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1.
To determine survival rates of released birds.
2.
To determine cause of death.
3.
To determine rate of residency (% of released birds
that stay).
4.
To determine whether surviving birds breed successfully.
5.
To determine whether a population establishes in the
target area(s) under prescribed management regimes.
6.
To determine the dispersal patterns of any birds that
leave the target area.
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Objectives
1 & 2: To determine survival rates of released
birds and cause of death
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Priority
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Essential
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Performance
measure
|
Annual and
seasonal survivorship determined for 80% of released
birds and cause of death estimated for 50% of carcasses
retrieved.
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Field
methods
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·
Radio-tag with mortality transmitters and individually
colour-band all released birds as per 5.2.
·
Intensive one month post-release monitoring
involving daily roll calls to ascertain whether birds
are alive and to determine their approximate location.
If mortality is low (<20% of birds die) after four
weeks and mortality was clustered near release time,
reduce frequency of monitoring to twice weekly. However,
if mortality continues at a steady rate during the four
weeks, continue with monitoring every 1-2 days until
mortality rate declines.
·
Monitoring could be on the ground or from an
aircraft depending on the site characteristics and dispersal
patterns of released birds.
·
If mortality mode is activated, locate transmitter
and bird and examine scene and process carcass as per
5.5.
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Priority
|
Essential
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|
Performance
measure
|
Average
breeding success (fledglings produced per radio-tagged
female), and juvenile survival (n = 20 in two years)
determined following two years of release per site.
Flock counts might also provide an effective measure
of success.
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Field
methods
|
·
Monitor location of radio-tagged adults/released
birds.
·
Radio-tag 2-3 juveniles per brood.
·
Monitor adults and juveniles twice weekly as
per 5.2 – 5.6.
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Objective
5: To determine the dispersal patterns of any birds
that leave the target area
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|
Priority
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High – essential
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Performance
measure
|
75% of dispersed
birds relocated and further monitored.
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Field
methods
|
·
Monitor twice weekly as per 5.4 and 5.6.
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Annual
Reporting
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Report on
individual objectives as guided by relevant reporting
protocol in objectives 5.1-5.6 (project leader).
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Post-release monitoring
at these sites should always follow the procedures identified
in Section 6. Subsequent monitoring will depend on the questions
being asked, the situation and resources available.
“To
determine whether successful breeding occurs and to establish
inter-year trends in populations.”
Recommended monitoring
methods are:
1.
Annual or biannual dog surveys (Kapiti, Mana)
·
Carry out annual or biannual dog surveys to
identify individuals present.
·
Remove transmitters from released birds after
a year.
·
Metal band all new birds captured.
2. Colour-banding and annual or biannual dog surveys if needed
(Karori, Warrenheip and Tiritiri Matangi)
·
Colour-band released birds (note that Karori
may wish to colour-band only the more visible pairs).
·
Radio-transmitters removed one year after release,
or replaced, depending on experimental objectives and monitoring
capability (Section 6).
·
Provide roosts that allow for suitable observations
of colour-bands.
·
Carry out regular (weekly) observations for
banded birds at these roosts – unbanded birds indicate either
breeding on site or immigration.
·
Carry out regular breeding season observations
for broods.
·
Potential extras would be to dog survey for
unbanded birds annually (if evidence of breeding/unbanded
birds) and metal band or colour-band with reflective tape
(cohort probably adequate) depending on objectives; and carry
out telemetry as per intensive sites, but only if experimental
questions are important (Section 6), resources allow and weekly
monitoring is achievable.
3. Observations
of flocks and brood sizes (Russell
Peninsula)
·
Survey historic and potential flocking areas
in March as per Section 5.1.
·
Carry out at least two counts of each potential
flocking area every March following procedures in Section
5.1.
·
Maintain a schedule of sightings of pateke,
detailing date, time, location, observer, number of ducklings
and their size class.
·
Map each year’s distribution of sightings.
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Priority
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High
|
|
Objective
7.1
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To provide
relevant information to the predator controller on what
species of mammalian predator (cats, dogs, mustelids)
are present within management areas and need to be removed.
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|
Objective
7.2
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To measure
the relative abundance of mustelids, rats, harriers
and pukeko (all potential predators of pateke and other
species) seasonally and annually.
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Objective
7.3
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To measure
relative abundance of rabbits at Okiwi.
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Performance
measure
|
Mammalian
predators detected and information conveyed to trapper
immediately. Mustelids (Mimiwhangata), rats (Okiwi)
and pukeko (both sites) monitored at least quarterly
(pukeko monthly during peak breeding period, June-October),
harriers weekly during June-October at both sites.
Mimiwhangata mustelids and Okiwi rats indexed according
to DoC indexing protocols, and rabbits
by weekly road transects during winter-spring at Okiwi.
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Field
methods
|
·
Report mammalian predator sightings (and mustelid
index results) to trapper immediately and maintain database
of predator sightings (Appendix 6).
·
Carry out frequent predator-dog searches of
management areas, focussing on times of year when risks
have historically been greatest (September-December
and mid March-June) and following mortality events.
·
Identify and record rats caught as by-catch
in Mimiwhangata fenn traps, calculate monthly and seasonal
totals, compare inter-year capture rates for four seasons
for each species and total rats.
·
Carry out rat indexing at representative sites
at Okiwi at three month intervals following standard
protocols.
·
If non-treatment reference sites (no predator
control) exist in region/island, take the opportunity
to compare results,
·
Count pukeko in prescribed paddocks (Okiwi)
and from prescribed hilltops and other vantage points
at Mimiwhangata weekly in June-October.
