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Stormwater Technical Memo · MCU23/0096
5 WATER QUALITY ANALYSIS
Stormwater quality modelling is based on split surface areas and their associated export pollutant
load. As per Table 1, above, the roof area increases by approximately 1,200 m2, while the road
area decreases by approximately 1,200m2. In accordance with MUSIC Modelling Guidelines, roof
pollutant export values are significantly less than road pollutant export parameters (see Table 3). As
such, it could be expected that stormwater pollutant loads would decrease with the proposed
developed. Therefore, no additional stormwater quality improvement devices are required.
Table 3. Pollutant Export Parameters.
Pollutant Export Parameters for Split Catchment Land-use (Log10 values)
Land Split Flow Type TSS TP TN
Use Mean Std. Dev Mean Std. Dev Mean Std. Dev
Roof Baseflow N/A N/A N/A N/A N/A N/A
Stormflow 1.3 0.38 -0.89 0.34 0.37 0.34
Commercial
Roads Baseflow 0.78 0.39 -0.6 0.5 0.32 0.3
Stormflow 2.43 0.38 -0.3 0.34 0.37 0.34
Ground Baseflow 0.78 0.39 -0.6 0.5 0.32 0.3
Stormflow 2.16 0.38 -0.39 0.34 0.37 0.34
Source: Table 3.9 (MUSIC Modelling Guidelines).
6 CONCLUSION
As there have been no significant changes to the overall impervious area associated with the
proposed Arts Centre, it has been determined that no additional detention or stormwater quality
improvement devices are required. This advice is based on the current Masterplan layout (Burling
Brown’s drawing: GSL05-SK-02, Dated 24/2/23) and aligns with QUDM (2017) and MUSIC Modelling
Guidelines (2018) requirements, and Noosa Shire Council requirements.
If Council require further explanation of the above or additional information, please contact the
undersigned at [email protected] DISCLAIMER
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incorrect or that is inaccurate, nor for changes to the conditions over the passage of time or from
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findings and conclusions expressed in this report.
Technical Memo | 21-0211TM-SW01-v3 |Good Shepherd Page 4
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