Control of bush encroachment in Borana zone of southern Ethiopia: effects of different control techniques on rangeland vegetation and tick populations
© Negasa et al.; licensee Springer. 2014
Received: 28 September 2014
Accepted: 10 October 2014
Published: 25 November 2014
A study on effects of bush encroachment control techniques on rangeland productivity and tick population dynamics was conducted in Arero district of Borana zone, southern Ethiopia, for three consecutive years. The study targeted two main and dominant encroaching bush species in Borana rangeland, Acacia drepanolobium and Acacia mellifera, and their effects on some vegetation attributes and tick population dynamics. A hectare of rangeland encroached by these two acacia species was replicated/divided into three plots, and each plot was subdivided into five sub-plots to receive five treatments: cutting at 0.5 m above ground and pouring kerosene on stumps (T1), cutting at 0.5 m above ground and debarking the stumps down into the soil surface (T2), cutting at 0.5 m above ground alone (T3), cutting at 0.5 m above ground and dissecting the stumps (T4) and control (T5). Data on basal and litter covers, soil erosion and compaction, dead and re-sprouted encroaching tree/shrub species and nymph- and adult-stage tick populations were collected before and after treatment applications. The applied treatments significantly influenced (p < 0.05) basal cover, nymph- and adult-stage tick population and the two encroaching tree species. The results of this study showed that T3 and T2 were good in controlling A. drepanolobium in that order. T4 and T2 had a significant effect in controlling A. mellifera in their order. Controlling bush encroachment had also a positive effect in eradicating the tick population. The most dominant grass and non-grass species observed after the control actions were Cenchrus ciliaris, Chrysopogon aucheri, Abutilon hirtum, Pennisetum mezianum, Dyschoriste hildebrandtii, Zaleya pentandra and Eragrostis papposa. Therefore, controlling encroaching tree/shrub species had created a conducive grazing area with palatable herbaceous species for the livestock and unequivocally reduced tick population which play a role in reducing cattle milk production through closing off teats. The management of bush encroachment, if sustained, will contribute in stabilizing rangelands and help minimize the negative effects of feed and food crises in the future.
Worldwide, rangelands contribute about 70% of the feed needs of domestic ruminants and contribute about 85% of the total feed needs of ruminants in African and South American countries (Holechek et al. ). In Ethiopia, rangelands account for more than 60% of the country's total land mass (Hogg ). Past studies have indicated that Borana rangelands in the southern parts of the country were considered to be one of the best grazing lands (Coppock ). However, these rangelands are experiencing increasing pressure from livestock and human populations, bush encroachment and tick infestation (Ayana ). According to Gemedo et al. ([2006a]), in the Borana rangelands, woody plant cover increased from 50% as reported in the late 1990s by Oba () to 60%. Bushes are transforming open grazing lands into impenetrable thicket-forming noxious trees/shrubs and suppressing desirable grasses and non-grasses through competition, thus becoming unsuitable for browsing and grazing (Tamene ). Acacia species such as Acacia drepanolobium, Acacia reficiens and Acacia mellifera and Commiphora species are identified as the most encroaching species (Oba ). Oba et al. () reported that bush encroachment in the Borana rangelands reduces livestock productivity and survival particularly during drought years, when forage scarcity is the greatest.
Furthermore, livestock production in Borana pastoral communities has been constrained by ticks. Ticks have a great importance in the production of animal diseases. Heavy infestation can cause direct production loses, apart from their role as vectors and potential reservoirs of infectious and often fatal East Coast fever (ECF). A survey of 560 milking cows in Borana in 1989 revealed that 15% of the cows' teats were closed off due to tick damage. This situation exacerbates the pastoralists' potential to secure their household food needs as milk is the predominant food for the pastoralists in the study area.
Therefore, this study was aimed to determine the response of herbaceous and woody vegetation to different bush control techniques and to assess the efficacy of controlling excessive tick loads in the rangelands.
Materials and methods
The study period elapsed between the hot dry season of 2008 and the main rainy season of 2011 in Arero district of Borana zone, southern Ethiopia, which is about 630 km south of the capital Addis Ababa. Land use in the Borana rangelands is largely communal, but crop cultivation and private enclosures appear to be increasing in recent decades (Coppock ). In this extensive communal semi-arid rangeland of Borana, herbaceous plants are the major feed sources of grazers. The area has a bimodal pattern of rainfall, with the long rainy season between March and May and the short rainy season between September and November. Spatial and temporal variability in both the quantity and distribution of rainfall renders the area semi-arid, with an average annual rainfall ranging from 400 mm in the south to 600 mm in the north. The average temperature varies from 13.1°C to 25.2°C per annum (Coppock ). The site is dominated by black clay soils.
