Background: Understanding the epidemiological distribution of legionellosis across demographic groups, exposure histories, and temporal patterns is essential for targeted public health interventions.
Methods: We conducted a descriptive epidemiological analysis of 224 confirmed Legionnaires’ disease and Pontiac fever cases reported between 2020 and 2024. Case distributions were examined by demographics, symptoms, and 35 potential exposure variables. Time series analysis assessed seasonality and trends using lab collection date as a proxy for disease onset.
Results: Cases were predominantly male (70.5%) and aged 50-74 years (65.6%). The most prevalent symptoms were fatigue (92.2%), fever (87.4%), and cough (86.6%). Among exposures with adequate response rates, the top five were: national travel (24.1%), showering away from home (23.6%), out-of-county travel (19.3%), clinic/dentist visits (16.5%), and CPAP/BiPAP use (13.0%). Overall, 24.6% of cases reported any travel exposure. Time series analysis revealed significant seasonality (p=0.001), with 53.4% of cases in summer months and peak incidence in June. No significant trend was detected across the 5 years of the study (p=0.888).
Conclusions: This analysis identifies key demographic and exposure risk factors for Legionellosis. Travel-related exposures, particularly domestic travel, represent a significant proportion of cases. The strong summer seasonality aligns with known Legionella ecology. These findings in this data support targeted interventions focusing on travel-associated risks, respiratory equipment users, and enhanced summer surveillance.
Legionella bacteria can cause Legionnaires’ disease and
Pontiac fever, collectively referred to as legionellosis. Legionnaires’
disease is a severe form of pneumonia, typically acquired through
inhalation of contaminated water aerosols. Pontiac Fever is an
inflammatory response to Legionella endotoxin (CDC, 2024).
Understanding the epidemiological distribution of cases—including
demographic characteristics, exposure histories, and temporal
patterns—is essential for developing effective public health
interventions.
Common exposure sources include cooling towers, hot water systems,
whirlpool spas, decorative fountains, and respiratory therapy equipment.
Travel-associated cases represent a recognized risk factor, with
exposure often occurring in hotels, hospitals, or other buildings with
complex water systems (Garrison et al., 2016).
The objectives of this analysis were:
On April 29, 2025, a query for Legionnaires’ disease of EpiTrax, the surveillance management system at the Kansas Department of Health and Environment (KDHE), retrieved a total of 591 records reported during 2020-2024. After deduplication and other data cleaning processes there were 224 records left for this analysis. Most of the remaining records (96%) were labeled Legionnaires’ disease, Pontiac Fever(1 or 0.5%), Other or the label was missing. Each case record included demographic information, clinical symptom data, laboratory collection date, and responses to 35 standardized exposure questions covering healthcare, travel, water/recreation, residential, occupational, and commercial/public exposure categories.
Demographic variables included sex, age category (18-29, 30-49, 50-74, 75+ years), race, and ethnicity. Exposure variables were coded as YES, NO, or UNKNOWN/missing. Travel-related exposures included international travel, national travel, out-of-county travel, and U.S. travel.
Exposures were grouped into six categories: Healthcare/Medical (CPAP, nebulizer, healthcare facilities), Travel (all travel variables), Water/Recreation (pools, spas, water parks), Residential (long-term care, humidifiers, showering away from home), Occupational (construction, plumbing, food service), and Commercial/Public (cooling towers, stores, clinics).
Descriptive statistics included frequencies and percentages for categorical variables. Exposure prevalence was calculated as the proportion of cases reporting YES among those with valid (YES/NO) responses. Response rates were calculated as the proportion of cases with non-missing data.
For identification of top exposure factors, analysis was restricted to variables with response rates ≥30% to ensure adequate data quality. Chi-square goodness-of-fit tests assessed demographic distributions. Mann-Whitney U tests compared prevalence distributions between travel and non-travel exposures.
Time series analysis included seasonal decomposition, Kruskal-Wallis tests for seasonality, Mann-Kendall trend tests, and autocorrelation analysis. Statistical significance was set at α=0.05. All analyses were conducted using R version 4.5.1.
The analysis code and data processing scripts are available upon request to ensure reproducibility of results. GitHub repository: https://github.com/SOK-KDHE/legion_desc_24.git. GitHub Copilot was used to assist in code generation and documentation.
