Conversion of degraded free grazing lands into exclosures is one option to promote natural regeneration of plants and to restore degraded ecosystems in Ethiopia. The present study investigated the change in ecosystem carbon stocks (ECS) and the enhancement of plant species richness and diversity following the establishment of exclosures on free grazing lands in Tigray, Ethiopia. Exclosures of 10, 15, and 20 years old were selected and each exclosure was paired with an adjacent free grazing land. A total of 120 quadrants were sampled using a stratified preferential sampling design technique with flexible systematic model. The differences in carbon stocks and vegetation composition between an exclosure and free grazing lands were assessed using a paired t-test. Data analyses also included descriptive statistics, inferential statistics using one way ANOVA, t-test and Chi-square test. All exclosures displayed higher ECS, and plant species richness, diversity and aboveground standing biomass than the free grazing lands. Differences in ECS between exclosures and free grazing lands varied between 32.96 and 61.0 t. ha-1 increasing with exclosure age. Over a period of 20 years, the carbon dioxide sequestered in the investigated exclosures was 223.88 t. ha-1. Differences in plant species richness and aboveground standing biomass between exclosures and free grazing lands also increased with exclosure age. The results of the present study confirm that establishment of exclosures on degraded free grazing lands in the Northern Highlands of Ethiopian is a viable option to restore ECS. The study showed that ECS in exclosures, in free grazing lands and the change in ECS following the establishment of exclosures on free grazing lands can be predicted using easily measurable biophysical and management-related indicators. Such information is necessary for the establishment of baseline information for carbon sequestration projects, for evaluation of whether exclosure establishment should be expanded, and for policymakers to take into account the value of exclosures in their management decisions. Although the study showed that exclosures are effective to restore ECS, expansion of exclosures would increase grazing pressure on the remaining free grazing area. Therefore, the decision to establish additional exclosures should also include an economical analysis and an evaluation of the social consequences of such a decision.
Published in | American Journal of Biological and Environmental Statistics (Volume 3, Issue 4) |
DOI | 10.11648/j.ajbes.20170304.14 |
Page(s) | 65-80 |
Creative Commons |
This is an Open Access article, distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution and reproduction in any medium or format, provided the original work is properly cited. |
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Copyright © The Author(s), 2018. Published by Science Publishing Group |
Ecosystem Carbon Stock (ECS), Exclosure, Free Grazing Land, Northern Highlands of Ethiopia (Tigray)
[1] | Stocking, M., and Murnaghan, N. (2001). Handbook for the field assessment of land degradation. Earthscan publications Ltd, London, Stering VA. 169p. |
[2] | UNFPA and POPIN (1995). Population and Land Degradation. FAO/ UNFPA TSS. |
[3] | Betru, N., Jawad, A., and Ingrid, N. (2005). Exploring ecological and socio-Economic issues for the improvement of area enclosure management: A Case Study from Ethiopia. DCG Report No. 38. May 22005. Pp 3-30. |
[4] | Yayneshet, T., Eik, L. O. and Moe, S. R. (2009). The effects of exclosures in restoring degraded semi-arid vegetation in communal grazing lands in northern Ethiopia. Journal of Arid Environments 73 (5): 542-549. |
[5] | Dasgupta, P. and Maler, K. G. (1994). Poverty, Institutions and the environmental resource base, World Bank Environment paper 9. World Bank. Washington D. C. |
[6] | Hurni, H., Kebede, T., Gete, Z. (2005). The implications of changes in population, land use, and land management for surface runoff in the Upper Nile Basin area of Ethiopia. Mt. Res. Dev. 25: 145–149. |
