
Thursday, 29 October 2015
Thursday, 22 October 2015
Groundwater's Biggest Problem: Uneven Distribution Part 1
As shown in Figure 3, SSA has approximately three times the
per capita groundwater availability of China and nearly six times that of India,
the world's two biggest players in groundwater-fed irrigation systems (Giordano
2006). However, only 6% of cultivated
land in Africa is irrigated (PAVE Irrigation Systems 2015). One of the reasons
it has not been exploited to data is because Africa’s groundwater distribution
is highly variable, with the majority of groundwater storage in North Africa. An intermix of factors have caused this spatial
variability including geology and climate.
Geology
Supplies are dependent upon the ability of underlying rock to store and transfer water. A
large proportion groundwater is located in hard rock areas or at extremely deep
distances below the ground, making abstraction difficult or costly. Giordano
(2006) outlines four geological zones, of which Africa is made up of (see
Figure 5 for their distribution across the region), that alter the ability of
the ground to store and transfer water. A summary of these zones can be found
in Table 1.
Table 1: Four geological zones across SSA, information summarized
from Giordano (2006)
Hydrogeologic Zone
|
% of Region
|
Potential as a Groundwater Reserve
|
Crystalline Basement Rock
|
40
|
Poor supply source for groundwater due to its low
transmissivity.
|
Consolidated Sedimentary Rock
|
32
|
Can hold large amounts of water so high potential.
|
Unconsolidated Sediments
|
22
|
Groundwater is often held in hold in unconstrained
conditions within sands and gravels, and often found in river beds, so easily
accessible. However, “many African river systems are typified by fine and
very fine sediments, rather than coarse sand and gravel, reducing extraction
possibilities” (312).
|
Volcanic Rock
|
6
|
Can produce high groundwater yields and supply springs.
|
However, hard rock aquifers should not be totally written
off. Even those with low yield potential may be suitable for small-scale
irrigation. For a community water supply fitted with a hand pump, only a
sustained supply of >0.1 l s-1 is needed, in comparison to >51 l s-1 for
boreholes for commercial irrigation schemes (MacDonald et al. 2012). Supplies or recharge rates may mean that these larger
yields may be unreachable, but could hold potential for smaller scale, less
intensive activities.
Climate
Groundwater also depends on recharge potential, in order to
make it a sustainable resource. Unfortunately, due to past and current climatic
conditions, groundwater distribution is highly correlated with rainfall
patterns, meaning it tends to be highest in areas of high rainfall and lowest in
areas of low rainfall (Calow and MacDonald 2009). This depletes the
human value of groundwater.
Depth to
Groundwater
The depth of the groundwater below the surface is again,
unsurprisingly, highly variable. Depth affects both the practical accessibility
of the resource, and whether it is economically viable (MacDonald et al. 2012). Levels deeper than 50m are
not easily accessible by a hand pump and for those >100m, the cost of
extraction increases dramatically because more advanced drilling equipment is
required (MacDonald et al. 2012).
Thursday, 15 October 2015
Groundwater's Climate Resilience
Global climate change is expected to affect both temperature
and precipitation across Africa. Temperatures are expected to rise by 3-4°C,
increasing evapotranspiration rates, whilst mean annual rainfall is predicted
to vary by up to ±10-20% (Carter and Parker 2009). Both inter-annual and
seasonal variability in rainfall patterns are likely to increase in a region
already characterized by variable rainfall (Carter and Parker 2009). Extreme
weather events such as flooding and drought are set to intensify (Kusangaya et
al. 2013). All of this contributes to making Africa’s water supply even
more difficult to manage. Increasing the reliability of supply is key. Africa’s
agriculture is particularly vulnerable to climate change due to its widespread
reliance on rain fed agriculture, its extreme intra and inter-season climate
variability and recurrent dry and wet seasons, coupled with its extensive
poverty and consequent low ability to adapt (IPCC 2014b).
More than 95% of food grown in Sub-Saharan Africa is
rain-fed. Climate change, therefore, threatens food security because surface
water supplies are more likely to be affected by it than groundwater. They are significantly
affected by changes in rainfall (Pavelic et
al. 2013). With most areas of Africa expected to face decreases in
precipitation, this decrease will be passed onto surface water supplies,
particularly run-off (Ziervogel et al. 2010).
Streamflow projections show they are likely to decrease under climate change –
river runoff faces declines of 10-30% in the dry tropics and most conclusions
have them set to decrease more generally overall in Africa (Kusangaya et al. 2013). The magnitude of this decrease
is uncertain. Additionally, evaporative increases, due to temperature
increases, could reduce outflows from reservoirs (Kusangaya et al. 2013). When faced with drought or
prolonged dryness, surface water supplies are prone to fail and can prove insufficient
(Calow and MacDonald 2009). Changes is surface water supply have proved rather
destructive in the past, leaving people without access to water, and
consequently food (deWit and Stankiewicz 2006). The vulnerability of surface
water to climatic changes means they are not a suitable resource to rely upon in
the uncertain face of global climate change.
A well dug in Kunjuru - the prolonged drought has meant that the river has dried up
Source: UN Multimedia
Deep groundwater stores generally prove to be more resilient to changes in rainfall - its “buffering capacity” makes it a more consistent source of water for irrigation in a region facing increasingly variable precipitation (Calow and MacDonald 2009: 1, Conway et al. 2008). Sub-surface aquifers' water storage capacity is often greater than their yearly recharge, meaning they are able to continue to supply water even when rainfall supply is low for an extended period (Calow and MacDonald 2009). Groundwater recharge can be stored for several decades (MacDonald et al. 2012). During periods of prolonged drought, deep groundwater supplies prove more reliable than their shallow counterparts and surface supplies (Calow and MacDonald 2009). Climate change will also likely result in an intensification of precipitation, which will benefit groundwater recharge. The relationship between rainfall and recharge is non-linear, meaning that extreme rainfall is required to generate significant groundwater storage, which is required for agricultural uses (Taylor et al. 2013, Calow and MacDonald 2009).
Groundwater stores are not immune to the effects of climate change. However, it does appear to be a better insulated water supply, therefore proving more reliable water supply for agricultural needs (Kusangaya et al. 2013).
We need a sustainable solution
Agriculture is by far the most dominant motivation for freshwater withdrawals in Africa, accounting for 83.1% of withdrawals (Wada et al. 2011). So finding a sustainable solution seems vital in order to improve and maintain food security in a region that is set to potentially be drastically affected by climate change and continues to suffer from vast socio-economic issues.
Source: http://www.un.org/africarenewal/magazine/april-2011/investing-africas-farms-—-and-its-future
Groundwater is proposed by many as an abundant, resilient and less variable alternative to rain-fed irrigation, especially in particularly seasonal and variable climates, predicted to be exacerbated by climate change (Pavelic et al. 2013).
Source: http://www.hydrology.nl/iahpublications/201-groundwater-cartoons.html
Over the next few months (and perhaps longer!), this blog seeks to explore the possibility of, and make a case for, groundwater as a future tool and resource for agricultural production and irrigation in Africa.
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