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220328 - Edwards Street - Slope Stability Assessment
Bev Jenner Const. 22073-001-Rev0 C/- Westera Partners 25 March 2022 The existing timber retaining wall to the north-eastern boundary should be removed and replaced with a new structure preferably of more durable materials (e.g. concrete) behind the pool shells and pool terraces. While only landscaping works appear to the proposed in the southern corner adjoining 166 Edwards Street, an assessment should be made of the existing masonry blockwork/concrete wall and surcharge from features above (e.g. the swimming pool) such that a non-worsening condition eventuates from the proposed construction, and especially that no ‘undermining’ through cut earthworks occurs. 4.2 Earthworks Care should be taken to ensure construction works do not cause excessive ground vibrations that could result in damage to existing nearby structures. Should vibratory techniques be proposed (e.g. vibratory fill compaction, sheet piling, etc.), ground vibrations should be monitored, and construction methods may need to be altered should adverse impacts be anticipated or encountered. It would be prudent to conduct a dilapidation survey of nearby structures before commencement of construction. 4.2.1 Site Preparation and Trafficability Following removal of the existing structures (where required) and associated construction elements (e.g. footings, services, etc.), any tree stumps and large roots should be ‘grubbed out’. Any organic rich topsoil and uncontrolled fill should then be stripped and set aside. Any organic affected topsoil materials must not be used in structural fill; however, may be placed across landscaping areas. The natural subgrade following stripping will likely be in a loose condition. Where slab on ground construction is proposed the ground surface should be compacted by several passes of a vibrating plate compactor or small smooth drum roller (or similar), in conjunction with surface application of ample water. After initial stripping the subgrade is expected to comprise a mixture of silty sands and relatively ‘clean’ beach ridge sands. Although relatively good trafficability should initially be encountered, these materials could be subject to strength loss from repetitive vehicle loading (particularly from heavy rubber tyred plant) and if they become excessively dry. Due to the potential for poor trafficability, placement of a minimum 150 mm thick granular working platform will likely be required, at least across access and laydown areas. Groundwater seepage was not encountered during the Unearthed ‘soil test’ fieldwork; however, depending on the prevailing weather conditions at the time of construction, groundwater seepage may develop at relatively shallow depths. The site should be graded to shed surface water runoff away from construction areas. Swale drains should be constructed along the toes of any cuts, and above cuts where possible, with the drains graded to discharge collected waters to a control point before release off-site. Appropriate erosion and sediment control measures must be installed prior to commencement of earthworks at this site. 4.2.2 Filling The existing sandy soils (excluding any topsoil) may be reused as structural fill, subject to appropriate moisture adjustment. It should be noted that compaction of relatively ‘clean’ sands (expected to form most of the semi-basement excavation spoil) as structural fill requires the addition of substantial volumes of water (‘flooding’) combined with the use of vibratory compaction equipment (typically a smooth drum roller or vibrating plate). Should importation of fill be required, it is recommended that such fill should comply with the following: Minimum CBR of 10 % Maximum plasticity index of 15 % Shrink-swell index ≤ 1 % Maximum particle size of 100 mm Any fill should be compacted at moisture contents within the range of ±2 % of optimum moisture content for Standard Compaction. Select fill should have a maximum particle size of 100 mm for an uncompacted layer thickness of 200 mm and shall be compacted by repeated rolling with a small compactor to achieve a dry density ratio of at least 95 % of the Standard Maximum Dry Density for cohesive soils, or 70 % Dry Density Index for any imported cohesionless soils. 10/14
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