Rural Affairs and Islands Committee

Meeting date: Wednesday, June 14, 2023

Official Report 786KB pdf

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Wildlife Management and Muirburn (Scotland) Bill: Stage 1

Good morning, everyone, and welcome to the 18th meeting in 2023 of the Rural Affairs and Islands Committee. I remind all those who are using electronic devices to switch them to silent. Ariane Burgess will join us at approximately 9.45, and Emma Harper is substituting for Christine Grahame.

Our first item of business today is an evidence session on the Wildlife Management and Muirburn (Scotland) Bill. I welcome our first panel of witnesses, who are from the grouse moor management review group. With us are Professor Alan Werritty, the chair; and Professor Ian Newton and Professor Colin Reid, members of the group. We have scheduled about 90 minutes for this session.

I will kick off with the first question. In 2019, the Werritty report recommended that

“a licensing scheme be introduced for the shooting of grouse if, within five years ... there is no marked improvement in the ... sustainability of grouse moor management, as evidenced by the populations of”

certain breeds of raptors. Professor Werritty, is there sufficiently strong evidence of wildlife crime on grouse moors to justify the intervention of licensing? Do you believe that the bill reflects the position that your review intended?

Under our remit, we started by considering the 2017 report by Scottish Natural Heritage, which demonstrated that a third of tagged golden eagles had disappeared in mysterious circumstances. The way that it was put was that they had disappeared in suspicious circumstances on or around grouse moors, and we confirmed that suspicion in our findings.

There is a clear spatial association between the recovery of illegally killed raptors and managed land for grouse shooting. At that stage, we were unable to produce a map demonstrating that association, although I understand that Hugh Dignon may now be able to provide you with such a map. We had privileged access to information from Police Scotland to underpin our recommendations and support our findings.

Since then, time has moved on and I have not had access to the same amount of data that was available to me as chair of the review group. However, I turn to Professor Newton, who can, I think, provide us with an update on the situation since we reported.

As we understand it, the situation is that the persecution of birds of prey has not declined substantially in the years since the report was written. In fact, during the year with the most lockdown, which was 2020, the rate of killing or the number of cases reported to the RSPB was the highest so far this century. In other words, when there were fewer people in the countryside, the level of persecution almost certainly increased. The total for Britain as a whole in that year was 146 cases, of which 26 were in Scotland. In 2021, the following year, the numbers were still high, although they dropped somewhat. I think that the total for the whole of Britain was 108 and the number of cases in Scotland was about 17. The RSPB produces a crime report every year. The figures for 2022 are not yet available, but I understand that they are of a similar magnitude to what they were in the past.

There is a limit to the emphasis that we can put on those figures, because they depend on carcases or other evidence being found in the countryside, largely by chance, and reported. The general feeling—among conservationists, at any rate—is that the figures represent the tip of an iceberg. Nonetheless, the statistics have not declined significantly since the report was written.

You are referring to reports by the RSPB, which is not independent. Surely, the national wildlife crime report would be the place where such findings would be reported. I think that you said there were 26 cases in Scotland. Does that refer specifically to grouse moors?

No. It refers to the country as a whole. Not all the cases would be on grouse moors. Some will be in lowland areas.

On the point about the evidence, it is now between eight and 15 years since there has been a review by the Scottish Government or whoever that would inform the national wildlife crime report. Why are we about to bring in legislation that would appear to depend on research done by the RSPB?

The RSPB has traditionally been the body that has collated this sort of information, but one has to remember that it is not the RSPB that collects the information; it is members of the public. Most of the survey work on raptor populations in Scotland has been done by what we now call the Scottish raptor groups. They are groups of interested amateurs—“citizen scientists” would be the words that we use these days—who go out and monitor raptors of various species in their home areas by checking all the known sites every year. There is a broad body of people who are responsible for collecting the information—people drawn from all walks of life. The RSPB collates the information, or most of it, because it is the organisation that is concerned with bird protection and it has the biggest interest in it.

Okay. Thank you.

Good morning. The bill sets out a range of relevant offences in relation to which a licence under proposed new section 16AA of the Wildlife and Countryside Act 1981 may be revoked or suspended. Do you agree that the list of offences is relevant and appropriate?

Yes. The problem so far, as I am sure you are aware, has been that one needs sufficient evidence for a criminal court to prosecute, but most of these offences take place in remote areas where there are no people to see them, so it is very easy to hide them. Hardly any cases of somebody killing a bird of prey are witnessed. A number of cases have been filmed, but you can appreciate how difficult it is to do that. The important thing is that we can use circumstantial and other kinds of indirect evidence to indicate the scale of this killing.

Do you believe that the current scope of relevant offences is proportionate?

Yes. The difficulty is in getting a prosecution under criminal legislation.

There is a choice to be made in these situations. You are trying to identify offences that suggest that somebody is not an appropriate person to hold a licence. You can approach that in a very narrow way whereby all that you look at is their conduct in the exact area of activity, or you can say that the form of behaviour is reflected in and shown by the way that people react in other situations.

There are similar considerations in all sorts of other areas where licensing is involved. For example, they have arisen in relation to firearms offences. If you are deciding whether to give somebody a firearms licence, do you look only at the way that they have behaved in relation to firearms or do you look at other forms of behaviour that may suggest that they are not to be trusted, that they are unreliable and so on? That is a policy choice to be made.

The list could be a lot shorter or it could be a lot longer. You could make cogent arguments both ways.

I am keen to explore a wee bit further the range of relevant offences. The bill identifies relevant offences under part I of the Wildlife and Countryside Act 1981, the Protection of Badgers Act 1992, part III of the Conservation (Natural Habitats, &c) Regulations 1994, section 1 of the Wild Mammals (Protection) Act 1996 and the Hunting with Dogs (Scotland) Act 2023. Given that your review looked specifically at raptor persecution, do you believe that the inclusion of all those things in the bill is proportionate?

Our remit was not just to look at raptor persecution; it was to look at grouse moor management more widely. In the report, we made a point about the need to look at the matter in a wider context. It would not be sensible to fragment the different bits too much. It could be said people who commit those offences are generally showing an attitude, approach and willingness to behave in a way in relation to the natural environment that is in line with the things that the bill is trying to stop.

If you see the measures as being purely about raptor persecution on grouse moors, I would say that that is an excessively narrow view of what our review tried to look at. Indeed, one of my regrets is that, despite the time that has passed since our report, we have not seen a wider review of the context of upland management. We would have hoped for integration of the outcome of the deer review and the legislation associated with that. We would have hoped that, by now, the post-Brexit rural support systems would be clearer, along with what is happening in relation to carbon management and so on in the upland areas. Looking at any one bit in isolation is a danger.

As I said, however, in relation to this particular issue, you could take a very narrow approach whereby only activities that are immediately involved are deemed to be relevant offences, or you could take a much wider approach whereby a person showing disregard for the elements of the natural environment that we value is enough to be relevant for these purposes.

You have made a number of points, Professor Reid, and I want you to clarify some of them. Are you saying that what the Scottish Government has done in shaping the bill is broader that what the Werritty review recommended in terms of the scope of triggering a licence for suspension or revocation? I would also like to explore what the Werritty review believed was the causal link between raptor persecution and grouse moors.

09:15  

On the first issue, I do not think that that is the case. We were asked to look at the matter more widely. We expressly did not look at the details of a licensing scheme, because we were very aware of issues such as the duration of licences. We may move on to discuss that today. We consciously identified a number of issues that would have to be thought about, but we did not explore them in detail. We consciously left them for the next stage, knowing that there could be a range of options, all of which would be reasonable.

Raptor persecution was the trigger for setting up the review, but it is not the only thing that we were asked to look at.

The point is that the bill that the Government has shaped covers a broader range of crimes.

What has been identified as being relevant indicators that would put a licence at risk captures a range of behaviours in relation to the natural environment, and not just raptor persecution.

My colleagues have asked about proportionality. Do you have any comment to make about that, given the recommendations that the Werritty review made?

We did not get into that issue, because we did not work through the details of a licensing scheme. We recognised that you could design a scheme that would be wholly disproportionate or you could describe a light-touch scheme that would have absolutely no problem in passing any test, in any legal or political sense, of proportionality. The balance has to be looked at.

In looking at the issue of proportionality, you have to look at the legislative package as a whole. What are the tests for intervening? What are the appeal mechanisms? What are the procedures? What sanctions are available? It is very much a package, rather than any particular measure being identified in isolation.

Can I press you on the licensing scheme, Professor Reid? I was on the committee that looked at the review originally, back in the day. I have read through the papers and I note that you said:

“We want to see a licensing scheme that is more flexible and responsive than a black-and-white scheme whereby you have to apply every year to get a licence.”—[Official Report, Environment, Climate Change and Land Reform Committee, 21 January 2020; c 12.]

However, proposed new section 16AA(5)(b) of the 1981 act provides that licences may be granted for a maximum of one year. Would the scheme be improved if licences were granted for a longer period?

My personal view is that it would. Given that the activities involve long-term management of the land and that businesses expect to be able to plan ahead, I think that annual licence renewal is unnecessary. There could be longer-term licences, subject to the provision that they may be amended or suspended.

Again, it is the idea of the whole package. If, once a licence was granted, you could do very little about it, there would be a stronger case for having annual licences, because the annual renewal would be the only way of keeping an eye on things, changing things or affecting things. Given that the bill provides quite wide powers for ministers or NatureScot to modify, suspend or revoke licences, I think that annual renewal is probably unnecessary.

Your review recommended SNH—or NatureScot, as it is now—as the licensing authority. Does the bill that we are looking at allow for a scheme that you feel NatureScot is in a position to deliver?

I think NatureScot is the obvious body to undertake the regulatory function. I cannot think of another public body that could take it on board. It currently operates a general licensing scheme, so it has experience of managing licences. I very much concur with what Professor Reid just said. In my view, licences of up to five years on a rolling basis would be welcomed. I am sensitive to the concern about the bureaucracy and the costs involved, so I think it should be as light touch as is commensurate with the effective delivery of regulation.

