Metropolitan Coal Project Independent ... - Peabody Energy
Metropolitan Coal Project Independent ... - Peabody Energy
Metropolitan Coal Project Independent ... - Peabody Energy
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METROPOLITAN COAL PROJECT INDEPENDENT ENVIRONMENTAL AUDIT<br />
mm/m, however this maximum observed value was in the base of a valley. The observed tilts<br />
along the D-Line away from the topographic highs and lows are generally similar to or below<br />
the predicted tilts. No anomalous movements have been identified”.<br />
The End of Panel Report for LW20 (dated 25 January 2012) included the results of the Subsidence<br />
Monitoring Program that forms part of the Extraction Plan for LWs 20 to 22. The extraction of Longwall<br />
20 commenced on 9 May 2010 and was completed 16 August 2011.<br />
In summary, measured surface subsidence effects and impacts were generally within predicted<br />
ranges. The occurrences where measured subsidence was in excess of predicted subsidence effects<br />
were either associated with disturbed pegs or movements that were within the accuracy of the survey<br />
and prediction methods (i.e. the subsidence magnitudes were very low). The observed subsidence<br />
impacts were also consistent with, or less than those predicted.<br />
Aboriginal Heritage sites within 35 o angle of draw are not scheduled to be surveyed / inspected until 3<br />
to 6 months after LW20 is completed. The pre-mining condition of the sites was assessed during the<br />
Environmental Assessment phase of the project.<br />
A summary of the predicted subsidence effects after the completion of LW20 were:<br />
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Measured subsidence effects above LW20 were less than predicted values or within survey<br />
tolerances where several minor exceedences had occurred.<br />
Valley closure and uplift were minor and less than predicted values.<br />
No impact (i.e. cracking) or instability (i.e. rock-falls) was observed along Cliff No’s OH1 and<br />
OH2 and complies with prediction that less than 3% of length of cliff line would be impacted<br />
by mining.<br />
No impact (i.e. cracking) or instability (i.e. rock-falls) was observed on steep slopes and<br />
complies with prediction that tension cracks are not expected to exceed 0.1 m width and 25 m<br />
length due to mining.<br />
Some minor cracking along existing joints with fresh widely spaced cracking across Waratah<br />
Rivulet and exposed rock bars was consistent with the range of predicted impact have<br />
occurred due to valley closure effects south of LW20.<br />
No surface water flows appear to have been diverted or re-routed through rock bars or below<br />
the creek bed, which was indicated to be a potential impact.<br />
No surface ponds along the Waratah Rivulet have been impacted by the observed mine<br />
subsidence to-date, which was indicated to be a potential impact.<br />
No mining related impact to upland or valley swamp surface and groundwater levels have<br />
been detected in Swamps that exist above or within a 35 o angle of draw from LW20 (S16-18,<br />
20 and 25). Paired piezometers in the sub-strata and underlying sandstone units supporting<br />
the swamps clearly show natural recharge/discharge cycles are continuing to occur. Several<br />
new piezometers were installed along Waratah Rivulet and Eastern Tributary during the<br />
review period as indicated in the management plans.<br />
Ecological surveys have not detected any change to flora species populations, riparian<br />
vegetation or creek bank instability.<br />
Stream water quality sampling results were presented along the Waratah Rivulet, Tributary B<br />
and D and Eastern Tributary (C) and appear to meet the Performance Measure requirement<br />
of “negligible environmental consequence”.<br />
raw water quality data demonstrates that the overall water quality of most Indicator<br />
parameters has not been noticeably affected by mining.<br />
Analyte concentrations were relatively consistent between the sites with all watercourses<br />
experiencing spikes or pulses throughout the time series. The Waratah Rivulet appeared to<br />
have higher manganese concentrations and the Woronora River higher aluminium<br />
concentrations.<br />
4.14.5 Gas Releases<br />
The AEMR’s have reported a gas release from Pool H on the Waratah Rivulet identified on 5 January<br />
2011. The gas release is not an exceedance of the <strong>Metropolitan</strong> Colliery performance measures that<br />
34 trevor brown & associates<br />
applied environmental management consultants<br />
aemc