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280 Garfield Road East and 259 Riverstone Road – Flood Assessment Reference: R.N20909.001.01.docx Date: October 2017 Final Report A part of BMT in Energy and Environment

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280 Garfield Road East and 259 Riverstone Road – Flood Assessment

Reference: R.N20909.001.01.docx Date: October 2017 Final Report

A part of BMT in Energy and Environment

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280 Garfield Road East and 259 Riverstone Road – Flood Assessment

610 Princes Highway, Rockdale - Flood Impact Assessment 610 Princes Highway, Rockdale - Flood Impact Assessment

Prepared for: at&l

Prepared by: BMT WBM Pty Ltd (Member of the BMT group of companies)

Offices Brisbane Denver London Mackay Melbourne Newcastle Perth Sydney Vancouver

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Document Control Sheet

BMT WBM Pty Ltd 126 Belford Street Broadmeadow NSW 2292 Australia PO Box 266 Broadmeadow NSW 2292 Tel: +61 2 4940 8882 Fax: +61 2 4940 8887 ABN 54 010 830 421 www.bmtwbm.com.au

Document: R.N20909.001.01.docx

Title: 280 Garfield Road East and 259 Riverstone Road – Flood Assessment

Project Manager: Daniel Williams

Author: Daniel Williams / Stephanie Lyons

Client: at&l

Client Contact: Dane Segail

Client Reference:

Synopsis: Flood Assessment for the proposed residential development of 280 Garfield Road East and 259 Riverstone Road, Riverstone. This report details the model development, establishment of existing flood conditions and the assessment of flood impacts associated with the proposed development.

REVISION/CHECKING HISTORY

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DISTRIBUTION

Destination Revision

0 1 2 3 4 5 6 7 8 9 10

at&l.

BMT WBM File

BMT WBM Library

e

e

e

e

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280 Garfield Road East and 259 Riverstone Road – Flood Assessment ivContents

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Contents

1 Introduction 1

1.1 Background 1

1.2 Study Area 1

1.3 Report Purpose 2

2 Model Development 5

2.1 Hydrologic Model 5

2.1.1 Design Rainfall 5

2.1.2 Subcatchment Delineation 6

2.2 Hydraulic Model 6

2.2.1 Model Topography 6

2.2.2 Extents and Layout 9

2.2.3 Hydraulic Roughness 9

2.2.4 Hydraulic Structures 10

2.2.5 Boundary Conditions 10

3 Existing Conditions and Constraints 11

3.1 Existing Conditions 11

4 Assessment of Proposed Development 13

4.1 Proposed Development Details 13

4.2 Flood Impacts 15

4.3 Flood Planning Considerations 18

5 Conclusion 20

6 References 21

Appendix A Masterplan Layout A-1

Appendix B Existing Scenario Results B-1

Appendix C Developed Scenario Results C-1

Appendix D Change in Peak Flood Level D-1

List of Figures

Figure 1-1 Study Locality 3

Figure 1-2 Study Catchment and Topography 4

Figure 3-1 1% AEP Peak Flood Results – Existing Scenario 12

Figure 4-1 Proposed Development Layout and Topography 14

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280 Garfield Road East and 259 Riverstone Road – Flood Assessment vContents

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Figure 4-2 1% AEP Peak Flood Results - Developed Scenario 16

Figure 4-3 1% AEP Change in Peak Flood Level 17

Figure 4-4 1% AEP Flood Level along Channel (refer Figure 4-5) 18

Figure 4-5 1% AEP Peak Flood Levels - Developed Scenario 19

List of Tables

Table 2-1 Average Design Rainfall Intensities (mm/h) 5

Table 2-2 Adopted Hydrologic Model Roughness Values 6

Table 2-3 Adopted Model Roughness Parameters 9

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280 Garfield Road East and 259 Riverstone Road – Flood Assessment 1Introduction

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1 Introduction

1.1 Background A new 550 lot residential development is proposed for a site at 280 Garfield Road East and 259

Riverstone Road. The site is located on the alignment of a tributary of First Ponds Creek within the

Riverstone East Precinct Growth Centre, within the Blacktown City Council LGA, as shown on

Figure 1-1. Sunglow Australia is planning and coordinating the proposed subdivision of the site.

BMT WBM has been engaged by at&l on behalf of Sunglow Australia to assist in the assessment of

flood requirements for the proposed development. The provided concept masterplan for the site

has been reproduced in Appendix A.

