Byron Flora and Fauna Study 1999 - Byron Shire Council
Byron Flora and Fauna Study 1999 - Byron Shire Council
Byron Flora and Fauna Study 1999 - Byron Shire Council
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BYRON FLORA AND FAUNA STUDY, <strong>1999</strong><br />
5.4 METHODS<br />
Records within <strong>Byron</strong> <strong>Shire</strong> of flora species scheduled in the TSC Act, 1995 <strong>and</strong>/or in the NSW list of Rare<br />
or Threatened Australian plants (Briggs <strong>and</strong> Leigh 1996) were obtained from NSW NPWS Wildlife Atlas<br />
database, Quinn et al. (1995), Sheringham <strong>and</strong> Westaway (1995) <strong>and</strong> numerous reports. As the former<br />
source in particular includes numerous inaccuracies, all records were validated before incorporation into the<br />
database. Validation was achieved by personal communication with the original observer, through local knowledge<br />
of the authors, or if necessary by field inspection. As a result, the accuracy of the location reported in the secondary<br />
sources was frequently improved, <strong>and</strong> inaccurate records discarded. In addition, a number of botanists contributed<br />
their unpublished records. As the study was focused on private l<strong>and</strong>s, Crown l<strong>and</strong> <strong>and</strong> council-owned l<strong>and</strong>, the<br />
occurrence of target species in National Parks, Nature Reserves <strong>and</strong> State Forests was recorded on a presence/<br />
absence basis for context <strong>and</strong> to establish <strong>Shire</strong>-level reservation status. Multiple records for public l<strong>and</strong>s<br />
were not solicited, although when readily available were incorporated in to the database.<br />
Regionally significant species (Sheringham <strong>and</strong> Westaway 1995) other than those also listed as Threatened<br />
or ROTAP species were not targeted.<br />
From the available information about the habitat of each species, other possible locations within the <strong>Shire</strong><br />
were predicted. Limited targeted surveys were carried out <strong>and</strong> further locations were recorded during API<br />
ground truthing <strong>and</strong> plot-based vegetation surveys.<br />
In addition, the survey was advertised in the local press, <strong>and</strong> residents invited to apply for a data record form<br />
(Appendix 6) listing target species <strong>and</strong> requesting details of records of Threatened species. A large number<br />
of forms was distributed. Records returned were validated <strong>and</strong> incorporated into the database.<br />
Each record was assigned a data type code (point location = X, mapped polygon = P, public l<strong>and</strong> polygon<br />
ie National Park, Nature Reserve or State Forest = R, general locality = L). The latter were frequently<br />
historical herbarium records for which the location was given as a general locality such as Mullumbimby.<br />
Records in this category were not mapped but are held in the database. Point locations by their nature are<br />
associated with an AMG grid reference. Records relating to polygons were assigned a grid reference of a<br />
convenient point for mapping purposes.<br />
In addition, each record was assigned an accuracy code (grid reference of point representing location to<br />
nearest 100 m = 1, grid reference of point representing location to nearest 1000 m = 2, grid reference of<br />
point representing location to less than 1000 m accuracy = 3).<br />
Dates, observers <strong>and</strong> sources of data were recorded. Part of the database table is shown to illustrate (Table 5.4).<br />
Modifications were made to some records for the genus Phaius. Some database records for P. tankervilliae are<br />
likely to represent P. australis (Sheringham <strong>and</strong> Westaway 1995), while others, having been recorded outside<br />
the flowering season, are designated as Phaius sp. (Stewart <strong>and</strong> McKinley 1997). In addition, some taxonomists<br />
are of the opinion that the two taxa will prove to be conspecific (P. Bostock, Queensl<strong>and</strong> Herbarium, pers.<br />
com.). Accordingly, all records for Phaius spp. were entered as P. australis.<br />
Changes in TSC Act, 1995 status to two Threatened species occurring in <strong>Byron</strong> <strong>Shire</strong> were gazetted during<br />
the study period. The Basket Fern Drynaria rigidula was presumed to be extinct in NSW (TSC Act, 1995)<br />
<strong>and</strong> was formerly listed on Schedule 3 (Extinct). The Basket Fern was recorded at Anderson’s Ridges in<br />
<strong>Byron</strong> <strong>Shire</strong> several years ago (Kinhill 1997) <strong>and</strong> has also been recorded recently from Cape <strong>Byron</strong> (S.<br />
Bower pers. comm.) <strong>and</strong> at Broken Head during current surveys. It is now listed on Schedule 1 (Endangered).<br />
The listing of Phaius australis has been altered from Schedule 2 (Vulnerable ) to Schedule 1 (Endangered).<br />
These listings have been updated in the database <strong>and</strong> throughout the report.<br />
Changes to l<strong>and</strong> tenure during the study period have affected the reservation status of some species. The<br />
Threatened species database requires updating where the names of record locations have changed. Forestryrelated<br />
threats have been removed from species which occur in those State Forests converted to National<br />
Parks (requiring updating in Table 5.7).<br />
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