcomes.
To better understand the major factors associated with chlamydial disease progression in koalas, we longitudinally sampled two SE Qld koala populations known to be differentially affected by chlamydial disease and occurring approximately 70 kms apart on either side of the BVB23,24. Koalas from these populations were classified into well-defined clinical groups and their infecting chlamydial genotypes, immunogenetics and KoRV subtypes were characterised. Assessment of these three major parameters determined that koala immunogenetics and chlamydial genotype had the most direct effect on koalas progressing to chlamydial disease, in these populations. This improved understanding of chlamydial epidemiology will assist with koala population management, including translocation risk assessments, habitat restoration and selective breeding programs, maximising the effectiveness of management interventions and ensuring successful conservation outcomes.
In this study, koalas from two geographically separated populations in SE Qld, at the Moreton Bay site (MB)9 and the Old Hidden Vale site (HV), underwent regular field monitoring and clinical examinations approximately every 6 months (or more frequently if required for health or welfare concerns). Blood samples, ocular conjunctival swabs and a urogenital tract swab were collected during each clinical examination. From these samples, C. pecorum load and genotype, koala MHC immunogenetics and KoRV proviral subtypes were determined. These results were evaluated in the context of clinical records compiled at the time of sample collection, which included chlamydial disease status.
Chlamydial epidemiology at each study site
The overall prevalence of chlamydial infection and disease differed between the study sites
Longitudinal monitoring of 24 HV koalas (over 113 individual sampling points) identified 24 chlamydial infections for strain typing analysis and eight new chlamydial infections for disease progression analysis. This complemented longitudinal monitoring of 148 MB koalas (over 479 individual sampling points)9 that identified 76 chlamydial infections for strain typing analysis and 38 new chlamydial infections for disease progression analysis. Overall, there was a significantly higher prevalence of infection at HV (58%, 14/24) compared to MB (35%, 89/254)26 (Fisher’s exact test p = 0.028) (Table 1), as well as a significantly higher prevalence of disease at HV (58%, 14/24) compared to MB (27%, 75/279) 26 (Fisher’s exact test p = 0.002).
Chlamydial disease progression was common at both study sites
A total of eight HV koalas met our study inclusion criteria for disease progression analysis by having a new chlamydial infection detected at the ocular (n = 1) or urogenital tract site (n = 7) by quantitative polymerase chain reaction (qPCR) over a period of 18 months. These koalas had no evidence of chlamydial infection (infection loads below detection limit) or disease (clinical examination within normal limits) at that anatomical site at their previous clinical examination. If disease was detected at their first clinical examination, they were excluded from disease progression analyses only (unless it was their first sampling as an independent offspring, n = 1).
Interestingly, all of the new chlamydial infections at HV (100%, 8/8) progressed to disease, which was not significantly different to the number of new chlamydial infections at MB that progressed to disease (66%, 25/38)9 (Fisher’s exact test p = 0.084) (Supplementary Fig. S1). For six of these new chlamydial infections at HV (one ocular and five urogenital tract), the infection was detected at the same clinical examination as disease. For the other two new chlamydial infections at HV (both urogenital tract), the infection was present at a clinical examination 2.5 months and 4 months before disease was detected.
The urogenital tract infection load dynamics were similar at both study sites
The urogenital tract infection load (C. pecorum genome copies/µL) in both HV and MB9 koalas was significantly higher when infections were detected at the same clinical examination as disease (1,028,000 copies/µL, range 11,400–4,760,000 copies/µL), in comparison to infections that were present for one or more consecutive clinical examinations before disease was detected or infections that did not progress to disease (600 copies/µL, range 49–522,800 copies/µL) (Mann–Whitney U = 3, p = 0.030). Similarly, the urogenital tract infection load in both HV and MB9 koalas was significantly higher when koalas acquired a new chlamydial infection (within the last three months) (1,834,000 copies/µL, range 52,400–4,760,000 copies/µL), compared to koalas who had long-term infections (present for more than three months) (724 copies/µL, range 35–7,142 copies/µL) (Mann–Whitney U = 0, p = 0.010). Interestingly, the urogenital tract infection load was significantly higher at HV (1,028,000 copies/µL, range 11,400–4,760,000 copies/µL) compared to MB (3,824 copies/µL, range 138–1,340,000 copies/µL) when infections were detected at the same clinical examination as disease (Mann–Whitney U = 11, p = 0.003). In contrast, the urogenital tract infection load was not significantly different between the study sites (HV 600 copies/µL, range 49–522,800 copies/µL vs MB 794 copies/µL, range 16–13,900 copies/µL) when infections were present for one or more consecutive clinical examinations before disease was detected or infections did not progress to disease (Mann–Whitney U = 28, p = 0.703).
The prevalence of chlamydial strains, as determined by Multi-Locus Sequence Typing, differed between the study sites
Overall, 69 C. pecorum-positive samples, comprised of 45 samples from MB (4 ocular and 41 urogenital tract samples from 25 koalas) and 24 samples from HV (2 ocular and 22 urogenital tract samples from 14 koalas), were analysed using a C. pecorum-specific MLST scheme27. Three sequence types (STs) were detected in this study: ST 69, ST 202 and a novel ST (ST 281). ST 69 and ST 202 were detected at both study sites, however their prevalence at each study site was significantly different (Fig. 1). ST 69 was the most prevalent ST at HV, detected in 63% of total samples (15/24) and in 59% of urogenital tract site samples (13/22). ST 69 was significantly less prevalent at MB, detected in 11% of total samples (5/45) and in 12% of urogenital tract site samples (5/41) (overall and urogenital tract site Fisher’s exact test p < 0.001). In contrast, ST 202 was the most prevalent ST at MB, detected in 87% of total samples (39/45) and in 88% of urogenital tract site samples (36/41). ST 202 was significantly less prevalent at HV, detected in 13% of total samples (3/24) and in 14% of urogenital tract site samples (3/22) (overall and urogenital tract site Fisher’s exact test p < 0.001). The novel ST at HV, ST 281, was detected at the urogenital tract site in three koalas, representing 25% of total samples (6/24) and 27% of urogenital tract site samples (6/22). In comparison to the other previously described koala C. pecorum STs, ST 202 clustered in a well-supported, closely related clade with STs commonly detected in Qld and NSW koalas, including ST 220, ST 199 and ST 70 (Supplementary Fig. S2). ST 69 and ST 281, however, clustered into their own clades.
