| Peer-Reviewed

The Effect of Coffee Expansion on Carbon Stock of Natural Forest in Gidame Woreda, West Ethiopia

Received: 28 August 2022    Accepted: 6 September 2022    Published: 14 November 2022
Views:       Downloads:
Abstract

The important climate-related functions of forest ecosystems are carbon sequestration, regulating the global carbon cycle and climate change mitigation. About 80% of the terrestrial carbon is stored as forest biomass and soil organic carbon. Deforestation and forest degradation show an alarming high, mainly due to the conversion of natural forest to commercial and cereal crop production. By considering this issue, this study was conducted with the aim to assess the effect of coffee expansion on carbon stock of the natural forest ecosystem in Gidame woreda. The study site was stratified in two strata: undisturbed natural forest and disturbed coffee forest. A total of 71 nested square sample plot was determined, proportionally allocated (29 for undisturbed and 42 for disturbed/coffee forest) and randomly distributed within each stratum. In both cases, the diameter at breast height and tree height were measured; litter sample was collected by harvesting and weighing technique. A total of 72 composite soil samples were also collected from proportionally and randomly selected 24 sample plots; 10 from undisturbed natural forest and 14 from disturbed coffee forest for SOC quantification in three layers (0-15cm, 16-30cm, and 31-45cm). From these forest inventory data, the above-ground biomass carbon stock was estimated by using allometric equations. The below-ground biomass carbon stock was derived from the above-ground carbon stock. The results showed that the biomass carbon stock was 298.758 ± 9.4tc/ha for undisturbed natural forest and 199.895 ± 11tc/ha for disturbed coffee forest and the difference is statistically significant as p < 0.05. This revealed that the disturbance of this natural forest ecosystem, which is associated with the conversion of natural forest to the coffee cultivation area, resulted in the loss of 33.09% of the biomass carbon stock. The SOC is 148.40 ± 12tc/ha for undisturbed forest and 153.80 ± 4.30tc/ha for disturbed coffee forest has no significant difference as p > 0.05. Therefore, maintaining the biomass carbon sequestration potential of this natural forest ecosystem should be required through the implementation of different conservation mechanisms.

Published in American Journal of Life Sciences (Volume 10, Issue 5)
DOI 10.11648/j.ajls.20221005.12
Page(s) 104-114
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.

Copyright

Copyright © The Author(s), 2024. Published by Science Publishing Group

Keywords

Carbon Stock, Coffee Forest, Disturbed Forest, Forest Degradation, Natural Forest, Undisturbed Forest

