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The American Journal of Tropical Medicine and Hygiene logoLink to The American Journal of Tropical Medicine and Hygiene
. 2010 Sep;83(3):633–636. doi: 10.4269/ajtmh.2010.09-0609

Risk Factors for Clinical Leptospirosis from Western Jamaica

John Keenan 1, Genine Ervin 1, Maung Aung 1, Gerald McGwin Jr 1, Pauline Jolly 1,*
PMCID: PMC2929062  PMID: 20810831

Abstract

A retrospective, matched case-control study was conducted in Jamaica's Western Regional Health Authority (WRHA). Forty-three individuals developing clinical leptospirosis between January 2005 and December 2007 (i.e., cases) were age and neighborhood matched to 89 controls. Odds ratios (OR) and associated 95% confidence intervals (CIs) and the relative excess risk due to interaction (RERI) were calculated. Cases had increased odds of contact with rodents OR 3.52, goats OR 3.38, and being engaged in outdoor labor OR 5.30. Knowledge of leptospirosis and indoor work was protective, OR 0.39 and OR 0.16, respectively. Positive RERI values were noted for joint exposure to rodents and goats (RERI 5.54), outdoor labor and goats (RERI 6.97), and outdoor labor and rodents (RERI 30.59). Our results suggest a synergistic effect of occupational and environmental exposures on clinical human leptospirosis from the WRHA. Knowledge of the disease and its risk factors allows for protection from the disease.

Introduction

The infectious disease caused by a pathogenic species of the Leptospira bacteria, leptospirosis, is considered the most widespread zoonotic disease in the world, potentially affecting millions of people each year.13 The World Health Organization (WHO) estimates yearly incidence rates from 1/100,000 endemically, rising to 100/100,000 during outbreaks in tropical climates, compared with 0.1–1/100,000 in temperate climates.4 In the Caribbean, incidence rates are the highest in the world5 and case fatality rates as high as 23.6% have been observed.2 Due in part to the often non-specific clinical presentation and lack of diagnostic capabilities, leptospirosis is often undiagnosed or misdiagnosed.4,6,7

Humans become exposed to the Leptospira organism by contact, either directly or indirectly, with urine from infected animals. Among the more important animal sources of human exposure are rats,7,8 horses, goats, cows, pigs, and dogs.9,10 Dogs may contribute significantly to human exposure, particularly in tropical countries.11 Exposure may also occur through occupational pursuits or from environmental sources such as standing water or soil containing the Leptospira organism.4,7,12

Human leptospirosis was first confirmed in Jamaica in 1953.13 By the mid-1960s, the number of Jamaicans with antibodies to the Leptospira bacteria was estimated between 50,000 and 100,000.14 Several studies consider Jamaica as having one of the highest incidence rates in the Caribbean,15 if not the world.5 In addition to humans, in Jamaica goats, horses, pigs, cattle, dogs, sheep, rodents, and the mongoose have all been found seropositive.14 Despite the long history of the disease on the island and the presence of seropositive reservoirs, few published reports detail the risks for human exposure. The main aim of this study is to identify the risk factors associated with contracting leptospirosis in four western parishes of Jamaica.

Methods

A retrospective matched case-control study of clinical leptospirosis from the Western Regional Health Authority (WRHA) of Jamaica was conducted from January 2005 to December 2007. The WRHA, one of Jamaica's four regional health authorities, serves over 464,000 people at 84 healthcare centers and four hospitals in Jamaica's Western Parishes. Four parishes constitute the WRHA, including Hanover, St. James, Trelawny, and Westermorland. This study received ethical approval from the Institutional Review Board (IRB) of the University of Alabama at Birmingham, the Advisory Panel of Ethics and Meidico-Legal Affairs from the Jamaican Ministry of Health (MOH), and the WRHA.

Study population.

