ZIP and COVID-19, May 2020 – a letter from our Chief Executive

ZIP and COVID-19, May 2020 – a letter from our Chief Executive

Kia ora,

I hope this finds you and your loved ones safe and well after what has been a strange and, at times, challenging few weeks.

With the recent easing of restrictions under COVID-19 Alert Level 2, I wanted to take this opportunity to provide another update on the status of the Zero Invasive Predators (ZIP) team and our programme of work.

During the Alert Level 4 lockdown period, all field work at the Perth River valley site was on hold, and only animal husbandry tasks (i.e. no trials) were carried out at Lincoln. All staff who were able to work from home did so, including our field team, who shared a house in Hokitika and were ironically a lot less socially isolated during this time than they are used to being!

On 28 April, the beginning of the Alert Level 3 period, the field team returned to work in the Perth River valley (a site re-entry that was particularly memorable for one of our rangers), and we resumed trials and the supply of products at our predator behaviour facility in Lincoln. We developed new safety procedures for both sites, to protect our people and manage any public health risk associated with returning to work. Where possible, the rest of our team continued to work from home during the Level 3 period, and many team members are continuing to do so through Level 2. We remain in regular contact by phone, email, video conferencing and the magic of social media.

Our network of lured trail cameras in the Perth River field site has revealed that a small number of rats survived the spot treatment operation that we carried out earlier this year, and are very likely to have begun to breed during our absence from the site. Given the speed with which rats can re-populate, removing these rats before their population can spread has become our most urgent priority in the Perth River valley. We are using a range of targeted ground-based methods, including traps and bait stations, to achieve this.

We have also begun work to remove the 3-5 possums that survived the predator removal operation, and to remove a small number of invading stoats. Both responses involve deploying ground-based methods around the locations where these animals have been detected on camera. We are pleased to report that, on Monday 18 May, our ranger Mike and his dog Pepper successfully removed one of the possums from the site!

We will continue to notify you as soon as possible about any significant developments that affect our programme of work. In the meantime, please don’t hesitate to contact us if required.

Wishing you all the very best, and thank you once again for your continued support.

Ngā mihi nui,

Al Bramley

Chief Executive, Zero Invasive Predators

An encounter with 27 kea in the Perth River valley, April 2020

An encounter with 27 kea in the Perth River valley, April 2020

The ZIP field team returned to work in the Perth River valley on Tuesday 28 April, shortly after the COVID Level Four restrictions were lifted. Our field ranger Mike and his possum detection dog Pepper spent their first night back in the field camping by the headwaters of the Barlow River, where they were tasked with tracking down a possum we had detected in our network of lured trail cameras.

The following morning they awoke at 5:00am to a tell-tale cacophony of shrieks and an ominous rustling. They dragged themselves outside, and were shocked to find their ultra-hardy canvas storage bags and dry bags chewed to ribbons, gear strewn about the campsite, and several juvenile kea engaged in a serious attempt to dismantle their tent.

It’s normal for our team to camp in single-person tents, with some gear stored outside the tent, packed in dry bags and thick canvas storage bags to protect it from weather and the odd curious kea. While there have been a few minor instances of kea interfering with gear at other locations in the Perth River valley, we have never experienced such a targeted, sustained attack at this particular campsite!

Some of the gear in question. Not pictured: an electronic rifle scope that will probably never be seen again!

While Pepper watched from a safe distance, shaking ‘like a fish’, Mike counted an incredible 27 birds at the tahr camp, and caught the encounter on video (see below). Then, man and dog gathered what was left of their field gear and made a hasty retreat to the nearest bivvy.

The large number of young kea seen during this encounter coincides with the end of the fledgling season (November to May), a time when all juveniles from the previous breeding season reach independence. Although Mike and Pepper may not have been smiling at the time, a close encounter with such a large flock of juveniles is a very positive sign, and we are delighted by the frequent kea sightings reported by all of our field rangers. Along with the results of our recent kea survey, we are seeing increasing evidence that the Perth River kea population is thriving as we work to protect the site against possums, rats and stoats.

A few of the guilty kea…

Kea survey in the Perth River valley, March 2020

Kea survey in the Perth River valley, March 2020

On Wednesday 18 March, ZIP worked with several members of the South Westland community to conduct a kea survey in and around the Perth River valley field site. The purpose of the survey was to provide additional information to help us more confidently estimate the effect of our 2019 predator removal operation on the local kea population.

Background

ZIP has been working in the Perth River valley since early 2018. At this site we are testing and refining an approach to completely remove possums, rats and stoats from large areas, and then prevent them from re-establishing, for the long-term, sustainable protection of native species such as kea.

When we began work in the Perth River valley, experienced kea catchers spent three days banding kea within the field site. During this work, they caught and banded 55 kea, and estimated a total population of 75-100 kea within the area.

In autumn/winter 2019, we carried out an initial predator removal in the 12,000 ha field site using a modified technique for applying aerial 1080. While we anticipated that the complete removal of predators would have significant long-term benefits for kea in the valley, we recognised the need to mitigate any potential risks to kea that this modified technique might present. In the months leading up to the predator removal operation, we worked with DOC and the Kea Conservation Trust to develop and deploy two new methods to protect kea during the operation (alongside a range of more standard risk mitigation measures that were already in place).

Prior to the operation, we exposed kea to non-toxic baits that mimicked the look and smell of toxic baits, containing the bird repellent anthraquinone. This bait was used to train kea to avoid cereal baits.

To attract kea to these aversion baits, we also placed tahr carcasses (repurposed from tahr control operations) at several sites above the altitudinal boundary of the operational area.

Our research confirmed that tahr carcasses are highly attractive to kea, and capable of drawing groups of kea to specific locations within the field site. So, in winter 2018, we field trialled the use of trail cameras lured with tahr carcasses to survey kea at several alpine locations within the site. The images gathered from this network of cameras suggested a similar population to the kea catchers’ estimate.

In late 2019, after we had completed the predator removal operation, we carried out another survey using camera traps lured with tahr carcasses, to help us understand the effect of the operation on the kea population. The numbers of kea seen on camera during this work were similar to those seen in winter 2018, suggesting that the initial impact of our predator removal operation on the kea population was likely to have been small.

The March 2020 survey

The March 2020 survey was carried out at eight locations (marked as blue dots on the map below) in and around the Perth River valley field site. Tahr carcasses were used to attract kea to each of the survey locations.

We were grateful to be supported on the day by Kaylyn and Marcus Pinney (Te Taho Deer Park/ New Zealand Deerstalkers Association), Ashley Cassin (Chair of the Glacier Country Tourism Group), Cliff Goodwin (Glacier Valley Eco Tours) and Su Sinclair (Project Support Manager, Predator Free 2050 Limited). Gus Gordon (Glacier Country Helicopters) helped us select the survey locations and place the tahr carcasses.

One of the eight alpine locations at which kea were surveyed (Joseph Arand)

At each of the survey locations, we worked with Kaylyn, Marcus, Ash, Cliff and Su to conduct five hourly kea counts, between 7:30am and 11:30am. Each time a kea was counted, we noted whether it was on the tahr carcass itself, or simply perched nearby. We also recorded any banded individuals we were able to identify, and synchronised the counts to minimise the chance of double counting birds.

A group of four kea photographed during the March 2020 kea survey (Briar Cook)

Over the course of the survey, between 25 and 39 kea were counted at the beginning of each hourly period (or an average of 30 per hour). This rate of sightings is similar to the rate at which kea were photographed by our trail cameras before the predator removal operation, and suggests that the number of kea now living in the valley is unlikely to have changed.

