civil engineering report for development application

45
CIVIL ENGINEERING REPORT FOR DEVELOPMENT APPLICATION PROPOSED DEVELOPMENT AT 34-46 FLUSHCOMBE ROAD BLACKTOWN NSW 2148 Prepared For: Eastview Pty Ltd 3 Northcliff Street MILSONS POINT NSW 2061 Prepared by: Costin Roe Consulting Level 1, 8 Windmill Street WALSH BAY NSW 2000 Rev: A

Upload: others

Post on 21-Mar-2022

0 views

Category:

Documents


0 download

TRANSCRIPT

WALSH BAY NSW 2000
Document Title Civil Engineering Report for Development Application
Project No. Co14189.00
Name Signature
Copies
28 Jan. 2021 A Jim Simons, Eastview Pty Ltd PDF
Co14189.00-03a.rpt ii
2.2 Existing Site 2
2.3 Proposed Development 2
3 SITE WORKS 4
4 STORMWATER MANAGEMENT 5
4.1 Hydrologic Modelling and Analysis 5 4.1.1 General Design Principles 5 4.1.2 Minor/ Major System Design 5 4.1.3 Rainfall Data 5
4.1.4 Runoff Models 5
4.2 Hydraulics 6 4.2.1 General Requirements 6 4.2.2 Freeboard 6
4.2.3 Public Safety 7 4.2.4 Inlet Pit Spacing 7
4.2.5 Overland Flow 7
4.3 Site Drainage 7
5 WATER QUANTITY MANAGEMENT 8
5.1 Stormwater Quantity and Detention 8
6 STORMWATER QUALITY & RAINWATER REUSE 10
6.1 Stormwater Quality 10
6.2 Stormwater Harvesting 10 6.2.1 Internal Base Water Demand 10 6.2.2 External Base Water Demand 11 6.2.3 Rainwater Tank Sizing 11
6.3 Maintenance And Monitoring 12
7 EROSION & SEDIMENT CONTROLS 14
7.1 Introduction 14
7.7 Site Inspection and Maintenance 16
8 CONCLUSION 19
9 REFERENCES 20
Co14189.00-03a.rpt 1
1 INTRODUCTION
Eastview proposes to develop 34-46 Flushcombe Road, Blacktown, NSW as a
multistorey hotel and apartment building.
Costin Roe Consulting Pty Ltd has been commissioned by Eastview, to prepare this
Engineering Report in support of the proposed Development Application for the
development.
This report provides a summary of the design principles and planning objectives for the
following civil engineering components of the project:
• Stormwater Management; and
• Erosion Control.
The engineering objectives for the development are to create a site which, based on the
proposed architectural layout, responds to the topography and site constraints and to
provide an appropriate and economical stormwater management system which
incorporates best practice in water sensitive urban design and is consistent with the
requirements of council’s water quality objectives.
A set of drawings have been prepared to show the proposed engineering and stormwater
management strategy for the development. These drawings are conceptual only and
subject to change during detail design.
The subject site is located within Blacktown City Council LGA, the requirements of the
Blacktown City Council Engineering Guide for Development, Part J of the
Development Control Plan 2015 and the WSUD Developer Handbook – MUSIC
Modelling and Design Guide 2020 have been considered in the design documentation.
Co14189.00-03a.rpt 2
2.1 Location
The proposed development is located in the suburb of Blacktown on eastern side of
Flushcombe Road as shown in Figure 2.1.
Figure 2.1: Locality Map (Source: Nearmap – 27 August 2020)
2.2 Existing Site
The development site encompasses an area of 0.159 Ha. It currently contains
commercial and residential allotments located at 34-46 Flushcombe Road, Blacktown.
The detail survey plan, completed by Paul A. Lawson, shows levels vary from RL
63.05m AHD at the south-east of the site to RL 66.20m AHD at the north-west corner.
Levels grade to the south-east toward Cobb Lane.
2.3 Proposed Development
The proposed development comprises the construction of a new multistorey building for
commercial and residential use. The development layout is shown on the architectural
drawings by Marchese Partners as shown in Figure 2.2 and 2.3. The development
includes basement level car parking, hotel and gaming levels, and residential apartment
levels.
