The Scottish Invasive Species Initiative is a 8-year partnership project working with communities and volunteers to control invasive non-native species along rivers in northern Scotland. Funded by the Scottish Government's Nature Restoration Fund. Visit our website – www.invasivespecies.scot – or email us at: sisi@nature.scot
Paul Castle, High Life Highland Ranger, April 2025
Paul Castle is the dedicated Countryside Ranger for North Sutherland and North Caithness with High Life Highland. He has been volunteering with the Scottish Invasive Species Initiative for several years and has written about American mink and the challenges of monitoring for this invasive non-native species in the far north of Scotland.
The American mink (Neovison vison or Mustela vison) is a small member of the Mustelid family of mammals, related to otters, stoats, weasels, and pine martin and an invasive species in the UK.
My journey with mink monitoring began in north Sutherland several years ago, where I took on the role of monitoring a mink raft. For years, I faithfully checked the raft for footprints, and while I never confirmed mink presence, I was often greeted by the tracks of otters and, occasionally, rats. These experiences gave me an insight into the lives of our native wildlife and the ever-present need for vigilance against invasive species.
The Mink may look harmless given their size (smaller than an otter) but their presence has had devastating effects on native species. Introduced to the UK in 1929 for fur farming, for the once desirable fur industry (mink coats etc), mink have slowly escaped either accidentally or through deliberate releases over many years. They were eventually confirmed breeding in the wild in 1956.
Andrew Davidson, Inverness sculptor, with his wife wearing a Mink Garment. Source: Helen Mackintosh Credit: Am Baile
In Scotland, the first mink farm opened in 1938, and by the 1980s, wild mink had spread north of the Great Glen, though they are yet to reach the far north of Scotland and some of the Scottish islands.
Mink are highly effective predators and once established they can have significant adverse impacts on local species. Prey includes birds and their eggs (native and domestic), small mammals, fish, amphibians, shellfish, and crustaceans, but their effect on water voles is particularly alarming.
Water voles (Arvicola amphibius), the UK’s fastest-declining mammal, have suffered a 95% loss of range in the past century, partly due to habitat loss but increasingly because of mink.
Water voles of course have native predators, such as herons, owls, pike, and foxes but their defence against these natural predators was to retreat inside their bankside burrows. Unlike native predators, female mink can enter water vole burrows, wiping out entire colonies.
Mink are quick to colonise areas and easily cross waterbodies such as lochs, rivers and even sea channels to reach islands, this makes monitoring essential part of conservation efforts.
A mink – Jan Den Ouden – Pixabay
Currently, I’m responsible for the only mink raft in Caithness. It’s positioned along a small burn that flows from an important loch, home to a variety of wild bird species. The burn provides a lifeline for wildlife, but it’s also a potential corridor for mink, which makes the raft’s presence vital.
What is a Mink Raft?
For those unfamiliar, a mink raft is a simple yet effective tool used to monitor mink activity.
Caithness Mink Trap – showing the tunnel
These anchored rafts float on the water surface and house a container of moist clay. This surface layer is positioned in the centre of the tunnel. Mustelids are very inquisitive mammals and mink are no exception. They will naturally investigate any unusual objects found around water courses and tunnels seem irresistible to them. Passing through one of these raft tunnels, they they leave their prints on the clay, which can then be identified by volunteers. Regular monitoring of these clay surfaces may indicate any presence of mink in an area.
My old Mink Raft
Over time, my Caithness raft took a battering from the elements. When I discovered it recently, it was in quite a sorry state and needed replacing. The tunnel was completely missing, it is anyone’s guess where that finally ended up, after the wind carried it away! The plywood boards were also split and damaged yet amazingly the clay lined container was still there, complete with faint otter prints.
Otter footprints – Paul Castle
Thankfully, the West Sutherland Fisheries Trust, as part of the Scottish Invasive Species Initiative (SISI), stepped in to replace the damaged raft. This initiative is another great example of cooperative conservation, bringing together ten fishery trusts and over 350 volunteers to monitor invasive mink across 43 river catchments in northern Scotland. It’s an extraordinary effort, with around 650 rafts and traps regularly checked by dedicated volunteers.
So, with a new raft in place, fresh clay and tunnel attached – back into the burn it went and I have resumed monitoring. The replacement Caithness raft has so far, only produced otter prints – and long may that continue. If mink tracks were to be identified, following careful consideration and approval, live trapping may be introduced. Live traps are also monitored by volunteers but any handling and dispatch of captured mink is only undertaken by fully trained and licensed individuals.
New Mink Raft installed
How You Can Help
I’m proud to be part of this collective effort. Several of my colleagues in the High Life Highland Ranger service also monitor mink rafts in their areas. Every set of otter prints we find and every mink footprint we don’t find feels like a small victory. Volunteers are always needed to help with raft monitoring. Together, we can protect Scotland’s native wildlife. Conservation is a team effort, and together we aim to keep the Highlands a haven for native species.
Paul Castle has devoted over two decades to the ranger service of North Sutherland and North Caithness. His commitment reflects his love for the area, marked by its breathtaking landscapes, diverse wildlife, friendly communities and rich natural heritage. Paul’s work plays a pivotal role in promoting and protecting the wildlife, flora, and fauna that make this part of Scotland so extraordinary.
Visit Nature Unveiled for more blogs by Paul and the Highlife Highland Rangers and Am Baile for more on Highland History and Culture.
