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2 David Low Way - Attachment 4 - Specific Engineering Assessments - Cardno 10-8-17
Attached to the e-mail Reconfiguration of a Lot (1 lot into 6) - RAL17/0501.
9 August 2017 Trevor Johnson Engineering Consultant 252 Pacific Parade BILINGA QLD 4225 Urban Systems By Email 20 Patterson Street AUCHENFLOWER QLD 4066 Attention: Mr Peter Cumming Dear Peter KENLYNN PTY LTD — PROPERTY 2, DAVID LOW WAY, CASTAWAYS BEACH SPECIALIST ENGINEERING ADVICE TO SUPPORT DEVELOPMENT APPLICATION Introduction In accordance with your instructions, please find below full details of the engineering investigations which have been undertaken for this project. The project involves the proposed subdivision of the subject property into 6 lots, as per the attached Subdivision Proposal Plan. | have been responsible for five elements of specialist engineering design for this project: Coastal Hazard and Erosion Flooding Acid Sulfate Soils Geotechnical Assessment for Land Instability Stormwater Management The site is located in the Eastern Beaches area. Based on current Noosa Shire Council planning scheme mapping, the site is affected by the following overlays: e Natural Resources: Coastal Protection Area e Natural Hazard: Landslide & Flooding e Natural Hazard: Bushfire & Acid Sulfate Soils Relevant plans are attached. The site is also determined as being subject to Coastal Hazard (Erosion Prone), according to mapping available from the website of the Department of Environment and Heritage Protection (DEHP). The site is not designated as being subject to Coastal Hazard (Storm Tide Inundation). The site lies within the Catchment Management District designated by the Department. | will deal with each constraint in turn as follows.
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763345 2 9 August 2017 Coastal Hazard (Erosion Prone) Dealing with the State issue first, the site is designated as being subject to Coastal Erosion by DEHP. According to the Erosion Prone Area map for Noosa Shire Local Government Area, the width of the erosion zone is specified to be 175 m from the seaward toe of the frontal dune. This would encompass the entire site. Since the site also lies within the Coastal Management District, the State has a jurisdiction over the development application under the Planning Regulation 2017, and the application needs to be assessed under the State Development Assessment Provisions (SDAP). Under State code 8 of the SDAP, there are a number of performance outcomes which potentially affect the proposal, and these are discussed below. However, prior to that assessment, it is necessary to consider the Purpose of State code 8, as follows: The purpose of this code is to ensure that development is designed and located to: protect life, buildings and infrastructure from the impacts of coastal erosion maintain coastal processes conserve coastal processes maintain appropriate public use of, and access to and along, state coastal land account for the projected impacts of climate change and avoid impacts on matters of state significant significance and, where avoidance is not reasonably possible, minimise and mitigate impacts, and provide an offset for significant residual impacts where appropriate. PARONsA In this specific situation, | believe that the project complies precisely with the above Purpose, as | will demonstrate shortly. In the Performance Outcomes, particularly PO1, there is an implicit assumption that the erosion prone areas designated in the State mapping are accurate and inviolate. In fact, detailed analysis (see Appendix A) has determined that there is sufficient evident to conclude that the erosion prone width at this location is less than shown on the State mapping. This issue has been discussed with DEHP officers, and it has been agreed that DEHP will review the detailed erosion assessment for adequacy. DEHP has also advised, on the basis on information provided to date, that it considers that the proposed development does not represent a significant erosion risk. Consequently, it has been determined that the development does not lie within the coastal erosion risk area. In that context, the development will: e protect life, buildings and infrastructure from the impacts of coastal erosion, since it will lie outside if the erosion zone maintain coastal processes since these will be unaffected by the proposed works conserve coastal processes since the works are outside of the erosion zone have no impact on appropriate public use of, and access to and along, state coastal land account for the projected impacts of climate change and has no impacts on matters of state significance. | have also attached the current SARA mapping for this matter. The potential erosion prone area, based on current State mapping, encompasses many existing residential areas on the Sunshine Coast including substantial medium density development at Coolum. C\Users\trevor johnson\Documents\castaways.docx
