PRIORITIES IN BIODIVERSITY CONSERVATION IN BARAK VALLEY WITH REFERENCE TO INNER-LINE RF, INDIA

Authors

  • Dr. Nilam Basumatary Assistant Professor, Department of Zoology Cachar College, Silchar, Assam

DOI:

https://doi.org/10.53555/f04fse91

Keywords:

North-eastern region, biodiversity, inner-line reserve forest, conservation, Wildlife protection.

Abstract

The Northeastern Region of India, comprising Arunachal Pradesh, Assam, Manipur, Meghalaya, Mizoram, Nagaland, Sikkim, and Tripura, is physiographically divided into the Eastern Himalaya, the northeastern hill ranges, and the Brahmaputra-Barak valley plains. Spanning 262,180 km², this region forms a major biodiversity hotspot at the Indo-Burma and Eastern Himalayan junction, supporting nearly 25% of India’s flora, over 14,000 species, and 3,169 endemics. Within this landscape, the Barak Valley of Assam represents an ecologically significant domain marked by extensive forest cover and a network of protected areas. The Inner-Line Reserve Forest (ILRF), one of Assam’s largest reserve forests, covers approximately 44,266 hectares, bordering Mizoram and Manipur, and historically supports diverse fauna, including five primate species. Declining awareness among local communities and delayed implementation of conservation actions have contributed to progressive wildlife depletion. Land-use and land-cover assessments from 1998 to 2011 indicate a clear reduction in forest area within and around ILRF, reflecting broader ecological degradation across the Barak Valley. Compounding these threats is the limited legal protection afforded to many species. While the Wildlife (Protection) Act, 1972 categorizes fauna under Schedules I-V and plants under Schedule VI, effective conservation remains skewed toward Schedule I and portions of Schedule II. This disparity fosters public misperception and neglect of lower-tier species. Consequently, there is an urgent need for policymakers to re-evaluate conservation strategies in light of evolving land-use patterns, climate change, and rapid urbanisation to safeguard the region’s threatened biodiversity.

 

References

[1].Barbhuiya, R. A., Talukdar, N. R., & Choudhury, P. (2022). Time budget and activity pattern of capped langur (Trachypithecus pileatus) in Barail Wildlife Sanctuary, Assam, India. Ecology, Environment and Conservation https://doi. org/10.53550/eec, v28i04s.

[2].Barooah, C., & Sarma, L. (2016). Vertebrates of Assam: a checklist with IUCN status. Assam Science Technology and Environment Council.

[3].Caviedes, J., & Ibarra, J. T. (2017). Influence of anthropogenic disturbances on stand structural complexity in Andean temperate forests: implications for managing key habitat for biodiversity. PloS one, 12(1), e0169450.

[4].Choudhury, A. S., & Choudhury, P. (2017). Conservation concern to the primates outside protected areas: A study from Hailakandi, Assam, India. Journal of Entomology and Zoology Studies, 5(3), 499-506.

[5].Das, T., & Das, A. K. (2020). Agrobiodiversity in Northeast India: A Review of the Prospects. Socio-economic and Eco-biological Dimensions in Resource use and Conservation: Strategies for Sustainability, 117.

[6].Dattagupta, S., & Gupta, A. (2016). Non-timber forest product (NTFP) in northeast India: an overview of availability, utilisation, and conservation. Bioprospecting of Indigenous Bioresources of North-East India, 311-322.

[7].Deb, M., Roychoudhury, S., Bhattacharjee, P. C., Sharma, I., Nautiyal, S., & Sláma, P. (2019). DISTRIBUTION OF WESTERN HOOLOCK GIBBONS AND NUTRITIONAL STATUS OF FOOD PLANTS IN CACHAR DISTRICT OF ASSAM, INDIA: REACHING OUT TO LOCAL COMMUNITIES FOR CONSERVATION. Acta Universitatis Agriculturae et SilviculturaeMendelianaeBrunensis, 67(1).

[8].Gogoi, H., Purkayastha, J., & Roychoudhury, S. (2023). Avian diversity in the paddy field ecosystem surrounding the Assam University campus in Silchar during the rainy season. Int. J. Exp. Res. Rev, 34, 120-137.

[9].Gupta, A. (2018). Integrated Water Resources Management in the Biodiversity-rich, high rainfall, northeastern region of India: Issues and challenges. Экологическая, промышленная и энергетическая безопасность-2018, 18-21.