References
[1] Geldenhuys CJ. Concepts and Process to Control Invader Plants in and Around Natural Evergreen Forest in South Africa1. Weed Technology. 2004 Dec; 18 (sp1): 1386-91.
[2] Virgilio N, Marshall S. Forest carbon strategies in climate change mitigation: confronting challenges through on the-ground experience. The Nature Conservancy. Arlington, Virginia. 2009.
[3] Hamdan O, Aziz HK, Rahman KA. Remotely sensed L-Band SAR data for tropical forest biomass estimation. Journal of Tropical Forest Science. 2011 Jul 1: 318-27.
[4] Pearson TR. Measurement guidelines for the sequestration of forest carbon. US Department of Agriculture, Forest Service, Northern Research Station; 2007.
[5] Ontl TA, Schulte LA. Soil carbon storage. Nature Education Knowledge. 2012; 3 (10).
[6] Tremblay S, Périé C, Ouimet R. Changes in organic carbon storage in a 50 year white spruce plantation chronosequence established on fallow land in Quebec. Canadian journal of forest research. 2006 Nov 1; 36 (11): 2713-23.
[7] Change IP. 2006 IPCC guidelines for national greenhouse gas inventories. Institute for Global Environmental Strategies, Hayama, Kanagawa, Japan. 2006.
[8] Bhartendu A. Deforestation causing global warming and climate change. International Journal of Chemical Sciences. 2012; 10 (3): 1731-4.
[9] WeldeMichael G, Alamerew S, Kufa T. Genetic Diversity Analysis of Some Ethiopian Specialty Coffee (Coffea arabica L.) Accessions for Cup Quality Attributing Traits. J. of Biology, Agriculture and Healthcare. 2015; 5 (5): 88-96.
[10] Mishra MK, Nishani S, Gowda M, Padmajyothi D, Suresh N, Sreenath H, Raghuramulu Y. Genetic diversity among Ethiopian coffee (Coffea arabica L.) collections available in Indian gene bank using sequence related amplified polymorphism markers. Plant breeding and seed science. 2014 Dec 18; 70: 29-40.
[11] Engels JM, Hawkes JG, Hawkes JG, Worede M, editors. Plant genetic resources of Ethiopia. Cambridge University Press; 1991 Mar 21.
[12] Taye K. Plant composition and growth of wild Coffea arabica: Implications for management and conservation of natural forest resources. International Journal of Biodiversity and Conservation. 2011 Apr 30; 3 (4): 131-41.
[13] Senbeta F, Denich M. Effects of wild coffee management on species diversity in the Afromontane rainforests of Ethiopia. Forest Ecology and Management. 2006 Aug 15; 232 (1-3): 68-74.
[14] Hundera K, Aerts R, Fontaine A, Van Mechelen M, Gijbels P, Honnay O, Muys B. Effects of coffee management intensity on composition, structure, and regeneration status of Ethiopian moist evergreen afromontane forests. Environmental management. 2013 Mar; 51 (3): 801-9.
[15] Aerts R, Hundera K, Berecha G, Gijbels P, Baeten M, Van Mechelen M, Hermy M, Muys B, Honnay O. Semi-forest coffee cultivation and the conservation of Ethiopian Afromontane rainforest fragments. Forest Ecology and Management. 2011 Mar 15; 261 (6): 1034-41.
[16] Basnyat B. Impacts of demographic changes on forests and forestry in Asia and the Pacific. Bangkok, FAO of the United Nations Regional Office for Asia and the Pacific. 2009.
[17] Hundera K. Effects of Coffee Forest Management and Fragmentation on Plant Communities and Regeneration Patterns In Afromontane Moist Evergreen Forests in South West Ethiopia. Jimma University. 2013.