3 SITE WORKS
Earthworks excavation and shoring will be required to facilitate the basement level
construction. Shoring requirements will be undertaken as part of future detailed
structural engineering designs, informed by a detailed geotechnical investigation.
It is anticipated that the basement shoring system will comprise bored pier and shot-
crete system with temporary anchors in place until such time that the internal floors are
constructed to form a diaphragm support system. As noted, details of the system will
form part of detailed structural engineering designs at Construction Certificate stage of
the development.
Soil Erosion and Sediment Control measures including sedimentation basins are to be
placed in accordance with submitted drawings and the Soil and Water Management Plan
in Section 7 of this report. Minor changes will be made to suit the current layout and
site requirements.
will be undertaken in accordance with AS3798-2007.
Co14189.00-03a.rpt 5
4.1.1 General Design Principles
The design of the stormwater system for this site will be based on relevant national
design guidelines, Australian Standard Codes of Practice, Blacktown City Council and
accepted engineering practice.
Runoff from buildings will generally be designed in accordance with AS 3500.3
National Plumbing and Drainage Code Part 3 – Stormwater Drainage.
Overall site runoff and stormwater management will generally be designed in
accordance with the Institution of Engineers, Australia publication “Australian Rainfall
and Runoff” (1987 Edition), Volumes 1 and 2 (AR&R).
Storm events for the 20- & 100-Year ARI event have been assessed.
4.1.2 Minor/ Major System Design
The piped stormwater drainage (minor) system has been designed to accommodate the
20-year ARI storm event (Q20). Overland flow paths (major) which will convey all
stormwater runoff up to and including the Q100 event have also been provided which
will limit major property damage and any risk to the public in the event of a piped
system failure.
4.1.3 Rainfall Data
Rainfall intensity Frequency Duration (IFD) data used as a basis for DRAINS
modelling for the 2 to 100 Year ARI events, was taken from Blacktown City Council’s
Engineering Guidelines for Development 2005.
4.1.4 Runoff Models
In accordance with the recommendations and standards of Blacktown City Council, the
calculation of the runoff from storms of the design ARI has been calculated with the
catchment modelling software DRAINS.
Co14189.00-03a.rpt 6
The design parameters for the DRAINS model are to be based on the recommendations
as defined by BCC and parameters for the area and are as follows:
Model Model for Design and analysis run Rational method
Rational Method Procedure ARR87
Supplementary Area Depression Storage 1 mm
Grassed (Pervious) Area Depression Storage 5 mm
AMC Antecedent Moisture Condition (ARI=1-5 years) 2.5
AMC Antecedent Moisture Condition (ARI=10-20 years) 3.0
AMC Antecedent Moisture Condition (ARI=50-100 years) 3.5
Sag Pit Blocking Factor (Minor Systems) 0
On Grade Pit Blocking Factor (Minor Systems) 0
Sag Pit Blocking Factor (Major Systems) 0.5
On Grade Pit Blocking Factor (Major Systems) 0.2
Inlet Pit Capacity
Hydraulic calculations will be carried out utilising DRAINS modelling software during
the detail design stage to ensure that all surface and subsurface drainage systems
perform to or exceed the required standard.
4.2.2 Freeboard
The calculated water surface level in open junctions of the piped stormwater system will
not exceed a freeboard level of 150mm below the finished ground/ grate level, for the
peak runoff from the Minor System runoff.
The calculated water surface for the peak runoff from the Major System runoff will not
exceed a freeboard level of 300mm below the finished floor level of the building.
Co14189.00-03a.rpt 7
4.2.3 Public Safety
For all areas subject to pedestrian traffic, the product (dV) of the depth of flow d (in
metres) and the velocity of flow V (in metres per second) will be limited to 0.4, for all
storms up to the 100-year ARI.
For other areas, the dV product will be limited to 0.6 for stability of vehicular traffic
(whether parked or in motion) for all storms up to the 100-year ARI.