A hectare of land encroached by A. drepanolobium and A. mellifera was divided into three plots. Each replication (plot) with an area of 33.33 m by 100 m was divided into five sub-plots, each with 20 m by 33.33 m ready to accommodate five treatments, namely cutting at 0.5 m above ground and pouring kerosene on the stumps T1, cutting at 0.5 m above ground and debarking the stumps down into the soil surface T2, cutting at 0.5 m above ground alone T3, cutting at 0.5 m above ground and dissecting the stumps T4 and no cutting T5.
Data on basal and litter covers, soil erosion and compaction, tick population dynamics and standing A. drepanolobium and A. mellifera were collected before treatment application. Data collections on tick population dynamics, basal and litter covers and soil erosion and compaction were carried out on the third year after treatment application. However, data on dead and re-sprouted A. drepanolobium and A. mellifera were collected on the first year after treatment application. The percentage basal and litter covers and estimated soil erosion and compaction were obtained by randomly throwing five 0.5 m × 0.5 m quadrats within each sub-plot. Tick population was determined by dragging a transect cloth of 3 m × 2 m over the sub-plots, and then ticks attached to the cloth were counted separately according to their growth stage as nymph and adult. Percentage basal and litter covers were estimated using visual assessment in each quadrat. Soil compaction percentage was estimated by assessing the degree of inserting any sharpened materials (sharpened trees were used in this study) into the soil in each quadrat. The assessment of soil erosion was based on the method described by Baars et al. (). The values in percentage given are as follows: no soil movement (0% to 15%), slight sand mulch (16% to 30%), slope-sided pedestals (31% to 45%), steep-sided pedestals (46% to 60%), pavements (61% to 75%) and gullies (76% to 100%).
Data were analysed using SAS (SAS Institute ) software, and Tukey's studentized range (HSD) tests were used for post hoc multiple comparisons of means.
Results and discussion
Response of A. drepanolobium and A. mellifera to treatments
Effects of treatments on different parameters after treatment application
Basal cover (%)
Litter cover (%)
Soil erosion (%)
Soil compaction (%)
Effects of treatments on soil erosion and compaction and on tick population
Mean difference value of parameters between before and after the control actions
Mean differences across treatments
Overall mean difference
Basal cover (%)
Litter cover (%)
Soil erosion (%)
Soil compaction (%)
Number of nymph-stage tick/ha
Number of adult-stage tick/ha
Bush control effects on vegetation structure and basal and litter covers
Overall grass and non-grass species recorded in the study district
Alakuu ajoo (not known)
Mixixiqaa (not known)
Basal cover was significantly increased from 41.8% before the control actions to 57.7 ± 4.1 after the control actions (Tables 1 and 2). The high basal cover in the study area could be associated with reduced soil erosion by 3.3% and reduced encroaching tree species densities which created a conducive environment for recruiting new grass species. Furthermore, canopy gaps created by tree/shrub removal are expected to result in increased herbaceous cover, diversity and abundance due to reduced competition for water and nutrients as well as increased availability of light (Casado et al. ). In line with this finding, Karuaera () found that non-encroached sites had a higher grass cover than the bush-encroached sites.
Litter cover was increased from 22.2% ± 3.7% before the control actions to 30.6% ± 3.8% after the control actions that might be attributed to the increment in basal cover percentage and the newly introduced grasses after the control actions specially Digitaria naghellensis, Sporobolus pellucidus, Bothriochloa insculpta and Heteropogon contortus. These grasses are very important livestock feed resources in the rangeland ecosystem. This finding indicated that grass diversity is negatively correlated with woody plant density which is in accordance with Abule et al. (). The increase in density of woody plants beyond a critical density suppresses herbaceous growth and its production in semi-arid ecosystems (Richter et al. ).