A total of 224 cases were analyzed. Males comprised 70.5% (n=158), with the 50-74 year age group accounting for 65.6% (n=147). White individuals represented 77.7% of cases. Chi-square tests show significant statistical differences among all demographic subgroups considered (all p<0.001).
| Variable | Category | N | % |
|---|---|---|---|
| Sex | Male | 158 | 70.5 |
| Female | 66 | 29.5 | |
| Age (years) | 18-29 | 3 | 1.3 |
| 30-49 | 36 | 16.1 | |
| 50-74 | 147 | 65.6 | |
| 75+ | 38 | 17.0 | |
| Race | Black or African American | 34 | 15.2 |
| Other/Unknown | 16 | 7.1 | |
| White | 174 | 77.7 | |
| Ethnicity | Hispanic or Latino | 10 | 4.5 |
| Not Hispanic or Latino | 201 | 89.7 | |
| Unknown | 13 | 5.8 |
Figure 1. Case distribution by demographic characteristics.
| Variable | Chi-square | df | P-value | Significant |
|---|---|---|---|---|
| Sex | 37.79 | 1 | <0.001 | Yes |
| Race | 620.13 | 5 | <0.001 | Yes |
| Ethnicity | 320.69 | 2 | <0.001 | Yes |
| Age Category | 210.96 | 3 | <0.001 | Yes |
The most common symptoms were fatigue/malaise/weakness (92.2%), fever (87.4%), and cough (86.6%). Chills (64.9%) and headache (61.0%) were moderately prevalent. No significant differences were observed between sexes for any symptom (all p>0.05).
| Symptom | Overall (%) | Male (%) | Female (%) |
|---|---|---|---|
| Fatigue/Malaise/Weakness | 92.2 | 91.1 | 94.2 |
| Fever | 87.4 | 86.8 | 88.7 |
| Cough | 86.6 | 84.1 | 91.5 |
| Chills | 64.9 | 65.0 | 64.6 |
| Headache | 61.0 | 60.7 | 61.5 |
| Diarrhea | 49.7 | 50.8 | 47.8 |
| Abdominal Cramps | 22.9 | 25.6 | 17.9 |
A total of 35 exposure variables were analyzed, with response rates ranging from 4.5% to 75.9%. 28 variables had response rates ≥50%, and 28 variables had response rates ≥30%.
Among exposure variables with adequate response rates (≥30%), the five most prevalent were:
| Exposure | Yes | No | Prevalence | Response Rate |
|---|---|---|---|---|
| National Travel | 41 | 129 | 24.1 | 75.9 |
| Shower Away from Home | 34 | 110 | 23.6 | 64.3 |
| Out-of-County Travel | 32 | 134 | 19.3 | 74.1 |
| Clinic Dentist Visit | 26 | 132 | 16.5 | 70.5 |
| CPAP BiPAP | 21 | 141 | 13.0 | 72.3 |
| Store Mister | 18 | 140 | 11.4 | 70.5 |
| Swimming Pool | 18 | 143 | 11.2 | 71.9 |
| Healthcare Exposure | 18 | 148 | 10.8 | 74.1 |
| Construction Near Home | 14 | 127 | 9.9 | 62.9 |
| Sprinkler | 12 | 131 | 8.4 | 63.8 |
Figure 2. Top 15 exposure factors by prevalence. Red bars indicate travel-related exposures.
Analysis of any exposure within predefined categories revealed that residential exposures (26.3%) had the highest prevalence, followed by travel (32.4%), commercial/public (28.6%), healthcare/medical (24%), water/recreation (19%), and occupational exposures (17.1%).
| Category | Variables | Any Exposure | Valid N | Prevalence (%) |
|---|---|---|---|---|
| Travel | 5 | 59 | 182 | 32.4 |
| Commercial/Public | 5 | 48 | 168 | 28.6 |
| Residential | 5 | 44 | 167 | 26.3 |
| Healthcare/Medical | 6 | 41 | 171 | 24.0 |
| Water/Recreation | 5 | 31 | 163 | 19.0 |
| Occupational | 9 | 26 | 152 | 17.1 |
Figure 4. Exposure rate by category.
