| Literature DB >> 25978383 |
Olivier Duron1, Valérie Noël1, Karen D McCoy1, Matteo Bonazzi2, Karim Sidi-Boumedine3, Olivier Morel4, Fabrice Vavre4, Lionel Zenner4, Elsa Jourdain5, Patrick Durand1, Céline Arnathau1, François Renaud1, Jean-François Trape1, Abel S Biguezoton6, Julie Cremaschi1, Muriel Dietrich1, Elsa Léger1, Anaïs Appelgren1, Marlène Dupraz1, Elena Gómez-Díaz7, Georges Diatta8, Guiguigbaza-Kossigan Dayo9, Hassane Adakal10, Sébastien Zoungrana9, Laurence Vial11, Christine Chevillon1.
Abstract
Q fever is a highly infectious disease with a worldwide distribution. Its causative agent, the intracellular bacterium Coxiella burnetii, infects a variety of vertebrate species, including humans. Its evolutionary origin remains almost entirely unknown and uncertainty persists regarding the identity and lifestyle of its ancestors. A few tick species were recently found to harbor maternally-inherited Coxiella-like organisms engaged in symbiotic interactions, but their relationships to the Q fever pathogen remain unclear. Here, we extensively sampled ticks, identifying new and atypical Coxiella strains from 40 of 58 examined species, and used this data to infer the evolutionary processes leading to the emergence of C. burnetii. Phylogenetic analyses of multi-locus typing and whole-genome sequencing data revealed that Coxiella-like organisms represent an ancient and monophyletic group allied to ticks. Remarkably, all known C. burnetii strains originate within this group and are the descendants of a Coxiella-like progenitor hosted by ticks. Using both colony-reared and field-collected gravid females, we further establish the presence of highly efficient maternal transmission of these Coxiella-like organisms in four examined tick species, a pattern coherent with an endosymbiotic lifestyle. Our laboratory culture assays also showed that these Coxiella-like organisms were not amenable to culture in the vertebrate cell environment, suggesting different metabolic requirements compared to C. burnetii. Altogether, this corpus of data demonstrates that C. burnetii recently evolved from an inherited symbiont of ticks which succeeded in infecting vertebrate cells, likely by the acquisition of novel virulence factors.Entities:
Mesh:
Year: 2015 PMID: 25978383 PMCID: PMC4433120 DOI: 10.1371/journal.ppat.1004892
Source DB: PubMed Journal: PLoS Pathog ISSN: 1553-7366 Impact factor: 6.823
Fig 1Geographic origin of the sampled ticks and distribution of Coxiella and Rickettsiella infections.
Square size indicates the number of populations sampled per geographic area. Numbers refer to the tick species whereas letters discriminate the different populations screened within a species; this nomenclature is detailed in Table 1. The colors within squares indicate the infection status of populations. Two tick species were infected by both Coxiella and Rickettsiella at the species level, but not at individual and population levels.
List of tick species and populations included in the analysis, with details on their origin, the population sample size, and the prevalence of Coxiella spp. and Rickettsiella spp.