[18] Hundera K. Shade tree selection and management practices by farmers in traditional coffee production systems in Jimma Zone, Southwest Ethiopia. Ethiopian Journal of Education and Sciences. 2016; 11 (2): 91-105.
[19] Pearson T, Walker S, Brown S. Sourcebook for land use, land-use change and forestry projects.
[20] Avery TE, Burkhart HE. Forest measurements. Waveland Press; 2015 May 18.
[21] Hairiah K, Sitompul SM, Van Noordwijk M, Palm C. Methods for sampling carbon stocks above and below ground. Bogoi: ICRAF; 2001 Dec.
[22] Bhishma PS, Shiva SP, Ajay P, Eak BR, Sanjeeb B, Tibendra RB, Shambhu C, Rijan T. Forest Carbon Stock Measurement: Guidelines for measuring carbon stocks in community-managed forests. Funded by Norwegian Agency for Development Cooperation (NORAD). Asia Network for Sustainable Agriculture and Bioresources (ANSAB) publishing, Kathmandu, Nepal. 2010: 17-43.
[23] Chave J, Réjou-Méchain M, Búrquez A, Chidumayo E, Colgan MS, Delitti WB, Duque A, Eid T, Fearnside PM, Goodman RC, Henry M. Improved allometric models to estimate the aboveground biomass of tropical trees. Global change biology. 2014 Oct; 20 (10): 3177-90.
[24] Putz FE. Liana biomass and leaf area of a" tierra firme" forest in the Rio Negro Basin, Venezuela. Biotropica. 1983 Sep 1: 185-9.
[25] Negash M, Starr M, Kanninen M, Berhe L. Allometric equations for estimating aboveground biomass of Coffea arabica L. grown in the Rift Valley escarpment of Ethiopia. Agroforestry systems. 2013 Aug; 87 (4): 953-66.
[26] DeWalt SJ, Chave J. Structure and biomass of four lowland Neotropical forests. Biotropica. 2004 Mar; 36 (1): 7-19.
[27] Karki S, Joshi NR, Udas E, Adhikari MD, Sherpa S, Kotru R, Karky BS, Chettri N, Ning W. Assessment of forest carbon stock and carbon sequestration rates at the ICIMOD Knowledge Park at Godavari. ICIMOD Working Paper. 2016 (2016/6).
[28] Walkley A, Black IA. An examination of the Degtjareff method for determining soil organic matter, and a proposed modification of the chromic acid titration method. Soil science. 1934 Jan 1; 37 (1): 29-38.
[29] Kuruppuarachchi KA, Seneviratne G, Madurapperuma D. Carbon sequestration in tropical forest stands: its control by plant, soil and climatic factors.
[30] Addi A. The Ecology, Carbon Stock, Bee Forage diversity In A Moist Afromontane Forest Of Gesha And Sayilem Districts In Kaffa Zone, South West Ethiopia. J. Mater. Process. Technol. 2018.
[31] Dibaba A, Soromessa T, Workineh B. Carbon stock of the various carbon pools in Gerba-Dima moist Afromontane forest, South-western Ethiopia. Carbon balance and management. 2019 Dec; 14 (1): 1-0.
[32] Sahoo A. Assessment of Biomass and Total Carbon Stock in a Tropical Wet Evergreen Rainforest of Eastern Himalaya along a Disturbance Gradient. Assessment. 2017 Apr; 4 (1).
[33] Feyissa A, Soromessa T, Argaw M. Forest carbon stocks and variations along altitudinal gradients in Egdu Forest: Implications of managing forests for climate change mitigation. Science, Technology and Arts Research Journal. 2013; 2 (4): 40-6.
[34] Addi A, Demissew S, Soromessa T, Asfaw Z. Carbon stock of the moist Afromontane forest in Gesha and Sayilem Districts in Kaffa Zone: An implication for climate change mitigation. J Ecosyst Ecograph. 2019; 9 (1): 1-8.
[35] Ullah MR, Al-Amin M. Above-and below-ground carbon stock estimation in a natural forest of Bangladesh. Journal of forest science. 2012 Aug 24; 58 (8): 372-9.