·
Count harriers weekly along discrete transect
lines (Okiwi) and from prescribed vantage points (Mimiwhangata)
during June – October.
·
If resources allow, set up a series of tracking
tunnels to detect mustelids in the core of Mimiwhangata
as per recommendations of Ian McFadden and following
Craig Gillies draft protocol. Operate monthly during
high risk periods (Dec-March mustelid dispersal period
and at times when pateke are perceived to be at increased
risk).
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Annual
Reporting
|
·
Describe objectives, methods.
·
Graph indices of abundance of rats, harriers
and pukeko, predator-dog results and sightings of cats/dogs,
and compare with previous years.
·
Identify subsequent action taken and results,
e.g. whether predators subsequently removed from area,
or any links with pateke mortality.
(All project
leader.)
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Priority
|
Essential.
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|
Objective
9.1
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To evaluate
and refine overall pateke monitoring on an annual basis.
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Objective
9.2
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To advise
on the effectiveness of management of pateke and recommend
changes in management approach as appropriate.
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Objective
9.3
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To identify
gaps in knowledge and recommend means of filling them.
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|
Performance
Measures
|
Annual assessment
of monitoring and management programmes provided to
recovery group.
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Methods
|
Project
leaders and technical staff to evaluate effectiveness
of monitoring programmes, identify problems and develop
and implement appropriate refinements (SCO).
From monitoring
results, interpret the responses of pateke to specific
management changes accordingly (SCO).
With project
leaders and technical staff, identify key gaps in our
knowledge of pateke and their management (SCO).
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Research
opportunities
|
There are
clear needs for further research which are provisionally
prioritised below, but which could change when recent
research findings are available. Some of these needs
provide clear opportunities for students or other researchers
to focus on specific questions, but integrate with the
existing monitoring programmes.
·
Change in composition of flock sites related
to seasonal weather, breeding status/juveniles, bird
condition, etc (Priority 1).
·
Dispersal and habitat use of juveniles (Priority
1).
·
Breeding dispersion in relation to flock sites,
pest management areas, habitat quality, grazing regimes,
etc. (Priority 1).
·
Who are the predators of ducklings? Can we
develop a faster way of identifying key duckling predators
than the research by management approach (Priority 1
or 2).
·
Population modelling (Priority 1 in helping
to determine management targets).
·
Genetics and hybridisation (Priority 2).
·
Ecology and movements of predators (Priority
2 or 3).
·
Alternative means of collecting demographic
data, e.g. plumage observations and photography at flock
sites (Priority 1 or 2).
·
Weak-links for harnesses – is there a problem
with pateke and what can be done about it including
other options e.g. tail mounts? (Priority 3).
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Technical advice
was provided by Dave Agnew, Dave Barker, Tony Beauchamp, Sam
Ferreira, James Fraser, John Innes, Nigel Miller, Richard
Parrish, Ian Westbrooke and Murray Williams. Ralph Allen,
Margaret Honey and Willie Shaw (Wildland Consultants Ltd)
assisted with report production.
REFERENCES
Agnew D. 2001: Summary of Great Barrier Pateke/Brown Teal Programme.
Report to Brown Teal Recovery Group meeting, August 2001.
Barker D. 1998: Brown Teal on Okiwi Station, Aotea. Report 1: July 1997-June
1998. Unpublished report to Department of Conservation. 38
pages.
Barker D. 1999: Brown Teal on Okiwi Station, Aotea. Report 2: July 1998-June
1999. Unpublished report to Department of Conservation. 71
pages.
Barker D.; Williams M. 2000: Estimating productivity of Brown Teal at
Okiwi, Aotea 1999, and a re-appraisal of productivity measurement.
Field report to Auckland Conservancy, Department of Conservation
and to Brown Teal Recovery Workshop (December 2000). 10 pp.
Dumbell G.S. 1987: The ecology, behaviour and management of New
Zealand Brown Teal, or Pateke.
Unpublished PhD thesis, University
of Auckland, Auckland,
New Zealand.
Dumbell G.S. 2000: Brown Teal Captive Management Plan. Threatened Species
Occasional Publication No. 15. Department of Conservation
Fraser J. 2000: The Mimiwhangata Brown Teal management experiment: did
it work? Draft report to the Department of Conservation, Whangarei
Area Office.
Fletcher D.; MacKenzie D. 2002: Statistical review of the draft National
Pateke Monitoring Guidelines. Unpublished report.
Innes J.; Jansen P.; Baucke A. 2000: Audit of the Brown Teal recovery
program. Department of Conservation, unpublished report.
Moore S.J. 2002: Pateke (Brown Teal) monitoring, Kapiti and Mana Islands, 2001. Unpublished report to Department of Conservation, Kapiti Area
Office.
O’Connor S 2001: Pateke short-term recovery plan (WGNCR 29977). Unpublished
report, Department of Conservation, Wellington.
Parrish R.; Williams M. 2001: Decline of Brown Teal in Northland, New
Zealand 1988-99. Notornis 48: 131-136.
Williams M.; Barker D. 1995: A summary of Brown Teal research on Aotea:
September 1994, February 1995 and September 1995. Unpublished
report to Brown Teal Recovery Group.
Williams M. 2001: Productivity and survival within two declining populations
of Brown Teal (Anas chlorotis). Notornis 48:
187-195.
Williams M.; Dumbell G.S. 1996: Brown teal Anas chlorotis recovery
plan. Wellington,
Department of Internal Affairs.
Worthy T. H. 2002: The fossil distribution of Brown Teal (Anas chlorotis)
in New Zealand.
Unpublished report to Department of Conservation, Wellington
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