| Tick species | Sample sites | Tick host species or habitat | n |
|
| |
|---|---|---|---|---|---|---|
| Argasidae (soft ticks) | ||||||
| 1 - |
| 1-A, Porto Velho, Rondonia, Brazil | Bat guano in cave | 4 | 0.00 (0) | 0.00 (0) |
| 2 - |
| 2-A, Chaco, Argentina | Unknown | 3 | 1.00 (3) | 0.00 (0) |
| 3 - |
| 3-A, Lobos de Tierra Island, Peru, 2009 | Peruvian Pelican ( | 5 | 1.00 (5) | 0.00 (0) |
| 4 - |
| 4-A, Sao Francisco de Paula,Brazil | Unknown | 3 | 1.00 (3) | 0.00 (0) |
| 5 - |
| 5-A, Juan de Nova Island, Mozambic Channel, 2011 | Sooty Tern ( | 28 | 1.00 (28) | 0.00 (0) |
| 5-B, Réunion Island | Sea bird nests | 3 | 1.00 (3) | 0.00 (0) | ||
| 6 - |
| 6-A, Kenitra, Morocco, 2006 | Rodent burrows | 7 | 0.00 (0) | 1.00 (7) |
| 6-B, Sidi Akhfennir, Morocco, 2006 | Rodent burrows | 18 | 0.00 (0) | 1.00 (18) | ||
| 6-C, Boujdour, Morocco, 2006 | Rodent burrows | 2 | 0.00 (0) | 1.00 (2) | ||
| 6-D, El Argoub, Morocco, 2006 | Rodent burrows | 2 | 0.00 (0) | 1.00 (2) | ||
| 6-E, Lahmiris, Morocco, 2010 | Rodent burrows | 1 | 0.00 (0) | 1.00 (1) | ||
| 6-F, Mostaganem, Algeria, 2012 | Rodent burrows | 4 | 0.00 (0) | 1.00 (4) | ||
| 6-G, Oudhna, Tunisia, 2010 | Rodent burrows | 4 | 0.00 (0) | 1.00 (4) | ||
| 7 - |
| 7-H, unknown | Sea bird nests | 1 | 1.00 (1) | 0.00 (0) |
| 8 - |
| 8-A, La Calle, Tunisia, 2009 | Rodent burrows | 1 | 1.00 (1) | 0.00 (0) |
| 8-B, Taher, Algeria, 2010 | Rodent burrows | 2 | 1.00 (2) | 0.00 (0) | ||
| 9 - |
| 9-A, Kairouan, Tunisia, 2010 | Rodent burrows | 3 | 1.00 (3) | 0.00 (0) |
| 10 - |
| 10-A, Medes Island, Spain, 2009 | Yellow-legged Gull ( | 20 | 1.00 (20) | 0.00 (0) |
| 10-B, Zembra Island, Tunisia, 2009 | Yellow-legged Gull ( | 20 | 1.00 (20) | 0.00 (0) | ||
| 10-C, Carteau, France, 2014 | Yellow-legged Gull ( | 8 | 1.00 (8) | 0.00 (0) | ||
| 11 - |
| 11-A, Izemmourèn, Morocco, 2009 | Rodent burrows | 1 | 1.00 (1) | 0.00 (0) |
| 11-B, Berkane Oued Kiss, Morocco, 2006 | Rodent burrows | 1 | 1.00 (1) | 0.00 (0) | ||
| 11-C, Bir-Jdid, Morocco, 2009 | Rodent burrows | 1 | 1.00 (1) | 0.00 (0) | ||
| 12 - |
| 12-A, Guelmin, Morocco, 2006 | Rodent burrows | 1 | 0.00 (0) | 1.00 (1) |
| 12-B, Sidi Akhfennir, Morocco, 2006 | Rodent burrows | 2 | 0.00 (0) | 1.00 (2) | ||
| 13 - |
| 13-A, Laboratory strain derived from field specimens of unknown origin | Unknown | 3 | 0.00 (0) | 0.00 (0) |
| 14 - |
| 14-A, Bizerte, Tunisia, 2010 | Rodent burrows | 1 | 0.00 (0) | 1.00 (1) |
| 14-B, Oudhna, Tunisia, 2010 | Rodent burrows | 2 | 0.00 (0) | 1.00 (2) | ||