Perhaps I should point out the nature of the remit that we had as a review group. We have been focusing entirely on licensing thus far, but licensing was only one of the possible options that we explored. Given the wide-ranging nature of our review, which was to look at more sustainable management of grouse moors in the round, we did not zero in on licensing in great detail, anticipating—as Professor Reid said—that, should this come to this stage where legislation was being proposed, a whole new set of questions would emerge, hence your questioning. Our review was very wide-ranging and triggered a number of quite separate conversations and discussions.

Without second guessing what SNH—or NatureScot—might do, do you have any views about the choices that it faces in terms of licensing? You said that it should be light touch. What is the scope of the options that you feel we should be considering?

I think it will build on its experience of operating general licences, which it has done for a number of years now. I have confidence that it has the professional capacity to undertake this. As a public body, it clearly needs to be concerned about the public perception of how it operates. If it were to be unduly heavy handed, that would not serve it well. It has to negotiate an understanding with landowners. The vast majority of grouse moors are well managed. We are looking at a very small minority where raptor persecution is a major concern. With good will on both sides, I think it can negotiate a system that is effective but not unduly onerous.

On the light touch, Professor Reid, you said back in 2020 that licences would more or less be approved automatically. How do the licence application tests at proposed new section 16AA(1) and (2) compare with the vision that you had on the light touch? Could what we have in the bill at the moment be improved?

Bills can always be improved, whatever they are. In any licensing scheme there is a choice to be made between rigidity, which gives you clarity and certainty, and flexibility, which inevitably involves a degree of discretion and uncertainty. The choices that have been made here are not to have a particularly rigid system where there is a checklist—you do this exactly and you get a licence; you fail to do it exactly and you do not get the licence, or you get your licence taken away or suspended or whatever.

In an area where the scientific evidence is uncertain and changing, where the natural environment is always changing, and where you are dealing with enterprises of a vast range of size, scale and nature, I think that having flexibility is almost inevitable and is the best, fairest and most proportionate way to operate a licence system. With anything else, you would have to have rigid tests, and one size would not fit all, certainly given the changing climate, the changing natural environment and the changing understanding of the pressures on it.

I can quite understand why some people are concerned about the uncertainty of this, the breadth of the test and the fact that it is not fully defined, but the alternative of having something much clearer would pose equal, if not more, problems. As Professor Werritty said, we are relying on a public authority that is subject to internal controls, appeals, external controls and, ultimately, ministerial control, to make sure that it operates the system in a sensible and proportionate way.

Given the gravity of the consequences of losing a licence and the other legislation in place—the Wildlife and Countryside Act 1981, the Protection of Badgers Act 1992 and so on—are there safeguards in the legislation at the moment to make sure that we do not potentially see licences being lost for what could be a minor offence? Do we have flexibility but also safeguards?

The appeal mechanism provides a safeguard. There is also the potential for judicial review eventually, ministerial control and the ombudsman, but it is a matter of choice. If you have an absolute checklist and there are items on the checklist that you cannot prove one way or another, there will have to be flexibility. That means giving discretion to public authorities, but our entire public administration system depends on discretion being in the hands of licensing bodies, Government grant-awarding bodies and so on. There are remarkably few situations where you are absolutely entitled to certain licences and so on. There is always an element of discretion.

Professor Werritty, coming back to the point that you made, the discussion has focused very narrowly on licensing grouse moors, and clearly your report goes much wider than that. I think that you considered at some point the power to impose fines on grouse moor managers in the same way as the Scottish Environment Protection Agency would have the ability to impose fines. Was that in addition to licensing or was it a separate thing? Are they two different things, or did you think that both of them would work together?

In addition to the review group, I had four special advisers assisting me. One of those was a senior official from SEPA who manages its regulatory controls, particularly on discharges into water bodies. Picking up on how that operates, I thought there might be an analogous situation in terms of licensing grouse moors. SEPA issues permits to discharge into watercourses, controlled in terms of the specified pollutant or whatever is going into the watercourse, and it has the ability to monitor that and charges a fee for so doing. I am particularly picking up the point that there is income recovery for SEPA from that activity. I notice that, in the bill as drafted, there is no mechanism for cost recovery by NatureScot. My understanding is that NatureScot at the moment does not seek to recover the costs of issuing licences. I wonder whether it would be wise to revisit that, following SEPA’s experience.

My concern is that, at the end of the day, compliance is crucial to the success of this whole enterprise and one has to monitor that compliance. If NatureScot does not have the resources, either via gathering a fee from a licence or from an increase in its Government grant, I am very concerned that it may not be able to monitor the performance of this bill, should it become an act, in an effective manner. That was the context in which I thought the SEPA experience might be an interesting one.

Correct me if I am wrong—I may be misinterpreting or misunderstanding you—but, if you were going to fine somebody because they had done something on the grouse moor or on the land that would be subject to a fine, you would need a burden of proof to do that.

Yes.

Given that the licensing scheme has the potential for an investigation and suspension of the licence, does the fine element of it make it a lot harder to retrieve any money? Would there be more cost in trying to get the burden of proof to a level where a fine could be imposed?

I do not quite follow you.

If I could come in, I think that there is—

I am possibly misunderstanding.

09:30  

There are several different issues here. The Regulatory Reform (Scotland) Act 2014 created a system of what is generally known as civil penalties or civil sanctions. When somebody has a licence, one of the responses to discovering a breach can be to use the powers, as in this bill, to suspend or revoke the licence or modify it so that you put in extra conditions that make future behaviour different. In some areas of environmental and other law, the regulatory body has the power itself to impose a fine—either a fixed fine or a variable fine—or to take an enforcement undertaking. A whole range of sanctions are provided for in the 2014 act. Those are not being copied here. There may be a question as to whether they should be, but for those, as you say, there still has to be a burden of proof. The Scottish legislation has generally used the civil burden of proof as the basis for imposing fines but, as always, it is subject to appeals and later controls.

One option in this bill would be that, when NatureScot or the ministers find things are going wrong, rather than being forced into considering whether to suspend or revoke the licence, knowing the major consequences that that would have for the enterprise, they could consider whether to impose a penalty. You are then faced with a further question: for what sort of breaches is that appropriate? Again, you will have endless arguments over these things. I am sorry if I am sounding very uncertain about this, but in designing a regulatory scheme there are all these choices to be made. It is about trying to think about all the circumstances that will be relevant. What will make sense, what will be practical and how the different bits fit together is complicated. There will never be one right answer. There will be plenty of scope for argument on all the different bits and how they fit together.

You have definitely added more questions than answers, that is for sure.

I am sorry. That is the job on this side of the table.

I will bring in Rachael Hamilton to ask, I think, the last question on licensing for a few moments.

Professor Reid explained the situation pretty well, but I want to get some clarity on the suspension of licences. The bill includes proposed powers for NatureScot to suspend licences even if it is not satisfied, in relation to the civil burden of proof, that an offence has been committed. Of course, there would be an official investigation relating to the person who had been accused of committing an offence. What are your observations on proposed new section 16AA, if you have had an opportunity to look at it? Do the proposals contain a lower evidential bar to suspension than was envisaged in the Werritty report?

We did not get into the detail of envisaging what the bar for different interventions would be. I can see why that provision has been included—it has been included to enable quick interim action to be taken when there is perhaps not a complete case but strong indicative evidence. That may be useful, and it is, of course, a power that only “may” be exercised. I cannot imagine the power being used in many circumstances, but it has been included to cover situations in which a formal investigation will take a long time—getting to the stage of a prosecution certainly takes a long time—and there is a desire to intervene more rapidly. It is a fairly strong power, and I envisage it being used very rarely, if at all.

In a previous session, stakeholders said that an appeal could take a long time—up to a year. With regard to your vision of how the legislation should be shaped, should sheriffs have a discretionary power to decide that a penalty imposed by NatureScot should have no effect, pending determination of an appeal?

Such provision appears in several environmental licensing schemes. The question relates to which danger we think is greater. The evidence—not in relation to grouse moors, but in other areas—is that, in circumstances in which sanctions are put in abeyance during an appeal process, that appeal process is sometimes seriously abused by people dragging it out for as long as possible to ensure that the sanction is not imposed on them. If we make it that way, the public interest suffers. If we make it the other way, the private interest suffers, because the person who is subject to the sanction is affected. It is a question of knowing whom to trust and finding that balance. I expect that NatureScot and ministers would take into account the length of time of an appeal and the difficulties associated with that when deciding whether they would be justified in suspending a licence during an investigation rather than beforehand. I see it as a very extreme power, and I cannot imagine it being used.

Do you think that an investigation should be triggered by a vexatious allegation?

If an investigation is triggered by something that is not incredibly strong evidence, I cannot imagine ministers or NatureScot deciding that that is a basis for suspending a licence, because the whole point of an investigation is to find out whether something is going wrong. I totally expect that a decision to suspend would be taken only when things were going wrong and there was a need to act immediately. If there was a single—possibly vexatious—complaint, I do not see how NatureScot could reasonably come to the conclusion that strong action needed to be taken immediately. Having read the evidence from the previous session, I accept the concerns that there are not absolute written guarantees, but that is inevitable unless we have an incredibly fixed, rigid system that cannot respond to changing circumstances and cannot respond quickly to situations that involve real problems.

The difficulty lies in whether there are serious allegations and serious evidence and the basis on which a licence can be suspended. The difficulty is in ensuring that, as you say, there are safeguards in that regard. We will move on.

I want to focus on the licensing system. We have not allowed the witnesses to explain why they came to the conclusion that it was necessary to legislate in order to address abuses. You have mentioned that the vast majority of estates operate responsibly, but what evidence led you to conclude that there is a need for a code of practice, for example? Can you give us a flavour of the incidents and evidence that drew you to the conclusion that a code of practice is necessary?