It was a great experience to head up on the kea observation trip alongside Cliff Goodwin (owner/operator Glacier Valley Eco Tours). We were in an amazing spot and observed a good population of kea on our hourly inspections. With multiple locations observed at the same time, it was interesting to see the large numbers of kea that were present at certain sites.
— Ashley Cassin, Franz Josef Glacier Hotpools
It was interesting to discuss the ZIP program with [Science and Technical Ranger] Briar, and the ambitious nature of their plans. Being on the ground we could appreciate the scale of the area and how well the team has done to get the possum numbers down to just 3 animals. We appreciated the opportunity to see what is happening and we look forward to seeing how the project goes in the coming years.
— Marcus and Kaylyn Pinney, Te Taho Deer Park/ New Zealand Deerstalkers Association

A juvenile kea spotted during the March 2020 kea survey (Marcus and Kaylyn Pinney)

Along with the many kea sightings our rangers enjoy while going about their work, helicopter pilot Gus Gordon’s recent estimate of 100-200 kea (based on the large numbers he has spotted while placing tahr for our survey and risk mitigation work), and the large collection of images captured by our trail cameras (including the one below), the results of this survey make us confident that there has been little change to this population.

A group of six juvenile kea caught on camera at a tahr carcass in August 2019

A group of six juvenile kea caught on camera at a tahr carcass in August 2019

The relatively large population of kea in the valley can likely be attributed in part to a long history of predator control in the area. DOC has carried out five aerial 1080 operations here since 1997, which will have given several generations of kea an opportunity to breed successfully. Another factor is that these kea have had access to an abundance of nutrient-rich food in the form of tahr carcasses left by trophy hunters and by DOC’s tahr control operations.

The continued strong population of kea also suggests that the combined use of aversion bait and tahr carcasses has been largely successful in mitigating risks to kea from ZIP’s predator removal operation.

Seeing a healthy population of kea in the Perth River valley a year after our predator removal operation is hugely rewarding. We expect this population will continue to flourish as we learn to maintain an area free from the impact of possums, rats and stoats.

The work ZIP’s doing in the Perth River valley is really necessary to help protect kea. These birds are intelligent, so we need to train them not to eat the baits while still getting rid of the rats, stoats and possums. ZIP has put a lot of work and thought into reducing risks to kea from 1080, and it’s been bloody awesome to see so many kea in the valley a year after their operation.
— Gus Gordon, Glacier Country Helicopters

Zero Invasive Predators (ZIP) and COVID-19 – a letter from our Chief Executive

Zero Invasive Predators (ZIP) and COVID-19 – a letter from our Chief Executive

Kia ora, 

I hope this finds you and your loved ones safe and adjusting to our collective new 'normal'.

Now that we have settled into our new work environments for at least the next four weeks, I wanted to let you know the status of the Zero Invasive Predators (ZIP) team and our programme of work. 

All of the ZIP team members are now working from either their usual residences in Wellington, Christchurch and Hokitika, or staying with family members in other parts of the country. We are all in regular video, internet and/or phone contact with one another.

Almost all biosecurity and conservation work has ceased on public conservation land (with the exception of some offshore islands) and, consequently, our programme of work in the Perth River Valley is on hold. Likewise, trials at our Lincoln predator behaviour facility are also on hold, although we are continuing to look after the resident possums, rats and stoats. 

While our field work and trials are on hold, we are well placed to stay busy and productive during this period. Disruptions to the planned programme of work are not unusual in our context, and the ZIP team is well set up to cope with change. We also know that each disruption also represents an opportunity to review and refine our work programme, and perhaps to even catch up on some overdue tasks. You may remember that our predator removal operation in the Perth River Valley was scheduled to be carried out in 2018, but delayed until the following year by weather conditions and heavy snow. We took this opportunity to develop and test new techniques to mitigate risks to kea, and then deployed these alongside the operation when it was eventually carried out in 2019. Another year on, and we are pleased to see a healthy population of kea living and breeding within the field site.

Over the next few weeks our team will take this current opportunity to complete a range of tasks including writing up and publishing research results, analysing the immense database of images acquired through our network of trail cameras, ensuring we are ready to continue developing our new predator detection camera when supply chains re-open, checking and maintaining our field supplies, reviewing and refining our programme of work, and refining and developing our internal administrative systems. For those of you running landscape-scale predator free projects, we are just a phone call away (although we are currently unable to supply products).

We will continue to notify you as soon as possible about any significant developments that affect our programme of work, and for some of you, seek your continued input into planning the work and your advice on how we can deliver it. Please don’t hesitate to contact us if required.

In the meantime, I’d like to wish you and your families all the best over the coming weeks. 

Al Bramley
Chief Executive, Zero Invasive Predators

Update on Perth River valley work programme – response to isolated rat breeding

Update on Perth River valley work programme – response to isolated rat breeding

Tuesday 7 January 2020

In late July 2019, Zero Invasive Predators (ZIP) completed a predator removal operation in the Perth River valley, South Westland. This operation is part of a research and development project that aims to test and refine the ‘Remove and Protect’ approach for the complete removal of possums, rats and stoats from large mainland areas, and subsequent protection of these areas against predator re-establishment. The research area covers 12,000 hectares.

Since the operation, we have been using our network of 147 trail cameras paired with MotoLure automated lure dispensers and approximately 3,000 chew cards lured with peanut butter to detect any remaining possums, rats or stoats.

By mid-November, just 3 possums and 5 rats had been detected within the area – and no stoats. We established a small network of traps and extra cameras at the site of each rat detection, and caught 4 rats.

In mid-December 2019 we discovered evidence that localised rat breeding had occurred after the predator removal operation, across a small ‘footprint’ of approximately 50 hectares. We’ve always anticipated that the Remove and Protect approach will require a range of techniques to respond to animals that survive a predator removal operation or reinvade an otherwise predator-free area. Given the nature of the terrain, the only feasible response to remove this emerging population and prevent rats from re-establishing in the valley is to carry out a small-scale aerial ‘spot treatment’.

Consequently, today we applied non-toxic cereal prefeed bait (at a rate of 1kg/ha) across the 50 hectare footprint and a surrounding buffer zone. When the weather conditions next allow, we propose to apply a single application of 1080 bait (at a rate of 2kg/ha) over the emerging rat population footprint.

The location where bait is applied will be displayed on the DOC Pesticide Summaries website, and on a map accompanying the signage within the project area itself.

 

Image credit: Ngā Manu Nature Images, 2007

Video update: We are making great progress developing the 'Remove and Protect' approach in the Perth River valley

Video update: We are making great progress developing the 'Remove and Protect' approach in the Perth River valley

18 December 2019

Since early 2018, Zero Invasive Predators (ZIP) has been carrying out a trial which aims to completely remove possums, rats, and potentially stoats from 12,000 hectares of rugged back-country in the Perth River valley, South Westland – and to then permanently prevent these predators from re-establishing.

The Perth River predator removal operation was completed on 23rd July 2019. Since this time the ZIP field team has been carrying out an intensive detection effort within the valley, so that any remaining possums, rats or stoats can be removed before they begin to re-populate the area. Four months after the operation, very few possums and rats, and no stoats, had been detected in the valley – an extraordinary achievement.

This programme of work is made possible by the generous support of NEXT Foundation, the Department of Conservation, and Predator Free 2050 Limited.

Taonga species in the Perth River valley, South Westland

Taonga species in the Perth River valley, South Westland

While our field team is working in the Perth River valley they have the great pleasure of regularly seeing kea, pīwauwau (rock wren) and whio. This update shares videos that one of our rangers has taken of these special birds.

A group of up to 10 kea were caught on film in the Upper Barlow area in May, after the first phase of the predator removal operation.

This whio was spotted alongside the Lower Barlow River, approximately one month after the completion of the predator removal operation.

Several pīwauwau (rock wren) were also filmed in the Prospectors Creek area during monitoring in April this year.

So far, we have not seen any possums, rats or stoats in the area since the predator removal operation was completed. We expect that this means kea, whio and pīwauwau will all have a very good upcoming breeding season.

Update on Perth River Valley work programme – predator removal operation completed

Update on Perth River Valley work programme – predator removal operation completed

On Tuesday 23rd July, Zero Invasive Predators (ZIP) completed the second phase of a predator removal operation in the Perth River valley, South Westland.

We are pleased to report that all 12 radio-tagged kea[1] and all 15 radio-tagged tahr that were present during the second phase of the operation are alive.

Since the operation, sufficient rain has fallen in the area to remove any remaining toxicity from baits on the ground. Visual surveys of whio (blue duck) and pīwauwau (rock wren) will be carried out during the coming months, as weather and snow conditions allow.

