removed, and then through sand filtration and
secondary sedimentation, the vast majority of
particles obtained can be removed, and then after that
chlorine disinfection or ultraviolet ray disinfection
can be used to kill the microorganisms and pathogens
in the water, and finally, the ph value is adjusted to a
usable range. The water can then be used for non-
potable water supplies such as irrigation, cleaning,
cooling water and toilet flushing.
Incorporating filtration layers and settling basins
directly into the man-made aqueduct system reduces
the chance of pollutants entering the natural water
body. This can be at the intersection of each aqueduct,
which is usually equipped with a sluice gate. A filter
layer that can be raised and lowered at the inlet can be
installed, consisting of a large barrage and gravel. It
can be ensured that the drains do not become clogged
with clumps or larger pollutants during any time,
resulting in the loss of unclogging. Natural biological
filtration can also be done using the river parks
mentioned above, where wetland plants, aquatic
organisms and other natural elements purify the water.
They absorb some of the nutrients in the runoff, such
as nitrogen and phosphorus, and convert these
potential pollutants into harmless biomass through
plant growth, thus reducing the risk of eutrophication
of the water body. It also stops the soil on both sides
of the aqueduct from being excessively washed into
the aqueduct by the water flow.
5 CONCLUSION
This paper discusses the limitations and challenges of
the existing artificial aqueduct system in flood
prevention and control by analyzing the geographic
characteristics, precipitation distribution, and water
system in northwest Beijing. By combining multiple
perspectives of hydraulic engineering design, system
maintenance and intelligent management, and natural
ecological management, it is found that although the
existing aqueduct system can prevent and control
flooding to a certain extent, it still suffers from
insufficient design redundancy and poor maintenance
in coping with extreme weather events.
In addition, the study points out that the flood
prevention and control capacity of the aqueduct
system can be effectively improved by using
modelling tools such as SWMM for dynamic
simulation, enhancing the flexibility of aqueduct
design, introducing intelligent monitoring systems
and public participation mechanisms, and natural
ecological management tools.
With the frequent occurrence of extreme climate
events, the design and management of man-made
aqueduct systems need to be further optimized to
better adapt to the flooding risks associated with
climate change. Meanwhile, this study not only
provides practical guidance for urban flood control in
Beijing but also provides a reference for the
construction of water conservancy projects and urban
management in other similar areas. The efficiency and
sustainability of urban water management systems
can be further enhanced in the future through more
interdisciplinary studies and field tests, leading to
higher ecological and social stability.
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