| 15 - |
| 15-A, Fes, Morocco, 2010 | Rodent burrows | 4 | 1.00 (4) | 0.00 (0) |
| 15-B, Kenitra, Morocco, 2006 | Rodent burrows | 4 | 1.00 (4) | 0.00 (0) | ||
| 15-C, Beb-Lerba, Morocco, 2010 | Rodent burrows | 4 | 1.00 (4) | 0.00 (0) | ||
| 15-D, Oued Choufcherk, Morocco, 2010 | Rodent burrows | 4 | 1.00 (4) | 0.00 (0) | ||
| 15-E, Bouira, Algeria, 2010 | Rodent burrows | 4 | 1.00 (4) | 0.00 (0) | ||
| 15-F, Berrouaghia, Algeria, 2010 | Rodent burrows | 4 | 1.00 (4) | 0.00 (0) | ||
| 15-G, Chlef, Algeria, 2010 | Rodent burrows | 4 | 1.00 (4) | 0.00 (0) | ||
| 16 - |
| 16-A, Chile | Common vampire Bat ( | 3 | 1.00 (3) | 0.00 (0) |
| 17 - |
| 17-A, Laboratory strain derived from field specimens collected in Mahitsy, Madagascar, 2008–2010 | Unknown | 3 | 0.00 (0) | 0.00 (0) |
| 18 - |
| 18-A, Salta, Argentina | Environement | 18 | 1.00 (18) | 0.00 (0) |
| 18-B, Laboratory strain derived from field specimens collected in Nhecolandi, Pantanal, Brazil | Environement | 4 | 1.00 (4) | 0.00 (0) | ||
| 19 - |
| 19-A, Saïda Mt Daïa, Algeria, 2012 | Rodent burrows | 1 | 1.00 (1) | 0.00 (0) |
| 19-B, Mostaganem, Algeria, 2012 | Rodent burrows | 2 | 1.00 (2) | 0.00 (0) | ||
| 20 - |
| 20-A, Dielmo, Senegal, 2002 | Rodent burrows | 20 | 1.00 (20) | 0.00 (0) |
| 20-B, Kanène Khar, Senegal, 2003 | Rodent burrows | 17 | 1.00 (17) | 0.00 (0) | ||
| 20-C, Richard-Toll, Senegal, 2003 | Rodent burrows | 19 | 1.00 (19) | 0.00 (0) | ||
| 20-D, Sogoli, Mali, 2007 | Rodent burrows | 10 | 1.00 (10) | 0.00 (0) | ||
| 20-E, M’Chounèche, Algeria, 2009 | Rodent burrows | 37 | 1.00 (37) | 0.00 (0) | ||
| 21 - |
| 21-A, Pan de Azucar, Chile, 2010–2013 | Humboldt penguin ( | 3 | 1.00 (3) | 0.00 (0) |
| 22- |
| 22-A, Boa Vista Island, Cape Verde, 2008 | Cape Verde Shearwater ( | 16 | 1.00 (16) | 0.00 (0) |
| Ixodidae (hard ticks) | ||||||
| 23 - |
| 23-A, Laboratory strain derived from field engorged females collected in Oklahoma, USA, 1976–2004 | Unknown | 20 | 1.00 (20) | 0.00 (0) |
| 24 - |
| 24-A, Chapada Gaucha, Brazil, 2013 | Unknown | 3 | 1.00 (3) | 0.00 (0) |
| 25 - |
| 25-A, Petite Ile, La Réunion, 2012 | Wedge-Tailed Shearwater ( | 3 | 1.00 (3) | 0.00 (0) |
| 26 - |
| 26-A, La Réunion | Unknown | 2 | 1.00 (2) | 0.00 (0) |
| 27 - |
| 27-A, Cavaillon, France, 2011 | Vegetation | 1 | 1.00 (1) | 0.00 (0) |
| 27-B, Les Plantiers, France, 2013 | Vegetation | 1 | 1.00 (1) | 0.00 (0) | ||
| 28 - |
| 28-A, Hopland, Mendocino Co, California, 1985 | Environement | 6 | 0.00 (0) | 0.00 (0) |