The first phase of the operation was completed in April, and resulted in a significant knock-down of possums, rats and stoats. Our team has now begun to carry out intensive detection in the area, to determine whether the second phase of the operation succeeded in removing the small number of individual possums and rats that survived the first phase, and to confirm the impact of the operation on stoats. This work will continue for several months.

This operation was carried out with the support of the Department of Conservation, NEXT Foundation and Predator Free 2050 Limited, and is part of a wider programme of research and development led by ZIP in a 12,000 ha area within the Perth River valley. The work aims to develop an approach to completely remove possums, and potentially rats, and to then enable long-term protection of the area, without the ongoing use of aerial toxins at landscape scales.

The Perth River valley is bounded by the Perth, Bettison and Barlow Rivers, and capped by Kā Tiritiri o te Moana – the Southern Alps. We have reinforced these natural boundaries to invasion by possums and rats with a network of traps and devices that automatically alert our team (via satellite) when predators are detected. We may further reinforce the barriers through the targeted use of toxins.

We anticipate that the permanent removal of possums and, potentially, rats, along with the work to control stoats to very low numbers, will help restore the mauri of the Perth River valley and safeguard its many natural treasures. Most importantly, if we successfully develop an approach to completely remove introduced predators and prevent them from re-establishing, then this approach could be applied to protect native species elsewhere in South Westland.

For more information about this programme of work, please contact us at info@zip.org.nz.

 

[1] This figure includes the 11 radio-tagged kea that were present during the first phase of the operation, along with another kea from the radio-tagged population that returned to the research area prior to the second phase.

An Insight into ZIP

An Insight into ZIP

This piece was originally published in the Greymouth Star, on Friday 14 June 2019.

Over the past few weeks some of the activities of the research and development organisation Zero Invasive Predators Ltd (ZIP) have featured in articles and letters to the editor in the Greymouth Star and Hokitika Guardian. Here, ZIP Chief Executive Al Bramley provides an insight into the organisation and its work to protect our natural environment by completely removing introduced predators.

A member of the ZIP team in the remote and spectacular Perth River valley, where ZIP is developing new methods to completely remove introduced predators and protect the natural environment.

A member of the ZIP team in the remote and spectacular Perth River valley, where ZIP is developing new methods to completely remove introduced predators and protect the natural environment.

ZIP was established by the Department of Conservation and the philanthropic NEXT Foundation in 2015. Our mission is to develop tools and techniques that completely remove possums, rats and stoats from mainland New Zealand and prevent them from re-establishing. What we learn along the way will help communities throughout New Zealand restore native biodiversity and reduce the economic impacts of these introduced predators.

Some commentators have observed that this is huge task – and we agree! But, by building on what has been learned from the past efforts of others, and drawing on the advice and skills of a wide range of people, along with new advances in technology, we are making progress.

We’re a small team of field rangers, engineers, scientists and support staff. Our team members range in age from the early 20s to the late 50s, and live in Wellington, the Marlborough Sounds, Christchurch and the West Coast. Many of us have worked closely with native wildlife, including kiwi, kakapo, takahe and kea, and have experienced first-hand the devastating impact that introduced predators have on these, and other, treasured native species. What gets us out of bed in the morning is the opportunity we now have to help bring an end to the destruction of our wild ecosystems at the teeth and claws of possums, rats and stoats. We want to leave our natural environment in a better state for our children.

Like many people, we also would like to see New Zealand reach a stage where it is no longer necessary to kill introduced predators on an ongoing basis, in order to protect our environment.

Our work is funded by our founders and other supporters – it’s a mix of public funding and private contributions by generous New Zealanders who wish to leave a legacy of environmental excellence for all New Zealanders. The funding is pooled and used to support a range of projects, at the Perth River valley site and elsewhere.

ZIP is a registered charity, with no commercial or profit motive. Any revenue we generate is required to be reinvested back into our programme of work – it’s not paid as a dividend to DOC or the NEXT Foundation (or to me or to my team). Our charitable status also means that we are able to make the products we develop – such as our possum trap system and automated lure dispenser – as cheap as possible, because we do not have to recoup the costs of developing them.

We try to meet with people who have a significant interest in our work, to seek their advice and share results. In the case of the Perth River valley work, we’ve benefitted from ongoing conversations with Te Rūnanga o Makaawhio, Te Rūnanga o Ngai Tahu, Westland Regional Council, West Coast District Council, West Coast Conservation Board, New Zealand Deerstalkers Association, Game Animal Council, Federated Mountain Clubs, Forest and Bird, Development West Coast, and Federated Farmers.

We also try to provide regular updates and findings on our website about our activities and what we’ve learned, and to respond promptly to inquiries (although admittedly not as promptly as we’d like to, at times!)

I also want to acknowledge the concerns that some people have about some of the research and development projects we are undertaking in the Perth River valley. This article is not the place to address those concerns in detail.

However, some readers might be interested to know that if we are successful in developing cost-effective tools and techniques to completely remove possums, rats and stoats from the Perth River valley, and can prevent these predators from re-establishing, then it will not be necessary to continue to use aerial 1080 there at the landscape scale. I suspect such a result that would be welcomed by many people. Importantly, it would mean that the unique wildlife of the Perth River valley will have been maintained and restored, for West Coasters and visitors to appreciate and enjoy.

Of course, the nature of research and development means that we cannot guarantee this result. But, with the support of others, we’re giving it our best shot – and we will continue to share what we are learning as the work progresses.

Update on Perth River Valley Work Programme – 7 June 2019

Update on Perth River Valley Work Programme – 7 June 2019

Zero Invasive Predators (ZIP) has recently completed the first phase of a predator removal operation in the Perth River valley (South Westland).

This operation is part of a wider programme of research and development that seeks to develop cost-effective tools and techniques to completely remove possums and, potentially, rats, from large mainland areas, and prevent these predators from re-establishing. If this work is successful, it will have significant benefits for the many native species that live in the Perth River valley, and will mean that it is no longer necessary to use landscape-scale aerial 1080 to control predators in the valley.

Detecting possums, rats and stoats after the first phase of the operation

Our network of 142 lured trail cameras has enabled us to keep an eye on predator abundance in the operational area for several months. Before the first phase of the operation, 98% of cameras detected a possum; 65% detected a rat; and 36% detected a stoat. These detections represent an estimated starting population of 8,000-20,000 possums; 3,500-9,000 rats; and 20-40 stoats across the Perth River valley research area.

In the month since we completed the first phase of the operation, only 7 cameras have detected a possum; 1 has detected a rat; and 9 have detected a stoat. Based on these detections, our team has begun modelling the remaining population of possums, rats and stoats. Our initial estimates range from 13-35 possums; 5-15 rats; and 1-3 stoats across the research area. Our most recent camera data indicates have all three stoats have since died from secondary poisoning.

This is an excellent result for an aerial 1080 operation, which we think reflects (i) the benefits of two rounds of prefeeding, (ii) the careful attention to applying a consistent coverage of bait across the entire operational area, and (iii) the ideal weather conditions, with toxic baiting followed by 6 dry nights.

We are also continuing to search for any predators that survived the first phase of the operation, and we are using the results to help ensure the predator removal is successful. To do this, we’ll use the same network of 142 cameras, reinforced with a much larger number of chew cards.

Kea in the Perth River valley

Toxicology testing has confirmed that two of the 13 radio-tagged kea in the Perth River valley died after eating 1080 bait during the first phase of the predator removal operation.

The other 11 radio-tagged kea are all alive. We are also pleased to report that none of the adult female kea in the radio-tagged population died during the operation. This is an important outcome for kea in the area, because adult female kea are most vulnerable to predation, given their ground-nesting habits and extended nesting cycle[1].

Our team has frequently sighted kea in the Perth River valley since the first phase of the operation was carried out, both in person and via camera footage from our detection network (including the cheeky trio below).

IMG_2510.JPG

We anticipate that the removal of possums and rats, and the work to control stoats to very low numbers, will have significant benefits not only for kea, but for many of the treasured native species that live in the Perth River valley, including rock wren, whio and rata.