[7] | Emiru, B., Demel, T., and Barklund, P. (2007). Enclosures to enhance woody species diversity in the drylands of Tigray. East African Journal of Science, 1: 136-147. |
[8] | REST (Relief Society of Tigray). (1998). Soil andWater Conservation Programme. REST, Mekelle, Ethiopia. |
[9] | Tucker, N. I., and Murphy, T. M., (1997). The effects of ecological rehabilitations on vegetation recruitment: some observations from the wet Tropics of North Queensland. Forest Ecology and Management99: 133 – 144. |
[10] | WFP/MoA (2002). (World Food Program/Ministry of Agriculture. Impact assessment of the ETH-2488/MERET Project (Interim Report). Ministry of Agriculture. Addis Ababa, Ethiopia. |
[11] | Wolde, M., Veldkamp, E., Mitiku, H., Kindeya, G., Muys, B., and Nyssen, J. (2009). Effectiveness of exclosures to control soil erosion and local community perception on soil erosion in Tigray, Ethiopia. African Journal of Agricultural Research 4: 365-377. |
[12] | Ravindranath, N. H., Somashekhar, B. S. and Gadgil, M. (1997). Carbon flow in Indian forests. Clim. Chang. 35: 297-320. |
[13] | FSI. (1988). The state of Forest Report 1987, Ministry of Environment and Forests. India. |
[14] | Soil Survey Staff. (1996). Keys to Soil Taxonomy. Seventh edition. United States Department of Agriculture, Washington DC. |
[15] | Gebrekidan, T., (2004). Impact of free grazing and open access to communal lands on Natural Resource: The case of Tigray Regional state in Ethiopia. Ethiopian Journal of Natural Resources 6 (1): 55-69. |
[16] | Asfawossen, A. (2002). The Rock-Hewn churches of Tigrai, northern Ethiopia: A geological perspective. Geoarchaeology 17: 649-663. |
[17] | BoANRD. (2010). Bureau of agriculture and natural resources of Tigray: Five-year implementation plan. Mekelle, Ethiopia. Unpublished. |
[18] | Pickett S. Space-for-time substitution as an alternative to long-term studies. In: Likens GE, editor. Long-Term Studies in Ecology: Approaches and Alternatives. New York: Springer; 1989. pp. 110–135. |
[19] | Smartt, P. F. (1978). Sampling for vegetation survey: a flexible systematic model for sample location. Journal of Biogeography 5 (1): 43-56. |
[20] | Kent, M. and Coker, P. (1992). Vegetation Description and Analysis: A practical approach. New York: John Wiley and Sons Ltd. 363pp. |
[21] | Getinet, M. (2014). Diversity, Structure, Regeneration, and Status of Vegetation in Simien Mountains National Park, Northern Ethiopia. Ph. D. Dissertation, Addis Ababa University, Ethiopia. |
[22] | Van der Maarel, E. (1979). Transformation of cover/abundance values in phytosociology and its effect on community similarity. Vegetatio 39: 97-114. |
[23] | Walkley, A., and Black. I. A. (1934). An examination of the Degtjareff method for determining organic carbon in soils: effect of variations in digestion conditions and of inorganic soil constituents. Soil Sci.63: 251-263. |
[24] | Blake, G. R., and Hartge, K. H. (1986). Bulk density. In: Klute, A. (ed.), Methods of soil analysis: part 1. Physical and mineralogical methods, ASA Monograph9: 363-375. |
[25] | Gee, G. W., and Bauder, J. W. (1982). Particle size analysis. In: Klute, A. (ed.), Methods of soil analysis: part 1. Physical and mineralogical methods, ASA Monograph9: 383-411. |
[26] | Baker, T. R., Philips, O. L., Malhi, Y, Almeida, S., Arroyo, L. and Di Fiore, A. (2004). Variation in wood density determines spatial patterns in Amazonian forest biomass. Global Change Biology10: 545-562. |
[27] | WBISPP (Woody Biomass Inventory and Strategic Planning Project). (2000). Manual for woody biomass inventory. Woody Biomass Inventory and Strategic Planning Project, Ministry of Agriculture, Addiss Ababa, Ethiopia. |
[28] | Swai, G., Ndangalasi, H., Munishi, P., and Shirima, D. (2014). Carbon Stocks of Hanang forest, Tanzania: An Implication for Climate Mitigation. Journal of Ecology and Natural Environment 6 (3): 90-98. |
[29] | Pearson, T., Brown, S., and Birdsey, R. (2007). Measurement Guidelines for the Sequestration of Forest carbon. Northern Research Station, Department of Agriculture, Washington, D. C. |
