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2.0 STORMWATER CONCEPT DESIGN
2.1 Overland Flow Paths and Flooding
We have reviewed North Sydney Council 1m Contour Maps. The maps
indicate that the site is located near the top of a ridge falling
at approximately 4% grade from Military Road toward the
northwest.
Figure 3 – North Sydney Council 1m Contour Map with Upstream/
Downstream Catchment
Detailed topographic survey of the site prepared for this project
indicates a drainage easement in favour of North Sydney Council
extending across the site from the north end of Monford Place to
the intersection of Waters Road and Gerard Street near the
northwest corner of the site as schematically shown in Figure 3.
Our initial investigation suggests the existing pipe size is a
375mm diameter reinforced concrete pipe (RCP) starting in Monford
Street cul-de-sac.
Our initial analysis shows the existing 375mm pipe has less than
the 100-year average recurrence interval (ARI) capacity
(approximately 5-year ARI capacity subject to our detailed
analysis).
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Figure 4 – Topographic Survey and Drainage Easement Location
The proposed development scheme requires this existing easement/
pipe to be relocated.
TTW initially considered four stormwater diversion options sized to
cater for the 100-year ARI storm event including inlet capacity in
Monford Place due to lack of overland flowpath through the site.
These options were reviewed with North Sydney Council at a meeting
held on the 20
th January 2015.
2.2 North Sydney Council Stormwater Diversion Consultation
TTW met with Vesna Ristic, Development Engineer Assessments for
North Sydney Council on 20 January 2015. Ms. Ristic provided the
following comments on the proposed Council stormwater pipe
diversion options, overland flow path and easement:
• Pipe to be sized for 1 in 20 year storm event, or minimum
375mm
• Additional pits may be required in Monford Place to accommodate 1
in 20 ARI storm event
• Minimum 1% grade along pipe
• Provide overland flow path to direct water around the building in
the 1 in 100 year ARI storm event
• All changes in pipe direction shall occur at junction pits
• All new pits shall be accessible from the surface
• It is preferable that pipes are not suspended
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Comments were provided verbally in the meeting and via email dated
3 rd February 2015.
Following the meeting with Council, TTW proposed two additional
diversion options to the project team in order to comply with the
Council requirements.
See drawings in Appendix A the proposed schematic design layout
showing a 2.5m easement over the proposed stormwater pipe diversion
(sized for the 1:20 year ARI storm event) and a 1.6m easement over
the propose overland flow diversion (sized for the 1:100 year ARI
storm event).
2.3 Stormwater Detention
The North Sydney Council DCP (Section 3.5.7.P5) requires On-Site
Detention (OSD) to limit the post-development discharge rates to
less than pre-development discharge rates. DRAINS modelling was
used to demonstrate that the requirement can be met by increasing
pervious area on the site from the existing condition. Thus, OSD is
not required.
2.3.1 Stage 1
A catchment area for the site (excluding the Adams Centre) was
calculated to be 14,930 m 2
based on an architectural scheme with green roof areas. The
existing impervious fraction for this area is 87.3%.
The proposed Stage 1 development incorporates green roof and ground
level landscaping areas that reduce the site impervious fraction to
81.5%. Therefore, stormwater flows from the site are reduced from
existing flows as shown in the table below.
Table 1 Stage 1 Discharge Rates
Average Recurrence
1-year 386 370
2-year 512 497
5-year 685 670
10-year 732 718
20-year 917 903
50-year 977 963
100-year 1090 1080
Considering that the proposed development with green roof is
reducing impervious area, site discharge rates will be less than
the pre-development peak flow rates for all storms up to and
including the 100-year ARI storm events; hence OSD is not
required.
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2.3.2 Master Plan
A catchment area for the site was calculated to be 14,930 m 2 . The
existing impervious
fraction for this area is 87.3% and the proposed impervious
fraction following completion of all stages of Master Plan
Construction is 85.6%.
With the reduction in impervious area from existing conditions to
the Master Plan design, stormwater flows from the site are reduced
from existing flows as shown in Table 2.
Table 2 Master Plan Discharge Rates
Average Recurrence
1-year 386 381
2-year 512 508
5-year 685 681
10-year 732 728
20-year 917 913
50-year 977 972
100-year 1090 1090
Considering that the proposed development is not increasing the
existing impervious area the site’s discharge rates will be less
than the pre-development peak flow rates for all storms up to and
including the 100-year ARI storm events hence OSD is not
required.
2.3.3 Adams Centre
Similar to the proposed development on the north side of Military
Road, the proposed development on the Adams Centre parcel does not
significantly increase impervious area. Therefore, on-site
detention to serve the Adams Centre is not proposed.
2.4 Stormwater Retention
The DCP (Section 3.5.7.P4) encourages stormwater retention and
reuse for appropriate end use including toilet flushing, water
features, car washing and garden irrigation.
2.4.1 Stage 1
A 60m 3 rainwater reuse tank is proposed for the Stage 1
redevelopment. Stormwater
collected from the new building roof will be reused for landscape
irrigation.
