| Literature DB >> 25532828 |
Dennis Muhanguzi1,2, Kim Picozzi3, Jan Hattendorf4,5, Michael Thrusfield6, John David Kabasa7, Charles Waiswa8, Susan Christina Welburn9.
Abstract
BACKGROUND: African animal trypanosomiasis (AAT) is considered to be one of the greatest constraints to livestock production and livestock-crop integration in most African countries. South-eastern Uganda has suffered for more than two decades from outbreaks of zoonotic Human African Trypanosomiasis (HAT), adding to the burden faced by communities from AAT. There is insufficient AAT and HAT data available (in the animal reservoir) to guide and prioritize AAT control programs that has been generated using contemporary, sensitive and specific molecular techniques. This study was undertaken to evaluate the burden that AAT presents to the small-scale cattle production systems in south-eastern Uganda.Entities:
Mesh:
Substances:
Year: 2014 PMID: 25532828 PMCID: PMC4300167 DOI: 10.1186/s13071-014-0603-6
Source DB: PubMed Journal: Parasit Vectors ISSN: 1756-3305 Impact factor: 3.876
Description of the animal population
|
|
| |
|---|---|---|
|
|
| |
|
| ||
| 0-12 months | 1205 | 19.9 |
| 13-24months | 1264 | 20.9 |
| 25-36months | 953 | 15.7 |
| >36 months | 2632 | 43.5 |
|
| ||
| Female | 3117 | 51.5 |
| Male | 2568 | 42.4 |
| Neutered | 369 | 6.1 |
|
| ||
| Boran × short horn Zebu cross | 5869 | 96.9 |
| Boran × Holstein Friesian cross | 89 | 1.5 |
| African short horn Zebu (Nkedi) | 96 | 1.6 |
Prevalence of different trypanosome species in Tororo district (September- November 2011)
|
|
|
|
|
|
|
|---|---|---|---|---|---|
| Overall | 928/6048 | 15.3 (12.2-19.1) | - | 91 | 0.11 |
|
| 813/6053 | 13.4 (10.6-16.8) | 17.4 | 91 | 0.09 |
|
| 127/6049 | 2.1 (1.4-3.1) | 2.3 | 53 | 0.04 |
|
| 69/6050 | 1.1 (0.7-1.8) | 1.2 | 35 | 0.02 |
|
| 2/6050 | 0.03 (0.0-0.1) | 0.03 | 04 | 0.00 |
Adjusted for intra cluster correlation using generalised estimating equation (GEE) model.
bRogan-Gladon estimator assuming 100% specificity and sensitivities of 77.4%, 90.9%, 95%, 95% for T.vivax, T. c. savannah, T. b. brucei and T. b. rhodesiense [32], respectively.
cDue to the local farming systems, all animals within a certain village are considered as a herd.
dIntra cluster correlation coefficient or rate of homogeneity (rho).
Herd level prevalence of different trypanosome species in Tororo district
|
|
|
|
|
|
|
|
|---|---|---|---|---|---|---|
| Adumai | 124 | 0.8 | 0.8 | 0.0 | 0.0 | 0.0 |
| Akadoti | 60 | 20.0 | 16.7 | 3.3 | 0.0 | 0.0 |
| Alupe_A | 66 | 1.5 | 1.5 | 0.0 | 0.0 | 0.0 |
| Alupe_B | 60 | 36.7 | 35.0 | 0.0 | 3.3 | 0.0 |
| Agolol | 163 | 8.6 | 8.6 | 0.0 | 0.0 | 0.0 |
| Asinge-C | 232 | 0.4 | 0.4 | 0.0 | 0.0 | 0.0 |
| Atapara-Kaleu | 160 | 20.6 | 18.1 | 1.9 | 1.2 | 0.0 |
| Biranga-B | 82 | 1.2 | 1.2 | 0.0 | 0.0 | 0.0 |
| Biranga-A | 20 | 35.0 | 25.0 | 10.0 | 5.0 | 0.0 |
| Chawolo_ A | 213 | 11.7 | 11.7 | 0.0 | 0.0 | 0.0 |
| Chawolo_B | 188 | 15.4 | 11.7 | 2.7 | 1.6 | 0.5 |
| Dida | 100 | 33.3 | 34.0 | 1.0 | 3.1 | 0.0 |
| East-Central | 56 | 26.8 | 25.0 | 1.8 | 0.0 | 0.0 |
| Iyopoki | 86 | 1.2 | 1.2 | 0.0 | 0.0 | 0.0 |
| Iyoriang | 118 | 11.9 | 11.0 | 0.0 | 1.7 | 0.0 |