[30] | Gibbs, H., Brown, S., Niles, J., and Foley, J. (2007). Monitoring and Estimating Tropical Forest Carbon Stocks: Making REDD a Reality. Environment Research Letter 2 (4): 045023 doi:10.1088/1748-9326/2/4/045023. |
[31] | Zhu, B., Wang, X., Fang, J., Piao, S., Shen, H., Zhao, S. and Peng, C. (2010). Altitudinal Changes in Carbon Storage of Temperate Forests on Mt Changbai, Northeast China. Journal of Plant Research 123 (4): 39-52. |
[32] | Brown, S., Shoch D., Pearson, T., and Delaney, M. (2004). Methods for Measuring and Monitoring Forestry Carbon Projects in California. Winrock International, for the California Energy Commission, PIER Energy-Related Environmental Research. 500-04-072F. |
[33] | Verdoodt, A., Mureithi, S. M., and Ranst, E. V. (2010). Impacts of management and enclosure age on recovery of the herbaceous rangeland vegetation in semi-arid Kenya. Journal ofArid Environments74: 1066-1073. |
[34] | Muchiru, A. N., Western, D., and Reid, R. S. (2009). The impact of abandoned pastoral settlements on plant and nutrient succession in an African savanna ecosystem. Journalof Arid Environments73: 322-331. |
[35] | Hosseinzadeh, G., Jalilvand, H., and Tamartash, R. (2010). Short term impacts of enclosure on vegetation cover, productivity, and some physical and chemical soil properties. Journalof Applied Sciences10: 2001-2009. |
[36] | Carpenter, F. L., Mayorga, S. P., Quintero, E. G., & Schroeder, M. (2001). Land-use and erosion of a Costa Rican Ultisol affect soil chemistry, mycorrhizal fungi, and early regeneration. Forest Ecology and Management144: 1-17. |
[37] | Ayana, A., and Oba, G. (2010). Effects of grazing pressure, age of enclosures and seasonality on bush cover dynamics and vegetation composition in southern Ethiopia. J. Arid Environ.74: 111-120. |
[38] | Smit, G. N., Richter, C. G., and Aucamp, A. J. (1999). Bush encroachment: an approach to understanding and managing the problem. In: Tainton, N. M. (ed.), Veld Management in South Africa. University of Natal Press, Pietermaritzburg, South Africa. pp. 246-260. |
[39] | Woldeamlak, B., and Stroonijder, L. (2003). Effects of agroecological land use succession on soil properties in Chemoga watershed, Blue Nile basin, Ethiopia. Geoderma 111: 85–98. |
[40] | Girmay, G., Singh, B. R., Nyssen, J., and Borrosen, T. (2009). Runoff and sediment-associated nutrient losses under different land uses in Tigray, Northern Ethiopia. Journal of Hydrology376: 70-80. |
[41] | Descheemaeker, K., Nyssen, J., Rossi, J., Poesen, J., Mitiku, H., Moeyersons, J., & Deckers, J. (2006). Sediment deposition and pedogenesis in exclosures in the Tigray Highlands, Ethiopia. Geoderma, 132: 291-314. |
[42] | Abiy, T. (2008). Area closure as a strategy for land management: A case study at Kelala Dalacha enclosure in the central rift valley of Ethiopia. MSc thesis, Addis Ababa University, Ethiopia. pp107. |
[43] | Verdoodt, A., Mureithi, S. M., Ye, L., and Ranst, E. V. (2009). Chronosequence analysis of two enclosure management strategies in degraded rangeland of semi-arid Kenya. Agric. Ecosyst. Environ. 129: 332-339. |
[44] | Zenebe, G. (2007). Household fuel consumption and resource use in rural-urban Ethiopia. Ph. D. Dissertation. Wageningen University. The Netherlands. ISBN: 978-90-8504-745-2. |
[45] | Mulugeta, L., Karltun, E., and Olsson, M. (2005). Soil organic matter dynamics after deforestation along a farm field chronosequence in southern highlands of Ethiopia. Agric. Ecosyst. Environ.109: 9-19. |
[46] | Dereje, A., Oba, G., Weladji, R. B., and Colman, J. E. (2003). An assessment of restoration of biodiversity in degraded high mountain grazing lands in Northern Ethiopia. Land Degrad. Develop.14: 25–38. |
[47] | De Koning, G. H., Veldkamp, E., and Lopez-Ulloa, M. (2003). Quantification of carbon sequestration in soils following pasture to forest conversion in northwestern Ecuador. Global Biogeochem. Cy. 17: 1-12. |
[48] | Capoor, K., and Amborsi, P. (2008). State and trends in the carbon market 2008, Washington DC: The World Bank. |
