Abstract
Babesia spp. were detected from 4 asymptomatic pukus captured on a game ranch in central Zambia in October 2008. Blood smears were examined in 4 species of aymptomatic free-ranging antelopes, namely the puku (Kobus vordanii), reedbuck (Redunca arundinum), bushbuck (Tragelaphus sylvaticus), and kudu (Tragelaphus strepsiceros), and showed the presence of Babesia parasites only in the puku. In the puku, the prevalence of babesiosis was estimated at 33.3% (n=12), while the overall prevalence in all examined animals was 8.5% (n=47). The parasites showed morphological characteristics of paired ring-like stages with the length varying between 1.61 µm and 3.02 µm (mean=2.12 µm, n=27; SD=0.76 µm). Both the infected and non-infected pukus showed good body condition scores (BCS), while the dominant tick species detected from all animals were Rhipicephalus appendiculatus, Rhipicephalus spp., and Boophilus spp. To our knowledge this is the first report of Babesia spp. infection in pukus in Zambia. These findings suggest that wildlife could play an important role in the epidemiology of babesiosis in Zambia.
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Key words: Babesia sp., prevalence, puku, antelope, Zambia
Pukus (
Kobus vardoni) are small to medium-sized antelopes belonging to the subfamily Reduncinae under the family Bovidae [
1]. They are about 80 cm tall and weigh between 62-74 kg with an average weight of 68 kg. They are generally between 1.5-1.7 m long while the horn length for the males averages 54 cm. Pukus used to occupy large areas of open savannah in south-central Africa. Now the population has declined to near threatened species with largest populations being present in Tanzania and Zambia, while numbers in Malawi, Botswana, Democratic Republic of Congo, and Angola have declined tremendously [
2-
7]. Unlike lechwes (
Kobus leche) which are semi-aquatic, pukus utilize moist savannah and floodplain as well as narrow stretches of grasslands lying between water sources and woodland areas [
1,
5].
As a result of the population declining, there has been a deliberate shift in policy to promote ex-situ conservation of this species with approximately 42 game ranches keeping pukus in Zambia. However, one of the greatest constraints to the expansion of ex-situ conservation is the introduction of wildlife into territories endemic with livestock diseases that have the potential to cause clinical diseases in susceptible wildlife species. In Zambia, tick-borne diseases are one of the greatest challenges to livestock production [
8], which has led most cattle ranchers to switch to game ranching. Although it is generally perceived that wildlife are resistant to tick-borne diseases, risk factors emanating from transmission of wildlife diseases to livestock are often overestimated. On the other hand, it is important to determine the impact of diseases of livestock origin on wildlife introduced in areas previously occupied by livestock. This would provide more effective advice to ranchers who are switching from cattle to game ranching. Hence, in the present study, we examined different antelope species on a game ranch that used to be a cattle ranch for the presence of ticks and tick-borne infections, in particular, babesiosis.
The study was carried out in October 2008 in central Zambia on a game ranch which used to be a cattle ranch 12 years prior to this study. The game ranch is endowed with several antelope species. As shown in
Table 1, 4 animal species captured for translocation were used in the study. At capture, animals were immobilized using M99 (etorphine hydrochloride, Norvatis, Johannesburg, South Africa). The body condition score (BSC) for each animal was determined by physical inspection. Emaciated animals with little muscle and no fat deposits on body surfaces with the skin of the neck falling slowly or staying longer in a fold after the pliability test were scored as poor (-). Moderately fat animals with the skin of the neck falling moderately faster than those of the poor BCS were scored fair (+) while animals with a lot of fat with the skin falling faster to its original state after the pliability test were scored as good (++).
Blood smears were made by puncturing the ear vein soon after immobilization. Ticks were collected and stored in 70% alcohol for identification. Once all samples had been collected and BCSs determined, animals were revived using M5050 revivon (dreprenorphine, Norvatis, Johannesburg, South Africa). At the School of Veterinary Medicine, which is based at University of Zambia, slides were stained using Giemsa stain and were examined for the presence of blood parasites under a light microscope. The observed blood parasites were identified as
Babesia spp. based on morphological characteristics (
Fig. 1) [
9]. As pointed out by others [
10,
11] that the presence of pairs or tetrads also known as 'Maltese cross' in stained erythrocytes is diagnostic for babesiosis, we detected the presence of pairs of ring-like
Babesia organisms as shown in
Fig. 1, although other growth stages were also seen. The length of the parasites varied between 1.61 µm and 3.02 µm with an average of 2.12 µm (n=27; SD=0.76 µm). Similarly, ticks were identified using standard keys as described elsewhere [
9]. Body condition scores are shown in
Table 1.
Babesia parasites were detected only in 4 pukus (
Table 1) giving a species prevalence of 33.3% (n=12), while the overall prevalence for all examined animals was 8.5% (n=47).
