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Appendix D - Acid Sulphate and Dewatering Managment Plan · OPW23/0179
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ADG Consulting Pty Ltd All Correspondence
ACN: 630 555 225 PO Box 6405
ABN: 98 630 555 225 Yatala DC QLD 4207
P 07 3801 1564
E [email protected]
W adgconsulting.com.au
Dewatering Management Plan
Proposed Residential Development:
Lot 1 on MCH3881, 128 Gympie Terrace, Noosaville, Queensland
May 2023
Prepared for:
Michael and Caroline Cullen
c/‐ SCG Consulting Engineers & Sparks Architects
Acid Sulfate Soil Assessment On‐site Wastewater Management Contaminated Land Assessment & Remediation
Dewatering Management Environmental Management Plans Surface & Groundwater Investigation & Monitoring
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Report details
Project ref: ADG1535.23
ADG Project Contact: Michael Campbell
Report title: Dewatering Management Plan
Proposed Residential Development:
Lot 1 on MCH3881, 128 Gympie Terrace, Noosaville, Queensland
Version: Rev0
Author(s): ADG
Reviewer: Michael Campbell
Client: Michael and Caroline Cullen
c/‐ SCG Consulting Engineers & Sparks Architects
Client contact: Tom Harrington – SCG Consulting Engineers
Distribution date: 31 May 2023
Distributed to: SCG Consulting Engineers & Sparks Architects
Copies: 1 PDF
ADG Consulting Pty Ltd
Michael Campbell BEnvSc, BSc[Hons],
DipProjMgt, DipOHS, DipBusMgt, DipBus(Quality Auditing)
MEIANZ, MALGA, MASSI
Director & Principal Environmental Scientist
Date: 31 May 2023
This document and all its content is copyright. Apart from fair dealing for the purposes of study, research, criticism
and/or review as permitted under the Copyright Act 1968, no part of the content may be reproduced, reused or
redistributed without the prior written permission of ADG Consulting Pty Ltd.
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Table of Contents
1 INTRODUCTION 1
1.1 PROPOSED DEVELOPMENT 1
1.2 RELEVANT GUIDELINES 1
1.3 GENERAL ENVIRONMENTAL DUTY 1
1.4 DMP OBJECTIVES 2
1.5 SCOPE OF WORK 2
2 SITE CHARACTERISTICS 3
2.1 PROPERTY DESCRIPTION 3
2.2 SURROUNDING ENVIRONMENT 3
2.3 TOPOGRAPHY 3
2.4 GEOLOGY & SOILS 3
2.5 HYDROGEOLOGY 3
3 PREVIOUS INVESTIGATIONS 4
3.1 PACIFIC GEOTECH PTY LTD 2022 4
3.1.1 SOILS 4
3.1.2 GROUNDWATER 4
3.2 GROUNDWATER QUALITY 4
4 WATER QUALITY OBJECTIVES 6
4.1 RECEIVING ENVIRONMENT 6
4.2 DEVELOPMENT OF WATER QUALITY OBJECTIVES 6
4.3 PROPOSED WATER QUALITY OBJECTIVES 7
5 DEWATERING METHODOLOGY 9
5.1 BASEMENT EXCAVATION AND SHORING 9
5.2 GROUNDWATER EXTRACTION 9
5.3 EXTRACTION/DISCHARGE RATES AND VOLUME 9
5.3.1 DEWATERING EXTRACTION CALCULATION BASED ON SUBSURFACE SOIL PROFILE 9
5.4 DEWATERING DURATION 10
5.5 GROUNDWATER DRAWDOWN 10
5.6 GROUNDWATER TREATMENT 11
5.7 NOMINATED HOLD POINTS 11
6 WATER QUALITY MANAGEMENT 12
6.1 RESPONSIBILITY 12
6.2 OPERATIONAL POLICY 12
6.3 PERFORMANCE CRITERIA 12
6.4 IMPLEMENTATION STRATEGY 12
6.4.1 GROUNDWATER TREATMENT SYSTEMS 12
6.4.2 DEWATERING STRATEGY 13
6.4.3 INITIAL PUMP‐OUT 13
6.5 MONITORING 13
6.5.1 VISUAL MONITORING 13
6.5.2 WATER QUALITY MONITORING 13
6.5.3 MONITORING RESPONSIBILITIES 14
6.6 MAINTENANCE 15
6.7 REPORTING 15
6.8 CONTINGENCIES 15
7 NOISE & ODOUR MANAGEMENT 17
7.1 RESPONSIBILITY 17
7.2 OPERATIONAL POLICY 17
7.3 PERFORMANCE CRITERIA 17
7.4 IMPLEMENTATION STRATEGY 17
7.4.1 NOISE 17
7.4.2 ODOUR 17
7.5 MONITORING 17
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7.6 REPORTING 18
7.7 CONTINGENCIES 18
8 LIMITATIONS 19
9 REFERENCES 20
APPENDIX A: FIGURES
APPENDIX B: DRDMW LICENCED BORE SEARCH
APPENDIX C: BASEMENT INSTALLATION PLAN (DRAFT)
APPENDIX D: DEWATERING CALCULATION OUTPUT
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1 Introduction
ADG Consulting Pty Ltd (ADG) was engaged by Michael and Caroline Cullen care of SCG Consulting
Engineers (SCG) & Sparks Architects to prepare a Dewatering Management Plan (DMP) for the proposed
residential development within property described as Lot 1 on MCH3881, situated at 128 Gympie
Terrace, Noosaville, Queensland.
1.1 Proposed development
The proposed development comprises the construction of a two‐storey residential building (2 unit
dwellings) overlying a single level in‐ground basement on the 556 m2 site. Supplied information indicates
that excavations to facilitate the basement construction will extend to a maximum of approximately
2.2 m below ground level (bgl) to approximately ‐0.5 m Australian Height Datum (AHD). Localised deeper
excavations may be required for the construction of other structural elements (i.e. footings and pile caps),
where required.
Groundwater seepage was recorded at depths of between 1.0 to 1.1 mbgl (equating to an approximate
elevation of 0.6 m AHD), during preliminary geotechnical works (drilling) on the site by Pacific Geotech in
October 2022. Given the sites proximity to the Noosa River and the presence of groundwater within the
excavation extent, dewatering will be necessary to allow the basement to be constructed in dry
conditions.
1.2 Relevant guidelines
The DMP was prepared with reference to the following documents:
Australian and New Zealand Guidelines for Fresh and Marine Water Quality. 2018. Australian and
New Zealand Governments and Australian state and territory governments (ANZG), Canberra ACT,
Australia.
Australian and New Zealand Guidelines for Fresh and Marine Water Quality. 2000. Australian and
New Zealand Environment and Conservation Council and Agriculture and Resource Management
Council of Australia and New Zealand (ANZECC/ARMCANZ).
Environmental Protection (Water & Wetland Biodiversity) Policy 2019. Department of Environment
and Science (DES), Queensland Government.
Noosa River environmental values and water quality objectives. 2022. Department of Environment
and Science (DES), Queensland Government.
Guidelines for Managing Risks in Recreational Water. 2018. Australian Government, National Health
and Medical Research Council (NHMRC).
Monitoring and Sampling Manual 2018, Version 2 June 2018. 2018. Department of Environment and
Science (DES).
Queensland Water Quality Guidelines 2009, Version 3. 2013. The Department of Environment and
Heritage Protection (DEHP).
1.3 General environmental duty
The Environmental Protection Act 1994 describes that all persons in Queensland have a “General
Environmental Duty” and that “a person must not carry out an activity that causes, or is likely to cause
environmental harm unless the person takes all reasonable and practicable measures to prevent or
minimise the harm”.
The Act requires that appropriate action be taken to report that environmental harm is occurring or has
the potential to occur, unless the harm is authorised under an environmental protection policy, an
environmental management program, a development approval, or an environmental protection order.
This is known as the “Duty to Notify”. Failure to fulfil this duty is an offence and may result in prosecution.
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1.4 DMP objectives
The objectives of the DMP are to:
Describe the dewatering methodology, groundwater treatment, monitoring and reporting
procedures to be employed at the site during dewatering activities.
Provide effective management procedures to prevent environmental harm resulting from the
discharge of extracted groundwater from the site.
1.5 Scope of work
To achieve the investigation objectives, the following scope of work was undertaken:
A desktop study including:
1. Review of the development proposal and proposed shoring/dewatering designs.
2. Review of geology and soil maps for the area.
3. Search of groundwater bores licensed by the Department of Regional Development,
Manufacturing and Water (DRDMW) within a 200 m radius of the site.
4. Review of relevant existing reports and groundwater data from the local area.
5. Review of current aerial photographs of the site and surrounds.
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2 Site characteristics
2.1 Property description
The site is described as Lot 1 on MCH3881, and is situated at 128 Gympie Terrace, Noosaville, Queensland.
From recent available aerial mapping (Nearmap) the site has been cleared of aboveground infrastructure
(circa June‐July 2022) and is generally rectangular in shape. The site has a total area of 556 m2. The site
locality is shown in Figure 1, Appendix A.
2.2 Surrounding environment
The surrounding environment and land use is described briefly in Table 1.
Table 1 Surrounding land use and environment
Direction Environment
North Chaplin Park, then Noosa River.
East Vacant land, then 2‐ storey residential lots, then canal network associated with Noosa
River.
South Gympie Terrace, then multiple residential lots.
West Easement, then Mill Street.
2.3 Topography
The site and surrounding land is considered to be generally level (PG, 2022), with the site surface
elevations ranging between approximately 1.6 m to 2.0 m AHD from the southern boundary toward the
north of the site.
2.4 Geology & soils
The surface geology at the site is mapped as being Pleistocene aged sandy mud, muddy sand and minor
gravel: estuarine channels and banks. The dominant rock type is identified as miscellaneous
unconsolidated sediments as referenced through detailed surface geology (accessed via Queensland
Globe online, 31 May 2023).
The Acid Sulfate Soils (ASS) map 1:100,000 scale categorises the site as ‘SEA’ or ‘Disturbed Land with
probability of ASS’, indicating that the site is likely to contain acid sulfate soils but the type and depth to
ASS has not been defined (accessed via Queensland Globe online, 31 May 2023).
2.5 Hydrogeology
A search of groundwater bores licensed by DRDMW was conducted by ADG on 31 May 2023. The search
identified no licensed bores within a 200 m radius of the site. A map showing the bore search area is
provided in Appendix B.
Based on the local geology and topography, and the site’s proximity to the Noosa River, the inferred
groundwater flow is to the north and/or east. Groundwater beneath the site is likely to be hydraulically
connected to the river and/or canal network, therefore saline groundwater conditions are anticipated,
and additional saltwater intrusion is likely to occur during dewatering.
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3 Previous investigations
This DMP is based on site specific information sourced from the following, provided to ADG by
SCG Consulting Engineers:
Acid Sulfate Soil Investigation, Proposed Residential Development, 128 – 132 Gympie Terrace,
Noosaville. November 2022. Pacific Geotech Pty Ltd. Ref: PG‐9236, 2022‐10‐31, ASR VER 1.