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753345 3 9 August 2017 | will now consider the Performance Outcomes in Module 8 in detail. Performance outcome PO1 states: PO1 Development does not occur in the erosion prone area unless the development: 1. is one of the following types of development: a. coastal-dependent development; or b. temporary, readily relocatable or able to be abandoned; or c. essential community infrastructure; or d. redevelopment of an existing permanent building or structure that cannot be relocated or abandoned; and 2. cannot feasibly be located elsewhere. The proposed development is not one of the forms of development specified in PO1, and the application would therefore fail if assessed under the current erosion designation attached to the local area. However, for the reasons outlined immediately above, it is apparent that the development will not occur within an erosion prone area, and the requirements for PO1 will be satisfied. The development is considered to be entirely compliant with the remaining performance outcomes, as noted following: PO2 Development other than coastal protection work: 1. avoids impacting on coastal processes; and 2. ensures that the protective function of landforms and vegetation is maintained. Note: In considering reconfiguring a lot applications, the state may require land in the erosion prone area to be surrendered to the State for coastal management purposes under the Coastal Protection and Management Act 1995. Where the pianning chief executive receives a copy of a land surrender requirement under the Coastal Protection and Management Act 1995, this must be considered in assessing the application. PO3 Development is located, designed and constructed to minimise the impacts from coastal erosion by: 1. locating the development as far landward as practicable; or 2. where it is demonstrated that 1 is not feasible, mitigate or otherwise accommodate the risks posed by coastal PO4 Development does not significantly increase the risk or impacts to people and property from coastal erosion. PO5 Development other than coastal protection work avoids directly or indirectly increasing the severity of coastal erosion either on or off the site. A detailed review of coastal management issues for this site has been undertaken by review of historical aerial photography, as well as a first principles numerical assessment in accordance with the Coastal Hazards Technical Guide produced by the Department. A copy of this report is attached. In respect of available aerial photography, the analysis indicates that this site has suffered no consistent erosion since at least 1958. The erosion line for each set of aerial photographs lies well to the east of the property boundary, with the maximum extent of erosion coming no closer than 70 m to the existing seaward house on the property. The erosion is consistent with a maximum storm bite of 30 to 40 m, with there being no evidence of long term erosion caused by littoral drift. CA\Users\trevor.johnson\Documents\castaways.docx
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753345 4 9 August 2017 The detailed numerical assessment is presented in Appendix A. The conclusion of that assessment is that the erosion prone area width (EPAW) should be reduced to 77 m, rather than the 175 m contained in the current State mapping. On this basis, the erosion prone area lies outside the property boundary, and has no effect on the site. It is also noted that the development proponent will retain the vegetation on the site outside of the proposal building envelopes. In particular, the vegetation on the downslope and dunes eastward of the building line will be completely retained. This will provide an additional factor of safety against future erosion which may affect the beach in this location. State Assessment Development Provisions — State Code 8 Assessment against SDAP State Code 8: Coastal development and tidal works is triggered by the application because the site is designated as erosion prone by DEHP. A completed template for State Code 8 is attached. The project complies with all relevant Performance Outcomes with the notional exception of PO1 (on the basis of the current State coastal hazard mapping). In that respect, the site is currently included in the Erosion Prone area mapping for the local authority. However, a detailed coastal assessment (see attached and above) has determined that the site is not erosion prone. A detailed assessment against the State Code 8 provisions is included in Appendix B. Coastal Protection Area (Noosa Shire Council Planning Scheme) The site and the coastal areas seaward of it are classed as being in the Coastal Protection Area by Council. Proposed development in these areas is therefore required to be assessed under Part 13 Overlays of the Planning Scheme, and in particular Division 10 - Natural Resources Overlay Code. From an engineering point of view, the relevant specific outcome listed in that Code for coastal protection areas is as follows: 018 The siting and design of development and materials used within the Coastal Protection Area, as identified on the Natural Resources Overlay Maps, do not cause any significant adverse impacts on the coastal resources of the location nor interrupt the natural cycles of erosion and accretion of foreshore areas and beaches. Given that the site-based coastal processes study carried out for this proposal has determined that the site lies completely outside of the erosion prone area, O18 is obviously complied with. A detailed assessment against the provisions of Noosa Shire’s Natural Resources Overlay Code is included in Appendix C. Flooding Burgess Creek adjoins the site to the north. It has been determined that the peak water level in this creek will be governed by storm tide conditions in the coastal zone. The peak water level for the 1% Average Exceedance Probability (AEP) flood event is therefore expected to not exceed 3.2 m AHD, taking into account an expected 0.8 m sea levei rise by 2100 as a result of climate change. All proposed development on this site will be located above 14 m AHD, and the only part of the site which is subject to flooding is the steep area adjoining Burgess Creek. No works will take place on this slope below 14 m AHD. There are no flood impacts on the development proposal. C:\Users\trevor. johnson\Documents\castaways.docx