To our knowledge this is the first report of
Babesia spp. infection in pukus in Zambia. Although the infection was detected only in pukus (
Table 1), we could not rule out the possibility of other animals being infected because we did not use other diagnostic tests, such as molecular biology based tools that are more sensitive to detect the presence of parasites in animals that had low infection rates not easy to detect on blood smears. On the other hand, use of serological assays, such as ELISA or indirect flourescent antibody tests (IFAT), could have been used to determine the seroprevalence of animals previously exposed to the disease but not having active infections at the time of sampling. Suffice to mention that experimental studies have shown differences in susceptibility to different
Babesia spp. within the Bovidae family. For example, Karbe et al. [
12] showed that 2 elands (
Taurotragus oryx) inoculated with
Babesia bigemina obtained from infected cattle did not express the parasite in their blood, and the parasite was not detected after splenectomizing 1 of the animals. In another experiment, Karbe et al. [
12] established a carrier state in African buffaloes (
Syncerus caffer) injected with
B. bigemina obtained from cattle. Hence, it is likely that the absence of
Babesia organisms in other animal species (
Table 1) was indicative of that these animals were not susceptible to the
Babesia spp. detected in the puku. However, there is need for more detailed studies to verify these assertions.
Given that BCSs obtained in
Table 1 were good for both the infected and non-infected pukus, these findings suggest that
Babesia parasites in pukus did not cause clinical diseases, although we did not carry out hematological tests to determine whether these parasites caused changes in blood parameters of the infected animals. Consistent with our observations, Penzhorn [
13] suggested that the occurrence of
Babesia parasites in wildlife is often an incidental finding and that affected animals do not often present clinical diseases. Observation made by several scientists show that clinical babesiosis in wildlife is often stress-related leading to mortality in some cases [
13-
17]. For example, Martinaglia [
15] reported clinical babesiosis in a sable antelope (
Hippotragus niger) that was translocated to a zoo in South Africa. The animal died of stress-related babesiosis due to adaptation to the new environment in the zoo. Similarly, babesiosis-related mortalities caused by stress of translocation have been reported in Black rhinoceros (
Diceros bicornis) in Kenya and Tanzania [
14,
16].
Although we report here the first case of
Babesia infection in pukus in Zambia,
Babesia bovis and
B. bigemina have been reported to cause red-water disease in cattle for a long time in Zambia [
8,
18,
19]. As pointed out by Jongeian et al. [
19], the epidemiology of babesiosis in cattle in Zambia is highly influenced by the distribution and life cycle of the vector ticks. It is likely that these ticks have a similar influence on the occurrence and seasonal variations of
Babesia infections in wildlife. It is interesting to note that the first report of
B. bovis, a species infecting bovids, was first reported from central Zambia [
18] in the same area where the present finding of
Babesia spp. in the puku was detected. Given that various tick species involved in the transmission of
Babesia parasites have been present in the area for a long time, it is likely that these tick-borne diseases have been endemic in this area for a long time. Hence, introducing wildlife in such ecosystems exposes wild animals to tick-borne infections. However, there is need to develop molecular biologic tools for characterizing different
Babesia parasites infecting wildlife and to develop a trace back system for monitoring the transmission dynamics of
Babesia infections between cattle and wildlife in Zambia. Future studies should determine the role of wildlife in the persistence of babesiosis in Zambia.
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Fig. 1Pairs of Babesia parasites (ring-like organisms) in the erythrocytes of a puku designated as A, while B shows Babesia parasites at different stages of the growth cycle.
Table 1.Animal species examined for the presence of blood parasites
Table 1.
|
Animal species |
No. of animals examined |
No. of animals infected with Babesia spp. |
Body condition score (BCS) |
Tick species (No. of animals infested) |
|
Puku (Kobus vardonii) |
12 |
4 |
Good (++) |
12 |
Rhipecephalus appendiculatus (9) |
|
|
Fair (+) |
0 |
Rhipecephalus evertsi (9) |
|
|
Poor (-) |
0 |
Rhipecephalus spp. (10) |
|
|
|
|
Boophilus decoralatus (8) |
|
|
|
|
Boophilus species (10) |
|
Reedbuck (Redunca arundinum) |
14 |
0 |
Good (++) |
10 |
Rhipecephalus appendiculatus (14) |
|
|
Fair (+) |
3 |
Rhipecephalus spp. (8) |
|
|
Poor (-) |
1 |
|
|
Bushbuck (Tragelaphus sylvaticus) |
13 |
0 |
Good (++) |
12 |
Rhipecephalus appendiculatus (10) |
|
|
Fair (+) |
1 |
Rhipecephalus evertsi (8) |
|
|
Poor (-) |
0 |
Rhipecephalus spp. (8) |
|
|
|
|
Boophilus decoralatus (9) |
|
|
|
|
Hyaloma spp. (3) |
|
Kudu (Tragelaphus strepsiceros) |
8 |
0 |
Good (++) |
5 |
Rhipecephalus appendiculatus (5) |
|
|
Fair (+) |
3 |
Rhipecephalus evertsi (4) |
|
|
Poor (-) |
0 |
Rhipecephalus spp. (8) |
|
|
|
|
Boophilus decoralatus (4) |
|
|
|
|
Boophilus species (7) |
|
|
|
|
Amblyomma variegatum (3) |
|
Total |
47 |
4 |
|
|
|
Citations
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