The main issue relating to grouse management is the illegal killing of valued birds of prey. Over the past six or seven decades, most other measures that might reduce such persecution have been tried nationwide, but the practice still persists. Licensing provides the next potentially big deterrent to the practice. It is the penultimate measure; the ultimate measure would be to ban grouse shooting altogether. We did not want to get to that stage, so licensing was the next measure that was open to us.

We felt that licensing would raise the profile of the activity, both to the applicant and the general public, and provide some reassurance to concerned members of the public that grouse shooting activities are being taken seriously. Some members of the public would otherwise have called for the banning of grouse shooting, which we did not want to happen.

We have already covered the other advantage of a licensing system. The current penalties rest on criminal convictions, which are almost impossible to obtain. Licensing opens up the possibility of taking much more account of circumstantial evidence and of introducing a number of penalties or sanctions of varying severity, ultimately leading to suspension or revocation. By acting largely on circumstantial evidence in relation to penalties, we move from the criminal burden of proof to the civil burden of proof.

Even though a licence might be offered for, say, a three to five-year period, NatureScot would have the opportunity to ask for annual information on things such as the number of animals killed, and the sort of animals killed, associated with grouse shooting. For example, information could be provided on the bag sizes, the number of hares, the number of predators and so on. That would give NatureScot an opportunity to learn more about what happens on grouse moors before deciding how to proceed. Annual statistics are available on most major land uses. For example, in relation to forestry, information on the number of hectares and the kinds of tress that are planted each year is readily available, and, in relation to agriculture, we have information on the crops that are grown and so on. However, absolutely no evidence on anything that happens in relation to grouse shooting is fed into central Government.

What we recommended seemed to be a way of filling that gap at no major cost to landowners. In order for NatureScot to monitor the situation, it would be useful for it to have information on the animals that are being killed, to be alerted to any unexpected changes and to follow population trends. Such information would fill an important evidence gap in relation to land use in Scotland.

For those various reasons, we were persuaded, after a lot of discussion, that licensing was a sensible option.

One of our most striking findings, which is perhaps not as self-evident as it ought to be from our report, was our key recommendation that, if raptor numbers continued to deteriorate over a period of five years, there should be licensing. That was a unanimous recommendation by the whole group, which included two members who, in effect, represented the grouse shooting sector. That implies that there is a willingness across Scotland to regard licensing as an appropriate way forward, given that, in a sense, everything else has failed. That is where we feel we are.

We looked at a number of alternatives. We looked at self-regulation, but that has not worked. We looked at accreditation schemes and financial incentives that might be introduced. We looked at a range of alternatives; we did not lightly or immediately descend on licensing as the way forward. As you can see from our report, we explored a range of options in some detail, and we recommended licensing because we thought that it was the only credible way forward. That was agreed by all members of the review group, including those who, arguably, represented a shooting interest.

Are you satisfied that the code of conduct deals with the recommendations from the review of medicated grit?

Yes. Medicated grit was an interesting area for us to explore. We recommended that there should be a voluntary code in that regard, rather than a legally binding or statutory code. Our concerns were twofold. First, in relation to the administration of medicated grit, we recommended that the grit be withdrawn at a fixed period in the year to prevent it from potentially entering the food chain. We were somewhat concerned that estates should engage with the veterinary profession to ensure that the administration is done to the highest possible standard. Secondly, there were concerns about leaching of the chemical attached to the medicated grit into watercourses. Although SEPA could not give us any clear indication as to whether that would potentially be inimical, it thought that some degree of regulation through a voluntary code of practice could perhaps improve the way in which medicated grit is used.

There was no suggestion that medicated grit should be withdrawn. We could see that it was a crucial element in the business model of grouse moor management, but we felt that a voluntary code of practice, with all estates adopting best practice, would be valuable in both those respects.

Good morning. It is interesting to hear that this is not just about the management of grouse. The convener has brought up the issue of medicated grit, and we have heard about raptors. I want to confirm whether the introduction of a licensing scheme would be the optimal way to manage grouse moors, track what is happening and collect data. I am looking at Professor Newton because that is what he has said: this is the only way forward for being able to manage or trace what is happening, rather than just having a voluntary code of practice.

09:45  

What was the specific question?

Specifically, is the optimal way forward the introduction of a licensing scheme?

As we have said, the various other methods that we could use have not worked. We are driven to the position of licensing because the other methods have not worked. However, introducing licences brings other advantages, which I have outlined, particularly the central acquisition of important data on what is happening on a major area of land, which at the moment we have little or no information on.

One of the most striking things that we discovered in our review was that the science base is heavily contested between, on the one hand, peer-reviewed journals publishing experts’ findings in the international literature and, on the other, what one could call local vernacular knowledge arising from gamekeepers and land managers. There is enormous antipathy between evidence in those two arenas. One of the things that will be a valuable outcome of the bill is that we will begin to develop a more credible science base across the whole area of moorland management. It is very striking how little we know when it comes to robust detail about the way in which the natural environment of a grouse moor operates.

We will probably come on to muirburn in due course. The muirburn literature is full of enormous contradictions and uncertainty. As Professor Newton has said, if we can assemble a much richer database as an ancillary benefit of the bill, that will advance the science. There will then be a virtuous loop that can inform adjustments to the regulatory system so that we can begin to tweak it as the science becomes more secure and firmly attested.

Good morning. Thank you for being with us this morning; so much good information has already come from your experience. You are already beginning to touch on what I wanted to get into in the meeting, which is the bigger picture in relation to land management and grouse moors, identifying the fact that we could start to create a credible science base and understand what is really going on. I am interested in hearing what you think is the potential for sustainable grouse moor management contributing to tackling the climate and biodiversity crisis. Could the bill support that?

Yes. Indirectly, it could move us in the right direction. Professor Newton will be able to speak with more authority on bird ecology and the significance of appropriate management of moorland for promoting appropriate habitat for birds. I am sure that, in a moment, we will come on to the question of carbon budgets and carbon sequestration, particularly in those parts of grouse moors that have a very thick peat layer. In how we manage muirburn and its interaction with wildfires and so on, a contribution can clearly be made in terms of the climate crisis. Perhaps I could invite Professor Newton to address the ecological aspects of your question.

Grouse moor is a fairly unique habitat and it supports a number of birds that are relatively rare by international standards. A lot of predators can be legally controlled on grouse moors, which means that the species that nest there generally nest with good success and can maintain their populations. That is not necessarily the case in many other parts of Scotland or Britain. Certain species can maintain themselves on grouse moors at densities that would not be possible in the rest of Britain, and they sustain their populations in the long term. Many species are now declining in Britain as a whole, but one of the areas where they are maintaining themselves is grouse moors, which is due to grouse moor management. There is a lot to be said for that.

A few years ago, I did an exercise in which I looked at the environmental impacts of different major land uses in the uplands of not just Scotland but Britain as a whole. I found that, leaving aside the raptor issue, grouse moors are the least environmentally damaging of all the major land uses. Forestry, for example, has destroyed much more peatland than grouse moors have ever done. It has also been responsible for a lot of acidification of landscapes, which puts it in a totally different field to grouse moors. Agriculture in the uplands, with huge densities of sheep and so on, has had a huge impact over a period of several decades in changing upland vegetation, mostly to species of plants that sheep do not like to eat, and has caused a lot of erosion and soil compaction.

As I said, looking at the different land uses, I found that the one that causes the least damage, apart from the raptor issue, is managed heather moorland for grouse. If you take out the raptor aspect, grouse moor stands up very well and the birds that live there are able to sustain good populations. It is becoming increasingly important as an area for maintaining ground-nesting open-land birds as general predators in the countryside such as foxes increase in number in Britain as a whole, which has tipped a lot of bird species into decline. Grouse moors are one of the areas where that has not happened. We have no interest in reducing the area of grouse moors.

I want to come back to the code of practice. I am interested in the idea that you are looking at the scientific evidence base and the bigger picture. Have you looked into the issue of lead shot being used? I realise that that is being phased out, but I am aware that, in parts of my region, at least historically, lead shot might be fired from what is a grouse moor but ends up being shot into trees on neighbouring land. Is there any understanding of the problems of chemical grit running into the watercourse? Is that talked about? Have we looked into lead seeping into our ground and our watercourses?

I do not know of any research relating specifically to grouse moors, but, obviously, lead shot has been tipped on to grouse moors for well over a century now. Several people have commented to me that, if you get a grouse and cut it open, you will very often find that they have bits of lead shot in their crop. Grouse, like a lot of other herbivorous birds, pick up bits of grit and swallow it to help with food digestion. The assumption is that they pick up little bits of lead shot in mistake for grit, if we can put it that way, so they are being contaminated indirectly, as are a lot of other birds in Britain. However, I would not say that lead shot is used more on grouse moors than it is on any other areas where game is shot. It is a general problem, and we need to reduce or, preferably, eliminate the use of lead shot in Britain. It is the final remaining use of lead that the public are still exposed to, and we could so easily remove it.

Good morning, panellists. Following on from Ariane Burgess’s question, does the bill support the full potential of what grouse moors could do to support biodiversity and climate change?

It is clearly not a primary driver for the proposed legislation, so I guess we have to ask whether it is supporting other initiatives that the Scottish Government is developing as we deal with the climate and nature emergency. On the biodiversity side of things, as Professor Newton has just argued very cogently, it is a positive contribution to sustaining the current level of biodiversity and not allowing it to deteriorate further. For climate change, it is a much more mixed picture.

When we come to muirburn, as I said earlier, the literature is incredibly confused. I do not know whether you have had access to a recent NatureScot report that was published in 2022, which was a meta-analysis of all the literature on muirburn. The single most important takeaway message is that we know so little about the impact of muirburn on carbon budgets, wildfire and greenhouse gas fluxes. In terms of the precautionary principle, which we have mentioned on a number of occasions, we need to proceed circumspectly with muirburn, given the lack of clear scientific evidence. The regulation that is proposed for muirburn takes the current system, which relates to a piece of legislation that was passed in 1949 and which we discovered was no longer fit for purpose. A statutory code on muirburn with all the regulations implicit within it will provide us with a very positive way forward.

