Figures
Abstract
Objectives
We aimed to determine the environmental sources of C. neoformans and C. gattii species complexes in Uganda.
Methods
One hundred fifty (n = 150) environmental specimens of chicken droppings, marabou stork bird droppings and eucalyptus tree barks in Uganda were examined phenotypically. The specimens were grown on Sabouraud dextrose agar and the colonies examined by India ink microscopy, urea hydrolysis and formation of blue colonies on chromogenic L-Canavanine glycine blue bromothymol blue agar of C. gattii species complex
Results
The prevalence of C. neoformans species complex was 4% (6/150). Of the positive environmental samples from which C. neoformans species complex were isolated; the predominant source was marabou stork droppings; 8% (2/25) followed by eucalyptus tree barks; 3.96% (4/101). However, there was no Cryptococcus gattii species complex; 0% (0/150).
Citation: Achan B, Wembabazi A, Luggya T, Ebwongu IR, Musinguzi B, Itabangi H, et al. (2025) Environmental sources of Cryptococcus neoformans species complex in Kampala, Uganda: A preliminary study. PLoS One 20(8): e0329947. https://doi.org/10.1371/journal.pone.0329947
Editor: Felix Bongomin, Gulu University, UGANDA
Received: January 27, 2025; Accepted: July 23, 2025; Published: August 18, 2025
Copyright: © 2025 Achan et al. This is an open access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Data Availability: All relevant data are within the manuscript and its Supporting Information Microsoft Excel files which has two tabs.
Funding: This project is part of the EDCTP2 programme supported by the European Union (grant number: TMA2018CDF-2371), NURTURE/NIH Fogarty International Training grant number D43TW01032 and, Uganda Government’s Makerere University Research and Innovation Fund awarded to BA. The funders had no role in the study design, data collection and analysis, decision to publish, or preparation of the manuscript.
Competing interests: The authors have declared that no competing interests exist.
Introduction
Cryptococcus neoformans species complex is the leading cause of fungal attributable mortality in HIV/AIDS [1]. The basidiospores of C. neoformans species complex inhaled from environmental sources such as wood debris and birds’ droppings rarely cause disease in immunocompetent individuals [2]. However, disseminated disease with a predilection for the meninges to cause cryptococcal meningitis (CM) occurs due to abrogation of cell-mediated immunity following depletion of CD4 + T cells (< 100/mL) [3]. CM is usually the first AIDS-defining illness in HIV infection [3]. The annual global burden of CM is estimated at 152,000 incident cases which results in 112, 000 cryptococcal-related of which 70% occur in Sub-Saharan Africa AIDS [1]. CM is so highly fatal that even with ART and antifungal therapy, the 6-month survival remains ≤ 40% in routine care [4,5].
Two closely related opportunistic yeasts; Cryptococcus neoformans and C. gattii species complexes cause CM [6]. The two Cryptococcus species complexes are basidiomycetous encapsulated yeast species which are likely inhaled from the environment However, the two closely related species complexes differ in ecology and geographic distribution [7].
C. neoformans species complex which causes CM in immunocompromised individuals, for example, in patients with cancer, solid organ transplant, and HIV/AIDS is the most prevalent and globally distributed [8,9]. C. neoformans species complex is ubiquitous in the environment, where it is usually associated with avian droppings [10]. The sibling species Cryptococcus gattii species complex, which induces cryptococcal meningitis more often than C. neoformans species complex in immunocompetent patients, has traditionally shown a geographic restriction to tropical and subtropical regions [11,12] and [13–16]. C. gattii species complex is often associated with the red gum trees; Eucalyptus species (Eucalyptus camaldulensis) [17–19]. More than 50 tree species have yielded C. gattii species complex [20], especially, in Egypt and Tunisia [21,22], Cassia tree in Kenya [10] and Almond tree in Tunisia [22]. In Zambia, environmental sampling identified C. neoformans species complex from Zambezi Mopane woodlands and C. gattii species complex primarily recovered from Central Miombo woodlands [23]. Since these fungi are acquired from nature, environmental sampling is key to understanding their ecological niches. However, the source of Cryptococcus in nature has not yet been identified in Uganda. Therefore, we aimed to screen C. neoformans and C. gattii species complexes environmental isolates from Eucalyptus tree barks, Marabou stork bird droppings and domestic chicken droppings in Kampala, Uganda.