Cases were defined as individuals who were hospitalized between January 2005 and December 2007 with serologically confirmed leptospirosis and resided in one of the four parishes served by the WRHA. Fatal leptospirosis cases from the study period were excluded from the study for accuracy of measuring exposures. Serological diagnosis was by either an immunoglobulin G (IgG) enzyme-linked immunosorbent assay (ELISA) (Diagnositc Automation Inc., Calabasas, CA) or a rapid IgM dot-ELISA dipstick test (DST) (PanBio Diagnostics, Queensland, Australia). Each test detected antibodies to the cross-reactive Leptospira biflexa patoc 1. Only individuals with test results of three full dots (strong positive) from the DST or a titer of 1:640 and above for the IgG ELISA was included in the analysis. Both tests are capable of detecting antibodies to several serovars and the DST has showed high sensitivity and specificity particularly during the acute phase.16,17 A symptomatic patient with positive results by either of these methods is considered to have clinical leptospirosis by the Jamaica MOH. Controls were matched (1:n) to cases on neighborhood and age (±10 years). Controls were individuals without reported clinical leptospirosis, who resided in the same neighborhood as a case during the study period. Up to three controls were selected for convenience by the interviewers and interviewed on the same day as the case interview.

Data collection and statistical analysis.

Data collection was conducted from May 2008 to August 2008. An in-home interviewer-administered questionnaire was conducted for both cases and controls to collect exposure information. Cases were only questioned about possible exposures from the 3 months preceding his or her leptospirosis diagnosis. Controls were questioned about possible exposures corresponding to the same 3 months as the matched case. Information gathered included occupation, animal contacts, highest education level, and behavioral habits such as walking barefoot and environmental factors such as home flooding history.

Odds ratios (OR) and 95% confidence intervals (CIs) were calculated to measure the association between potential risk factors and clinical leptospirosis using conditional logistic regression. Relative excess risk due to interaction (RERI) was calculated for significant results. Relative excess risk due to interaction measures the additional risk experienced as a result of joint exposures.18 The recommended reporting of interactions is to report each effect separately then the combined effects compared with the unexposed group.19 This method allows one to use the unexposed group as a reference group to evaluate interaction on both an additive and multiplicative scale.

Results

Of the 77 clinical human leptospirosis cases from the WRHA, residences were available for 50. Three of the 50 were fatal cases of leptospirosis and excluded from the analysis. Suitable controls could not be obtained for four cases, resulting in a total of 43 cases matched (1:n) to variable numbers of a total of 89 controls. Cases were mostly male (79.1%) and had a mean age of 37.8 years. Similar to cases, the majority of controls were male (62.9%) (conditional logistic OR = 5.15, 95% CI = 1.14–23.37, P = 0.03) and the overall mean control age was 38 years (Table 1). With regard to animal contact, cases were more likely than controls to have contact with rodents, OR = 3.52 (95% CI = 1.33–9.36, P = 0.01) and goats OR 3.38 (95% CI = 1.24–9.06), P = 0.02) (Table 2). Significant findings were noted in two occupational groups. Indoor work (healthcare, clerical, culinary, and those working from home) was protective with an OR 0.16 (95% CI = 0.04–0.71, P = 0.02) and outdoor labor (farming, masonry, fishing) increased the odds of disease, OR = 5.30 (95% CI = 1.41–19.92, P = 0.01). None of the environmental/behavioral variables were significant. Analysis of the educational variables found that knowledge of leptospirosis was protective OR 0.39 (95% CI = 0.16–0.93, P = 0.03), and a non-significant trend of higher OR associated with lower levels of education (Table 2). Table 3 illustrates that the relative excess risk for those engaged in outdoor labor and those who had contact with goats or rodents, and those exposed to rodents and goats exceeded the sum of each singular risk factor.

Table 1.

General demographic information for clinical leptospirosis among cases and age-matched neighborhood controls from the Western Regional Health Authority

Cases N = 43 Controls N = 89
Age (years)
0–19 7 14
20–29 10 20
30–39 7 19
40–49 8 10
50–59 5 16
60+ 6 10
Average age 37.84 38
Gender
Males 34 56
Females 9 33
Parish
Hanover 17 41
St. James 7 10
Trelawny 12 27
Westmoreland 7 11

Table 2.