4.2.4 Inlet Pit Spacing
The spacing of inlets throughout the site will be such that the depth of flow, for the
Major System design storm runoff, will not exceed the top of the kerb (150mm above
gutter invert).
4.2.5 Overland Flow
Dedicated flow paths have been designed to convey all storms up to and including the
100-year ARI. These flow paths will convey stormwater from the site to the estate road
system and to the existing trunk drainage system.
4.3 Site Drainage
4.3.1 Proposed Site Drainage
The proposed stormwater system consists of a major/ minor system which conveys
surface water from the roofs to various water quality improvement devices prior to
discharge from the site.
Reference to drawing Co14189.00-DA04 shows the proposed drainage layout including
stormwater management measures. Further discussion on the stormwater management
measures are made in Sections 5 and 6 of this report.
4.3.2 Site Discharge
Discharge from the site will be to Cobb Lane. The proposed discharge points can be
seen on drawing Co14189.00-DA04, with details of the storage and discharge devices
in drawing Co14189.00-DA05, in Appendix A.
Further investigations pertaining to the outlet will need to be undertaken during
Construction Certificate design phase.
Blacktown City Council consider limiting stormwater runoff discharged from private
property into the underground piped drainage system to pre-development flows.
Options within Blacktown City Council for OSD include via site specific systems (on-
site detention/ OSD) or via a regional system provided by Council through contributions
under S7.11 scheme or other contribution scheme depending on the location within the
LGA.
The requirements for on-site stormwater detention are contained in Section 4.4 of
Blacktown City Council Part J DCP 2015 and their included OSD Requirement Map.
Figure 5.1 shows the site in relation to the OSD zones within the LGA.
Figure 5.1. BCC OSD Requirement Map
Co14189.00-03a.rpt 9
Figure 5.1 shows the development site is located within an OSD Catchment Area.
Therefore, on lot detention is required for the development.
The detention system proposed comprises of a detention tank of approximately 75m3 in
volume, proposed below the gaming room and ground floor slab. Reference to
drawings Co14189.00-DA04 shows the proposed drainage layout including stormwater
detention measures.
Sizing of the detention system has been completed in accordance with the Blacktown
City Council Developers WSUD Guidelines 2020 and the SQ3M Small Lot web
interface tool. Refer to Appendix C.
Co14189.00-03a.rpt 10
6.1 Stormwater Quality
Blacktown City Council has nominated, in Part J of their DCP 2015 and Section 3 of
their WSUD Developer Handbook – MUSIC Modelling and Design Guide 2020, that
developments of less than 2,000m2 do not require tertiary treatment. Therefore, this site
does not require any treatment devices prior to discharge.
Confirmation that no water quality is required for this development was also made using
the Blacktown Council SQ3M Web Interface Tool, as included in Appendix C.
6.2 Stormwater Harvesting
Stormwater harvesting refers to the collection of stormwater from the developments
internal stormwater drainage system for re-use in non-potable applications. Stormwater
from the stormwater drainage system can be classified as either rainwater where the
flow is from roof areas, or stormwater where the flow is from all areas of the
development.
For the purposes of this development, we refer to a rainwater harvesting system, where
benefits of collected stormwater from roof areas over a stormwater harvesting system
can be made as rainwater is generally less polluted than stormwater drainage.
Rainwater harvesting is proposed for this development with re-use for non-potable
applications. Internal uses include such applications as toilet flushing while external
applications will be used for irrigation. The aim is to reduce the water demand for the
development by a minimum of 80% and to satisfy the requirements of Blacktown City
Council DCP2015 Part J.
In general terms, the rainwater harvesting system will be an in-line tank for the
collection and storage of rainwater. At times when the rainwater storage tank is full,
rainwater can pass through the tank and continue to be discharged via gravity into the
stormwater drainage system. Rainwater from the storage tank will be pumped for
distribution throughout the development in a dedicated non-potable water reticulation
system.
Rainwater tanks have been designed, using MUSIC software to balance the supply and
demand, based on the below base water demands and the requirement of Blacktown
Council DCP2015 Part J to provide 80% reduction in non-potable water demand.