Materials and methods
Sample type
Environmental samples which were obtained from chicken droppings, marabou stork bird droppings and Eucalyptus tree barks in Kampala Metropolitan area were processed at the Clinical Microbiology, and Mycology laboratories of Makerere University College of Health Sciences, Kampala, Uganda.
Sample size
One hundred fifty (n = 150) environmental samples were obtained from chicken droppings, Marabou stork bird droppings and Eucalyptus tree barks in Kampala metropolitan area, Uganda (S1 Data). A positive control for C. neoformans species complex was included. The origin of the positive C. neoformans species control used was a patient’s cerebrospinal fluid which was identified through phenotypic-based positive India ink stain, growth of cream mucoid colonies on Sabouraud Dextrose agar and positive urease hydrolysis. A previous study in Uganda showed that 99% of C. neoformans isolates are urease positive [24]. However; we did not have a positive control for C. gattii species complex.
Sampling technique
Sampling was performed by swabs of bird, marabou stork droppings and at the under surfaces of tree barks or sites not directly exposed to the sunlight. For each sample; two swabs were collected until the sample size of 150 environmental samples was achieved. The samples were collected from chicken droppings, marabou stork bird droppings and eucalyptus tree barks in Kampala metropolitan area, Uganda.
Laboratory procedures
Sample collection and transport.
Environmental samples were collected from chicken droppings, marabou stork bird droppings and Eucalyptus tree barks in Kampala metropolitan area, Uganda, using sterile moist cotton swabs. The swabs were transported in amies transport medium to the testing laboratory within 24 hours.
Culture and identification.
Each swab was streaked onto Sabouraud Dextrose Agar plate and cultured at 37o. After 48 hours, the first grown colonies were analysed phenotypically while the plates without colonies were incubated and examined regularly up to 4 weeks. Firstly, the colonies were stained with India Ink and examined under x40 objective for the presence of the polysaccharide capsule then streaked onto urea agar and incubated for 48 hours to observe the pink colour of urease positive isolates of C. neoformans and C. gattii species complexes. Lastly, urease positive pure colonies were streaked on CGB agar which is a differential medium with bromothymol blue indicator which is used to identify C. gattii that form blue colonies. CGB agar plate preparation was done as described here [19].
Ethical consideration.
Ethical approval was sought from the Makerere University College of Health Sciences’ School of Biomedical Sciences’ Higher Degrees’ Research and Ethics Committee (SBS 639) and the Uganda National Council for Science and Technology (HS1127ES) to carry out the study in Uganda.
Quality assurance.
Standard procedures were followed while preparing the reagents and media (agar) and performing the experiments. Their accuracy was double-checked by performing quality control. The research assistants underwent a basic laboratory training before the start of the study. All activities were under the supervision of the Principal Investigator.
Results
In this study, 150 environmental samples from different sites within Kampala Metropolitan area were analysed for Cryptococcus strains. A positive control for C. neoformans species complex was included; however, we did not have a positive control for C. gattii species complex. The samples included swabs from 24 chicken droppings, 25 Marabou stork droppings and 101 eucalyptus tree bark swabs (Table 1). Of the N = 150 specimens, 4% (6/150) isolates (0 Chicken, 2 Marabou stork and 4 eucalyptus tree barks) were India ink and urease test positive and thus, confirmed as C. neoformans species complex (Tables 2 and 3, Fig 1). However, all the isolates were negative on CGB agar which suggests that no C. gattii species complex was present (Table 3).