[49] | Timothy, R., Pearson, H., Brown, S., Sohngen, B., Henman, J. and Ohrel, S. (2013). Transaction costs for carbon sequestration projects in the tropical forest sector. Open access at Springerlink.com. Mitig Adapt Strateg Glob Change. DOI 10.1007/s11027-013-9469-8. |
[50] | Usuga, J., Toro, J., Alzate, M. and Tapias, Á. (2010). Estimation of Biomass and Carbon Stocks in Plants, Soil and Forest Floor in Different Tropical Forests. Forest Ecology and Management 260: 1906–1913. |
[51] | Yitebitu, M., Zewdu, E., and Sisay, N. (2010). Ethiopian Forest Resources: Current Status and Future Management Options in View of Access to Carbon Finances. A Review: Prepared for the Ethiopian Climate Research and Networking and the United Nations Development Program (UNDP). |
[52] | Achard, F., Eva, H. D., Mayaux, P., Stibig, H. J. and Belward, A. (2004). Improved estimates of net carbon emissions from land cover change in the tropics for the 1990s Glob. Biogeochem. Cycles 18: 1029-1042. |
[53] | Anup, K. C., Bhandari, G., Joshi, G. R. and Aryal, S. (2013). Climate change mitigation potential from carbon sequestration of community forest in mid hill region of Nepal. Int. J. Environ. Prot. 3 (7): 33-40. |
[54] | Brown, S. and Lugo, A. E. (1982). The storage and production of organic matter in tropical forests and their role in the global carbon cycle. Biotropica. 14: 161-187. |
[55] | Lasco, R. D., Pulhin, F. B., Visco, R. G., Racelis, D. A., Guillermo, I. Q. and Sales, R. F. (2000). Carbon stocks assessment of Philippine forest ecosystems. Paper presented at the Science-Policy workshop on terrestrial carbon assessment for possible carbon trading, Bogor, pp. 28-29. |
[56] | Sheikh, M. A., Kumar, M., and Bussmann, R. W. (2009). Altitudinal variation in soil organic carbon stock in coniferous subtropical and broadleaf temperate forests in Garhwal Himalaya. Carbon Balanceand Management 4: 1-6. |
[57] | Houghton, R. A. (2005). Tropical deforestation as a source of greenhouse gas emissions. In: Moutinho, P., and Schwarzman, S. (eds.). Tropical deforestation and climate change. IPAM – Instituto de Pesquisa Ambiental de Amazonia; Washington DC, USA. |
[58] | Asner, G. P., Anderson, C. B., Martin, R. E., Knapp, D. E., Tupayachi, R., Sinca, F. and Malhi, Y. (2014). Landscape-scale changes in forest structure and functional traits along an Andes-to-Amazon elevation gradient. Biogeosciences 11: 843-856. |
[59] | Murphy, P. G., and Lugo, A. E. (1986). Ecology of Tropical Dry Forest. Annual Review of Ecology and Systematics 17: 67-88. |
[60] | Bayat, T. A. (2011). Carbon stock in an Apennine beech forest. MSc. Thesis. University of Twente, Enschede, the Netherlands. |
[61] | Muluken, N. (2014). Carbon Stock in Adaba-Dodola Community Forest of Danaba District, West-Arsi Zone of Oromia Region, Ethiopia: An Implication for Climate Change Mitigation. MSc. Thesis. Addis Ababa University. |
[62] | Nesru Hassen (2015). Carbon Stocks along Altitudinal Gradient in Gera Moist Evergreen Afromontane forest, Southwest Ethiopia. MSc. Thesis. Addis Ababa University. |
[63] | Abel, G., Teshome, S., and Tesfaye, B. (2014). Forest Carbon Stocks in Woody Plants of Mount Zequalla Monastery and its Variation along Altitudinal Gradient: Implication of Managing Forests for Climate Change Mitigation. Science, Technology, and Arts Research Journal 3 (2): 133-141. |
[64] | Belay, M., Ensermu, K., and Teshome, S. (2014). Forest Carbon Stocks in Woody Plants of Arba Minch Ground Water Forest and its Variations along Environmental Gradients. Science, Technology, and Arts Research Journal 3 (2): 141-147. |
[65] | Adugna, F., Teshome, S., and Mekuria, A. (2013). Forest carbon stocks and variations along altitudinal gradients in Egdu Forest: Implications of managing forests for climate change mitigation. Science, Technology, and Arts Resesearch Journal 2 (4): 40-46. |
[66] | Mesfin, S. (2011). Estimating and Mapping of Carbon Stocks based on Remote Sensing, GIS and Ground Survey in the Menagesha Suba State Forest, Ethiopia. MSc. Thesis, Addis Ababa University. |