6.2.1 Internal Base Water Demand
Indoor water demand has been based on Section 11.14.3 of Blacktown Councils WSUD
Developers Handbook 2020 for an industrial/ commercial development. Section
11.14.3 requires an allowance of 0.1kL/day/toilet or urinal including disabled toilets.
The use is proposed for 7 days a week hence has not been proportioned for 5-day use.
The above rates result in the following internal non-potable demand:
Public/Residential 11 Toilets 1.1kL/day
Co14189.00-03a.rpt 11
It is noted that there are no proposed vehicle wash downs, and no wash down reuse has
been allowed for in the assessment.
6.2.2 External Base Water Demand
The external base water demand has also been based on Section 11.14.3 of Blacktown
Councils WSUD Developers Handbook 2020 for an industrial/ commercial development
Section 11.14.3 requires an allowance of 0.4kL/year/m2 as PET-Rain for subsurface
irrigation and one non-potable tap per 50m perimeter with a demand of
0.005kL/day/tap.
The above regime for the landscaped area for the site gives the following yearly outdoor
water demand:
Non-potable Tap (0.005kL/d/tap) 3 units 0.015 kL/day
6.2.3 Rainwater Tank Sizing
The use of rainwater reduces the mains water demand and the amount of stormwater
runoff. By collecting the rainwater run-off from roof areas, rainwater tanks provide a
valuable water source suitable for flushing toilets and landscape irrigation.
Rainwater tanks have been designed, using MUSIC software to balance the supply and
demand, based on the calculated base water demands and proposed roof catchment
areas. Allowances in the MUSIC model have been made for high flow bypass which
will be managed by a dual high flow (225mm downpipe) and low flow (100mm
downpipe) roofwater collection configuration along a portion of the southern elevation
of the warehouse. This has been shown on drawings Co14189.00-DA04.
Roof
Catchment
(m2)
Highflow
Bypass
(l/s)
1592 100 25 80.79 25
Table 6.1: Rainwater Reuse Requirements
The MUSIC model rainwater tank sizing results summarised in Table 6.1, predicts that
the requirements of Blacktown Council DCP2015 Part J (80% reduction in non-potable
water demand) will be met for the development with the provision of the above noted
rainwater tanks.
The MUSIC model incorporates a 10% loss in rainwater tank size volume to allow for
anaerobic zones, mains water top up levels and overflow levels as required of Section
11.14.4 of WSUD Developers Handbook 2020.
We note that the final configuration and sizing of the rainwater tanks is subject to detail
design considerations and optimum site utilisation and Basix requirements.
Co14189.00-03a.rpt 12
6.3 Maintenance And Monitoring
It is important that each component of the water quality treatment train is properly
operated and maintained. In order to achieve the design treatment objectives, an
indicative maintenance schedule has been prepared (refer to Table 6.2 below) to assist
in the effective operation and maintenance of the various water quality components.
Note that inspection frequency may vary depending on site specific attributes and
rainfall patterns in the area. In addition to the below nominated frequency it is
recommended that inspections are made following large storm events.
Table 6.2: Indicative Maintenance Schedule
MAINTENANCE
ACTION
Monthly Maintenance
cleaned out
removed from the inlet
removed from rainwater
maximum allowable
hydraulic consultant
Contractor
After Major
Inspect pit sump for
Inspect storage areas
and remove debris/
damaged.
corrosion, especially at
corners or welds.
Inspect overflow weir
and remove any
blockage.
7.1 Introduction
An erosion and sediment control plan (ESCP) is included in drawings Co14189.00-
DA02, included in Appendix A.
The drawings show the works can proceed without unduly polluting receiving waters
during construction. A detailed plan will be prepared after development consent is
granted and before works commence.
7.2 General Conditions
1. The ESCP will be read in conjunction with the engineering plans, and any other
plans or written instructions that may be issued in relation to development at the
subject site.
2. Contractors will ensure that all soil and water management works are undertaken as
instructed in this specification and constructed following the guidelines stated in
Landcoms Managing Urban Stormwater, Soils and Construction (1998) – The Blue
Book, and Blacktown City Council specifications.