A Water Cycle Management Report was completed by Mott MacDonald for the broader Riverstone

East Priority Growth Area to assist in the planning of an indicative lot layout for the site. The scope

of works undertaken by Mott MacDonald involved hydrologic, hydraulic and water quality

assessment of the development, aiming to provide an integrated approach to flood risk and water

cycle management. The modelling indicated that the site is subject to inundation from the tributary

of First Ponds Creek.

This study will develop local hydrologic and hydraulic models for the development site, at a finer

resolution than that completed by Mott MacDonald. Increased model resolution will enable a more

detailed representation of flood behaviour at the site to be established. The modelling tools

developed for this study will be used to re-establish existing flood conditions at the site, from which

post-development flood conditions can be assessed.

1.2 Study Area The development site is situated within the catchment of First Ponds Creek. The northern extent of

the site is bound by Garfield Road East. To the south, the site is bound by Riverstone Road. The

catchment area upstream of Garfield Road East is just over 1.0 km2, as shown in Figure 1-2. The

catchment comprises of two tributary alignments of First Ponds Creek, both flowing to the north-

west. Typically, the study area is elevated between 30 - 50 m AHD, with terrain grades of around

5%. Maximum elations of around 65 - 67 m AHD are reached along the south-eastern catchment

boundary.

Existing landuse in the study area is predominantly cleared, with pockets of industrial development

and remnant vegetation. The main residential precinct of Riverstone is located west of the

catchment, between First Ponds Creek and the larger system of Eastern Creek.

Watercourses within the site are largely modified from their natural flow conditions. The main

watercourse alignment within the catchment is located outside of the study site and is intercepted

by a number of dams before draining under Garfield Road East. The smaller tributary located near

the south-western site boundary is conveyed under Riverstone Road. This tributary alignment is

also intercepted by a number of smaller dams.

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280 Garfield Road East and 259 Riverstone Road – Flood Assessment 2Introduction

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1.3 Report Purpose This report documents the flood impact assessment in relation to the proposed development at the

280 Garfield Road East and 259 Riverstone Road subdivision. The flooding assessment incudes

consideration of the following:

existing design flood conditions (to be used as the baseline for impact assessment);

estimation of post-development flood conditions, to be informed by the proposed digital

elevation model (DEM) of the subdivision development and change in imperviousness of the

catchment; and

assessment of the impacts of the proposed development (specifically, performance of proposed

temporary detention basins and required flood planning levels).

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280 Garfield Road East and 259 Riverstone Road – Flood Assessment 3Introduction

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Figure 1-1 Study Locality

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280 Garfield Road East and 259 Riverstone Road – Flood Assessment 4Introduction

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Figure 1-2 Study Catchment and Topography

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280 Garfield Road East and 259 Riverstone Road – Flood Assessment 5Model Development

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2 Model Development

The integrated flooding and water quality management modelling for the Riverstone East Priority

Growth Area was completed by Mott MacDonald for the NSW Department of Planning and

Environment in May 2016. The flood modelling involved the development of an XP-RAFTS

hydrologic model and a TUFLOW hydraulic model. This modelling has been accepted by

Blacktown Council and currently forms the basis for flood planning in the study area.

Due to the detailed nature of local hydraulic controls and the required model representation of the

proposed subdivision development, a more detailed TUFLOW model was developed specifically for

this assessment. The Riverstone East Priority Growth Area TUFLOW model adopted a 5 m 2-D

grid cell resolution, whereas the detailed model developed for this assessment has adopted a finer

2 m resolution. Additionally, a finer resolution XP-RAFTS hydrologic model was developed to

provide inflows at key locations to the TUFLOW model.

Design flood events were simulated for the 20% AEP, 10% AEP, 5% AEP, 2% AEP and 1% AEP

magnitudes.

2.1 Hydrologic Model The hydrologic model predicts the amount of runoff from rainfall and the attenuation of the flood

wave as it travels down the catchment. This process is dependent on catchment area, slope and

vegetation; variation in distribution, intensity and amount of rainfall; and antecedent conditions of

the catchment. Runoff-routing software XP-RAFTS was used to generate flow hydrographs for the

study catchment.

2.1.1 Design Rainfall

For design events, rainfall depths are usually determined by the estimation of intensity-frequency-

duration (IFD) design rainfall curves for the catchment. Standard procedures for derivation of these

curves are defined in AR&R (2001).

Table 2-1 shows design rainfall intensities for the study area for a range of design events.