| 29 - |
| 29-A, Proveysieux, France, 2011 | Vegetation | 1 | 0.00 (0) | 0.00 (0) |
| 30 - |
| 30-A, Laboratory strain derived from field specimens collected in Xiaowutai National Natural Reserve Area, China | 2 | 1.00 (2) | 0.00 (0) | |
| 31 - |
| 31-A, Queen's biology station, Ontario, Canada, 2013 | Vegetation | 2 | 0.00 (0) | 0.00 (0) |
| 32 - |
| 32-A, East Sussex, England, 2011 | Vegetation | 5 | 1.00 (5) | 0.00 (0) |
| 33 - |
| 33-A, Zimbabwe, 1998 | Zebu ( | 3 | 0.00 (0) | 0.00 (0) |
| 34 - |
| 34-A, Veneguera, Canaries, 2010 | Vegetation | 2 | 0.00 (0) | 0.00 (0) |
| 35 - |
| 35-A, Bretagne, France, 2008 | Eurasian Collared Dove ( | 1 | 0.00 (0) | 0.00 (0) |
| 36- |
| 36-A, Bretagne, France, 2008 | European Red Fox ( | 1 | 1.00 (1) | 0.00 (0) |
| 36-B, Beaumont-Monteux, France, 2008 | European Hedgehog ( | 2 | 1.00 (1) | 0.00 (0) | ||
| 37 - |
| 37-A, Crozet Archipelago, 2003 | Sea bird nests | 2 | 0.00 (0) | 0.00 (0) |
| 38 - |
| 38-A, Hopland, Mendocino Co, California, 1985 | Environement | 6 | 0.00 (0) | 0.00 (0) |
| 39 - |
| 39-A, Oulu, Finland, 2011 | Vegetation | 3 | 0.00 (0) | 0.00 (0) |
| 40 - |
| 40-A, Lehmäsaari, Finland, 2011 | Vegetation | 20 | 0.00 (0) | 0.00 (0) |
| 40-B, Rioja, Spain, 2011 | Vegetation | 20 | 0.00 (0) | 0.00 (0) | ||
| 40-C, Mafra, Portugal, 2013 | Vegetation | 16 | 0.00 (0) | 0.00 (0) | ||
| 40-D, Neuchâtel, Switzerland, 2012 | Vegetation | 16 | 0.00 (0) | 0.00 (0) | ||
| 40-E, Chur, Switzerland, 2012 | Hazel grouse ( | 4 | 0.00 (0) | 0.00 (0) | ||
| 40-F, Sénart, France, 2010 | European Roe Deer ( | 22 | 0.00 (0) | 0.05 (1) | ||
| 40-G, Ain, France, 2004 | Vegetation | 2 | 1.00 (1) | 0.00 (0) | ||
| 41 - |
| 41-A, Queen's biology station, Ontario, Canada, 2013 | Vegetation | 3 | 0.00 (0) | 0.00 (0) |
| 42 - |
| 42-A, Kilarney Circuit, Coolangubra, Australia, 1982 | Common Wombat (Vo | 2 | 0.00 (0) | 1.00 (2) |
| 43 - |
| 43-A, Ariy Kamen Islet, Kamchatka, Russia, 2008 | Black-legged Kittiwake ( | 4 | 0.00 (0) | 0.00 (0) |
| 44 - |
| 44-A, Possession Island, Crozet Archipelago, 2003 | King Penguin ( | 20 | 0.00 (0) | 0.00 (0) |
| 44-B, Hornoeya Island, Norway, 2010 | Brünnich's Guillemot ( | 20 | 0.00 (0) | 0.00 (0) | ||
| 44-C, Triangle Island, Canada, 2010 | Rhinoceros Auklet ( | 14 | 0.50 (7) | 0.00 (0) | ||
| 44-D, Pitchie2, Kamchatka, Russia, 2008 | Red-faced Cormorant ( | 20 | 0.00 (0) | 0.00 (0) | ||
| 44-E, Grimsey, Iceland, 2003 | Atlantic Puffin ( | 25 | 0.00 (0) | 0.20 (5) | ||
| 45 - |