Geotechnical Investigation, Proposed 128 – 132 Gympie Terrace, Noosaville. November 2022. Pacific
Geotech Pty Ltd. Ref: PG‐9236, 2022‐11‐08, GR VER 1.
Proposed Dual Occupancy – 128 Gympie Terrace, Noosaville, QLD. Drawing set Rev C September
2022. DME Projects Pty Ltd (Refer Appendix C).
It is noted that dilapidation reports for surrounding structures and services are proposed to be
undertaken prior to commencement of construction and dewatering, however are to be provided to
Council separately from this DMP.
A brief discussion of relevant soil and groundwater conditions is provided below.
3.1 Pacific Geotech Pty Ltd 2022
A Geotechnical Investigation and concurrent Acid Sulfate Soils Investigation was undertaken at the site
in October 2022 (reported November 2022) by Pacific Geotech Pty Ltd (PG).
3.1.1 Soils
A total of four (4) boreholes (BH01 to BH04) were drilled on the proposed development footprint to
between 4.0 and 9.0 mbgl.
The subsurface profile encountered is generally described as clay and sand fill material at the ground
surface, extending to depths ranging between 1.0 m and 1.1 m. Fill material is underlain by natural sand
and silty sand which is initially medium dense, becoming loose with depth, extending to depths ranging
between 2.5 m and 2.9 m. The upper‐level sand is underlain by very dense, indurated sand which extends
to depths ranging between 2.8 m and 3.2 m. This indurated sand is underlain by stiff to hard, silty and
sandy clay, which extends to the borehole termination depths.
Alongside the Geotechnical Investigation (2021), Acid Sulfate Soil (ASS) samples were collected at 0.5 m
intervals in BH01 & BH02 to 4.0 m depth. A total of sixteen (16) samples were collected for ASS screening
and eight (8) samples were selected for further analysis by the Chromium Reducible Sulfur suite (CRS).
ADG notes that the testing was limited to two boreholes with ASS testing to 4.0 m depth, and PG reports
that within part of this depth profile the natural sands are considered to contain potential ASS requiring
liming at rates of up to 8 kg/tonne. All excavated spoil from depths between 1.5 to 2.5 mbgl within the
excavation footprint will be appropriately neutralised with lime and validated in accordance with
recommendations by PG in the ASS Investigation Report (PG, 2022).
3.1.2 Groundwater
During drilling activities for the Preliminary Geotechnical Investigation, groundwater seepage/inflow was
encountered at 1.0 to 1.1 m depth below the ground surface (approx. 0.6 m AHD)(PG, 2022).
It should be noted however, that groundwater depths and ground moisture conditions are affected by
weather and climatic conditions, tidal variations, surface and subsurface drainage/permeability
conditions, and human influence and will therefore vary with time. Groundwater levels are expected to
be similar to the water level in the canal to the east and river to the north, albeit somewhat a dampened
response to tidal variations.
3.2 Groundwater quality
No groundwater quality data was obtained by PG as part of the preliminary geotechnical investigation.
However, based on numerous groundwater investigations and dewatering monitoring projects that have
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been undertaken by ADG throughout the Noosa Coast Region in recent years, our understanding of the
groundwater quality in the region is provided below:
Groundwater is generally mildly acidic to neutral, with pH levels ranging from approximately 5.5 to
6.5 and electrical conductivity ranging from brackish to saline between 2,000 µS/cm to
48,000 µS/cm. Groundwater pH has the potential to reduce (become more acidic) following
oxidisation of PASS as dewatering progresses, particularly if re‐wetting of the soils occurs.
Dissolved oxygen levels in static groundwater typically range from approximately 35 – 40 %
saturation.
The groundwater associated with indurated sand strata is moderately to highly turbid as a result of
staining and organic content.
Concentrations of dissolved metals are typically below the available marine water trigger values
(MWTV’s) provided in ANZECC/ARMCANZ (2000) for the receiving waters, however elevated levels
of aluminium and particularly iron are expected in the untreated groundwater and have the
potential to increase following oxidisation of PASS as dewatering progresses or as a result of existing
acidic groundwater conditions.
Given the location and previous use of the site, groundwater impacts resulting from site
contamination are not anticipated.
A groundwater investigation will be undertaken at the commencement of dewatering as described in
Section 6.5.2 of this report. This assessment will be representative of the groundwater being extracted
and treated from the entire site, as opposed to localised monitoring well data which is often misleading.
Based on previous experience with dewatering in the area, ADG expects the groundwater to require
treatment to increase pH and dissolved oxygen levels, as well as reduce turbidity, suspended sediments
and dissolved metal concentrations prior to being discharged to the Noosa River.
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4 Water quality objectives
4.1 Receiving environment
It is proposed to discharge extracted groundwater to the stormwater network via gully pit on Gympie
Terrace (adjacent the bus stop) which discharges to the canal network associated with the Noosa River
located approximately 60 m east of the site. The exact location of the receiving waters/environment will
be confirmed on commencement of dewatering.
The receiving environment in this location identifies as a moderately disturbed, marine canal
environment. The following section establishes water quality objectives (WQOs) to ensure that the
environmental values of the receiving waters are protected and maintained.
4.2 Development of water quality objectives
WQOs have been developed to support and protect the designated environmental values (EVs) for the
receiving environment. The WQOs have been developed with reference to the following guideline
documents:
Australian and New Zealand Guidelines for Fresh and Marine Water Quality 2018. (ANZG 2018) The
selected trigger values apply to moderately disturbed systems to provide a 95% level of species
protection for marine waters.
Environmental Protection (Water & Wetland Biodiversity) Policy 2019. 2019. Queensland
Government.
Noosa River environmental values and water quality objectives. 2022. DES.
Queensland Water Quality Guidelines, Version 3, September 2009. 2013. DEHP.
The Australian and New Zealand Guidelines for Fresh and Marine Water Quality by the Australian and
New Zealand Environment and Conservation Council and Agriculture and Resource Management Council
of Australia and New Zealand (ANZECC/ARMCANZ, 2000), has undergone review, with the publication of
the 2018 version. The revised Australian and New Zealand Guidelines for Fresh and Marine Water Quality
2018 is a joint initiative between the Australian and New Zealand Governments and Australian state and
territory governments (ANZG, 2018) and supersedes the ANZECC/ARMCANZ 2000 publication. Where
ANZECC/ARMCANZ (2000) is referenced, the relevant sections are still relevant and consistent with the
updated ANZG 2018 publication, as referenced in the ANZG 2018 publication.
The Queensland Water Quality Guidelines 2009 (DEHP, 2013) was made pursuant to the provisions of the
Environmental Protection (Water) Policy 1999, now the Environmental Protection (Water & Wetland
Biodiversity) Policy 2019 (the EPP(Water)), which is a subordinate legislation under the Environmental
Protection Act 1994 and was developed as the State response to the ANZECC/ARMCANZ (2000)
Guidelines. The EPP(Water) provides a framework for:
Identifying environmental values for Queensland waters, and deciding the water quality objectives
to protect or enhance those environmental values.
Including the identified environmental values and water quality objectives under Schedule 1 of the
EPP (Water).
WQOs are long term goals for surface water quality management. They are indicators established for
receiving waters to support and protect the designated Environmental Values (EVs) for those waters. DES
(2022) describes that for slightly to moderately disturbed waters, the guideline values should be
compared with the median of values at a test site, whilst ANZG (2018) stresses that the aquatic ecosystem
guideline values are triggers to further action, are inherently conservative, and that the response to non‐
compliance should match the magnitude and impacts (if any) of the exceedance.
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Regardless of the WQOs adopted in this DMP, the General Environmental Duty set out in the EP Act is
paramount, which requires that “a person must not carry out an activity that causes or is likely to cause
environmental harm unless the person takes all reasonable and practicable measures to prevent or
minimise the harm”.
4.3 Proposed water quality objectives
The proposed water quality objectives that have been developed for the discharge of extracted
groundwater from the site are provided in the Tables below. All water discharged from the site must
comply with the discharge criteria provided in Table 2. In addition, the receiving water quality within a
20 m radius of the discharge point entry to the receiving water shall comply with the receiving water
criteria provided in Table 3. Receiving waters data will be assessed against background monitoring data
if non‐compliant results are obtained at the receiving waters monitoring location.
Table 2 Discharge criteria
Parameter Criteria
Physico‐chemical
pH (pH units) 6.5 – 8.51
Dissolved oxygen (% saturation) ≥802
Suspended solids (mg/L) ≤501,2
Turbidity (NTU) ≤502
Litter None visible
Totals metals (µg/L)
Aluminium No ANZG criteria / 2003
Iron No ANZG criteria / 3003
Table notes:
1. QWQG 2009 (2013) Refer to Table 8.2.1. Summary of design objectives for management of stormwater quality and flow –
construction phase of development in Queensland.
2. Typical discharge criteria recognised throughout Queensland & NSW.
3. Criteria subject to anticipated Development Application (DA) notice and conditions by Noosa Shire Council.
Table 3 Receiving waters criteria
Parameter Criteria
Physico‐chemical
pH (pH units) 7.8 – 8.31
Dissolved oxygen (% saturation) 85 – 1051
Suspended solids (mg/L) ≤141
Turbidity (NTU) ≤81
Dissolved metals (µg/L)
Aluminium No relevant ANZG criteria available
Arsenic 2.32*
Cadmium 5.52
Chromium 4.42
Copper 1.32
Iron No relevant ANZG criteria available
Lead 4.42
Nickel 702
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Parameter Criteria
Zinc 82
Mercury 0.42
Totals metals (µg/L)
Aluminium No ANZG criteria / 2003
Iron No ANZG criteria / 3003
Table notes:
1. DES (2022). Noosa River environmental values and water quality objectives (canal).
2. ANZG (2018). Supersedes ANZECC/ARMCANZ (2000) ‐ Marine water trigger values for 95% species protection.
3. Criteria subject to expected condition in Development Application (DA) notice by Noosa Shire Council.
* = Insufficient data to derive a reliable trigger value. Low reliability value adopted (refer ANZECC/ARMCANZ (2000) Section
8.3.7.
Although ADG has not been provided a copy of the DA notice and conditions for the proposed
development, based on previous dewatering projects in the Sunshine/Noosa Coast Region it is expected
that total iron and aluminium concentrations as listed in Table 3 (above) are likely to be conditioned by
Noosa Shire Council for compliance. It should be noted that these concentrations are considered to be
onerous with respect to the risk‐based (worst‐case) bioavailable trigger value criteria contained in ANZG
2018 & ANZECC/ARMCANZ (2000) for marine water (moderately disturbed) 95% species protection, and
are likely to be difficult to achieve given the groundwater conditions encountered in the locality on
previous dewatering projects on the Sunshine/Noosa Coast.
Prior to discharge to the stormwater system or any waterway, discharges are to be tested to meet the
requirements of the ANZG 2018 & ANZECC/ARMCANZ (2000) Guidelines for Fresh and Marine Water
Quality. There is currently no chemical toxicant trigger value criteria available for total or dissolved (i.e.
bioavailable) concentrations of aluminium or iron for marine or estuarine waters under the Australian
and New Zealand Guidelines for Fresh and Marine Water Quality Guidelines (ANZG 2018 &
ANZECC/ARMCANZ 2000 – i.e. ANZECC Guidelines) or the Guidelines for Managing Risks in Recreational
Waters (NHMRC 2008), with regards to managing environmental impacts to the waterway.