For more information, please email us at info@zip.org.nz.

[1] Kemp JR, Mosen C, Elliott GP, Hunter CM. (2018). The effects of aerial poisoning for pest mammal control on the productivity of the kea (Nestor notabilis). New Zealand Journal of Ecology 42.

Update on Perth River Valley Predator Removal Operation – Phase One Completed

Update on Perth River Valley Predator Removal Operation – Phase One Completed

On Sunday 14 April, Zero Invasive Predators (ZIP) completed the first phase of a predator removal operation that forms part of a wider research and development work programme in the 12,000 ha Perth River valley in South Westland.  This is a significant milestone for the first large-scale trial of a promising technique for completely removing possums (and potentially rats) from large areas of rugged back-country. The technique, which has been successful in smaller-scale trials, has two phases, each of which comprises two applications of non-toxic “prefeed” bait and one of toxic bait containing 1080.

The complete and permanent removal of possums and, potentially, of rats (along with the sustained control of stoats) is expected to have significant benefits for many of the treasured native species that live in the Perth River valley, including kea, rock wren, rata, and whio. The healthy kea population in the valley is believed to be the result of the history of predator control in this area, which includes multiple 1080 predator control operations.

If successful, this research and development programme will demonstrate techniques that can be used to completely remove predators from large, remote, mainland areas – bringing us one small step closer to achieving the goal of a predator-free New Zealand.

Heavy rain fell in the valley over the past weekend, which is sufficient to start breaking down the baits and reduce their toxicity to low levels.

We will begin intensive searching for any surviving predators after the second (and final) phase of the predator removal operation is completed (in June, depending on the weather).

Kea and tahr were radio tagged in 2018, in order to monitor them through both phases of the predator removal operation. These animals are monitored using the Sky Ranger system, which consists of a radio receiver flown in a light plane to collect data from the radio transmitters.

On Saturday 13 April, during the initial stages of toxic baiting, we determined that 13 radio-tagged kea, and 14 radio-tagged tahr, were present in the operational area. Further rounds of Sky Ranger monitoring were carried out, on Tuesday 16, Thursday 18, and Monday 22 April.

All 14 tahr were found alive in the operational area during each round of post-toxin monitoring.

11 of the 13 kea were found alive in the operational area during the monitoring period. Two radio tags were found to have switched to ‘static’ mode on Tuesday 16 April, and on Friday 19 April a ranger recovered the radio tags and confirmed that the kea wearing them had died. The kea, one young female and one young male, have been sent to Wildbase at Massey University for an independent toxicology assessment, to confirm the cause of death.

It is well-known that the use of aerial 1080 poses a potential risk to kea when used in close proximity to sites where kea scrounge food from humans, such as occurs around Franz Josef glacier. With the assistance of kea experts at the Department of Conservation and Kea Conservation Trust, we undertook several measures to minimise this potential risk, including two new approaches (namely, using repellent bait to ‘train’ kea not to eat the toxin, and providing tahr carcasses to attract kea away from the operational area).

While two of the birds have died, 11 of the 13 radio-tagged birds are alive. This is particularly pleasing given that the increased number of prefeed applications and higher quantity of toxic bait used in the ZIP technique could pose an elevated risk to kea compared to a standard 1080 operation.  The results indicate to us that the measures we implemented have helped to minimise the risk to kea, but we have yet to complete the work that will help to confirm whether or not this is the case.

Interestingly, one of the two kea was known to have high levels of lead in its blood, which experts have suggested may increase a bird’s susceptibility to 1080 poisoning. The other bird had not yet been tested for lead (but this will be done as part of the toxicology assessment).

For the ZIP team, the loss of these individual birds is disappointing.  We spend a lot of time in the valley, often in the company of kea, as well as reviewing hundreds of hours of camera footage of them, so we are particularly fond of these birds and their antics.  In that regard, it’s reassuring to know that the results of monitoring kea in other aerial predator control operations has shown that removing predators from the Perth River valley will result in improved breeding success for the kea population.    

This predator removal operation is part of a wider programme of research and development that is intended to also prevent possums, and potentially rats, from re-invading the area so kea and other native species will continue to enjoy improved breeding success. DOC has confirmed that it will maintain the intensive stoat trapping network established by ZIP as part of the wider programme of work in the long term (to secure conservation outcomes). 

We’re going to continue to do all we can to refine the new methods to completely remove introduced predators across large areas of the New Zealand mainland, and to prevent them from re-establishing there, in order to help reverse the decline of kea and other native species.

 

For more information, please email us at info@zip.org.nz.

Update on Perth River Valley Work Programme - Kea Monitoring

Update on Perth River Valley Work Programme - Kea Monitoring

April 11th, 2019

Zero Invasive Predators is conducting a trial predator removal operation in the Perth River valley in South Westland, which aims to remove all possums, and potentially rats, from 12,000 hectares of rugged back country.

If successful, this trial will provide important information about how 1080 can be used to completely remove predators from a large mainland area.

The Perth River valley is a mountainous area that contains a population of 75-100 kea. Predator removal operations that use 1080 are known to benefit kea populations, but these operations can kill individual kea if they eat toxic bait. With advice from kea experts at the Department of Conservation and the Kea Conservation Trust, ZIP has implemented measures to mitigate the potential risk to kea from the operation, including applying non-toxic cereal baits containing a bird repellent prior to the operation to ‘train’ kea to avoid baits, and distributing a small number of tahr carcasses above the operational area, to attract kea away from toxic baits.

We are also monitoring kea survivorship before, during and after the operation.

Between 12 February and 9 March 2018, 29 kea were fitted with transmitters to monitor their survivorship through the planned 2018 aerial operation. This included 19 adults (12 female and 7 male), and 10 juveniles. In June 2018, one additional adult female kea was fitted with a transmitter, bringing the sample up to 30.

A kea is gently (but securely!) held by a ranger while being fitted with a radio transmitter, Perth River valley March 2018.

The transmitters are fixed to kea in a way that is designed to be relatively secure, while allowing them to move freely and behave naturally.

Monitoring is carried out using the Sky Ranger system, whereby a light aircraft fitted with radio receivers flies over the area and records the location and status of each transmitter.

The results of all of the Sky Ranger monitoring we have completed to date are shown in the table below.

The most recent Sky Ranger monitoring has determined that 13 of the 30 kea are still in the Perth River valley. Seven kea are in undetectable locations (either outside the area or in a location where the transmitter is unable to communicate with the Sky Ranger system), and ten of the remaining transmitters are now in ‘static mode’, indicating that either they have fallen off, or the kea wearing them have died.

Interestingly, two of the kea whose transmitters are in static mode have since been seen on camera, identifiable by their leg bands (pictured below, with leg bands circled in orange – click on the images to enlarge). This confirms that in at least two cases, the static signal represents a dropped transmitter.

One more Sky Ranger flight will be made on the day that toxic bait is applied in the Perth River valley, to confirm the number of kea in the operational area at that time.

Results of kea monitoring in the Perth River valley, May 2018-April 2019. Click on the table to enlarge.

Most of the kea in the Perth River valley have been wearing transmitters for over a year.

They are wild birds, and so we did not expect that all of them would remain in the valley. Other kea monitoring projects have witnessed a similar ratio of birds leaving the area or dropping their transmitters.

We will continue to monitor kea in the valley throughout the predator removal operation, and then through the following breeding season.

In the longer term, we expect that mark-recapture analysis of camera footage of the 55 kea in the valley fitted with leg bands will enable us to build a fuller picture of the outcome for kea in the Perth River valley.

We will continue to report the results of our research on our website.

Update on Perth River Valley Work Programme - February 2019

Update on Perth River Valley Work Programme - February 2019

We are looking forward to progressing our research and development programme of work in the Perth River valley, South Westland, after receiving permission from the Department of Conservation on Monday 18 February to undertake a predator removal operation that seeks to completely remove possums and, potentially, rats, from approximately 12,000 hectares of rugged back-country.

This is the same operation that we had originally planned to carry out during winter 2018, that we were forced to delay as a result of poor weather.