3. All subcontractors will be informed of their responsibilities in minimising the
potential for soil erosion and pollution to down slope areas.
7.3 Land Disturbance
1. Where practicable, the soil erosion hazard on the site will be kept as low as possible
and as recommended in Table 7.1.
Table 7.1: Limitations to access
Land Use Limitation Comments
metres from the edge of any
essential construction activity as
All site workers will clearly recognise
these areas that, where appropriate,
are identified with barrier fencing
(upslope) and sediment fencing
(downslope), or similar materials.
5 metres
onsite. They can vary in position so as
to best conserve existing vegetation
and protect downstream areas while
being considerate of the needs of
efficient works activities. All site
workers will clearly recognise these
boundaries.
essential management works
7.4 Erosion Control Conditions
1. Clearly visible barrier fencing shall be installed as shown on the plan and elsewhere
at the discretion of the site superintendent to ensure traffic control and prohibit
unnecessary site disturbance. Vehicular access to the site shall be limited to only
those essential for construction work and they shall enter the site only through the
stabilised access points.
2. Soil materials will be replaced in the same order they are removed from the ground.
It is particularly important that all subsoils are buried, and topsoils remain on the
surface at the completion of works.
3. Where practicable, schedule the construction program so that the time from starting
land disturbance to stabilisation has a duration of less than six months.
4. Notwithstanding this, schedule works so that the duration from the conclusion of
land shaping to completion of final stabilisation is less than 20 working days.
5. Land recently established with grass species will be watered regularly until an
effective cover has properly established and plants are growing vigorously. Further
application of seed might be necessary later in areas of inadequate vegetation
establishment.
6. Where practical, foot and vehicular traffic will be kept away from all recently
established areas
7. Earth batters shall be constructed in accordance with the Geotechnical Engineers
Report or with as law a gradient as practical but not steeper than:
• 2H:1V where slope length is less than 7 metres
• 2.5H:1V where slope length is between 7 and 10 metres
• 3H:1V where slope length is between 10 and 12 metres
• 4H:1V where slope length is between 12 and 18 metres
• 5H:1V where slope length is between 18 and 27 metres
• 6H:1V where slope length is greater than 27 metres
8. All earthworks, including waterways/drains/spillways and their outlets, will be
constructed to be stable in at least the design storm event.
9. During windy weather, large, unprotected areas will be kept moist (not wet) by
sprinkling with water to keep dust under control. In the event water is not available
in sufficient quantities, soil binders and/or dust retardants will be used, or the
surface will be left in a cloddy state that resists removal by wind.
Co14189.00-03a.rpt 16
7.5 Pollution Control Conditions
1. Stockpiles will not be located within 5 metres of hazard areas, including likely areas
of high velocity flows such as waterways, paved areas and driveways. Silt/
sediment fences and appropriate stabilisation of stockpiles are to be provided as
detailed on the drawings.
2. Sediment fences will:
a) Be installed where shown on the drawings, and elsewhere at the discretion of the
site superintendent to contain the coarser sediment fraction (including
aggregated fines) as near as possible to their source.
b) Have a catchment area not exceeding 720 square meters, a storage depth
(including both settling and settled zones) of at least 0.6 meters, and internal
dimensions that provide maximum surface area for settling, and
c) Provide a return of 1-meter upslope at intervals along the fence where catchment
area exceeds 720 square meters, to limit discharge reaching each section to 10
litres/second in a maximum 20-year tc discharge.
3. Sediment removed from any trapping device will be disposed in locations where
further erosion and consequent pollution to down slope lands and waterways will
not occur.
4. Water will be prevented from directly entering the permanent drainage system
unless it is relatively sediment free (i.e. the catchment area has been permanently
landscaped and/or likely sediment has been treated in an approved device).
Nevertheless, stormwater inlets will be protected.
5. Temporary soil and water management structures will be removed only after the
lands they are protecting are stabilised.
7.6 Waste Management Conditions
Acceptable bind will be provided for any concrete and mortar slurries, paints, acid
washings, lightweight waste materials and litter. Clearance service will be provided at
least weekly.