A significant difference (p < 0.05) among treatments was noticed for the mean number of nymph-stage tick population per hectare. Accordingly, nymph-stage tick population per hectare was reduced significantly from 22,666.7 pre-control to 12,222.2 after control actions (Table 1). Likewise, the number of adult-stage tick population per hectare was reduced from 22,666.7 before the control actions to 2,888.9 after the control actions. The highest reduction in number of nymph-stage tick per hectare was noticed for T1 (cutting at 0.5 m above ground and applying kerosene) that reduced by 15,000 ha−1. This might be due to the inability of the nymph-stage ticks to withstand the unpleasant odour of kerosene gas over the plot. The study results suggest that A. mellifera and A. drepanolobium encroachment provides a conducive environment for the survival of ticks which is in line with Bertrand and Wilson () who reported that ticks in open fields suffered higher mortality rates than those in canopied habitats. A previous study by Scott and Jeffrey () found that adult tick density was positively correlated with percent coverage of live Japanese barberry. Adult-stage tick density was increased by 1,111.1 ha−1 after the control actions only in the control plot (T5) probably due to their ability to escape from the plots that were cleared off encroaching trees/shrubs species to the plots that were untouched, i.e. T5 (no treatment application) (Table 1). Overall, the density of nymph- and adult-stage tick population per hectare was decreased by 30% and 18.8%, respectively, due to the control actions. This implies that controlling encroaching tree/shrub species has also contributed in the reduction of tick density which had a negative impact on the milk yield by the livestock species via closing off teats.
Conclusion and recommendation
The study aimed to test controls for bush encroachment, an important factor hampering livestock production and improved living standards of the Borana pastoralist community. The grazing system of the Borana plateau has become increasingly unsuitable in recent decades due to range degradation in the form of woody plant encroachment. The widespread use of different bush control techniques would serve to stabilize forage supply in these semi-arid rangelands by improving overall forage production in drought years. According to our results, T2 and T4 were effective in controlling A. drepanolobium and A. mellifera, respectively. Changes in vegetation structure from thicket-forming bush encroachment to open grasslands have recruited herbaceous biomass and plant biodiversity and reduced the tick population, which has a positive impact on the rangeland ecosystem, livestock production and livelihoods of the pastoral communities. This agrees with studies by Richter et al. (), Briske et al. () and Abule et al. ().
Responses of individual encroaching woody species to the different control methods have important implications for management, conservation policy and public education, which in the future should be promoted through pastoralist participatory research and extension. Controlling encroaching tree/shrub species also contributed in the reduction of tick density which has a negative impact on the milk yield by the livestock species via closing off teats. The management of bush encroachment, if sustained, will contribute in stabilizing rangelands, livestock productivity and pastoralist livelihoods and help minimize the negative effects of feed and food crises in the future.
The authors wish to thank Oromia Agricultural Research Institute-Yabello Pastoral and Dryland Agriculture Research Center for providing financial support and the Animal Feed Resources and Rangeland Management Research Team staff for collecting good-quality data.
- Abule E, Snyman HA, Smit GN: Rangeland evaluation in the Middle Awash valley of Ethiopia: III. Relationships among soil and vegetation variables. Journal of Arid Environments 2007, 70: 293–303. 10.1016/j.jaridenv.2007.01.006View ArticleGoogle Scholar
- Archer S: Development and stability of grass/woody mosaics in a subtropical savanna parkland, Texas, USA. Journal of Biogeography 1990, 17: 453–462. 10.2307/2845377View ArticleGoogle Scholar
- Ayana, A. 2007. The dynamics of savanna ecosystems and management in Borana, southern Ethiopia. A PhD Thesis, Norwegian University of Life Sciences, Noragic. 183 pp.Google Scholar
- Baars RMT, Chileshe EC, Kalokoni DM: Technical notes: Range condition in high cattle density areas in the Western Province of Zambia. Tropical Grasslands 1997, 31: 569–573.Google Scholar
- Becher, H. H. 2003. Estimating soil loss due to erosion by water or wind. Field assessment of soil quality (resources management). Chair of Soil Science, Göttingen.Google Scholar
- Bertrand MR, Wilson ML: Microclimate-dependent survival of unfed adult Ixodes scapularis (Acari:Ixodidae) in nature: Life cycle and study design implications. Journal of Medical Entomology 1996, 33: 619–627.View ArticleGoogle Scholar