I emphasise again a point that we reflected on in our report, which is the notion of adaptive management. It goes back to what Professor Reid was saying earlier about the need to provide some wiggle room in the bill and not to make it unduly prescriptive, because, as the science base develops—I emphasise that the science base underpinning a lot of moorland management is incredibly fragmented, contested and incomplete—and as the gaps begin to be filled in, we can tighten up some of the regulatory models and adjust and move forward in a way that could be beneficial for both climate change and protecting biodiversity.

That is helpful. I do not want to put words in your mouth, but could we see the bill as more of a vehicle to get the full picture that we do not currently have?

Yes—absolutely.

We have two very short supplementary questions from Rachael Hamilton and Jim Fairlie.

I will try to keep my question brief. Professor Werritty, has the socioeconomic impact of grouse moor licensing been assessed adequately in this process, bearing in mind that there was no direct or indirect engagement with businesses as part of the business and regulatory impact assessment?

Yes. That was one of the major challenges that we had with our remit when the then cabinet secretary invited me to take on the review. One of the key elements of the remit was to have regard to the socioeconomic impact of any measures that we might recommend. However, we did not have the capacity or focus to drill down deeply into that area. We relied on work that had been done by a separate investigation, which was commissioned by the Scottish Government. The numbers are in our report, and I am just looking for them.

If I remember correctly, the grouse sector currently supports about 2,500 full-time jobs and generates more than £24 million of gross value added, so grouse moor management makes a very significant contribution, particularly to the rural economy. Were there to be a ban—I take that as the most draconian measure on grouse shooting—that would have an incredibly adverse impact locally on the rural economy. Therefore, in our recommendations, we seek to protect those jobs and interests and to encourage estates that do not demonstrate best practice in how they are managed to achieve that level of performance.

I just understand this—

Sorry—we have sort of jumped to a new topic. I will bring in Jim Fairlie for a supplementary question on our previous topic, and we will then go back to the socioeconomic topic. Jim Fairlie, please come in with your questions.

Professor Newton, I will come back to you. Something that struck me when you were talking about predator control and the effect that that will have on particular species of amber/red-list ground nesters, are you saying that the management on a grouse moor is helping to sustain those red-list type birds such as golden plover, redshank and snipe? Are they in better health on grouse moors than they are on unmanaged places?

That is exactly the point that I am making. As far as we can judge, the populations, for the most part, are good and self-sustaining on grouse moor areas, whereas in most areas elsewhere—not everywhere; I cannot speak for everything—they are declining, and they are declining mainly because they are not producing enough young to offset the usual mortality rate. Most of that poor reproduction, at least on the uplands, is due to predation. On the lowlands, you also have agriculture.

10:00  

Is it predation across the board, from mammals and particularly corvids? Corvids are particularly good at finding eggs.

The predation comes from all the ones that take bird eggs or young chicks, which are the corvids, foxes and mustelids such as stoats. They are probably the main ones, along with badgers in some areas.

Jim Fairlie, do you want to continue with exploring rural businesses and European convention on human rights considerations?

Yes. Professor Werritty, are you aware of any concerns that have been raised by stakeholders that the provisions in the bill on licensing may not be compliant with the ECHR, for example, due the potential of disproportionate interference with property rights?

I defer to Professor Reid on this one.

Any time that you are interfering with businesses and property rights, you could potentially fall foul of the ECHR. The question is, is it a proportionate interference? There are various elements to that. First, is the reason that you are interfering a legitimate one? The European Court of Human Rights and our own legislation made it clear that environmental protection is a legitimate reason for interfering, so you are over that first threshold. The question then is whether the detail of the interference is proportionate or not. That brings us back to the discussion that we had earlier about the precise details of the licensing scheme and how it operates. If the legislation were wide enough to allow a very extreme strict/harsh intervention that would fall foul, just because the legislation allows that to happen does not mean the legislation itself falls foul of the convention. It is a question of how it is operated in practice, and that means looking at the legal tests, how they are operated, how those operate with the various controls, redress mechanisms and so on.

I can see the legislation, as drafted just now, operating in a way that would be perfectly compliant with the ECHR. I can also see it being operated by a rogue NatureScot or a rogue minister in a way that would cause severe problems. I do not think that imposing the requirement for a licence in itself will fall foul of the convention unless the hoops you have to go through to get a licence are absolutely absurd.

Let us presume that the hoops are dead easy, you just apply for the licence and you get it. I think that you were suggesting that a heavy-handed NatureScot person could impose certain restrictions. At what point does that breach ECHR?

Sadly, the answer is when it is disproportionate. I am trying to think of an absurd example. Say the code of practice recommended people did not wear sunglasses when out shooting, because it affected their vision, and it was found that on one occasion one member of a shooting party had worn sunglasses and the result was, “Right, your licence is revoked.” That would be a clearly absurd use of it.

Can I put one further example that has been put to me? As a former sheep farmer, I may have had the desire to shoot a white-tailed eagle because it was lifting lambs. I would be fined and possibly imprisoned, and I would face the full force of the law, whatever that happened to be, but I would not be stopped from farming sheep. If I am a grouse moor manager and I do something and the licence is removed, I am effectively stopped from carrying out my way of making a living. Would that issue fall under the ECHR?

I could almost guarantee that that would go to the courts and you could never guarantee what the result would be. Although you would be stopped from grouse shooting, you would only be stopped for a time; it would not necessarily be a lifetime ban. The question would be whether there are other uses of the land at all. I am sorry—I apologise for all the lawyers. Proportionality is by its definition a rather vague test. It is a question of looking at all the factors and weighing the public and private interest factors together and allowing regulatory bodies an element of discretion.

This will be interesting.

If you keep thinking, life will throw up an endless range of circumstances, some of which will be absolutely in the grey area. This is exactly the sort of thing we try to think up when making problems for the students to get them to answer this way or that, without caring what the answer is. As a teacher, the argument is what you are interested in.

I am conscious of time and I would like to go on to wildlife traps, but I have a brief supplementary from Rachael Hamilton.

That is generous of you, convener. Thank you.

Going back to my original question, page 16 of the BRIA states that the Scottish Government has not consulted on the impact of licensing on businesses either directly or indirectly. Bearing in mind what you said about the challenges around determining the socioeconomic impact of grouse moor licensing, would you have expected the Scottish Government to have done that as part of the BRIA?

Speaking purely personally, that would seem to me to be something that it should have done. This whole area is problematic because we know so little about the socioeconomic impact of grouse moor management. As I mentioned earlier, the Scottish Government commissioned a separate study. That study, I have to say, was imperfect in a number of ways, not least because of the challenge of obtaining the appropriate data, for obvious reasons. There are elements of commercial confidentiality. It is, in fact, difficult to drill down into the socioeconomics of grouse moor management. There is a bit of an impasse here. We do not know in detail much about the socioeconomic impact of grouse moor management. Clearly, if the bill is to be well informed and evidence based, we need to get that additional information. I am not sure how that comes about. One of the frustrations of my review was that this area, which we were charged to give due regard to, was problematic because the evidence simply is not in the public domain other than the separate report that I mentioned, which we found imperfect.

We will now move on to wildlife traps with a question from Alasdair Allan.

Can you explain a little bit about how you came to the conclusion that there was a need for a new regulation around wildlife traps? Are you satisfied with what the bill has done in terms of making your recommendations real?

I ask Professor Reid to speak on this one.

We know that trapping and snaring is a long-running and controversial issue. There are problems with the misuse of traps. By introducing a licensing system, the hope is that the professionalism of many gamekeepers and land managers will be recognised and they will have the reassurance that they can defend themselves there. In speaking to the public they can say, “We do it in the proper way, which has been properly assessed, using the relevant traps in the relevant way.” The law on trapping and snaring has been a bit of a mess because it has been rather inconsistent, so anything that tries to make it simpler by drawing things together is good.

The experience has been that the requirement for training and the requirement for visiting traps and snares has reduced the misuse problems with animal cruelty. It seems sensible to try to have greater consistency and greater controls to make sure the abuse is not happening while giving this form of reassurance that professionally operated traps can be used.

Can you say anything about numbered traps?

Again, we did not look at the details of that. I have seen the varied evidence on that both ways. It is clearly incredibly helpful to be able to identify who is responsible. We drive cars that have licence plates, so we know who is responsible for a motor vehicle and therefore who has a stake in it. On the other hand, I understand the fears of some of those in the industry that it may lead to identification of people and harassment.

Given the grave consequences of the inappropriate or illegal use of traps—again, we are looking at the consequences of potentially losing a licence or whatever—are the concerns that we have heard from land managers well founded? Should there be a specific piece of legislation on tampering with traps to ensure that we do not get any more vexatious claims from someone with the wrong intent taking a tagged trap, setting it in an illegal manner and then calling the police, resulting, perhaps, in the loss of a licence? What are your views on a specific new criminal act with regard to traps?

Such activity is already criminal under malicious mischief or possibly vandalism; the question is whether it merits a separate crime. Indeed, this is another long-standing issue in many areas of law. On the one hand, there is value in having a specific crime that signals that a particular form of behaviour is unacceptable, but on the other, you then end up with endless layer upon layer of crimes, which makes it harder to understand what is going on and enforce and so on.

In one sense, about half the crime in Scotland could possibly just be dealt with as breaches of the peace, but we want separate named crimes that deal with different things for a variety of reasons. The question is whether one thinks it important to have a public signal of a specific named offence to justify criminalising something that is already criminal. There are lots of examples of activities that are already criminal where another crime gets put on top for policy or public signalling reasons. Depending on your view, that is either a helpful and useful function of the Parliament or it simply creates unnecessary complications.

I will not repeat the law that you stated that people who tamper with traps might be convicted of, but the fact is that there is a low rate of convictions from using that piece of legislation. From what you have said, it would appear that a specific law on tampering with traps might have a positive effect.