In addition, Section 5 (Guidelines for recreational water quality and aesthetics) of the ANZECC/ARMCANZ
(2000) Guidelines (per section 5.2 thereof) was superseded by the Guidelines for Managing Risks in
Recreational Water in 2008 (NHMRC, 2008). Therefore, a reference to the ANZECC/ARMCANZ (2000)
Guidelines is by association and extension a reference to the current 2008 NHMRC Guidelines. The 2008
NHMRC Guidelines contain no criteria for aluminium, and only includes an aesthetic criterion for iron –
noting this is an aesthetic criterion derived from the Australian Drinking Water Guidelines on the basis of
ingesting 2L of the recreational water solution per day. ANZECC/ARMCANZ (2000) Section 5.2.3.3, notes
that as a general guideline, under Toxic Chemicals, ‘Higher concentrations of toxicants may be tolerated
occasionally if it assumed that no person will ingest more than a maximum of 100 mL water during a
normal swimming session (NHMRC 1990) compared with 2L/d for potable water’, and Section 3.1.1.3,
under Risk based approach of the guidelines, ‘The guideline trigger values are based on bioavailable
concentrations, and hence are relatively conservative when compared with total concentrations in the
field, so the use of the decision frameworks will increase guideline concentrations in most cases’.
Therefore, any chemical toxicant trigger values would require reassessment and likely increase upwards
of any ANZG 2018 &/or ANZECC/ARMCANZ (2000) Guideline trigger values due to the slightly to
moderately disturbed nature (and thereby reduced sensitivity) of the receiving waters.
In conditioning more onerous criteria, rather than the available marine chemical toxicant trigger value
criteria contained within the ANZG/ANZECC Guidelines, an unachievable constraint may be placed on the
development. This DMP has allowed for contingency measures to be incorporated into the treatment
and discharge system if required, including silt curtains to be installed within the receiving waterway
surrounding the discharge location, or further onsite treatment measures such as filtration, to prevent
and/or minimise as far as reasonably practicable the potential for release of suspended solid loads into
the broader receiving waterway.
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5 Dewatering methodology
5.1 Basement excavation and shoring
It is understood that the excavation/basement perimeter will be stabilised along the perimeter of the
basement excavations using a contiguous secant pile wall (refer to supplied indicative basement design
at Appendix C). Excavations to facilitate the construction of the basement will extend to approximately
2.3 m below ground level, which corresponds to a maximum elevation of approximately ‐0.5 m AHD.
Localised deeper excavations may be required for construction of other structural elements (i.e. footings
& pile caps).
All excavated spoil from depths between 1.5 to 2.5 mbgl within the excavation footprint will be
appropriately neutralised with lime and validated in accordance with recommendations by PG in the ASS
Investigation Report (PG, 2022).
It is expected that the development will include a ‘tanked’ basement to prevent the requirement for a
permanent dewatering facility at the site.
5.2 Groundwater extraction
Dewatering is anticipated to be undertaken using a series of 6.0 m length, 40 mm diameter PVC spears
installed to below maximum excavation depth at 1.5 m intervals around the internal perimeter of the
basement excavation (refer to supplied indicative shoring design at Appendix C).
The basement excavation must be dewatered to a minimum of approximately 1.0 m below the deepest
point of excavation to allow construction to be undertaken in dry conditions. The water table is therefore
expected to be lowered by a minimum of approximately 2.1 m to around ‐1.5 m AHD. It is expected that
the cone of depression in the standing groundwater table will be predominantly limited to within the site
boundaries.
It is proposed that the development will include a ‘tanked’ basement to prevent the requirement for a
permanent dewatering facility at the site. Similarly, no permanent groundwater dewatering is proposed
or likely to occur as a result of the development, with all services and pipework proposed to be situated
above standing groundwater elevations (that is, at elevations above 0.6 mAHD) and subject to the
nominated hold points at Section 5.7. Where any deviation is proposed from this arrangement, all
pipework within the saturated zone, that outlets direct to waterways must be fitted with buried
headstocks at suitable intervals to prevent ongoing dewatering of groundwater along pipework bedding.
5.3 Extraction/discharge rates and volume
5.3.1 Dewatering extraction calculation based on subsurface soil profile
The dewatering extraction rate, area of influence and cone of depression has been estimated using the
Western Australian Department of Water and Environmental Regulation Cone of Depression Calculator.
The calculation results are based on the following parameters (as provided by SCG) and known site‐
specific conditions. The following is applicable to the basement excavations spanning across the lot:
Approximate length of excavation = 20 m
Approximate width of excavation = 11 m
Reduction in depth of groundwater across the basement footprint/excavation = 2.1 m
Approximate depth of saturated aquifer = 10 m (standardised conservative value applied)
The soil profile of comprised predominantly of fine to medium grained silty sands, which has a hydraulic
conductivity of 8.2 m/day, or equivalent 0.0000949 L/sec (WA Calculator). The results of the calculation
are shown in Table 4 below, and a copy of the output is provided in Appendix D.
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Table 4 Dewatering extraction rate results
Output Result
Effective radius of dewatering spears (m) 8
Dewatering radius of influence (m) 61
Discharge rate (L/sec) 6
Discharge rate (L/hr) 21,600
Establishment of cone of depression (hours) 62
Based on the above inputs, a groundwater flow rate of approximately 6 L/sec or 360 L/min or 21,600 L/hr
has been predicted for the development, with the estimated cone of depression radius to be
predominantly limited to within 3 m of the secant pile shoring wall. Flow rates are predicted to be highest
during initial drawdown of the groundwater table within the basement excavation footprint, and
reducing to approximately 5 L/sec following establishment of the cone of depression within the
excavation. Flow rates may fluctuate due to tidal variations, generally approximately ± 0.5 m, and will
also be influenced by rainfall and surface water collection within the basement excavation footprint
noting the underlying predominantly sand profile encountered during geotechnical investigations.
Regardless of the contractor employed, groundwater treatment systems should be installed with
capability for treating flow rates of up to 8 to 10 L/sec, as a contingency against higher than anticipated
flow rates exceeding the estimated 6 L/sec as a result of varying ground conditions across the extent of
excavation.
However, it should be noted that the WA Calculator provides a conservative assessment of inflows to an
excavation footprint based on area and depth, but does not take account of the method of perimeter
piling i.e. steel sheet pile, which will inhibit lateral inflows. Also note that the cone of depression radius
measure includes water table depressions of 1 mm depth or more, so any significant depression of the
water table is limited to much closer to the spear point dewatering spears (generally within 3 to 10 m
from the shoring wall in fine‐medium grained sands, depending on density of the strata).
5.4 Dewatering duration
Dewatering will be necessary throughout the basement construction phase, which is expected to require
dewatering for approximately 8 to 12 weeks. To minimise the potential impacts during construction of
short‐term dewatering, periods of active dewatering will be minimised as much as possible. However,
ADG notes that once active dewatering has commenced, dewatering will not be able to be ceased until
both: a) the basement hydrostatic uplift forces have been compensated to the satisfaction of the
consulting RPEQ engineer; and b) potential hydraulic loading on the external face of the sheet pile shoring
system has been compensated to the satisfaction of the consulting RPEQ engineer and shoring
contractor.
5.5 Groundwater drawdown
Groundwater drawdown caused by dewatering has the potential to create settlement in unconsolidated
sediments and loose sands. It is noted that dilapidation reports for surrounding structures and services
have been undertaken which were not supplied to ADG for the purposes of preparing this DMP, and are
to be provided to Council separately from this DMP.
Groundwater drawdown may also oxidise potential acid sulfate soils within the cone of depression,
subsequently producing acidic groundwater conditions and mobilising heavy metals. Monitoring of the
extracted untreated groundwater will be undertaken to detect potential in‐situ oxidation, as required
and at the frequencies stated in Section 6.5.2. Groundwater monitoring bores for groundwater level
gauging external to the excavation footprint are unable to be established and monitored prior to and
during construction on the site, due to limited space (SCG Consulting Engineers).
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A plan showing the proposed shoring and dewatering system is provided at Appendix C.
5.6 Groundwater treatment
All extracted groundwater will be treated on‐site using available technologies prior to discharge to the
stormwater network. The following treatment measures (or similar depending on final dewatering
contractor selection) will be adopted, and will be installed and operational prior to the commencement
of dewatering:
1. A groundwater pH buffering treatment system (primary treatment)
2. A sedimentation tank to provide additional residence time and sedimentation (secondary
treatment).
3. Installation of fine media filtration to retain suspended sediments and/or heavy metals (tertiary
treatment), if required.
Details of the treatment systems and methodologies are provided in Section 6 of this report.
Note: Consideration should be taken, regarding placement of treatment gear on site to enable easy
cleaning and maintenance throughout the dewatering phase for the project. Consider the potential
requirement for regular de‐sludging of sedimentation tank/s to suitable area onsite, if available (cost
minimisation).
5.7 Nominated Hold Points
In accordance with anticipated DA Conditions, nominated hold points to be enacted during construction
have been proposed to facilitate for certification by the suitably qualified person experienced with Acid
Sulfate Soils, as well as Council Development Engineer to ensure all possible avenues for continual
dewatering below permanent groundwater level, including around pipework bedding that outlet to
waterways, are appropriately sealed. The nominated hold points regarding dewatering for this project
are:
1. Prior to commencement of dewatering/initial pump out
2. At finished excavation level, prior to blinding layer application
3. External to basement service installation trench opening/s prior to backfilling.
The above nominated hold points are subject to confirmation by the consulting engineer, and liaison with
council representatives and the Site Manager.
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6 Water quality management
6.1 Responsibility
The Site Manager is ultimately responsible for implementing the water quality management procedures
described in this DMP.
6.2 Operational policy
To prevent impacts on the receiving waters by effectively treating all extracted groundwater prior to
discharge from the site.
6.3 Performance criteria
The performance criteria for the discharge of extracted groundwater are the water quality objectives
provided in Table 2 and Table 3 in Section 4 of this report. Both the discharge and receiving waters (within
a 20 m radius of the stormwater discharge point) will be assessed against the WQOs to ensure that the
environmental values of the waterway are maintained. Receiving waters data will also be assessed
against background monitoring data if non‐compliant results are obtained at the receiving waters
monitoring location.
6.4 Implementation strategy
All extracted groundwater will be treated on‐site using available technologies prior to discharge to the
stormwater network. The treatment system described in Section 6.4.1 will be adopted, installed and
operational prior to the commencement of dewatering.
6.4.1 Groundwater treatment systems
Subject to final appointment of shoring and dewatering contractors (who all generally have different
treatment systems), the following treatment systems are generally proposed for dewatered groundwater
treatment prior to discharge. Regardless of the contractor employed, groundwater treatment systems
should be installed with capability for treating flow rates of up to 8 to 10 L/sec, as a contingency against
higher than anticipated flow rates exceeding the estimated 6 L/sec as a result of varying ground conditions
across the extent of excavation.