[67] | Tulu Tolla (2011). Estimation of Carbon Stock in Church Forests: Implications for Managing Church for Forest Carbon Emission Reduction. MSc. Thesis. Addis Ababa University. |
[68] | Getu, S. (2012). Carbon Stocks in Different Pools in Natural and Plantation Forests of Chilimo, Central Highlands of Ethiopia. MSc. Thesis, Addis Ababa Univesity, Ethiopia. |
[69] | Mohammed, G., Teshome, S., and Satishkumar, B. (2014). Forest carbon stocks in woody plants of Tara Gedam forest: Implication for climate change mitigation. Sci. Technol. Arts Res. J. 3 (1): 101-107. |
[70] | Marshet, T., and Teshome, S. (2015). Carbon Stock Potentials of Woody Plant Species in Biheretsige and Central Closed Public Parks of Addis Ababa and Its Contribution to Climate Change Mitigation. Journal of Environment and Earth Science 5 (13): 2216-2224. |
[71] | Dagnachew, T. (2016). Carbon stock of meskele gedam forest and its contribution to climate change mitigation. Msc. Thesis, Adis Ababa University, Addis Ababa. Pp.85. |
[72] | Fentahun, A., Yehualashet, B., Alemayehu, K., and Teshome, S. (2017). Carbon stock of Banja forest in Banja district, Amhara region, Ethiopia: An implication for climate change mitigation, Journal of Sustainable Forestry DOI: 10.1080/10549811.2017.1332646. |
[73] | FAO. (1984). Agroclimatic Resource Inventory for Land use Planning. Ethiopia. Technical Report 2. AG: DP/ETH/78/003, Rome. |
APA Style
Samson Shimelse, Tamrat Bekele, Sileshi Nemomissa. (2018). Effect of Exclosure Age on Carbon Sequestration Potential of Restorations in Tigray Region, N. Ethiopia. American Journal of Biological and Environmental Statistics, 3(4), 65-80. https://doi.org/10.11648/j.ajbes.20170304.14
ACS Style
Samson Shimelse; Tamrat Bekele; Sileshi Nemomissa. Effect of Exclosure Age on Carbon Sequestration Potential of Restorations in Tigray Region, N. Ethiopia. Am. J. Biol. Environ. Stat. 2018, 3(4), 65-80. doi: 10.11648/j.ajbes.20170304.14
AMA Style
Samson Shimelse, Tamrat Bekele, Sileshi Nemomissa. Effect of Exclosure Age on Carbon Sequestration Potential of Restorations in Tigray Region, N. Ethiopia. Am J Biol Environ Stat. 2018;3(4):65-80. doi: 10.11648/j.ajbes.20170304.14
@article{10.11648/j.ajbes.20170304.14, author = {Samson Shimelse and Tamrat Bekele and Sileshi Nemomissa}, title = {Effect of Exclosure Age on Carbon Sequestration Potential of Restorations in Tigray Region, N. Ethiopia}, journal = {American Journal of Biological and Environmental Statistics}, volume = {3}, number = {4}, pages = {65-80}, doi = {10.11648/j.ajbes.20170304.14}, url = {https://doi.org/10.11648/j.ajbes.20170304.14}, eprint = {https://article.sciencepublishinggroup.com/pdf/10.11648.j.ajbes.20170304.14}, abstract = {Conversion of degraded free grazing lands into exclosures is one option to promote natural regeneration of plants and to restore degraded ecosystems in Ethiopia. The present study investigated the change in ecosystem carbon stocks (ECS) and the enhancement of plant species richness and diversity following the establishment of exclosures on free grazing lands in Tigray, Ethiopia. Exclosures of 10, 15, and 20 years old were selected and each exclosure was paired with an adjacent free grazing land. A total of 120 quadrants were sampled using a stratified preferential sampling design technique with flexible systematic model. The differences in carbon stocks and vegetation composition between an exclosure and free grazing lands were assessed using a paired t-test. Data analyses also included descriptive statistics, inferential statistics using one way ANOVA, t-test and Chi-square test. All exclosures displayed higher ECS, and plant species richness, diversity and aboveground standing biomass than the free grazing lands. Differences in ECS between exclosures and free grazing lands varied between 32.96 and 61.0 t. ha-1 increasing with exclosure age. Over a period of 20 years, the carbon dioxide sequestered in the investigated exclosures was 223.88 t. ha-1. Differences in plant species richness and aboveground standing biomass between exclosures and free grazing lands also increased with exclosure age. The results of