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Abel Tasman Foreshore Scenic Reserve Draft Management Plan

Abel Tasman Foreshore Scenic Reserve Draft Management Plan

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(v)<br />

Indigenous bird habitats<br />

(see Appendix 7 for the New Zealand threat classification system)<br />

The islands along the <strong>Abel</strong> <strong>Tasman</strong> coast are being managed as mammalian pest free<br />

areas. Islands with no predators, and generally lower human disturbance than<br />

mainland habitats, provide important habitats for birds which use or cross the<br />

intertidal zone within the reserve. Reef herons (‘threatened’ –‘nationally vulnerable’)<br />

are regularly observed on the islands and the more isolated parts of the mainland<br />

shore, and may breed at Taupo Point and on Pinnacle and Fisherman/Motuarero-iti<br />

islands. Blue penguins (‘at risk’ – declining’) breed on Adele/Motuarero-nui, Tonga<br />

and Fisherman/Motuarero-iti islands, and along the mainland shore. Spotted shags<br />

(not threatened) breed on the Tata Islands and roost elsewhere, including parts of<br />

Adele/Motuarero-nui and Fisherman/ Motuarero-iti islands. The granite reefs and<br />

rocky shores throughout the reserve also provide important habitat for banded<br />

dotterel (‘threatened’ – ‘nationally vulnerable’) and variable oystercatcher (‘at risk’ –<br />

‘recovering’).<br />

Sand spits within the reserve provide important roosting or breeding sites for birds.<br />

The largest sand spits are at Awaroa and Wainui inlets. Smaller sand spits are<br />

located at Totaranui, Torrent Bay/Rakauroa, Falls River, Bark Bay/Wairinga and<br />

Marahau. White-fronted terns (‘at risk’ – ‘declining’) breed at the Awaroa sand spit,<br />

and variable oystercatchers use most of the sand spits in the reserve, including those<br />

at Torrent Bay/Rakauroa, Awaroa and Falls River.<br />

The estuaries within the reserve seldom attract the large numbers of waders that<br />

utilise the extensive fine-sediment estuaries in the region such as Farewell Spit and<br />

Waimea Inlet. However, they do provide important unmodified habitats which may<br />

be used as stopover points for migrating waders. They also support approximately<br />

2000 South Island pied oystercatchers (‘at risk’ – ‘declining’) and 200 banded<br />

dotterels at various times through the year.<br />

Salt marsh and herbfield habitats comprise 23% of the estuarine areas within the<br />

reserve. This habitat, spread over 15 estuaries, provides critical habitat for<br />

approximately ten pairs of banded rail (‘at risk’ – ‘naturally uncommon’). Other<br />

‘threatened’ or ‘at risk’ bird species utilising estuarine habitats are the grey duck<br />

(‘threatened’ – ‘nationally critical’), Australasian bittern (‘threatened’ – ‘nationally<br />

endangered’), fernbird (‘at risk’ – ‘declining’), and marsh crake (‘at risk’ –<br />

‘recovering’).<br />

Table 1, Appendix 7 lists the ‘threatened’ and ‘at risk’ bird species that may be found<br />

in the reserve.<br />

(vi)<br />

Indigenous invertebrate habitats<br />

Invertebrate habitats within the reserve include granite shores, limestone shores,<br />

estuarine flats and sandy beaches. Fifty-three species of invertebrate have been<br />

recorded from granite shores within the reserve, compared with 27 species on<br />

limestone shores. Granite zonation patterns comprise a high tide zone dominated by<br />

two species of periwinkle, an upper tidal zone dominated by barnacles, a mid-tide<br />

zone dominated by barnacles and little black mussels, and a low tide zone dominated<br />

by tube worms. The zonation pattern on limestone is quite different, including the<br />

replacement of the granite barnacle species with another barnacle species, tube<br />

worms not confined to the one zone, the more common presence of a bryozoan<br />

species. A wide variety of invertebrate species are present on rocky habitats in the<br />

3. Conservation of natural resources 21

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