[10].Jena, A. K. (2024). Tree plantation for implementing the land utilisation policies incorporates with sustainable development towards environmental concerns in Assam, India. Land Use Policy, 141, 107085.

[11].Kasbekar, S. P., Kumara, H. N., Bhor, S. S., Babu, S., & Karunakaran, P. V. (2024). Size and canopy characteristics of community reserves determine primate occupancy in the state of Meghalaya, India, and implications for its conservation. Folia Primatologica, 96(1-2), 1-19.

[12].Kehie, P., & Pfoze, N. L. (2017). Phytochemical and ethnopharmacological overview of endangered Homalomenaaromatica Schott: An aromatic medicinal herb of Northeast India. Indian Journal of Natural Products and Resources (IJNPR)[Formerly Natural Product Radiance (NPR)], 8(1), 18-31.

[13].Mane, A. M., Prabakaran, N., & Manchi, S. S. (2019). Floral diversity, composition, and recruitment on the karstland of Baratang Island, India. Ecological Complexity, 37, 47-54.

[14].Marak, C. R., Marak, C. C., Sarkar, B. C., Dabral, A., Apshahana, K., Ananda, A., ... & Chakravarty, S. (2024). A Baseline Study of A’chikHomegardens in North-East India: Structure, Composition and Utilisation. Human Ecology, 52(3), 563-577.

[15].Mishra, N., & Behera, S. K. (2019). Tree ferns and giant ferns in India: their significance and conservation. In Environmental Concerns and Sustainable Development: Volume 2: Biodiversity, Soil and Waste Management (pp. 45-62). Singapore: Springer Singapore.

[16].Nath, A. J., Sileshi, G. W., & Das, A. K. (2018). Bamboo-based family forests offer opportunities for biomass production and carbon farming in North East India. Land Use Policy, 75, 191-200.

[17].Rajkumar, M. (2022). BIODIVERSITY CONSERVATION POTENTIAL OF AGROFORESTRY SYSTEMS. Agroforestry and Opportunities in Value Addition, 91.

[18].RAMADHINI, K. (2023). KOMPOSISI PAKAN OWA JAWA (Hylobates moloch) DAN LUTUNG JAWA (Trachypithecus auratus) DI PUSAT PENDIDIKAN KONSERVASI ALAM (PKKA) BODOGOL, TAMAN NASIONAL GUNUNG GEDE PANGRANGO, JAWA BARAT (Doctoral dissertation, UNIVERSITAS NEGERI JAKARTA).

[19].Reang, D., De, A., & Das, A. K. (2020). Heterogeneous landscape assessment using multi-temporal LISS4 and hybrid approach: A case study in Barak Valley, India. Indian Journal of Ecology, 47(3), 842-848.

[20].Singh, R. R. (2017). Tipaimukh high dam on the Barak river: Conflicting land and people. In Water Conflicts in Northeast India (pp. 231-241). Routledge India.

[21].Sinha, V., Glémet, R., Mustafa, G., & IUCN, B. G. (2018). Benefit-sharing opportunities in the Meghna Basin. Profile and preliminary scoping study, Bangladesh and India. IUCN: Bangkok, Thailand.

[22].Takacs, D. (2017). Are Koalas fungible? Biodiversity offsetting and the law. NYU Envtl. LJ, 26, 161.

[23].Talukdar, N. R., Singh, B., & Choudhury, P. (2018). Conservation status of some endangered mammals in Barak Valley, Northeast India. Journal of Asia-Pacific Biodiversity, 11(2), 167-172.

[24].Tripathi, R. S., Roy, A., Kushwaha, D., Lalnunmawia, F., Lalnundanga, L. H., Lalnunzira, C., & Roy, P. S. (2016). Perspectives of forest biodiversity conservation in Northeast India. Journal of Biodiversity, Bioprospecting and Development, 3(2), 1-9.

[25].Trivedi, S., & Bharucha, E. (2023). Identification, prioritisation, and management of biodiversity hotspots: a case study of Western Ghats of Maharashtra, India. Journal of Threatened Taxa, 15(4), 22990-23004.

Downloads

Published

2025-01-23

How to Cite

PRIORITIES IN BIODIVERSITY CONSERVATION IN BARAK VALLEY WITH REFERENCE TO INNER-LINE RF, INDIA. (2025). EPH-International Journal of Applied Science, 11(1), 73-79. https://doi.org/10.53555/f04fse91