Univariate and multivariate analysis for matched odds ratios (OR) of clinical leptospirosis from environmental, occupational, and animal exposures

Risk factors by category Matched unadjusted OR P value Matched adjusted OR* P value
Environmental/behavioral
Home flooded 0.31 (0.06–1.53) 0.15 0.24 (0.05–1.29) 0.10
Participate in fresh water activities (canoe, fish, swim) 1.12 (0.44–2.83) 0.81 0.60 (0.22–1.67) 0.33
Work in garden 0.64 (0.25–1.64) 0.35 0.62 (0.29–1.60) 0.32
Knowledge of leptospirosis 0.37 (0.16–0.89) 0.03 0.39 (0.16–0.93) 0.03
Presence of overgrown vegetation around the home 1.86 (0.75–4.62) 0.18 2.22 (0.87–5.68) 0.10
Occupational
Unemployed 0.50 (0.12–2.07) 0.34 0.56 (0.13–2.42) 0.44
Student 1.44 (0.34–6.11) 0.62 1.38 (0.31–6.20) 0.67
Domestic work 1.40 (0.33–6.01) 0.65 2.44 (0.51–11.71) 0.26
Outdoor labor (farming/masonry/fishing) 6.73 (1.84–24.63) < 0.01 5.30 (1.41–19.92) 0.01
Indoor non-labor 0.14 (0.03–0.62) < 0.01 0.16 (0.04–0.71) 0.02
Animal Contact
Dogs 0.61 (0.27–1.41) 0.25 0.54 (0.23–1.23) 0.14
Cats 0.69 (0.26–1.82) 0.45 0.75 (0.28–2.05) 0.58
Cows 1.34 (0.34–5.26) 0.68 1.16 (0.29–4.58) 0.84
Pigs 1.87 (0.57–6.07) 0.30 1.52 (0.41–5.48) 0.52
Goats 3.59 (1.33–9.39) 0.01 3.38 (1.24–9.06) 0.02
Rodents 3.43 (1.30–9.07) 0.01 3.52 (1.33–9.36) 0.01
Chickens 1.27 (0.45–3.61) 0.65 1.07 (0.37–3.04) 0.90
Education
University Ref Ref
Some Secondary 2.00 (0.68–5.58) 0.20 1.76 (0.59–5.22) 0.31
Primary 3.43 (0.96–12.26) 0.06 2.63 (0.70–9.91) 0.15
Some primary 4.23 (0.97–18.58) 0.06 2.83 (0.60–13.56) 0.19
None 0.50 (0.05–4.69) 0.55 0.47 (0.05–4.46) 0.51
Frequency of walking outside barefoot
Less than 1 day per week Ref Ref
1 day per week 1.07 (0.27–4.33) 0.92 1.03 (0.26–4.13) 0.96
2–7 days per 0.23 (0.04–1.24) 0.09 0.26 (0.05–1.36) 0.11
7 days per week 0.31 (0.09–1.09) 0.07 0.36 (0.10–1.30) 0.12
Frequency of walking outside in sandals
Less than 1 day per week Ref Ref
1 day per week 1.40 (0.43–4.51) 0.57 1.28 (0.37–4.48) 0.70
2–7 days per 2.27 (0.40–13.03) 0.33 1.75 (0.30–10.13) 0.53
7 days per week 2.97 (0.82–10.74) 0.10 2.72 (0.74–9.96) 0.13
*

Adjusted for sex.

Each exposure is not mutually exclusive; the unexposed group is the reference for the exposed.

Table 3.

Relative excess risk caused by interactions calculated from unadjusted odds ratios (ORs) with those unexposed to both variables serving as the reference group

Contact with goats Outside labor
+
+ 14.17 2.54
4.69 1
RERI 6.94
Contact with rodents Outside labor
+
+ 44.11 4.35
10.17 1
RERI 30.59
Contact with goats Contact with rodents
+
+ 9.94 2.56
2.84 1
RERI 5.54
*

RERI = relative excess risk due to interaction.