I am not convinced that it would, because you would hit exactly the same problems that you have with raptor persecution with regard to gathering the evidence. It has been suggested that the number of reported wildlife offences is a lot lower than the number that occur in reality, and I am sure that it is the same with tampering. From some of the evidence I have heard in other contexts and in the Werritty review, it certainly seems that gamekeepers and landowners are telling people that this is happening but they are not reporting it to the police. If they did, you would face exactly the same problems of finding the evidence beyond reasonable doubt in rural and remote areas.

I call Rachael Hamilton, to be followed by Jim Fairlie.

I do not have a question just now, convener.

Okay. I call Jim Fairlie.

My question has been asked, convener.

That is grand. We move on to muirburn and questions from Rhoda Grant.

You talked earlier about the science around muirburn and whether it was beneficial and what the impact was. Why did you come to the conclusion that it should be subject to increased legal regulation?

The current system is a voluntary code, and our experience is that it is not working. We were presented with evidence, particularly from the Cairngorms national park, of wildfires that were perhaps associated with out-of-control muirburn. Our starting point was that the current system was broken and that we needed to move from a voluntary to a statutory code. Regulated and well-conducted muirburn, as Professor Newton has indicated in his comments on upland bird ecology, can be positive. It is important that muirburn is conducted in a way that complies with the code, meets the regulations imposed and can be properly reported.

Another issue that we are concerned about goes back to a lack of evidence on how moorlands are managed. Under the code, it will be necessary to report where the muirburn is taking place in addition to all the other permissions that will need to be gathered in advance.

A statutory code for muirburn is therefore a major positive step forward. Perhaps Professor Newton can say a bit more about the impact of muirburn more widely.

10:15  

It is important to realise that muirburn is central to the whole issue of driven grouse management. If you could not burn heather moor, you would not get the densities of grouse that you get with burning. The idea of burning on grouse moors is, as you probably know, to burn it in small patches; each pair of grouse will have, in their nesting territory, some patches of short heather, rapidly growing heather on which it can feed and long heather in which it can take shelter from predators or nest. That is the reason for the small patches of burning that you will see on grouse moors.

Generally, the burning happens on a 10 to 15-year rotation, so it is not that frequent, and it creates on grouse moors a structure in which patches of ground have different heights of vegetation. That is important in increasing biodiversity, as some animals will live in the patches of low vegetation and others will live only in the high vegetation. If you were to burn the whole lot in one go, the ground would be absolutely uniform. The environmental impact of burning on grouse moors is therefore lower than it would be if you were burning much bigger patches.

The other advantage of that patchy burning—or strip burning—is that it provides a firebreak, which ensures that any accidental fire does not spread quite as rapidly as it otherwise would. Of course, the other advantage of fairly frequent burning is, as I am sure you have discussed already, that it prevents the build-up of a lot of dry trash that would create a really hot fire that could get out of control.

It is interesting to look at all the well-known cases in recent years of fires getting out of hand and burning many square kilometres in one go. All of them happened in summer. As they were outside the proper burning season, they were not the result of controlled burns. In fact, all the big fires have happened in areas that have not been burned for several decades, which means that there has been a huge build-up of dry trash on the ground that has got the fire going. It is mostly under those circumstances that we have cases of fires penetrating deep into the peat, which is where the problems start.

With most of the controlled burning that is done more frequently—that is, every 10 years or so—the ideal is to get the fire spreading rapidly in what is called a cool burn. Such a fire does not last long; instead, it sweeps over the ground without penetrating the peat below it, which is from where most of the carbon would be released.

Obviously that has the benefit of stopping the sort of wildfires that we have seen quite recently and the resulting devastation, but how do we get that kind of land management—or at least the kind of management that stops wildfires and the damage that they cause? How do we replicate that elsewhere outwith grouse moors?

I would imagine that the rest of the burning is carried out on land for agriculture such as sheep-grazing land in the upland. If you are burning, you need to make sure that firebreaks are always on hand if anything goes out of control, and you should not burn every year. I remember that, in the 1950s and 1960s, a lot of sheep farmers were burning every year, which is too frequent. However, you need to control things in some way or other by, say, having firebreaks and preventing the build-up of trash over a number of years.

So, as well as having licensing, should we also be saying to landowners that they need to control the risk of wildfire on their land, too?

Yes. Landowners—or, at least, the ones to whom we spoke—are all conscious of the risk of wildfires. The management of fires in general, at least on grouse moors, has improved enormously over my lifetime. For example, when there is a fire, a lot of land managers will now take water up on to the hill—they will tow it up in a trailer—so that they have water on hand; there will also be enough men around to keep it under control. A lot of the controlled fires that got out of hand happened due to insufficient manpower, the wrong weather conditions and so on.

The code of conduct has helped a lot in this respect. My impression from our meetings with landowners is that they were much more conscious of muirburn than they used to be and were doing it correctly for their own benefit, apart from anything else.

Alasdair Allan has a brief supplementary.

In some of the evidence that we have taken and some of the things that we have looked at, there has been a concentration on the proposed distinction between peatland and non-peatland areas and on questions relating to the 40cm figure for peat depth and all the rest of it. From what you are saying, I am trying to get a picture of whether there is evidence that muirburn per se is responsible for the kinds of fires that you are alluding to, where peat burns on the hill, or whether this is an entirely different type of fire that we are talking about. Is muirburn a factor in the type of fire in which peat burns on the hill?

It is bound to be a factor in that, occasionally, you will get a controlled burn that will get out of hand to some extent. In the past, some of those burns might well have led to local peat fires. In general, though, such fires have not had the sort of impact that the wildfires have had in recent years, simply because of the amount of stuff that can burn and the length of time that the fire rages over an area.

Inevitably, if you are burning vegetation, something is going to get out of control sooner or later, and you just have to make sure that you have the equipment and the manpower on the ground to stamp it out as soon as possible. During our interviews for the review, we learned that landowners occasionally had controlled fires that got out of hand, but generally they brought them under control themselves without the need to call the fire brigade, just because they were prepared for it. That sort of thing has improved in recent years.

I call Karen Adam.

What are your views on the proposed licensing system for muirburn? Do you feel that it meets the needs of the review’s recommendations?

I think that, broadly, it does. As we have repeatedly said, we did not in the review drill down to the level of detail that we are now scrutinising at this legislative phase. Our strongest recommendation related to the fact that the existing code, because it was voluntary, was not proving effective. The existing code is well constructed, by and large; however, we felt that, because it was purely voluntary, it had loopholes, and there were occasions when non-adherence to it had produced the problems that we have been speaking about.

As far as I am aware, we do not have any details of what the proposed code might look like yet. Presumably, it will emerge at a later stage in the legislative process. If it follows the existing voluntary code, with suitable tweaks and adjustments, I will regard it as meeting our recommendations.

I do not know whether Professor Reid has any thoughts on this.

There will be the same challenges that arise with designing any licensing system. How much flexibility will you have? Will you have rigid requirements and conditions? It will be exactly the same sort of debate.

It appears that most of the peat damage is done when fires get out of control, whether they be wildfires or whatever, so it seems quite strange to impose regulations that are based on peat depth.

Following on from that, Professor Werritty, your report suggests the need for an increase in regulatory control relating to the muirburn code. Do you think the bill’s provisions in adequately address that?

I am satisfied that the regulations as currently written in the bill deliver on what we recommended.

Okay. Thank you. Rachael Hamilton has a very brief question.

Professor Newton, you have described the habitat benefits of muirburn. With regard to the questions that Alasdair Allan and the convener have asked and the issues of peat depth and cool burning, should there be a single licensing scheme rather than two schemes, one for peat depth under 40cm and the other for peat depth over 40cm?

I do not know. I would be happy if there were one licensing scheme to cover the lot, but with regard to this magical figure of 40cm—or 30cm or 50cm or whatever it might be—that is a difficult question to answer, because we just do not know. If you were to lower the figure by 10cm or raise it by 10cm, for example, we would have no idea of the acreage of land that would be affected. The more that you lower it, the more land will be taken in if you, for example, ban burning. If you dropped the figure by, say, 10cm or 20cm, how much acreage would that cover? It is a difficult question. To my mind, I can see the value of having a definite figure such as 40cm, 30cm or whatever, but it does not really tell you all that you need to know, which is who will be affected and over what sort of area.

This is an example of the difficulty of having, say, one licence for muirburn wherever it is and assuming that the licensing body will reflect differences in peat and so on in that licence. It brings us back to things being flexible and uncertain. I can see that having a specific requirement in the bill is an attempt to provide greater certainty and greater knowledge, but we can also see the problems that it will give rise to. Is it appropriate to have it at all? What should the measure be?

We come back to the issue of there being two sides to the coin. Precision and certainty have their advantages, but flexibility and discretion have their advantages, too.

And what about the scientific data?

There are opportunities for the scientific data to change. That is why the bill specifically provides that the figure can be changed to reflect the fact that the science on this is developing.

I will take a short supplementary from Emma Harper, and I will then bring in Jim Fairlie.

My short supplementary is about training and education. Professor Newton, you described the complexity of muirburn, with small patches being burned and the fire being managed to make sure that it does not get out of control. Should the issuing of licences be correlated with a requirement to provide education and training for our gamekeepers and land managers?

We made such a recommendation in our report. If you are going to have a code that will be strongly adhered to, you will need to ensure that all the personnel involved are up to speed with best practice. Training—and, indeed, updating that training from time to time—will therefore be quite important. We see training of key personnel as a fundamental part of the proposed code, and we very much hope that it will be included.

I should say that such training should cover all aspects—not just muirburn, but trap operation, employment of medicated grit and so on. A good background of training is needed for everything.

I call Jim Fairlie, to be followed by Beatrice Wishart.

Professor Reid, I want to come back to what you said about licensing and the figure for peat depth, whether it be 30cm, 40cm, 50cm or whatever. Among the current weaknesses of the muirburn code are that few of its provisions incur penalties and there is no robust system of monitoring and compliance. Given that we are now about to put something else in place, does the bill provide solutions to the issue of compliance? Are there robust enough penalties to ensure that that happens?