the present study confirm that establishment of exclosures on degraded free grazing lands in the Northern Highlands of Ethiopian is a viable option to restore ECS. The study showed that ECS in exclosures, in free grazing lands and the change in ECS following the establishment of exclosures on free grazing lands can be predicted using easily measurable biophysical and management-related indicators. Such information is necessary for the establishment of baseline information for carbon sequestration projects, for evaluation of whether exclosure establishment should be expanded, and for policymakers to take into account the value of exclosures in their management decisions. Although the study showed that exclosures are effective to restore ECS, expansion of exclosures would increase grazing pressure on the remaining free grazing area. Therefore, the decision to establish additional exclosures should also include an economical analysis and an evaluation of the social consequences of such a decision.}, year = {2018} }
TY - JOUR T1 - Effect of Exclosure Age on Carbon Sequestration Potential of Restorations in Tigray Region, N. Ethiopia AU - Samson Shimelse AU - Tamrat Bekele AU - Sileshi Nemomissa Y1 - 2018/01/08 PY - 2018 N1 - https://doi.org/10.11648/j.ajbes.20170304.14 DO - 10.11648/j.ajbes.20170304.14 T2 - American Journal of Biological and Environmental Statistics JF - American Journal of Biological and Environmental Statistics JO - American Journal of Biological and Environmental Statistics SP - 65 EP - 80 PB - Science Publishing Group SN - 2471-979X UR - https://doi.org/10.11648/j.ajbes.20170304.14 AB - Conversion of degraded free grazing lands into exclosures is one option to promote natural regeneration of plants and to restore degraded ecosystems in Ethiopia. The present study investigated the change in ecosystem carbon stocks (ECS) and the enhancement of plant species richness and diversity following the establishment of exclosures on free grazing lands in Tigray, Ethiopia. Exclosures of 10, 15, and 20 years old were selected and each exclosure was paired with an adjacent free grazing land. A total of 120 quadrants were sampled using a stratified preferential sampling design technique with flexible systematic model. The differences in carbon stocks and vegetation composition between an exclosure and free grazing lands were assessed using a paired t-test. Data analyses also included descriptive statistics, inferential statistics using one way ANOVA, t-test and Chi-square test. All exclosures displayed higher ECS, and plant species richness, diversity and aboveground standing biomass than the free grazing lands. Differences in ECS between exclosures and free grazing lands varied between 32.96 and 61.0 t. ha-1 increasing with exclosure age. Over a period of 20 years, the carbon dioxide sequestered in the investigated exclosures was 223.88 t. ha-1. Differences in plant species richness and aboveground standing biomass between exclosures and free grazing lands also increased with exclosure age. The results of the present study confirm that establishment of exclosures on degraded free grazing lands in the Northern Highlands of Ethiopian is a viable option to restore ECS. The study showed that ECS in exclosures, in free grazing lands and the change in ECS following the establishment of exclosures on free grazing lands can be predicted using easily measurable biophysical and management-related indicators. Such information is necessary for the establishment of baseline information for carbon sequestration projects, for evaluation of whether exclosure establishment should be expanded, and for policymakers to take into account the value of exclosures in their management decisions. Although the study showed that exclosures are effective to restore ECS, expansion of exclosures would increase grazing pressure on the remaining free grazing area. Therefore, the decision to establish additional exclosures should also include an economical analysis and an evaluation of the social consequences of such a decision. VL - 3 IS - 4 ER -