Cat Cooper, Project Officer, Scottish Invasive Species Initiative, published March 2025
When the Scottish Invasive Species Initiative began operations in 2018 we faced a situation where there was no carryover mink trapping network remaining from the Scottish Mink Initiative (SMI) which ended in 2015. This meant that we had to rebuild a trapping network from scratch and in combination with rolling out landscape scale plant control in the Tay system – mink are not our sole focus and so our resources are spread more widely. Our initial emphasis was placed on re-establishing a core trapping network on the main stem of the Tay and Tummel, with targeted deployment where possible to smaller rivers and tributaries and areas of environmental importance like the Tay Reedbeds and Loch of the Lowes. From 2018 to 2024 a robust network was built up and maintained in these areas, catching more mink than any other Scottish Invasive Species Initiative project area in that time. However, with additional seasonal project staff employed in 2024, there was an opportunity to grow the network to fill gaps and expand west, to bring rivers like the Earn into the project area. Cat Cooper (now Project Officer for the Esk catchments) played a leading role in delivering that expansion over her time working with us as a Seasonal Project Officer in 2024.
“Remoti – Unit Activation.”
These words via text have become a regular occurrence in the past couple of months, and with each comes the excitement of knowing that there may be another American mink waiting in a live trap within the Tay system…
I began my seasonal role in May 2024 with the Scottish Invasive Species Initiative, working alongside the Project Officer on the River Tay and its tributaries. As part of my role I was given the opportunity to work on the expansion of the mink trapping network into the River Earn and to fill in a gap within the current network on the River Ericht. American mink trapping was a new undertaking for me and I was keen to get started.
The Earn: Expanding the network
The Earn is roughly 74km long, beginning at Loch Earn on the edge of the Trossachs and joining the Tay at Abernethy. Whilst we knew there was a population of American mink on the Earn, this tributary in the south-west of the Tay catchment (a border region for the project) hadn’t yet been reached. However, contact had been made with the River Earn Improvement Association to establish interest, and a list of willing volunteers was waiting to get set up and change that situation.
Remoti units are attached to a live capture trap and triggered when the trap closes – this sends a text message as an alert
A raft deployed on a tributary of the Earn. This was a rockier area which meant we had to use the trees for anchors.
Once I had my list, I reached out to each potential volunteer and arranged a site visit to determine a suitable location for a raft and live trap. Many of our new recruits are gamekeepers, ghillies and estate employees who have been working the land for years (in some cases over 40!!) and their knowledge of the area and past mink experiences was invaluable to identify the right locations.
At each site we looked for areas where mink had been spotted historically but also for locations that would provide excellent territory for them. Ponds, streams and ditches were all investigated as well as the main stem of rivers and their confluences (where two or more watercourses join).
Once we had agreed on a site the next phase would begin – deploying the equipment as quickly as possible. Our set up includes a floating raft and tunnel, a live capture trap, and a Remoti unit. The Remoti devices have proven to be invaluable to many of our new volunteers – particularly if they are busy with their day-to-day tasks or responsible for large areas of land or river beats. The Remoti unit is attached to a live capture trap and is triggered when the trap closes – this sends a text message to both the volunteer and the Project Officer to alert them. On our first new site success arrived much faster than even we had expected, with five mink caught and dispatched within the first week of operation. Many of these captures were on an estate pond but we also had success on the main stem of the river… we even had two mink in one day!
Our volunteer decided to paint his trap to conceal it and then moved it from the original location to a field ditch closer to the Earn. This was successful and a mink was captured here.
Our first raft on the Earn system was deployed on a duck pond which proved to be a huge success.
Sometimes we didn’t get the trap position quite right first time around and needed to make small changes to the location to maximise the chances of mink entering the trap – and minimise the likelihood of non-target species being captured. One volunteer had two red squirrels and even a hedgehog but these were safely released to continue their day and we subsequently moved the raft…and even camouflaged it!
By the end of 2024 we had 18 mink captures on the River Earn and 10 volunteers in place, with twelve traps deployed and a further ten awaiting placement next season, with coverage from Bridge of Earn all the way to Loch Earn. Mink activity slows down over winter and most volunteers will bring their equipment out of the water to avoid damage and lost equipment in storms and spates, but this end of year coverage puts us in an excellent position to hit the ground running in spring 2025.
The Ericht: A Gap in the Network
The Ericht originates in Highland Perthshire, where the Rivers Ardle and Blackwater meet near the Spittal of Glenshee, and flows down to Blairgowrie where it merges with the Isla. Historically the Ericht was a vital source of power, driving numerous mills and factories along its banks, particularly in Blairgowrie. Today the river is known for its salmon fishing, diverse habitats, and scenic walks. However, like many Scottish waterways, it faces ecological threats from invasive species like the American mink.
The Ericht has proved tricky for us to set up a consistent network so this was a key target area for me in May 2024. The only coverage up until this point had been through a gamekeeper who began trapping on the upper Ericht in mid-2023.
As with the River Earn, we had already received interest from one of the local estates. The keepers, ghillies, and their guests were regularly seeing mink travelling up the river systems so they were keen to lend their time and expertise to the project. One volunteer, Adam, had several sites in mind, including an adventurously out of the way hill loch where he had spotted mink in the past, and a confluence on the main river. One obstacle we faced here was the patchy mobile network. Remoti units operate using mobile phone masts and in Highland Perthshire this can be tricky, but Adam was happy to trial these and give it a go – knowing that he might have some additional journeys to make if the signal were to dip out.
Adam with our rather adventurous loch raft. Sadly signal wasn’t reliable enough, so the raft was moved to a different spot.
An adult female mink, captured by Adam on the Ericht
Rafts were placed and traps were set. On this occasion we decided to maximise our chances by placing mink scent in the back of the traps and less than 24 hours later we had a juvenile female – followed the next day by a young male!