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753345 5 9 August 2017 Acid Sulfate Soils The northern part of the site is shown as being in the low potential acid sulfate area (5-20 m AHD). There is no reason for this designation other than the existing level of the land. As far as | am aware, no acid sulfate soil investigations have been carried out on the site. It is my opinion based on site inspection and review of available data that the site basically consists of a prehistoric sand dune which was formed when the ocean water level was significantly higher than moder times. A further two dune systems are evident in the area between the site and the current beach location, indicating additional dune areas which have been abandoned as water levels fell over the past 10,000 years. It is most likely that the sub-surface stratigraphy consists of clean beach sand formed under aeolian processes, similar to that which is evident at the surface and in the dune profiles. On that basis, it is most unlikely that acid sulfate soils are likely to be present on this site. Further, it is not proposed to carry out any subsurface excavation other than to potentially level the top of the site to create building platforms. It is possible that the dwelling houses to be constructed on site will be piled for structural purposes. Any material below 10 m AHD which is disturbed during the construction process will be tested for acid sulfate potential and treated accordingly. Geotechnical Assessment The site is shown as being land-slide prone under the Natural Hazards Overlay in the Planning Scheme. In that context, there is a requirement to assess the application under the relevant Natural Hazards Code in Part 13 of the Scheme. The specific requirements of that Code are as follows: O7 Development is located to ensure it does not compromise the safety of people, property or hazardous materials manufactured or stored in bulk by increasing risk of landslide; AND O2 Development, including access ways is designed and constructed to— a) minimise impacts on the natural landform; b) minimise risk to people and property from landslide; c) avoid any potential instability and associated problems, including long term stability of the site and long term stability of the development. Planning Scheme Policy PSP1 sets out the information that Council may request in relation to a development application. For development in areas identified as having Landslide Hazard Potential on the Overlay Maps, PSP1 requires a site-specific geotechnical analysis to consider the long-term stability of the site, and the long-term stability of proposed development. The potential for geotechnical instability to be present on the site has therefore been assessed by site investigation by an experienced geotechnical engineer. The findings of this investigation are included herein as Appendix D. It was determined that the site is not subject to geotechnical instability in its current state, and the proposed development will not affect geotechnical stability. CAUsers\trevor johnson\Documents\castaways.docx
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753345 6 9 August 2017 Stormwater Management The site is effectively its own catchment, encompassing the plateau which sits above the most landward sand dune. The site has a total area of 9,677 m2. Under the worst possible development conditions for water quality purposes, it has been assumed that the site could consist of approximately 4,000 m? of roof and hardstand area. It has been recommended that each dwelling on the site be fitted with a water tank with a volume of 10,000 L. The potential for water quality impacts external to the site are considered minimal in the context that the site consists of clean beach sand with little potential for contamination. If water quality treatment is required, it is proposed that individual bio-retention filters be constructed on each proposed allotment. Each filter should have an area of approximately 30 m%, if Council determines that such treatment is required. Alternatively, and given the sandy nature of the site, it is proposed that all stormwater generated on the sire could be directed to small infiltration basins to be constructed for each dwelling. A basin with surface area of about 70 m? per residence, and a depth of about 300 mm, will be sufficient to manage all stormwater runoff from the site. Conclusions A number of specialist engineering investigations have been undertaken for the proposed project. It has been determined that there are no issues in the following study areas which would prevent the proposed 6 lot subdivision from proceeding as planned. Coastal Hazard and Erosion Flooding Acid Sulfate Soils Geotechnical Assessment for Land Instability Stormwater Management Yours sincerely Dr Trevor Johnson Engineering Consultant Enel: Subdivision Proposal Plan SARA Coastal Mapping Coastal engineering report State Code 8 compliance Natural hazards overlay code compliance Geotechnical report C.\Usersitrevor johnsox\Documents\castaways,doox
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This plan has been prepared as a proposed subdivision
and should not be used for any other purpose.
