Leptospirosis is a widespread but under-reported cause of morbidity and mortality. Global re-emergence of leptospirosis has been associated with the growth of informal urban settlements in which rodents are thought to be important reservoir hosts. Understanding the multi-host epidemiology of leptospirosis is essential to control and prevent disease. A cross-sectional survey of rodents in the Kibera settlement in Nairobi, Kenya was conducted in September–October 2008 to demonstrate the presence of pathogenic leptospires. A real-time quantitative polymerase chain reaction showed that 41 (18.3%) of 224 rodents carried pathogenic leptospires in their kidneys, and sequence data identified
Disclaimer: The findings and conclusions are those of the authors and do not necessarily represent the official position of the Centers for Disease Control and Prevention.
Leptospirosis has been described as the most geographically widespread and prevalent zoonosis in the world.
Among patients hospitalized with acute febrile illness in northern Tanzania, 33.3% of 832 patients showed evidence of exposure to leptospires and 8.8% of 453 patients with paired serum samples had acute leptospirosis based on a ≥ 4-fold increase in microscopic agglutination test titer.
In the Kibera informal settlement, where this study was conducted, acute febrile illness is a common syndrome, with an average of 2.7 episodes per person/year for children < 5 years of age and 0.58 episodes for persons ≥ 5 years of age based on household visit data.
Leptospirosis is maintained through chronic renal infection of maintenance hosts, which shed leptospires in their urine.
Globally, leptospirosis is recognized as a re-emerging infection and has been described as a paradigm for an urban health problem emerging as a consequence of the growth of slums.
As a starting point for advancing our understanding and awareness of leptospirosis in the Kibera settlement in Nairobi, Kenya, we performed a study to determine patterns of
A cross-sectional survey of the rodent population within the Kibera study site was conducted during September–October 2008. The study site lies within the Kibera settlement in Nairobi, Kenya and includes the study area of an ongoing population-based infectious disease surveillance study conducted by the Kenya Medical Research Institute and Centers for Disease Control and Prevention.
The study site was divided into five zones (A–E) on the basis of existing administrative boundaries (
Map of the Kibera study site. Small gray filled polygons indicate individual buildings/structures within the study site. Thick gray lines and writing indicate pre-existing administrative boundaries within the site, which were used to define the five study zones (labeled at the top of the figure). The gray squares within each zone illustrate the location of the rodent trapping grids. The scale and orientation of the figure are indicated (bottom left).
Trapped rodents were humanely euthanized by halothane (Abbott Laboratories, Abbott Park, IL) overdose.
A standardized questionnaire-based survey was conducted to determine the nature and frequency of contacts between rodents and persons in and around households. Questionnaires were administered at 100 households in September–October 2008. In each trapping area, 20 households were selected at random for questionnaire administration from those that had already been recruited for rodent sampling.
A central portion of approximately 25 mg of each kidney was processed for DNA extraction at the University of East London. Tissues were digested by using 180 μL of buffer ATL (QIAGEN, Hilden Germany) and 20 μL of proteinase K (QIAGEN), mixed and incubated overnight at 56°C, and heated at 80°C for 25 minutes to inactivate any pathogens present in the samples before DNA extraction. All tissues were processed for DNA extraction by using the DNeasy Blood and Tissue Kit (QIAGEN) according to the manufacturer's protocol for Purification of Total DNA from Animal Tissues (Spin-Column Protocol) and a final elution volume of 200 μL.
All kidney DNA extracts were diluted 1:5 in sterile water and tested in triplicate by using the SYBR Green
Generalized linear models were used to identify variables associated with the infection status of trapped rodents. In all models, the response variable was a binary measure of infection status (positive or negative) based on the results of the qPCR analyses of kidney samples. The covariates considered were rodent genus (
The phylogenetic analysis included 80 sequences (
Phylogenetic tree of partial
Written informed consent for sampling and questionnaire administration was obtained from representatives of the study households. The protocols and consent forms were reviewed and approved by the Animal Care and Use and Ethical Review Boards of the Kenya Medical Research Institute (#1191) according to institutional guidelines. The study protocols were also approved by the Institutional Animal Care and Use Committee and Institutional Review Board of the U.S. Centers for Disease Control and Prevention (#5410) and complied with the Public Health Service Policy on Humane Care and Use of Laboratory Animals.
