Wambo Coal AEMR 2011-2012 - Peabody Energy
Wambo Coal AEMR 2011-2012 - Peabody Energy Wambo Coal AEMR 2011-2012 - Peabody Energy
2.3 Discussion 2.3.1 Species Diversity within Quadrats Variation in the number of species recorded in 2011 between quadrats is a factor of: • Within vegetation communities: » Differences in quadrat conditions, such as minor differences in aspect, slope, and soil type; » Inherent differences in the species composition of a single vegetation community throughout the community; and » Variation in the amount of rainfall at each quadrat. • Between vegetation communities: » The different species composition of different vegetation communities, generally as a result of different site characteristics, such as slope, aspect, soil type, etc. Variation in the number of species recorded across the five years of sampling is likely a factor of: • Seasonal conditions: » The increase in the number of species at all quadrats in 2007 is likely a result of a good season; » The general decrease in the number of species at quadrats in 2008 is likely a result of a poor season; and » Moderate to minor fluctuations in the number of species recorded in quadrats in 2009, 2010 and 2011 are likely a result of moderate seasonal conditions. • The timing of surveys: » Cryptic species such as orchids have only a short flowering and detectable period. Surveys completed in different months or even weeks of the year are likely to detect a different range of cryptic species; » There is no evidence to suggest that the number of flora species at any quadrat are being affected by current mining practices; and » Current land management practices within the RWEP areas appear to be appropriate for the conservation of flora species diversity. 2.3.2 Introduced Species Percentage Composition Variation in the introduced species percentage composition is likely due to: • Vegetation community/quadrat landform location. The three vegetation communities that recorded more than 25 percent of introduced species are all located within riparian locations where propagules (seeds and vegetative material) from weed species are easily distributed by moving water; • Variation in seasonal conditions from year to year; 2011 Annual Ecological Monitoring Report, Final Report, May 2012 Page 12
• Natural fluctuations in the abundance and distribution of introduced species from year to year; and • The timing of surveys from year to year. Annual introduced species may be detected in one month but not another. There is no evidence to suggest that the fluctuations recorded in the percentage composition of introduced species are due to any factor other than a combination of those listed above. 2.3.3 Introduced Species Abundance Variation in the number of introduced species recorded in quadrats in 2011 is likely a result of the same factors affecting the number of all flora species, as discussed above in Section 2.3.1. • Fireweed: » The distribution of Fireweed has increased from six quadrats in 2006 to a peak of 27 quadrats in 2010, but decreased to 24 quadrats in 2011; » The increase in abundance is likely due to a favourable season in 2007 when the species was recorded in 21 quadrats followed by the natural spread of the species by airborne seed dispersal; » At most sites Fireweed was recorded at a low density; and » Due to the low density of Fireweed at sites where it occurs, the small size of the plant and the absence of a species specific control measure (i.e. a species specific herbicide), no control actions are currently recommended for this species. • Prickly Pear: » The distribution of Prickly Pear has remained relatively constant from 2006 to 2011 being recorded in 17 and 21 quadrats respectively; » At most quadrats Prickly Pear was recorded at moderately low densities; » The variation in the abundance of this weed species is likely due to natural variation in this species abundance, most likely as a result of the species interaction with the Cactoblastis moth (Cactoblastis cactorum); and » Although Prickly Pear occurs at moderate density in parts of RWEP area A (outside quadrats), no control measures are recommended as it is anticipated that the Cactoblastis moth will respond to the increased density through increased fecundity. It is expected that the density of Prickly Pear will decrease over the next two years. • Scarlet Pimpernel: » Like Fireweed, the Scarlet Pimpernel increased its distribution between 2007 and 2010 from 9 to 15 quadrats respectively, however in 2011 a slight decrease in its distribution occurred, being recorded at 12 quadrats; » At most sites Scarlet Pimpernel was recorded at a low density; and 2011 Annual Ecological Monitoring Report, Final Report, May 2012 Page 13
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2.3 Discussion<br />
2.3.1 Species Diversity within Quadrats<br />
Variation in the number of species recorded in <strong>2011</strong> between quadrats is a factor of:<br />
• Within vegetation communities:<br />
» Differences in quadrat conditions, such as minor differences in aspect, slope, and<br />
soil type;<br />
» Inherent differences in the species composition of a single vegetation community<br />
throughout the community; and<br />
» Variation in the amount of rainfall at each quadrat.<br />
• Between vegetation communities:<br />
» The different species composition of different vegetation communities, generally<br />
as a result of different site characteristics, such as slope, aspect, soil type, etc.<br />
Variation in the number of species recorded across the five years of sampling is likely a<br />
factor of:<br />
• Seasonal conditions:<br />
» The increase in the number of species at all quadrats in 2007 is likely a result of a<br />
good season;<br />
» The general decrease in the number of species at quadrats in 2008 is likely a<br />
result of a poor season; and<br />
» Moderate to minor fluctuations in the number of species recorded in quadrats in<br />
2009, 2010 and <strong>2011</strong> are likely a result of moderate seasonal conditions.<br />
• The timing of surveys:<br />
» Cryptic species such as orchids have only a short flowering and detectable<br />
period. Surveys completed in different months or even weeks of the year are<br />
likely to detect a different range of cryptic species;<br />
» There is no evidence to suggest that the number of flora species at any quadrat<br />
are being affected by current mining practices; and<br />
» Current land management practices within the RWEP areas appear to be<br />
appropriate for the conservation of flora species diversity.<br />
2.3.2 Introduced Species Percentage Composition<br />
Variation in the introduced species percentage composition is likely due to:<br />
• Vegetation community/quadrat landform location. The three vegetation communities<br />
that recorded more than 25 percent of introduced species are all located within<br />
riparian locations where propagules (seeds and vegetative material) from weed<br />
species are easily distributed by moving water;<br />
• Variation in seasonal conditions from year to year;<br />
<strong>2011</strong> Annual Ecological Monitoring Report, Final Report, May <strong>2012</strong> Page 12