Table 2-1 Average Design Rainfall Intensities (mm/h)

Duration (hrs)

Design Event

20% AEP 10% AEP 5% AEP 2% AEP 1% AEP

0.25 87.1 104 121 144 161

0.5 58.3 69.5 80.6 95.6 107

1 36.3 43.1 49.8 59.1 66.4

2 22.2 26.3 30.4 36.1 40.8

3 16.9 19.9 23.1 27.6 31.2

6 10.9 13.0 15.2 18.2 20.8

The recently released ARR update (2016) revised the recommended application of temporal

patterns for use in design flood estimation. For simplicity, this study has adopted the temporal

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patterns and initial and continuing loss guidance in accordance with AR&R (2001). This is in

keeping with the approach adopted in the Riverstone East Priority Growth Area. For the First

Ponds Creek catchment, design temporal pattern Zone 1 and an initial loss of 10 mm and

continuing loss of 2.5 mm/h were selected for pervious areas, as is recommended for catchments

located in eastern NSW.

2.1.2 Subcatchment Delineation

The First Ponds Creek catchment area upstream of Garfield Road East was delineated into twelve

sub-catchments utilising the available LiDAR data. The Bransby-Williams approach was adopted to

determine lag times between each sub-catchment. Figure 2-1 and Figure 2-2 show the delineation

of sub-catchments for the existing and proposed development.

For the development scenario, urbanised sub-catchments were modelled using the second sub-

catchment approach, to represent the influence of the higher proportion of imperviousness in these

areas. Future urban areas were assumed to be 85% impervious and 15% pervious in accordance

with Blacktown City Council guidelines. For impervious areas, an initial loss of 2 mm and continuing

loss of 0 mm/h were applied.

The roughness values adopted in the hydrologic model are detailed in Table 2-2 and are in

accordance with those adopted in the Riverstone East Priority Growth Area XP-RAFTS model

developed by Mott MacDonald.

Table 2-2 Adopted Hydrologic Model Roughness Values

Material Description Model Roughness

(PERN)

Existing impervious areas

0.025

Existing pervious areas

0.04

Post-developed impervious areas

0.015

Post-developed pervious areas

0.035

Inflow hydrographs were determined for each sub-catchment using the XP-RAFTS software. A

range of storm durations were simulated with the XP-RAFTS software and it was found that the 90

minute rainfall event resulted in the critical flow condition at the site.

2.2 Hydraulic Model

2.2.1 Model Topography

The ability of the model to provide an accurate representation of the flow distribution on the

floodplain ultimately depends upon the quality of the underlying topographic model. For this study,

a 1 m by 1 m gridded Digital Elevation Model (DEM) was derived from the LiDAR survey datasets

captured for NSW LPI in 2011, as presented in Figure 1-2.

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Figure 2-1 RAFTS Sub-catchment delineation (Existing)

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Figure 2-2 RAFTS Sub-catchment delineation (Proposed Development)

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Topographic survey data of the study site and some of the adjacent area was provided by at&l

(adjointopo_3d.dwg) and was used to define the model elevations where available.

In the study area, the dam embankments located along the tributary watercourse alignment are

significant topographical controls to flood behaviour. These embankments range from around 0.5 m

to 2.5 m above the typical dam surface water level. The largest of these embankments is located

approximately 170 m upstream of Garfield Road East and spans around 230 m across the entire

width of the floodplain. Adopting a model grid resolution of 2 m will ensure that the dam

embankment crests are captured from the input DEM to be represented within the hydraulic model.

2.2.2 Extents and Layout

Consideration needs to be given to the following elements in constructing the model:

topographical data coverage and resolution,

location of recorded data (e.g. levels/flows for calibration),

location of controlling features (e.g. dams, levees, bridges),

desired accuracy to meet the study’s objectives, and

computational limitations.

With consideration to the available survey information and local topographical and hydraulic

controls, a 2D model was developed covering the study area at a 2 m grid cell resolution. With a 2

m grid TUFLOW samples elevations at 1 m intervals, at grid cell sides, corners and centres, hence

fully utilising the resolution of the input DEM. A model resolution of 2 m is generally required to

adequately represent complex overland flow paths in urban environments, which will be of

relevance when representing the proposed subdivision development within the model.

2.2.3 Hydraulic Roughness

The development of the TUFLOW model requires the assignment of different hydraulic roughness

zones. These zones are delineated from aerial photography and cadastral data identifying different

land-uses (e.g. forest, cleared land, roads, urban areas, etc.) for modelling the variation in flow

resistance.

