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NZ Kea

20 Reasons why DoC should not poison kea habitat

An average of 12% of marked kea have been reported dead within the first few days of aerial poisonings (DoC, 2016; Kemp et al., 2016, unpublished); range up to 78% (Graf, 2011). (Figures do not include later deaths from carcass scavenging or slow deaths from poisoning.)

New-Zealand-100%-pure-1080-poison-1

Loss of science quality in NZ is having dire consequences

Back in the 1990s, in at least one institution, rigorous government science was alive and well. At Invermay Agricultural Research Centre, “Lab” meetings were being held where the scientist (or trembling student) presented his or her proposed experiment: the background, hypotheses to be tested and methods.

Why is there an argument over 1080?

For many decades New Zealand has been racked by arguments over the widespread use of aerial 1080 poison. Both sides of the argument are supported by intelligent and committed conservationists so why can’t consensus be found when both sides care deeply about the birds and the forests.

New Zealand government poisons kea

1080 Poison | Science and Facts

PUBLISHED BY THE GREYMOUTH STAR

Any true scientist would be intensely annoyed to see wishful thinking and casual observations (rather than properly replicated experiments with appropriate controls) masquerading as science, especially when lots of people actually believed in it. Quinn Whiting-O’Keefe is a true scientist. In the film Poisoning Paradise he is so incensed at the lack of science and fact underlying 1080 poison use in NZ his words are like steam escaping. The same feelings led me to 2 years of reading and tapping furiously away at a keyboard to expose the facts on 1080 poison, as given to our Environmental Risk Management Authority (ERMA) for their review in 2007. Here they are:

1080 is toxic to species of all forms of life from microbes to plants, insects, birds and humans. In mammals, it causes birth defects, reduced fertility, damage to reproductive organs and other organs including the brain and heart. Anecdotal reports indicate there may also be a link with cancer but there has been no research at all on this. Claims that 1080 poison does not cause mutations arise from a study on mice, that ERMA was unable to get a full copy of.

1080 has an amazing ability to spread. Again and again in research, “control” samples have become accidentally contaminated. Because 1080 poison is highly soluble it spreads very fast in water and also up food chains. For example, researchers found 100% mortality of aphids on broad bean plants grown in 0.00005% 1080 solution. Likewise, 1080 has been shown to pass readily into milk and meat.

When 1080 poisoned cereal pellets are dropped from the air, the poison in cereal dust is found over the entire treated area and beyond. Very little is known about the spread of this toxic dust but it was found 1 km beyond the application zone 5 days after an aerial 1080 drop (sampling for dust further away, and later after the drop, was not carried out).

There has been no research into how long 1080 poison persists in treated areas. In the ERMA documents it was recognised that it might persist indefinitely at low concentrations. It has been found to persist in many varied situations including dry places, cool water, water lacking aquatic plants, some types of soil and in carcasses. The rate of breakdown of 1080 poison in New Zealand forests and streams is unknown, but it is extremely slow at around 5oC. Thus ERMA’s Agency warned that “No studies have been conducted using standard international guidelines to assess the route and rate of degradation of 1080 in soil. The rate of such degradation under New Zealand conditions is uncertain.” And regarding water: ”Overall, the relevance of the aquatic plant/water studies to the degradation of 1080 in water in NZ is not clear.”

In the ERMA review, there was no consideration of effects of breakdown products which include highly toxic fluorocitrate.

The ERMA review also brought to light that, among several unexpected properties of 1080 poison, degradation occurred in biological samples stored at -20oC, meaning that most results from water and soil sampling to date are useless because storage conditions were either not reported or were not adequate.

Birds reported killed by 1080 poisoned cereal baits include morepork, weka, tomtits and grey warbler and animals known to eat cereal bait include kea, kaka, little spotted kiwi, kokako, saddleback, kakariki, pukeko, insects, koura and lizards. DoC’s reporting on bird deaths cannot be relied upon. Their usual method of assessing bird numbers, 5 minute counts, were acknowledged as useless by ERMA’s Agency who reported that “Five-minute counts have been identified as not reliable for assessing population impacts after 1080 operations unless high mortality occurs..and not reliable for rarer species”.