| Kadanya | 132 | 3.8 | 3.8 | 0.0 | 0.0 | 0.8 |
| Kajalau | 64 | 28.1 | 21.9 | 7.8 | 3.1 | 0.0 |
| Kasoli | 197 | 19.8 | 19.8 | 0.0 | 0.0 | 0.0 |
| Katandi | 106 | 13.2 | 12.3 | 0.9 | 0.0 | 0.0 |
| Kateki | 69 | 4.3 | 4.3 | 0.0 | 0.0 | 0.0 |
| Kirewa | 132 | 22.7 | 22.7 | 0.8 | 7.6 | 0.0 |
| Kisera | 101 | 5.9 | 5.9 | 0.0 | 0.0 | 0.0 |
| Kogala | 127 | 3.1 | 2.4 | 0.8 | 0.0 | 0.0 |
| Komolo | 112 | 0.0 | 0.0 | 0.0 | 0.0 | 0.0 |
| Macharimeri | 180 | 38.9 | 36.7 | 2.8 | 4.4 | 0.0 |
| Mailombili | 50 | 20.0 | 16.0 | 4.0 | 0.0 | 0.0 |
| Maliri | 71 | 22.5 | 15.5 | 2.8 | 4.2 | 0.0 |
| Mella | 144 | 0.7 | 0.7 | 0.0 | 0.0 | 0.0 |
| Mikwana | 169 | 21.3 | 19.5 | 5.3 | 0.0 | 0.0 |
| Munyinyi | 164 | 33.7 | 26.4 | 8.5 | 3.0 | 0.0 |
| Mwelo | 36 | 38.9 | 36.1 | 11.1 | 0.0 | 0.0 |
| Ngeta-A | 127 | 18.9 | 18.1 | 0.8 | 0.0 | 0.0 |
| Nyabanja | 139 | 30.9 | 23.0 | 9.4 | 2.9 | 0.0 |
| Nyafumba | 94 | 18.1 | 16.0 | 2.1 | 0.0 | 0.0 |
| Nyemera | 88 | 11.4 | 10.2 | 1.1 | 1.1 | 0.0 |
| Okwira | 18 | 33.3 | 33.3 | 0.0 | 0.0 | 0.0 |
| Opule | 72 | 9.7 | 9.7 | 0.0 | 0.0 | 0.0 |
| Oriyoyi | 124 | 26.6 | 26.6 | 0.0 | 0.0 | 0.0 |
| Osia | 112 | 0.0 | 0.0 | 0.0 | 0.0 | 0.0 |
| Pabasi | 110 | 2.7 | 2.7 | 0.0 | 0.0 | 0.0 |
| Pabendo | 76 | 28.9 | 26.3 | 3.9 | 0.0 | 0.0 |
| Pamaraka | 80 | 18.8 | 11.2 | 8.8 | 0.0 | 0.0 |
| Panyandere | 74 | 1.4 | 1.4 | 0.0 | 0.0 | 0.0 |
| Pasaya | 104 | 21.4 | 16.3 | 7.8 | 0.0 | 0.0 |
| Pawira | 215 | 5.1 | 2.8 | 1.4 | 0.9 | 0.0 |
| Poti | 78 | 6.4 | 6.4 | 0.0 | 0.0 | 0.0 |
| Rubuleri | 91 | 31.9 | 29.7 | 6.6 | 4.4 | 0.0 |
| Rukuli | 32 | 9.4 | 9.4 | 0.0 | 0.0 | 0.0 |
| Segero | 100 | 20.0 | 17.0 | 3.0 | 2.0 | 0.0 |
| Seseme | 52 | 28.8 | 25.0 | 0.0 | 7.7 | 0.0 |
| Sesera | 49 | 42.9 | 24.5 | 18.4 | 4.1 | 0.0 |
| Singisi | 76 | 26.3 | 17.1 | 10.5 | 0.0 | 0.0 |
| Ticaf | 204 | 0.0 | 0.0 | 0.0 | 0.0 | 0.0 |
| Totokidwe | 144 | 25.7 | 24.3 | 1.4 | 2.1 | 0.0 |
| Tuba | 90 | 0.0 | 0.0 | 0.0 | 0.0 | 0.0 |
| Wakasiki | 119 | 29.4 | 22.7 | 2.5 | 5.0 | 0.0 |
| West-Central | 4 | 0.0 | 0.0 | 0.0 | 0.0 | 0.0 |
Figure 1Prevalence of in cattle in 57 villages of Tororo District, Uganda. T.brucei s.l. prevalence was categorized into five classes for which symbols differ in size and colour. County boundaries were included for ease of assessment of the location of sample sites within the district. The estimated number of cases per 100 animals is presented within the symbols. Only names of villages with the highest prevalence estimates are added.
Figure 2Spatial distribution of bovine trypanosome species and land cover. The overall prevalence of different trypanosome species in each village was categorized into five classes for which symbols differ in size and colour. County boundaries were included for ease of assessment of the location of sample sites within the district. The estimated number of cattle infected with different trypanosome species per 100 animals are presented within the symbols. Only name labels of villages with the highest prevalence estimates were added to avoid overcrowding the map. A background layer of land cover classes (GLC2000) was added to assess the likely effect of land use on trypanosome prevalence.