2.4.2 Master Plan
The 60m 3 rainwater reuse tank proposed for Stage 1 will remain in
place throughout the
Master Plan development with additional stormwater collection pits
and piping as required.
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2.4.3 Adams Centre
Rainwater reuse is not proposed for the Adams Centre redevelopment
as the proposed improvements do not significantly change the
impervious make-up of this portion of the school.
2.5 Water Sensitive Urban Design
In order to comply with the DCP (Section 3.5.7.P11), the
development must achieve the stormwater quality targets outlined in
Table 3. The DCP encourages green roofs, minimum 50% pervious
pavements, grass swales and rainwater tanks to reduce runoff and
meet stormwater quality pollutant reduction targets.
Table 3 Stormwater Quality Targets
POLLUTANT RETENTION CRITERIA
Litter and vegetation larger than 5mm 90% reduction compared to the
Baseline Annual Pollutant Load
Total suspended solids 85% reduction compared to the Baseline
Annual Pollutant Load
Total phosphorus 65% reduction compared to the Baseline Annual
Pollutant Load
Total nitrogen 45% reduction compared to the Baseline Annual
Pollutant Load
2.5.1 Stage 1
Stormwater quality modelling in the MUSIC software program
indicates that a treatment train including 310m
2 green roof, 60m
3 rainwater reuse tank, trash screen, and proprietary
stormwater treatment devices, such as a SPEL Stormceptor and 4 SPEL
Filters can be utilized to meet stormwater quality requirements for
the Stage 1 redevelopment.
Figure 5 – Stage 1 MUSIC Model Layout and Results
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2.5.2 Master Plan
Stormwater quality modelling in the MUSIC software program
indicates that a treatment train including 310m
2 green roof in Stage 1, 60m
3 rainwater reuse tank, trash screen, and
proprietary stormwater treatment devices, such as a SPEL
Stormceptor and 6 SPEL Filters can be utilized to meet stormwater
quality requirements for the Master Plan redevelopment.
Figure 6 – Master Plan MUSIC Model Layout and Results
2.6 Sediment, Erosion and Dust Controls
Construction works are to be carried out in accordance with the
“Blue Book” erosion and sediment control requirements. The controls
for each Stage will depend on construction staging and methodology,
but will most likely include sediment fences, sandbags around pits
and a vehicle wash down. An erosion and sediment control plan has
been prepared as part of the schematic design drawings for Stage 1.
Similar erosion and sediment control measures will be required in
subsequent stages of the Master Plan redevelopment.
2.7 Schematic Stormwater Design
We have prepared schematic stormwater design for the redevelopment
showing the layout and level of stormwater pits and piping, on-site
detention, rainwater reuse and water quality treatment systems. The
stormwater schematic design plan is shown in Appendix A of this
report.
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3.0 CONCLUSION
Stormwater infrastructure has been designed to provide stormwater
quantity and quality outcomes to meet the stormwater quality
targets outlined in the DCP and North Sydney Council Performance
Guide for Engineering Design and Construction.
Prepared by: Authorised by:
Heather Spencer Stephen Brain
P:\2014\1415\141531\Reports\TTW\150514 Redlands Stormwater
Report.doc
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APPENDIX A
NTS WW SB
SKC210 STAGE 1 - EROSION & SEDIMENT CONTROL PLAN
SKC230 STAGE 1 - SITEWORKS PLAN - GROUND LEVEL
SKC240 STAGE 1 - DETAILS SHEET 1
SKC241 STAGE 1 - DETAILS SHEET 2
NOTES AND LEGENDS SHEET
PIT SCHEDULE
Note:
C241
A1
48 Chandos Street St.Leonards NSW 2065
T: +61 2 9439 7288 F: +61 2 9439 3146
[email protected]
Consulting Engineers
Taylor Thomson Whitting (NSW) Pty Ltd A.C.N. 113 578 377
141531
Architect Sheet SubjectProject
Rev Description Eng DateDraft Rev Description Eng DateDraft
This drawing is copyright and is the property of TAYLOR
THOMSON
WHITTING (NSW) Pty Ltd and must not be used without
authorisation.
THIS DRAWING TO BE READ IN CONJUNCTION WITH ALL
RELEVANT NOTES ON DRAWING S0001
STAGE 1
RL 79.49 (AHD)
NOTE: UNDERGROUND ELECTRICITY CABLES
NOTE: UNDERGROUND ELECTRICITY CABLES
TOTAL AREA 1.493Ha
SEDIMENTATION TRAP
48 Chandos Street St.Leonards NSW 2065
T: +61 2 9439 7288 F: +61 2 9439 3146
[email protected]
Consulting Engineers
Taylor Thomson Whitting (NSW) Pty Ltd A.C.N. 113 578 377
141531
Architect Sheet SubjectProject
Rev Description Eng DateDraft Rev Description Eng DateDraft
This drawing is copyright and is the property of TAYLOR
THOMSON
WHITTING (NSW) Pty Ltd and must not be used without
authorisation.
THIS DRAWING TO BE READ IN CONJUNCTION WITH ALL
RELEVANT NOTES ON DRAWING S0001