It was recognised in the ERMA review that certain species (survivors that are fastest to breed and disperse within the vacant habitat) will be most likely to recover after aerial 1080 poisoning. This will apply not just to birds but all organisms including invertebrates (“1080 is highly toxic to terrestrial invertebrates” – ERMA’s Agency) which are an integral part of food chains and nutrient recycling. Thus ecological effects of the poisoning will be far-reaching and favour rapidly colonising species.

Not surprisingly then, 1080 poison is now clearly associated with plagues of pests including stoats, rats and mice, that have devastating effects on native species. For example, a DoC employee reported in 2002: “Four months after an effective possum and rat knock-down by a 20,000-ha aerial 1080 operation over Tongariro Forest, stoats reappeared in the centre of the forest and began killing kiwi chicks. So far five of the 11 chicks have been predated, and all in the centre of the treatment area.” Closer to home, a West Coast DoC employee reported on kaka in 2003 “A dramatic increase in fledgling mortality has been noted coinciding with a change to the pest control regime. Seventeen female chicks were monitored since the breeding season and excluding missing birds, eleven of fourteen fledglings have died. Nine of these were probably (some certainly) killed by stoats..The pest control regime was an aerial 1080 pollard operation in October [2002].” Going on to report on rowi: ”The current rowi breeding season has been very disappointing. All 14 of the monitored chicks were dead by early January, with stoat predation being the major cause..a huge irruption of rats and stoats, coincided with the height of the rowi breeding season.. Stoats completely saturated the core area during December and January..Similarly, rat numbers were 5-10 times higher this season compared with the same time last season.” (West Coast, April 2003).

Our remaining native species need all the genetic diversity they have if they are to survive forthcoming challenges such as drought, storms, disease and habitat modification, therefore they should be managed with extreme care. New, unique species are still being discovered regularly, making nonsense of claims that DoC knows what its doing with aerially spread poisons. DoC’s legal duty under the Conservation Act is to manage natural resources for conservation purposes so their willingness to allow the killing of massive numbers of native animals is nothing short of criminal.

Contrary to DoC’s scaremongering about possums preying on birds, numerous studies have shown that possums are principally herbivores. Where possums are currently invading new areas and decimating favoured plants such as mistletoe, it would make sense to target them there, using humane, safe techniques such as hunting, live traps, and well-designed kill traps. I have operated a natural pet food business for the last 6 years and the demand for the raw product has been escalating as the world becomes increasingly short of animal protein, and as Asian pet ownership increases dramatically. The Asian markets for natural NZ pet food are insatiable and it makes sense to employ hunters and use pests as a resource rather than squander our 200 million-year-old natural heritage.

Like DoC, the Animal Health Board has no rational basis for using aerial 1080 poison to kill possums. Its arguments were left in tatters in the ERMA review. Firstly, the RTCI, the possum catch index that underlies the AHB’s strategy, was deemed unreliable (Agency, Appendix F). Then both economic experts got stuck in. Professor Ross Cullen, regarding market perceptions of NZ’s Tb status: “No research is cited in the Application that studies the dollar losses occurring from the loss of one or more export markets..Clough & Nixon (2000) conclude…a trade ban would be difficult to sustain under current international trade rules, the risk is very small and the expected value of an avoided trade ban is modest” and “The Application…fails to demonstrate evidence or understanding of economic research on use of 1080, pest control or Tb…this section of the application is unsophisticated, uses crude approaches to estimate even the largest benefits and costs associated with the use of 1080, lacks awareness of many pertinent economic research techniques, seems unaware of almost all relevant economic research.” And from NZ health experts: “around 3% of all human Tb cases are M. bovis…The Ministry of Health attributes these low rates to herd testing and the widespread pasteurisation of milk”…“even if bovine Tb were prevalent in cattle it would not present a real risk to human health”…”We recommend that in making its decisions, ERMA de-emphasise the importance of bovine Tb”. Then from ERMA’s Agency: “the applicants have provided little factual support to demonstrate efficacy of aerial compared with ground application of 1080 as it relates to possums and Tb control”…”the relative contributions of possums and other wildlife (particularly ferrets) to Tb infection of cattle and deer herds are not clearly defined at this time.” And finally, from the ERMA Committee itself: “there is no evidence to support the suggestion that trade is significantly reduced by not having bovine Tb-free status.”