In total, the Ericht had 16 mink captures in 2024 and, like the Earn, we expect to catch more when activity heightens again in spring. We now have six volunteers together monitoring 11 traps in the Ericht catchment – thank you to everyone who has signed up!
The Earn and Ericht expansion have already seen 34 mink captures between them since we started to expand these networks in July 2024. We are also delighted to welcome Comrie Men’s Shed to the project, our newest construction recruits who have kindly agreed to make rafts and tunnels for us to be deployed in the new year. Volunteers are absolutely essential to the Scottish Invasive Species Initiative and without them there simply wouldn’t be the time and skills available to cover such an expansive area. Thank you to each and every person who has offered advice, cups of coffee and, most importantly, their time to get these new networks up and running.
In total the Scottish Invasive Species Initiative captured 74 American mink from across the Tay catchment in 2024, with the help of over 50 volunteers. Of these, 34 captures were from the Earn and Ericht systems – a great success following these local expansion efforts. American mink are an invasive non-native species which have severe detrimental impacts on native wildlife. By controlling their population we aim to reduce their impact on native species and protect local wildlife. Thank you to everyone who has been involved across the Tay catchment!
To find out more about the Scottish Invasive Species Initiative and how to get involved, you can visit our website, follow us on social media or contact us on sisi@nature.scot
Greg Miller, Mink Monitoring and Control Officer, SISI Project, February 2025
The Isle of Martin is part of the Summer Isles archipelago in Wester Ross, located about 3 miles north of Ullapool. The island is owned and maintained by The Isle Martin Trust and is uninhabited but seasonally accessible by a small ferry. Isle Martin is a recognised bird sanctuary but unfortunately also visited by the invasive non-native American mink, which prey on the vulnerable native birds which live there. Greg Miller, Mink Monitoring and Control Officer with the Scottish Invasive Species Initiative, has been monitoring live-capture traps with the help of the local community and recently has had to visit the island on short notice when the traps have been triggered. Find out more from Greg about how he travelled over to the island on cold January day with the help of the Ullapool Sea Savers, followed by another trip just a few weeks later.
The view from Isle Martin. All photos in this blog are credited to: Janis at Ullapool Sea Savers
I was preparing for a day on the water, skippering the Ullapool Sea Savers boat for the Native Oyster Restoration project, when I got the ping from the remoti located on the Isle of Martin. Isle Martin is a community owned island which is at the entrance of Loch Broom; I’ve had two mink traps on the island for a number of months but this was the first time that one had been triggered. The custodians of the island had approached me to see if it would be possible to place traps on the island as they had noticed a steep decline in bird life over the years, with the occasional mink spotted. Mink are not the only pressures causing the sea birds (and birds in general) to decline but they sure don’t help – and it would be a step in the right direction to alleviate this added pressure.
It was going to be a cold one with the mercury hovering around freezing in the day and nose-diving at night, making for a picture postcard day, but one for wrapping up warm. I had a few jobs to do on the water before I could get to the trap. When I got to the boat the mooring ropes were frozen solid after continuous days of cold weather and the boat was full of snow that needed to be moved – deep snow can dangerously unbalance a boat. With the jobs on the water done it was time to head to the island, with Ullapool Sea Savers accompanying me for the trip. The island is a quiet place at the best of times but with snow and the light fading it felt even quieter. The snow was pristine apart from some geese prints and scat and I was wondering if the trap was triggered at all – maybe the cold had got to the remoti?
The trap was located in the centre of the island at the back of the old abandoned settlement that used to house the mill and old herring curing station. When this island was bustling with life, they tried to make a paddock by draining the few flat areas and walling them in. Where the drain met the wall and ran underneath, this I thought, made the ideal place to intercept a mink if they were to travel across the island. As I approached it became clear that I was correct as in the silence I could hear the snow and the vegetation I had used to cover the trap rustling – indicating that something had indeed been captured. I slowly approached and confirmed that it was a mink. Once I had humanely dispatched the animal I took measurements and photos of its teeth, which can help to estimate age. Then it was time to head back to the mainland as the sun had already disappeared below the hill and the temperature was dropping quickly.
As it happens I was back to the island in February, only a few weeks later, to dispatch another mink that triggered the very same trap behind the settlement. As I was not skippering the Ullapool Sea Savers boat this time I accessed the island via The Isle Martin Trust work boat located at Ardmair jetty, where the ferry to the island departs from in season. It’s always good when working in these remote locations that there are a number of volunteers who can assist – with the help of John McIntyre and the rest of the Isle Martin Trust members monitoring the traps, this makes control work on the island a viable option.
Greg will continue to monitor traps on the Isle of Martin with the help of the local community. Trapping on an uninhabited island is no easy feat, and we are grateful to everyone who has helped in these efforts including The Isle Martin Trust and Ullapool SeaSavers. Thank you for helping us to keep mink populations under control and protect native wildlife!
And thank you to Ullapool Sea Savers for sharing the photos for this blog!
Adam Lovell, Seasonal Project Officer, SISI Project, published February 2025
We asked Adam Lovell, Seasonal Project Officer for the Dee and Don catchments, about his experiences working with volunteer groups to tackle Himalayan balsam last summer.
As I sit down to write this blog in mid-October, I find myself reflecting on the busy summer just passed and the culmination of my time as a seasonal Project Officer for the Scottish Invasive Species Initiative in the Dee and Don catchments. The season dedicated to tackling Himalayan balsam (Impatiens glandulifera) has come to an end, and what an educational journey it has been! Witnessing the extent of this invasive plant’s impact first hand has been eye-opening, especially when considering the positive effects of careful management and treatment undertaken in previous seasons.