You will need a licence, and serious non-compliance with the code will be a ground for revoking, modifying or suspending it. As we discussed with the grouse shooting licences, there could be scope for financial penalties as an alternative remedy. With the requirement for a licence, the code moves from being something voluntary, under which there are absolutely no sanctions for ignoring it, to something that, if ignored, will put your licence at risk.

The third step is to say that breaching any provision of the code will, by itself, become a criminal offence. However, there are huge problems with that, as it would overcriminalise things. The code would have to be written in a way that would allow you to judge in black and white whether an offence had been committed.

The current position, therefore, is appropriate, subject to the possibility of there being scope for fixed penalties if, for example, you did not give adequate notice to your neighbours. Perhaps it might be more appropriate to have a fixed-penalty notice for that sort of thing instead of ministers or NatureScot not granting a licence the next year or simply revoking it. Having those more minor sanctions might be appropriate for minor breaches.

Would that also not require NatureScot to be able to go out and measure the depth of peat?

For peatland issues, the measuring is a problem, yes.

I call Ariane Burgess.

10:30  

I would be interested in hearing whether you feel that the recommendations on muirburn have been addressed in the bill and whether there is anything else that you would like to see in it. For example, in your review, you recommended increased training, which you have already addressed with my colleague Emma Harper. You also recommended that a fire danger rating system for Scotland should be introduced to better support decision making about where and when to burn, and that the Scottish Government should explore changes to the current rural payments and inspections division payments. It might not be appropriate to deal with those recommendations in the bill, but how do we ensure that they are dealt with? Is there anything else that you think should be addressed in the bill?

I am very much of the view that those issues are not appropriate for a bill. They are policy matters that should be pursued with the Government through the stakeholders and this committee and others.

On muirburn, is there anything else that you think needs to be in the bill, or are you content with it?

On muirburn, until we see exactly what the code will cover and what it says, it is a bit hard to say. However, the bill creates a structure or framework that is adequate and meets the requirements.

When we were talking about wildfires earlier, I picked up that we need to follow the precautionary principle. The desire to move from a voluntary practice to a regulated and licensed practice is because we will potentially see more wildfires happening. Maybe that will be from natural causes, but my understanding from talking to people who work in that area is that wildfires are always at the hand of a human, whether it is in error or by intention.

I picked up from what you were saying that, as wildfires increase, we will need to increase the workforce and the equipment that is on hand to attend to those. Regulating muirburn is a way of moving towards a more precautionary approach so that we limit what might happen in other areas. We have already seen, with the fires in Cannich and Corrimony, that deploying people to attend to the fires is quite challenging.

I concur with what you have said. That is the right direction of travel.

Before we move on to the last couple of questions, can I have your views on the presumption against muirburn and why it should be the last management tool, given what you have said about control of wildfire and improving species habitat?

Also, do we need more accurate data on peat depths—to 50cm rather than 40cm—before we bring in any regulations, to give land managers a little bit more certainty?

The problem with peat depths is that I understand that the existing map is based on a depth of 50cm. Therefore, if you migrate away from that, you clearly have a challenge in how you determine peat depth, although there is commentary on the bill about ways of dealing with that by using probes over, say, squares of 100m by 100m.

It would perhaps be good to have the James Hutton Institute give us more detailed information on Scotland’s peat soils, particularly seeing that they are so vulnerable, but it would be a major undertaking to effectively remap Scotland’s peat soils. In the interim, we will have to rely on the measures in the bill. I very much hope that NatureScot and grouse moor managers will be able to find a way of determining peat depth that is not unduly onerous in the demands that it makes on the estate managers but satisfies the requirements in the bill.

And on the point of the presumption against muirburn?

The provision that

“no other method of vegetation control is available”

sets a very high standard. It is possible that the term “reasonably available” or something like that might be more appropriate. Again, you have the problem that setting a rigid test takes away your flexibility and your ability to respond to different circumstances. People will differ on whether other control is available for rocky ground, on steep ground and so on. There can be issues. A bit of fuzziness can be helpful for operating the system.

Coming back to peat depth, my understanding is that that is an historical measurement that was used by the United Kingdom Government at the time when trying to identify energy sources. The measurement was about something different. We are looking at peat in relation to the damage that can be caused.

We have a peatland restoration initiative in Scotland in which we fund land managers to restore peat, so it seems to me that we are talking about two different things when we start to talk about depth. Peat is a continuous cover and, no matter its depth, we need to protect that in terms of our carbon emissions. What are your thoughts on that?

The soil map would have been produced many years ago and would not have had in mind what we have been talking about. Certainly peatland restoration is a whole different area that is not within the remit of this inquiry or our report.

We try to protect peat because we recognise that it is a super carbon sink. It is great that we are moving potentially to the licensing of it, but it seems odd that, on the one hand, we are funding the protection of it and, on the other hand, we are saying that it is okay to burn it, no matter the depth.

The current restoration programme is taking degraded peatlands and restoring them to as near as can be back to their original pristine condition. That often involves raising the water table and removing trees. It is a totally different agenda to what we have been talking about in terms of grouse moors. Although you can see certain parallels between the two areas, they are quite discrete in terms of the underlying science.

We need to move to an ecosystem approach and look at everything as a whole.

Yes.

Finally, you made recommendations in your review on issues such as satellite tagging, additional sentences and consolidation of wildlife law. To what extent have those have been implemented? Should those recommendations be in the bill or should they form part of a non-legislative approach? Not all your recommendations have been adopted. How would you like to see that addressed?

Perhaps I could ask Professor Newton to speak about satellite tagging, because I think that there have been some developments.

Satellite tagging has turned out to be one of the main methods that we have of monitoring how birds of prey die. It has revealed, as you know, a lot of interesting results. The bulk of the mortality in several species occurs on or near grouse moors. Satellite tagging has been a major source of evidence. It may be necessary to continue that into the future to keep monitoring the situation. It has been extremely revealing both for the golden eagles—their tagging started off this whole process—and also for hen harriers and other birds that have been tagged.

An issue that we have not touched on so far is the evidence that birds of prey suffer on grouse moors. The evidence is a lot more substantial than one might believe. It is not just finding a few carcasses on a grouse moor—that is a trivial aspect of it. The populations that live there are monitored annually by so-called citizen scientists. There are multiple strands to the evidence that things are going wrong on grouse moors. For one thing, a lot of the known territories are much less frequently occupied each year than they are on areas outside of grouse moors. Birds disappear during the breeding season. Pairs disappear much more frequently on grouse moors than they do outside grouse moors. The nesting success of the birds there is very low compared with elsewhere.

In addition, quite a lot of the breeding population of some species consists of young individuals that would not normally get the chance to breed in a bird population, but they can do so because the adult population has been reduced and territories have become available to them. The proportion of youngsters in the breeding population has grown. A lot of evidence is collected for individual species, and those are highly significant differences between grouse moor and other terrain.

Furthermore, if you have a change in the management of grouse moor, you immediately get a response in the case of the raptors—when a different manager comes in, their numbers either go down or they go up. How they manage the moor and their attitude to birds of prey is immediately reflected in what happens to local raptor populations. That is just one other line of evidence that we have.

On consolidation of the legislation, the bill is clearly a backward step, because we are talking about introducing section 16AB into the Wildlife and Countryside Act 1981. I am delighted to see that the Scottish Law Commission’s new programme of work includes consolidation of wildlife legislation as one of its medium-term plans. I would be absolutely delighted by anything that this committee and others can do to make sure that that happens and that the Government supports it.

Do you have any comments on that, Professor Werrity?

I have no further comments.

I thank the witnesses for attending this morning. It has been a hugely useful session. I will now suspend the meeting for 15 minutes to allow for a changeover in witnesses.

10:40 Meeting suspended.  

10:55 On resuming—  

Welcome back, everyone. We are joined by our second panel of witnesses: Libby Anderson is a member of the Scottish Animal Welfare Commission; Ian Andrew is chief executive officer of the British Pest Control Association; Ross Ewing is director of moorland at Scottish Land & Estates; Chief Superintendent Mike Flynn is from the Scottish Society for the Prevention of Cruelty to Animals; Liz McLachlan is from NatureScot’s wildlife management team; and Alex Hogg is chairman of the Scottish Gamekeepers Association. Again, we have approximately 90 minutes scheduled for this session.

I will kick off with the first question. Do you agree with the provisions in the bill that ban the use and purchase of glue traps, which follows the advice of the Scottish Animal Welfare Commission? Do you agree that a ban on the use of glue traps is more appropriate than a licensing system?

I am sorry, but I have no comment to make on that. The issue does not come under our remit.

It is probably appropriate to bring in Ian Andrew.

Our position is very clear: a public ban on the purchase and use of rodent glue traps is absolutely the right thing to do. However, it would have devastating results for us, as professional pest controllers, if we were to lose that tool. It is the only tool that we have for capturing rodents quickly. It is true that we have alternatives. We have biocidal products, although the lifespan of those is in question. We also have break-back traps. However, there is increasing genetic resistance to biocidal products, and there is increasing behavioural resistance to break-back traps and to biocidal products. Rats and mice are clever creatures. They understand that these things are not good for them.

If we lose the only tool that we have to capture a rodent quickly, it will result in increased populations, which in itself is not good for animal welfare. In addition, businesses and organisations such as supermarkets, restaurants, pubs, hospitals and schools where there are infestations will be closed for longer periods of time. At the moment, an environmental health officer who goes into a premises where there is a rodent infestation will want to see three clear instances of no capture on glue boards so that the premises can reopen quite quickly. Biocidal products take approximately two weeks. That is two weeks of businesses being closed before they can be reopened. With break-back traps, it can take many days before rodents will go anywhere near them.

The glue trap is just a method of capture. If the rodent is not on the glue board for a considerable length of time and is then humanely dispatched, the position is more favourable from an animal welfare perspective than it is with biocidal death and death caused by a break-back trap. Of course, the issue with glue traps has been misuse. Mike Flynn’s team has found instances of glue traps being put outside buildings. I cannot think of any conceivable excuse for a glue trap to be deployed outside a building. Internal use for high-level infestations in high-risk areas is the only way of capturing it.