The prevalence and diversity of chlamydial strains, as determined by ompA genotyping, differed between the study sites
To compare ompA genotypes between MB and HV, all 24 C. pecorum-positive HV samples were genotyped and compared to previously reported MB genotypes (62 total samples, 12 ocular and 50 urogenital tract samples)9 (Fig. 1). The ompA genotype F was the most prevalent ompA genotype at HV, detected in 79% of total samples (19/24) and in 82% of urogenital tract site samples (18/22). The ompA genotype F was significantly less prevalent at MB, detected in 10% of total samples (6/62) and in 12% of urogenital tract site samples (6/50)9 (overall and urogenital tract site Fisher’s exact test p < 0.001). In contrast, the ompA genotype E´ was the most prevalent ompA genotype at MB, detected in 60% of total samples (37/62) and in 64% of urogenital tract site samples (32/50)9. The ompA genotype E´ was significantly less prevalent at HV and was the second most prevalent ompA genotype at this study site, detected in 17% of total samples (4/24) and in 18% of urogenital tract site samples (4/22) (overall and urogenital tract site Fisher’s exact test p < 0.001). The only other ompA genotype detected at HV was the ompA genotype A´, which was detected in a single ocular site sample.
Although a diverse range of ompA genotypes was detected at the urogenital tract site at MB, including A´, E´, F, F´, G and an ompA sequence fragment identical to that of the bovine E58 strain9, only ompA genotypes F and E´ were detected at the urogenital tract site at HV (Supplementary Fig. S2). For multifocal infections (ocular and urogenital tract sites) at HV (n = 2), the ompA genotype detected at each anatomical site differed. In one case, ompA genotype A´ was detected at the ocular site and ompA genotype F was detected at the urogenital tract site, and in the other, ompA genotype F was detected at the ocular site and ompA genotype E´ was detected at the urogenital tract site. Overall, the diversity in ompA, where six genotypes were characterised, was higher than the diversity in STs, where only three STs were characterised (Fig. 1). The C. pecorum plasmid was detected in all chlamydial strains except for a single ocular site sample from one koala at MB (see Supplementary Information for more details).
The dynamics of chlamydial strains during long-term infections differed between the strain typing methods
A total of 10 long-term urogenital tract infections were analysed with both strain typing methods, three at HV and seven at MB (Fig. 2). Although identical STs were detected over time in all long-term urogenital tract infections (100%, 10/10), genetically distinct ompA genotypes were detected over time in three of these long-term urogenital tract infections (30%, 3/10) at MB9. ST 202 was always detected in these infections, however the ompA genotype changed from F to A´ (4.5 months later) in one case, G to E´ (12 months later) in another case and G to E´ (7 months later) and again to A´ (10.5 months later) in the last case. An additional six ompA sequences from ocular (n = 1) and urogenital tract site (n = 5) samples collected from MB koalas, not previously reported by us9, were included in this analysis. Unfortunately, although the ompA fragment was amplified in a further two ocular and six urogenital tract site samples, we were not able to resolve the ompA sequences from these chromatograms.
Impact of chlamydial genotype on disease progression
Urogenital tract disease progression at each study site was associated with the chlamydial strain
At MB, ST 69 was significantly more prevalent in koalas that resolved their infections without progressing to disease (60%, 3/5) (the resolver group) compared to koalas that did not resolve their infections (6%, 2/36) (the chronic infection, the diseased after chronic infection and the infected and diseased groups combined) (Fisher’s exact test p = 0.009). Interestingly, at HV, ST 281 was significantly more prevalent in koalas that had not progressed to disease (56%, 5/9) (the chronic infection group) compared to koalas that had progressed to disease (1/12, 8%) (the infected and diseased and the diseased after chronic infection groups combined) (Fisher’s exact test p = 0.046). Further, when STs and ompA genotypes were concatenated to form a Multi-Locus Sequence Analysis (MLSA) type, MLSA type 2 (ST 281 with ompA genotype F) was significantly more prevalent in koalas that had not progressed to disease (56%, 5/9) compared to koalas that had progressed to disease (8%, 1/12) (Fisher’s exact test p = 0.046). In contrast, MLSA type 1 (ST 69 with ompA genotype F) was significantly more prevalent in koalas that had progressed to disease (75%, 9/12) compared to koalas that had not progressed to disease (22%, 2/9) (Fisher’s exact test p = 0.030).
When urogenital tract disease progression and chlamydial strains were analysed across both study sites combined (41 MB and 21 HV koalas for STs, 35 MB and 21 HV koalas for ompA genotypes and MLSA types), there were no significant differences in the prevalence of STs, ompA genotypes or MLSA types in koalas that had progressed to disease compared to koalas that had not progressed to disease.
Immunogenetic profiles at each study site
The major histocompatibility complex haplotypes were genetically diverse between the study sites
To investigate MHC gene diversity at each site, 60 koalas were selected from MB (30 koalas from our previous chlamydial epidemiology analyses (see Robbins et al.9 for more details) and 30 additional healthy koalas) and 20 koalas were selected from HV (sexually mature koalas undergoing monitoring). The MHC allele diversity in two Class I genes (UA and UC) and four Class II genes (DAb, DBb, DMb and DCb) was determined (Supplementary Fig. S3).
Overall, MHC haplotypes clustered based on study site (Fig. 3). Koalas grouped into three MHC haplotype clusters based on more than 65% genetic similarity. Two of these clusters represented MB koalas while the third cluster represented HV koalas. There was a tendency for MB koalas to belong to the same MHC cluster when they were captured from a similar geographical location within the 13 km site, suggesting some geographical sub-population structure. MB clusters 1 and 2 overlapped, however, and there are records of both natural dispersal and koala translocations within this study site. Interestingly, despite the separation of the MB and HV koalas by the BVB23,24 (and approximately 70 kms), three MB koalas genetically grouped within HV cluster 3 while two HV koalas genetically grouped within MB cluster 1.
The prevalence of major histocompatibility complex alleles differed between the study sites
Overall, 61 MHC alleles were detected in this study (Supplementary Fig. S3). In total, 21 MHC alleles were only detected at MB, 14 MHC alleles were only detected at HV and 26 MHC alleles were detected at both study sites. There were eight MHC alleles that had a significantly higher prevalence at each study site (Fisher’s exact test p < 0.05), with UA 10:01, UA 14:01, UC 01:01, UC 05:02, DAb 10, DAb 19, DBb 03 and DMb 04 significantly more prevalent in MB koalas and UA 08:01, UA 11:01, UA 17:01, UC 01:03, DAb 22, DAb 23, DAb 37 and DBb 04 significantly more prevalent in HV koalas (Supplementary Table S1). In addition, this study expanded our knowledge of koala MHC allele diversity, with a total of 28 previously unreported MHC alleles being identified (15 at MB, 12 at HV and one at both study sites) (Supplementary Fig. S3).