The dimensions, areas and total number of lots shown
hereon are subject to field survey and are also to the
requirements of council and any other authority which
may have requirements under any relevant legislation.
Certificate of Title for this site has not been obtained.
Therefore, no reliance should be placed on the
information on this plan for any financial dealings
involving the land.
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3
Easement Schedule %
Identifier Benefit Type \
712 Access/Services)
711,713 Access/Services
711,712,714 Access/Services
711-713,715 Access/Services
711-714,716 Access/Services
711-715 Access/Services
Statistics Table
6
946 m? - 3336 m*
1612 m?
Nil
Nil
AMOoOOWY
Lots
Area range
Area average
Road
Park
Covenant 3643 m?
Contour Interval - 1m, 5m major
REVISIONS
2iD7A7|__Amend Covenant P and Covenant areas
‘2oinaa7| Amend Big Env Lot 714-713 8 716, ealgn Eml AC with driveway, widen
Emt E & F as per usdated HRV tumaround
3/06/17) Widen access diveway to 8m.
i067 — Add 3.0m Sewer Easement
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Proposed Lots 711-716 & Emt's A-F & Cov P-V CLIENT:
Cancelling Lot 74 on MCH 2854
2 David Low Way, Castaways Beach Kenlynn Pty Ltd
SCALE —1:750(A3)
PLAN REF: S0054-P4(E)
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Page 10
753345 9 August 2017 APPENDIX A COASTAL ENGINEERING REPORT CCAUserstrevor johnson\Documents\castaways.docx
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1 Assessment of Erosion Prone Area Widths For the purposes of informing permissible development locations in the coastal zone of the Castaways Beach Development site, the Queensland Coastal Hazard Guidelines provided by the Department of Environment and Heritage Protection were used to determine the erosion prone areas widths (EPAW). Appendix A provides the relevant definitions for this coastal management region. 1.1 General Discussion and EPAW Overview The Queensland Coastal Hazard Guidelines (2015) outline a method for assessing erosion prone area widths (EPAWs). These widths are intended to accommodate both short-term and long-term erosion over specified planning periods. This erosion prone area width is a specified horizontal distance back from the HAT water line, and is calculated by the following equation provided in the guidelines. E =[(NxR)+C+S] x (14+F) + D Where:- E = erosion prone area width (metres). N = planning period (years). R = rate of long-term erosion (metres per year). C = short-term erosion from the design storm (metres). S = erosion due to sea level rise (metres). F = factor of safety. D = dune scarp component to allow for slumping of the erosion scarp (metres) The Department of Environment and Heritage Protection (DEHP) has developed default EPAW setback distances at many Queensland coastal sites. For planning purposes, these lines are established for projected sea level rise (SLR) of 0.8m to 2100. At Castaways Beach this default setback distance (from the 2100 HAT contour) is 175m. As part of development plan investigations, the owners at Castaways Beach have engaged Cardno to investigate whether or not a more realistic EPAW line could be developed. Discussions would then be held with DEHP to address such a requested change. 1.1.1 Planning Period (N) The planning period for this erosion prone area width assessment was to 2100. This planning period was deemed the most practical when taking into consideration the design life of the study site structures and appropriate level of risk. This affects the sea level rise applied to present-day highest astronomical tide (HAT).
