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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 />

Page 61

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