Primary treatment
A groundwater treatment system will be installed to provide primary treatment of the extracted
groundwater. The system will provide the following capabilities:
1. A baffled treatment tank with 5 kL minimum capacity
2. Automated in‐line chemical dosing systems for the addition of buffering solutions and coagulants
3. A filtration system to reduce fine particulates (if required)
4. Emergency response alarms for non‐routine situations.
Based on the estimated extraction rate, this system will provide approximately nine minutes contact time
during the initial chemical dosing, prior to secondary treatment using a sedimentation tank. Primary
treatment tank will be vertically stacked on the secondary treatment tank wherever practicable to
minimise site area required for groundwater treatment equipment.
Secondary treatment
A 23 kL sedimentation tank will be utilised to provide the necessary residence time for secondary
treatment of the groundwater prior to discharge to the stormwater system. Based on the estimated
groundwater extraction rate of approximately 21,600 L/hr (equivalent 360 L/min) from Section 5.3.1 of
this Report, one sedimentation tank will provide approximately forty‐two minutes retention time
following primary treatment of the extracted groundwater. This is considered to be sufficient secondary
settling / retention time based on extensive prior experience on other sites in similar ground conditions.
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Tertiary treatment – may be required following initial testing of extracted groundwater.
A filtration treatment system with specialised fine filtration media and chlorine dosing will be utilised to
provide the required heavy metal removal (specifically for total and dissolved iron) where not
precipitated and retained within the sedimentation tank/s (secondary treatment). This treatment system
will provide tertiary treatment of the groundwater prior to offsite discharge. This type of fine media
filtration treatment system is a forced‐flow system under pressure, and generally capable of treating flow
rates of up to 20 L/sec per filtration unit (therefore residence time is inconsequential to treatment quality
achieved).
Tertiary treatment will only be required if the required water quality is unable to be achieved following
primary and secondary stages of treatment. Subject to the results of field and laboratory testing during
the pre‐discharge monitoring event.
6.4.2 Dewatering strategy
The Site Manager, Dewatering Contractor and ADG Consulting must formulate a dewatering strategy to
ensure that the dewatering treatment system is sufficient to meet the requirements of the project and
that the necessary equipment can be accommodated within the site prior to the commencement of
dewatering.
Where the construction of the proposed development requires occupation of the road reserve (verge
area and/or road formation) for either short term or long term, a road reserve permit must be obtained
from Council prior to any occupation of the road reserve.
6.4.3 Initial pump‐out
Prior to discharge of any extracted groundwater to the canal system, the following pre‐dewatering
procedure will be undertaken:
1. The basement area will be excavated down to the standing groundwater level.
2. The initial dewatering discharge will be directed (via the treatment systems) into the excavation and
allowed to infiltrate/recharge the aquifer. This process will provide initial clarification of the extracted
groundwater as disturbed sediment loads are typically reduced following the initial pump‐out.
3. Samples of the treated groundwater will be recovered and analysed for the parameters detailed in
Table 2 and Table 3.
4. The extracted groundwater will be directed into the canal system following confirmation that the
water quality complies with the discharge criteria.
6.5 Monitoring
6.5.1 Visual monitoring
Visual inspections of the site and dewatering equipment shall be undertaken daily by the Site Manager
to identify the following:
Quantity of chemical product within the dosing system
Effective operation of all dewatering treatment equipment
Short circuiting of water around baffles and filter media in sediment tanks, where required to be
installed.
Visible hydrocarbon sheens and odours
Green blue or extremely clear water indicating high levels of dissolved aluminium.
6.5.2 Water quality monitoring
Water quality monitoring will be undertaken for the duration of dewatering activities at the site by a
suitably qualified and independent person. The monitoring will include analysis of the extracted
groundwater, treated discharge water and off‐site monitoring in the receiving waters (in the mixing zone
within a 20 m radius of the discharge point). The exact location within the receiving waterway (Noosa
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River) is to be confirmed, however it is anticipated to be directly north of the site. Background water
quality monitoring of field parameters will also be conducted during each sampling event, if applicable.
Background samples will be recovered from the river, either upstream or downstream from the receiving
water location (tide dependant).
The proposed monitoring locations are shown in Figure 1, Appendix A are a subject to confirmation
following mobilisation of dewatering gear to site.
Monitoring will be undertaken at the following frequencies:
Daily monitoring of field parameters (pH, electrical conductivity, dissolved oxygen, temperature and
turbidity) in the treated discharge water and pH of the untreated extracted groundwater (to
determine potential acidification). Daily monitoring will be undertaken by a suitably trained site
employee under the supervision of the Site Manager.
Weekly monitoring of field parameters (pH, electrical conductivity, dissolved oxygen, temperature
and turbidity) in the untreated extracted groundwater, treated discharge water, receiving waters
and background waters by ADG Consulting.
Weekly laboratory analysis of treated discharge water and receiving waters for suspended solids
and dissolved 0.45µm filterable metals (aluminium, arsenic, cadmium, chromium, copper, iron, lead,
nickel, zinc and mercury). Total aluminium and iron will also be analysed for, if required.
Pre‐discharge/initial monitoring of field parameters (pH, electrical conductivity, dissolved oxygen
and oxidation‐reduction potential) in the extracted groundwater (prior to treatment) to assess
changes in groundwater chemistry associated with PASS oxidation.
Pre‐discharge/initial laboratory analysis of extracted groundwater (prior to treatment) for
suspended solids, dissolved 0.45µm filterable metals (aluminium, arsenic, cadmium, chromium,
copper, iron, lead, nickel, zinc and mercury) and for soluble sulfate and chloride to assess changes
in groundwater chemistry associated with PASS oxidation. Total aluminium and iron will also be
analysed, if required.
Laboratory analysis of untreated groundwater would also be performed periodically (monthly) if
changes in untreated groundwater pH levels are detected that may indicate local acidification, and
to determine any changes in local groundwaters that may require further investigation of potential
environmental impacts.
All samples will be recovered by a suitably qualified Environmental Scientist and submitted to a National
Association of Testing Authorities (NATA) accredited laboratory for analysis.
6.5.3 Monitoring responsibilities
The persons responsible for undertaking the compliance monitoring described in Section 6.5.2 above are
shown in Table 5.
Table 5 Monitoring responsibilities
Activity Frequency Responsibility Person
Monitoring of field parameters in discharge water
Daily Site Manager Site Manager
and untreated extracted groundwater
Monitoring of field parameters in untreated
Environmental
extracted groundwater, discharge water, Weekly ADG Consulting
Consultant
receiving waters and background waters
Laboratory analysis of samples recovered from Environmental
Weekly ADG Consulting
discharge water and receiving waters Consultant
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Monitoring of field parameters in extracted Environmental
Weekly ADG Consulting
groundwater (pre‐treated) Consultant
Laboratory analysis of samples recovered from Initially, then as Environmental
ADG Consulting
extracted groundwater (pre‐treated) required Consultant
6.6 Maintenance
The groundwater treatment systems must be regularly maintained. Maintenance must include:
Regular cleaning and or replacement of the filters within the filtration unit, where required to be
installed.
Regular removal of sediment from the sedimentation tank. The sediment must be either returned
to the excavation pit for dewatering and bulking out with excavated material, or removed from the
site by a licensed liquid waste contractor.
Regular check of the dosing system and top‐up of buffering solutions and flocculants.
6.7 Reporting
Dewatering management procedures and monitoring results will be reviewed by ADG Consulting weekly
to ensure that the treatment procedures are effective, and that the receiving waters are not being
impacted by the extracted groundwater being discharged.
The following reporting procedures will be adopted:
A summary report will be prepared upon completion of the initial pre‐discharge monitoring. The
report will be submitted to the Site Manager, Dewatering Contractor, and NSC upon request.
Weekly interim reports will be prepared upon receipt of laboratory data for each round of ongoing
compliance monitoring. The interim reports will display all data obtained during the previous
monitoring event, and provide comments and recommendations based on the results.
A dewatering compliance report will be prepared on completion of the project (upon request).
The above reports will be prepared by ADG Consulting and provided to the Site Manager and Dewatering
Contractor as they become available. The reports will include all water quality results and comparison to
the WQOs, corrective actions and recommendations made to the Site Manager and Dewatering
Contractor during the monitoring period.
The Site Manager must keep records of complaints, volumes of chemicals used, and treatment methods
employed. These records must be available on‐site at all times and submitted to NSC by the Site Manager
upon request.
6.8 Contingencies
If water quality monitoring indicates ongoing exceedances of the performance criteria, and the water
quality objectives for the receiving waters cannot be met, then corrective actions will be adopted as
necessary. Possible contingencies may include one or more of the following:
Installation of additional sedimentation tanks to provide increased residence time and assist with
the retention of precipitated iron hydroxides, other heavy metals and/or suspended sediments.
Installation of additional flocculant and/or coagulant dosing systems to assist in precipitation of
suspended sediments and/or heavy metals.
Installation of activated carbon filtration or other fine media filtration to retain suspended
sediments and/or heavy metals.
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Install a floating sediment curtain/s around the stormwater termination point in the receiving
waterway to prevent unsightly plumes and contain sediment and/or heavy metals for periodic
removal (subject to approval by Noose Shire Council).
Preventive and corrective actions shall be taken in the event that groundwater monitoring
observations indicate that unexpected groundwater contamination has been encountered during
dewatering. The most appropriate action(s) shall be dependent on the stage of construction and
risk of adverse impacts to groundwater users and the receiving environment.
Any modification to the dewatering system and pumping rates shall be in consultation with a
suitably qualified scientist/geotechnical/engineer.
Following heavy rainfall all ponded surfaces waters are to meet discharge criteria (Table 3) prior to
offsite discharge. Where discharge criteria not met, Site Manager to obtain approval from
Dewatering Contractor regarding treating surface waters with treatment gear before offsite
discharge.
Pumping systems and shoring works to be maintained in fit for purpose state by Dewatering
Contractor and/or shoring contractor. In the event that dewatering equipment has failed and is
likely to cause a significant impact on the environment, or surrounding properties (i.e. flooding) the
Dewatering Contractor is to be contacted immediately. The Principal Contractor, in consultation
with the Dewatering Contractor shall be responsible in rectifying the failure in a practicable time
frame to minimise potential impacts. Equipment, spare parts, materials and tools necessary to
manage aspects of the system/s which present a high risk of significant impacts in the event of
failure (if any) shall be readily available.
Construction vibrations could potentially cause settlement in the loose upper level sands, thereby
damaging nearby structures founded in these strata. Prior to commencement of construction on
site (including staged works), it is recommended that a detailed dilapidation survey be undertaken
to establish the condition of all existing adjacent structures, roads and services.
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7 Noise & odour management
7.1 Responsibility
The Project Manager is responsible for ensuring the appropriate management of noise and odour during
dewatering operations.
7.2 Operational policy
To minimise noise and odour emissions generated from the site during dewatering.
7.3 Performance criteria
The appropriate criteria to measure the performance of dewatering management at the site are provided
below.