In response to the financial memorandum that goes alongside the bill, we made the very conservative estimate that, if glue traps are banned, that will have an impact of about £22 million on the Scottish economy every year through the closure of businesses. That represents half of all restaurants, shops and supermarkets being closed for a week once every 30 years. That was very conservative. That would have £22 million-worth of commercial impact on the Scottish economy. It is absolutely the case that animal welfare is critical, but that has to be balanced with public health.

11:00  

Are there any other comments? Libby Anderson.

Clearly, I am a member of the Scottish Animal Welfare Commission, which provided the report on the basis of which the Scottish Government formed the view that it would go for a full ban. To explain the history of the report, we took evidence from many stakeholders, including Ian Andrew’s organisation, the pest control industry, animal welfare advocates and environmental health and enforcement organisations, and we considered all of that seriously.

First, nobody disputed—I am grateful to Ian Andrew for agreeing with this—that glue traps cause severe and generally prolonged animal suffering. The wide view is that that is at a level that is so unacceptable that an outright ban is now justified. I could go into some of the detail of the injuries, but you may not need that.

In our reasoning in the report, we took into account the public health risks and the severe animal welfare consequences, and we looked at other models. For example, in New Zealand, a strict licensing scheme, which involves ministerial approval for the use of any glue trap, was brought in in 2015. In the past year or two, the number of approvals has dwindled down to zero. We accept that there is a different demographic and a different pattern of living in New Zealand, so we are not necessarily comparing like with like, but with the approvals literally at zero, we can see that that system is effective in many situations.

The other thing that we did in our report, while saying that the animal welfare issues merited a full ban and that public opinion would back that, was to set out a potential fail-safe licensing scheme, which would be specific, case by case and for a limited period. We offered that as a potential alternative that might see us through the period while further developments arise in technology and science. I know that the industry works with scientists and is keen to develop it, and I know that the industry acknowledges the suffering.

On the point that Ian Andrew made about glue traps being relatively quick, the industry code requires traps to be inspected twice daily—in other words, that could happen 12 hours after an animal had been trapped in that horrible and painful situation. To require almost immediate inspection would be so onerous on the industry that that would be difficult. It is a question of balance. The commission’s view was that an outright ban is justified, and we are pleased that that is the approach that the bill takes.

I have a couple of questions. Out of curiosity, what is a glue trap and how does it work? It sounds ridiculously simple, but what is it and how does it work?

It is a piece of board covered in glue. Typically, you would form a barrier. Let us say that there was a rat running around at a supermarket. You would identify where the point of ingress was and you would form a barrier so that the rodent had to cross the glue trap and they would get fixed to it. In the worst case, that would be for 12 hours, but from a BPCA perspective, we are happy for our members to stay on site so that the period is nowhere near 12 hours. The glue trap catches the rodent and then it is humanely dispatched, usually by blunt force trauma.

Libby Anderson said that, in New Zealand, the level has dwindled down to zero. How has New Zealand managed to go from using glue traps to not using them?

That is comparing apples with pears. We have near pandemic levels of rodent infestations, particularly in the city centres of Edinburgh and Glasgow. The populations are different. In New Zealand, the rodents have no genetic resistance to biocidal products. There is no research on this, but it would appear that there is little evidence of behavioural resistance to traps in New Zealand. It is a different standard. They do not have the big cities that we have. Population levels of rodents are much less significant in that country.

In other countries, other methods are used. For example, in Europe, the drowning trap is effective and popular, but it is illegal in this country.

How does our population of rodents compare with those of other countries? Do you have like-for-like figures?

I am sorry, but there is very little data. There has been a lot of press speculation about an increased population, but it is probably more the case that there was a change in the behaviour of rodents during lockdown, for example, when takeaways and restaurants were closed, which meant that they had to forage in other, more domestic environments and urban environments. However, it is hard to say what the actual numbers are.

Another measure that could be looked at or a methodology for working out the size of the population could be the number of operators who have been called out to various institutions, such as hospitals and supermarkets, which has increased. I do not want to cause alarm among the public, but you have indicated that we have a growing problem with rodents. It would be good to get some understanding of how you have come to that conclusion.

Our members are busier than ever and are getting increasingly busy. It is not just rodents that they are dealing with, and there is a high level of seasonality, but they are getting busier, so they have an increased number of pests to deal with. To be absolutely clear, if glue boards are banned, my members will do much better commercially, because it will take much longer to get a rodent infestation under control. For my members, if glue traps are banned, their businesses will boom.

There is little by way of specific data on volume. It is mainly anecdotal. Some research was done recently that included Scottish local government call-outs. That would indicate that there was a slight increase. Of course, most local authorities deal only with local authority housing stock; they do not deal with takeaways, hospitals, supermarkets and so on. Sadly, there is no tangible data.

What is your understanding of the current extent of the use of glue traps in settings such as hospitality and hospitals?

Thankfully, it is fairly rare, but, if there is an infestation in a high-risk area—particularly a food environment, for example—the food safety legislation has to be adhered to. There is a risk to public health and therefore the rodents need to be dealt with swiftly. My technical manager, who was a pest controller for 15 years, used them twice in her career.

Again, there will be geographical differences. For example, on the Byres Road in Glasgow, I suspect that they are used daily, because there is an endemic problem. Despite the Prevention of Damage by Pests Act 1949, which allows local authorities to take a much more global approach to pest control, rats and mice move from one premises to another and from one building to another. There is no real block approach to rodent control. Each takeaway will have its own pest control company or will do it themselves. Better use of the 1949 act would make control much more effective.

Are you saying that there would be public health implications if glue traps are not used?

Absolutely. I am not sure whether the committee is including the Royal Environmental Health Institute of Scotland in its research.

I am not aware that we are. It is not taking part in any of the witness sessions.

On that theme, I wonder whether, in coming to a view about banning glue traps, it was envisaged, discussed or debated what that transition would be to, given what Ian Andrew has said. What is the transition to, in schools and hospitals?

We have to hope that the industry will continue to work to develop improved traps. Electric traps, for example, are not well distributed around the country. New traps are coming along all the time. When we talk about spring traps later, we may consider those as well. That is being developed all the time.

I hear Ian Andrew’s point that rodents do not readily go into new traps. The conventional solutions are things such as improved proofing and prevention. No doubt, many pest controllers will come along and do that or advise people to do that first of all. In an industrial or health premises, that work would have to be on-going constantly. On rodenticides, we know that anticoagulants are pretty cruel, so we cannot just say, “Use those, and that will be fine.” You do not generally see the animals that have died as a consequence of that but, if you do, it is not attractive.

The commission was aware of potential unintended consequences, which is why we wanted to give it time. However, the overwhelming weight of evidence about the suffering that is caused by glue traps led us to believe that they had to go. Certainly, everyone agrees that they should not be used by the public.

Perhaps it is not in your remit to say what the alternative is, but that is the big question that we are all considering. What is the alternative for a hospital?

There is no one solution. It would not be correct to say that we can recommend an alternative. The notes accompanying the bill state that 11 of the 14 local authorities that responded to the bill said they do not use glue traps. Many organisations do not use them. Ian Andrew mentioned that they are little used in the industry, which I am pleased to hear.

It seems to me that it is feasible, given the overwhelming evidence about animal welfare and the good will and productive thinking, that a couple more years should bring better solutions. I cannot tell you what they will be, but there are men of science out there, and we hope that that will be the case. That is a reasonable assumption.

It is, but hope is not a strategy. We hope that we will have alternatives but, just to be absolutely clear, at the moment we do not. The glue trap is the only means of rapid capture and, when used professionally, rapid dispatch through blunt force trauma. It is the only thing that we have. Everything else takes time. Biocidal products and break-back traps take time, which means that hospital wards and school canteens will be closed for much longer periods. The already fragile hospitality sector will probably be the first to suffer. Environmental health officers have no choice—they have to close premises until they are free from infestation.

11:15  

To clarify, you are saying that the use of a break-back trap would take much longer than if you set up a barrier with a glue trap and a rat comes over the top of it. However, you more or less know the behaviour of a rat. I get that there will be some resistance to it, but is there not a method that you can use with a break-back trap that will catch the rat? I am trying to think of the behaviour of the rat and why it is coming out in the first place. It will come out for a particular reason, and not because you drive it out. Therefore, if it will be done quickly, somebody has to be on site to alleviate the problems that Libby Anderson has talked about. If you were using break-back traps, would you not just use more of them and make sure that they were baited appropriately?

Absolutely. A break-back trap is small; a glue board is larger. You would be putting down literally thousands of break-back traps.

How many rats are you trying to catch if you are putting down thousands? I am sorry—I am not trying to be facetious; I am trying to get a picture in my head of what this looks like.

If there was a point of ingress behind the convener, for example, and that was identified as the point of ingress, although that would be nothing to do with the convener being there—

That did actually happen once in committee many years ago.

Okay. As a barrier, in effect, a dozen glue boards would be placed around the convener so that the rodent had to cross one to get to any food source, harbourage or water. That is why they are coming in—it is for food, water or harbourage.

What is the difference between having glue traps and break-back traps in exactly the same numbers?

The problem is that a break-back trap is small, so thousands of them would need to be deployed, which is just impractical.

Ariane Burgess has a supplementary question.

I am not quite sure where to bring this in, but I want to clarify something. We are talking in detail about how and where traps are used, which is very helpful, so I thank Ian Andrew for that. I get the sense that we need to do a 360° look if we are bringing in this legislation. However, primarily the legislation is being introduced to address raptor persecution. In the policy memorandum, paragraph 13, under “Policy objectives”, says:

“The use of glue to trap birds is an offence”.

That is what we are trying to tackle here, is it not?

No, we are not covering that just now. We are talking specifically about glue traps.

I understand that, but I am confused as to why we are talking at length about glue traps, and I am trying to get clarity. We are talking about them because the bill is bringing in provisions on glue traps, but it is about wildlife management, muirburn and specifically raptor control. I want to get clarity.