Volunteers help tackle a large patch of Himalayan balsam at Goals in Aberdeen
One of the most rewarding aspects of this project has been the collaboration with a diverse range of volunteers. Each group brings its own unique perspectives and knowledge to our shared goal of managing Himalayan balsam. From corporate teams to local youth groups and community groups like ‘Bolland’s Balsam Bashers’, it has been inspiring to see everyone come together to form an impressive coordinated and united effort. The synergy created by these differing groups is remarkable; each person contributes not just their physical labour but also fresh ideas and spirit, which only enhances the project.
Project volunteers Rick, Donald and Alan tackle Himalayan balsam at Ardoe in the Dee catchment
Managing Himalayan balsam presents its own set of challenges as this plant can dominate environments where it takes root. Introduced to the UK in 1839, it has become an established invasive species, particularly flourishing along riverbanks and in disturbed soils. Its ability to thrive in low light and outcompete native vegetation can significantly disrupt habitats and biodiversity, leading to the decline of other plant species. Not only does it change ecosystems, but it can also have detrimental non-biotic effects, like reducing waterflow and/or leading to potential flooding and bank erosion, which can have knock-on effects for freshwater ecosystems.
Volunteers from Oil Spill Response joined us for a Conservation Volunteer Day in July in Deeside
Employee groups help to provide extra people power to tackle balsam monocultures
What makes managing Himalayan balsam even more satisfying is that control work is a manual endeavour. Unlike many invasive species, where chemical control is generally needed to be effective (requiring training, specialised equipment and expertise), working with Himalayan balsam needs only a bit of elbow grease (sometimes lots of it), making it an accessible task to everyone who is physically able. Armed with our scythes, gloves, and a can-do spirit, it’s a great way for people with varied abilities and experience to get involved in invasive plant control. It’s been a joy to see volunteers discover how impactful ordinary tools and dedicated teamwork can be in removing this plant effectively and in making a difference to each control location.
Himalayan balsam can be controlled by pulling the plant out by the roots and piling them up to help prevent rerooting
Himalayan balsam flowers are strikingly beautiful, producing clusters of purplish-pink blooms that attract bees and provide a good source of nectar. This might all sound rather positive and beneficial but it is not quite as straightforward as that unfortunately! There are significant downsides to Himalayan balsam, for example, bees will often visit Himalayan balsam in preference to native plants meaning that native plants may not be pollinated as effectively when Himalayan balsam is present. This can impact the ability of native species to produce seed and maintain viable populations and ecosystems. Think of it like using a big burger chain to buy lunch instead of a small local independent place.
Himalayan balsam flowers may look pretty…
… but this invasive plant has significant detrimental impacts on native vegetation and ecosystems
Once pollinated, each Himalayan balsam plant can produce up to 800 seeds, with pods that explosively launch these seeds up to 7 meters away. Great tactics for spreading and reproducing but unfortunately this means that, once established it can rapidly spread, often aided by human activities and water currents, and form dense monocultures which outcompete native plants.
Throughout the 2024 season we collectively managed to pull, cut, and control the spread of Himalayan balsam, sharing in the triumphs and the inevitable frustrations along the way as we tucked into an essential Tunnocks Tea Cake and coffee. The community spirit has been inspiring! Volunteers have bonded over our common goal, exchanged stories from past seasons with us and other projects, learned from each other and ultimately had fun and a good laugh—whether they were seasoned conservationists or trying their hand at practical ecological management for the first time.
Before at Ardoe: project volunteer Sandra clears a clump of Himalayan balsam
After at Ardoe
As the season winds down and my time with the Initiative comes to an end, I am filled with gratitude and admiration for the dedicated volunteers who have helped this year, the invaluable experiences we have gained, and the hope that our joint efforts will lead to healthier ecosystems in the Dee and Don catchments for the future. We have laid and continued to build solid foundations, and, although the battle with Himalayan balsam is ongoing, I am optimistic for the future. Thank you for being a part of this journey with me – your passion and enthusiasm have made a world of difference!
To find out more about the Scottish Invasive Species Initiative and how to get involved, you can visit our website, follow us on social media or contact us on sisi@nature.scot
Connor Wood, Seasonal Project Officer and PhD Student with the University of the West of Scotland, January 2025
Introduction
We know that invasive non-native species are a major threat to biodiversity, but the danger they pose to our ecosystems can often be hard to see. Picture a sewer pumping sludge into a river or a forest being cleared and replaced with concrete—those are obvious, visible threats. But when an ecosystem is taken over by a non-native species, the damage can be much harder to recognize. Unless you can identify which species are native and which are non-native and invasive, the problem might not stand out. An understanding of why these invaders are a threat requires knowledge of their subtle differences from similar native species and how these differences can disrupt the balance of the ecosystem.
At first glance, some invasive non-native species don’t seem all that different from their closely related native counterparts. Take the invasive giant hogweed (Heracleum mantegazzianum) and the native common hogweed (Heracleum sphondylium) — sure, the invader stands much taller than its British relative, but they appear to function quite similarly overall. Or consider the Eurasian otter (Lutra lutra) and American mink (Neovison vison): the otter may be noticeably larger, but both are semi-aquatic predators from the weasel family, swimming through the same rivers. So, why is one a valued part of our ecosystem and the other a serious biodiversity threat?
Connor (left) took a break from his PhD research this summer to join us in the Spey catchment and help tackle invasive non-native species like American mink and giant hogweed
Connor sets up a mink trap on a floating raft
The answer isn’t just blind favouritism for native species. The danger posed by invasive species is very real, and it often comes down to small, crucial details – differences in biological traits (for example, size or fecundity) and how these traits shape their interactions with other species.