The hydraulic roughness is one of the principal calibration parameters within the hydraulic model

and has a major influence on flow routing and flood levels. The roughness values adopted for use

in this study have been based on available literature and previous experience in modelling

catchments of a similar nature and are presented in Table 2-3.

Table 2-3 Adopted Model Roughness Parameters

Land Use Manning’s ‘n’

Cleared / parkland areas 0.04

Dams and waterways 0.03

Urban blocks 0.10

Roads 0.02

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Land Use Manning’s ‘n’

Car parks and industrial storage areas 0.03

In order to represent the hydraulic impact of buildings within the TUFLOW model, urban blocks

have been represented with a higher Manning’s roughness values. This represents the combined

flow impedance offered by buildings, gardens and fences. This provides a suitable representation

of the constriction of flood waters imposed by these features, whilst accounting for potential flood

storage volumes within or under the buildings themselves and within other urban areas such as

gardens.

2.2.4 Hydraulic Structures

The drainage culvert beneath Riverstone Road is the main existing hydraulic structure of note

within the study area extent. Incorporation of this structure in the model provides for flow

conveyance through the road embankment whilst simulating the hydraulic losses associated with

the structure and its influence on peak water levels within the study area.

The culvert has been modelled as a 1-D structure embedded within the 2-D domain. This enables

an accurate representation for structures smaller than the model grid resolution. This culvert has

been assumed to be a 450 mm diameter pipe. For the purposes of design flood modelling the

hydraulic structures have been modelled at full capacity, with no allowance for additional structure

blockage.

2.2.5 Boundary Conditions

The downstream model boundary has been represented as a constant water level and is located a

suitable distance downstream from the study site. This allows for the adopted model boundary

conditions to be resolved and not influence flood behaviour at the site.

Each dam within the catchment was modelled with a typical initial water level. This is the standard

approach to simulate a conservative scenario whereby the dam is full at the onset of a flood event.

Local hydrological inflows for sub-catchments located within the study area catchment were input

using runoff hydrographs from the XP-RAFTS hydrological model.

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280 Garfield Road East and 259 Riverstone Road – Flood Assessment 11Existing Conditions and Constraints

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3 Existing Conditions and Constraints

3.1 Existing Conditions The establishment of existing design flood conditions provides for description of the:

general flood behaviour throughout the study area,

existing flooding conditions based on design flood events, and

constraints and limitations to potential development with respect to flooding regimes.

TUFLOW model results for the existing scenario are shown for the 20% AEP, 10% AEP, 5%, AEP,

2% AEP and 1% AEP design flood events in Appendix B and are used as a baseline for the

assessment of the proposed development in Section 4.

Under existing conditions the site is flooded along the alignment of the small tributary watercourse

located near the south-west boundary. At the 1% AEP design event, there is minor spill-over from

the dams, with overland flow paths typically less than 0.2 m in depth and with velocities of 0.2 – 0.6

m/s. Figure 3-1 presents the flow distribution across the floodplain for the 1 % AEP design event.

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Figure 3-1 1% AEP Peak Flood Results – Existing Scenario

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280 Garfield Road East and 259 Riverstone Road – Flood Assessment 13Assessment of Proposed Development

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4 Assessment of Proposed Development

Civil works (i.e. earthworks, buildings, altered channel alignments) within a floodplain can

potentially increase flood levels, re-distribute flows, increase inundation times and increase

velocities. These impacts need to be minimised, especially in populated areas and in areas of

agricultural or environmental significance.

4.1 Proposed Development Details The proposed subdivision development on the site consists of around 150 residential lots. BMT

WBM was provided with the proposed masterplan for the subdivision of the site (included as

Appendix A).

A number of key components were required to accurately model the potential flood impacts

associated with the proposed subdivision development, including:

increase in impervious area associated with urban development and the impact of flow regimes,

design levels for external surfaces, and

modification to existing watercourses including the inclusion of storage basins.

In order to simulate the impact of the proposed subdivision on existing flood flows in the study area,

the XP-RAFTS hydrological model was modified to represent the increase in impervious area

associated with the developed scenario. Alterations made to the XP-RAFTS model were described

in Section 2.1. Inflow hydrographs were determined for each sub-catchment using the developed

scenario XP-RAFTS model.

The proposed development involves significant cut and fill earthworks to be undertaken across the

site. The proposed finished ground levels and lot layout for the site are presented in Figure 4-1.