Impact of host genetics on disease progression
Urogenital tract disease progression was associated with major histocompatibility complex alleles
At each study site, the prevalence of only one individual MHC allele was significantly different between koalas that progressed to disease and koalas that did not progress to disease. At MB, the Class II allele DAb 10 was significantly more prevalent in koalas that did not progress to disease (50%, 17/34) compared to koalas that progressed to disease (13%, 3/23) (Fisher’s exact test p = 0.005). In contrast, at HV, the Class II allele DCb 03 was significantly more prevalent in koalas that progressed to disease (75%, 9/12) compared to koalas that did not progress to disease (14%, 1/7) (Fisher’s exact test p = 0.020).
When urogenital tract disease progression and koala immunogenetics were analysed across both study sites combined (57 MB and 19 HV koalas), the prevalence of four individual MHC alleles was significantly different between koalas that progressed to disease and koalas that did not progress to disease. The Class II allele DCb 03 was significantly more prevalent in koalas that progressed to disease (66%, 23/35) compared to koalas that did not progress to disease (34%, 14/41) (Fisher’s exact test p = 0.011), and koalas with DCb allele 03 were 3.70 times (95% CI 1.43–9.56 times) more likely to progress to disease. The Class II allele DBb 04 was also significantly more prevalent in koalas that progressed to disease (11%, 4/35) compared to koalas that did not progress to disease (0%, 0/41) (Fisher’s exact test p = 0.041). In contrast, the Class II allele DAb 10 was significantly more prevalent in koalas that did not progress to disease (42%, 17/41) compared to koalas that progressed to disease (11%, 4/35) (Fisher’s exact test p = 0.004), and koalas with DAb allele 10 were 5.49 times (95% CI 1.63–18.46 times) less likely to progress to disease. Finally, the Class I allele UC 01:01 was also significantly more prevalent in koalas that did not progress to disease (100%, 41/41) compared to koalas that progressed to disease (89%, 31/35) (Fisher’s exact test p = 0.041).
MHC haplotypes were not, however, associated with overall disease progression, with koalas that progressed to disease at any anatomical site at any time during the period of monitoring distributed evenly throughout the genetic clusters (Fig. 3).
Koala retrovirus profiles at each study site
The prevalence of most koala retrovirus subtypes, except KoRV-F, was similar between the study sites
To investigate the KoRV profiles of koalas at each study site, the KoRV proviral env gene was amplified and sequenced for the same 80 koalas used for the MHC gene diversity analysis (60 MB koalas over 68 individual sampling points and 20 HV koalas over 22 individual sampling points). Overall, five KoRV subtypes were detected, with KoRV subtypes -A, -B, -D and -F detected at both study sites and KoRV-G only detected at MB.
When only the first time-point was included for koalas with longitudinal samples, KoRV-F was significantly more prevalent in MB koalas (77%, 46/60) compared to HV koalas (25%, 5/20) (Fisher’s exact test, p < 0.001) (Supplementary Fig. S4. There were no significant differences in the prevalence of any other KoRV subtype between the study sites. As expected, KoRV-A prevalence was 100% in both MB koalas (60/60) and HV koalas (20/20). The prevalence of KoRV-B was 40% (24/60) in MB koalas compared to 55% (11/20) in HV koalas (Fisher’s exact test p = 0.301), the prevalence of KoRV-D was 97% (58/60) in MB koalas compared to 100% (20/20) in HV koalas (Fisher’s exact test p = 1.000), and the prevalence of KoRV-G was 2% (1/60) in MB koalas compared to 0% (0/20) in HV koalas (Fisher’s exact test p = 1.000).
Impact of co-infection with koala retrovirus on disease progression
Urogenital tract disease progression was not associated with koala retrovirus profiles
There were no significant differences in the prevalence, proportional abundance or diversity (number of OTUs per koala) of any KoRV subtype between koalas that had progressed to disease (the infected and diseased and the diseased after chronic infection groups combined) and koalas that had not progressed to disease (the chronic infection group) at either study site (35 MB and 13 HV koalas), or when urogenital tract disease progression and KoRV profiles were analysed across both study sites combined.
C. pecorum is highly prevalent in northern Australian koala populations and causes infertility and mortality in susceptible koalas, threatening the viability of these increasingly fragmented and declining populations2. Population management programs that incorporate chlamydial disease control may help to stabilise these populations1, however limitations in our understanding of chlamydial epidemiology might affect program efficiency and success. To address these limitations and build on our previous findings9, we analysed two unique, longitudinally-studied koala populations with well-defined clinical groups. These koala populations were geographically separated and differentially affected by chlamydial disease, allowing us to investigate several factors thought to contribute to chlamydial epidemiology. We found that in these two SE Qld koala populations, koala immunogenetics and chlamydial genotypes had a more direct impact on urogenital tract disease progression than KoRV proviral subtypes. Four individual MHC alleles were linked with overall urogenital tract disease progression, with the Class II alleles DCb 03 and DBb 04 significantly associated with progression to disease and the Class II alleles DAb 10 and Class I allele UC 01:01 significantly associated with remaining healthy. We also found that chlamydial strains appeared to vary in pathogenicity, and chlamydial genotypes belonging to both ST 69 and ompA genotype F were associated with urogenital tract disease progression whereas ST 281 was associated with the absence of urogenital tract disease progression. Finally, we also detected different ompA genotypes, but not different STs, over time, in long-term infections.
Although a complex range of factors is known to influence chlamydial disease progression in koalas, the koala’s immune response to C. pecorum plays a key role and the MHC loci are known to be important in this response17. Our analysis of MHC alleles and urogenital tract disease progression in SE Qld populations identified two putative susceptibility (DCb 03, DBb 04) and protective variants (DAb 10, UC 01:01). The Class II allele DCb 03 was significantly more prevalent in HV koalas that progressed to disease, and overall, disease progression was 3.70 times more likely in SE Qld koalas with the DCb allele 03. This finding contrasts with a modelling study in SE Qld that suggested that the absence of DCb allele 03 was associated with disease progression13, however disease progression at both the ocular and urogenital tract sites was combined in this analysis, and this may have impacted the findings. Further, overall, disease progression in SE Qld koalas was significantly associated with the Class II allele DBb 04. Interestingly, a study in NSW koalas reported significantly higher chlamydial-hsp60 antibody titres in koalas with DBb allele 04, suggesting this variant recognises and binds to c-hsp60 epitopes17. High c-hsp60 antibody titres in koalas have been associated with fibrous occlusion of the uterus or uterine tube, however their role in chlamydial pathogenesis in koalas remains unclear as they were also associated with lower levels of active inflammation and fewer chlamydial inclusions28. Human studies suggest that although the Class II MHC defined anti-chlamydial antibody response appears to be important for chlamydial clearance and c-hsp60 antibodies are protective, it does not always prevent pathology29,30.
