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Response to Stormwater Management Approval Conditions Letter
Attached to the e-mail Operational Works Application OPW16 /0203 - 1 of 4.
Calibre Consulting (Qld) Pty Ltd Ground Floor, 545 Queen Street Brisbane QLD 4000 PO Box 10349 Adelaide Street Brisbane QLD 4000 T +61 7 3895 3444 ABN 38 109 428 506 Our Ref: 16-001014.01L.ms.cm.docx Contact: Andrew McPhail 12 September 2016 Noosa Council Level 1, 9 Pelican St Tewantin Qld 4565 Attention: Cherie O’Sullivan Dear Cherie, Palm Lake Retirement Village (Operational Works) at 2 & 4 Lamonts Road and 18 & 20 Trading Post Road, Cooroy. Responses to Stormwater Management Approval Conditions for Operational Works Approval Calibre Consulting (QLD) has prepared Operational Works documentation for stormwater management devices for the Palm Lakes Retirement Village, Cooroy. This letter has been prepared to provide responses to stormwater & flooding approval conditions outlined in Council’s Decision Notice (MCU15/0111 & REC15/0031 dated 22 July 2016) to support Operational Works approvals for stormwater management works over the site. This letter references the Stormwater Management Plan (SWMP) Report No. 16-001014-01A dated September 2016 and the Stormwater Management Construction & Maintenance Plan (SMCMP) Report No. 16-001014-02A dated September 2016 that has been submitted in conjunction with this letter. Refer to this documentation for details. With this submission we seek overall strategy approval for the balance stormwater management works (including the Central Basin and Southern Basins). We also seek the approval for the Northern Bioretention Basin design however inflow pipes are subject to future Civil Drainage Operational Works approval. Bio-Pod D2 and D3 are subject to future Civil Drainage Operational Works approvals. Earthworks (Stormwater Related Items) 59. Buildings floor levels and bulk earthworks finish levels must take into consideration any building Minimum Floor Level required by the planning scheme at the time of construction. Response Building floor levels and final finish levels have been designed with adequate flood immunity to the maximum regional 1% AEP climate change flood level of 97.8m AHD. Design of internal stormwater drainage, overland flow paths and basins ensure that adequate flood immunity will be achieved during local flooding. Refer to Section 3.2.6 of Stormwater Management Plan (SWMP) Report No. 16-001014-01A for details of local and regional flood management. 60. Earthworks carried out on site must not adversely affect the drainage conditions on any other properties or existing roads, and/or the patterns and severity of flooding in the area particularly on downstream properties. Filling works required on site shall not cause additional ponding of water on any adjoining lands or the blockage of, or interference with, any natural watercourses. Detailed site surveys indicating natural calibreconsulting.co
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surface levels and contours of any potentially affected properties must be provided with any application for
a Development Permit for Operational Works for earthworks and/or stormwater drainage works.
This may require the design and construction of drainage pipes and/or an overland flow-path within the
development site to cater for drainage from the adjoining sites for a 1% AEP design storm.
Response
Section 3.2.6 of Report No. 16-001014-01A demonstrates that the proposed earthworks to be carried out on site will
not adversely impact the pattern and severity of flooding downstream, as no filling is proposed within the regional
flood extents (up to and including the regional 1% AEP climate change storm event).
Stormwater Drainage (Quantity & Quality)
61. A suitably qualified Registered Professional Engineer, specialising in hydraulics shall prepare engineering
drawings and specifications for stormwater designs and shall be submitted in conjunction with an
application for a Development Permit for Operational Works.
Response
A suitably qualified Registered Professional Engineer, specialising in hydraulics, has prepared drawings and
specifications for stormwater design and management. Refer to Operational Works Drawings for the proposed
stormwater devices (Drawing Set No. 16-001014-400 Series) and Report No. 16-001014-01A.
62. Stormwater pipelines within the site shall cater for 10% AEP storm event and secondary flow paths shall be
provided within the site to cater for 1% AEP storm event.
Response
Stormwater pipelines have been designed to cater for the 10% AEP storm event and higher storm scenarios. Road
network and secondary overland flowpaths have been designed to convey runoff from the 1% AEP storm event.
Refer to Stage 2 Operational Works Drawing Set No. 16-001014-100 Series for details.
63. The development must not adversely impact on the existing drainage conditions on other properties. The
applicant must demonstrate that all stormwater runoffs from the fully developed site must be maintained at
predevelopment rates for all storm events up to and including the 1% AEP storm event.
