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Appendix 2 - Vegetation Communities and Regional Ecosystems

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Plant taxonomy <strong>and</strong> distributional data have been considerably advanced through initiatives such<br />

as CYPLUS <strong>and</strong> various taxonomic treatments.<br />

Studies of past environments have also developed an increasing body of literature. Palynological<br />

studies (Rowe 2006, Parr 2003, Barham 1999) <strong>and</strong> archaeological <strong>and</strong> anthropological<br />

investigations (David et al. 2004, David <strong>and</strong> Badugal 2006, Barham <strong>and</strong> Harris 1987, Barham et<br />

al. 2004, Shnukal 2004, McNiven 2008) offer an important cultural context for biodiversity<br />

assessment <strong>and</strong> elucidate anthropogenic influences on isl<strong>and</strong> biodiversity over a period of human<br />

occupation in the region of between 8 000 <strong>and</strong> 6 000 years (Rowe 2006) with permanent isl<strong>and</strong><br />

occupation occurring between around 3 800–2 500 years (BP) (David <strong>and</strong> Badugal 2006).<br />

3.2 Image Base Compilation <strong>and</strong> Aerial Photograph Analysis<br />

The initial stage of desktop assessment involved a compilation of remotely sensed imagery<br />

suitable for vegetation mapping purposes. Aerial photography was the preferred information<br />

base, allowing stereoscopic assessment of vegetation <strong>and</strong> l<strong>and</strong>form patterns <strong>and</strong> giving greater<br />

confidence to assignment of l<strong>and</strong> zone <strong>and</strong> vegetation structure classification. Historical aerial<br />

photography also provided a means to assess the pre-clearing distribution of vegetation<br />

communities in a large number of cases. Satellite imagery was used as a secondary means of<br />

vegetation community assessment where suitable aerial photography was not available, <strong>and</strong> was<br />

used as a base for photo-registration during digital processing, as well as a means of st<strong>and</strong>ardising<br />

vegetation mapping scales. A summary of aerial photography used in this assessment is provided<br />

in Table 4 below. Assessment of photograph quality relates to a subjective appraisal of image<br />

clarity, site coverage, shadow <strong>and</strong> cloud cover.<br />

Table 4. Aerial photography used for vegetation assessment purposes.<br />

Isl<strong>and</strong>/Isl<strong>and</strong><br />

Group<br />

Year Scale<br />

Schenckler Aerial Survey<br />

Negative Quality<br />

Buru 1999 1:12 000 Colour Excellent<br />

Mabuiag 1999 1:8 000 Colour Excellent<br />

Erub 1999 1:8 000 Colour Excellent<br />

Stephen 1999 1:4 000 Colour Excellent<br />

Iama 1999 1:4 000 Colour Excellent<br />

Yorke 1999 1:4 000 Colour Excellent<br />

Zagai 1999 1:16 000 Colour Excellent<br />

Ului 1999 1:8 000 Colour Excellent<br />

Zurat 1999 1:8 000 Colour Excellent<br />

Aureed 1999 1:9 000 Colour Excellent<br />

Warral 1999 1:16 000 Colour Excellent<br />

Deliverance 1999 1:4 000<br />

Commonwealth Flying<br />

Colour Excellent<br />

Murray 1988 1:30 000 B&W Moderate<br />

Dauan 1988 1:18 000 B&W Moderate<br />

Gabba 1988 1:25 000 Colour Excellent<br />

Deliverance 1971 1:42 000 B&W Moderate<br />

Adolphus 1973 1:34 000 B&W Poor<br />

Tudu 1973 1:12 000 B&W Excellent<br />

Moa<br />

Badu<br />

1974 1:34 000 B&W Poor<br />

Moa-Badu 1971 1:85 000 B&W Excellent<br />

Sassie, Burpa,<br />

Warraber<br />

1973 1:50 000<br />

State Flying<br />

B&W Moderate<br />

3d Environmental – Torres Strait <strong>Regional</strong> Ecosystem Mapping Project – August 2008<br />

9

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