Wambo Coal AEMR 2011-2012 - Peabody Energy
Wambo Coal AEMR 2011-2012 - Peabody Energy
Wambo Coal AEMR 2011-2012 - Peabody Energy
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<strong>2011</strong>-<strong>2012</strong> <strong>AEMR</strong><br />
prior to undermining. The results from that survey<br />
concluded the stand is generally healthy with<br />
respect to Age Classes, Recruitment, Health,<br />
Infestations and Senescence. The stand shows the<br />
typical attributes of a dynamic population which is<br />
self-propagating and is likely to continue to do so<br />
provided no stochastic events impact upon the area.<br />
Underground mining activities below this stand of<br />
Acacia species were completed during the reporting<br />
period. In accordance with the Acacia pendula<br />
Management Plan for LW Panel 4, post inspections<br />
were undertaken on 5 December <strong>2011</strong> by an<br />
ecologist. These investigations were conducted as a<br />
due diligence precaution to compare the condition of<br />
the population with regards to the health,<br />
recruitment, extent and habitat attributes<br />
subsequent to undermining by LW-4.<br />
The stand of Acacia pendula (Weeping Myall) within<br />
the RWEP area is generally healthy with respect to<br />
Age Classes, Recruitment, Health, Infestations and<br />
Senescence. The stand shows the typical attributes<br />
of a dynamic population which is currently<br />
selfpropagating and is likely to continue to do so<br />
provided no stochastic events impact upon the area.<br />
There are large numbers of the parasitic mistletoe<br />
Amyema pendula present on many of the Weeping<br />
Myall trees. In high numbers these mistletoes have<br />
a detrimental effect on the Weeping Myall and have<br />
most likely caused the death of some specimens.<br />
For the complete assessment report, please refer to<br />
Appendix 2G.<br />
3.7.2.3 Remnant Woodland Enhancement<br />
Program<br />
The objective of the Remnant Woodland<br />
Enhancement Program (RWEP) is to help conserve<br />
regional biodiversity, whilst enhancing the habitat<br />
available to flora and fauna. The RWEP will provide<br />
a strategy that gives protection in perpetuity for<br />
RWEP Area A and long-term protection of RWEP<br />
Areas B and C. The RWEP also includes the area<br />
within the area of the WRD rail loop (see Figure<br />
3.18).<br />
During late 2009, WCPL added another area of<br />
approximately 50ha to the Remnant Woodland<br />
Enhancement Program. The additional area offset<br />
construction of the new South Dam. This recent<br />
offset area is now referred to as RWEP Area D (see<br />
Figure 3.18).<br />
<strong>2011</strong> Annual Ecological Monitoring Summary<br />
Flora monitoring identified 266 flora species across<br />
34 flora quadrats. Based on these observations, the<br />
current management practices within the RWEP<br />
areas of <strong>Wambo</strong> <strong>Coal</strong> Mine is appropriate for the<br />
conservation of flora species. Variation evident in<br />
the results from the six years of monitoring is most<br />
likely related to natural variation in species<br />
distribution, natural variation in species abundance<br />
and variation inherent in the sampling design, and<br />
not due to current management practices. There<br />
was no evidence to suggest that current<br />
management practices or mining activity was having<br />
any effect on the flora species within the RWEP<br />
areas of <strong>Wambo</strong> <strong>Coal</strong> Mine.<br />
While no Swift Parrots (Lathamus discolor) or<br />
Regent Honeyeaters (Anthochaera phrygia) were<br />
identified during targeted winter bird surveys, annual<br />
surveys for these species should continue into the<br />
future, particularly during years of heavy eucalypt<br />
blossom when either or both species may occur on<br />
<strong>Wambo</strong> <strong>Coal</strong> land.<br />
Diurnal bird monitoring identified a total of 126 bird<br />
species across 26 survey sites and<br />
opportunistically, including nine threatened species.<br />
Current management practises within the RWEP<br />
areas of <strong>Wambo</strong> <strong>Coal</strong> Mine appear to be<br />
appropriate for the conservation of bird species.<br />
Variation evident in the results across the years of<br />
monitoring is most likely related to natural variation<br />
in species diversity, natural variation in species<br />
abundance and variation inherent in the sampling<br />
design, and not to current management practises.<br />
One Powerful Owl (Ninox strenua), which is listed<br />
as Vulnerable under the NSW Threatened Species<br />
Conservation Act 1995 (TSC Act), responded during<br />
call playback surveys. Owl species targeted by call<br />
playback also included Masked Owl (Tyto<br />
novaehollandiae), Barking Owl (Ninox connivens)<br />
and Sooty Owl (Tyto tenebricosa). Due to the large<br />
home range area of the target owl species, which<br />
each have a home range in the vicinity of or greater<br />
than 1000 hectares and the relatively few (four) call<br />
playback sessions undertaken each year it is not<br />
unexpected that threatened owls species are rarely<br />
detected.<br />
Spotlighting surveys identified the Common<br />
Brushtail Possum (Trichosurus vulpecula) as the<br />
most common arboreal mammal species in RWEP<br />
areas of the <strong>Wambo</strong> <strong>Coal</strong> Mine. Across five years of<br />
annual monitoring only four arboreal mammal<br />
species have been identified. The Common<br />
Brushtail Possum was identified each year and the<br />
Sugar Glider (Petaurus breviceps) was recorded for<br />
the first time in <strong>2011</strong>. The threatened Yellow bellied<br />
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