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Effect of Human Activities on the Degradation of Vegetation Cover in the Sudano-Guinean Savannahs of Adamaoua, Cameroon

Received: 26 July 2023    Accepted: 21 August 2023    Published: 31 August 2023
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Abstract

The high savannahs of Guinea are highly diverse and play an important role in maintaining biodiversity. However, they are periodically subjected to various pressures that sometimes have a negative impact on the productivity of these ecosystems. The aim of this study was to assess the impact of logging and bush fires on the regeneration dynamics of plant species in the high savannahs of Adamaoua, Cameroon. To this end, 18 square plots, each measuring 10 metres on a side, were delimited in both a shrub and tree savannah, following a randomised block experimental set-up with the different anthropogenic actions applied as treatments (logging without fire, logging with fire and control). During the two years of experimentation, the rate of erosion and biological degradation were assessed by simple observation, as well as some anthropisation indices. The results showed that 100% of the sites where wood was cut without fire (CSF) and cut with fire (CAF) had a flat surface in the tree savannas, unlike the shrub savannas where only the CAF and the control site (T) were all 66.67% flat. In the shrub savannah, zero erosion had the same rate (66.67%) for the three different treatments. However, it was 100% for the CSF treatments, 66.67% for the control sites and 33.33% for the CAF sites in the shrub savannas. The fine structure is represented in all treatments; it is 100% in the CAF treed savannah treatments and 66.67% in the CSF shrub and tree savannah treatments. Ground cover by vegetation is very high, at 100% in the treed savannah, 66.67% in the CSF and 33.33% in the CAF and T treatments in the shrub savannah. Regardless of the type of savannah, grazing is the most common activity, with a rate of 66.67%. The presence of termite mounds (33.33%), anthills (33.33%) and wood cuttings (33.33%) is moderately represented. The rate of soil degradation by livestock is 66.67% at the CSF and CAF sites, but 100% at the T site. In the wooded savannah, this rate is 100% in the CSF and CAF sites, but T is only impacted by livestock at a rate of 66.67%. There has been a remarkable increase in the area of shrub savannah (129411 ha), and a 14.56% reduction in the area of gallery forests between 2007 and 2017.

Published in Ecology and Evolutionary Biology (Volume 8, Issue 3)
DOI 10.11648/j.eeb.20230803.12
Page(s) 55-66
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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