1. No noise or odour related complaints received from neighbouring residents or the community.
2. No degradation of air quality due to fumes or odours emanating from the dewatering process.
7.4 Implementation strategy
Noise and odour emissions will be managed as described in the following sections.
7.4.1 Noise
All dewatering equipment must be operated appropriately and maintained in good working order. All
dewatering systems and plant must be fitted with the appropriate noise reduction equipment to comply
with the performance criteria. Non‐complying dewatering plant will be replaced or repaired as necessary.
It is proposed to employ noise mitigation strategies including use of electric pumps and dewatering
systems rather than diesel powered equipment. Noise attenuation blankets and screens will be installed
around noise generating dewatering pumps and equipment where practicable. Noise monitoring
equipment (unattended) will be installed by the site manager prior to commencement and monitored for
the duration of dewatering.
7.4.2 Odour
All dewatering plant must be fitted with the appropriate emission reduction devices. Where practicable,
all dewatering plant will be sealed to prevent the release of odours to the atmosphere. Fine mist odour
control sprays will be applied to reduce offensive odours if complaints are received from neighbouring
residents.
7.5 Monitoring
An inspection of the site and dewatering equipment shall be undertaken daily by the Site Manager to
identify the following:
Excessive noise being generated by the dewatering systems and plant; and
Strong or offensive odours being generated by the dewatering equipment and/or extracted
groundwater.
Noise monitoring equipment (unattended, continuous logging) is proposed to be installed by the Site
Manager prior to commencement and monitored for the duration of dewatering. The Environmental
Protection (Noise) Policy 2019 (EPP(Noise)) identifies specific acoustic quality objectives (noise criteria)
to assist in preventing significant impacts on noise sensitive receptors and as a guide to long‐term
acoustic quality for sensitive receptors. The primary EPP(Noise) criteria relevant to this investigation is
outside a dwelling (i.e. adjacent dwellings), which should not have noise at levels in the daytime or
evenings greater than 50dB(A) LAeq,adj,1hr. This means that noise levels in the receiving environment
outside of nearby dwellings (i.e. on balconies) should not exceed an equivalent sound energy as would
be received from a one hour continuous sound of 50 decibels on the A‐weighted scale (adjusted for tonal
character perceptible by the human ear).
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While this report has not been generated for the purpose of assessing compliance with the requirements
of workplace health and safety legislation, it is noted that a person conducting a business or undertaking
must ensure that workers are not exposed to noise that exceeds the exposure standard for noise. The
exposure standard for noise is defined in the Work Health & Safety Regulation 2011 (QLD) as LAeq,8h of
85 dB(A) or an LC,peak of 140 dB(C). As such, it is considered appropriate to adopt these exposure
standards to assess average and peak noise generated at the site with the potential to affect exposure
levels of nearby sensitive receptors (noting there will be some attenuation between source and receptors
and actual noise experienced by receptors would need to be measured at the receptor location).
7.6 Reporting
The Site Manager must keep records of complaints, monitoring records (including continuous noise
monitoring data), and corrective and preventive actions/methods employed for noise abatement. These
records must be available on‐site at all times and submitted to NSC by the Site Manager upon request.
7.7 Contingencies
If noise levels consistently exceed the performance criteria, temporary acoustic barriers will be
constructed around the offending dewatering systems and plant. Odour control sprays will be applied as
necessary to mask odour emissions if complaints are received from neighbouring residents. This may
include the direct injection of deodorisers to the groundwater treatment system.
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8 Limitations
ADG Consulting Pty Ltd has prepared this report for Michael and Caroline Cullen and SCG Consulting
Engineers in accordance with the agreed scope of work. The services performed by ADG have been
conducted in a manner consistent with the normal level of care and expertise exercised by members of
the environmental consulting profession. No other warranty or guarantee, expressed or implied, is made
as to the professional advice included in this report.
This report is solely for the use of Michael and Caroline Cullen and SCG Consulting Engineers and ADG
accepts no responsibility for the use of any part of this report for any other purpose or by third parties,
as it may not contain sufficient information for the purposes of other parties or users. This report must
only be presented in full, and may not be used for any other objective, except where prior written
approval is obtained from ADG. This report does not comment on legal obligations, as legal advice can
only be given by qualified legal practitioners.
The information contained in this report is provided to minimise potential impacts on the receiving
environment, however implementation of the described management procedures does not guarantee
that the objectives will be achieved.
The information contained in this report is considered to be accurate at the date of issue. Subsurface
conditions, including contaminant concentrations can change in space and time, either through natural
processes or by the accidental or intentional addition of contaminants to a site. Where conditions
encountered subsequently at the site are significantly different from those reported herein, ADG must
be notified and be provided the opportunity to review the conclusions and recommendations of this
report.
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9 References
ANZG 2018. Australian and New Zealand Guidelines for Fresh and Marine Water Quality. Australian and
New Zealand Governments and Australian state and territory governments, Canberra ACT, Australia.
ANZECC/ARMCANZ. 2000. Australian and New Zealand Guidelines for Fresh and Marine Water Quality.
Australian and New Zealand Environment and Conservation Council and Agriculture and Resource
Management Council of Australia and New Zealand.
DES. 2019. Environmental Protection (Water & Wetland Biodiversity) Policy 2019. Department of
Environment and Science, Queensland Government. Brisbane, Queensland, Australia.
DEHP. 2013. Queensland Water Quality Guidelines 2009, Version 3. Department of Environment and
Heritage Protection. Brisbane, Queensland, Australia.
DES. 2022. Noosa River environmental values and water quality objectives. Department of Environment
and Science (DES), Queensland Government.
DES. 2018. Monitoring and Sampling Manual 2018, Version 2 June 2018. Department of Environment and
Science. Brisbane, Queensland, Australia.
DNRME. 2002. Redcliffe to Teewah – Map 2 1:25,000. Queensland Department of Natural Resources and
Mines. Brisbane, Queensland, Australia.
Government of Western Australia. 2011 (Amended 2015). Cone of Depression. Department of Water and
Environmental Regulation. Accessed 31 May 2023, https://www.der.wa.gov.au/your‐environment/acid‐
sulfate‐soils/66‐cone‐of‐depression.
NHMRC. 2018. Guidelines for Managing Risks in Recreational Water. Australian Government, National
Health and Medical Research Council.
Noosa Shire Council. Noosa Council Interactive Mapping, Stormwater Infrastructure. Accessed 31 May
2023.
https://enterprise.mapimage.net/IntraMaps910/?project=Public&module=Property%20Recreation%20
Utilities&configId=64251f07‐9411‐4a61‐930e‐2bd9b45d8fff&startToken=8fb07456‐4db7‐45a7‐89df‐
64e9b5a76aff&touch=false
Pacific Geotech Pty Ltd. November 2022. Acid Sulfate Soil Investigation, Proposed Residential
Development, 128 – 132 Gympie Terrace, Noosaville. Ref: PG‐9236, 2022‐10‐31, ASR VER 1.
Pacific Geotech Pty Ltd. November 2022. Geotechnical Investigation, Proposed 128 – 132 Gympie Terrace,
Noosaville. Ref: PG‐9236, 2022‐11‐08, GR VER 1.
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Appendix A: Figures
Figure 1 Site and proposed monitoring locations
ADG1535.22 Dewatering Management Plan_Rev0_31.05.23
Page 26
Figure 1 - Site and proposed monitoring locations (to be confirmed) A product of
Lot 1 on MCH3881, 128 Gympie Terrace, Noosaville, QLD
26°23'48"S 153°3'7"E 26°23'48"S 153°3'27"E
Legend located on next page
0 50 metres
Scale: 1:1883
Printed at: A3
Print date: 31/5/2023
Not suitable for accurate measurement.
Projection: Web Mercator EPSG 102100 (3857)
For more information, visit https://qldglobe.information.qld.gov.au/help-info/Contact-
us.html
Includes material © State of Queensland 2023. You are responsible for ensuring that
the map is suitable for your purposes. The State of Queensland makes no
representation or warranties in relation to the map contents and disclaims all liability.
If imagery is displayed, imagery includes material © CNES reproduced under license
from Airbus DS, all rights reserved © 21AT © Earth-i, all rights reserved, © Planet Labs
PBC, 2023
26°24'2"S 153°3'7"E 26°24'2"S 153°3'27"E Department of Resources
Page 27
Figure 1 - Site and proposed monitoring locations (to be confirmed)
Lot 1 on MCH3881, 128 Gympie Terrace, Noosaville, QLD
Legend Attribution
Includes material © State of Queensland (Department of Resources); ©
Places: Land parcel Commonwealth of Australia (Geoscience Australia); © 21AT, © Earth-i, all rights
reserved, 2023.
Site
© State of Queensland (Department of Resources) 2021
Places: My Places
© State of Queensland (Department of Resources) 2023
Site Discharge
Receiving Waters (TBC)
Background Waters (tide
dependent, TBC)
Background Waters (tide
dependent, TBC)
Road Crossing
Bridge
Tunnel
Road
Highway
Main
Local
Private
Railway
Cities and Towns
Page 28
ADG Consulting Pty Ltd Appendix B: DRDMW licenced bore search ADG1535.22 Dewatering Management Plan_Rev0_31.05.23
Page 29
DRDMW Licensed Bore Search A product of
200 m radius
26°23'48"S 153°3'3"E 26°23'48"S 153°3'23"E
Legend located on next page
0 50 metres
Scale: 1:1883
Printed at: A3
Print date: 31/5/2023
Not suitable for accurate measurement.
Projection: Web Mercator EPSG 102100 (3857)
For more information, visit https://qldglobe.information.qld.gov.au/help-info/Contact-
us.html
Includes material © State of Queensland 2023. You are responsible for ensuring that
the map is suitable for your purposes. The State of Queensland makes no
representation or warranties in relation to the map contents and disclaims all liability.
If imagery is displayed, imagery includes material © CNES reproduced under license
from Airbus DS, all rights reserved © 21AT © Earth-i, all rights reserved, © Planet Labs
PBC, 2023
26°24'2"S 153°3'3"E 26°24'2"S 153°3'23"E Department of Resources
Page 30
DRDMW Licensed Bore Search
200 m radius
Legend Attribution
Includes material © State of Queensland (Department of Resources); ©
Registered water bores [RDMW Railway Commonwealth of Australia (Geoscience Australia); © 21AT, © Earth-i, all rights
and private] reserved, 2023.