Response
Section 3.2.6 in Report No. 16-001014-01A demonstrates that peak flows from the site will be reduced back to or
below existing levels for all recurrence interval storm events up to and including the 1% AEP storm. This
demonstrates that the development will not adversely impact existing drainage conditions on other properties.
While aerial imagery indicates that there appears to be no existing dams on downstream properties, water balance
analysis demonstrates that the proposed Northern (Bioretention) and Central (Water Quality Control Pond) Basins
will not deprive downstream dams of their natural stormwater runoff. Water balance analysis results indicate that the
average annual runoff volume at each site discharge location has not been reduced. Refer to Section 3.2.6 in
Report No. 16-001014-01A for details.
64. Stormwater runoff generated from the development must be treated to achieve the Water Quality Objectives
as specified under Healthy Waterways Water Sensitive Urban Design – Technical Guidelines for South East
Queensland (2006) as well as the State Planning Policy 2014 (SPP 2014) prior to release off site. For the
purpose of this condition, treatment of waters from catchments B1 and C1 as shown on Drawing B14158.W-
SK100 A by Calibre Consulting, dated 050/2/16 shall be considered as part of the development to determine
mitigation requirements and load reduction targets.
If detailed design demonstrates insufficient footprint is available for the water quality treatment devices to
achieve the pollutant reduction targets of 80% reduction in Total Suspended Solids, 60% reduction in Total
Phosphorous, and 45% reduction in Total Nitrogen compared to an unmitigated development, the applicant
must increase available space to ensure the water quality objectives can be achieved.
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Response
As indicated in Section 4.5 in SWMP Report No. 16-001014-01A, proposed stormwater management devices are
adequate to treat stormwater runoff to meet Water Quality Objectives (WQOs) specified under the Healthy
Waterways WSUD Technical Guidelines for SEQ (2006) and the SPP (2014) prior to release off site.
Table 4-7 from SWMP Report No. 16-001014-01A has been provided below demonstrating that WQOs will be
achieved.
Table 4-7: MUSIC Modelling Results (Extract from SWMP Report No. 16-001014-01A)
TSS TP TN Gross Pollutants
Description
(kg/yr) (kg/yr) (kg/yr) (kg/yr)
Developed Site Only (Without
29,700 65 425 4,270
Mitigation)
WQOs (Percentage Reduction) 80% 60% 45% 90%
Load Retention Target 23,760 39 191 3,843
Developed Site plus External
36,500 77 480 4,630
Catchment (Without Mitigation)
Developed Site plus External
12,700 33 289 488
Catchment (With Mitigation)
Load Retention Achieved 23,800 44 191 4,142
Load Retention Achieved as % of
80% 68% 45% 97%
Developed Site Load
Objective Achieved? YES YES YES YES
Two models have been provided to Council, the “Developed Site Only” model and the “Developed Site with External
- Mitigated” model. The methodology for demonstrating that WQOs for the site have been met is summarised below.
The Load Retention Target (in kg/yr) for the site was determined using the “Developed Site Only” model,
estimating the pollutants generated from the developed site only.
The Load Retention Achieved (in kg/yr) was determined using the “Developed Site with External - Mitigated”
model, estimating the amount of pollutants removed from site and External Catchment B1 and C1 as a result of
the stormwater quality improvement devices.
A comparison between the targets and pollutant retention achieved demonstrate that WQO’s for the site have been
met. This approach is consistent with past DA approvals (for the interim layout) and earlier discussions with
Council.
Catchment B1 and C1 as shown on Drawing No. B14158.W-SK102 are external and are not part of the site area.
While External Catchment B1 and C1 have been included in the stormwater quality analysis (as runoff from these
areas enter the site and into proposed stormwater quality treatment devices), these areas are not considered a “part
of the development” or identified as ‘site area’. As such, determining the amount pollutant reduction required to meet
objectives for the site (i.e. Load Retention Target) does include the pollutants generated from the external
catchment areas. The Load Retention Achieved has been determined by the total pollutants removed by the
proposed SQID’s prior to discharge from the site.
The approach and methodology outlined above is in line with past approved documentation and is therefore
considered to be appropriate as it demonstrates that WQO’s for the site will be achieved through the proposed
stormwater quality improvement devices.
