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2015-04-28 Planning and Organisation Committee Agenda
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PLANNING & ORGANISATION COMMITTEE MEETING AGENDA 28 APRIL 2015
Constituent Reasons for management
Total Nitrogen Nitrogen is a natural element in the atmosphere. Over vegetated
areas the nitrogen settles onto the ground and the plants are able to
absorb the nitrogen and release it to the atmosphere again as a gas.
When vegetated areas are replaced with non-vegetated areas, the
nitrogen settles on grounds and roofs and then in rainfall events
washes direct to the waterways. Once in the waterways the nitrogen
is like a fertiliser and is able to encourage algal growth within the
water and increased environmental weed growth along riparian areas.
This is called eutrophication. Eutrophication affects oxygen balance
in the water and also changes the natural habitat for water and
riparian dwelling fauna.
Total Phosphorous Phosphorous is delivered via atmospheric deposition, as well as
cycling of animal and plant wastes through the soil to be taken up by
plants again. In urban areas, additional inputs of phosphorous enter
the system via external sources through general garden fertilisers and
detergents etc. As with nitrogen, when the ground surfaces become
impervious through urban development, the atmospheric
phosphorous, along with the additional imported phosphorous is able
to wash direct into the waterways to act as a fertiliser with similar
consequences as nitrogen increases.
Gross Pollutants Gross pollutants can clog natural and man-made drainage lines then
affect local flooding. Non-degradable gross pollutants are harmful to
wildlife if ingested. It is also visual pollution.
4. Computer Modelling and Stormwater Quality Treatment
The computer model used to determine whether the pollutant removal targets can be
achieved is called MUSIC (this is the acronym for its function which is “Model for Urban
Stormwater Improvement Conceptualisation”). MUSIC modellers are able to input site
specific rainfall data, the development footprint (i.e. roads, roofs, grassed areas etc) then the
MUSIC model is able to compare the estimated annual loads of Nitrogen, Phosphorous,
Suspended Solids and Gross Pollutants (i.e. litter) likely to be released from the proposed
development with the loads of these pollutants able to be reduced via the site specific
WSUD treatment strategies.
The most common WSUD treatment strategy that has been used in the MUSIC modelling is
called ‘bioretention basins’. Bioretention basins are basically a sandpit which contains
specially engineered sand, plants that are very effective at removing the nutrients and
underdrainage pipes to convey the treated water back to the conventional stormwater
system or discharge direct to the receiving watercourses. Typical cross sections of
bioretention basins showing the functions of each element of them are shown following.
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