SECTION
5 ASSIMILATIVE CAPACITY CAPITAL STOCK
5.3 |
Assimilative
Capacity of Freshwater Systems |
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5.3.4.5 |
There
are other linkages between freshwater assimilative
capacity (and associated environmental quality)
and other aspects of the natural capital
stock (see Figure
5.3b for these linkages and sustainability
issues generally for freshwater assimilative
capacity). Land use and land use change
has implications for water quality, particularly
through changes in agricultural activity
(Paragraph 5.3.3.2). Freshwater quality
has direct implications for the renewable
and non-renewable natural resources and
ecological functions which may be supported
within a water body. The sustainability
of the fish and invertebrate community supported
within rivers will depend on the level of
pollution. Similarly, the diversity of habitats
and species within and alongside rivers
and streams will be influenced by their
environmental quality.
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5.3.4.6 |
The
future sustainability of the freshwater
resource therefore depends upon a range
of measures to prevent polluting discharges,
enforce regulation to protect watercourses
from waste disposal and illegal pollution,
and to consider rivers and streams as part
of the natural and ecological capital stock.
Despite reductions in pollutant loadings
to Hong Kong's rivers, there are still many
point source discharges of both treated
and untreated wastewaters from domestic,
commercial, industrial and agricultural
activities. Given the low flows of most
rivers in Hong Kong (aside from flooding
events), it seems unlikely that there will
be sufficient assimilative capacity to deal
with discharges other than those from non-point
sources (ie run-off). Future water quality
and assimilative capacity will therefore
rest with measures to close off point source
discharges to rivers, and instead direct
wastewater discharges to sewer for eventual
treatment at STWs.
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5.3.4.7 |
ThIn
common with marine waters, further research
into determining assimilative capacity of
freshwaters may help to further understand
assimilative capacities of river systems
and provide a scientific foundation to establish
the discharge loadings which could collectively
be accommodated within the assimilative
capacity of the waterbody, taking account
of the level of pollution already being
discharged. It is recognised, however, that
this approach would require a different
analysis of each individual watercourse
and may be a more complex task than its
equivalent for marine waters.
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