The ZIP team is pleased to be granted this opportunity to continue our work to develop the tools and knowledge required to completely remove possums, rats and stoats from the New Zealand mainland.

With the support of DOC, we will continue to engage with Te Runanga o Makaawhio, Te Runanga o Ngai Tahu, local people and recreational users of the valley (particularly hunters, climbers and trampers) to update them about the work, and seek their advice and feedback. The high level of interest and support for the work – and anticipation of the results – are very encouraging.

Predator removal operations that use 1080 are known to benefit kea populations, but these operations can kill individual kea if they choose to eat toxic bait. Based on the results of trials that ZIP has undertaken over the past 6 months, two measures will be implemented from late February 2019 to minimise this potential risk:

  • Apply non-toxic bait containing a bird repellent because our trials demonstrated that after experiencing the ill effects of consuming bait containing the repellent, kea quickly learn to avoid all cereal baits (even those that do not contain the repellent).

  • Provide tahr carcasses as an alternative food source and to attract kea to sites where non-toxic baits containing bird repellent will be provided. Our trials demonstrated that even a single carcass is capable of drawing sizeable groups of kea to a site – and that a tahr carcass typically lasts no longer than 7 days before being completely stripped of meat by kea!

Kea, whio and rock wren – all nationally threatened species - will be monitored through the operation.

ZIP is continuing to support the Game Animal Council, who are leading a project in association with New Zealand Deerstalkers Association, Professional Hunting Guides Association, and DOC, to assess whether the operation has an impact on tahr.

Following the operation, ZIP aims to demonstrate that the area can be maintained as a predator-free site, by preventing re-establishment using a network of detection devices and traps and, if necessary, the targeted use of toxic bait.

We will continue to provide regular updates about and descriptions of the findings from this programme of work on our website.

This programme of research and development is supported by the NEXT Foundation, Department of Conservation (DOC) and Predator Free 2050 Limited.

Perth River Valley Work Programme - Information Sheet (Updated January 2019)

Perth River Valley Work Programme - Information Sheet (Updated January 2019)

This information sheet is also available as a printable PDF. Click here to download a copy.

A programme of work is underway in a 12,000 hectare block within the Perth Valley (South Westland) to test and refine an approach to completely remove possums from large areas, and prevent them from re-establishing. The work will also seek to develop this predator management approach for ship rats and stoats. If successful, the approach will have significant beneficial outcomes for native plants and animals.

It could also reduce the need for the repeated use of landscape-scale aerial 1080 to control these predators here and elsewhere in New Zealand, and help pave the way for a predator-free New Zealand.

This work is a collaboration between Zero Invasive Predators Ltd (ZIP), the Department of Conservation (DOC), and Predator Free 2050 Ltd.

The indicative boundaries of the research area are shown on the map below.

Click here to download a copy.

The approach being developed has three main parts:

  1. Reinforcing natural barriers to the movement of predators into the block (e.g. rivers, alpine tops) with a network of traps.

  2. Completely removing predators within the block. This approach uses a more rigorous method of applying aerial 1080 than standard operations. The operation was originally scheduled to be carried out during winter 2018, but was delayed as a result of unfavourable weather conditions. We now propose to begin the operation in March 2019 (subject to receiving approval from DOC and the Medical Officer of Health).

  3. Detecting predators that either survive the 1080 treatment or reinvade the block from beyond its boundaries, and removing them before they can establish a population.

The work programme is evident through the presence of:

  1. ZIP field staff. Staff are regularly flown by helicopter to and around the site.

  2. traps, as well as detection devices such as chew cards and motion-sensor cameras.

  3. satellite communication facilities at Scone Hut, some temporary access routes, and three temporary bivvies (for ZIP and DOC staff).

  4. a predator gate on the swing-bridge across the Perth River near Scone Hut.

Please do not interfere with the equipment or any trapped animals because doing so will compromise the results of the research.

Kea in research area (Chad Cottle)

Kea in research area (Chad Cottle)

Rata in flower at research area (Devon McLean)

Rata in flower at research area (Devon McLean)

Possum eating bird egg (Nga Manu Images)

Possum eating bird egg
(Nga Manu Images)

ZIP and DOC staff are continuing to meet with Te Rūnanga o Makaawhio, Te Rūnanga o Ngāi Tahu, local people and recreational users of the valley (particularly climbers, trampers and hunters) to identify any impacts of the research programme, and options to reduce the impacts.

An estimated 75-100 kea are present in the research area. Although 1080 has been shown at other sites to benefit kea populations, individual birds have been known to die as a result of 1080 poisoning. Consequently, the work programme includes a range of measures to minimise potential impacts of the removal operation on kea, including:

  • applying non-toxic cereal baits containing a repellent prior to the operation to ‘train’ kea to avoid baits; and

  • distributing a small number of tahr carcasses above the operational area, as a more attractive, preferred, food source.

We have also fitted bands and radio-transmitters to kea, to monitor the impact of applying aerial 1080 on their mortality and breeding success. We are also monitoring the impacts, if any, of the operation on whio, rock wren, and tahr (the latter in collaboration with the Game Animal Council and New Zealand Deerstalkers Association).

Possums are the initial focus of this work because:

  • they are known to prey on native bird species such as kereru and kea and their eggs, as well as invertebrates such as wētā;

  • they are the major cause of the decline of trees such as kāmahi and rātā; and

  • the results of similar research at smaller sites suggest it is likely that the approach described will be successful.

The Perth Valley was selected for this research because:

  • ZIP already had existing working relationships with local DOC staff;

  • the rivers and streams and alpine tops are expected to be strong natural barriers;

  • the area contains valued biodiversity; and

  • the control area is relatively accessible (by helicopter) from a road end.

To learn more about this project, please email us at info@zip.org.nz, or call ZIP’s Operations Director, Duncan Kay, on 021 069 0167.

Update on Perth River Valley Work Programme – November 2018

Update on Perth River Valley Work Programme – November 2018

In August this year we reported that the aerial predator removal phase of our programme of work in the Perth River valley had been delayed, because weather and snow conditions (experienced and forecast) had reduced our ability to fully implement the ‘1080 to Zero’ method to completely remove possums (and potentially rats). The aerial operation was originally scheduled to be carried out during winter 2018, but we now intend to carry out this work from March 2019.

The decision to delay  this operation provided us with an opportunity to continue to develop and build confidence in strategies to (i) minimise potential risks to kea from the removal operation, and (ii) completely remove possums and rats, and prevent them re-establishing in the area.

Reducing risks to kea from the aerial predator removal operation

During the last two months we have been carrying out trials to assess the effectiveness of two measures to reduce the potential risk to kea from a ‘1080 to Zero’ operation.

The use of tahr carcasses as an alternative food source or ‘distraction’ from baits

In late June we began a trial to quantify the extent to which providing a small number of tahr carcasses as an alternative food source or ‘distraction’ could reduce consumption of toxic baits by kea. The carcasses of 21 tahr (shot with a high powered rifle) were initially placed at approximately 1km intervals along the upper boundary of the 1080 to Zero treatment zone, in order to ‘lure’ kea away from baits. Each carcass was placed as high in the alpine zone as snow and weather conditions would allow. Over subsequent weeks, we replaced any heavily scavenged carcasses to maintain their availability to kea as a food source.

Kea activity at each tahr carcass was monitored using trail cameras. These camera observations during the last four months have confirmed that the carcasses are highly attractive to kea, with 56% of the banded kea population within the research area (i.e. 31 out of 55 banded birds) appearing on camera at tahr sites. Based on a mark-recapture analysis, we estimate the population of kea visiting these tahr sites during this period to be 53 birds (42-79 birds, 95% C.I.).

Four kea feeding at a tahr site, including one of the birds in our banded population (second from left) and one from our radio-monitored population (second from right)

Four kea feeding at a tahr site, including one of the birds in our banded population (second from left) and one from our radio-monitored population (second from right)

A minor scuffle between two kea at a tahr site

A minor scuffle between two kea at a tahr site

Six kea feeding at a tahr site

Six kea feeding at a tahr site

An additional small-scale trial, to be carried out from November 2018, will involve placing tahr in known kea locations (within the research area) with and without non-toxic prefeed baits (which do not contain repellent), and monitoring kea behaviour using trail cameras.