[36] Baccini AG, Goetz SJ, Walker WS, Laporte NT, Sun M, Sulla-Menashe D, Hackler J, Beck PS, Dubayah R, Friedl MA, Samanta S. Estimated carbon dioxide emissions from tropical deforestation improved by carbon-density maps. Nature climate change. 2012 Mar; 2 (3): 182-5.
[37] Gullison RE, Frumhoff PC, Canadell JG, Field CB, Nepstad DC, Hayhoe K, Avissar R, Curran LM, Friedlingstein P, Jones CD, Nobre C. Tropical forests and climate policy. Science. 2007 May 18; 316 (5827): 985-6.
[38] Harris NL, Brown S, Hagen SC, Saatchi SS, Petrova S, Salas W, Hansen MC, Potapov PV, Lotsch A. Baseline map of carbon emissions from deforestation in tropical regions. Science. 2012 Jun 22; 336 (6088): 1573-6.
[39] Change IP. Report of The Nineteenth Session Of The Intergovernmental Panel on Climate Change (IPCC) Geneva, 17-20 (am only) April 2002.
[40] Thong P, Pebam R, Sahoo UK. Recovery pattern of vegetation during succession following slash and burn agriculture in Mizoram, North-East India. Journal of Plant Biology and Soil Health. 2016; 3 (2): 8-16.
[41] Berenguer E, Ferreira J, Gardner TA, Aragão LE, De Camargo PB, Cerri CE, Durigan M, Oliveira RC, Vieira IC, Barlow J. A large-scale field assessment of carbon stocks in human-modified tropical forests. Global change biology. 2014 Dec; 20 (12): 3713-26.
[42] Chidumayo EN. Forest degradation and recovery in a miombo woodland landscape in Zambia: 22 years of observations on permanent sample plots. Forest Ecology and Management. 2013 Mar 1; 291: 154-61.
[43] MacDicken K, Jonsson Ö, Piña L, Maulo S, Contessa V, Adikari Y. & D’Annunzio, R. (2016). Global forest resources assessment. 2015.
[44] Virgilio NR, Marshall S, Zerbock O, Holmes C. Reducing emissions from deforestation and degradation (REDD): a casebook of on-the-ground experience. Reducing emissions from deforestation and degradation (REDD): a casebook of on-the-ground experience. 2010.
[45] Hylander K, Nemomissa S, Delrue J, Enkosa W. Effects of coffee management on deforestation rates and forest integrity. Conservation biology. 2013 Oct; 27 (5): 1031-40.
[46] Lassauce A, Paillet Y, Jactel H, Bouget C. Deadwood as a surrogate for forest biodiversity: meta-analysis of correlations between deadwood volume and species richness of saproxylic organisms. Ecological Indicators. 2011 Sep 1; 11 (5): 1027-39.
[47] Franklin JF, Spies TA, Van Pelt R, Carey AB, Thornburgh DA, Berg DR, Lindenmayer DB, Harmon ME, Keeton WS, Shaw DC, Bible K. Disturbances and structural development of natural forest ecosystems with silvicultural implications, using Douglas-fir forests as an example. Forest ecology and management. 2002 Jan 1; 155 (1-3): 399-423.
[48] Binkley D, Fisher RF. Ecology and management of forest soils. John Wiley & Sons; 2019 Jun 10.
[49] Barbosa RI, dos Santos JR, da Cunha MS, Pimentel TP, Fearnside PM. Root biomass, root: shoot ratio and belowground carbon stocks in the open savannahs of Roraima, Brazilian Amazonia. Australian Journal of Botany. 2012 Jul 11; 60 (5): 405-16.
[50] Mohammed A, Bekele L. Changes in carbon stocks and sequestration potential under native forest and adjacent land use systems at gera, south-western Ethiopia. Global Journal of Science Frontier Research: D Agriculture and Veterinary. 2014 Jan; 14 (10): 11-9.
