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Appendix 2 - Vegetation Communities and Regional Ecosystems

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3. Methods<br />

3.1 Desktop Literature Review<br />

A search of relevant literature <strong>and</strong> databases provided background information on the intensity<br />

<strong>and</strong> results of previous survey, the presence <strong>and</strong> distribution of vegetation communities <strong>and</strong> flora<br />

species in the broader region. Site data sourced from the Queensl<strong>and</strong> Herbarium’s CORVEG<br />

database provided information on the location of previous survey sites <strong>and</strong> data extracts sourced<br />

from HERBRECS <strong>and</strong> the CORVEG database provided information on flora species distribution.<br />

The method also included a review of previous studies completed by private organisations <strong>and</strong><br />

government agencies over relevant sections of the study area. Relevant publications included<br />

project specific reports, state government biodiversity planning studies, regional management<br />

strategies, as well as any useful academic studies.<br />

A regional perspective of the vegetation communities across the Torres Strait Isl<strong>and</strong>s is limited to<br />

the mapping carried out as part of the Cape York Peninsula L<strong>and</strong> Use Study (CYPLUS) in 1995<br />

(Neldner <strong>and</strong> Clarkson 1995). This work produced pre-clearing mapping at 1: 250 000 scale<br />

using Aerial Photograph Interpretation (API) only for isl<strong>and</strong>s north of Badu Isl<strong>and</strong> <strong>and</strong> a<br />

combination of API <strong>and</strong> limited ground-truthing. Using the analysis of that work by Neldner<br />

(1998), the regional analysis of vegetation prior to the current survey is as follows.<br />

Table 1. Extent of amalgamated broad vegetation groups in the Torres Strait isl<strong>and</strong>s (Neldner 1998).<br />

Amalgamated Broad <strong>Vegetation</strong> Groups<br />

Area<br />

(km 2 )<br />

% of total<br />

area<br />

Corymbia/Eucalyptus spp. dominated woodl<strong>and</strong>s, open-woodl<strong>and</strong>s <strong>and</strong><br />

open-forests<br />

231.7 25.9<br />

Melaleuca spp. low open-woodl<strong>and</strong>s, low woodl<strong>and</strong>s <strong>and</strong> tall shrubl<strong>and</strong>s 105.0 11.7<br />

Grassl<strong>and</strong>s <strong>and</strong> grassy open-woodl<strong>and</strong>s 59.7 6.7<br />

Closed-forests (excluding mangroves) 156.1 17.5<br />

Mangrove closed-forests 220.9 24.7<br />

Heathl<strong>and</strong>s 11.7 1.3<br />

Other communities (littoral vegetation, sedgel<strong>and</strong>s, saltpans <strong>and</strong> wetl<strong>and</strong>s) 108.1 12.1<br />

TOTAL 893.2 100.0<br />

Table 2. Percentage <strong>and</strong> area of each structural formation in Torres Strait Isl<strong>and</strong>s (Neldner 1998)<br />

Torres Strait Isl<strong>and</strong>s<br />

Structural Formation No. of map<br />

Area km 2 % of total area<br />

Woodl<strong>and</strong><br />

Low open-woodl<strong>and</strong><br />

Tall woodl<strong>and</strong><br />

Open woodl<strong>and</strong><br />

Closed-forest<br />

Open-heath<br />

Open-forest<br />

Closed-tussock grassl<strong>and</strong><br />

Tussock grassl<strong>and</strong><br />

Sparse-herbl<strong>and</strong><br />

Low closed-forest<br />

Low woodl<strong>and</strong><br />

Low open-forest<br />

Open-sedgel<strong>and</strong><br />

Tall shrubl<strong>and</strong><br />

Lakes <strong>and</strong> lagoons<br />

units<br />

7<br />

3<br />

-<br />

-<br />

7<br />

2<br />

5<br />

4<br />

1<br />

4<br />

9<br />

2<br />

1<br />

-<br />

1<br />

-<br />

233.2<br />

43.5<br />

-<br />

-<br />

212.0<br />

1.6<br />

11.0<br />

56.5<br />

3.3<br />

58.4<br />

183.1<br />

55.5<br />

18.0<br />

-<br />

0.6<br />

-<br />

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

26.1<br />

4.9<br />

-<br />

-<br />

23.7<br />

0.2<br />

1.2<br />

6.3<br />

0.4<br />

6.5<br />

20.5<br />

6.2<br />

2.0<br />

-<br />

0.1<br />

-<br />

7

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