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3. Noosa Project Restoration Plan V12
Attached to the e-mail Noosa Oyster Project _ Construction and Environmental Management Plan (CEMP).
Attached to the e-mail DA Application - Noosa Oyster Project (1 of 3).
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Log in to see the plans as drawn2.3 Restoration suitability
TNC overlayed the Habitat Suitability Model with ecological considerations, logistical constraints, and
details of the built infrastructure and human uses of the Noosa River. These parameters were then
allocated exclusion criteria, to minimise potential interactions of the river users with restoration sites
(e.g. distances from tidal works, foreshore access points, moorings, submarine cables) (Table 2.2). The
results of this analysis are presented, geospatially, in the restoration suitability model (Figure 2.2). The
exclusion criteria where determined in consideration of regulated distances applied to vessels (e.g.
distances from moorings) and on practical consideration of river uses (e.g. access to foreshores from
the river, distances from navigation channels). This assessment was undertaken in consultation with
Maritime Safety Queensland (MSQ) and NSC and reviewed by the Noosa TAG.
Table 2.2: Restoration suitability parameters and exclusion criteria for rock oyster ecosystems in the
Noosa River estuary
PARAMETER ENVELOPE CRITERIA (more RATIONALE SOURCE
suitable = 4, less
= 0)
Marine plants 10m – Areas within 10- Connectivity to other structured habitats such as (Duncan et
proximity 500m 500m buffer =4; seagrass, mangroves, increases diversity. 10m al. 2019)
(including all other areas minimum distance used to mitigate damage to Confirmed
seagrasses) =2 marine plants and 2m from mangroves, aerial with
mangrove roots and fallen timber, but ensuring engineers
connectivity.
Rocky reef 2m – 500m Areas within 5- Connectivity to other structured habitats
proximity 500m buffer =4; increases diversity. 2 metre minimum distance
all other areas included to mitigate damage to rock substrates
=2 while maintaining connectivity. Direct
augmentation of degraded rocky reef by permit
only.
Extant oyster 2m – 250m Within 2m – Connectivity to other structured habitats (Boor et al.
ecosystems 250m = 4; all increases biodiversity. Connection to other oyster 2018, Guy
proximity other areas = 2 reefs increases meta-population connectivity, et al. 2018,
successful reproduction and oyster recruitment. 2 Duncan et
metre minimum distance included to mitigate al. 2019)
damage to extant oyster ecosystems but ensuring
connectivity.
Historical oyster Within 250 Within 250m = Sites which have historically supported oyster (Gillies
ecosystem m 4; all other areas ecosystems are thought to be able to support 2018)
proximity =2 future oyster ecosystems. Restoration takes place
on the sites of historic oyster ecosystems, which
may now be lost, where known and practical.
Mobile seabed Exclusion Within exclusion Highly mobile seabeds generally offer unsuitable Agreed
area area = 0, all substrates for shellfish restoration. with TNC
other areas = 4 restoration
scientists
Mangroves +2m Within exclusion Minimum distance of 2m maintained between (Boor et al.
(including minimum area = 0, all intertidal marine plants and oyster ecosystems to 2018, Guy
pneumatophores), distance other areas = 4 protect plants, as well as fallen trees (which are et al. 2018,
fallen trees and also important habitats) from works associated Duncan et
timber in with the oyster ecosystem. Relatively close al. 2019).
waterways. proximity maintained to maximise ecological Discussed
connectivity. with
engineers
18
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