In contrast, the Class II allele DAb 10 was significantly more prevalent in MB koalas that did not progress to disease, and overall, disease progression was 5.49 times less likely in koalas with DAb 10. In a study in NSW koalas, DAb allele 10 was associated with chlamydial infection and persistence17, however chlamydial infection only and diseased koalas were combined in this hospital data set analysis, and these factors might contribute to our contrary results. Overall, the Class I allele UC 01:01 was also significantly associated with the absence of disease progression in SE Qld koalas. The UC gene has been identified as a classical MHC gene in koalas and appears to be under diversifying selection, suggesting it might be important in the anti-chlamydial immune response31. Analysis of the koala genome showed that UC and UE genes were located only approximately 72 bp apart in the core MHC region in the genome and shared 95.5% similarity, likely originating as a gene duplication event31. Further, although limited variability in the UE gene was reported, it had tissue-specific expression in the testes (and thymus)31, indicating it is active at a site of chlamydial exposure. Taken together, these findings suggest that the UE gene should be included in subsequent investigations into associations between MHC gene polymorphisms and chlamydial disease progression. Finally, the significantly higher prevalence of putative protective variants (DAb 10 and UC 01:01) at MB and a putative susceptibility variant (DBb 04) at HV may have contributed to the significantly higher overall prevalence of chlamydial infection and disease at HV. Focused future study of the chlamydial epitopes that bind to these putative susceptibility and protective variants, as well as the cytokine profile and MHC gene expression levels in variant positive and negative koalas is necessary to better understand the role of koala immunogenetics in chlamydial disease progression.
Our findings also strengthen a growing body of data that support the infecting chlamydial strain as an important contributor for chlamydial disease progression in koalas9,11,12,32. Our approach was to combine a MLST scheme, which has been shown to be congruent with whole genome phylogeny and is a robust method for investigating genetic diversity33, with ompA genotyping, which appears to capture more genetic diversity due to the polymorphic nature of the ompA gene. This combined approach allows for fine-scale C. pecorum epidemiological investigations12,34. At this fine-scale, we determined that chlamydial genotypes belonging to both ST 69 and ompA genotype F appeared to be more pathogenic at HV and were associated with urogenital tract disease progression. Further, the significantly higher prevalence of this chlamydial strain at HV correlated with a higher overall prevalence of infection and disease in this population. This finding strengthens the known association of ompA genotype F with higher urogenital tract infection loads and chlamydial disease progression in koalas9,11. In contrast, ST 69 was associated with resolved urogenital tract infections at MB in this study, while ST 69 has previously been associated with clinical disease in NSW koalas12 as well as being detected in koalas without clinical signs of disease33. We also found that ST 281 appeared to be less pathogenic at HV and was associated with the absence of disease progression and milder urogenital tract disease once progression had occurred. The highly conserved housekeeping genes analysed for MLST are unlikely to directly be involved in pathogenicity, and whole genome sequencing (WGS) might be necessary to determine whether there are associations between particular STs and other potential virulence-associated loci, such as ORF 663 and incA35,36, that are driving chlamydial epidemiology in koalas. In addition, the impact of these chlamydial genotypes on pathogenicity could be further investigated with in vitro studies.
The polymorphic ompA gene, encoding the surface-exposed major outer membrane protein, may undergo more rapid evolution than the rest of the chlamydial genome, due to selection pressure from the host immune system37. This feature can make the ompA gene very useful in longitudinal and multifocal infection analyses. We detected genetically distinct ompA genotypes over time in 30% of the long-term urogenital tract infections examined, and these were all at MB where we detected a variety of genetically diverse ompA genotypes. Further, genetically distinct ompA genotypes were detected in the eyes and urogenital tract of koalas at both study sites during multifocal infections. This compared to detected STs, which were identical both over time in long-term urogenital tract infections and at each anatomical site during multifocal infections and were less genetically diverse overall in comparison to ompA genotypes. Interestingly, although we were able to resolve all the ompA genotypes from our HV samples, regardless of infection load, we were not able to resolve the ompA genotypes from eight MB samples despite MLST being successful. Taken together, these findings could be consistent with mixed genotype infections38 and extensive recombination in the ompA gene39,40 driving chlamydial strain microevolution in koalas. WGS could address the limitations of amplicon sequencing for detecting mixed genotype infections38, allowing us to better characterise circulating chlamydial strain diversity and its impact on chlamydial epidemiology.
Our understanding of the relationship between koalas and KoRV is rapidly evolving as a growing number of koalas are evaluated with increasingly sensitive methods. KoRV was originally thought to be spreading southwards after it was introduced to northern koala populations less than 200 years ago41, but recent analyses suggest it crossed into koalas up to 49,000 years ago42 and a range of subtypes have been detected in both northern and southern koala populations43. Consistent with these analyses, we found a strikingly similar prevalence of KoRV subtypes at each of our study sites, suggesting that the spread of KoRV in this region occurred before gene flow between our populations was limited by the BVB24 and the rapid and widespread declines in koala populations 30,000–40,000 years ago23. Utilising deep sequencing of the KoRV proviral env gene and our well-defined clinical groups, we failed to detect any association between the proviral detection of any KoRV subtype, including KoRV-B15, and disease progression16,44,45. This suggests that the presence of KoRV provirus alone is not sufficient to influence chlamydial disease progression and that subtype expression might be more important46. Acknowledging that KoRV detection methods have different targets and sensitivities43,46, further study is clearly needed to tease out the complex interactions between this putative pathogen and its host.
Although our data were collected from longitudinal studies of two koala populations using identical protocols, several factors differed between the study sites that may have impacted our findings. Variation in environmental factors exists between MB and HV in terms of rainfall, soil, vegetation communities, sympatry with livestock and proximity to human habitation. While evidence linking ‘habitat quality’ and chlamydial disease progression is inconclusive18,32, climate stress can impact population health47,48 and HV was drought-affected at the time of our study. Many of the koalas at HV also shared their habitat with cattle, and the likelihood and frequency of cross-host transmission of chlamydial strains from livestock to koalas is currently unknown33. Hence, sympatric sampling is a priority for future research at this site. It is interesting to note that in our study, proximity to human habitation was not associated with a higher prevalence of chlamydial infection or disease13, and there was a significantly higher prevalence of chlamydial infection and disease at the rural HV compared to the peri-urban/urban MB. Finally, in contrast to MB where an estimated 95% of the resident koala population was monitored4, a much smaller proportion of koalas at HV was able to be recruited into the monitoring program and the sample size was limited.