Anthropogenic Actions, Degradation, Sudano-Guinean Savannahs, Adamawa, Cameroon

References
[1] Agbahungba G., 2001. Situation des ressources génétiques forestières du Benin. Atelier sous régional FAO/ICRAF sur la conservation, la gestion, l’utilisation durable et la mise en valeur des ressources génétiques forestières de la zone sahélienne (Ouagadougou, 22-24 sept. 1998). Document FGR/12F. Département des forêts, FAO, Rome, Italie, 124p.
[2] Anonyme, 2015. Importance de la biodiversité et transformation du milieu physique. 2p.
[3] Aubreville A., 1958. À la recherche de la forêt de Côte d’Ivoire, Bois et Forêts des Tropiques, 57: 16-84.
[4] Auroi C., 1992. La diversité biologique. La vie en péril. Collection « dossier de l’environnement », société Suisse pour la protection de l’environnement. 37p.
[5] Bazile D., 1998. La gestion des espèces ligneuses dans l’approvisionnement en énergie des populations. Cas de la zone soudanienne du Malie. Thèse de géographie, Université de Toulouse, le Mirail, UFR de géographie, 338p.
[6] Biba H. P., 2013. Etat de dégradation et gestion des ressources pastorales dans les pâturages de la station fourragère de Wakwa (Adamaoua, Cameroun). 33p.
[7] Bode S., 2004. Pratiques pastorales et biodiversité des parcours dans le canton de Dantchandou (fakara). Mémoire de D. E. S. S, Université Abdou Moumouni, Niger, 59p.
[8] Boulaud A. L., 2014. Agriculture familiale au Cameroun, analyse comparée entre forêt et savane, Mémoire de fin d'études, Présenté pour l'obtention du diplôme d’ingénieur agronome, pp. 55-60.
[9] Boutrais J., 1983. Elevage soudanien (Cameroun, Nigeria). Paris, ORSTOM Editions, 147p.
[10] Dadem G. C., 2017. Dynamique de la végétation des savanes en relation avec l’usage des feux de brousse dans le Parc national du Mbam et Djerem (Cameroun), Thèse de Doctorat ph. D, Université de Dschang, Cameroun, pp. 120-125.
[11] Danboya E., 2013. Contribution à la mise en place d’une stratégie de gestion durable des galeries forestières dans la savane humide de l’Adamaoua (cas de la galerie de Mayo-Binou), Mémoire de Master, Université de Ngaoundéré. pp. 26-66.
[12] Defourny P., 1989. Etude de la dynamique de la végétation ligneuse en région soudano-sahélienne à partir des données Landsat MSS. Photointerprétation, 89 (2): 654-665.
[13] Dogmo., 2002. Etudes floristiques et ethnobotaniques dans un village de la zone forestière du Cameroun: cas de Nkolbibanda. Mémoire de Master, Université de Yaoundé I, Cameroun, 72p.
[14] Donfack P., 1998. Végétation des jachères du Nord-Cameroun: typologie, diversité, dynamique et production. Thèse d’Etat. Université de Yaoundé. 270 p.
[15] FAO, 2002. Evaluation des ressources forestières mondiales 2000. Rapport principal. Etude FAO Forêt, 140p.
[16] Fayé E. H., 2002. Dynamique de la régénération ligneuse durant la phase de culture dans le système de culture semi-permanente du Sud du Sénégal. Actes du colloque, 27-31 mai 2002, Garoua, Cameroun.
[17] GIEC., 2007. Bilan 2007 des changements climatiques, contribution des groupes de travail I, II, III au quatrième rapport d’évaluation du Groupe d’expert Intergouvernemental sur l’évolution du climat. Genève, Suisse, 103p.
[18] Gignoux J., Clobert J. & Menaut J. C., 1997. Alternative fire resistance strategies in savanna trees. Oecologia, 110: 576-583.
[19] Grouzis M., 1982. Restauration des pâturages sahéliens. Mise en défens et reboisement. ORSTOM, Ouagadougou, 37 p.
[20] Haiwa G., 2018. Impact de la déforestation sur la dynamique de la végétation en zone soudano-sahélienne (cas de la région de l’Extrême-Nord, Cameroun). Thèse de Doctorat ph. D, Université de Ngaoundéré, Cameroun. pp. 79-186.
[21] Hamado S., Nabsanna P. Z., Laurent B. & Daniel L., 2008. Evolution de l’occupation du sol de Ziga dans le Yatenga (Burkina Faso) à partir de photographies aériennes. Télédétection, Editions Scientifiques, 8 (1): 59-73.
[22] Hussain M., Chen D., Cheng A., Wei H. & Stanley D., 2013."Change detection from remotely sensed images: From pixelbased to object-based approaches", ISPRS Journal ofPhotogrammetry and Remote Sensing, 80: 91-106.
[23] IRZ & GTZ, 1989. Livestock farming systems in Adamawa. Research Report no1 wakwa, IRZ, + annexes.