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1.1.2 Rate of Long Term Erosion (R) Gradual and imperceptible long term shoreline erosion may occur as the result of an imbalance in the net sediment budget. This gradual net loss of sediments may occur as a result of the following processes: e Differential Longshore Sediment Flux: Whilst incident wave direction at the study site is likely to fluctuate naturally about the shore-normal direction due to incomplete wave refraction at times, if the mean wave direction differs slightly from shore-normal then the result will be a net longshore flux of sediments. Differential longshore flux across the shoreline may result in either a net supply or loss of sediment at any particular location. e = Artificial Sand Mining or Beach Nourishment: Anthropogenic gains and losses can constitute a significant component of the sediment budget when material is artificially added or removed from the coastal cell. e Sand Losses Due to Coastal Dunes: Another potentially significant process is that of aeolian transport. Onshore winds can blow sand inland off the beach so it cannot be reached by wave action. This results in dune growth and in some cases inland dune migration and a net loss of sand from the present beach system. If there is not a matching supply of sand from the surf zone or alongshore shoreline recession occurs. This process was quantified from aerial photograph analysis as described in Section 1.2.1. 1.1.3 Short Term Storm Erosion (C) In order to determine setback distances for planning as part of the coastal risk assessment framework, it is necessary to understand the magnitude and frequency of storm related erosion, and the resulting fluctuations of the beach face over time. The values for short-term erosion from design storms (C) on the resort beach are described by the outcomes of the SBEACH modelling described in Section 1.2.2. 1.1.4 Shoreline Recession Due to Sea Level Rise (S) There are several models available that relate shoreline retreat to an increase in local sea level. The best known of these is The Bruun Rule (Bruun, 1962), which is a popular approach based on the concept that an equilibrium beach profile is maintained during a sea level rise, but is translated up and landward. Sediment is removed from the upper beach and dune during shoreline retreat (erosion) and deposited onto the adjacent nearshore zone, thus maintaining both the original beach profile and nearshore shallow water conditions. The estimated sea level rise is based on the best information currently available, and the current value adopted for calculating the erosion prone area is 0.8m by 2100 (relative to 1990 MSL). The horizontal foreshore erosion due to sea level rise (S) was determined for the 83 years planning period (from present day to 2100). Based on data presented in State Development (2014) and the LIDAR based profiles, a nearshore seabed slope of 1:30 between the estimated top of wave run-up at the shoreline and closure depth (*10m), the shoreline recession arising from projected sea level rise has been estimated to be 30 x 0.8m = 23m. 1.1.5 Factor of Safety (F) The calculation procedures adopted for erosion prone area width determinations are consistent with current engineering practice in this field, but are subject to uncertainties and limitations. Therefore, the QLD Coastal Hazard Guidelines stipulates that a factor of safety should be applied to these calculations. For this purpose, the factor of safety (F) of 0.4 has been adopted by DEHP for use in this equation. This means that design long term, storm and sea level rise erosion distances would be scaled up by 40%.
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1.1.6 Dune Scarping Component (D) Dune slump (D) was accounted for in the SBEACH modelling, but there is no dune at the resort beach, which is not proposed as the main resort beach amenity, which will be an internal beach around the main pool. 1.2 Erosion Prone Area Width This analysis begins with analyses of two sets of data, namely historical aerial photographs and LIDAR. 1.2.1 Long Term Erosion The aerial photographs were examined and historical vegetation lines determined on each photograph. The vegetation line varies with storm events and changes in sea level, as well as losses in sand from potential offshore and alongshore sediment transport. They may also vary as a result of human and animal traffic, which lead to blow-outs, sand mining and stream flows. Figure 1.1 shows these vegetation lines relative to the Castaways Beach development site — in red. Aerial photographs for the following dates and were available and applied to these analyses:- 6 May 1958 25 September 1961 10 July 1973 July 1977 (no day specified) 20 April 1979 29 October 1982 5 September 1990 1 August 1996 25 July 2002 11 June 2004 21 July 2010 3 July 2012 25 May 2016 17 February 2017
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Figure 1-1 Historical Vegetation Lines Relative to the Castaways Beach Site Figure 1.2 describes seventeen cross-section location tines at 20m spacings applied to the analyses of long term vegetation line changes. SBeach profiles were prepared for the shoreline near Cross- section lines 6 and 14.
