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2020-07-16-sm-agenda-item-1-attachment-5-final-noosa-plan-2020-part-8-10-schedules-appendix
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Survey Technique Methods Minimum Duration
Council
SC6.4.9 Habitat Condition and Breeding Places Assessment
(1) The purpose of a fauna assessment is to assess and document the habitat values, including the presence of animal breeding
places, on site.
(2) The methodology for undertaking a vegetation community assessment is as follows:
(a) Desktop Assessment
(i) Prior to undertaking habitat assessments, the consultant must undertake a desktop assessment to research and
evaluate the potential for an animal breeding place to be present on a works site using a variety of resources
including but not limited to:
(A) WildNet records
(B) Museum records
(C) Atlas of Living Australia
(D) Essential habitat mapping
(E) Legislative requirements and listings (State and Federal Governments)
(F) Species Management Programs previously approved by the department
(b) Habitat Assessment and Breeding Places Assessment
(i) A field survey must be conducted to assess the habitats present, the listed threatened species known to occur or
potentially occurring within the locality, and the occurrence of specific breeding places or breeding habitat for these
species. For the purposes of this assessment, the definition of “breeding places” follows that provided in s332 of the
Nature Conservation (Wildlife Management) Regulation 2006. For species such as Koala and native frogs, who do
not use a habitual breeding place, the term ‘breeding habitat’ is used in lieu of ‘breeding place’.
(ii) Habitat features that are considered significant for assessing the presence of breeding places and/or habitation
value for native fauna, include but are not limited to:
(A) Presence of hollowbearing trees: These may be used by birds, reptiles or arboreal mammals for the purpose
or incubating or rearing offspring;
(B) Presence of bowers, nests, dreys: These structures are commonly used by birds or mammals to incubate or
rear offspring;
(C) Presence of caves, mounds, burrows, ground hollows and/or coarse woody debris: These structures are
commonly used by birds, mammals, reptiles or amphibians to incubate or rear offspring;
(D) Presence of permanent water, ephemeral ponding, depressions and/or, seasonally inundated areas:
Waterbodies may be used for breeding by aquatic species or amphibians, or that may provide intermittent
breeding habitat for opportunistic species;
(E) Presence of large trees: Large trees can be a dominant feature of native vegetation and are difficult to replace
once lost. Their influence for wideranging species can extend over a considerable distance from their
location.
(iii) Breeding places assessments are to be coordinated and led by a person experienced in conducting fauna surveys,
wildlife ecology and/or environmental management, including the identification of animal breeding places for EVNT,
special least concern or colonial breeding species.
(iv) A reasonable attempt must be made as part of any survey for animal breeding places to identify those that belong to
birds and mammals as a priority.
(v) Reptile breeding places are considered by DES to be impractical to identify in most circumstances. As a
consequence, surveying for them specifically is not necessary. Should the surveyors become aware of a specific
reptile breeding site on a property, prior to the survey, then the surveyor must make a reasonable attempt to find it
and identify the site on the survey.
(3) Outputs shall include:
(a) A Breeding Places Report must include:
(i) A list of all animal breeding places identified within the impact area, including conservation status.
(ii) A statement to justify the suitability and qualifications of the person undertaking the animal breeding place survey.
NOOSA PLAN 2020 Page 37 of 99
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