The provisions that we are discussing do not relate to wildlife control; they are specifically about glue traps.

I will bring in Karen Adam.

My question is for Libby Anderson and Ian Andrew. What are your views on the proposals for a transition period?

The commission recommended that the proposed strict licensing scheme should last for no more than three years. We made that recommendation two years ago. It is fairly simple: we would like the transition to be as short as possible.

We fundamentally do not want a transition period; we want to keep glue boards, as they are the only tool that we have for rapid capture. Our members are already licensed by Liz McLachlan’s team for bird work—and for gull work in particular. We are carefully, closely and robustly licensed to do other aspects of pest control. Similarly, our members cannot purchase rodenticides without proof of qualification and, shortly, they will require proof of continuing professional development. The same applies for insecticides.

Control measures and licensing schemes are already in place that work effectively. The bird licensing is now online and it is effective. The same applies south of the border. We do not want a transition; we believe that we can have an effective licensing scheme for professional pest controllers that limits the use of glue boards to high-risk situations. South of the border, consideration is given to the training, the qualification and the CPD of anyone who is licensed to use glue boards, which is absolutely right. However, we need to keep the access to these tools. A transition will not work.

I will bring in Mike Flynn.

Thanks, convener. I want to pick up on a couple of points.

On the last point that Mr Andrew raised, not every pest controller is a member of his organisation, so they do not have that governing body. Nobody needs a licence to use a glue trap, and I am pleased to hear Mr Andrew saying they should 100 per cent be banned for general public use. I must admit that the general public have caused concerns for us. Not everybody has the confidence and wherewithal to destroy an animal once it has been caught. We have had live animals on glue traps being put in bins or being drowned. They are horrendous things to use, and they are totally indiscriminate.

Since the late 1950s, it has been illegal to use any kind of glue to trap a bird, so there is already a precedent. These things will catch anything. We have found home-made ones. With the traditional ones, you used to be able to buy them for 99p at B&M, so anybody could put one in their loft and then forget about it. We have had home-made ones that have caught foxes, and we have had gulls caught in them—they have been totally misused. That has nothing to do with reputable pest controllers, but it is just an easy way. They cause suffering. I agree that 12 hours is better than just being left there, but it is still a long time for a sentient mammal to be trapped and doing whatever to try to free itself.

On the 12 hours, we are more than happy to stay on site, if that is required. You cannot stay in the same room, because that will prevent the rodent from coming on to the glue board, but you can stay on the premises for three or four hours or whatever.

On the technology point, there is greater use of cameras, for example. Traps can be monitored remotely and, as soon as something goes on to one, the pest controller will have visibility of that. The 12-hour period is very much the extreme.

I will move on to my next question. Police Scotland has advised that perhaps the possession as well as the use and purchase of glue traps should be included in the ban. Can I ask for views on that?

I have nothing to add on that, really.

The reality is that professional pest controllers get their products, whether they are biocidal products, break-back traps or glue traps, from about half a dozen suppliers in the UK. For the public, it is a different story, but professional pest controllers use about half a dozen. For rodenticides, there are point-of-sale checks—you have to show that you have done your qualification before you can purchase them. Through our relationships with Amazon and eBay, we get things taken off almost overnight. If something is banned for public use and comes on to eBay, our relationship is such that it would be taken down immediately.

I want to pursue the question that I raised earlier. The policy memorandum mentions that the bill will bring in a ban on glue traps. It says that the bill

“is being introduced to address raptor persecution and ensure that the management of grouse moors and related activities are undertaken in an environmentally sustainable and welfare conscious manner.”

Paragraph 13 of the policy memorandum states that

“The use of glue to trap birds is an offence”.

Are glue traps used? Is that what we are trying to do here with the glue-trap ban?

No. It is quite clear that the provisions on glue traps are not related to grouse-moor management. They are related to general animal welfare concerns.

In that case there is something confusing in the policy memorandum, which may need to be clarified with the Government bill team. I wonder why the memorandum mentions that

“The use of glue to trap birds is an offence”.

Are glue traps used to trap birds?

It is not my position as convener to answer that, but my understanding is that they are not.

Jim, do you have a supplementary on glue traps before we move on to wildlife traps?

Mike Flynn has already answered my question, thank you.

We will move on to the theme of wildlife traps.

Do panel members agree that there is a need for additional regulation of use of wildlife traps? What is your experience of use of spring traps and live-capture bird traps? What evidence is there that traps are misused in relation to both animal welfare and wildlife crime concerns?

The rationale is broadly set out in the policy memorandum. Paragraph 58 refers to illegal use of traps in or around grouse moors and qualifies that with two references to incidents where raptors were persecuted using a spring trap. Paragraph 59 then goes on to say:

“Where live capture traps have been used to persecute raptors, they are usually either ladder traps, or funnel traps.”

The inference is that traps are sometimes used to persecute raptors on grouse moors. The only thing that I would draw the committee’s attention to in terms of the actual evidence base for that is the official wildlife crime record. From the latest record, which was published this year and covers 2021, incidence of birds of prey crime involving trapping raptors is consistently lower than it is for shooting or poisoning, for example. It happens far less than shooting and poisoning.

The other important thing to say—I need to make this point clear—is that the wildlife crime record does not specify where incidents have taken place. We cannot say with certainty that trapping incidents, for example, all happened exclusively on grouse moors.

There is a fairly weak evidence base, to be honest, for the introduction of further regulation on use of certain wildlife traps in this context. It is regrettable that the policy memorandum has not expanded on that in a little bit more detail. We are talking about introducing a licensing scheme for numerous spring traps, the supporting evidence for which is summarised in two anecdotal references to raptor persecution. The evidence base is largely deficient and probably needs to be clarified further by the Scottish Government.

In previous sessions, Hugh Dignon referred to Fenn traps on more than one occasion. However, it is my understanding that the setting of Fenn traps is illegal at the moment, so those Fenn traps would not come under any new potential licensing scheme.

I could not speak to the exact legalities around it, but the traps that are generally used on grouse moors are DOC traps. I will defer to Alex Hogg, who can speak in a little bit more detail about the sort of traps that are generally associated with grouse moor management.

Last year, the Russian Federation made it illegal to use Fenn traps to kill stoats because the traps were not killing them in 38 seconds. The break-back trap that we were using was a Fenn trap, so we all had to change our management. We now use either a DOC or a Tully trap to catch a stoat. The traps are so strong that if you catch your fingers in one, you will break your fingers. The traps immediately kill the animal. They are good traps. Every grouse moor has now transferred over, at a cost of thousands of pounds. A Fenn trap was about £9 or £10 but the new traps all run at about £40. It is a huge expense, but we have done it and it works well. The animals do not suffer—that is for sure.

Is the licensing scheme proportionate and workable, including the requirement for compulsory training and registration for all trap use? Should there be a bespoke scheme that is identified to one serial number rather than individual serial numbers, where an operator may not use all of those traps?

We are doing a lot of training. We have done all the snare training. We are up for doing the trap training and getting it right. Whatever you decide on, we will comply with it and get the guys up to speed with their training.

11:30  

The question was whether the licensing scheme is workable and proportionate. Broadly, given the current provisions, the answer is no. That is not the Scottish Government’s fault, but there has been a lack of awareness about the potential unintended consequences of the scheme.

The key problem relates to the imposition of unique licence numbers on traps that are used much more readily than, for example, traps that are used to catch live birds, which are the only traps that are currently required to have unique licence numbers.

The implication of putting unique licence numbers on all trapping infrastructure, including spring traps, essentially results in that trapping infrastructure becoming personalised. It is tied to a specific operator. That should not be a problem, but it is, because of the extent of trap interference, tampering and sabotage in the Scottish countryside. This committee probably has the biggest wealth of evidence anywhere to suggest what the scale of the problem is because a number of gamekeepers responded to your recent call for views and made clear the sort of incidents that they were faced with.

In your summary of the responses to the call of views, where you did your analysis, under the question:

“Do you agree that there is a need for additional regulation of the use of certain wildlife traps?”,

for those who disagreed, one of the key words used was “sabotage”. A lot of people spoke to that in their responses to this committee.

That is a problem because if you have a unique licence number that is tied to a trap, that trap could then be sabotaged and be made illegal through other ways and means, through the actions of a third party. That trap would then tie the illegally set operation to an individual. If there is a unique licence number, that individual is much more likely to be the suspect in any investigation that then comes down the line. Of course, we know that if you are under investigation in the context of this licensing scheme, you can have your personal licence to trap suspended. Moreover, the licence to shoot grouse could be suspended by the initiation of an official investigation.

I can appreciate that that was a lot of steps to go through, but the unintended consequence of personalising trap infrastructure where there is rife interference, sabotage and tampering with infrastructure in the Scottish countryside has unintended consequences. It is important to set that out.

As soon as people have done it, they put it on Facebook and it is all over the place before they even get back, which encourages the behaviour. It is scary—it really is.

Convener, I want to explore what happens—

We have jumped ahead a bit. That is fine—it is the nature of a round-table discussion. However, can we focus on trap tampering at the moment? It will probably be helpful to explore that issue.

For the purpose of clarity and for the record, why would somebody be sabotaging and tampering with traps?

That is a good question. Some people are ideologically opposed to grouse shooting. If they are walking on a grouse moor and there is a trap there, they might take it into their own hands to sabotage it. Some people are ideologically opposed to use of traps for wildlife management. For some people, killing a sentient being is too much—they do not agree with it and therefore they take matters into their own hands. Some people, frankly, do not know what they are doing; they come across a trap and think that it is fun to smash it. There are all sorts of broad motivations. I should stress that these are my assumptions, but I imagine that these are the things that go through people’s heads when it comes to sabotaging, interfering and tampering with trap infrastructure.

What are the implications for the humane use of traps if they are interfered with? I have spoken to gamekeepers in my constituency whose traps have been interfered with, which is quite distressing. However, Ross Ewing is suggesting that having related serial numbers could lead to a potential for prosecution for the gamekeepers.