This week’s blogpost will focus on the role of citizens in
water resource assessment. Very often water resource assessments are carried
out solely by experts (e.g. scientists and government employed consultants).
This may lead to exclusion of local and often indigenous people in the process
of decision making, rendering them on the receiving end of unwanted and
negative impacts (examples). However, there have been successful cases of incorporating
the local communities in the assessment of water resources. Not only did this
allowed the contribution of local knowledge, it also empowered the locals in
ways that have not been practiced before! Over the next few posts I will
introduce examples of citizen science at work in the field of hydrology. This
week, let’s focus on how the participatory monitoring programme in Tanzania has
succeeded.
In Tanzania a large dam had been repeatedly proposed at Stiegler’s
Gorge and it could have significant impacts on the floodplain lakes that
support major socio-economic activities and livelihoods of the local
communities (Figure1 and 2). This takes places against the backdrop of
increasing dominance of developing countries such as China and Brazil in the
water and hydropower industry in Africa (McDonald
et al 2009). For example, in this BBC news article, it hints
at China becoming the ‘Africa’s new colonial master’ as China infiltrates into
industries ranging from cotton, shoe-making and construction of hydropower
stations. According to Briscoe
(2010), these emerging countries do not necessarily abide by the guidelines
of World Commission on Dams (WCD) and pay less attention to the socio-economic
and environmental needs of the locals.
Figure1. Map of the study area.
There are around 100,000 inhabitants likely to be affected
by this development. Historically, during the wet season, the peak discharge
allows the threshold that parts the lakes from the river (known as ‘Kingo’
Swahili) to be surpassed (Hamerlynck
et al. 2011). However, with the proposed dam, the water source of the
floodplain lakes will diminish. As the lakes provide income, drinking water and
food source (fish) and are also of high cultural values with folklores that
embed deeply in the spirituality of the locals (Duvial
et al 2007), its socio-economic implications are significant. Furthermore,
the adjacent forests which rely on the lakes are important biodiversity hotspot
(Myer et al 2000)
and provide fuelwood and wooden products for locals. With potential relinquished
connectivity, little nutrients and organisms will be exchanged, further
exacerbating the already deteriorating biodiversity.
In light of the potential impacts of the proposed dam on the
wider communities and ecosystem, two approaches have been adopted to increase hydrological
data collection. One is the use of sophisticated monitoring equipment (data
loggers) funded 26.3 M$US by the Worldbank through the River Basin Management
and Small-scale Irrigation Improvement Project (RBMSIIP) across 43 stations,
the other is the implementation of a participatory monitoring system where
locals are trained to do daily readings of stageboards across 8 sites. The study
(Duvial
et al 2013) shows the use of data logger have produced poor results of
the while the data yielded from community efforts are much more consistent and
of better quality. This is because there was a lack of funding for the maintenance
and consistent download of data from the data logger while the latter through
consistent workshops and feedbacks allowed efficient sharing of local and
scientific knowledge. It informs both the locals and government of the
significance of the flood and improved the relationships between the locals,
local government and the national water ministry.
In sub-Saharan Africa, despite the increasing popularity of the
IWRM concept, there remains a large gap that needs to be bridged between the
theory and reality (Garcia
2008). One might wonder why this is the case. Well given that one of the
main ethos of IWRM is to allow fair use of water resources, it follows that ‘equitable
access to knowledge about the resource use options between different kinds of
stakeholders’ is a prerequisite of IWRM. However in reality it is almost always
the case that information is generated and shared asymmetrically, with powerful
stakeholders such as the government, hydropower and commercial agriculture
actors having the most data and information (Miranda
et al 2011). This case study shows by
involving the less powerful stakeholders in the process of water resource assessment,
a more just and equitable outcome is possible!
One small step towards ‘Integrated Water Resource Management’,
one giant leap for the people in Tanzania
indeed!
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