| 45-A, Guiglo, Ivory Coast, 1994 | Leopard ( | 12 | 1.00 (12) | 0.00 (0) |
| 46 - |
| 46-A, Guiglo, Ivory Coast, 1994 | Dog ( | 12 | 1.00 (12) | 0.00 (0) |
| 47 - |
| 47-A, Burkina-Faso, 2013 | Zebu ( | 17 | 1.00 (17) | 0.00 (0) |
| 47-B, Gogonou, Benin, 2012 | Zebu ( | 5 | 1.00 (5) | 0.00 (0) | ||
| 48 - |
| 48-A, CCA Farm, New Caledonia, 2003 | Cattle ( | 12 | 1.00 (12) | 0.00 (0) |
| 48-B, BMMMM Farm, New Caledonia, 2003 | Cattle ( | 12 | 1.00 (12) | 0.00 (0) | ||
| 49 - |
| 49-A, Italia | Cattle ( | 2 | 1.00 (2) | 0.00 (0) |
| 50- |
| 50-A, Burkina-Faso, 2013 | Zebu ( | 20 | 0.95 (19) | 0.00 (0) |
| 50-B, Gogonou, Benin, 2012 | Zebu ( | 9 | 1.00 (9) | 0.00 (0) | ||
| 50-C, Sandvelt, South Africa, 2011 | Blue Wildebeest (Connochaetes taurinus), Greater Kudu ( | 20 | 1.00 (20) | 0.00 (0) | ||
| 50-D, Queenstown, South Africa, 2011 | Zebu ( | 17 | 1.00 (17) | 0.00 (0) | ||
| 50-E, Vaalwater, South Africa, 2010 | Zebu ( | 19 | 1.00 (19) | 0.00 (0) | ||
| 50-F, Lephalale, South Africa, 2010 | South African Giraffe ( | 9 | 1.00 (9) | 0.00 (0) | ||
| 50-G, Zimbabwe, 1998 | Impala ( | 11 | 1.00 (11) | 0.00 (0) | ||
| 51 - |
| 51-A, Zimbabwe, 1998 | Zebu ( | 8 | 1.00 (8) | 0.00 (0) |
| 52 - |
| 52-A, Burkina-Faso, 2013 | Zebu ( | 18 | 0.94 (17) | 0.00 (0) |
| 52-B, Gogonou, Benin, 2012 | Zebu ( | 3 | 1.00 (3) | 0.00 (0) | ||
| 53 - |
| 53-A, Kpinnou, Benin, 2012 | Zebu ( | 20 | 1.00 (20) | 0.00 (0) |
| 53-B, Ambalanirana, Madagascar, 2013 | Zebu ( | 18 | 1.00 (18) | 0.00 (0) | ||
| 53-C, Imeritsiatosika, Madagascar, 2013 | Zebu ( | 14 | 1.00 (14) | 0.00 (0) | ||
| 53-D, Eglinton, South Africa, 2011 | Zebu ( | 20 | 1.00 (20) | 0.00 (0) | ||
| 53-E, Welverdiemda, South Africa, 2011 | Zebu ( | 11 | 1.00 (11) | 0.00 (0) | ||
| 53-F, Laboratory strain derived from field engorged females collected in Kpinnou, Benin, 2012 | Girolando (Cattle x Zebu hybrid) | 7 | 1.00 (7) | 0.00 (0) | ||
| 54 - |
| 54-A, Gard, France, 2006 | Vegetation | 2 | 1.00 (2) | 0.00 (0) |
| 55- |
| 55-A, Brazil | Dog ( | 1 | 1.00 (1) | 0.00 (0) |
| 55-B, Montferrier-sur-Lez, France, 2013 | Dog ( | 1 | 1.00 (1) | 0.00 (0) | ||
| 56 - |
| 56-A, Italia | Vegetation | 2 | 1.00 (2) | 0.00 (0) |
| 56-B, Kerkyra, Greece, 2012 | Human ( | 3 | 1.00 (3) | 0.00 (0) | ||
| 57- |
| 57-A, Guiglo area, Ivory Coast, 1994 | Leopard ( | 3 | 1.00 (3) | 0.00 (0) |
| 58- |
| 58-A, Guiglo, Ivory Coast, 1994 | Dog ( | 2 | 1.00 (2) | 0.00 (0) |
Genetic estimates for 85 Coxiella-like strains and for 15 Coxiella burnetii reference strains.