Since there are now relatively few Tb-infected farms (due to amalgamation of farms, herd testing and movement control) a relatively cheap, harmless and effective approach to prevent livestock becoming infected by wildlife would be to control pests only around farm boundaries. In this way Tb-infected wildlife (which may include pigs, cats, hedgehogs, ferrets, stoats, weasels, rats, deer and feral stock) could be identified, the livestock would be protected, and the vacant habitat created as pests were eliminated would draw further potential Tb vectors out of wild areas for elimination. Additionally, livestock can be vaccinated against Tb.

If stupidity prevails and another aerial 1080 poison operation goes ahead, some minimum controls are imperative. An untreated buffer zone of at least 1 km should be allowed around any catchment used for human or stock drinking water, taking care that all tributaries are identified. In addition, environmental effects must be monitored. Last year, our Conservation Authority recommended that the Government require the Animal Health Board to begin monitoring for changes in forest health. Any such monitoring must be comprehensive, competent and independent. History tells us that left to DoC or the AHB, the results would be frustratingly inadequate.

Dog-poisoned-by-1080

At least 65 dogs in a year poisoned by 1080 in New Zealand

PUBLISHED BY SCOOP INDEPENDENT NEWS

Research by the National Poisons Centre and the Otago University’s Pharmacy School which was presented at an International Poisons Congress in 2008 found that dogs across New Zealand are at extreme risk of poisoning from 1080(1).

The researchers carried out a postal survey of 125 randomly-selected veterinarians. Fifty-two vets responded and within their practices over a one year period, 65 dogs poisoned by 1080 had been dealt with. Three of the 52 respondents had each treated 10 cases. Only 25% of the treated dogs survived (only those that had not shown clinical signs of poisoning before treatment).

The 65 dogs will be a fraction of actual cases dealt with because not all vets in the country were involved in the survey, and not all dogs poisoned with 1080 will get to the vet. The researchers told the conference that in New Zealand “Poisoning of dogs by 1080 is widespread with no defined management in place.”

This finding contrasts sharply with what our Environmental Risk Management Authority (ERMA) claimed in its reassessment of 1080 poison in 2007. According to ERMA “Controls in place to ensure dogs are not exposed are adequate” (2)

It also makes nonsense of the claim made this June by our Parliamentary Commissioner for the Environment (Dr Jan Wright) that only 8 dogs have been reported killed in New Zealand by 1080 poison since 2007.  Dr Wright quoted only the number of dogs in incidents reported to ERMA about 1080 operations. The “8 dogs” figure is clearly a gross misrepresentation of the actual number of dogs killed. This is just one of a large number of misleading statements in her report on 1080, which is heavily biased towards its use, as was the ERMA reassessment. (3)

Unfortunately for dogs and their owners, it is likely that the real number of deaths has actually increased in recent years. This is because the area over which 1080 poison is being spread has been increasing; a significant increase in its use (proposed by the Department of Conservation (DoC) and the Animal Health Board (AHB)) was a major reason for ERMA’s re-assessment of 1080 (Committee Decision, page 15).

Furthermore, the controls outlined by ERMA in 2007 require that signs warning of 1080 poison must be removed, after remaining in place for a minimum of six months (or less if toxin removal or testing indicates the area is safe)(4). This control was imposed without any knowledge of how long 1080 remains a risk in carcasses, although it was admitted that “1080 residues in the carcasses of poisoned possums may be very slow to break down” (5).

ERMA stated in its assessment “There is limited information available on the degradation of 1080 in animal carcasses..It is clear that 1080 residues remain in the guts of dead animals for prolonged periods (at least 75 days under cool winter conditions..) and only degrade slowly” (6). Furthermore the low rate of degradation “may be a function of low pH in the gut, absence of bacteria able to degrade 1080, toxicity to gut bacteria, low levels of..invertebrate activity, accompanied by cool temperatures at the time of 1080 bait distribution.” (7)

This possible effect of the toxin helping to preserve the carcass has not been taken into account by DoC when drawing up its operating procedures. For some years now DoC has monitored carcass breakdown at poisoned sites but these carcasses “can be sourced from anywhere” and are not required to be poisoned (8).  According to ERMA, the AHB (the biggest user of 1080 in NZ) and other users merely assume that six months after the operation the signs can come down.