In conclusion, our research of longitudinally studied koalas with well-defined clinical outcomes has shown that MHC genetics and chlamydial genotypes were more directly linked to chlamydial disease progression than subtype-specific KoRV proviral profiles. These findings provide new focus for investigations into susceptibility and protective immune phenotypes, informing selective breeding programs, and highlight the risks of poorly planned translocations and the restoration of habitat connectivity to naïve koalas. Overall, our research has also shown that chlamydial disease progression commonly occurs in SE Qld koalas, suggesting that chlamydial disease control should be incorporated into population management programs in this region if the threat of chlamydial disease is to be abated.
This study utilised two monitored koala populations in SE Qld. North of Brisbane (27.0946° S, 152.9206° E), MB is peri-urban/urban koala habitat composed of open and closed forest and woodland that was undergoing development as part of a large-scale infrastructure project (see Hanger et al.5 for more details). West of Ipswich (27.6594° S, 152.4672° E), HV is rural koala habitat composed of open forest and grassland that included farmland and a nature reserve. These study sites are separated by approximately 70 kms and the BVB23,24 (Fig. 1).
The koala populations in our study were part of population management programs conducted by Endeavour Veterinary Ecology Pty Ltd (see Hanger et al.5 for more details). Koalas underwent regular capture, telemetric monitoring and comprehensive clinical examinations under anaesthesia (see below), and were treated for chlamydial disease when detected (see Robbins et al.49 for more details). During clinical examinations, swab samples were collected from the ocular conjunctiva and urogenital sinus (females) or urethra (males) and blood samples were collected from the cephalic vein. All samples were stored at −20 °C before being transported to the lab for processing. Detailed field observations and clinical examination records were compiled for each koala during their period of monitoring, which occurred between 2013 and 2017 at MB and 2018 and 2019 at HV.
In total, 24 koalas were recruited from HV, which was 100% of the sexually mature koalas monitored at this site (Table 2). We also utilised data from 47 koalas in our previous study at MB9 and recruited an additional 30 healthy, chlamydial infection- and disease-free koalas at MB to serve as a control group for our MHC and KoRV analyses. Control koalas were matched for age, sex, location and reproductive status, although this was not always possible at HV due to limitations in the number of koalas available. Multiple time-points were available for some koalas with chlamydial infections, and these were utilised to investigate how chlamydial load and genotype and KoRV profiles changed over time.
Assessing chlamydial disease progression
Comprehensive clinical examinations were performed on koalas under anaesthesia by experienced koala veterinarians, and included a thorough physical examination, sonographic examination of the urogenital tract (including kidneys), and cytological examination of blood, bone marrow, peritoneal fluid and urine sediment. Koalas were defined as progressing to chlamydial disease if signs of chlamydial disease were detected during a clinical examination and the koala had been diagnosed as healthy (chlamydial disease-free) at their previous clinical examination. The minimum requirement for the diagnosis for ocular chlamydial disease was conjunctivitis, however keratoconjunctivitis, corneal ulceration, neovascularisation, scleral injection, pannus formation and blepharitis were also observed. The minimum requirement for the diagnosis of cystitis was an inflammatory urine sediment, with or without thickening of the bladder wall sonographically (> 2 mm mean wall diameter), however a urine stained, damp rump, secondary dermatitis and decubital ulcers were also observed. The minimum requirement for the diagnosis of reproductive disease was sonographic changes in the reproductive tract. In females, this included pyometra or cystic dilatation in the reproductive tract and in males, this included orchitis or prostatic lesions.
Sample analysis for C. pecorum
Ocular conjunctiva and urogenital tract swab samples were mixed with 500 µL of phosphate-buffered saline. Total DNA was extracted from a 200 µL aliquot of this swab suspension using a QIAamp DNA mini kit (Qiagen), according to the manufacturer’s instructions. The extracted DNA was then used to screen for C. pecorum DNA using a C. pecorum-specific qPCR assay that targets a 209 bp region of the conserved gene CpecG_05739,50, and chlamydial plasmid DNA using a CDS5-specific qPCR assay that targets a 233 bp fragment of the C. pecorum plasmid (CDS5 or Pgp3 locus)51. A standard curve was generated for quantification of C. pecorum infection loads using a known concentration of C. pecorum genomic DNA diluted to 107–101 copies/µL, followed by a high-resolution melt (HRM) analysis. Samples with less than 10 copies/µL and with no or below threshold HRM were considered below the detectable limit of the assay and were reported as negative. Samples were reported as either positive or negative for the C. pecorum plasmid based on positive amplification and confirmation with an HRM curve at 79.0 °C + /−0.5 °C. Samples were run in duplicate, and positive and negative controls were included in all qPCR assays.
To evaluate the genetic diversity of infecting strains, two strain typing methods were employed. Availability and longitudinal data dictated which samples were analysed from MB and all HV samples were analysed. A 359 bp fragment of the V3/V4 regions of the ompA gene was amplified9,10 in 38 C. pecorum-positive samples from 28 koalas (14 from MB and 24 from HV). A C. pecorum-specific Multi-Locus Sequence Typing scheme, based on the seven housekeeping genes gatA, oppA_3, hflX, gidA, enoA, hemN and fumC27, was applied to 69 C. pecorum-positive samples from 39 koalas (45 from MB and 24 from HV). The PCR products were electrophoresed on a 1.5% agarose gel, followed by visual confirmation under a UV transilluminator and amplicons were bidirectionally sequenced at Macrogen Inc (Korea). Sequence analyses were performed in Geneious Prime (2019.2.3) (https://www.geneious.com/), including Clustal X alignments and Bayesian phylogenetic analyses using Mr Bayes. ompA sequences were analysed by BLAST against the nr/nt database using megablast to determine their similarity to other publicly available ompA sequences, whereas MLST sequences were interrogated in ChlamydialesPubMLST as previously described27. The novel ST that was detected, ST 281, as well as the individual alleles, was deposited in the ChlamydialesPubMLST ref: https://www.ncbi.nlm.nih.gov/pubmed/30345391 (https://pubmlst.org/chlamydiales/).