| Locus | Function | L | Strains | Ni | Pnsi | Na | Ps | Ad | π | D |
|---|---|---|---|---|---|---|---|---|---|---|
| 16S rRNA | Small ribosomal subunit | 1066 |
| 85 | 93.0–100 | 40 | 262 | 0.985 | 0.038 | 39.960 |
|
| 15 | 99.7–100 | 4 | 4 | 0.552 | 0.001 | 1.224 | |||
| 23S rRNA | Large ribosomal subunit | 496 |
| 82 | 84.2–100 | 34 | 177 | 0.978 | 0.079 | 39.393 |
|
| 15 | 99.4–100 | 2 | 2 | 0.133 | 0.001 | 0.267 | |||
|
| Chaperone protein GROEL | 550 |
| 82 | 68.7–100 | 37 | 292 | 0.982 | 0.179 | 98.527 |
|
| 15 | 99.4–100 | 5 | 5 | 0.562 | 0.002 | 0.895 | |||
|
| DNA-directed RNA polymerase beta chain | 474 |
| 85 | 68.7–100 | 38 | 250 | 0.981 | 0.205 | 97.136 |
|
| 15 | 99.3–100 | 4 | 4 | 0.467 | 0.001 | 0.648 | |||
|
| Chaperone protein DNAK | 423 |
| 74 | 69.6–100 | 33 | 227 | 0.979 | 0.177 | 75.789 |
|
| 15 | 99.8–100 | 3 | 1 | 0.362 | 0.001 | 0.381 | |||
| Full concatenated data set | 3009 |
| 71 | 81.8–100 | 36 | 1139 | 0.984 | 0.115 | 346.990 | |
|
| 15 | 99.6–100 | 7 | 16 | 0.781 | 0.001 | 2.933 |
Analyses are based on nucleotide sequences of five housekeeping genes, excluding sites with alignment gaps and/or missing data. L, sequence fragment length in base pairs; Ni, Number of examined strains; Pnsi, Pairwise nucleotide sequence identity (%); Na, number of alleles; Ps, number of polymorphic sites; Ad, allelic diversity; π, nucleotide diversity; D, average number of nucleotide differences between sequences.
Fig 2Phylogenetic network with concatenated 16S rRNA, 23S rRNA, GroEL, rpoB and dnaK sequences (3009 unambiguously aligned bp), including 71 Coxiella-like strains of ticks, 15 C. burnetii reference strains, and bacterial outgroups.
The four Coxiella clades are labeled A to D. A zoom on the A clade which contains C. burnetii isolates is shown in Supplementary Fig C in S1 Text. Each number corresponds to one tick species as detailed in Table 1. Blue—Coxiella-like organisms; red—C. burnetii; green—Rickettsiella; black- other bacteria. All multi-locus typing of Coxiella and Rickettsiella of ticks are new sequences from this study. The scale bar is in units of substitution/site.
Fig 3Characterization of new Coxiella strains derived from whole-genome sequencing (WGS) of the cattle tick Rhipicephalus microplus.
(a) Percent identity of 50 genes uniquely attributable to Coxiella from R. microplus WGS versus 15 sequenced C. burnetii genomes and other reference genomes. (b) Bacterial phylogeny, comprising the Coxiella found in the R. microplus WGS data, reconstructed from the concatenated sequences of Fig 3A (19,304 unambiguously aligned bp) using maximum-likelihood (ML). Branch numbers indicate percent bootstrap support for major branches (1,000 replicates; only bootstrap values >90% are shown). The scale bar is in units of substitution/site.