Monthly case counts ranged from 0 to 15 cases (mean: 3.7, SD: 3.8). The Kruskal-Wallis test confirmed significant differences across months (χ² = 30.63, p = 0.001) and seasons (χ² = 24.67, p < 0.001). Summer months (June-August) accounted for 53.4% of all cases, with Jun showing the highest seasonal index (+7.88).
| Season | Total Cases | Mean Monthly | SD | % of Total |
|---|---|---|---|---|
| Winter | 23 | 1.53 | 1.25 | 10.3 |
| Spring | 33 | 2.20 | 2.65 | 14.8 |
| Summer | 119 | 7.93 | 4.45 | 53.4 |
| Fall | 48 | 3.20 | 2.31 | 21.5 |
Figure 5. Monthly Legionnaire’s disease cases (2020-2024) with smoothed trend line.
Figure 6. Seasonal indices by month showing deviation from overall mean.
Figure 7. Seasonal patterns by year showing consistent summer peaks.
The Mann-Kendall test showed no significant monotonic trend (Z = 0.14, p = 0.888), indicating stable rate of infection over the study period. Annual case counts ranged from 1 to 51, with no evidence of increasing or decreasing incidence.
This analysis of 224 Legionnaires’ disease cases in Kansas reported from 2020 to 2024 provides insights into demographic patterns, exposure risk factors, and temporal trends. The demographic profile—predominantly male (70.5%) and older adults (65.6% aged 50-74 years)—is consistent with established risk factors (Falagas et al., 2007).
The exposure analysis identified several key findings. First, travel-related exposures were the single most prevalent category, with nearly a quarter (24.6%) of cases reporting domestic or international travel before illness onset. National travel (24.1%) and out-of-county travel (19.3%) were more common than international travel, suggesting that most travel-associated cases involve domestic rather than international exposure.
Second, showering away from home was the second most prevalent type of exposure (23.6%). This is epidemiologically significant because shower heads and hotel water systems are recognized sources of Legionella exposure, particularly in buildings with complex plumbing systems or inadequate water temperature maintenance (US EPA 2025).
Third, respiratory equipment use (CPAP/BiPAP) was reported by 13% of cases. Contaminated water reservoirs in respiratory equipment represent a known risk factor, particularly for individuals with underlying pulmonary conditions (Woo et al. 1992).
The finding that 24.6% of cases reported any travel exposure has important public health implications. Legionnaires’ disease is reportable to the KDHE, and clusters linked to hotels, cruise ships, and other accommodations represent opportunities for intervention. The predominance of travel-associated cases suggests that prevention efforts should focus lodging facilities and an opportunity to collaborate with the Kansas Department of Agriculture which regulates the lodging industry in the state.
The pronounced summer seasonality, with 53.4% of cases occurring June through August, aligns with known Legionella ecology (Hicks et al. 2017). Warmer temperatures promote bacterial growth in water systems, cooling tower use increases during summer, and outdoor water features become more common. The consistent seasonal pattern across all five study years suggests this is a robust finding that should inform the timing of prevention efforts.
Several limitations warrant consideration. First, exposure data were self-reported and subject to recall bias. Second, variable response rates may introduce selection bias for exposures with substantial missing data. Third, the absence of control data precludes calculation of odds ratios or attributable fractions. Finally, the small counts in some categories lead to unstable rates. Therefore, the reader should use caution in interpreting the statistics.
This analysis provides an epidemiological profile of Legionnaires’ disease in Kansas, identifying key demographic, exposure, and temporal patterns. The findings support several actionable recommendations:
Enhanced travel-associated surveillance: Given that a quarter of the cases reported travel, continued vigilance for travel-associated clusters is warranted.
Respiratory equipment education: Patients using CPAP/BiPAP devices should receive guidance on proper cleaning and water reservoir maintenance.
Seasonal preparedness: Enhanced surveillance and cooling tower inspections would be beneficial during May-August.
Targeted outreach: Prevention messaging should focus on high-risk groups (males, older adults, those with respiratory conditions).
Water management: Building owners and facility managers should maintain water management programs, particularly in hotels and healthcare facilities.
CDC. (2024). Legionella (Legionnaires’ Disease and Pontiac Fever). Centers for Disease Control and Prevention.
Garrison, L. E., et al. (2016). Vital Signs: Deficiencies in environmental control identified in outbreaks of Legionnaires’ disease—North America, 2000–2014. MMWR Morb Mortal Wkly Rep, 65(22), 576-584.