The design strings of proposed finished ground levels for the subdivision were provided by at&l

(17-10-24 DESIGN TIN_DWG.dwg). These were processed into a 1 m gridded DEM to be

incorporated into the TUFLOW model for the development scenario.

The proposed subdivision layout includes five detention basins within the study area. These have

been included to manage the increase in runoff and flow rates from the site due to the higher

proportion of impervious area associated with the developed scenario. Proposed basin locations

are included on Figure 4-1. The detention basins were sized by at&l using Blacktown City Council’s

deemed to comply OSD tool. The corresponding basin outlet details were incorporated into the

TUFLOW model.

Another key feature of the proposed topography of the site is the provision of an open channel

along the existing tributary alignment adjacent to Basin A in Figure 4-1. The channel widens to form

into a secondary storage structure with capacity of around 3000 m3. The secondary storage outlet

is a 525 mm diameter RCP. Upstream of the storage area, the channel is confined and is around

1.5 m deep and is roughly trapezoidal in shape. The design strings provided by at&l contain details

of the channel and secondary storage, and as such both are represented in the finished ground

level DEM.

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Figure 4-1 Proposed Development Layout and Topography

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The inflow hydrographs derived from the developed scenario XP-RAFTS model were applied to the

modified TUFLOW model (i.e. proposed finished ground level DEM to replace existing LiDAR input

DEM where appropriate) and the entire suite of design floods were simulated. TUFLOW model

results for the developed scenario are shown for the 20% AEP, 10% AEP, 5%, AEP, 2% AEP and

1% AEP design flood events in Appendix C.

The 1% AEP design peak flood conditions for the developed scenario is presented in Figure 4-2.

For the developed scenario, the previous overland flow path through the site is now simulated as

two distinct flow paths intercepted by Basin A and Basin B, respectively.

4.2 Flood Impacts Model results for the development scenario have been used to assess relative flood impacts of

developing the site. Afflux diagrams are presented for peak water level for the 20% AEP, 10%

AEP, 5% AEP, 2% AEP and 1% AEP design events in Appendix D. These diagrams show the

afflux (difference) between flood conditions resulting from developing the site and the existing

baseline flood conditions in the vicinity of the site. They are useful for presenting the magnitude

and extent of flood impacts as a result of developing the site.

Figure 4-3 presents the peak flood level impact for the 1 % AEP design event. Within the site, the

re-alignment of the tributary watercourse into a defined channel and storage system has

significantly limited the flood inundation extents at the 1% AEP event. Almost all of the previously

inundated areas on-site are removed as a result of the proposed development earthworks, seen as

the bright green extents in Figure 4-3.

Inclusion of detention storage at Basin A has resulted in reduced peak flows off the site. Previously,

flows from the upper catchment would exceed the capacity of the existing dam and flow in a north-

westerly direction toward Clarke Street (downstream of Basin B). These flows are now attenuated

and discharged offsite immediately downstream of Basin A. Consequently, a reduction in off-site

peak flood levels downstream of Basin B of around 0.1 – 0.2 m is simulated for the developed

scenario.

Minor off-site impacts can be seen downstream of Basin D at the model boundary. This is due to

the concentration of flow out of Basin D and into an engineered swale running parallel with Garfield

Road East. Previously the flow off the undeveloped catchment flowed freely across Garfield Road

East. It is noted that the significant reduction in flood inundation extent at this location is likely

favourable over minor increases within the road boundary. Furthermore, it is understood that

Garfield Road East will be upgraded, rendering the marginal increase in flood level only temporary.

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Figure 4-2 1% AEP Peak Flood Results - Developed Scenario

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Figure 4-3 1% AEP Change in Peak Flood Level

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280 Garfield Road East and 259 Riverstone Road – Flood Assessment 18Assessment of Proposed Development

S:\WATER\PROJECTS\N20909_Riverstone\Docs\R.N20909.001.01.docx

4.3 Flood Planning Considerations The Blacktown City Council Development Control Plan (DCP) contains a number of controls in

relation to flood management of new subdivisions. Key controls of relevance to this site are:

no residential allotments are to be located at a level lower than the 1% Annual Exceedance

Probability (AEP) flood level plus a freeboard of 500 mm (i.e. within the ‘flood planning area’),

and

roads are generally to be located above the 1% AEP level.

Figure 4-5 shows the 1% AEP design flood condition at each basin location. A peak flood profile

along the defined channel in the south west corner of the site is also provided in Figure 4-4.