[24] Jeltsch F., Weber G. E. & Grimm V., 2000. Ecological buffering mechanisms in savannas: a unifying theory of long-term tree-grass coexistence. Plant Ecology, 161p.
[25] Khalid E. H., Youssef B., Lahcen O. & Abdelhak L., 2022. Evaluation de l’effet des facteurs anthropiques sur la dégradation des forêts du Moyen atlas central (cas de la forêt Ain Nokra) Revue Espace Géographique et Société Marocaine Nº59, Avril 2022. p5.
[26] Mahamat A., Megueni C., Haouvang L C., Raimund K. & Oumar Mahamat Oumar., 2020. Restoration of soil physical parameters by an ecological Revitalization Technology (ReviTec) in Maroua, Far North Region, Cameroon. Int. J. Adv. Res. Biol. Sci. 7 (3): 139-151. DOI: http://dx.doi.org/10.22192/ijarbs.2020.07.03.017
[27] Maigari P., Tchobsala., Massai Tchima J., Babe N G., Bitjoka L. & Ibrahima Adamou., 2020. Variations of the Functional Leaf Traits in Some Agroforestry Woody Species of the Sudano-guinea Savannahs of Ngaoundere, Adamawa Cameroon: Effects of Plant Taxonomy, Life Forms, Habits and Habitats. Asian Journal of Research in Botany4 (4): 122-137.
[28] Ndam N., 1998. Tree regeneration, vegetation dynamics and the maintenance of biodiversity on MountCameroon: the relative impact of natural and human disturbance. Thesis, University of Wales, Bangor, UK. 278 p.
[29] Ndjidda., 2001. Structure et dynamiques des espèces ligneuses dans les zones Sud Est du Parc National de Waza. Mémoire du Diplôme d’Ingénieur des Eaux et Forêts. Université de Dschang. 62 p.
[30] Ntoupka M., 1994. Impact de la gestion de la matière organique sur le statut minéral des sols et des récoltes dans les savanes soudano-guinéennes de Ngaoundéré, Cameroun, 6p.
[31] Ntoupka M., 1999. Influence des perturbations anthropiques (pâturage, feu et coupe de bois) sur la dynamique de la savane arborée en zone soudano-sahélienne Nord du Cameroun, 226p.
[32] Peltier R., Njiti F. C., Ntoupka M., Manlay R. J., Matieu H. & Morillon V., 2007. Évaluation du stock de carbone et de la productivité en bois d’un parc à karités du Nord-Cameroun. Bois et Forêts des Tropiques, Montpellier: CIRAD, pp. 39-50.
[33] Pourtier R., 2002. Savanes africaines: des espaces en mutation, des acteurs face à des nouveaux défis. Actes du colloque Garoua Cameroun, Ndjamena, Tchad, PRASAC.
[34] Ranava D., 2015. Impact des coupes de bois et des feux de brousse sur la dynamique de la végétation des savanes soudano-guinéennes (cas de Ngaoundéré III). Mémoire de Master, Université de Ngaoundéré, pp. 36-66.
[35] Rippstein G., 1985. Etude sur la végétation de l’Adamaoua; évolution, conservation, régénération et amélioration d’un écosystème pâturé au Cameorun. Etude et synthèse de l’IEMVT, 14p.
[36] Tchobsala, 2011. Impact des coupes de bois sur la végétation naturelle de la zone périurbaine de Ngaoundéré (Adamaoua). Thèse de Doctorat ph. D, Université de Yaoundé I, Cameroun, 204p.
[37] Tchotsoua M., 2005. Evolution Récente des Territoires de l’Adamaoua central: de la spatialisation à l’aide pour un développement maîtrisé. Vol 3. Mémoire original et projet de recherche.
[38] Tchotsoua M., 2006. Évolution récente des territoires de l’Adamaoua central: de la spatialisation à l’aide pour un développement maitrisé. Université d’Orléans. École doctorale Sciences de l’homme et de la société. HDR en Géographie-Aménagement-Environnement. 267p.
[39] Walker B. H. & Noy M. I., 1982. Aspects of the stability and resilience of savanna ecosystems. In Huntley B. J. & Walker B. H. (Eds.), Ecology of tropical savannas. Ecological studies, 42p.
[40] Yonkeu S., 1993. Végétation des pâturages de l’Adamaoua (Cameroun): Ecologie et potentialités pastorales. Thèse de doctorat. Université de Rennes I.
[41] Zoumana C. J. C., 1993. Les rôles des jachères et desq cultures fourragères dans le maintien de la fertilité des terres. In: Savane d’Afrique, Terres fertiles, Acte des rencontres Internationales, Décembre 1990, Montpéllier, France, pp. 10-14.
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    Ranava Dieudonne, Maigari Pale, Massai TchimaJacob, Jean Boris Sounya, Ignatchimbie Bethlehem, et al. (2023). Effect of Human Activities on the Degradation of Vegetation Cover in the Sudano-Guinean Savannahs of Adamaoua, Cameroon. Ecology and Evolutionary Biology, 8(3), 55-66. https://doi.org/10.11648/j.eeb.20230803.12