Thirty-two of the cases were positive by the DST, 15 by the IgG ELISA, and four of the seven tested by both tests were dually positive. Three individuals whose test results did not correlate were each positive for the IgG and negative for the DST. A separate unadjusted analysis was conducted on only those testing positive by the DST with the presence of overgrown vegetation around the home OR = 4.51 (95% CI = 1.23–6.52, P = 0.02) and sex OR = 3.69 (95% CI = 0.77–17.63, P = 0.10) being the only variables with a change in significance. The ORs for the DST only sub-analysis for the other significant findings were 6.96 (95% CI = 1.96–24.78), 4.51 (95% CI = 1.42–14.28), 5.75 (95% CI = 1.51–21.86), 0.08 (95% CI = 0.10–0.64), and 0.37 (95% CI = 0.14–1.00) for contact with rodents, goats, outdoor occupations, indoor occupations, and the knowledge of leptospirosis, respectively.

Discussion

In this retrospective case-control study from Western Jamaica, those with clinical leptospirosis were more likely to have one or more of the following: exposure to rodents, contact with goats, and employment in occupations involving outdoor labor. Those with the disease were less likely to have knowledge of the disease and to be engaged in indoor occupations such as culinary, clerical, or healthcare. This represents the first evidence of the protective effects of leptospirosis educational efforts in Jamaica.

The association with rodent exposure and outdoor labor occupations is expected. Rats are an important reservoir host for pathogenic serovars of Leptospira and the most common source for human leptospirosis.7 Additionally, rodents have been documented as carriers of the bacteria in many Caribbean nations15 and exposure to rodents was found to increase the odds of disease 8-fold in Barbados.20 Similar to contact with rodents, the association between occupations involving outdoor labor and developing human leptospirosis is well documented.7 Numerous reports from the Caribbean have documented those working in outdoor labor or farming as having the highest seroprevalence rates.21,22 Although finding goats as contributing to human disease was not expected, it is not unreasonable. In Barbados, contact with goats was found to increase the odds of developing the disease almost 2-fold21 and a study from Jamaica found 62% of the goats positive for Leptospira antibodies.23 One of the more important findings, with respect to public health impact, was that knowledge of leptospirosis is protective. This perhaps provides evidence for the value of public health education in the region. Unlike studies in other Caribbean areas, exposure to dogs, gardening, walking barefoot, and home flooding were each non-significant.

Unlike previous studies investigating risk factors for human leptospirosis, we also explored the role of interactions among significant exposures. Positive RERI values were noted in three separate categories, 1) individuals with a combined exposure to rodents and goats, 2) employment as an outdoor laborer with exposure to goats, and 3) employment as an outdoor laborer with exposure to rodents. Exposures to these combinations of risk factors produces an amplified effect compared with what one would expect based on exposure to either risk factor. As this study was largely exploratory, RERI values were not calculated for every possible combination of interaction. Furthermore, RERI values for protective measures are difficult to interpret,19 thus were not calculated.

The results of this study may have been affected by several limitations. The length of time between time of disease and interview may have caused a general problem of remembering exposure to possible risk factors. However, such recall bias would be non-differential misclassification thus biasing the results toward the null. Cases were diagnosed by one of two serological methods. Several studies have showed prolonged elevated anti-Leptospiral antibody levels.2427 Thus, higher titer cut-off levels are recommended for endemic areas such as Jamaica.7 A higher cut-off was used for the IgG test in an effort to detect current disease rather than past exposure. It should be noted that each of the cases were hospital patients with symptomatic disease highly suggestive of leptospirosis and when possible other diseases with non-specific febrile symptoms were tested and ruled out. In addition, the Jamaica MOH considers a positive result from either of these tests as confirmatory for clinical leptospirosis in symptomatic patients. It is possible the MOH method misclassifies some previously exposed individuals as current clinical cases. In this situation misclassifying the individual with persistently elevated IgM would not depend on any of the exposure variables and would be considered non-differential misclassification. Controls were not randomly but conveniently selected from the same neighborhoods as the cases. Using neighborhood controls ensured selection was from the same source population as cases and it would not be unreasonable to assume conveniently selected neighborhood controls would behave differently from randomly selected ones. Interviewers knew the disease status of the interviewee, raising the possibility of introducing interviewer effects by asking probing questions differently for cases than controls. The small sample size and matched design limited power to detect significant findings among variables with larger OR. Finally, although attempts were made to recruit all 77 cases identified, only 43 were actually recruited. Similarities or differences of the excluded cases to the recruited cases cannot be determined.