Sample analysis for major histocompatibility complex genes and koala retrovirus subtypes
Total DNA was extracted from 200 µL of blood serum clots using a QIAamp DNA mini kit (Qiagen), according to the manufacturer’s instructions. The DNA extracted from serum clots was used to amplify two Class I (UA and UC) and four Class II (DAb, DBb, DCb, DMb) MHC genes based on published primer sets17,31, as well as the receptor binding domain of the koala retrovirus env gene46 with PCR. The PCR products were electrophoresed on a 1.5% agarose gel, followed by visual confirmation under a UV transilluminator and amplicons were deep sequenced at the Ramaciotti Centre for Genomics (Australia). Forward and reverse amplicons were filtered, trimmed with cutadapt52 and merged with FLASH53. KoRV OTUs were determined with QIIME using UCLUST and USEARCH54 and BLAST searched against a known env gene library to allocate provirus subtypes46. Merged MHC sequences were aligned with Clustal X55 and trimmed in GeneDoc56 before being BLAST searched against a known MHC gene library to allocate alleles. Novel MHC gene sequences were translated to proteins to establish whether a new allele had been characterised, and novel MHC alleles were deposited with accession numbers MT321017-MT321064. MHC haplotype clusters were analysed with a Gower clustering analysis57 in RStudio 3.5.1 (2018.07.02) (https://www.R-project.org/) and compared to capture locations plotted on Google Earth. Neighbour-joining phylogenetic trees were generated in Geneious Prime (2019.02.03) (https://www.geneious.com/).
Koala management programs were conducted under approvals issued by the Queensland Department of Agriculture and Fisheries (approvals CA 2012/03/597, CA 2013/09/719, CA 2014/06/777, CA 2015/03/852, and CA 2016/03/950), and work with koalas was authorised by scientific purposes permits issued by the Queensland Department of Environment and Heritage Protection (approvals WISP 11525212, WISP 16125415, WISP 13661313, WITK 14173714, WISP 17273716 and WA 0008304). Swab samples were analysed under approval numbers AN/A/13/80 and AN/E/19/33 issued by the University of the Sunshine Coast Animal Ethics Committee. All experiments were performed in accordance with the relevant guidelines and regulations.
Statistical analyses were performed using the Kruskal-Walis test, Mann–Whitney U test, two-tailed Fisher’s Exact test, chi-square test and independent t-test as appropriate. Data were not normally distributed for any parameter except KoRV-A diversity, and some analyses were limited by small sample size. All statistical analyses were performed with the IBM SPSS Statistics software package (version 26, https://www.ibm.com/products/spss-statistics), and the statistical significance of all tests was concluded at p-values of < 0.05.
Beyer, H. L. et al. Management of multiple threats achieves meaningful koala conservation outcomes. J. Appl. Ecol. 55, 1966–1975. https://doi.org/10.1111/1365-2664.13127 (2018).
Polkinghorne, A., Hanger, J. & Timms, P. Recent advances in understanding the biology, epidemiology and control of chlamydial infections in koalas. Vet. Microbiol. 165, 214–223. https://doi.org/10.1016/j.vetmic.2013.02.026 (2013).
Jackson, M., White, N., Giffard, P. & Timms, P. Epizootiology of Chlamydia infections in two free-range koala populations. Vet. Microbiol. 65, 255–264 (1999).
4Hanger, J. et al. Moreton Bay Rail Koala Management Program: Final Technical Report for Queensland Department of Transport and Main Roads., 1–351 (Toorbul, Queensland, 2017).
Burach, F. et al. Chlamydiaceae and Chlamydia-like organisms in the koala (Phascolarctos cinereus)–organ distribution and histopathological findings. Vet. Microbiol. 172, 230–240. https://doi.org/10.1016/j.vetmic.2014.04.022 (2014).
Pagliarani, S. et al. Chlamydia pecorum infection in the reproductive tract of female koalas (Phascolarctos cinereus). J. Comp. Pathol. 174, 189. https://doi.org/10.1016/j.jcpa.2019.10.160 (2020).
Palmieri, C. et al. Chlamydia pecorum infection in the male reproductive system of koalas (Phascolarctos cinereus). Vet. Pathol. 56, 300–306. https://doi.org/10.1177/0300985818806963 (2018).
Rhodes, J. R. et al. Using integrated population modelling to quantify the implications of multiple threatening processes for a rapidly declining population. Biol. Cons. 144, 1081–1088. https://doi.org/10.1016/j.biocon.2010.12.027 (2011).
Robbins, A., Hanger, J., Jelocnik, M., Quigley, B. L. & Timms, P. Longitudinal study of wild koalas (Phascolarctos cinereus) reveals chlamydial disease progression in two thirds of infected animals. Sci. Rep. https://doi.org/10.1038/s41598-019-49382-9 (2019).
Nyari, S. et al. Epidemiology of chlamydial infection and disease in a free-ranging koala (Phascolarctos cinereus) population. PLoS ONE 12, e0190114. https://doi.org/10.1371/journal.pone.0190114 (2017).
Legione, A. R. et al. Identification of unusual Chlamydia pecorum genotypes in Victorian koalas (Phascolarctos cinereus) and clinical variables associated with infection. J. Med. Microbiol. 65, 420–428. https://doi.org/10.1099/jmm.0.000241 (2016).
Fernandez, C. M. et al. Differences in the genetic diversity of Chlamydia pecorum between neighbouring sub-populations of koalas (Phascolarctos cinereus): a potential issue for wildlife corridor construction in population management. Vet. Microbiol. 231, 264–270. https://doi.org/10.1016/j.vetmic.2019.02.020 (2019).
Quigley, B. L., Carver, S., Hanger, J., Vidgen, M. E. & Timms, P. The relative contribution of causal factors in the transition from infection to clinical chlamydial disease. Sci. Rep. https://doi.org/10.1038/s41598-018-27253-z (2018).
Wan, C. et al. Using quantitative polymerase chain reaction to correlate Chlamydia pecorum infectious load with ocular, urinary and reproductive tract disease in the koala (Phascolarctos cinereus). Aust. Vet. J. 89, 409–412. https://doi.org/10.1111/j.1751-0813.2011.00827.x (2011).
Waugh, C. A. et al. Infection with koala retrovirus subgroup B (KoRV-B), but not KoRV-A, is associated with chlamydial disease in free-ranging koalas (Phascolarctos cinereus). Sci. Rep. 7, 134. https://doi.org/10.1038/s41598-017-00137-4 (2017).