If these trials continue to show sufficient promise, we intend to place a small number of tahr carcasses outside the 1080 to Zero treatment zone, but still within the research area, to lure kea well away from toxic baits during the aerial predator removal operation.

The use of repellents to discourage kea from eating baits

The objective of this work is to quantify whether repellent laced bait could discourage kea from eating bait and, if so, devise a strategy to use repellents when the aerial predator removal operation is carried out.

Beginning in July, we applied non-toxic prefeed bait containing a repellent, anthraquinone, along a narrow section of the alpine boundary of the research area. We are currently analysing camera footage of kea behaviour, in order to understand whether the baits are having a repellent effect (i.e. if individual marked birds reduce their interaction with the baits, this would indicate that the repellent is working).

We are also working with a bait manufacturer to produce non-toxic baits containing anthraquinone at a range of concentrations, for trials with captive kea at Willowbank Wildlife Park. These trials are intended to determine the optimal concentration of anthraquinone required to guarantee that the birds experience a short-term feeling of illness, and learn to associate this with the baits. These trials are expected to begin in early November.

Assessing the effectiveness of rivers as natural barriers to possums, rats and stoats

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In April this year we began a trial to determine the likely rate of invasion by rats across the river boundary, using a 3.2km long section of the Perth River as the trial site.

We established a network of 128 ZIP automated lure dispensers at 25m intervals along the true left side of the river, lured with mayonnaise that contains the bio-marker rhodamine B. To confirm uptake of the biomarker within the resident population, we undertook two rounds of trapping, each over multiple nights. The results indicated that 82% and then 90% of the trapped rats had ingested the bio-marker. Based on these results, it is very likely that we will be able to identify any rats that do manage to cross the river. We are also pleased to note that the mayonnaise, a new lure we are testing, appears to be both attractive and palatable to rats, possums and stoats.

To date 75 rats have been trapped on the true right side of the river, none of which have shown signs of rhodamine B, which typically shows up as a glowing ‘band’ in whiskers when observed under a fluorescence microscope.

We are now planning further trials in the Perth River research area to determine the rate of rat and possum invasion across different sections of the ‘river barrier’, particularly in summer conditions or where the rivers are braided, shallow, or slow-moving.

These trials will help us to design the layout of traps and devices required to reinforce the river barrier in a range of conditions.

Learning more about what we’re up against

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Elevation of possums and rats

In March and April this year we carried out monitoring to assess the relative abundance of possums and rats in the Perth River research area.

Analysis of the results of this monitoring also provided us with some insights into how high into the alpine zone these species are present. This information is helping to inform the baiting strategy for the upcoming 1080 to Zero operation in the Perth Valley, and the extent of the detection network required to detect survivors and invaders.

We established a total of 12 monitoring lines throughout the 7,500ha treatment area, each 500m in length and positioned evenly across different vegetation types and elevations, between 290 and 1,600m. Lines were widely spaced, to ensure individual animals were unlikely to encounter devices on multiple lines. Motion-sensing cameras were deployed at 100m intervals along each line, for a total of 7 days.

The camera footage gathered during this trial showed us that possums are present above 1300m (i.e. in heavy snow) while rats have not yet been seen above 1100m.

We intend to repeat this monitoring in late summer 2018, prior to the aerial removal operation, to determine seasonal variations in the population and the distribution of possums and rats.

Developing a lean detection network for stoats

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Stoat 3.JPG

A network of 124 trail cameras were also installed throughout the research area over winter, at a density of 1 camera approximately every 35 hectares – we refer to this as a ‘lean network’. The camera sites are lured with mayonnaise, delivered using the ZIP automated lure dispenser.

Approximately one quarter of the camera sites have seen stoats. Half of the sightings occurred within the first 7 days of deployment. Approximately one-third of these cameras recorded multiple visitations (although it is unclear whether these represent repeat visits from individual stoats, or multiple stoats).

Further trials using marked stoats are proposed (either at Perth Valley or at our Bottle Rock peninsula field site), in order to observe their behaviour and better understand the likelihood that individual stoats will re-visit camera sites that provide a food ‘reward’ (e.g. food dispensed from an automated lure dispenser).

More information

For more information about this work, and about ZIP’s broader research and development programme, please visit the following two sections of our website:

  1. Findings, which detail new developments and key areas of learning; and

  2. Updates, which provide information about progress with our work programme.

We also recently published our 2017-18 Annual Report, which summarises our work over the previous year and highlights several key projects that relate to the Perth River valley programme. 

If you have a question or feedback for the ZIP team, please contact us at info@zip.org.nz.

Update on Perth River Valley Project – assessing the effectiveness of a ‘river barrier’ for rats

Update on Perth River Valley Project – assessing the effectiveness of a ‘river barrier’ for rats

In 2017, ZIP ran a promising trial in Remutaka Forest Park, which provided strong evidence that rivers are an effective barrier to possum migration.

But what about rats..?

We are currently carrying out a project in the Perth River valley to attempt to answer that very question.

The Perth River research area is bordered to the south and west by the Perth and Barlow Rivers – both fast flowing, rocky, glacial waterways that converge on the southern boundary of the research area.

Since April 2018 we have been bio-marking rats along a 3.2km stretch of the true left side of the Perth River, to enable us to identify whether any rats caught on the true right are likely to have crossed the river (see map below).

This project was designed to be carried out following the completion of a predator removal operation on the true right side of the river, which would provide a ‘clean’ side along which to measure rat crossing events. We had originally intended to complete the removal operation during winter 2018, but this has now been reprogrammed until early 2019.

We are now investigating a range of alternative methods to begin to assess the effectiveness of the Perth River as a barrier to rats, within the near future. The river is at its lowest flow during the winter months, so gaining an understanding of its effectiveness as a barrier at this time of year is important.

As to how we will measure that effectiveness – watch this space for an update soon!

In the meantime, some useful and interesting information has already been gathered from the river barrier project site. To date, we have been able to assess: (i) the relative abundance of rats immediately adjacent to the river on the true left side (to provide an indication of current rat ‘pressure’ on the river barrier), and (ii) whether enough rats will eat the bio-marker to provide robust data for this trial. These findings are outlined below.

Map of river barrier assessment site, Perth River

Map of river barrier assessment site, Perth River

Measuring rat pressure on the river

ZIP-developed automated lure dispenser containing Pics peanut butter laced with rhodamine B biomarker

ZIP-developed automated lure dispenser containing Pics peanut butter laced with rhodamine B biomarker

ZIP-developed automated lure dispensers were installed on the true left side of a 3.2km stretch of the Perth River in the first week of April 2018. Every 24 hours, these dispensed Pics peanut butter laced with non-toxic rhodamine B bio-marker, which produces a fluorescent band visible under microscope in the growing whiskers of rats after they have eaten it. These were left in place to ‘feed’ rats for a month before measuring rat relative abundance in the same area.

Rat relative abundance is a measure used in predator control to estimate the relative number of rats within an area. This measure, in turn, provides us with an indication of the invasion ‘pressure’ on the river.

 

Relative abundance was measured over three fine nights along the same stretch of river where the automated lure dispensers were installed. A total of 53 Victor Professional rat kill traps were deployed at 50m spacing, lured with Pics peanut butter, in single entry black corflute tunnels. Results were calculated as the mean number of rats caught per 100 corrected trap nights (C100TN).

A total of 41 rats were caught over the three nights. After accounting for sprung traps, we determined a relative abundance of 39.4 rats/C100TN.

This is a relatively high score and may well be influenced by pre-feeding with Pics peanut butter (via the automated lure dispensers) for a month before trapping. If true, this pre-feeding principle may have wider application in trapping operations, including the Remove and Protect model. If invaders can be cued onto a lure before they invade, they may then be significantly more likely to be trapped using that same lure.

As for the river barrier assessment project, we now have confidence that there are plenty of rats present in the research area, and therefore the ‘rivers as a barrier’ concept remains a real test.