© State of Queensland (Department of Resources) 2021
Artesian bore
Cities and Towns
Artesian bore (abandoned but © State of Queensland (Regional Development, Manufacturing and Water) 2021
useable) © State of Queensland (Department of Resources) 2023
Artesian bore (abandoned and
Road crossing
destroyed)
Bridge
Artesian bore, ceased to flow
Tunnel
Artesian bore, ceased to flow
(abandoned but useable Road
Artesian bore, ceased to flow Highway
(abandoned and destroyed) Main
Sub-artesian facility Local
Sub-artesian facility (abandoned Private
but useable)
Sub-artesian facility (abandoned
and destroyed)
Surface water facility
Surface water facility (abandoned
but useable)
Surface water facility (abandoned
and destroyed)
Places: Land parcel
Site
Places: My Places
200 m radius
Page 31
ADG Consulting Pty Ltd Appendix C: Indicative Basement Installation Plan (Draft) ADG1535.22 Dewatering Management Plan_Rev0_31.05.23
Page 32
DME
PROJECTS
Proposed Dual Occupancy
128 Gympie Terrace, Noosaville, QLD, 4566
PROPERTY DESCRIPTION
Lot 1 MCH3881
LOCALITY PLAN LGA: Noosa
Area: 556m2
QLD GLOBE
SCALE DRAWING STATUS
DME
APPROVED PROJECT DRAWING TITLE
DESIGN - DM AS SHOWN
Dale Martin - RPEQ 16845
FOR APPROVAL
C MAR 23 FURTHER ADVICE DM
HORIZONTAL DATUM PROPOSED DUAL OCCUPANCY COVER PAGE DRAWING NUMBER
DRAWN - DM B JAN 23 INFORMATION REQUEST DM
PROJECTS P.O. BOX 7481 00
A SEP 22 FOR APPROVAL DM SIPPY DOWNS, QLD, 4556
Phone: 0438 157 612
128 GYMPIE TERRACE JOB NUMBER
APPROVED 06/03/2023 ISSUE DATE DESCRIPTION BY
VERTICAL DATUM
Engineering - Design - Civil Project Services Email: [email protected] NOOSAVILLE, QLD, 4566 220508
AHD ©DME Projects Pty. Ltd.
Page 33
SCALE DRAWING STATUS
DME
APPROVED PROJECT DRAWING TITLE
DESIGN - DM AS SHOWN
Dale Martin - RPEQ 16845
FOR INFORMATION
C MAR 23 FURTHER ADVICE DM
HORIZONTAL DATUM PROPOSED DUAL OCCUPANCY NOTES DRAWING NUMBER
DRAWN - DM B JAN 23 INFORMATION REQUEST DM
PROJECTS P.O. BOX 7481 01
A SEP 22 FOR APPROVAL DM MGA 56 SIPPY DOWNS, QLD, 4556
Phone: 0438 157 612
128 GYMPIE TERRACE (AS APPLICABLE)
JOB NUMBER
APPROVED 06/03/2023 ISSUE DATE DESCRIPTION BY
VERTICAL DATUM
Engineering - Design - Civil Project Services Email: [email protected] NOOSAVILLE, QLD, 4566 220508
AHD ©DME Projects Pty. Ltd.
Page 34
T
COUNCIL FOOTPATH
N 165
SP223758
EXISTING SEWER
SW
W E CONNECTION POINT
T
S
Emt A Emt CA
SW
T
SP311624
LEGEND
T W
EXISTING BUILDINGS
SW
1.40
0 1.40
1.2
0
SP305586
T W
EXISTING CONCRETE SURFACES
1.20
E EXISTING ELECTRICAL 1.60
1.80
SW EXISTING STORM WATER 1.60
2.00
SW
TW
1.20
T EXISTING TELSTRA
W WATER RETICULATION
EET
TW
EXISTING SEWER
SW
S
1.4
0
MILL STR
17.00 EXISTING CONTOURS
EXISTING BLOCK
WALL
LOT BOUNDARIES
1.
TW
EXISTING RESIDENCE
40
SW
(ADJACENT LOT)
EXISTING FENCING 1.8
0
0000 3
SP305586 2 MCH3881
TW
1 MCH3881
SW
1.80
1.2
0
MCH3881
1 0
. 2
W
EXISTING STRIP SW T
DRAIN AND
1.80
DRIVEWAY GATE
1.80
T
W
0 1.60
0 2.4 1.6
0
1.20
SP305586
2.20
T
EXISTING WATER
W
2.20
1.800
2.0
MAIN CONNECTION
POINT
W
T 2.00
W 1.80
T 1.60 W
W
T
T W T
W
0
0
W W T
1.2
1.4
T W T
W T W T
T W T
W TW T
W
PP
W
CONTRACTOR TO DETERMINE THE EXACT
PP
LOCATION OF ALL EXISTING SERVICES IN
THE VICINITY OF THE PROPOSED WORKS
GYMPIE TCE
PRIOR TO THE START OF ANY
W
Meters
CONSTRUCTION - CONTRACTOR IS EXISTING CONCRETE DRIVEWAY 5 0 5 10
RESPONSIBLE FOR ANY DAMAGE TO EXISTING BLOCK AND ACCESS EASEMENT
EXISTING SERVICES WALL
EXISTING FEATURES PLAN 1:300
NOT FOR CONSTRUCTION SCALE 1:300 @ A3
SCALE DRAWING STATUS
DME
APPROVED PROJECT DRAWING TITLE
DESIGN - DM AS SHOWN
Dale Martin - RPEQ 16845
FOR APPROVAL
C MAR 23 FURTHER ADVICE DM
HORIZONTAL DATUM PROPOSED DUAL OCCUPANCY EXISTING FEATURES DRAWING NUMBER
DRAWN - DM B JAN 23 INFORMATION REQUEST DM
PROJECTS P.O. BOX 7481 02
A SEP 22 FOR APPROVAL DM MGA56 SIPPY DOWNS, QLD, 4556
Phone: 0438 157 612
128 GYMPIE TERRACE JOB NUMBER
APPROVED 06/03/2023 ISSUE DATE DESCRIPTION BY
VERTICAL DATUM
Engineering - Design - Civil Project Services Email: [email protected] NOOSAVILLE, QLD, 4566 220508
AHD ©DME Projects Pty. Ltd.
Page 35
N
TW
1.40
1.40
1.2
W E
0
-0.30
TW
E OVER
-0.30 BUILDING LIN
-0.30
S 1.20 -0.30
1.60
LEGEND
W
T
1.80
1.20 2.00 1.60
PROPOSED BUILDING (BASEMENT)
W
T
PROPOSED DRIVEWAYS AND PATHS BASEMENT
DRAINAGE SUMP
-0.30
DESIGN MAJOR CONTOUR
E OVER
DESIGN MINOR CONTOUR
WT
BUILDING LIN
-0.30
1.4
+ 4.200 DESIGN SPOT LEVEL
0
-0.40
E EXISTING ELECTRICAL
BUILDING LIN
SW EXISTING STORM WATER
T
W
T EXISTING TELSTRA
OVER E
1.
WATER RETICULATION
4
W
0
-0.30
-0.30
EXISTING SEWER
T
S
W
1.8
LOT BOUNDARIES 0
17.00 EXISTING CONTOURS
-0.29
-0.30 -0.30
T
-0.17
W
-0.18
SERVICES NOTE: -0.01
1.80
1. EXISTING SEWER CONNECTION TO BE USED FOR NEW DEVELOPMENT -0.01
1.2 -0.32
2. EXISTING WATER METER TO BE REMOVED AND METERS INSTALLED 0
IN NEW LOCATION CLEAR OF DRIVEWAYS. NEW METERS INSTALLED
T
SW
1.20
W
IN ACCORDANCE WITH UNITYWATER PRIVATE WORKS APPLICATION 0.69
3. ELECTRICAL AND TELECOMMUNICATIONS CONNECTIONS TO CORE FILLED 0.69
AUTHORITIES STANDARDS BLOCK WALLS
TOP OF WALL
MIN. RL = 2.700
SW T
DRAINAGE NOTE:
1. ENGINEERING ASSESSMENT HAS IDENTIFIED THAT THERE ARE NO RAMP DRIVEWAY 1.80
W
MATCH NEW DRIVEWAY TO RL = 2.400 AT
SIGNIFICANT EXTERNAL CATCHMENTS OR OVERLAND FLOW PATHS SURFACE NEATLY TO BOUNDARY TO
THAT CONSTRAIN THIS DEVELOPMENT. ACHIEVE FLOOD 1.80
EXISTING PEDESTRIAN
2. ALL INTERNAL SURFACES AND ROOFWATER TO DRAIN TO STREET VIA IMMUNITY
BLOCK WAL
ACCESS PATH
REQUIREMENTS
T
2.05 MIN. RL = 2.700
APPROVED KERB ADAPTORS 2.05
3. 300sq DOMESTIC INLET PITS MAY BE INSTALLED IF SURFACE FLOWS
W
2.22 1.61
2.22 2.40
L
TO STREET ARE NOT POSSIBLE DUE TO FINAL LEVELS. ENSURE THAT 2.70
PITS ARE CONNECTED TO INTERNAL DRAINAGE SYSTEM AND
2.40
DISCHARGE TO KERB ACCORDINGLY. 0 2.40 1.60
T
2.4 2.40 1.6
0
DRIVEWAY NOTE: 2.25
2.25
L
DRIVEWAY GEOMETRY AND GRADES AS PER AS2890.1 AND
BLOCK WAL
2.20
2.05
STD DWG RS-050 WHERE APPLICABLE. ACCESS VIA EXISTING
EASEMENT DRIVEWAY. 2.20
CORE FILLED
2.00
T
1.80
BLOCK WALLS
FINISHED FLOOR LEVEL AND FLOOD IMMUNITY NOTE: 2.12 TOP OF WALL
2.25 2.35 MIN. RL = 2.700
FINISHED FLOOR LEVELS AS NOTED ARE AS PER CURRENT 2.00 2.25 2.35
2.40 2.35
NOOSA COUNCIL FLOOD INFORMATION SEARCH. BASEMENT
1.80
FLOOD IMMUNITY PROVIDED BY DRIVEWAY BUND AT RL =
BLOCK WAL
2.400m AHD AS SHOWN. 1.60 2.23
T L
BLOCK WAL
T
0
0
1.2
1.4
L
L
BLOCK WAL W
W
CONTRACTOR TO DETERMINE THE EXACT T
LOCATION OF ALL EXISTING SERVICES IN T 2.13 W
T W T
THE VICINITY OF THE PROPOSED WORKS W T W T
W T W T
PRIOR TO THE START OF ANY T W T
CONSTRUCTION - CONTRACTOR IS W W T T
W
W
RESPONSIBLE FOR ANY DAMAGE TO Meters
EXISTING SERVICES
PP 5 0 5 10
NOT FOR CONSTRUCTION PROPOSED LAYOUT - DRIVEWAY AND BASEMENT
SCALE 1:200 @ A3 1:200
SCALE DRAWING STATUS
DME
APPROVED PROJECT DRAWING TITLE
DESIGN - DM AS SHOWN
Dale Martin - RPEQ 16845
FOR APPROVAL
C MAR 23 FURTHER ADVICE DM
HORIZONTAL DATUM PROPOSED DUAL OCCUPANCY PROPOSED LAYOUT DRAWING NUMBER
DRAWN - DM B JAN 23 INFORMATION REQUEST DM
PROJECTS P.O. BOX 7481
DRIVEWAY AND 03
A SEP 22 FOR APPROVAL DM MGA 56 SIPPY DOWNS, QLD, 4556
Phone: 0438 157 612
128 GYMPIE TERRACE JOB NUMBER
APPROVED 06/03/2023 ISSUE DATE DESCRIPTION BY
VERTICAL DATUM
Engineering - Design - Civil Project Services Email: [email protected] NOOSAVILLE, QLD, 4566 BASEMENT 220508
AHD ©DME Projects Pty. Ltd.