A total of 237 rodents were trapped from 948 trap placements in 270 Kibera households, with an overall trap success of 24.9% (95% confidence interval [CI] = 22.2–27.8%). Most trapped rodents were
Pathogenic leptospires were detected in the kidneys of 18.3% (41 of 224; 95% CI = 13.5–24.0%) of rodents by qPCR. Only 4 (10.3%) of 39
One hundred questionnaires were completed and most respondents reported daily sightings of rodents and their excreta in and around Kibera households (
The generalized linear model of infection status revealed that rodents of the genus
Pathogenic leptospires were identified in the Kibera rodent population. Nearly one in five rodents trapped within houses in Kibera had pathogenic leptospires in their kidneys and were thus potentially capable of shedding leptospires into the environment. The questionnaire data showed sightings of multiple rodents and their excreta within households on a daily basis by most study respondents. Previous studies at other urban slum sites have identified rodent sightings around the household as a risk factor for human
According to the results obtained with the Taqman PCR, all positive samples belonged to clade 1, consisting of
The probability of
There is a large population of domestic dogs in Kibera and their density within this study site has been estimated at 740–1,086 dogs/km2.
The multivariate model indicates that rodents trapped in zones D and E, to the east of the site, were significantly more likely to be positive than rodents trapped in the reference zone A (
This study had some limitations. The kidney extracts were diluted to reduce the influence of qPCR inhibitors present in these kidney tissue samples. This dilution step, as well as the effect of any residual inhibition in tissue extracts, could result in false-negative qPCR results. Therefore, 18.3% is considered to be a conservative estimate of true prevalence in the Kibera rodent population. Renal colonization as high as 80.3% has been detected by culture (83.9% by PCR) among rats sampled in an urban setting in Salvador, Brazil.
In this study, we have demonstrated the presence of pathogenic leptospires in the Kibera rodent population. Although the epidemiology of leptospirosis is complex and humans can acquire infection through indirect or direct contacts with a variety of animal reservoir hosts, rodents are frequently identified as important reservoirs in urban slum settings particularly, and household rodent sighting frequencies have been shown to correlate with human exposure risks in other urban slum settings. Our findings, which are consistent with reports from slum sites in South America
Despite increasing recognition of the clinical threat posed by leptospirosis, the impact of leptospirosis on the health and productivity of animal and human populations continues to be widely unrecognized and under-reported. In many human populations, including Kibera, the burden of undifferentiated febrile illness is significant.
We thank the field staff at the National Museums of Kenya; the team at the Kenya Medical Research Institute/Centers for Disease Control and Prevention Public Health and Research Collaboration; and Stella Kiambi, Samuel Chege, John Mugo, and Gilbert Ogango for assistance with the field components of this study; Hans van der Linden for assisting with qPCR assays at KIT; and the residents of Kibera for their support throughout the research project.
Financial support: This study was supported by the Wellcome Trust, United Kingdom (grants 081828/B/06/Z and 096400/Z/11/Z), the Biotechnology and Biological Sciences Research Council, United Kingdom (grant BB/J010367/1) and the Medical Research Council, United Kingdom (grant G0902417 94378).