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Legend ——— Transects === Baseline Vegetation_Lines Date_ ————~ 02/17/2017 04/20/1979 —— 05/06/1958 05/25/2016 —— 06/11/2004 ———= 07/03/2012 ~~ 0701973 —— 07/15/1977 = 07/21/2010 > 07/25/2002 ——— 08/01/1996 09/05/1990 —— 09/25/1961 10/29/1982 (18\ |16) 15] | ee 14 [13] Figure 1-2 Cross-Sections Used in Analyses of Long Term Vegetation Line Changes
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Long term shoreline changes were determined from linear regression analyses of the available long
term vegetation line changes. These analyses were undertaken using the Digital Shoreline Analysis
System (DSAS) developed by the US Geological Survey (Himmelstoss, 2009). Figures 1.3 and 1.4
describe results for two of these cross-sections, 6 and 14. They show gradual shoreline progradation
rather than long term erosion (recession). Note the poor fit at Cross-section 14 caused by unknown
processes in the 1970-80s period — perhaps sand mining or a blow-out. Overall the analysis results, in
terms of the linear regression rate (LRR) of shoreline change, show shoreline progradation rates in the
order of 0.73m/year at the southern end, reducing to about 0.14m/year at the northern end — the latter
affected significantly by the unknown activity at the northern end — Figure 1.4. These results are
presented in Table 1.1.
40 Profile 6
¥ = 0.002x~28.32
R= 0,734
50 °
40
30
Distance from Baseline (m)
19
0
29/06/1957 8/03/1971 14/11/1984 24/07/1998 3/04/2012
Date
Distance from Baseline (m) Linear {Distance from Baseline (my)
Figure 1.3 — Long Term Shoreline Change at Profile 6
Profile 14
45
y=0,0004x + 19.204
40 R 20.07
Distance from Baseline (m)
8/03/1971 14/11/1984 24/07/1998 1/04/2012
Distance fram Baseline (m} Linear (Distance from Baseline (m)}
Figure 1.4 Long Term Shoreline Change at Profile 14
9/12/2025
9/12/2025
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Rates of Shoreline Progradation at the Castaways Beach Site Transect_ID | Rate of Shoreline Change (m/year) 2 0.62 3 0.72 4 0.74 5 0.75 6 0.73 7 0.74 8 0.64 9 | Ost 10 | 0.45 co 0.33 12 0.29 13 0.27 14 0.14 15 0.12 16 0.06 17 0.02 18 0.24 Based on the outcomes of these analyses, which demonstrate a long term shoreline progradation rather than long term erosion, the long term erosion effect has been set at zero for the purposes of the EPAW calculation. The observed rates vary from about 0.7m/year in the south to 0.1m/year in the north. 1.2.2 Storm Erosion The LIDAR survey data was used to develop two shore normal beach profiles for application in the SBeach storm erosion model. These profiles are located near the one-third points along the Castaways Beach shoreline. The beach profile included characteristic sediment particle sizes of 0.15 and 0.35mm, based on typical beach sand sizes and the need to test sensitivity to particle size. Storm erosion of the shoreline at the site was investigated using the SBEACH modelling system. SBEACH was developed by the U.S. Army Corps of Engineers (USACE) to investigate storm induced profile response on fine to medium grain sand beaches. It is an empirically based model that includes wave shoaling, refraction, breaking, set-up and run-up. The model can simulate a temporally varying wave-breaking point, which produces offshore bar migration. The model has been widely applied at sites all over the world and has demonstrated reasonable levels of calibration. An SBEACH analysis was undertaken for the selected profiles at the study site using the 100-years ARI cases described in Table 1.2 as part of a 12 hours storm, peaking at 6 hours. Storm tide levels and nearshore wave heights were determined from information presented in State Development (2014). Based on these analyses at two shore normal profiles, the storm erosion component of the EPAW calculation is 32m — including post-storm slumping.