7.7 Site Inspection and Maintenance
1. A self-auditing program will be established based on a Check Sheet. A site
inspection using the Check Sheet will be made by the site manager:
• At least weekly.
• Immediately before site closure.
• Immediately following rainfall events in excess of 5mm in any 24-hour period.
Co14189.00-03a.rpt 17
• Recording maintenance requirements (if any) for each sediment control device
• Recording the volumes of sediment removed from sediment retention systems,
where applicable
• Recording the site where sediment is disposed
• Forwarding a signed duplicate of the completed Check Sheet to the project
manager/developer for their information
2. In addition, a suitably qualified person will be required to oversee the installation
and maintenance of all soil and water management works on the site. The person
shall be required to provide a short monthly written report. The responsible person
will ensure that:
• Repairs are undertaken as required
• Essential modifications are made to the plan if and when necessary
The report shall carry a certificate that works have been carried out in accordance with
the plan.
3. Waste bins will be emptied as necessary. Disposal of waste will be in a manner
approved by the Site Superintendent.
4. Proper drainage will be maintained. To this end drains (including inlet and outlet
works) will be checked to ensure that they are operating as intended, especially that,
• No low points exist that can overtop in a large storm event
• Areas of erosion are repaired (e.g. lined with a suitable material) and/or velocity
of flow is reduced appropriately through construction of small check dams of
installing additional diversion upslope.
• Blockages are cleared (these night occur because of sediment pollution,
sand/soil/spoil being deposited in or too close to them, breached by vehicle
wheels, etc.).
5. Sand/soil/spoil materials placed closer than 2 meters from hazard areas will be
removed. Such hazard areas include and areas of high velocity water flows (e.g.
waterways and gutters), paved areas and driveways.
6. Recently stabilised lands will be checked to ensure that erosion hazard has been
effectively reduced. Any repairs will be initiated as appropriate.
7. Excessive vegetation growth will be controlled through mowing or slashing.
8. All sediment detention systems will be kept in good, working condition. In
particular, attention will be given to:
a) Recent works to ensure they have not resulted in diversion of sediment laden
water away from them
Co14189.00-03a.rpt 18
b) Degradable products to ensure they are replaced as required, and
c) Sediment removal, to ensure the design capacity or less remains in the settling
zone.
9. Any pollutants removed from sediment basins or litter traps will be disposed of in
areas where further pollution to down slope lands and waterways should not occur.
10. Additional erosion and/or sediment control works will be constructed as necessary
to ensure the desired protection is given to down slope lands and waterways, i.e.
make ongoing changes to the plan where it proves inadequate in practice or is
subjected to changes in conditions at the work site or elsewhere in the catchment.
11. Erosion and sediment control measures will be maintained in a functioning
condition until all earthwork activities are completed and the site stabilised
12. Litter, debris and sediment will be removed from the gross pollutant traps and trash
racks as required.
Co14189.00-03a.rpt 19
8 CONCLUSION
This Civil Engineering Report has been prepared to support the Development
Application for the proposed multistorey residential building at 34-46 Flushcombe
Road, Blacktown NSW.
A civil engineering strategy for the site has been developed which provides a best
practice solution within the constraints of the existing landform and proposed
development layout. Within this strategy a stormwater quality management strategy has
been developed to reduce pollutant loads in stormwater leaving this site. The
stormwater management for the development has been designed in accordance with
Blacktown City Council’s Part J of DCP2015 and WSUD Developers Handbook 2020.
During the construction phase, a Sediment and Erosion Control Plan will be in place to
ensure the downstream drainage system and receiving waters are protected from
sediment laden runoff.
The site is located in an area that requires an OSD, as such an OSD is required for the
development. OSD storage of 75m3 has been adopted for this site.
Rainwater reuse is proposed via 25m3 of rainwater storage to reduce demand on non-
potable uses by 80%.
It is recommended the management strategies in this report be approved and
incorporated into the future detailed design.