The GPS locations of Kampala metropolitan areas where samples of eucalyptus tree bark, marabou stork and chicken droppings were collected are shown in the map of Uganda. The inset of Kampala metropolitan areas within the map of Uganda is marked with a square and an arrow used to show the display.
Discussion
This study reports the environmental screening report for Cryptococcus species in Uganda where 70% of all meningitis cases especially in immunocompromised patients are due to cryptococcal meningitis [2]. We found 4% (150) environmental prevalence of C. neoformans species complex, however, no C. gattii species complex was isolated. This suggests that there was no C. gattii species complex in the sampled specimens in Uganda’s environment. Our finding is in consistence with our previous publication in which we demonstrated C. neoformans species complex infections but no C. gattii species complex infections among Ugandan HIV-infected patients presenting with cryptococcal meningitis [24]. C. neoformans species complex were predominantly identified in marabou stork droppings at 8% (2/25) followed by eucalyptus tree barks; 3.96% (4/101) similar to other environmental studies reported in the nearby Kenya [10]. However, no C. neoformans species complex was isolated from chicken droppings.
C. gattii species complex is traditionally associated with the red gum trees, Eucalyptus species [19,22], and has shown a geographic restriction to tropical and subtropical regions, however, in this study, none was identified from the samples analyzed. Several other studies have reported environmental presence of C. neoformans/C. gattii species complexes globally [11,19,22].
In this study, samples were analyzed phenotypically as described above in the culture and identification section because of the limited resources within the scope of this study. However, recent studies have employed genetic and molecular means in determining genotypic diversity of C. neoformans/C. gattii species complexes [5,18,25] which would give a better accuracy of identification.
This study highlights the isolation of C. neoformans species complex from eucalyptus tree barks and marabou stork droppings. Eucalyptus tree species grow across the whole country in both cooler and hotter areas and are choice for many commercial farmers because it is multipurpose, fast-growing and has a ready market. This followed decimation of natural forests and woodlands across Africa which could no longer keep pace with the required demand for forest cover, energy usage, timber and construction work associated urbanization [26]. Marabou storks are common in urban areas especially around the garbage collection sites and markets due to their vulturous nature of diet. The finding of the urban ecological niches of C. neoformans species complex in this study is in agreement with the previous study which showed that up to 93.5% (n = 200) of the Infectious Diseases Institute’s recruited patients with AIDS-associated cryptococcal meningitis were from Uganda’s central region the capital city; Kampala, is located [24]. Furthermore, the previous clinical study showed that 45% of the patients with cryptococcal meningitis were in the age category 30–39 years old [24], which represents the most physically productive age group that would be involved with urban economic activities such as building using timber from eucalyptus tree. This calls for safety measures when dealing with Marabou stork and farmers/ individuals who work in eucalyptus tree plantations.
However, there could be many more undocumented environmental reservoirs of C. neoformans species complex/C. gattii species close to or within human habitation which might be a significant exposure risk factor for the high prevalence of cryptococcal meningitis especially among the immunocompromised patients in Uganda.
Study limitations and strengths
Limitations of the study include the small sample size, limited geographical coverage of sample collection sites and use of phenotypic assays. A significant strength of the study is that this is the first report of environmental presence of Cryptococcus neoformans species complex in Uganda.
Conclusion
The prevalence of C. neoformans species complex in Uganda’s environment is 4%, predominantly, in marabou stork droppings. However, there seems to be no species belonging to the C. gattii species complex in our pool of samples. We recommend further genetic and molecular studies on a larger number of isolates from increased numbers of different environmental specimens which may unearth the distribution of the of a C. neoformans and C. gattii species complexes in Uganda.
Supporting information
S1 Data.
Environmental specimen types that were collected.
https://doi.org/10.1371/journal.pone.0329947.s001
(XLSX)
Acknowledgments
We would like to thank the staff and management of Clinical Microbiology laboratory, Department of Medical Microbiology, College of Health Sciences, Makerere University for their support, permission and assistance in samples collection and laboratory work. We thank Luwum Innocent for administrative support.
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