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Table 1-2 Met-Ocean Input for Storm Erosion Analyses at Castaways Beach Component 100-Years ARI Value Significant Wave Height 9.64m Peak Wave Period 16s Storm Tide Level 2.44m AHD 1.2.3 EPAW Calculation Based on the analyses described herein, the calculation of the EPAW was taken to be:- E=[(NxR)+C +S] x (1+F)+D = [(83x0) + 32 + 23] x (1.4) =77m According to the Queensland Coastal hazard Guidelines, this calculated EAWP is to be set back from the seaward toe of the frontal dune at the site. The seaward toe of the frontal dune is normally approximated by the seaward limit of terrestrial vegetation or, where this cannot be determined, the level of present day HAT. 'Present day HAT' in the definition is always taken to be the present day level of HAT for the coastline as defined in the Queensland Tide Tables for that year, or as defined by empirical methodology at the site. In this way the landward boundary of the erosion prone area defined above will continue to move landward over time as sea level rises in the future.
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2 References Department of State Development (2014): Sunshine Coast Airport, Section B4, Coastal Processes, prepared in conjunction with Sunshine Coast Council.
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753345 9 August 2017 APPENDIX B STATE CODE 8 COMPLIANCE CAUsersitrevor johnson\Documents'castaways.docx
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753345 9 9 August 2017 APPENDIX C NATURAL HAZARDS OVERLAY CODE COMPLIANCE CAUsers\trevor johnson\Documents\castaways.docx
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“AELOAG Ajsuealpolg ay) Aq peyaye sease Aue JO S@SiNOOa}EM UO JOOYO OU EAeY |JIM SYJOM O}IS OYL “PATIY. 8q JOU WM IIS BY oupseg Papiaoid uonnjos ON *]2A9] POoY pepsooad yseyBiy oy} MOjEq pue| Surjy Aq peaagiyoe jou si seese juswidojaaep 404 Aun] pooy ‘ajqepeae jou si Buyjjapow asayAA JO ‘JaAe] POoY (yy Je8A O01: L) dav %} eu} Mojaq pue| Bully Aq persiyoe jou si seaue jUsWdojaaep 404 AjuNLULU! poo) anv ‘Aun Peo a4} sayojew Jeu) L/S) B1IGeL ul peynuep! Bose 92. POOY ey} 0} ssacoe sAeY sj} ||e ‘(epINd youny pue |/BJUIeY UeeySsNy Oy} pue jenueW uBiseq aBeuresg pue peoy podsues! pid euj jo 9 se}deyD Aq psurwwejep se) AjunWW! pooy ayloeds e aplAoud juewidojenap e HuldiAles speos Busixs ayy ausuA, "aJaymes|s soaiiadoid uo sjaag] Jaye (9 pue ‘|6WO -L' LINO sdey Aepyeagc AjisueAlpoig uo payijuep! puke] UO uOReaBe (q pue ‘spuenem pue saul) s6euleip ‘sasunoouayem (2 —uo yoedul Ajesseape JOU seop }! eseUM s1n990 AjUO UOMeAROXe JO Bulls Z0zs ‘quawidojsaap dy} }INS 0} WoypUeR] oY} BurAypow uey} Joyyes Wuopue] jeinyeu L'0zS 9u) YIM sayesBejul jUeLUdOjeASq “8SN papusjul 49U) ayepOULUCDIe Ajayenbepe pue Ajajes 0} ‘}eA9| Z6LS pooy pepiooa ysayBiy euy ‘aiqeyreae
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Lv oupsea Loz Aine ‘ays ay) Jo AUepunog PUEMBAS a4} WO Lug JO LUNI 2 yorqjas ae sijem Buiulejos pue saunjonys Jeujo ‘s6ulpying uoyyoreq ay) Bululofpe aalasal e 10 JuOyYyoRaq au} Bunuoy saiedoud uo ys1xo “@WDINE oy!oadg ey} YM AjdWOd jm JUaWUdO|eAep OU, “paplaosd uo|Njos oN 'LZS jou seop aul Bulpying jeyseoo e aJaUNA—s« LZO “(Zeb aunbig 9ag) Alepunog puemeas ay Woy Wg JO WNnuIUIW eB yoRqies ae (q pue ‘out Buipling je}se09 au} Jo puemeos we ueu} J9]e06 pus}xe you Op Jey} SefuOzjeq poseaa|ques pasojoueun pue peseaooun (2 —jdeoxe eur Buipling je}se09 au) Jo PJeMBdS PUZ}X9 JOU Op s}jem Bulule}oI pue sjood Burwiwims Bulpnjout b0zs saunjonys Joyo pue sbulpying == 0ZO. uodsex WNIes Sarat “@WODING dy!99dg ay} YM A[dWOd |]IM JUeLUdOJeASp OY, “paplacid uoINjOs ON
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753345 9 August 2017 APPENDIX D GEOTECHNICAL REPORT ‘CAUsersttrevor johnson\Documents\castaways.docx 10