Page 36
N
TW
1.40
1.40
1.2
PEDESTRIAN
W E
0
ACCESS PATH
MIN. RL = 2.700
TW
S 1.20
1.60
CONTINUOUS CORE FILLED
LEGEND
W
BLOCK WALLS ON BOUNDARY
T
TOP OF WALL MIN. RL = 2.700 1.80
1.20 2.00 1.60
PROPOSED BUILDING
WT
PROPOSED DRIVEWAYS AND PATHS
DESIGN MAJOR CONTOUR
DESIGN MINOR CONTOUR CORE FILLED
WT
BLOCK RETAINING
+ 4.200 DESIGN SPOT LEVEL
1.4
WALL
0
E EXISTING ELECTRICAL GROUND FLOOR
FFL = MIN. RL 2.700
SW EXISTING STORM WATER
T
W
T EXISTING TELSTRA
1.
WATER RETICULATION
40
W
S EXISTING SEWER
1.8
LOT BOUNDARIES 0
SERVICES NOTE:
1.80
1. EXISTING SEWER CONNECTION TO BE USED FOR NEW DEVELOPMENT
2. EXISTING WATER METER TO BE REMOVED AND METERS INSTALLED 1.2
0
IN NEW LOCATION CLEAR OF DRIVEWAYS. NEW METERS INSTALLED
IN ACCORDANCE WITH UNITYWATER PRIVATE WORKS APPLICATION
1.20
3. ELECTRICAL AND TELECOMMUNICATIONS CONNECTIONS TO
AUTHORITIES STANDARDS
DRAINAGE NOTE:
1. ENGINEERING ASSESSMENT HAS IDENTIFIED THAT THERE ARE NO 1.80
SIGNIFICANT EXTERNAL CATCHMENTS OR OVERLAND FLOW PATHS
THAT CONSTRAIN THIS DEVELOPMENT. 1.80
2. ALL INTERNAL SURFACES AND ROOFWATER TO DRAIN TO STREET VIA PEDESTRIAN
APPROVED KERB ADAPTORS ACCESS PATH
3. 300sq DOMESTIC INLET PITS MAY BE INSTALLED IF SURFACE FLOWS MIN. RL = 2.700
TO STREET ARE NOT POSSIBLE DUE TO FINAL LEVELS. ENSURE THAT
PITS ARE CONNECTED TO INTERNAL DRAINAGE SYSTEM AND
DISCHARGE TO KERB ACCORDINGLY.
0 1.60
DRIVEWAY NOTE: 2.4 1.6
0
DRIVEWAY GEOMETRY AND GRADES AS PER AS2890.1 AND
STD DWG RS-050 WHERE APPLICABLE. ACCESS VIA EXISTING
2.20
EASEMENT DRIVEWAY. 2.20
2.00
CORE FILLED
1.80
FINISHED FLOOR LEVEL AND FLOOD IMMUNITY NOTE: BLOCK WALLS
FINISHED FLOOR LEVELS AS NOTED ARE AS PER CURRENT TOP OF WALL
NOOSA COUNCIL FLOOD INFORMATION SEARCH. BASEMENT 2.00 MIN. RL = 2.700
FLOOD IMMUNITY PROVIDED BY "FLOW DEFENCE" FLOOD 1.80
BARRIER OR SIMILAR. 1.60
0
0
CONTRACTOR TO DETERMINE THE EXACT
1.2
1.4
LOCATION OF ALL EXISTING SERVICES IN T W
T W
THE VICINITY OF THE PROPOSED WORKS T W T
W T W T
PRIOR TO THE START OF ANY T W T
W T W T
CONSTRUCTION - CONTRACTOR IS
W W T T
RESPONSIBLE FOR ANY DAMAGE TO W
EXISTING SERVICES
PROPOSED LAYOUT - GROUND FLOOR
PP
NOT FOR CONSTRUCTION
SCALE 1:200 @ A3
SCALE DRAWING STATUS
DME
APPROVED PROJECT DRAWING TITLE
DESIGN - DM AS SHOWN
Dale Martin - RPEQ 16845
FOR APPROVAL
C MAR 23 FURTHER ADVICE DM
HORIZONTAL DATUM PROPOSED DUAL OCCUPANCY PROPOSED LAYOUT DRAWING NUMBER
DRAWN - DM B JAN 23 INFORMATION REQUEST DM
PROJECTS P.O. BOX 7481
GROUND FLOOR 04
A SEP 22 FOR APPROVAL DM MGA 56 SIPPY DOWNS, QLD, 4556
Phone: 0438 157 612
128 GYMPIE TERRACE JOB NUMBER
APPROVED 06/03/2023 ISSUE DATE DESCRIPTION BY
VERTICAL DATUM
Engineering - Design - Civil Project Services Email: [email protected] NOOSAVILLE, QLD, 4566 220508
AHD ©DME Projects Pty. Ltd.
Page 37
SUMP PUMP
DISCHARGE PIPE
POLY AS PER PUMP 1.80
MIN. 600SQ BASEMENT SUMP
MANUF. SPECS FITTED WITH AUTOMATIC PUMP
-0.30
OUT SYSTEM. DISCHARGE TO
STREET VIA PIT
2.05
2.05
150mm STRIP DRAIN 1.61
2.22
ACROSS DRIVEWAY
SL = RL 1.75m 2.22 2.40
IL = RL 1.5m 2.70 -0.30
FREE DRAINING TO
PIT. OUTLET TO HAVE
BACKFLOW 2.40
PREVENTION FLAP -0.40
2.40
0
2.40 1.6
2.25 SUMP PUMP
DISCHARGE PIPE
POLY AS PER PUMP
MANUF. SPECS
STRIP DRAIN 2.05
2.20
OUTLET PIPE
PIT
100Ø
TO
E
AD
1%
2.00
GR
GR
1%
1.80
AD
-0.30
ET
-0.30 200 STRIP DRAIN AT BOTTOM
O
PI
OF RAMP. CONNECT TO
T
2.35 BASEMENT SUMP
2.25 2.35
2.40
2.35
RAINWATER
TANK O/FLOW
600SQ INLET PIT TO PIT
SUITABLE BACKFLOW
DEVICE FITTED TO 2.23
OUTLET PIPE TO -0.29
PREVENT -0.30 -0.30
0
FLOODWATER
1.4
ENTERING LOT VIA
-0.17
SYSTEM
SL = RL 2.01m 2.13 -0.18
W
IL = RL 1.35m W
W -0.01
W
1.80
W T -0.01
W T
W T
T W T
W T T T
T -0.32
T T
PP DRAINAGE OUTLET TO STREET
AT APPROX RL = 1.25. LEVELS
TO BE CHECKED AND ADJUSTED
0.69
0.69
TO ENSURE STRIP DRAINS ARE
FREE DRAINING
SURFACE DRAINAGE - GROUND LEVEL SURFACE DRAINAGE - BASEMENT
SCALE 1:200 @ A3 SCALE 1:200 @ A3
DRAINAGE NOTE:
1. ALL PIPES MIN 100Ø UPVC U.N.O. MIN. 0.5% GRADE AND FREE
CONTRACTOR TO DETERMINE THE EXACT
LOCATION OF ALL EXISTING SERVICES IN
DRAINING AT ALL TIMES.
THE VICINITY OF THE PROPOSED WORKS 2. ALL INTERNAL SURFACES AND ROOFWATER TO DRAIN TO STREET VIA
PRIOR TO THE START OF ANY APPROVED KERB ADAPTORS
CONSTRUCTION - CONTRACTOR IS 3. 300sq DOMESTIC INLET PITS MAY BE INSTALLED IF SURFACE FLOWS
RESPONSIBLE FOR ANY DAMAGE TO TO STREET ARE NOT POSSIBLE DUE TO FINAL LEVELS. ENSURE THAT
EXISTING SERVICES PITS ARE CONNECTED TO INTERNAL DRAINAGE SYSTEM AND
DISCHARGE TO KERB ACCORDINGLY.
NOT FOR CONSTRUCTION
SCALE DRAWING STATUS
DME
APPROVED PROJECT DRAWING TITLE
DESIGN - DM AS SHOWN
Dale Martin - RPEQ 16845
FOR APPROVAL
C MAR 23 FURTHER ADVICE DM
HORIZONTAL DATUM PROPOSED DUAL OCCUPANCY STORMWATER DETAILS DRAWING NUMBER
DRAWN - DM B JAN 23 INFORMATION REQUEST DM
PROJECTS P.O. BOX 7481 05
A SEP 22 FOR APPROVAL DM MGA 56 SIPPY DOWNS, QLD, 4556
Phone: 0438 157 612
128 GYMPIE TERRACE JOB NUMBER
APPROVED 06/03/2023 ISSUE DATE DESCRIPTION BY
VERTICAL DATUM
Engineering - Design - Civil Project Services Email: [email protected] NOOSAVILLE, QLD, 4566 220508
AHD ©DME Projects Pty. Ltd.
Page 38
0
0.05m
B B 0
B85 (LOW CLEARANCE) ENTRY AND EXIT
5
A
GROUND CONFLICT MODEL
50mm CLEARANCE BOTTOM RAMP
110mm CLEARANCE TOP RAMP
A 5
0.07m 10
0
NORTHERN PARK - ENTER SOUTHERN PARK - ENTER
SCALE 1:200 @ A3 SCALE 1:200 @ A3
A 15
B 0
B
20
35
0.11m
30
5
A
25
T
0.11m
T W
T W
T
W T W T 0
T W T
W
W
W T T 10
PP NORTHERN PARK - EXIT SOUTHERN PARK - EXIT 5.2
DRIVEWAY ACCESS SCALE 1:200 @ A3 SCALE 1:200 @ A3
SCALE 1:200 @ A3
0.95 3.05
12% 0% 8% 0% B99 Vehicle (Realistic min radius) (2004)
17% Overall Length 5.200m
Overall Width 1.940m
Overall Body Height 1.878m
25% Min Body Ground Clearance 0.272m
Track Width 1.840m
% Lock-to-lock time 4.00s
12.5% 15 Curb to Curb Turning Radius 6.250m
4.91
Datum -3.000
-0.311
-0.287
-0.157
-0.300
-0.300
-0.300
0.019
0.269
0.518
0.768
2.018
2.196
2.297
2.385
2.393
2.385
2.392
2.400
2.334
2.256
2.250
2.250
2.239
2.197
1.018
1.268
1.518
1.768
CONTROL LINE LEVELS
0.92 2.8
CHAINAGE
21
22
23
25
29
31
32
33
35
37
39
40
41
42
43
44
45
46
46
10
11
12
13
14
15
16
17
18
19
20
24
26
27
28
30
34
36
38
0
0
2
3
4
5
6
7
8
9
1
B85 Vehicle (Realistic min radius) (2004)
Overall Length 4.910m
Overall Width 1.870m
Overall Body Height 1.421m
DRIVEWAY LONG SECTION Min Body Ground Clearance
Track Width
Lock-to-lock time
0.159m
1.770m
4.00s
SCALE 1:200 @ A3 Curb to Curb Turning Radius 5.750m
SCALE DRAWING STATUS
DME
APPROVED PROJECT DRAWING TITLE
DESIGN - DM AS SHOWN
Dale Martin - RPEQ 16845
FOR APPROVAL
C MAR 23 FURTHER ADVICE DM
HORIZONTAL DATUM PROPOSED DUAL OCCUPANCY DRIVEWAY & ACCESS DRAWING NUMBER
DRAWN - DM B JAN 23 INFORMATION REQUEST DM
PROJECTS P.O. BOX 7481
DETAILS 06
A SEP 22 FOR APPROVAL DM MGA 56 SIPPY DOWNS, QLD, 4556
Phone: 0438 157 612
128 GYMPIE TERRACE JOB NUMBER
APPROVED 06/03/2023 ISSUE DATE DESCRIPTION BY
VERTICAL DATUM
Engineering - Design - Civil Project Services Email: [email protected] NOOSAVILLE, QLD, 4566 220508
AHD ©DME Projects Pty. Ltd.