This is the focus of my ongoing PhD research, where I compare the traits of a native freshwater shrimp (Gammarus pulex) with two closely related invasive species (the killer- and demon shrimp, Dikerogammarus species) to understand how these differences play out. In this blog, I’ll focus on the traits that give invasive species like giant hogweed and American mink their destructive edge over native species.
Case Study 1: Giant Hogweed vs Common Hogweed
Giant hogweed, a member of the carrot family from the Caucasus Mountains, is closely related to common hogweed which is native to the UK. In fact, they’re so closely related they’re even capable of producing the occasional hybrid offspring [14]. Despite these similarities, their ecological roles differ dramatically. Here are some of the key differences between them which can explain why giant hogweed is considered a high-impact invader.
Common hogweed (above) is a native species which is very similar to the invasive giant hogweed (right). Photo credit: Rasbak, Wikimedia Commons.
There are key biological differences which make giant hogweed (above) a high impact invader.
Growth and Light Competition Giant hogweed can grow up to 5 meters tall, dwarfing the smaller common hogweed which grows to a maximum of only 2 metres. The leaves of giant hogweed are similarly oversized, spanning 1.5 to 3 metres in width compared to the much smaller 55cm length leaves of the common hogweed. This size, when combined with rapid vegetative growth, allows giant hogweed to form dense leaf canopies that block out sunlight for smaller native plants. Competition for light is one of the major drivers of plant community composition [21], and the giant hogweed has a clear advantage in this contest.
Seed production and Emergence High reproductive output is one of the most commonly reoccurring traits in successful and high impact invasive species [17]. Looking at the hogweed species, we can see a major difference between the two. Both species take around three years to reach the flowering stage. However, the reproductive potential of giant hogweed far outstrips its native counterpart. While common hogweed produces about 850 seeds per flowering season and usually flowers two to three times during its lifespan [16], giant hogweed can produce anywhere from 20,000 to a staggering 100,000 seeds in a single season. These seeds also germinate more frequently and emerge earlier in the season, giving the giant hogweed a big head start on outgrowing the competition [15]. What’s more, the seeds can remain viable in the soil for up to 15 years.
The reason for this difference lies in the giant hogweeds evolutionary history – the high seed production is a vital adaptation to survive the extreme cold and nutrient poor soil of the mountains in its native range. This reproductive advantage means that once giant hogweed takes hold, it is difficult to eradicate, allowing it to spread rapidly and persistently.
The oversized leaves of giant hogweed form dense canopies which block out light while it’s high reproductive output allows it to spread rapidly in new environments
Brown seedheads from the previous summer are visible among a dense covering of giant hogweed leaves
Toxic sap Giant hogweed is notorious for its highly toxic sap, which can cause painful, long-lasting burns due to a chemical compound called furocoumarin. While common hogweed also contains furocoumarin and can cause skin irritation, its effects are far milder because the chemical is present in significantly lower quantities. Whether giant hogweed’s toxic sap provides an ecological advantage over common hogweed or other native plants remains unclear—it may deter some herbivores [20], but our sheep trials have shown that certain livestock are unaffected. However, the difference in impact on human health is undeniable, with giant hogweed posing a far greater threat.
Insects and Pollination Common hogweed is a vital part of the local insect food web, attracting a broad variety of pollinators such as bumblebees, butterflies, hoverflies, and beetles. These pollinators play an important role in maintaining biodiversity. Giant hogweed, on the other hand, attracts a much narrower range of insects. Studies have shown that areas dominated by giant hogweed experience a decrease in pollinator diversity [13], which can have ripple effects throughout the entire ecosystem. The loss of specialist insect species in areas overtaken by giant hogweed is particularly concerning, as it impacts the broader insect community and the health of native plants that rely on these pollinators [19].
Common hogweed attracts a variety of native pollinators, providing a food source for bees, butterflies, hoverflies and beetles. Photo credit: Anne Burgess, Wikimedia Commons.
Summary Giant hogweed’s size, reproductive capacity and highly toxic defence strategies have made it a highly successful and destructive invader. As they overtake and dominate plant communities, the abundance and diversity of both native plant species and specialist insect species declines in turn. Without this native biodiversity and the ecosystem services it provides – pollination, nutrient cycling and habitat creation – the ecosystem suffers as a whole.
Case Study 2: American Mink vs. Native Otter
Background The American mink and the European otter are both top predators, members of the weasel family and share similar wetland and river habitats across the UK. Despite these overlaps, these two species have sharply different ecological impacts. The American mink poses a significant threat to native species, particularly causing dramatic declines in water vole and ground-nesting bird populations [1], whereas the otter is often regarded a keystone species crucial in maintaining ecosystem health. These are some of the trait differences that make mink a danger when compared to the otter.
The European otter (above) and American mink (right) are both semi-aquatic mustelids which inhabit rivers, wetlands and coastlines in Scotland. Photo credit: Peter Trimming, Wikimedia Commons
Despite their similarities, the invasive American mink (above) has a very different ecological impact compared to the native European otter (left). Photo credit: NatureScot
Size Differences and Competitive Advantage One key difference between the two species is size. Quite the opposite from the giant- and common hogweed, in this case the native otter is the larger animal. Otters can grow up to 130 cm in length, while mink are much smaller, ranging from 42 to 65 cm. Given the significant size difference, otters would be expected to hold a dominant competitive advantage over mink, enabling them to essentially bully them out of their territories or away from their food sources [4] [12]. Unfortunately, this is frequently not the case – many sites in the UK show a coexistence of otters and mink rather than competitive exclusion (we’ll discuss why later). All to say, the negative environmental impacts of American mink aren’t seen through direct competitive interaction with otters, rather through the direct predatory impacts on a variety of prey species.