Uptake of the bio-marker by rats

The rat relative abundance survey also enabled us to determine the proportion of rats that were eating from the automated lure dispensers, by looking for evidence of the biomarker in the trapped rats. Whisker samples were taken from 37 of the 41 rats caught, and an additional two rats caught at Scone Hut during the same time period. We analysed those whisker samples under a microscope at Lincoln University, looking for the bright, solid bands of fluorescence from the rhodamine B. If three or more whiskers were found to show traces of rhodamine B, the rat was deemed to have fed on the prefeed from the automated lure dispenser.

Taking whisker samples for analysis

Taking whisker samples for analysis

A ship rat showing visible rhodamine B traces in belly fur

A ship rat showing visible rhodamine B traces in belly fur

A total of 82% (32/39) of rats caught and analysed were found with traces of rhodamine B, meaning this proportion of the resident population (as a minimum) had been feeding from the automated lure dispensers. This is a very encouraging result for the rat river barrier assessment, especially considering that uptake of the bio-marked lure is likely to increase the longer the automated lure dispensers are in place.

Ensuring a high proportion of marked rats is important as it gives us the best opportunity to determine whether any rats caught on the true right side of the river have braved the icy waters to get there.  

Further Update on Perth River Valley Project – possum removal operation

Further Update on Perth River Valley Project – possum removal operation

Zero Invasive Predators Ltd (ZIP) will undertake the aerial 1080 predator removal phase of the research and development programme in the Perth River valley from early 2019.

This phase was originally scheduled to be completed during winter 2018, but the forecast weather and snow conditions in the valley are such that we now cannot be confident that the 1080 to Zero method can be fully implemented in a timely fashion, in order to completely remove introduced predators. After consulting with our colleagues from the Department of Conservation it was decided to carry out the aerial phase from early 2019, in order to increase the likelihood of its success.

The weather factor

As detailed in a previous Update, the baiting schedule that is the basis of the 1080 to Zero method is weather dependent. In general, the ideal weather window each time we apply bait comprises one fine, calm day, followed by at least two nights of fine weather. The weather over the past three months has presented very few suitable weather windows. Despite that, we have successfully applied non-toxic prefeed bait on two occasions (on 30-31 May and 21 June).

Weather experts have advised that there is a 70-80% chance of an El Nino weather pattern emerging this spring, which will bring a predominantly south-west airflow, with cooler and wetter than normal conditions predicted for the West Coast. If this pattern does eventuate, then it is unlikely that we will be able to complete the four remaining applications of bait.

Perth River in flood, near Scone Hut (Credit: Briar Cook)

Perth River in flood, near Scone Hut (Credit: Briar Cook)

The snow factor

Ideally, toxic bait is not applied on snow that has settled on the ground. Snow can prevent target predators from accessing bait, and the moisture in the snow begins to degrade the bait, making it less effective. 

Considerable snow has fallen within the project area. It is now estimated that the ‘permanent’ snow line, i.e. the lowest elevation of snow not expected to recede until spring, is at approximately 1,250 metres above sea level.

Intermittent snow storms are likely to continue to bring snow to lower levels, where it will melt away. The image below shows snow conditions around one of the temporary bivvies located at approximately 800 metres above sea level.

Snow at 800m above sea level, 23 July 2018 (Credit: Chad Cottle)

Snow at 800m above sea level, 23 July 2018 (Credit: Chad Cottle)

Comments

The programme of work we are undertaking in the Perth River valley is research and development. We are focused solely on developing and refining a new way of tackling the predator management challenge, in an attempt to halt, and ultimately reverse, the decline of our native species. We are making good progress, but there is still much to do and learn along the way.

It is important to acknowledge that the fundamental nature of research and development is that there is inherent uncertainty, and risk. In this case, we are no longer confident that proceeding with the 1080 to Zero operation under current and forecast snow and weather conditions will deliver the predator-free results sought.

Between now and early 2019, we will continue to test and refine techniques to reduce potential impacts on kea (in association with Department of Conservation scientists), and increase our confidence in successfully delivering the Remove and Protect model in the Perth River valley.

Update on Perth River Valley Project – possum removal operation

Update on Perth River Valley Project – possum removal operation

Zero Invasive Predators Ltd (ZIP) has received permission from the Department of Conservation (DOC) to proceed with the aerial 1080 phase of our programme of research and development in the Perth River valley, but weather and other conditions currently prevent the operation going ahead for the foreseeable future.

The permission will enable us to maintain our efforts to develop a promising new approach to completely and permanently remove introduced predators from large mainland areas, in order to help New Zealand’s native biodiversity to thrive.

If successful, the approach will have particular relevance for the more than one million hectares of similar landscapes in South Westland.

The permission is conditional on ZIP completing two actions in the treatment area to minimise the risk to kea, namely: (i) locating tahr carcasses to provide an alternative food source and foraging focus, and (ii) applying non-toxic repellent bait to induce an aversion to cereal baits, prior to applying the toxic bait.

Since the inception of the programme of work, we have worked with kea experts from the Department of Conservation to identify and minimise the risk to kea of the programme of work in the Perth River valley. 

We’re very grateful for their help. And we’ll continue to strive to help kea flourish, both locally and nationally.

As for when the aerial operation will go ahead, the application of the predator removal approach is subject to local environmental conditions, particularly wind, rainfall and snow cover.

We will not proceed with the aerial 1080 operation until we are confident that it will completely remove all possums and significantly reduce rats and stoats. The current conditions in the Perth River valley are, however, not suitable to proceed with the aerial 1080 operation for the foreseeable future.

Update on Perth River Valley Project – opportunities to reduce risk to kea

Update on Perth River Valley Project – opportunities to reduce risk to kea

Updated Wednesday 19 July 2018

Zero Invasive Predators Ltd (ZIP), with the support of the Department of Conservation (DOC) and Predator Free 2050 Limited, is currently undertaking a programme of research and development work in the Perth River valley on the West Coast of the South Island.

The purpose of the work is to test and refine an approach to completely remove possums from large areas and prevent them from re-establishing, and to develop this approach for ship rats and stoats. We call the approach ‘Remove and Protect’. This is the first time such an attempt has been made on the New Zealand mainland. The results are expected to help enable New Zealand to achieve predator-free status by 2050.

The Perth River research area contains kea, which is a nationally endangered species. The purpose of this Update is to outline some new measures that we are progressing to mitigate potential impacts on kea of the work underway in the Perth River research area. 

Background

Kea are the world’s only mountain parrot and considered by scientists to be one of the most intelligent bird species in the world. The national population of kea is expected to decline by 50-70% over the next 10 years unless the causes of decline are addressed.  Predation by introduced predators like possums and stoats is considered one of the key reasons for the decline in kea numbers. 

One component of ZIP’s ‘Remove and Protect’ approach that is being tested and refined in the Perth River research area is the use of a method called ‘1080 to Zero’ to completely remove predators.

Predator control using aerial 1080 has an overall beneficial impact on kea nesting success. In one recently published study, kea nest survival at a monitored site increased from 46.4%, before the application of 1080 to 84.8% after the application of 1080 (Kemp et al. 2018). 

However, kea have an inquisitive nature, and some kea have died as a result of 1080 poisoning. Consequently, from its inception, the research and development work programme in the Perth River valley has actively considered ways to reduce risk to kea. 

Steps already taken to reduce risk to kea in the Perth River research area

Minimising the risk to kea was part of the decision making process when it came to deciding the location of the Perth River research area. We reduced the size of the original proposed research area from c.20,000ha to 12,000ha, to lessen the number of kea exposed to 1080 baits (the 1080 to Zero treatment area is only 7,500ha).

The research area was located as far as possible from the nearest kea scrounging site, Franz Josef township, which is 28km away at its closest point. We also selected an area that had a history of aerial 1080 operations – in this case five operations since 1997. The site was also selected on the basis of a number of other criteria related to our research requirements.

Since then, 30 kea have been fitted with radio transmitters (and another 25 have been banded) to monitor the impact of applying aerial 1080 on kea mortality and breeding success. Radio-tagged kea are scheduled to be monitored (using a light aircraft) after each application of prefeed and toxic bait. Monitoring was done after each of the two prefeeds that were applied on 30-31 May and 21 June.