Legione, A. R. et al. Koala retrovirus genotyping analyses reveal a low prevalence of KoRV-A in Victorian koalas and an association with clinical disease. J. Med. Microbiol. 66, 236–244. https://doi.org/10.1099/jmm.0.000416 (2017).
Lau, Q., Griffith, J. E. & Higgins, D. P. Identification of MHCII variants associated with chlamydial disease in the koala (Phascolarctos cinereus). PeerJ 2, e443. https://doi.org/10.7717/peerj.443 (2014).
Patterson, J. L. et al. The prevalence and clinical significance of Chlamydia infection in island and mainland populations of Victorian koalas (Phascolarctos cinereus). J. Wildl. Dis. 51, 309–317. https://doi.org/10.7589/2014-07-176 (2015).
Fabijan, J. et al. Chlamydia pecorum prevalence in South Australian koala (Phascolarctos cinereus) populations: identification and modelling of a population free from infection. Sci. Rep. 9, 5. https://doi.org/10.1038/s41598-019-42702-z (2019).
Bryant, L. M. & Krosch, M. N. Lines in the land: a review of evidence for eastern Australia’s major biogeographical barriers to closed forest taxa. Biol. J. Lin. Soc. 119, 238–264. https://doi.org/10.1111/bij.12821 (2016).
Lee, K. E. et al. Anthropogenic changes to the landscape resulted in colonization of koalas in north-east New South Wales, Australia. Austral. Ecol. 38, 355–363. https://doi.org/10.1111/j.1442-9993.2012.02414.x (2013).
Kjeldsen, S. R. et al. Genomic comparisons reveal biogeographic and anthropogenic impacts in the koala (Phascolarctos cinereus): a dietary-specialist species distributed across heterogeneous environments. Heredity 122, 525–544. https://doi.org/10.1038/s41437-018-0144-4 (2018).
Johnson, R. N. et al. Adaptation and conservation insights from the koala genome. Nat. Genet. 50, 1102–1111. https://doi.org/10.1038/s41588-018-0153-5 (2018).
Neaves, L. E. et al. Phylogeography of the Koala, (Phascolarctos cinereus), and harmonising data to inform conservation. PLoS ONE 11, 0162207. https://doi.org/10.1371/journal.pone.0162207 (2016).
Koroleva, E. et al. Chlamydial type III secretion system needle protein induces protective immunity against chlamydia muridarum intravaginal infection. Biomed. Res. Int. https://doi.org/10.1155/2017/3865802 (2017).
Quigley, B. L., Ong, V. A., Hanger, J. & Timms, P. Molecular dynamics and mode of transmission of Koala retrovirus as it invades and spreads through a Wild Queensland Koala population. J. Virol. 92, 01871–01917. https://doi.org/10.1128/JVI.01871-17 (2018).
Jelocnik M., P. A., Pannekoek Y. In Chlamydia trachomatis. Methods in Molecular Biology. Vol. 2042 (Humana, 2019).
Higgins, D. P., Hemsley, S. & Canfield, P. J. Association of uterine and salpingeal fibrosis with chlamydial hsp60 and hsp10 antigen-specific antibodies in Chlamydia-infected koalas. Clin. Diagn. Lab. Immunol. 12, 632–639. https://doi.org/10.1128/CDLI.12.5.632-639.2005 (2005).
Poston, T. B. et al. Cervical cytokines associated with chlamydia trachomatis susceptibility and protection. J. Infect. Dis. 220, 330–339. https://doi.org/10.1093/infdis/jiz087 (2019).
Murthy, A. K., Li, W. & Ramsey, K. H. Immunopathogenesis of chlamydial infections. Curr. Top. Microbiol. Immunol. 412, 183–215. https://doi.org/10.1007/82_2016_18 (2018).
Cheng, Y. Y. et al. Characterisation of MHC class I genes in the koala. Immunogenetics 70, 125–133. https://doi.org/10.1007/s00251-017-1018-2 (2018).
Wedrowicz, F., Mosse, J., Wright, W. & Hogan, F. E. Using non-invasive sampling methods to determine the prevalence and distribution of Chlamydia pecorum and koala retrovirus in a remnant koala population with conservation importance. Wildl. Res. 45, 366–380. https://doi.org/10.1071/wr17184 (2018).
Jelocnik, M., Frentiu, F. D., Timms, P. & Polkinghorne, A. Multilocus sequence analysis provides insights into molecular epidemiology of Chlamydia pecorum infections in Australian sheep, cattle, and koalas. J. Clin. Microbiol. 51, 2625–2632. https://doi.org/10.1128/JCM.00992-13 (2013).
Mohamad, K. et al. Preliminary phylogenetic identification of virulent Chlamydophila pecorum strains. Infect. Genet. Evol. 8, 764–771. https://doi.org/10.1016/j.meegid.2008.06.009 (2008).
Higgins, D. P., Beninati, T., Meek, M., Irish, J. & Griffith, J. E. Within-population diversity of koala Chlamydophila pecorum at ompA VD1-VD3 and the ORF663 hypothetical gene. Vet. Microbiol. 156, 353–358. https://doi.org/10.1016/j.vetmic.2011.11.005 (2012).
Mohamad, K. Y. et al. Host adaptation of Chlamydia pecorum towards low virulence evident in co-evolution of the ompA, incA, and ORF663 Loci. PLoS ONE 9, e103615. https://doi.org/10.1371/journal.pone.0103615 (2014).
Kaltenboeck, B., Heinen, E., Schneider, R., Wittenbrink, M. & Schmeer, N. OmpA and antigenic diversity of bovine Chlamydophila pecorum strains. Vet. Microbiol. 135, 175–180. https://doi.org/10.1016/j.vetmic.2008.09.036 (2009).
Bachmann, N. L. et al. Culture-independent genome sequencing of clinical samples reveals an unexpected heterogeneity of infections by Chlamydia pecorum. J. Clin. Microbiol. 53, 1573–1581. https://doi.org/10.1128/JCM.03534-14 (2015).
Bachmann, N. L., Polkinghorne, A. & Timms, P. Chlamydia genomics: providing novel insights into chlamydial biology. Trends Microbiol. 22, 464–472. https://doi.org/10.1016/j.tim.2014.04.013 (2014).
Marsh, J., Kollipara, A., Timms, P. & Polkinghorne, A. Novel molecular markers of Chlamydia pecorum genetic diversity in the koala (Phascolarctos cinereus). BMC Microbiol. 11, 77. https://doi.org/10.1186/1471-2180-11-77 (2011).