[51] Rhoades CC, Eckert GE, Coleman DC. Soil carbon differences among forest, agriculture, and secondary vegetation in lower montane Ecuador. Ecological Applications. 2000 Apr; 10 (2): 497-505.
[52] Dang TT, Do HT. Biomass and carbon stocks of the natural forests at Me Linh biodiversity station, Vinh Phuc province, Vietnam. Journal of Vietnamese Environment. 2014 Nov 5; 6 (3): 281-7.
[53] Alavaisha E, Mangora MM. Carbon stocks in the small estuarine mangroves of Geza and Mtimbwani, Tanga, Tanzania. International Journal of Forestry Research. 2016 Jan 1; 2016.
[54] Batjes NH. Soil organic carbon stocks under native vegetation–Revised estimates for use with the simple assessment option of the Carbon Benefits Project system. Agriculture, Ecosystems & Environment. 2011 Aug 1; 142 (3-4): 365-73.
[55] Victoria R, Banwart S, Black H, Ingram J, Joosten H, Milne E, Noellemeyer E, Baskin Y. The benefits of soil carbon. Foresight chapter in UNEP Yearbook. 2012; 2012: 19-33.
[56] Zhang Z, Zhou Y, Wang S, Huang X. Estimation of soil organic carbon storage and its fractions in a small karst watershed. Acta Geochimica. 2018 Feb; 37 (1): 113-24.
[57] Kukal SS, Bawa SS. Soil organic carbon stock and fractions in relation to land use and soil depth in the degraded Shiwaliks hills of lower Himalayas. Land Degradation & Development. 2014 Sep; 25 (5): 407-16.
[58] Wells T, Hancock GR, Dever C, Murphy D. Prediction of vertical soil organic carbon profiles using soil properties and environmental tracer data at an untilled site. Geoderma. 2012 Jan 15; 170: 337-46.
[59] Pauli N, Barrios E, Conacher AJ, Oberthür T. Farmer knowledge of the relationships among soil macrofauna, soil quality and tree species in a smallholder agroforestry system of western Honduras. Geoderma. 2012 Nov 1; 189: 186-98.
[60] Fontaine S, Barot S, Barré P, Bdioui N, Mary B, Rumpel C. Stability of organic carbon in deep soil layers controlled by fresh carbon supply. Nature. 2007 Nov; 450 (7167): 277-80.
[61] Luyssaert S, Schulze E, Börner A, Knohl A, Hessenmöller D, Law BE, Ciais P, Grace J. Old-growth forests as global carbon sinks. Nature. 2008 Sep; 455 (7210): 213-5.
[62] De Beenhouwer M, Geeraert L, Mertens J, Van Geel M, Aerts R, Vanderhaegen K, Honnay O. Biodiversity and carbon storage co-benefits of coffee agroforestry across a gradient of increasing management intensity in the SW Ethiopian highlands. Agriculture, Ecosystems & Environment. 2016 Apr 15; 222: 193-9.
[63] Chambers JQ, Higuchi N, Schimel JP, Ferreira LV, Melack JM. Decomposition and carbon cycling of dead trees in tropical forests of the central Amazon. Oecologia. 2000 Feb; 122 (3): 380-8.
[64] Dutta J, Banerjee K, Agarwal S, Mitra A. Soil Organic Carbon (Soc): A Proxy to Assess the Degree of Anthropogenic and Natural Stress. The Journal of Interrupted Studies. 2019 Jun 14; 2 (1): 90-102.
[65] Hertel D, Harteveld MA, Leuschner C. Conversion of a tropical forest into agroforest alters the fine root-related carbon flux to the soil. Soil Biology and Biochemistry. 2009 Mar 1; 41 (3): 481-90.
[66] Kessler M, Hertel D, Jungkunst HF, Kluge J, Abrahamczyk S, Bos M, Buchori D, Gerold G, Gradstein SR, Köhler S, Leuschner C. Can joint carbon and biodiversity management in tropical agroforestry landscapes be optimized?
Cite This Article
  • APA Style