In summary, our results suggest clinical human leptospirosis from the WRHA is a result of occupational, environmental, and animal exposures. Deviations from additivity exist for interactions of several exposures. Such deviations suggest important synergistic effects of several risk factors in producing clinical leptospirosis. Knowledge of the disease and its causes allows for protection from the disease, perhaps providing support for the effectiveness of regional public health campaigns.

Footnotes

Financial support: This study was supported by the Minority Health International Research Training (MHIRT) grant no. T37-MD001448 from the National Center on Minority Health and Health Disparities, National Institutes of Health, Bethesda, MD, and the Ministry of Health, Jamaica.

Authors' addresses: John Keenan, Genine Ervin, Gerald McGwin Jr, and Pauline Jolly, University of Alabama at Birmingham, School of Public Health, Department of Epidemiology, Birmingham, AL, E-mails: gre1979@uab.edu, JKeenan@uab.edu, Gerald.McGwin@ccc.uab.edu, and JollyP@ms.soph.uab.edu. Maung Aung, Western Regional Health Authority, Montego Bay, Jamaica, E-mail: rtdwrha@gmail.com.

References

  • 1.CDC . Leptospirosis. Atlanta, GA: CDC; 2005. [Google Scholar]
  • 2.WHO Leptospirosis worldwide, 1999. Wkly Epidemiol Rec. 1999;74:237–242. [PubMed] [Google Scholar]
  • 3.White F, Hospedales CJ. Communicable disease control as a Caribbean public health priority. Bull Pan Am Health Organ. 1994;28:73–76. [PubMed] [Google Scholar]
  • 4.WHO . Human Leptospirosis: Guidance for Diagnosis, Surveillance and Control. Geneva: World Health Organization; 2003. [Google Scholar]
  • 5.Pappas G, Papadimitriou P, Siozopoulou V, Christou L, Akritidis N. The globalization of leptospirosis: worldwide incidence trends. Int J Infect Dis. 2008;12:351–357. doi: 10.1016/j.ijid.2007.09.011. [DOI] [PubMed] [Google Scholar]
  • 6.Cachay ER, Vinetz JM. A global research agenda for leptospirosis. J Postgrad Med. 2005;51:174–178. [PMC free article] [PubMed] [Google Scholar]
  • 7.Levett PN. Leptospirosis. Clin Microbiol Rev. 2001;14:296–326. doi: 10.1128/CMR.14.2.296-326.2001. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 8.Ido Y, Hoki R, Ito H, Wani H. The rat as a carrier of Spirochaeta icterohaemorrhagiae, the causative agent of Weil's Disease (Spirochaetosis icterohaemorrhagica) J Exp Med. 1917;26:341–353. doi: 10.1084/jem.26.3.341. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 9.The Center for Food Security and Public Health. Ames, IA: Iowa State University; 2005. (Leptospirosis). [Google Scholar]
  • 10.Acha PN, Szyfres B, Bureau Pan American Sanitary . Zoonoses and Communicable Diseases Common to Man and Animals. Washington, DC: Pan American Health Organization, Pan American Sanitary Bureau, Regional Office of the World Health Organization; 1987. [Google Scholar]
  • 11.Weekes CC, Everard COR, Levett PN. Seroepidemiology of canine leptospirosis on the island of Barbados. Vet Microbiol. 1997;57:215–222. doi: 10.1016/s0378-1135(97)00127-2. [DOI] [PubMed] [Google Scholar]
  • 12.Waitkins SA. Leptospirosis as an occupational disease. Br J Ind Med. 1986;43:721–725. doi: 10.1136/oem.43.11.721. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 13.Bras G. Leptospirosis in Jamaica: case report. West Indian Med J. 1955;4:126–128. [PubMed] [Google Scholar]