Impact on Naïve Prey The small build of the mink actually contributes to one of their most devastating impacts – their predation on the UK’s endangered water voles [23]. The mink is small and agile enough to invade the burrows of the voles, chasing them into their dens through the underwater entrances that deter most of the voles native predators. Water voles, like many other native species, are considered “naïve prey” for the mink [22] – they have not evolved natural defences or behaviours to evade this newly introduced predator, making them easy targets. This inability to respond to new threats can have dramatic consequences for populations already weakened by habitat loss and other pressures [18]. What’s more, the aggressive prey drive of the mink leads them to kill more than they consume, which has led to the eradication of entire local vole populations.
Water voles are Britain’s most rapidly declining mammal and predation by American mink is a key contributing factor to their decline. Photo credit: Alan Ross
Diet, Habitat, and Adaptability While otters tend to have a more specialized diet focused on fish, mink are opportunistic generalist predators [6] [9]. They can hunt a wide variety of prey, including birds, amphibians, fish, rabbits, rodents, crayfish, domestic fowl and more, giving them a significant adaptive edge over otters. This dietary flexibility allows mink to thrive in diverse habitats and conditions, while otters are more limited in their prey choices. The otter needs a river with a good fish population, whereas the mink can find food just about anywhere. The specialized fish diet of the otter also makes them more susceptible to aquatic pollutants [7] [8] – if a river becomes contaminated with toxic chemicals, so too does the otter’s food source, while mink can sustain themselves on terrestrial prey and avoid the contaminant.
Reproduction and Fecundity The American mink exhibits an “r-selected” or “high output” reproductive strategy, which is typical among invasive species and contributes to their rapid population growth. Effectively this means the mink has higher fecundity (reproductive rate) compared to otters, so they can produce more offspring in a shorter time frame. While both species reproduce once a year, mink typically produce 4–6 kits per litter, compared to the otter’s 1–3 cubs. Additionally, mink can breed as early as one year old, while otters take 2–3 years to reach sexual maturity. Juvenile mortality is high for both species – as high as 50% before reaching maturity for both mink and otters, by some estimates [10] – and under these conditions the r-selected / high output reproductive strategy of the mink proves advantageous.
As well as the high fecundity, mink have a number of traits which make their reproduction adaptable to changing conditions. They’ve been shown to adjust their litter size and breeding times in response to changing population density [2] or prey availability [5]. They also have a rather unique capability for polyamorous breeding, where female mink can sire a single litter from multiple different males she has mated with [3]. These traits make the mink a particularly resilient invader as they can easily respond to changing conditions and “bounce back” after population control efforts.
American mink are opportunistic predators with high reproductive rates which makes them highly successful invaders. Their small size means they can enter burrows of vulnerable native wildlife like water voles. Photo credit: Marc Evans, Wikimedia Commons.
Summary The comparison between the American mink and the Eurasian otter gives an insight into the mink’s invasive success in the UK. Their high fecundity, adaptability, and aggressive predation make them a serious threat to native ecosystems. While both species face challenges from habitat loss and pollution, mink’s ability to thrive under these conditions compounds the pressure on vulnerable species like otters and water voles. Efforts to control mink populations must be sustained and strategic to protect native wildlife from further declines.
References
[1] Fraser, E.J., Harrington, L.A., Macdonald, D.W. and Lambin, X. (2018). Control of an invasive species: the American mink in Great Britain. Oxford Scholarship Online. Oxford University Press. doi:https://doi.org/10.1093/oso/9780198759805.003.0016.
[2] Melero, Y., Robinson, E. and Lambin, X. (2015). Density- and age-dependent reproduction partially compensates culling efforts of invasive non-native American mink. Biological Invasions, 17(9), pp.2645–2657. doi:https://doi.org/10.1007/s10530-015-0902-7.
[3] Thom, M. D., & Bagniewska, J. (2015). Biology, ecology, and reproduction of American mink Neovison vison on lowland farmland. Wildlife conservation on farmland: conflict in the countryside, 2, 126.
[4] Macdonald, D.W. and Harrington, L.A. (2003). The American mink: The triumph and tragedy of adaptation out of context. New Zealand Journal of Zoology, 30(4), pp.421–441. doi:https://doi.org/10.1080/03014223.2003.9518350.
[5] García-Díaz, P., & Lizana, M. (2013). Reproductive aspects of American minks (Neovison vison) in central Spain: Testing the effects of prey availability. Mammalian Biology, 78(2), 111-117.
[6] Bonesi, L., & W. Macdonald, D. (2004). Differential habitat use promotes sustainable coexistence between the specialist otter and the generalist mink. Oikos, 106(3), 509-519.
[7] Mason, C.F. and MacDonald, S.M. (1989). Acidification and other (Lutra lutra) distribution in Scotland. Water, Air, and Soil Pollution, 43(3-4), pp.365–374. doi:https://doi.org/10.1007/bf00279202.
[8] Androulakakis, A., Alygizakis, N., Gkotsis, G., Nika, M.-C., Nikolopoulou, V., Bizani, E., Chadwick, E., Cincinelli, A., Claßen, D., Danielsson, S., Dekker, R.W.R.J., Duke, G., Glowacka, N., Jansman, H.A.H., Krone, O., Martellini, T., Movalli, P., Persson, S., Roos, A. and O’Rourke, E. (2022). Determination of 56 per- and polyfluoroalkyl substances in top predators and their prey from Northern Europe by LC-MS/MS. Chemosphere, 287, p.131775. doi:https://doi.org/10.1016/j.chemosphere.2021.131775.