Co14189.00-03a.rpt 20
9 REFERENCES
• Part J, Development Control Plan (2015), Blacktown City Council
• WSUD Developer Handbook – MUSIC Modelling and Design Guide 2020,
Blacktown City Council
• Water Sensitive Urban Design – Technical Guidelines for Western Sydney (May
2004), URS Australia Pty Ltd
• Managing Urban Stormwater, Soils and Construction (1998) – The Blue Book,
Landcom
Co14189.00-03a.rpt 22
Co14189.00-03a.rpt 23
1/15/2021 https://www.s3qm.com.au/_/#/dtc/Blacktown
https://www.s3qm.com.au/_/#/dtc/Blacktown 1/7
Deemed to Comply pre screening tool Blacktown City Council offers some Development Applicants the opportunity to use this on-line deemed to comply tool.
If you have any suggestions or questions about the tool we welcome them.
In the first instance please contact Tony Merrilees at Council by email at [email protected] or Mark Liebman by email at [email protected]
Initial Questions Locate your site in the map by zooming and panning. Once your development site has been lcoated, click on the location to mark it on the map.
Alternatively, enter in the site coordinates (Latitude and Longitude) in the space provided, below.
Latitude
-33.7706
Longitude
150.9087
Address
+
-
1/15/2021 https://www.s3qm.com.au/_/#/dtc/Blacktown
https://www.s3qm.com.au/_/#/dtc/Blacktown 2/7
Development Zoning and Footprint Development footprint means the area of new work which is the subject of the development application. It refers only to new external work. It includes new paved areas and new buildings and new for old building replacements. The use of this tool is restricted to sites with a development footprint of 40,000m or less.
Zone of land Business
2
2
Is the proposed development a proposal to subdivide business or industrial land?
No
OSD Calculations This development requires an OSD system.
The questions that follow will establish the requirements for the On Site Stormwater Detention system. These questions refer to OSD terminology as per the following diagram
Area of Site Draining to OSD (m ) 1592
OSD Location Below Ground
Will filter cartridges be used to manage water quality? No
2
The preliminary storage requirements below the 50% AEP Weir is 47.76m and the storage below the 1% AEP weir is 72.44m .
This requirement will differ if there is a drowned orifice.
3
3
1/15/2021 https://www.s3qm.com.au/_/#/dtc/Blacktown
https://www.s3qm.com.au/_/#/dtc/Blacktown 3/7
Discharge Location Data (5) RL of 50% AEP Orifice Centreline 63.96
Number of 50% AEP Orifices 1
(6) RL of 1% AEP Orifice Centreline 63.79
Number of 1% AEP Orifices 1
(7) RL of invert to discharge to the next pit downstream 62.75
(8) RL of obvert of the higher downstream pit outlet pipe (Council or Internal)
1/15/2021 https://www.s3qm.com.au/_/#/dtc/Blacktown
https://www.s3qm.com.au/_/#/dtc/Blacktown 4/7
Internal) 63.00
OSD Data
(3) Length of Emergency Overflow Weir (m) 1.9
(2) RL of soffit (top) of the OSD Storage Tank 64.54
OSD Summary Table
Site Area NOT draining to OSD (m²) 0
Bypass (%) 0
(2) RL of soffit (top) of tank 64.54
(1) Average RL of the base of the OSD Tank 63.79
(3) RL of Emergency Overflow Weir 64.43
RL of 50% AEP Overflow Weir 64.21
(5) RL of 50% AEP Orifice Centre Line 63.96
(6) RL of 1% AEP Orifice Centre Line 63.79
(7) RL of Invert of Discharge to Downstream Pit 62.75
(8) RL of Obvert of pit outlet pipe 63
Minimum RL of Garage Floor 64.64
Minimum RL of Habitable Floor 64.74
OSD Volume
1/15/2021 https://www.s3qm.com.au/_/#/dtc/Blacktown
https://www.s3qm.com.au/_/#/dtc/Blacktown 5/7
OSD Volume
Required Storage BELOW the 50% AEP Overflow Weir (m ) 47.76
Required Storage BELOW Emergency Overflow Weir (m ) 72.436
Discharge Details
Discharge Location Drainage Pit
Orifice Details
Number of 50% AEP Orifices 1
Number of 1% AEP Orifices 1
50% AEP Orifice Diameter (mm) 77.5
1% AEP Orifice Diameter (mm) 133.5
Access grates to be provided such that the maximum reach from any point in the tank to the nearest grate is 2m.