Authors' addresses: Jo E. B. Halliday, Kathryn J. Allan, and Sarah Cleaveland, Boyd Orr Centre for Population and Ecosystem Health, Institute of Biodiversity, Animal Health and Comparative Medicine, College of Medical, Veterinary and Life Sciences, University of Glasgow, Glasgow, UK, E-mails:
| Code | Serovar | Serogroup | Strain | Species |
|---|---|---|---|---|
| Bif.SE02 | Patoc | Semaranga | Patoc I | |
| Bor.BM02 | Ballum | Ballum | S102 | |
| Bor.HB06 | Jules | Hebdomadis | Jules | |
| Bor.HB10 | Mini | Mini | Sari | |
| Bor.HB22 | Balcanica | Sejroe | 1627 Burgas | |
| Bor.HB23 | Polonica | Sejroe | 493 Poland | |
| Bor.HB30 | Nyanza | Sejroe | Kibos | |
| Bor.HB35 | Nero | Sejroe | Gamsulin | |
| Bor.JV03 | Poi | Javanica | Poi | |
| Bor.JV04 | Sorexjalna | Javanica | Sorex Jalna | |
| Bor.PY13 | Kwale | Pyrogenes | Julu | |
| Bor.TA01 | Tarassovi | Tarassovi | Perepelitsin | |
| Bor.TA11 | Tunis | Tarassovi | P 2/65 | |
| Bor.TA20 | Dikkeni | Sejroe | Mannuthi | |
| Bor.TA21 | Moldaviae | Bataviae | 114-2 | |
| Int.AS06 | Fugis | Australis | Fudge | |
| Int.AS07 | Bangkok | Australis | Bangkok D-92 | |
| Int.AT08 | Sentot | Djasiman | Sentot | |
| Int.AT11 | Djasiman | Autumnalis | Djasiman | |
| Int.BT02 | Bataviae | Bataviae | Van Tienen | |
| Int.BT03 | Paidjan | Bataviae | Paidjan | |
| Int.CA01 | Canicola | Canicola | Hond Utrecht IV | |
| Int.CA05 | Jonsis | Canicola | Jones | |
| Int.CA07 | Broomi | Canicola | Patane | |
| Int.CA12 | Portlandvere | Canicola | My 1039 | |
| Int.CA13 | Kuwait | Canicola | 136/2/2 | |
| Int.HB01 | Hebdomadis | Hebdomadis | Hebdomadis | |
| Int.HB18 | Medanensis | Sejroe | Hond HC | |
| Int.HB19 | Wolffi | Sejroe | 3705 | |
| Int.IC01 | Icterohaemorrhagiae | Icterohaemorrhagiae | RGA | |
| Int.IC03 | Mankarso | Icterohaemorrhagiae | Mankarso | |
| Int.IC04 | Naam | Icterohaemorrhagiae | Naam | |
| Int.Lai | Lai | Icterohaemorrhagiae | Lai | |
| Int.PO01 | Pomona | Pomona | Pomona | |
| Int.PO03 | Monjakov | Pomona | Monjakov | |
| Int.PO06 | Kennewicki | Pomona | LT 1026 | |
| Int.PY04 | Biggis | Pyrogenes | Biggs | |
| Int.PY09 | Manilae | Pyrogenes | LT 398 | |
| Int.PY14 | Camlo | Pyrogenes | LT 64-67 | |
| Kir.AT07 | Bulgarica | Autumnalis | Nicolaevo | |
| Kir.AT19 | Butembo | Autumnalis | Butembo | |
| Kir.AT20 | Bim | Autumnalis | 1051 | |
| Kir.CA02 | Galtoni | Canicola | LT 1014 | |
| Kir.CA03 | Bafani | Canicola | Bafani | |
| Kir.CA04 | Kamituga | Canicola | Kamituga | |
| Kir.CY01 | Cynopteri | Cynopteri | 3522 C | |
| Kir.GR03 | Ratnapura | Grippotyphosa | Wumalasena | |
| Kir.GR04 | Vanderhoedeni | Grippotyphosa | Kipod 179 | |
| Kir.HB03 | Kambale | Hebdomadis | Kambale | |
| Kir.HB09 | Kabura | Hebdomadis | Kabura | |
| Kir.IC09 | Ndahambukuje | Icterohaemorrhagiae | Ndahambukuje | |
| Kir.IC16 | Bogvere | Icterohaemorrhagiae | LT 60-69 | |
| Kir.PO04 | Mozdok | Pomona | 5621 | |
| Kir.PO07 | Tsaratsovo | Pomona | B 81/7 | |
| Kir.PO08 | Kunming | Pomona | K 5 | |
| Nog.AT18 | Huallaga | Djasiman | M 7 | |
| Nog.BT09 | Argentiniensis | Bataviae | Peludo | |