Tarlinton, R., Meers, J. & Young, P. Retroviral invasion of the koala genome. Nature 442, 79–81. https://doi.org/10.1038/nature04841 (2006).
Avila-Arcos, M. et al. One hundred twenty years of koala retrovirus evolution determined from museum skins. Mol. Biol. Evol. 30, 299–304. https://doi.org/10.1093/molbev/mss223 (2013).
Tarlinton, R. E. et al. Differential and defective expression of Koala Retrovirus reveal complexity of host and virus evolution. bioRxiv, 211466. https://doi.org/10.1101/211466 (2017).
Chappell, K. et al. Phylogenetic diversity of koala retrovirus within a Wild Koala population. J. Virol. 91, 01820. https://doi.org/10.1128/JVI.01820-16 (2017).
Sarker, N. et al. Koala retrovirus viral load and disease burden in distinct northern and southern koala populations. Sci. Rep. 10, 263. https://doi.org/10.1038/s41598-019-56546-0 (2020).
Quigley, B. et al. Changes in endogenous and exogenous koala retrovirus subtype expression over time reflect koala health outcomes. J. Virol. 93, undefined-undefined, https://doi.org/10.1128/JVI.00849-19 (2019).
Seabrook, L. et al. Drought-driven change in wildlife distribution and numbers: a case study of koalas in south west Queensland. Wildl. Res. 38, 509–524. https://doi.org/10.1071/WR11064 (2011).
Gordon, G., Brown, A. & Pulsford, T. A koala (Phascolarctos cinereus Goldfuss) population crash during drought and heat-wave conditions in southwestern Queensland. Aust. J. Ecol. 13, 451–461. https://doi.org/10.1111/j.1442-9993.1988.tb00993.x (1988).
Robbins, A., Loader, J., Timms, P. & Hanger, J. Optimising the short and long-term clinical outcomes for koalas (Phascolarctos cinereus) during treatment for chlamydial infection and disease. PLoS ONE 13, 0209679. https://doi.org/10.1371/journal.pone.0209679 (2018).
Jelocnik, M. et al. Development and evaluation of rapid novel isothermal amplification assays for important veterinary pathogens: Chlamydia psittaci and Chlamydia pecorum. PeerJ 5, e3799. https://doi.org/10.7717/peerj.3799 (2017).
Phillips, S. et al. Chlamydia pecorum gastrointestinal tract infection associations with urogenital tract infections in the koala (Phascolarctos cinereus). PLoS ONE 13, 0206471. https://doi.org/10.1371/journal.pone.0206471 (2018).
Martin, M. Cutadapt removes adapter sequences from high-throughput sequencing reads. EMBnet. J. 17, 10–12. https://doi.org/10.14806/ej.17.1.200 (2011).
Magoc, T. & Salzberg, S. L. FLASH: fast length adjustment of short reads to improve genome assemblies. Bioinformatics 27, 2957–2963. https://doi.org/10.1093/bioinformatics/btr507 (2011).
Edgar, R. C. Search and clustering orders of magnitude faster than BLAST. Bioinformatics 26, 2460–2461. https://doi.org/10.1093/bioinformatics/btq461 (2010).
Larkin, M. A. et al. Clustal W and Clustal X version 2.0. Bioinformatics 23, 2947–2948. https://doi.org/10.1093/bioinformatics/btm404 (2007).
Nicholas, K., Nicholas, H. G., Nicholas, K.B., Nicholas, H.B., Deerfield, D.W., Nicholas, H.B.J., Nicholas, H.J., Nicholas, K.R., Nicholas, H.B.J., Nicholas, A., Deerfield, D.W., Nicholas, H., Gauch, H. . GeneDoc: a tool for editing and annotating multiple sequence alignments. Embnet.news (1997).
Gower, J. C. A comparison of some methods of cluster analysis. Biometrics 23, 623–630. https://doi.org/10.2307/2528417 (1967).
This project was significantly supported by the Queensland Government (Department of Transport and Main Roads), and specifically the Moreton Bay Rail project. We also thank the many groups that have supported our overall koala disease work, including the Queensland Department of Environment and Science, the Moreton Bay Regional Council, the City of Gold Coast Council, Friends of the Koala (Lismore), Koala Action Inc., Endeavour Veterinary Ecology, Australia Zoo Wildlife Hospital, Lone Pine Koala Sanctuary, Currumbin Wildlife Sanctuary, Redland City Council, Zoos South Australia, and VIDO (Canada). Specifically, here we thank the Department of Transport and Main Roads – Moreton Bay Rail Project Team and the Turner Family Foundation – Hidden Vale Wildlife Centre, for enabling access to the data and samples collected as part of the Moreton Bay Rail koala management program and the Hidden Vale Koala Project. We also thank the dedicated staff at Endeavour Veterinary Ecology, particularly Jo Loader, for their help in capturing, radio-collaring and tracking the koalas, and undertaking health assessments and collecting samples. Finally, we thank David Lizárraga for his assistance with the statistical analyses. Funding for this project was provided by the Australian ARC Linkage Scheme (P.T.), Koala Action Inc. (P.T.), The Brisbane Koala Science Institute (P.T.) and the Australian DECRA award DE190100238 (M.J.). The Australian Government also contributed to the financial support of this project with a Research Training Program Scholarship for A.R.
A.R. and J.H. are employed by Endeavour Veterinary Ecology Pty Ltd, and A.R. is also a PhD candidate at the University of the Sunshine Coast. J.H. was involved in the development of the K-Tracker biotelemetry system used during the koala management program. J.H. and A.R. are members of Koala Action Inc. There were no potential conflicts of interest for M.J., B.Q. or P.T.
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Rights and permissions
Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons licence, and indicate if changes were made. The images or other third party material in this article are included in the article's Creative Commons licence, unless indicated otherwise in a credit line to the material. If material is not included in the article's Creative Commons licence and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this licence, visit http://creativecommons.org/licenses/by/4.0/.
About this article
Cite this article
Robbins, A., Hanger, J., Jelocnik, M. et al. Koala immunogenetics and chlamydial strain type are more directly involved in chlamydial disease progression in koalas from two south east Queensland koala populations than koala retrovirus subtypes. Sci Rep 10, 15013 (2020). https://doi.org/10.1038/s41598-020-72050-2
This article is cited by
Genotyping of Chlamydia abortus using multiple loci variable number of tandem repeats analysis technique
BMC Veterinary Research (2022)
By submitting a comment you agree to abide by our Terms and Community Guidelines. If you find something abusive or that does not comply with our terms or guidelines please flag it as inappropriate.