    Yadesa Akena Dinsa. (2022). The Effect of Coffee Expansion on Carbon Stock of Natural Forest in Gidame Woreda, West Ethiopia. American Journal of Life Sciences, 10(5), 104-114. https://doi.org/10.11648/j.ajls.20221005.12

    Copy | Download

    ACS Style

    Yadesa Akena Dinsa. The Effect of Coffee Expansion on Carbon Stock of Natural Forest in Gidame Woreda, West Ethiopia. Am. J. Life Sci. 2022, 10(5), 104-114. doi: 10.11648/j.ajls.20221005.12

    Copy | Download

    AMA Style

    Yadesa Akena Dinsa. The Effect of Coffee Expansion on Carbon Stock of Natural Forest in Gidame Woreda, West Ethiopia. Am J Life Sci. 2022;10(5):104-114. doi: 10.11648/j.ajls.20221005.12

    Copy | Download

  • @article{10.11648/j.ajls.20221005.12,
      author = {Yadesa Akena Dinsa},
      title = {The Effect of Coffee Expansion on Carbon Stock of Natural Forest in Gidame Woreda, West Ethiopia},
      journal = {American Journal of Life Sciences},
      volume = {10},
      number = {5},
      pages = {104-114},
      doi = {10.11648/j.ajls.20221005.12},
      url = {https://doi.org/10.11648/j.ajls.20221005.12},
      eprint = {https://article.sciencepublishinggroup.com/pdf/10.11648.j.ajls.20221005.12},
      abstract = {The important climate-related functions of forest ecosystems are carbon sequestration, regulating the global carbon cycle and climate change mitigation. About 80% of the terrestrial carbon is stored as forest biomass and soil organic carbon. Deforestation and forest degradation show an alarming high, mainly due to the conversion of natural forest to commercial and cereal crop production. By considering this issue, this study was conducted with the aim to assess the effect of coffee expansion on carbon stock of the natural forest ecosystem in Gidame woreda. The study site was stratified in two strata: undisturbed natural forest and disturbed coffee forest. A total of 71 nested square sample plot was determined, proportionally allocated (29 for undisturbed and 42 for disturbed/coffee forest) and randomly distributed within each stratum. In both cases, the diameter at breast height and tree height were measured; litter sample was collected by harvesting and weighing technique. A total of 72 composite soil samples were also collected from proportionally and randomly selected 24 sample plots; 10 from undisturbed natural forest and 14 from disturbed coffee forest for SOC quantification in three layers (0-15cm, 16-30cm, and 31-45cm). From these forest inventory data, the above-ground biomass carbon stock was estimated by using allometric equations. The below-ground biomass carbon stock was derived from the above-ground carbon stock. The results showed that the biomass carbon stock was 298.758 ± 9.4tc/ha for undisturbed natural forest and 199.895 ± 11tc/ha for disturbed coffee forest and the difference is statistically significant as p  0.05. Therefore, maintaining the biomass carbon sequestration potential of this natural forest ecosystem should be required through the implementation of different conservation mechanisms.},
     year = {2022}
    }
    

    Copy | Download

  • TY  - JOUR
    T1  - The Effect of Coffee Expansion on Carbon Stock of Natural Forest in Gidame Woreda, West Ethiopia
    AU  - Yadesa Akena Dinsa
    Y1  - 2022/11/14
    PY  - 2022
    N1  - https://doi.org/10.11648/j.ajls.20221005.12
    DO  - 10.11648/j.ajls.20221005.12
    T2  - American Journal of Life Sciences
    JF  - American Journal of Life Sciences
    JO  - American Journal of Life Sciences
    SP  - 104
    EP  - 114
    PB  - Science Publishing Group
    SN  - 2328-5737
    UR  - https://doi.org/10.11648/j.ajls.20221005.12
    AB  - The important climate-related functions of forest ecosystems are carbon sequestration, regulating the global carbon cycle and climate change mitigation. About 80% of the terrestrial carbon is stored as forest biomass and soil organic carbon. Deforestation and forest degradation show an alarming high, mainly due to the conversion of natural forest to commercial and cereal crop production. By considering this issue, this study was conducted with the aim to assess the effect of coffee expansion on carbon stock of the natural forest ecosystem in Gidame woreda. The study site was stratified in two strata: undisturbed natural forest and disturbed coffee forest. A total of 71 nested square sample plot was determined, proportionally allocated (29 for undisturbed and 42 for disturbed/coffee forest) and randomly distributed within each stratum. In both cases, the diameter at breast height and tree height were measured; litter sample was collected by harvesting and weighing technique. A total of 72 composite soil samples were also collected from proportionally and randomly selected 24 sample plots; 10 from undisturbed natural forest and 14 from disturbed coffee forest for SOC quantification in three layers (0-15cm, 16-30cm, and 31-45cm). From these forest inventory data, the above-ground biomass carbon stock was estimated by using allometric equations. The below-ground biomass carbon stock was derived from the above-ground carbon stock. The results showed that the biomass carbon stock was 298.758 ± 9.4tc/ha for undisturbed natural forest and 199.895 ± 11tc/ha for disturbed coffee forest and the difference is statistically significant as p  0.05. Therefore, maintaining the biomass carbon sequestration potential of this natural forest ecosystem should be required through the implementation of different conservation mechanisms.
    VL  - 10
    IS  - 5
    ER  - 

    Copy | Download

Author Information
  • Forestry Department, Natural and Environmental Science Faculty, Wollega University, Gimbi, Ethiopa

  • Sections