| Nog.TA18 | Carimagua | Shermani | 9160 | |
| San.BT05 | Kobbe | Bataviae | CZ 320 | |
| San.BT06 | Balboa | Bataviae | 735 U | |
| San.HB07 | Maru | Hebdomadis | CZ 285 | |
| San.BT08 | Brasiliensis | Bataviae | An 776 | |
| San.HB33 | Guaricura | Sejroe | Bov. G | |
| San.HB34 | Goiano | Hebdomadis | Bovino 131 | |
| San.IC12 | Weaveri | Sarmin | CZ 390 | |
| San.PO05 | Tropica | Pomona | CZ 299 | |
| San.PY06 | Bagua | Pyrogenes | MW-12 | |
| San.PY07 | Alexi | Pyrogenes | HS-616 | |
| San.PY11 | Sanmartini | Pyrogenes | CT 63 | |
| San.PY12 | Princestown | Pyrogenes | TRVL 112499 | |
| San.TA02 | Bakeri | Tarassovi | LT 79 | |
| San.TA03 | Atlantae | Tarassovi | LT 81 | |
| San.TA07 | Gatuni | Tarassovi | 1473 K | |
| San.TA08 | Atchafalaya | Tarassovi | LSU 1013 | |
| San.TA10 | Rama | Tarassovi | 316 | |
| Wei.JV05 | Coxi | Javanica | Cox | |
| Wei.TA13 | Langati | Tarassovi | M39039 | |
| ARK25 | Undefined | Undefined | – | |
| ARK59 | Undefined | Undefined | – | |
| ARK214 | Undefined | Undefined | – |
Samples with code starting ARK are described in this report. Details of the other strains included in this analysis have been reported.
Rodent trapping summary indicating the trapping effort, species trapped, and trap success in each trapping zone within the Kibera study site
| Trapping zone | No. trap attempts | No. (%) rodents caught | Trap success | |
|---|---|---|---|---|
| A | 152 nights | 4 | 71 (94.7) | 49.3 |
| 30 days | 0 | 7 (100) | 23.3 | |
| B | 98 nights | 6 | 40 (87.0) | 46.9 |
| C | 225 nights | 18 | 17 (48.6) | 15.6 |
| 44 days | 0 | 2 (100) | 4.5 | |
| D | 149 nights | 2 | 37 (94.9) | 25.5 |
| E | 250 nights | 13 | 20 (60.6) | 13.2 |
| Total | 948 | 43 | 194 (81.9) | 24.9 |
Number of rodents trapped include all individuals, including one case (
Trap success calculations are based on the number of successful trap attempts rather than the number of rodents trapped.
Household questionnaire data summary indicating the location, type and frequency of different rodent sighting measures within the Kibera study households
| Rodent sightings | Type | Frequency (%) | |||
|---|---|---|---|---|---|
| Location | Daily | Weekly | Monthly | Never | |
| In house | 1–4 rodents | 69 | 16 | 2 | 13 |
| ≥ 5 rodents | 60 | 11 | 1 | 28 | |
| rodent excreta | 53 | 13 | 0 | 34 | |
| Around/outside the house | 1–4 rodents | 70 | 8 | 5 | 16 |
| ≥ 5 rodents | 57 | 9 | 4 | 30 | |
| rodent excreta | 48 | 11 | 2 | 39 | |
Results of multivariate generalized linear model analysis of risk factors for positive rodent quantitative polymerase chain reaction status within the trapped Kibera rodent population
| Variable | Level | OR | 95% CI | No. | |
|---|---|---|---|---|---|
| Intercept | – | – | – | 1.63 × 10-7 | |
| Trapping zone | A | – | – | 82 | – |
| B | 0.94 | 0.23–4.08 | 46 | 0.96 | |
| C | 3.02 | 0.76–12.03 | 37 | 0.12 | |
| D | 4.92 | 1.65–14.63 | 39 | 0.004 | |
| E | 98.58 | 18.03–539.03 | 33 | 1.18 × 10-7 | |
| Genus | – | 43 | – | ||
| 15.03 | 2.61–86.62 | 194 | 0.002 |
OR = odds ratio, CI = confidence interval.