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Water Avaliability and Use
The total water potential of the region can be
represented by the sum of the mean discharge rates of the various tributaries,
estimated in 101,441 m3/s. The specific mean discharge rate
for the region is 26 l/s/km2 in the Brazilian section, varying
widely in the sub-basins, with values between 14 and 52 l/s.km2
(Figure 2).
The current situation of the Hydrographic Region of
the Amazon as regards availability and demand of water is shown in Table
3.
Figure 2
Specific discharge rates by sub-basin |
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The principal water demand in the region is for irrigation,
followed by human and livestock use. (Figure 3).
Figure 3
Distribution of demand |
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The highest water usage occurs in the sub-basins of the
Madeira, Tapajós and Xingu rivers, and is primarily for water for
irrigation purposes (91.5 % of the total demand) (Figure 4). The human
demand represents just 4.1%. Generally, the estimated levels of consumption
are relatively insignificant given the water availability in the respective
sub-basins. In fact, the highest demand, which occurs in the Tapajós/Juruena/Teles
Pires basin, represents only 0.67% of the average availability. As such,
no water deficits have been identified in the region, at this level of
analysis.
An overview of the main consumption types for water
use shows: estimated human public water use: 8.44 m3/s,
which represents only 4,1% of total demand. Approximately 45 % of the
population of the basin is concentrated in the sub-basins of the Negro
and Madeira rivers. The city of Manaus alone has a population of 1,405,835
inhabitants; Industrial use: Total demand for industrial use is 1.66 m3/s.
Although relatively insignificant in a national context, industry is responsible
for around 5% of the regional GDP, thanks to fiscal incentives. The specialization
of some centers to cater to exports markets is particularly noteworthy.
With the exception of Santarém and Manaus, that produce goods for
the local market, all the others are specialized; Irrigation: Demand for
water for irrigation purposes, amounting to 190.34 m3/s,
represents 91.5 % of the total water demand. The majority of this consumption
is for the irrigation of rice fields, concentrated in the sub-basins of
the Madeira, Tapajós and Xingu rivers. Of the three million hectares
of cultivated lands in the Amazon basin, approximately 90% are in these
sub-basins; Livestock: Water consumption for livestock is 7.61 m3/s,
corresponding to 3.7 % of the total demand.
Figure 4
Distribution of demand by sub-basin. |
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As regards underground water, in the northern and southern
regions of the basin there are igneous rocks, which are covered by a thick
layer of deposits left from erosion, with intermittent aquifers in which
the volume and circulation of water depends on the extent and depth of
the low permeability layers in the rock. The productivity of the wells
in this region is extremely variable, averaging around 10,000 l/hr.
The alluvial and fluviomarine sediment deposits are
widely distributed throughout the area, particularly in the central and
eastern sections. They form porous aquifers that are exploited mainly
in the towns of Manaus, Belém, Santarém and the Island of
Marajó, through piped wells, borehole systems and Amazon wells.
The yield of these aquifers is extremely variable (10,000 to 100,000 l/hr)
and the water often needs to be treated to correct the pH-level and the
high iron concentration.
The main non-consumption use is Power Generation: The
Amazon basin has considerable hydroelectric power generating potential
that has yet to be explored, estimated in 485,426.8 gWh. Of this amount,
only 0.46% is currently in operation or under construction and 32.8% is
inventoried or with feasibility studies in progress. The main hydroelectric
power plants in operation in the basin are those of Samuel (RO), Balbina
(AM), Curuá-Uma (PA).
Considering the estimated hydroelectric power generating
potential in the whole of Brazil (1,138,288 gWh), the Amazon basin represents
42.6% of this total. Despite its great potential, factors such as the
wide dispersion of the urban centers in the basin, the great distances
between the areas of high power generation potential and the main consumer
centers in the other regions of the country, in addition to the environmental
liability resulting from the flooded areas, mean that the region’s
electricity is, at present, supplied by thermoelectric power.
Of a total of 377 power generating units that exist
in the states that are totally or partially in the Hydrographic Region
of the Amazon River, 331 are thermoelectric power plants, 37 are small
hydroelectric units and only 9 are hydroelectric power plants.
In general terms, the Amazon River is highly navigable, with low declivities
between 2 to 3 cm/km. This characteristic, typical of rivers in plains,
with reduced declivity and low flow speeds, extends to many of its main
tributaries, such as the Purus, Madeira Icá and Japurá rivers.
Others, such as the Tapajós, Xingu and Trombetas, have the characteristics
of plateau rivers.
The concentration of decomposable organic matter in
the region is 277 tons BOD5/day,
which represents 3.7% of the national total.
Brazil has a network of approximately 40,000 km of permanently
navigable waterways, of which 26,000 km are already barely navigable.
Just in the Amazon basin, there are 25,000 km of waterways, representing
over 60% of the country’s navigable waterway network. The close
relationship between the size of the Amazon basin and the wealth of its
hydrographical network becomes more evident when extreme hydrological
events occur. In this context, droughts and low discharge rates during
dry seasons compromise the navigability of some stretches of the waterway
network. In the rainy season, vast areas of meadows become flooded, influencing
the dynamics of diverse species of fauna and flora, with high environmental
relevance and contributing to the conservation of the biodiversity of
the Amazon basin.
Close to Manaus, the mean annual amplitude of the Amazon
river is around 10 meters. The maximum annual quota is in the order of
29 m (May and June) and the average minimum quota around 19 m (October
and November) The amplitudes diminish towards the estuary, given the greater
regularity of the discharges, the vast floodplains and the larger drainage
areas.
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