The beautiful Siang (photo by Anirban Datta-Roy) |
The river
To begin with, it
is difficult to even imagine that the Yarlang Tsangpo river that
starts from Manasarovar lake near Mount Kailash (22,020 ft) and flows
easterly about 1625 km across Tibet, the Siang river that flows
north–south in Arunachal Pradesh and the Brahmaputra river that
flows westerly in Assam are one and the same. The river flows through
the deepest gorge in the world (about 5000 m deep) and bends towards
the south-east due to the Namchi Barwa peak (25,445 ft) to enter
India at Gelling in Arunachal Pradesh. The terrain where the river
flows and turns towards India is so rugged that the discovery that
the Tsangpo is in fact the Siang was only made a little over a
hundred years back by Kinthup, a Pundit who meticulously explored
Tibet.
The projects
This majestic river that flows through some of the least traversed areas in the world and through relatively undisturbed forests in Arunachal Pradesh is now severely threatened by 44 hydropower projects that are planned on the river and its tributaries. The length of the Siang river in Arunachal Pradesh is about 290 km and if even just the three larger projects among these are undertaken, there will be no free flowing water left! About two-thirds of the river will be converted into a reservoir with only a third left as free flowing water regime. This will have serious irreversible consequences for wildlife, forests and people of both Arunachal Pradesh and Assam downriver. While about 24,000 hectares of forest will be directly affected due to the 44 projects, other forests will also be affected due construction activities that will last for at least 10 – 15 years that will also open up access to hitherto relatively undisturbed forests and wildlife.
A 'cumulative impact study' including downstream impacts was undertaken by R S Envirotech Technologies for the Central Water Commission and presented in a report in December 2013. This study systemmatically listed the biodiversity values of the Siang river basin and assessed the cumulative impacts of the projects. It was acknowledged that while direct loss of 24,000 ha of forest due to submergence would occur, 'nibbling' effects of the projects during construction works, quarrying and road-building would lead to further major loss of forests. It was also reported that these reservoir based projects will affect aquatic life migration due to the conversion of lotic environment to lentic habitats causing species extirpations. Downstream impacts of these projects were also evaluated and listed as causing drastic daily fluctuations in river flows downstream, loss of fisheries, changes in wetland ecology in the floodplains, impacts on agriculture, impacts on livelihoods of people and also increased flood vulnerability. For instance, it was estimated that daily water level fluctuations in the D'Ering wildlife sanctuary will be more than 23 feet in the non-monsoon seasons!
Notwithstanding the information provided, the report falls short of various aspects in listing the 'cumulative' impacts of the 44 projects planned and more importantly the recommendations of the study completely contradict their findings. Firstly, 'Cumulative impact is the impact on the environment which results from the incremental impact of the acton when added to other past, present and reasonably foreseeable future actions regardless of what agency (federal or non-federal) or person undertakes such other actions (as defined in CEQ 1987, 1508.7)'. Here, 'impacts' include ecological, aesthetic, historic, cultural, economic, social, or health, whether direct, indirect or cumulative (CEQ 1987). The cultural, social and aesthetic impacts of the projects have been completely ignored in the study. Several collateral impacts of the projects such as those due to sand and boulder mining and road construction which often have been shown to have disastrous effects on river ecology (Padmalal et al. 2008) have been mentioned in the report but the recommendations made to control these effects are cursory. The report has also not assessed the damage that villages downstream in Assam will incur and has only focused on the impacts in few urban places (Dibrugarh, Bokaghat, Tezpur and Guwahati).
The most ludicrous aspect of the report is that after mentioning the disastrous impacts of large-scale hydropower projects, such as direct and indirect loss of forests and wildlife, critically affecting migration of fish species and thereby causing species extirpations and several downstream impacts, the recommendations of the report are to drop 15 small-scale projects (capacity less than 100 MW). The three larger projects, Siang Upper Stage I & II and Siang Lower Stage, will lead to a forest loss of over 18,000 ha and together are of about 12,500 MW capacity. Overall, the 44 projects are of 18,300 MW capacity and will lead to a forest loss of over 24,000 ha whereas the report recommends dropping of 15 projects that constitute 473 MW and will cause a forest loss of 334 ha; a mere 2.6 % of the capacity and 1.4 % of the forest loss!
The reality
In North-east India, the people and the wildlife, both terrestrial and aquatic are intricately dependent on the rivers. The Siang or the Brahmaputra that supports livelihoods of millions of people in India and the biocultural landscape it is located in is being envisaged to be converted into a powerhouse for electricity generation for others who have no stake in it. The communities that live along the river are majorly dependent on the river in many ways; they harvest an array of aquatic flora and fauna, they undertake agriculture which is dependent on the annual floods and recession and they use the river for transport. The natural annual changes in the river water levels are also important to the people in Assam and they have adapted to these fluctuations over several decades and ill-planned hydropower projects can disturb this delicate balance. It is high time that we realise that such projects can cause irrepairable physical, social, economic and ecological damage such as the one we recently witnessed in Uttarakhand just last year.
References:
- Padmalal, D., Maya, K., Sreebha, S. & Sreeja, R. (2008) Environmental effects of river sand mining: a case from the river catchments of Vembanad lake, Southwest coast of India. Environmental Geology, 54(4): 879-889.
- Council on Environmental Quality (CEQ) (1987) Regulations for Implementing the Procedural Provisions of the National Environmental Policy Act. 40 CFR Parts 1500 – 1508.
- Yashwant, S. (2013) Brahmaputra and the temples of doom. Infochange News & Features.
- D'souza, R. (2013) Unquiet flows the Brahmaputra. The Hindu, Business line, November 4, 2013.
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