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ADG1304.21 Dewatering Management Plan_Rev1.1_17.12.24
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ADG Consulting Pty Ltd
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 sheet pile wall in fine‐medium grained sands, depending on density of the
strata).
5.3.2 Dewatering discharge rate based on stormwater system size (estimation)
It is expected that the stormwater network on Mossman Court (designated stormwater discharge
location) has a maximum flow capacity of approximately 81 L/sec (i.e. based on a 300 mm diameter
stormwater network pipe and an unknown install grade, calculated using minimum grade of 0.5 % as per
AS 3500.3, however likely to be greater).
A conservative estimate of 12 L/sec or 43,200 L/hr has been calculated by ADG – refer to Section 5.3.1
above.
5.3.3 Conclusions on expected extraction rates
It is recommended that the conservative estimate of 43,200 L/hour be adopted based on the sand profile
encountered during the sub‐surface investigations onsite. Based on previous dewatering projects
undertaken by ADG and ADS within the area, it is anticipated that initial flow rates will reduce to between
500 – 650 litres/minute following the initial drawdown of the water table.
The estimated discharge rate as determined in the above section 5.3.1, is well below (14.8 %) the Council
stormwater infrastructure capacity estimate (81 L/sec), therefore it is considered unlikely that discharge
of extracted groundwater from the site to the stormwater network on Mossman Court will cause any
disturbance/damage to council infrastructure or risk to the public. The likelihood of overtopping the
stormwater network and/or adjacent gully pits is considered unlikely because any such occurrences
would be limited to instances of extreme rainfall intensity, which are generally of short duration, and in
such a circumstance stormwater runoff would be expected to first utilise the remaining stormwater
network capacity (some approximately 69 L/sec), and any excess flow would then drain via the kerb and
channel to adjacent gully pits.
Any risks to the public associated with the placement of dewatering equipment to enable discharge to
the designated stormwater gully pit, should be mitigated by fencing and signage, have appropriate
lighting in place for after site hours and may need pipe over ramps to the pathway and/or driveways
where header pipe is to be placed in roadside guttering.
5.4 Dewatering duration
Dewatering will be necessary throughout the basement construction phase, which is expected to require
dewatering for approximately 10 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. 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.
ADG1304.21 Dewatering Management Plan_Rev1.1_17.12.24 Page 10
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