Falagas, M. E., Mourtzoukou, E. G., & Vardakas, K. Z. (2007). Sex differences in the incidence and severity of respiratory tract infections. Respiratory Medicine, 101(9), 1845-1863.
Klein, S. L., & Flanagan, K. L. (2016). Sex differences in immune responses. Nature Reviews Immunology, 16(10), 626-638.
U.S. Environmental Protection Agency. (2025, August 27). Legionella in the indoor environment. https://www.epa.gov/indoor-air-quality-iaq/legionella-indoor-environment.
Hicks, L. A., et al. “Weather-Dependent Risk for Legionnaires’ Disease, United States.” Emerging Infectious Diseases, vol. 23, no. 10, Oct. 2017, pp. 1714–16. PubMed Central, https://pmc.ncbi.nlm.nih.gov/articles/PMC5652433/
Woo, A. H., et al. “Transmission of Legionella by Respiratory Equipment and Aerosol-Generating Devices.” Chest, vol. 102, no. 5, 1992, pp. 1586–1590. https://journal.chestnet.org/article/S0012-3692(16)59107-7/abstract
| Exposure | Yes | No | Valid N | Prevalence (%) | Response Rate (%) |
|---|---|---|---|---|---|
| U.S. Travel | 41 | 0 | 41 | 100.0 | 18.3 |
| CPAP Humidifier | 14 | 4 | 18 | 77.8 | 8.0 |
| National Travel | 41 | 129 | 170 | 24.1 | 75.9 |
| Shower Away from Home | 34 | 110 | 144 | 23.6 | 64.3 |
| Out-of-County Travel | 32 | 134 | 166 | 19.3 | 74.1 |
| Clinic Dentist Visit | 26 | 132 | 158 | 16.5 | 70.5 |
| CPAP BiPAP | 21 | 141 | 162 | 13.0 | 72.3 |
| Store Mister | 18 | 140 | 158 | 11.4 | 70.5 |
| Swimming Pool | 18 | 143 | 161 | 11.2 | 71.9 |
| Healthcare Exposure | 18 | 148 | 166 | 10.8 | 74.1 |
| Construction Near Home | 14 | 127 | 141 | 9.9 | 62.9 |
| Sprinkler | 12 | 131 | 143 | 8.4 | 63.8 |
| Clinic Dentist Visit 2 | 2 | 22 | 24 | 8.3 | 10.7 |
| Another Spa Exposure 1 | 1 | 11 | 12 | 8.3 | 5.4 |
| Longterm Care Facility | 13 | 148 | 161 | 8.1 | 71.9 |
| International Travel | 3 | 36 | 39 | 7.7 | 17.4 |
| Hospital Exposure 2 | 1 | 12 | 13 | 7.7 | 5.8 |
| Use Humidifier | 12 | 145 | 157 | 7.6 | 70.1 |
| Spa | 12 | 149 | 161 | 7.5 | 71.9 |
| Work in Construction | 9 | 138 | 147 | 6.1 | 65.6 |
| Building Cooling Tower | 8 | 127 | 135 | 5.9 | 60.3 |
| Other Type of Work | 7 | 141 | 148 | 4.7 | 66.1 |
| Water Feature | 7 | 152 | 159 | 4.4 | 71.0 |
| Convention Reception | 6 | 137 | 143 | 4.2 | 63.8 |
| Nebulizer | 6 | 154 | 160 | 3.8 | 71.4 |
| Work Involves Industrial Spray | 5 | 139 | 144 | 3.5 | 64.3 |
| Plumbing Maintenance Work | 5 | 145 | 150 | 3.3 | 67.0 |
| Work as a Trucker | 4 | 144 | 148 | 2.7 | 66.1 |
| Congragate Living | 3 | 141 | 144 | 2.1 | 64.3 |
| Custodial Work | 2 | 146 | 148 | 1.4 | 66.1 |
| Water Park | 2 | 159 | 161 | 1.2 | 71.9 |
| Waste Water Work | 1 | 146 | 147 | 0.7 | 65.6 |
| Therapy Equipment Humidifier | 0 | 10 | 10 | 0.0 | 4.5 |
| Works in a Kitchen | 0 | 150 | 150 | 0.0 | 67.0 |
| Work in the Leisure Industry | 0 | 149 | 149 | 0.0 | 66.5 |
Report generated on December 17, 2025 at 09:29
R version 4.5.1