We also recently completed a project to estimate how likely kea would be to consume baits, in order to assist DOC to decide whether the toxic bait application should proceed. In summary, the results confirmed what was already known - i.e. that kea interact with bait. However, owing to the small sample size, it was not possible to make a specific estimate of the likely level of actual consumption of toxic bait. 

Two new measures to mitigate potential impacts on kea

It was originally estimated that around 18 kea were likely to be present in the research area. During the course of our work, we discovered that there is a healthy population of approximately 75-100 kea in the research area. It is likely that the current population of kea can be partly attributed to the benefits of the previous five applications of aerial 1080 in the area.

We are committed to doing all we can to reduce the risk of kea mortality in the event that the decision is made to apply aerial 1080. Recently we have initiated two new measures to help achieve this.

Discourage kea from eating 1080 bait

To reduce the risk of birds consuming toxic bait, we are attempting to enable kea to learn that eating bait is not good for them, by applying non-toxic prefeed bait containing a repellent, anthraquinone, that makes them feel sick, before any toxic bait is applied.

Anthraquinone is a secondary repellent in that it has no smell or flavour, but makes birds feel sick after consumption. By associating the bait with the source of illness, birds will be less likely to eat it in future.

On Saturday 14th July, with the permission of the Department of Conservation, green-dyed baits laced with anthraquinone were applied within a thin band along a section of the alpine boundary of the research area.

This non-toxic bait was dyed green, in order to resemble the toxic bait as closely as possible.

We may reinforce any repellent effect with a repeat application of repellent bait, immediately prior to toxin baiting. The thinking behind doing this is that the more times kea have the opportunity to learn to avoid the bait, the greater the chance that they will avoid it in future.

Provide tahr carcasses as alternative food/distraction

Our field staff have observed, and there is substantial anecdotal evidence, that kea in this area already quickly locate and utilise dead tahr (either left by hunters or dead from natural causes) as a food source.

On Friday 29 June, the carcasses of 21 tahr shot by a DOC ranger (using a high-powered rifle – not lead shot), as part of a DOC’s wider programme of tahr control, were placed at approximately 1km intervals along the upper boundary of the 1080 to Zero treatment zone, in order to lure kea away from the baits.

Kea activity at each tahr carcass is being monitored using trail cameras, in order to help us understand whether this approach plays a role in limiting any impact from the aerial operation. Our staff have already observed a number of birds visiting the carcasses.

There is strong evidence to suggest that the risk to kea of secondary poisoning (i.e. from eating the meat of animals that have been poisoned by baits) is much lower than the risk of primary poisoning (i.e. from eating baits) following an aerial 1080 operation (van Klink and Crowell 2015).

Furthermore, it is not known if aerial 1080 impacts tahr. This is being investigated as part of a Game Animal Council-led project connected with the proposed aerial operation in the Perth River research area.

We will continue to record activity at the tahr sites from now until any toxic bait is rendered safe. From this data, it should be possible to determine whether or not the kea maintain interest in the tahr carcasses in the presence of bait.

Final thought

DOC is currently reconsidering the permission for ZIP to apply aerial 1080 as part of the Perth Valley research project.

Ultimately, the decision about whether to apply aerial 1080 in the research area will balance the risk of individual kea mortality against the potential population benefits to kea (and other native species) in the research area, as a result of predator removal, and the benefits of continuing to test, refine and develop the Remove and Protect approach and its potential contribution to a Predator Free New Zealand.

We will continue to provide updates via the ZIP website as this work progresses.

 

Reference

Kemp JR, Mosen C, Elliott GP, Hunter CM. (2018). The effects of aerial poisoning for pest mammal control on the productivity of the kea (Nestor notabilis). New Zealand Journal of Ecology 42.

Van Klink, P. A., & Crowell, M. D. (2015). Kea (Nestor notabilis) survivorship through a 1080 operation using cereal baits containing the bird repellent d-pulegone at Otira, central Westland. Publishing Team, Department of Conservation.

Update on Perth Valley Project - results of pre-operational monitoring

Update on Perth Valley Project - results of pre-operational monitoring

Background

Preparations continue for implementation of our ‘1080 to Zero’ operation in the Perth River Valley, South Westland. The objective of this operation is to completely remove possums (and potentially ship rats). The operation is also expected to have a substantial effect on the local stoat population; however, to what extent remains unknown.  In order to evaluate the success (or otherwise) of our operation, we need to have an understanding of relative abundance of these target species in the site pre-operation. So, at the end of March and early April, we undertook to measure the relative abundance of possums, rats, and stoats within our project area.

We also took the opportunity to measure the presence of non-target species within the area, in order to estimate whether these species are affected by the aerial operation.

Measuring predator relative abundance

The Perth River Valley site consists of 12,000ha of mountainous terrain, surrounded by substantial rivers and glaciers, up to 3,250m in elevation at some locations. An area of approximately 7,500ha within this site will be aerially treated with 1080.

Within this area a total of 12 monitoring lines were deployed, each 500m in length and positioned evenly across different vegetation types and elevations, between 290 and 1,600m. Lines were widely spaced, to ensure individual animals were unlikely to encounter devices from multiple lines.

We followed the National Pest Control Agency (NPCA) standard guidelines for monitoring possums and mustelids (in this case, stoats and weasels), and DOC standard protocol for rats.

Tracking tunnels were placed along lines at 50m intervals for rats. Tunnels were placed at 100m intervals for stoats, accompanied by motion-sensing cameras (positioned over tracking tunnels).  WaxTags™ were used for possums, deployed at 20m intervals along a 200m stretch of each line. Each monitoring line ran for 7 days. Rats were tracked on the first day, followed by three days of camera trapping and tracking for stoats. The full 7 days were used to monitor possums.

Measuring the non-target species

The same camera traps used to monitor stoats were also used to monitor the activity of various non-target species within the site. We deployed these cameras three weeks prior to the one-week abundance index surveying of target species. Cameras were not lured during this time; however, because many species prefer to follow cut tracks, the cameras were well placed to capture a variety of species.

Relative predator abundance results

In total, 59 out of 60 camera traps remained functional throughout the pre-operation target and non-target species surveys. Using the standard protocol for each target species, our results were:

  • 48% possum chew across site (58/120 WaxTags),

  • 12.5% tracking of rats across site (15/120 tracking tunnels), and

  • 1.7% stoat tracking across site (1/60 tracking tunnels).

Stoat exiting tracking tunnel, 18 April 2018

Stoat exiting tracking tunnel, 18 April 2018

Camera traps were used to increase confidence in results for stoats, as recent literature suggests they have a much higher sensitivity for these species than other available detection tools. However, over the course of the three-day survey for stoats, both camera trap and tracking tunnel results were the same.

 

Comparing the industry standard with camera detections

Camera traps used during the non-target species survey period were left running during the one-night tracking tunnel index for rats. When comparing only the 60 tracking tunnels paired with camera traps during this time, a total of 10 cameras across the site detected rats (16.7%), compared with only 6 tracking tunnel detections (10%). This result, although a seemingly small difference, shows once again the sensitivity of camera traps, even for smaller species such as rats.

We also observed numerous rat encounters over the course of the three-week non-target species camera survey (Table 1). Many recent studies have suggested that the length of time for device deployment is highly influential on the probability that it will detect an animal. For instance, looking only at the three days prior to the standard one-night tracking index for rats, a total of 17 cameras detected rats. Over the course of the three weeks in total, 29 out of the 60 cameras detected rats; stoats were detected on 11 cameras, and possums were detected on 37 cameras (Table 1). 

Table 1 Standard index monitoring and camera trapping results

Perth Valley pre-monitoring results.PNG

Non-target species seen on our camera network

During the three weeks of pre-operation camera trapping, we found chamois (on 7 cameras), deer (6), Kea (2), Tomtits (3), South Island robins (7), black birds (5), and a weasel (1) on camera.

South Island robin, 24 April 2018

South Island robin, 24 April 2018

Chamois, 24 April 2018

Chamois, 24 April 2018