Carcasses of 1080-poisoned animals are a huge risk to dogs because of the persistence of the poison and because dogs are so susceptible to it. Just 1.75 mg of 1080 poison will kill a 25 kg dog, and enough poison is spread aerially per hectare to kill over 2,500 dogs (Table 1) (and 125 times more poison than required per possum). 1080 poison concentrations in possum gut contents were 30.6 mg/kg after 25 days and 4.9 mg/kg after 75 days in one study (9). In another study 1080-poisoned rabbit carcasses became more toxic as they aged, possibly because of dehydration (10).

Table 1: 1080 application rate and killing power per hectare by species

* for 0.15% 1080/Kg applied at 3 kg/ha (4.5 gms/ha or one level teaspoon). For lower concentrations and sowing rates figures will be
proportionately lower.

 

Species

LD50 mg/kg body wt

Average species wt (kg)

LD50 (mg) for this weight

mg 1080  /ha*

LD50 doses/ha

Dogs

0.07

25

1.75

4,500

2,571

Sheep

0.4

35

14

4,500

321

Deer

0.5

80

40

4,500

113

Possums

1.2

3

3.6

4,500

1,250

Humans

2.5

80

200

4,500

22.5

Weka

8.0

1

8

4,500

563

Ducks

9.0

1.5

13.5

4,500

333

Rats

1.2

0.14

0.168

4,500

26,786

LD50 = dose per kg body weight to have a 50% kill risk

 

Source: Dr Hugh Barr, NZ Wildlands Biodiversity Management Society Inc.

Dogs exposed to less than lethal doses of 1080 are likely to suffer damage to the heart, other organs and reproductive tissues, and unborn puppies are likely to develop deformities, as these effects are seen in other mammals (11). Water supplies are a likely source of on-going exposure to 1080, wherever poisoned carcasses enter them (12).

Coupled with the risk of poisoned carcasses is the fact that the baits themselves can remain toxic for months, especially when carrot is used, and when baits fall in dry areas.  An example of the on-going risk was 78 sheep that died after grazing an airstrip used to load 1080 poisoned carrot bait, 20 weeks after the operation(13). In Fiordland, some cereal baits “looked quite fresh” after seven weeks, according to a report from DoC field staff (Waitutu 1080 operation, 2010) (14).

Another blow to dog owners from the ERMA re-assessment was its decision to remove the requirement to erect a sign warning of forthcoming poisoning. No prior warning sign at the site is required now  (15).

Historically, concerned officials have attempted to prevent the use of 1080 because of its extreme risk and cruelty to dogs. For example a biologist working for the US Fish & Wildlife Service wrote in 1948: “the spasm period of victims, particularly the canines, seems unduly violent…The severe spasms associated with 1080..[is an] outstanding objection” (16). Another example is a report from 1972 that stated that our own Rabbit Destruction Council had suggested arsenic as a substitute for 1080 due to the danger to farmers’ dogs (17).

Dogs owners are advised to read public notices carefully and to consider all 1080-treated areas as extremely hazardous.

References (note that the ERMA documents with reference numbers can be found on this website) ERMA Documents

(1) Hope, A., Smith M., Temple, W., 2008. Clinical Toxicology Volume 46, abstract 137
(2) ERMA Committee Decision, Appendix B, p 200: 1
(3) A scientific evaluation of the PCE’s views on 1080, this website
(4) ERMA Committee Decision, p 100: 1, 2
(5) ERMA Committee Decision, p 65: 1
(6) ERMA Agency, Appendix C, page 369: 2
(7) ERMA Agency, Appendix C, page 369: 4
(8) Bait and Carcass monitoring Guideline 2011 (DoC document DOCDM649647)
(9) ERMA Agency Appendix N p 727: 4
(10) ERMA Agency Appendix C p 371: 1
(11) Index to ERMA Documents, Health section, this website
(12) ERMA Agency Appendix C, p 370: 4; M, p 700: 2
(13) ERMA Agency, Appendix F, p 727: 4
(14) Waitutu Field Trip November 2910 (DoC Report by P. Dilks & T. Greene)
(15) ERMA Decision, Appendix A, p 167: 3
(16) Submitter to ERMA no. 9074
(17) ERMA Applicants’ References p 15: 1