  • 14.Segree W, Fitz-Henly M, Rawlins J, Bowen-Wright C. Leptospirosis: a review of the Jamaican experience compared with other Caribbean territories. West Indian Med J. 1982;31:54–60. [PubMed] [Google Scholar]
  • 15.Everard JD, Everard CO. Leptospirosis in the Caribbean. Rev. Med. Microbiol. 1993;4:114–122. [Google Scholar]
  • 16.Levett PN, Branch SL, Whittington CU, Edwards CN, Paxton H. Two methods for rapid serological diagnosis of acute leptospirosis. Clin Diagn Lab Immunol. 2001;8:349–351. doi: 10.1128/CDLI.8.2.349-351.2001. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 17.Bajani MD, Ashford DA, Bragg SL, Woods CW, Aye T, Spiegel RA, Plikaytis BD, Perkins BA, Phelan M, Levett PN, Weyant RS. Evaluation of four commercially available rapid serologic tests for diagnosis of leptospirosis. J Clin Microbiol. 2003;41:803–809. doi: 10.1128/JCM.41.2.803-809.2003. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 18.Rothman KJ, Greenland S. Modern Epidemiology. Philadelphia, PA: Lippincott-Raven; 1998. [Google Scholar]
  • 19.de Mutsert R, Jager KJ, Zoccali C, Dekker FW. The effect of joint exposures: examining the presence of interaction. Kidney Int. 2009;75:677–681. doi: 10.1038/ki.2008.645. [DOI] [PubMed] [Google Scholar]
  • 20.Everard CO, Bennett S, Edwards CN, Nicholson GD, Hassell TA, Carrington DG, Everard JD. An investigation of some risk factors for severe leptospirosis on Barbados. J Trop Med Hyg. 1992;95:13–22. [PubMed] [Google Scholar]
  • 21.Everard CO, Maude GH, Hayes RJ. Leptospiral infection: a household serosurvey in urban and rural communities in Barbados and Trinidad. Ann Trop Med Parasitol. 1990;84:255–266. doi: 10.1080/00034983.1990.11812465. [DOI] [PubMed] [Google Scholar]
  • 22.Everard CO, Hayes RJ, Fraser-Chanpong GM. A serosurvey for leptospirosis in Trinidad among urban and rural dwellers and persons occupationally at risk. Trans R Soc Trop Med Hyg. 1985;79:96–105. doi: 10.1016/0035-9203(85)90246-9. [DOI] [PubMed] [Google Scholar]
  • 23.Grant GH, Smith G, Schloss W. Seroprevalence of leptospiral antibodies in the Jamaican livestock population. Vet Rec. 1988;122:419–420. doi: 10.1136/vr.122.17.419. [DOI] [PubMed] [Google Scholar]
  • 24.Adler B, Faine S. The antibodies involved in the human immune response to leptospiral infection. J Med Microbiol. 1978;11:387–400. doi: 10.1099/00222615-11-4-387. [DOI] [PubMed] [Google Scholar]
  • 25.Lupidi R, Cinco M, Balanzin D, Delprete E, Varaldo PE. Serological follow-up of patients involved in a localized outbreak of leptospirosis. J Clin Microbiol. 1991;29:805–809. doi: 10.1128/jcm.29.4.805-809.1991. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 26.Silva MV, Camargo ED, Batista L, Vaz AJ, Brandao AP, Nakamura PM, Negrao JM. Behaviour of specific IgM, IgG and IgA class antibodies in human leptospirosis during the acute phase of the disease and during convalescence. J Trop Med Hyg. 1995;98:268–272. [PubMed] [Google Scholar]
  • 27.Winslow WE, Merry DJ, Pirc ML, Devine PL. Evaluation of a commercial enzyme-linked immunosorbent assay for detection of immunoglobulin M antibody in diagnosis of human leptospiral infection. J Clin Microbiol. 1997;35:1938–1942. doi: 10.1128/jcm.35.8.1938-1942.1997. [DOI] [PMC free article] [PubMed] [Google Scholar]

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