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Our Ref: WE17035 CJ Cardno Contact: Richard Maurice Shaping the Future Cardno (Qid) Pty Ltd 10 July 2017 ABN 57 051 074.992 Ken Lynn Pty Ltd Level 11 c/- Peter McGregor 515 St Paul's Terrace Fortitude Valley QLD 4006 Australia Locked Bag 4006 Fortitude Valley QLD 4006 Australia Dear Sir, Phone: 617 3369 9822 Fax: 617 3369 9722 SLOPE STABILITY AT 2 DAVID LOW WAY CASTAWAYS BEACH www.cardno.com.au Background At the request of Dr Trevor Johnson of Cardno | have conducted an investigation into potential slope stability issues at the above site. It is understood that the property owner wishes to subdivide the site into six lots for further housing development. The site is currently occupied by two houses and has an approval for a 2 lot subdivision. The subject site comprises Lot 71 on Plan MCH2854. Noosa Planning Scheme interactive mapping indicates that the site is located in a potential landslide hazard area, accordingly a geotechnical assessment by an RPEQ is required under the Planning Scheme. Regional Geology Queensland Government geological maps show that Lot 1 on MCH2854 is underlain by the following geological formations: 1. Quaternary age freshwater swamp deposits (extreme northern part of the lot, apparently associated with the creek to the north) 2. Holocene age parabolic dunes; quartz sand (bulk of the lot) 3. Holocene age dunes, mainly parabolic, quartz sand (extreme northern part of the lot) Slope Stability and Coastal Hazard Mapping Noosa Planning Scheme interactive mapping indicates that the site is located in a potential landslide hazard area. The boundary of this mapping appears to coincide with the Queensland Coastal Hazard Areas Map showing erosion prone areas. There appears to be no other basis for the site to be considered to be located in a potential landslide area. It is understood that the subject of coastal erosion is addressed in a separate report. Site Inspection On 15% June 2017 | undertook an inspection of the site, the following points were noted. e The site is currently occupied by two detached single unit houses. e Where visible, surface soils comprised clean dune or beach sand. Australia e Belgium « Canada » Ecuador e Germany e Indonesia e Italy e Kenya e New Zealand « Papua New Guinea e Peru » Tanzania « United Arab Emirates « United Kingdom e United States ¢ Operations in 85 countries Printed on 100% Recycled Paper
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2 cly Cardno 26 July 2017 Shaping the Future e Slopes across the currently developed part of the lot were assessed as flatter than 4H:1V. e No evidence of present or past instability was noted. Proposed Development It is understood that the proposed new buildings will be substantially larger than the current dwellings and may require piled foundations. From a geotechnical standpoint the site is considered suitable for such construction provided that appropriate standard engineering design and construction is undertaken. The following points should be noted: e Construction should not encroach on the area near the creek at the northern end of the site (recommended set back 50m from the extreme northern end of the lot). e Site specific geotechnical investigations (boreholes, field and laboratory testing) will be required at design stage to inform foundation and earthworks design. Such investigations are not required to assess the general suitability of the site for development. « Appropriate erosion protection measures including vegetation will be required where non-cohesive sands are exposed. Please do not hesitate to contact the undersigned should you have any enquiries. Yours faithfully POn Richard Maurice Senior Geotechnical Engineer R.P.E.Q. 8354 For Cardno Direct Line (07) 3100 2231 \\AubnecfsO7\wre$\WE17035\wp\WE17035 Geotech Letter,docx