[9] Wise, M.H., Linn, I.J. and Kennedy, C.R. (2009). A comparison of the feeding biology of Mink Mustela vison and otter Lutra lutra. Journal of Zoology, 195(2), pp.181–213. doi:https://doi.org/10.1111/j.1469-7998.1981.tb03458.x.
[10] Harrington, L.A., Birks, J., Chanin, P. and Tansley, D. (2020). Current status of American mink Neovison vison in Great Britain: a review of the evidence for a population decline. Mammal Review, 50(2), pp.157–169. doi:https://doi.org/10.1111/mam.12184.
[11] Bradshaw, A. V., & Slater, F. M. (2002). A postmortem study of otters (Lutra lutra) in England and Wales. Bristol, UK: Environment Agency.
[12] Erlinge, S. (1972). Interspecific relations between otter Lutra lutra and mink Mustella vison in Sweden. Oikos, 327-335.
[13] Zych, M. (2007). On flower visitors and true pollinators: the case of protandrous Heracleum sphondylium L.(Apiaceae). Plant Systematics and Evolution, 263, 159-179.
[14] Stewart, F., & Grace, J. (1984). An experimental study of hybridization between Heracleum mantegazzianum Somm. & Levier and H. sphondylium L. subsp. sphondylium (Umbelliferae). Watsonia, 15, 73-83.
[15] Pyšek, P., Cock, M. J., Nentwig, W., & Ravn, H. P. (2007). Master of all traits: can we successfully fight giant hogweed?. In Ecology and management of giant hogweed (Heracleum mantegazzianum) (pp. 297-312). Wallingford UK: CABI.
[16] Roberts, H. A. (1979). Periodicity of seedling emergence and seed survival in some Umbelliferae. Journal of Applied Ecology, 195-201.
[17] Jelbert, K., Stott, I., McDonald, R. A., & Hodgson, D. (2015). Invasiveness of plants is predicted by size and fecundity in the native range. Ecology and Evolution, 5(10), 1933-1943.
[18] Doherty, T. S., Dickman, C. R., Nimmo, D. G., & Ritchie, E. G. (2015). Multiple threats, or multiplying the threats? Interactions between invasive predators and other ecological disturbances. Biological Conservation, 190, 60-68.
[19] Bogusch, P., Vojtová, T., & Hadrava, J. (2023). High abundance but low diversity of floral visitors on invasive Heracleum mantegazzianum (Apiaceae). NeoBiota, 86, 193-207.
[20] Buttenschøn, R. M., & Nielsen, C. (2007). Control of Heracleum mantegazzianum by grazing. In Ecology and management of giant hogweed (Heracleum mantegazzianum) (pp. 240-254). Wallingford UK: CABI.
[21] Gioria, M., & Osborne, B. A. (2014). Resource competition in plant invasions: emerging patterns and research needs. Frontiers in Plant Science, 5, 501.
[22] Anton, A., Geraldi, N. R., Ricciardi, A., & Dick, J. T. (2020). Global determinants of prey naiveté to exotic predators. Proceedings of the Royal Society B, 287(1928), 20192978. [23] Aars, J., Lambin, X., Denny, R., & Griffin, A. C. (2001, August). Water vole in the Scottish uplands: distribution patterns of disturbed and pristine populations ahead and behind the American mink invasion front. In Animal Conservation forum (Vol. 4, No. 3, pp. 187-194). Cambridge University Press.
The Scottish Invasive Species Initiative has tackled invasive plants along rivers and watercourses in northern Scotland since 2018. Working across 43 major river catchments and over a third of mainland Scotland, it is the largest invasive non-native species management and control project in the British Isles. The project operates on a landscape scale and targets key invasive plants species including: giant hogweed, Japanese knotweed, Himalayan knotweed, Himalayan balsam and American skunk cabbage.
A giant hogweed infestation on the River Urie, a tributary of the Don in Aberdeenshire
To operate successfully on this scale we must be systematic and organised in our approach to plant control. Most obviously we need to identify the uppermost source (or sources) of each species in the river catchment and begin from there. Invasive plants in the wider environment, often introduced via escapees from ornamental gardens or in discarded plant materials, can readily spread downstream by seeds or rhizome fragments carried in the water flow. In this way, they can become widespread in a catchment using the river as their distribution highway and have detrimental impacts on biodiversity, local communities and economies. Starting control at the upstream sources and moving downstream from that point helps prevent reinfestation of cleared sites and enables us to work toward eradication.
A visualisation of an invasive plant spreading through a river catchment. The original source is from a garden (pictured in black) which then moves downstream via the river (green) where the plant is spread further along a footpath (yellow) and train tracks (red).
This all sounds fantastic in theory – but how do we put it into practice? The realities of implementing this basic strategy can seem overwhelming when faced with multiple species infestations in multiple tributaries – and when accumulations of species in lower rivers are very visible and scream for attention. To get the job done successfully we need to harness and coordinate input from a wide variety of people. This year for Invasive Species Week we thought that, rather than talk about the invasive plants themselves, it would be useful to work through our approach to harnessing the most important asset we have in the battle against these species – people!
Here’s how we approach things….
1. Our partners: the fishery boards and trusts
We are a partnership project led by NatureScot but with 10 different fishery and rivers trusts as delivery partners (and not forgetting the University of Aberdeen as our academic partner). The trusts employ our team of Project Officers and provide essential local support and knowledge of the catchments in which we operate – and of the people who live and work there too. Some partner trusts have controlled invasive plants in predecessor projects and made good progress in identifying the sources and controlling the upper infestations. Partner staff assist with our hands on control work and provide invaluable support at the height of the plant control season.
