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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 />

<br />

<br />

<br />

<br />

<br />

<br />

<br />

<br />

<br />

<br />

<br />

<br />

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

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