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    Ranava Dieudonne; Maigari Pale; Massai TchimaJacob; Jean Boris Sounya; Ignatchimbie Bethlehem, et al. Effect of Human Activities on the Degradation of Vegetation Cover in the Sudano-Guinean Savannahs of Adamaoua, Cameroon. Ecol. Evol. Biol. 2023, 8(3), 55-66. doi: 10.11648/j.eeb.20230803.12

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    Ranava Dieudonne, Maigari Pale, Massai TchimaJacob, Jean Boris Sounya, Ignatchimbie Bethlehem, et al. Effect of Human Activities on the Degradation of Vegetation Cover in the Sudano-Guinean Savannahs of Adamaoua, Cameroon. Ecol Evol Biol. 2023;8(3):55-66. doi: 10.11648/j.eeb.20230803.12

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  • @article{10.11648/j.eeb.20230803.12,
      author = {Ranava Dieudonne and Maigari Pale and Massai TchimaJacob and Jean Boris Sounya and Ignatchimbie Bethlehem and IbrahimaWanié Sago and Tchobsala and Ibrahima Adamou},
      title = {Effect of Human Activities on the Degradation of Vegetation Cover in the Sudano-Guinean Savannahs of Adamaoua, Cameroon},
      journal = {Ecology and Evolutionary Biology},
      volume = {8},
      number = {3},
      pages = {55-66},
      doi = {10.11648/j.eeb.20230803.12},
      url = {https://doi.org/10.11648/j.eeb.20230803.12},
      eprint = {https://article.sciencepublishinggroup.com/pdf/10.11648.j.eeb.20230803.12},
      abstract = {The high savannahs of Guinea are highly diverse and play an important role in maintaining biodiversity. However, they are periodically subjected to various pressures that sometimes have a negative impact on the productivity of these ecosystems. The aim of this study was to assess the impact of logging and bush fires on the regeneration dynamics of plant species in the high savannahs of Adamaoua, Cameroon. To this end, 18 square plots, each measuring 10 metres on a side, were delimited in both a shrub and tree savannah, following a randomised block experimental set-up with the different anthropogenic actions applied as treatments (logging without fire, logging with fire and control). During the two years of experimentation, the rate of erosion and biological degradation were assessed by simple observation, as well as some anthropisation indices. The results showed that 100% of the sites where wood was cut without fire (CSF) and cut with fire (CAF) had a flat surface in the tree savannas, unlike the shrub savannas where only the CAF and the control site (T) were all 66.67% flat. In the shrub savannah, zero erosion had the same rate (66.67%) for the three different treatments. However, it was 100% for the CSF treatments, 66.67% for the control sites and 33.33% for the CAF sites in the shrub savannas. The fine structure is represented in all treatments; it is 100% in the CAF treed savannah treatments and 66.67% in the CSF shrub and tree savannah treatments. Ground cover by vegetation is very high, at 100% in the treed savannah, 66.67% in the CSF and 33.33% in the CAF and T treatments in the shrub savannah. Regardless of the type of savannah, grazing is the most common activity, with a rate of 66.67%. The presence of termite mounds (33.33%), anthills (33.33%) and wood cuttings (33.33%) is moderately represented. The rate of soil degradation by livestock is 66.67% at the CSF and CAF sites, but 100% at the T site. In the wooded savannah, this rate is 100% in the CSF and CAF sites, but T is only impacted by livestock at a rate of 66.67%. There has been a remarkable increase in the area of shrub savannah (129411 ha), and a 14.56% reduction in the area of gallery forests between 2007 and 2017.},
     year = {2023}
    }
    