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65. Stormwater Quality Treatment must be designed in accordance with the Water by Design MUSIC modelling
Guidelines. Any deviation away from the recommendations of the Water by Design guidelines may only be
approved where:
65.1. Letters signed by the authors of the Water by Design MUSIC modelling guidelines and/or eWater
MUSIC modelling program are provided to confirm that the modelled design is expected to meet the
required water quality outcomes at the discharge point of the site; and
Response
As detailed in Section 4 of the SWMP Report No. 16-001014-01A, modelling of the site and design of stormwater
quality treatment devices have been undertaken in accordance with Water By Design MUSIC Modelling Guidelines
(2010) and other relevant Water By Design guidelines. The SWMP Report No. 16-001014-01A demonstrates that
WQOs for the site are achieved without modelling of the Water Quality Control Pond (WQCP). This is conservative
considering that the proposed pond will capture suspended solids through sedimentation and will treat some
nutrients. Furthermore, the proposed Gross Pollutant Traps (GPTs) were excluded from the modelling, which are
also expected to capture gross pollutants and suspended solids. The only treatment devices modelled are the
Bioretention Basins, which have been configured in accordance with Water By Design’s MUSIC Modelling
Guidelines (2010). Therefore, since there is no deviation from the recommendations specified in Water By Design
Guidelines, a letter from the authors of the Water By Design guidelines or eWater MUSIC program is not required.
For email correspondence with Water By Design and eWater regarding the modelling of the pond, refer to Calibre
Consulting Letter No. B14158.W-10A dated 5 February 2016.
65.2. A contingency plan to monitor for and to remove cyanobacterial and algal outbreaks from
waterbodies, including costs, is provided for approval with the Operational Works application and the
approved version is implemented throughout the lifetime of the development. All stormwater runoff
treatment must be undertaken within the development areas of the site. Stormwater likely to contain
grease and oil (i.e. from all roads and car parking areas) shall be managed via grease and oil
arrestors prior to treatment within bioretention basins, wetlands and water quality control ponds.
Response
As discussed above, modelling of the site and design of stormwater quality treatment devices have been undertaken
in accordance with Water By Design MUSIC Modelling Guidelines (2010) and other relevant Water By Design
guidelines. As detailed in Section 4 of the SWMP Report, all stormwater treatment is undertaken within development
areas of the site. Modelling has demonstrated WQO’s can be achieved prior to discharge from the site.
Stormwater from all significant roads and car parking areas are proposed to be treated with a HumeGard GPT.
Council specify that runoff from all road and car parking areas is to be pre-treated for grease and oil prior to
discharging to the downstream Bioretention systems. According to Water By Design Bioretention Technical Design
Guidelines (2014) Bioretention systems are suitable for treating runoff from roof, ground and road areas. Table 14 of
the guidelines outlines pre-treatment measures typically proposed upstream of Bioretention Basins based on
catchment size (i.e. for catchments between 2ha and 5ha vegetated swales, coarse sediment forebays, inlet pond or
GPT’s are recommended). The condition to pre-treat all runoff from road and car parking area specifically for oil and
grease prior to discharge into Bioretention Basins is considered to be conservative given the nature of the
Bioretention treatment device. There are also many examples of urban, commercial and industrial development that
propose Bioretention Basins without pre-treatment of oil and grease.
As per details provided in Section 3.1 of the Stormwater Management Construction & Maintenance Plan Report No.
16-001014-02A, the HumeGard GPT proposed upstream of the proposed Bioretention Basins has the capability of
trapping floating oil and grease pollutants. As demonstrated on Page 2 of the HumeGard GPT Technical Manual
provided in Attachment 2, the application of a floating boom provides separation at the surface of the waters
between the sediment storage chamber and the outlet chamber. This effectively captures pollutants such as oils and
greases that float to the surface. Based on laboratory and field testing, Table 1 on Page 3 of the Technical Manual
indicates 90% removal efficiency of Hydrocarbons during emergency spill events.
Also, the proposed Bioretention Basins and Pond are not to become Council assets, rather this will be operated by
the retirement community owner who is responsible for the maintenance and management of these treatment
devices. Managing and replanting of the Bioretention Basins and Pond will be the responsibility of the retirement
community owner.
Based on the above, all areas of road and car parking, except for the road areas in the northern catchment
(Catchment A1 & A2) will be treated by GPT’s. Since Catchment A is only 2.45ha with no significant areas for car
parking a sediment forebay is appropriate.