In regard to the planning controls detailed above, proposed roads on-site are located above the 1%

AEP design flood levels determined in this study. Residential allotments will be required to fulfil the

flood planning control requirements detailed in Council’s DCP i.e. they must be located above the

1% AEP design flood level plus 500 mm freeboard.

Figure 4-4 1% AEP Flood Level along Channel (refer Figure 4-5)

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280 Garfield Road East and 259 Riverstone Road – Flood Assessment 19

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Figure 4-5 1% AEP Peak Flood Levels - Developed Scenario

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280 Garfield Road East and 259 Riverstone Road – Flood Assessment 20Conclusion

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5 Conclusion

This Flood Assessment has included the development of a XP-RAFTS hydrologic model and a

TUFLOW hydraulic model for the First Ponds Creek catchment area upstream of Garfield Road

East. The models have been used to define existing flood conditions for a range of flood

magnitudes and form a baseline with which to assess potential flood impacts associated with the

proposed subdivision development.

The existing design flood conditions for the range of flood event magnitudes are represented in

Appendix B through a flood mapping series, incorporating peak flood extents, levels, depth and

velocity distribution. Developed scenario flood conditions for the range of flood events are

presented in Appendix C.

Overall, the developed flood conditions are largely compatible with existing conditions within the

site. The impacts of the proposed development are presented in terms of relative change from the

existing peak flood level distributions, and are presented in Appendix D.

The proposed subdivision development at 280 Garfield Road East and 259 Riverstone Road,

largely satisfies the flooding requirements in terms of manageable flood condition on-site.

Assessment of the proposed design surface level against design flood levels may need further

consideration in regard to fulfilling the flood management controls as outlined in the Blacktown City

Council DCP.

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280 Garfield Road East and 259 Riverstone Road – Flood Assessment 21References

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6 References

at&l (-) Stage 1 DA Villa Rosa 280 Garfield Road and 259 Riverstone Road

Blacktown City Council (2016) Blacktown City Council Growth Center Precincts Development

Control Plan

Mott MacDonald (2016) Water Cycle Management Report Riverstone East

Sitios Urban Design (2017) 280 Garfield Road and 259 Riverstone Road Masterplan - Staging

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280 Garfield Road East and 259 Riverstone Road – Flood Assessment A-1Masterplan Layout

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Appendix A Masterplan Layout

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Issue

Description

Date

100mm on Original

Project

Title

Client

Project No. IssueDrawing No.

Grid

Checked

Designed

Drawn

Height

A1

Datum

Approved

Status

ScalesBar Scales

Civil Engineers and Project Managers

02 9923 1055

02 9439 1777

Level 7, 153 Walker Street

North Sydney NSW 2060

Tel:

Fax:

ABN 96 130 882 405

www.atl.net.au

[email protected]

THIS DRAWING CANNOT BE COPIED OR REPRODUCED IN ANY FORM

OR USED FOR ANY OTHER PURPOSE OTHER THAN THAT ORIGINALLY

INTENDED WITHOUT THE WRITTEN PERMISSION OF AT&L

Key Plan

F:\17-494 Garfield Road\Drgs\Civil\Final\1000_DA Stage 1 Package\C1003.dwg

C1003

GENERAL ARRANGEMENT

PLAN

FOR APPROVAL

NOT TO BE USED FOR CONSTRUCTION

JB

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VILLA ROSA

280 GARFIELD ROAD AND

259 RIVERSTONE ROAD

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P1
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ISSUE FOR CLIENT REVIEW
AutoCAD SHX Text
18-10-17
AutoCAD SHX Text
P2
AutoCAD SHX Text
ISSUE FOR DEVELOPMENT APPLICATION
AutoCAD SHX Text
27-10-17
AutoCAD SHX Text
0
AutoCAD SHX Text
1 : 1250 @ A1 1 : 2500 @ A3
AutoCAD SHX Text
25
AutoCAD SHX Text
50
AutoCAD SHX Text
75
AutoCAD SHX Text
100
AutoCAD SHX Text
125m
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280 Garfield Road East and 259 Riverstone Road – Flood Assessment B-1Existing Scenario Results

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Appendix B Existing Scenario Results

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280 Garfield Road East and 259 Riverstone Road – Flood Assessment C-1Developed Scenario Results

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Appendix C Developed Scenario Results

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280 Garfield Road East and 259 Riverstone Road – Flood Assessment D-1Change in Peak Flood Level

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Appendix D Change in Peak Flood Level

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