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  • TY  - JOUR
    T1  - Effect of Human Activities on the Degradation of Vegetation Cover in the Sudano-Guinean Savannahs of Adamaoua, Cameroon
    AU  - Ranava Dieudonne
    AU  - Maigari Pale
    AU  - Massai TchimaJacob
    AU  - Jean Boris Sounya
    AU  - Ignatchimbie Bethlehem
    AU  - IbrahimaWanié Sago
    AU  - Tchobsala
    AU  - Ibrahima Adamou
    Y1  - 2023/08/31
    PY  - 2023
    N1  - https://doi.org/10.11648/j.eeb.20230803.12
    DO  - 10.11648/j.eeb.20230803.12
    T2  - Ecology and Evolutionary Biology
    JF  - Ecology and Evolutionary Biology
    JO  - Ecology and Evolutionary Biology
    SP  - 55
    EP  - 66
    PB  - Science Publishing Group
    SN  - 2575-3762
    UR  - https://doi.org/10.11648/j.eeb.20230803.12
    AB  - The high savannahs of Guinea are highly diverse and play an important role in maintaining biodiversity. However, they are periodically subjected to various pressures that sometimes have a negative impact on the productivity of these ecosystems. The aim of this study was to assess the impact of logging and bush fires on the regeneration dynamics of plant species in the high savannahs of Adamaoua, Cameroon. To this end, 18 square plots, each measuring 10 metres on a side, were delimited in both a shrub and tree savannah, following a randomised block experimental set-up with the different anthropogenic actions applied as treatments (logging without fire, logging with fire and control). During the two years of experimentation, the rate of erosion and biological degradation were assessed by simple observation, as well as some anthropisation indices. The results showed that 100% of the sites where wood was cut without fire (CSF) and cut with fire (CAF) had a flat surface in the tree savannas, unlike the shrub savannas where only the CAF and the control site (T) were all 66.67% flat. In the shrub savannah, zero erosion had the same rate (66.67%) for the three different treatments. However, it was 100% for the CSF treatments, 66.67% for the control sites and 33.33% for the CAF sites in the shrub savannas. The fine structure is represented in all treatments; it is 100% in the CAF treed savannah treatments and 66.67% in the CSF shrub and tree savannah treatments. Ground cover by vegetation is very high, at 100% in the treed savannah, 66.67% in the CSF and 33.33% in the CAF and T treatments in the shrub savannah. Regardless of the type of savannah, grazing is the most common activity, with a rate of 66.67%. The presence of termite mounds (33.33%), anthills (33.33%) and wood cuttings (33.33%) is moderately represented. The rate of soil degradation by livestock is 66.67% at the CSF and CAF sites, but 100% at the T site. In the wooded savannah, this rate is 100% in the CSF and CAF sites, but T is only impacted by livestock at a rate of 66.67%. There has been a remarkable increase in the area of shrub savannah (129411 ha), and a 14.56% reduction in the area of gallery forests between 2007 and 2017.
    VL  - 8
    IS  - 3
    ER  - 

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Author Information
  • Wakwa Agricultural Research Center, Institute of Agriculture Research for Development, Ngaoundere, Cameroon

  • Department of Biological Sciences, Faculty of Sciences, the University of Maroua, Maroua, Cameroon

  • Wakwa Agricultural Research Center, Institute of Agriculture Research for Development, Ngaoundere, Cameroon

  • Wakwa Agricultural Research Center, Institute of Agriculture Research for Development, Ngaoundere, Cameroon

  • Wakwa Agricultural Research Center, Institute of Agriculture Research for Development, Ngaoundere, Cameroon

  • Department of Life and Earth Sciences, HigherTteachers’ Trainingcollege, the University of Maroua, Maroua, Cameroon

  • Department of Biological Sciences, Faculty of Sciences, the University of Maroua, Maroua, Cameroon

  • Department of Biological Sciences, Faculty of Sciences, the University of Ngaoundere, Ngaoundere, Cameroon

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