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Further to this a contingency plan (including costs) to monitor for and to remove cyanobacterial and algal outbreaks
has been provided in Appendix A of the SMCMP Report No. 16-001014-02A. Monitoring of the stormwater quality
treatment devices will be implemented throughout the lifetime of the development.
66. Wetlands, bioretention basins and other water quality treatment devices shall be designed and constructed
in accordance with Healthy Waterways Water Sensitive Urban Design – Technical Guidelines for South East
Queensland 2006, Water by Design Bioretention Technical Design Guidelines 2014, Healthy Waterways
Water by Design Construction and Establishment Guidelines: Swales, Bioretention Systems and Wetlands
February 2009. In the case of any inconsistencies between these documents, the most recent document
shall prevail.
Response
Design of stormwater quality treatment devices is in accordance with the above mentioned documents. Further
details are provided in Section 2.1 and 3.1 of SMCMP Report No. 16-001014-02A.
67. Stormwater treatment strategy must be designed and maintained to achieve compliance with the
approved version of B14158.W.07L.AMcP.ag.docx dated 8 October for the Stormwater Management
Construction and Maintenance Plan Framework.
Response
The stormwater treatment strategy has been designed and maintained in accordance with Calibre Consulting’s
Letter No. B14158.W.07L.AMcP.ag.docx dated 8 October 2015. Refer to SMCMP Report No. 16-001014-02A for
details.
68. The detailed Stormwater Management Construction and Maintenance Plan (SMCMP) must be designed and
implemented in accordance with the framework detailed in the approved version of
B14158.W.07L.AMcP.ag.docx dated 8 October 2015 and approved by the Council prior to issue of
operational works approval.
Response
The SMCMP Report No. 16-001014-02A is in accordance with the framework provided in Calibre Consulting’s Letter
No. B14158.W.07L.AMcP.ag.docx dated 8 October 2015. Refer to the report for details.
69. The owner of the development is responsible for all costs associated with the construction and ongoing
maintenance and repair of the treatment of stormwater on the site and for all catchments that enter the site.
Response
As detailed in the SMCMP Report No. 16-001014-02A, the owner of the development will be responsible for the
construction, maintenance and repair of all stormwater quality treatment devices on site.
70. The Operational Works Application must include calculations in accordance with the Queensland Urban
Drainage Manual to demonstrate that the confluence of stormwater at the drainage easement will not cause
scour and that any required dissipater/erosion control can be contained wholly within the applicant’s
property.
Response
Calculations have been provided in Appendix A of the SMCMP Report No. 16-001014-02A to demonstrate that the
confluence of stormwater at the drainage easement will not cause scour and that adequate energy dissipation
wholly within the site will be provided.
71. Any waters captured on site must be plumbed to be available for all external uses including gardening,
irrigation, filling swimming pools and outdoor cleaning, as well as all ground floor toilet cisterns and
washing machine cold taps.
Response
The capture of all water for external uses was not proposed as part of the previously approved MCU submission.
The capture of all water on site is not required for the site to meet both Stormwater Quality and Quantity Objectives
to be achieved and is therefore not proposed or required.
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6 of 6 72. Operational Works Application must demonstrate that the peak 1-year ARI event discharge off site is limited to the pre-development peak 1-year ARI event discharge flow. Response Refer to the response to Condition 63. Peak flows including the 63% AEP (1 year ARI) storm will be reduced back to or below existing levels. 73. Prior to commencement of use, the applicant must provide Council with a performance bond to the value of 150% of the value of monitoring and maintenance of the water bodies for the first 5 years of full operation. The bonds shall be incrementally released annually following completion of the development and upon demonstration to the satisfaction of Council Officers that all aspects of the approved version of the detailed Stormwater Management Construction and Maintenance Plan required by this approval have been implemented to effectively prevent or reduce likelihood of cyanobacteria outbreaks for the site for the preceding year. Response As specified in Appendix A of the SMCMP Report No. 16-001014-02A, a performance bond to the value of 150% of the value of monitoring and maintenance of the water bodies for the first 5 years of full operation will be provided to Council. We trust the information provided in this letter is acceptable and satisfactorily addresses Council's Approval Conditions. We respectfully request that the Operational Works designs for stormwater management be approved. Should you require any further information please do not hesitate to contact the undersigned or Andrew McPhail on (07) 3895 3444. Yours sincerely, Calibre Consulting Matthew Starr Senior Engineer — Water & Environment