Page 39
DEPTH CUT/FILL (m) EARTHWORKS REFER TO ARCHITECTURAL PLANS
FOR FENCING EXTENTS AND TYPE
QUANTITIES - SITE
RP BOUNDARY
RP BOUNDARY
0.0 TO 1.0
RESIDENCE
CUT 659 m3
-0.5 TO 0.0 FILL 58 m3 CORE FILLED BLOCK
RETAINING WALL CORE FILLED BLOCK
3
NETT (EXPORT) 601 m FFL = 2.700 RETAINING WALL
-1.0 TO -0.5
-1.5 TO -1.0 FILL QTY IS MEASURED FROM
EXISTING SURFACE TO DESIGN EXISTING SURFACE
FINISHED SURFACE AND INCLUDES
-2.0 TO -1.5 GROUND SLABS
RAMP
-2.5 TO -2.0 BASEMENT FFL = -0.3
SECTION C
Datum -3.000
2.20
2.21
2.21
2.21
2.23
2.25
2.23
1.19
1.22
1.24
1.25
0 DEPTH CUT
0.92
0.77
0.74
0.82
0.81
0.80
0.79
0.79
0.79
0.79
0.68
0.68
0.70
0.64
DEPTH FILL
2.677
2.689
2.592
2.664
2.700
2.600
2.600
2.700
2.700
2.700
2.700
2.700
2.700
2.700
2.600
2.600
2.600
CONTROL LINE LEVELS
5
1.777
1.827
1.859
1.879
1.891
1.913
1.917
1.915
1.901
1.949
1.900
1.906
1.908
1.910
EXISTING SURFACE
CHAINAGE
13
15
10
11
12
14
16
17
17
3
4
5
9
0
0
1
2
6
7
8
SECTION B
SECTION B
10 SCALE 1:100 @ A3
RP BOUNDARY
RP BOUNDARY
CORE FILLED
BLOCK WALL
15
DFE = RL2.4m
DRIVEWAY
SECTION A
20
25
Datum -1.000
2.250
2.250
2.341
2.400
2.387
2.387
2.387
2.387
2.387
2.387
2.387
2.387
2.386
2.050
2.050
1.548
CONTROL LINE LEVELS
W
CHAINAGE
10
11
12
13
14
15
16
17
17
W
3
5
9
0
0
1
2
4
6
7
8
W T
SECTION D
W
SECTION A
SECTION LAYOUT SCALE 1:100 @ A3
SCALE 1:200 @ A3
SCALE DRAWING STATUS
DME
APPROVED PROJECT DRAWING TITLE
DESIGN - DM AS SHOWN
Dale Martin - RPEQ 16845
FOR APPROVAL
C MAR 23 FURTHER ADVICE DM
HORIZONTAL DATUM PROPOSED DUAL OCCUPANCY EARTHWORKS DRAWING NUMBER
DRAWN - DM B JAN 23 INFORMATION REQUEST DM
PROJECTS P.O. BOX 7481
SECTIONS 07
A SEP 22 FOR APPROVAL DM MGA 56 SIPPY DOWNS, QLD, 4556
Phone: 0438 157 612
128 GYMPIE TERRACE JOB NUMBER
APPROVED 06/03/2023 ISSUE DATE DESCRIPTION BY
VERTICAL DATUM
Engineering - Design - Civil Project Services Email: [email protected] NOOSAVILLE, QLD, 4566 220508
AHD ©DME Projects Pty. Ltd.
Page 40
TW
B
W
T
0.26m
W
T
A
T
B 0 0
A
0.27m
5 5
10 10
SUFFICIENT SPACE
WITHIN EXISTING
DRIVEWAY FOR
PASSING VEHICLES
A
15 15 B
B 5.2
0.19m B99 STREET
LEVEL PARKING
0.95 3.05
40
20
20
35
35
B99 Vehicle (Realistic min radius) (2004)
Overall Length 5.200m
30
30
Overall Width 1.940m
Overall Body Height 1.878m
25
A 25
Min Body Ground Clearance 0.272m
Track Width 1.840m
Lock-to-lock time 4.00s
Curb to Curb Turning Radius 6.250m
B99 BASEMENT ACCESS B99 BASEMENT EXIT
SCALE 1:200 @ A3 SCALE 1:200 @ A3
SCALE DRAWING STATUS
DME
APPROVED PROJECT DRAWING TITLE
DESIGN - DM AS SHOWN
Dale Martin - RPEQ 16845
FOR APPROVAL
HORIZONTAL DATUM PROPOSED DUAL OCCUPANCY B99 TURN PATHS DRAWING NUMBER
DRAWN - DM B MAR 23 FURTHER ADVICE DM
PROJECTS P.O. BOX 7481 08
A JAN 23 INFORMATION REQUEST DM MGA 56 SIPPY DOWNS, QLD, 4556
Phone: 0438 157 612
128 GYMPIE TERRACE JOB NUMBER
APPROVED 06/03/2023 ISSUE DATE DESCRIPTION BY
VERTICAL DATUM
Engineering - Design - Civil Project Services Email: [email protected] NOOSAVILLE, QLD, 4566 220508
AHD ©DME Projects Pty. Ltd.
Page 41
RP BOUNDARY CORE FILLED BLOCK RETAINING WALL CORE FILLED BLOCK RETAINING WALL RP BOUNDARY RESIDENCE FFL = 2.700 EXISTING SURFACE BASEMENT FFL = -0.3 ~ S ~ D D > S wm > Datum -3.000 DEPTH CUT 7, 7 F YF YF 8 FF BF BF BF 8 DEPTH FILL | os ot Sf OS ORO CONTROL LINE LEVELS | } gf 8 8 OS oR UR OR OR OR EXISTING SURFACE x, Rf} S]GTP) Bk) CHAINAGE clo “4 n o + ra © N ° a g a s a = a 4 a5 SECTION C SCALE 1:100 @ A3 z FLOOD BUND WITHIN DRIVEWAY AT s RL=2.4mAHD Zz > 5 z 2 a a 2 co RESIDENCE FFL = 2.700 F U POOL nN 2 DRIVEWAY SS = ee RAMP BASEMENT FFL = -0.3 DEPTH CUT gz aoa ad a a ay a el yd a ad ad a ce es ae ed a eo el yo s) al al sl ee Datum -3.000 ° o o a a a a a AN a AN a N a N AN N AN N AN Nn Nn Nn A a a a a al of al of of of uf of of ol af of af ef of of of sf uo 6st lef of Sf oo] of om cSt lof of ef hoe vot hoe hoof ost Us US! hued us] hue how DEPTH FILL s} s| 3} 3} 3} 3} 3} 3} gs} os} 6S} oS} gs} os} Sf oS} a} oS) oS} oS) Sp Ss} st Ss} Ss} Ss} Ss} Ss} Ss} os} sf Sos} SS} 8) Ss} a) a) a) os eof al of af af of of af of wf of vf of vf of of of vf sf af vf el ef ef ef af vt af af af ef ef ef ef ef sl ef sl st vl 2 2} | a] sl 8] gs} af al sf} al a] gl al ef} sf} a} a} al sl sf af gs) a} sl os} a} al a} gf el al gt sf a} a} a} a) af al af gf gs} oo} sl eg EXISTING SURFACE fH 6S) SPS] OS] ST OS] OO) OG] OS} OS} OR ORY CO} og] 8) } Sh} 8] ] so ]] } CO} Cy] SO] OS} ot] OR} Oy CS} OST OS} OS} SO] OS} OS} OS] OS} ST OA 8 FY oS} OS] OS] OS OS] OS} OS OS) OS) OS) Sp} OS] OS] OS} OS] OS) OS} OS) OS) OS} OS} OS] OS) OS} OS} OS) OS} OS) OPO) yo} os] OS a} of Sf SPAY oS CHAINAGE o afoot mf st wt we we PSPSPS RORY OOo) OPPS] OST OS] OST SCALE 1:150 @ A3 DESIGN - DM ms SHOWN APPROVED PROJECT DRAWING TITLE “FOR APPROVAL DM E Dale Martin - RPEQ 16845 EARTHWORKS | HORIZONTAL DATUM ____ PROPOSED DUAL OCCUPANCY ar) DRAWN -DM B_ | MAR23| FURTHER ADVICE P.O. BOX 7481 A | JAN 23 INFORMATION REQUEST [DM MGA 56 PROJECTS SIPPY DOWNS, QLD, 4556 128 GYMPIE TERRACE SECTIONS 2 a Phone: 0438 157 612 MBE VERTICAL DATUM APPROVED 06/03/2023 ISSUE DATE DESCRIPTION BY AHD Engineering - Design - Civil Project Services Email: [email protected] NOOSAVILLE, QLD, 4566 220508 ©DME Projects Pty. Ltd.
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ADG Consulting Pty Ltd Appendix D: Dewatering calculation output ADG1535.22 Dewatering Management Plan_Rev0_31.05.23
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Cone of Depression calculator This tool can be used to calculate the groundwater cone of depression in potential acid sulfate soil areas. Last updated: 2 May 2023 Related page Preliminary assessment of the radial extent of the cone of depression and pumping rates and times for all Acid sulfate soils dewatering operations is critical for assessing the risk of disturbing acid sulfate soils in potential acid sulfate soil areas Provided by Broad-scale acid sulfate soil risk maps for several coastal regions of WA are accessible via Data WA Department of Water and Environmental Regulation Empirical methods to calculate the radial extent of the groundwater cone of depression and pumping rates and times for dewatering operations are outlined in National Acid Sulfate Soils Guidance: Guidance for the dewatering of acid sulfate soils in shallow groundwater environments (3 oe ino in Calculator Input Length of excavation 20 metres Width of excavation metres Drawdown required: 2.1 metres Aquifer thickness'") metres Hydraulic conductivity: 0.0000949 metres/second Results Effective pumping radius, R. 8 metres Cone of depression radius, R, 61 metres Total pumping rate 6 |litres/second Pumping time required 62 hours
Used in these records
Appendix D - Acid Sulphate and Dewatering Managment Plan.pdfRelated documentApplication case desk ↗
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