- Briske DD, Fuhlendorf SD, Smeins FE: Vegetation dynamics on rangelands: A critique of the current paradigms. Journal of Applied Ecology 2003, 40: 601–614. 10.1046/j.1365-2664.2003.00837.xView ArticleGoogle Scholar
- Casado MA, Castro I, Ramirez-Sanz L, Costa-Tenorio M, de Miguel JM, Pineda FD: Herbaceous plant richness and vegetation cover in Mediterranean grasslands and shrublands. Plant Ecology 2004, 170: 83–91. 10.1023/B:VEGE.0000019021.62054.62View ArticleGoogle Scholar
- Clark DL, Wilson MV: Fire, mowing and hand removal of woody species in restoring a native wetland prairie in the Willamette Valley of Oregon. Wetlands 2001, 21: 135–144. 10.1672/0277-5212(2001)021[0135:FMAHRO]2.0.CO;2View ArticleGoogle Scholar
- Coppock DL: The Borana plateau of southern Ethiopia: Synthesis of pastoral research, development and change, 1980–1991. ILC (International Livestock Center for Africa), Addis Ababa, Ethiopia; 1994.Google Scholar
- Gemedo DT, Brigitte LM, Johannes I: Encroachment of woody plants and its impact on pastoral livestock production in the Borana lowlands, southern Oromia, Ethiopia. East African Wild Life Society, African Journal of Ecology 2006, 44: 237–246. 10.1111/j.1365-2028.2006.00638.xView ArticleGoogle Scholar
- Gemedo DT, Maass BL, Isselstein J: Rangeland condition and trend in the semiarid Borana lowlands, southern Oromia, Ethiopia. African Journal of Range and Forage Science 2006, 23: 49–58. 10.2989/10220110609485886View ArticleGoogle Scholar
- Hogg R: Pastoralists, ethnicity, and the state in Ethiopia. Haan Publishing, London; 1997.Google Scholar
- Holechek JL, Pieper RD, Herbel CH: Range management principles and practices. 5th edition. Pearson Prentice Hall, Upper Saddle River, NJ, USA; 2005.Google Scholar
- Jiang Z, Wang Z, Liu Z: Quantitative study on spatial variation of soil erosion in a small watershed in the loess hilly region. Journal of Soil Erosion and Soil and Water Conservation 1996, 2: 1–9. in Chinese, with English abstract in Chinese, with English abstractGoogle Scholar
- Karuaera, N. A. G. 2011. Assessing the effects of bush encroachment on species abundance, composition and diversity of small mammals at the Neudamm Agricultural Farm, Khomas Region, Namibia. MSc. Thesis, University of Namibia and Humboldt-universitat Zu Berlin, 136 pp.Google Scholar
- Oba G: Effects of wildfire on a semi-desert riparian woodland along the Turkwel River, Kenya, and management implication for Turkana pastoralists. Land Degradation & Rehabilitation 1990, 2: 247–259. 10.1002/ldr.3400020402View ArticleGoogle Scholar
- Oba, G. 1998. Assessment of indigenous range management knowledge of the Borana pastoralists of Southern Ethiopia. Borana Lowland Pastoral Development Program/GTZ consultancy paper. Negelle/Borana, May 1998.Google Scholar
- Oba G, Post E, Syvertsen PO, Stenseth NC: Bush cover and range condition assessments in relation to landscape and grazing in southern Ethiopia. Landscape Ecology 2000, 15: 535–546. 10.1023/A:1008106625096View ArticleGoogle Scholar
- Pinard MA, Lutz FE, Licona JC: Tree mortality and vine proliferation following a wildfire in a sub-humid tropical forest in eastern Bolivia. Forest Ecology and Management 1999, 116: 247–252. 10.1016/S0378-1127(98)00447-2View ArticleGoogle Scholar
- Richter CGF, Snyman HA, Smit GN: The influence of tree density on the grass layer of three sem-arid savanna types of southern Africa. African Journal of Range Forage Science 2001, 18: 103–109. 10.2989/10220110109485762View ArticleGoogle Scholar
- SAS Institute. 2002. Statistical analysis software. SAS Institute Inc., Cary, NC, USA; 2002.Google Scholar
- Sawadogo L, Nygard R, Pallo F: Effects of livestock and prescribed fire on coppice growth after selective cutting of Sudanian savannah in Burkina Faso. Annals of Forest Science 2002, 59: 185–195. 10.1051/forest:2002005View ArticleGoogle Scholar
- Scott CW, Jeffrey SW: Effects of Japanese barberry (Ranunculales: Berberidaceae) removal and resulting microclimatic changes on Ixodes scapularis (Acari: Ixodidae) abundances in Connecticut, USA. Environmental Entomology 2010, 39(6):1911–1921. http://www.bioone.org/doi/full/%2010.1603/EN10131View ArticleGoogle Scholar
- Tamene, Y. 1990. Population dynamics of the problem shrubs, Acacia drepanolobium and Acacia brevispica in the southern rangelands of Ethiopia. MSc Thesis, Department of Animal Sciences, School of Fiber Sciences and Technology, University of NSW, Australia.Google Scholar
- Vesk PA: Plant size and resprouting ability: Trading tolerance and avoidance of damage? Journal of Ecology 2006, 94: 1027–1034. 10.1111/j.1365-2745.2006.01154.xView ArticleGoogle Scholar
- Ward D: Do we understand the causes of bush encroachment in Africa savannas? African Journal of Range and Forage Science 2005, 22: 101–105. 10.2989/10220110509485867View ArticleGoogle Scholar
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