3
3
Water Quality Section 7.11 Contributions Plan Applicable? This development is subject to a water quality Section 7.11 Contributions Plan.
This Business development is required to make a financial contribution under S7.11
Contact Council's S7.11 Officer for information about the Contribution.
1/15/2021 https://www.s3qm.com.au/_/#/dtc/Blacktown
https://www.s3qm.com.au/_/#/dtc/Blacktown 6/7
Water Conservation This proposed Business development must meet a water conservation target of an 80% reduction in non- potable demand using rainwater.
At the completion of this questionaire, you will be directed to the water quality and conservation modelling tool where you can describe more details about the development and assess the water conservation performance.
Nearest watercourse Is the proposed development within 40m of a watercourse? No
Is there a groundwater control applicable to the proposed development? Does the proposed development (located > 40m away from the nearest watercourse) involve cut/fill > 1.5m from the predeveloped surface?
Yes
Your proposal requires the submission of a Groundwater Assessment and Management Plan as part of your DA in accordance with Section 4.6 of Part J of the Blacktown DCP 2015
Summary of Obligations Your proposal requires the submission of a Groundwater Assessment and Management Plan as part of your DA in accordance with Section 4.6 of Part J of the Blacktown DCP 2015
Applicable Development Controls
Water Conservation Yes
On-site water quality No
On-site works, Section 7.11 or VPA Section 7.11 mandatory contribution required
On-site detention Yes
1/15/2021 https://www.s3qm.com.au/_/#/dtc/Blacktown
https://www.s3qm.com.au/_/#/dtc/Blacktown 7/7
Groundwater (more than 1.5m of cut or fill or more than 1m of cut or fill if development is on waterfront land)
Yes
Waterfront Land (within 40m of a waterway) No
Please Save this record and proceed to describe the details of the development and the water quality measures. If you proceed by clicking on continue your answers will be saved and you will not be able to return to this page
Continue
Co14189.00-03a.rpt 25
Co14189.00-03a.rpt 26
Co14189.00-03a.rpt 27
Item
Consideration
Assessment
2 Entry/exit pads clear of excessive sediment deposition. . . . . . . . . . . .
3 Entry/exit pads have adequate void spacing to trap sediment. . . . . . . . . . . .
4 The construction site is clear of litter and unconfined rubbish. . . . . . . . . . . .
5 Adequate stockpiles of emergency ESC materials exist on site. . . . . . . . . . . .
6 Site dust is being adequately controlled. . . . . . . . . . . .
7 Appropriate drainage and sediment controls have been installed prior to
new areas being cleared or disturbed.
. . . . . . . . . . .
the site.
. . . . . . . . . . .
9 Drainage lines are free of soil scour and sediment deposition. . . . . . . . . . . .
10 No areas of exposed soil are in need of erosion control. . . . . . . . . . . .
11 Earth batters are free of “rill” erosion. . . . . . . . . . . .
12 Erosion control mulch is not being displaced by wind or water. . . . . . . . . . . .
13 Long-term soil stockpiles are protected from wind, rain and stormwater
flow with appropriate drainage and erosion controls.
. . . . . . . . . . .
15 Sediment-laden stormwater is not simply flowing “around” the sediment
fences or other sediment traps.
. . . . . . . . . . .
appropriate for the type of inlet structure.
. . . . . . . . . . .
17 All sediment traps are free of excessive sediment deposition. . . . . . . . . . . .
18 The settled sediment layer within a sediment basin is clearly visible
through the supernatant prior to discharge such water.
. . . . . . . . . . .
19 All reasonable and practicable measures are being taken to control
sediment runoff from the site.
. . . . . . . . . . .
20 All soil surfaces are being appropriately prepared (i.e. pH, nutrients,
roughness and density) prior to revegetation.
. . . . . . . . . . .