Charles and Atticus from the Spey Fishery Board helping with giant hogweed control
Bob Laughton, director of the Findhorn, Nairn & Lossie Rivers Trust (right), helping with giant hogweed control alongside intern Sarah (left) and Project Officer Elise (middle)
So, first things first, we have established and reliable local partners with local connections and knowledge of the catchments we work in.
2. The project team
The next step is to add a team of dedicated Project Officers. Our team identify and confirm sources of infestations; develop a management strategy and plan of action for each catchment; collaborate effectively with relevant stakeholders; organise training courses for volunteers and landowners; ensure all intended control work is completed and, essentially, be the eyes, ears and mouth (!) of the project on the ground!
The Scottish Invasive Species Initiative project team
Our Officers coordinate and carry out much of the practical control work themselves or alongside other individuals and organisations, and ensure our work is strategic and effective. They keep records of chemical use, time spent on control work and survey for abundance of invasive plant species at control sites – all of which allow us to monitor progress over time and, crucially, demonstrate progress across years and by species.
Step two then – hire a great team and add to your local partners!
3. Contractors
Each year our Project Officers identify the worst infestations and any sites where specialist skills are required before we can move towards community-based control. In these areas, we bring in the contractors.
One of our excellent contractors tackling a significant giant hogweed infestation on the River Almond in Perthshire
Contractors are often the go-to option for invasive plant control, for private landowners, organisations and projects. However, we use the contractor option sparingly. There are a number of reasons for this including:
The need to stretch our budget as far as possible and make each £ work hard. Contractor skills cost money and so if grant funding were to run out we have no fall back option if all work is completed using these groups.
There often aren’t enough contractors around to do the work needed! Therefore, we use contractors tactically and sparingly on the worst of sites in initial control years.
Our desire to build capacity in communities and with volunteers (local individuals and landowners and managers) so that we have a sustainable control programme delivered by those most invested in each area and catchment. We can do this when the worst of sites have been initially tackled by expert contractors.
We also use contractors when access to a site is difficult or dangerous. For example, we have several control sites on the Rivers North, South Esk and Findhorn where giant hogweed has managed to establish itself on cliff sides, which are only accessible by top roping. Our fantastic top-roping contractors (‘Bloke’s on Ropes!’) are deployed on these sites to ensure nowhere on the river is left untreated.
The ‘Bloke’s on Ropes’ expert contractor team
These Giant hogweed has infested cliff sides on the South Esk are only accessible by top roping
Next ingredient in the mix then is expert contractors deployed to the worst or most technically challenging of sites.
4. Collaborate with other organisations
Our catchments cover large areas and within each are different landowners and stakeholders to collaborate with. By working with organisations such as the Scottish Wildlife Trust, National Trust for Scotland, Abernethy Trust, the RSPB, Forestry and Land, NatureScot and local councils, we are able to make progress more rapidly than we would do on our own.
NatureScot staff from the Forvie National Nature Reserve help to control Himalayan balsam on the Foveran burn
The Foveran burn feeds into Forvie NNR – to protect the site it is necessary to tackle upstream sources of Himalyan balsam
Organisations such as these own and manage land and are invaluable allies in the fight against invasive species. Our team works with local organisation staff to carry out control work annually and, once the problem has improved, look to them to maintain and take responsibility for on-going management. To support this handover process we can, for example, provide training which enables staff to carry out control work independently of the project or lend equipment or supply chemicals to remove barriers to participation.
Japanese knotweed infestation at Dunkeld Bridge in 2019. This site is owned by the National Trust for Scotland who have been working with us to get the infestation under control.
The same site in 2021 – the site is much improved and NTS have taken over ongoing management, allowing Project staff to move to sites further downstream.
In recent years, we have also collaborated with Perth and Kinross Council and Moray Council to tackle infestations of invasive plants on the Almond, Findhorn, Lossie and Spey rivers. For example, the River Almond control project, which began in 2023, is funded by Perth and Kinross Council and jointly managed by the Council and Scottish Invasive Species Initiative staff. There has been a fantastic response within the local community with many enthusiastic volunteers joining to help with control work – you can find out more about this project here.
So, after partners, staff and contractors we add local organisation collaboration to the mix – and then add communities!
5. Work with communities
Community groups are an integral part of the Initiative, helping to control invasive plant species in their local area. Such groups do not normally own the land they help to manage but take ownership of their local environment and give their time, passion and enthusiasm to the cause.
The Upper Tay Paths group is a constituted community group helping to manage the core footpaths on the River Tay. They work with our local Project Officer to control giant hogweed and Japanese knotweed around Aberfeldy.
Similarly to land-owning organisations, we provide training, advice, practical support and, where possible, look to hand over responsibility of sites for groups to manage independently. Some of the groups we work with include Green Hive in Nairn, the Upper Tay Paths Group and the Fearnan community group in Perthshire, various local angling clubs, the educational charity Wild Things, and the ‘Beauly Balsam Bashers’ and ‘Bolland’s Balsam Bashers’ on the River Dee. The enthusiasm and commitment for local places within such groups, we believe, exists in many communities and groups and so our role is to support such groups and to translate and harness their goodwill and passion to contributions within a wider control programme.
Volunteers from Greenhive helping Japanese knotweed, giant hogweed and Himalayan balsam around Nairn
The ‘Beauly Balsam Bashers’ are a community group working together to control Himalayan balsam around Beauly village
So having now added community groups we turn to individuals committed to making a difference – volunteers.
6. Volunteers
We consider anyone giving up their time for the project to be a volunteer. However, we give special recognition here to everyone who has signed up with the project and given up their time to help tackle invasive plants. Hundreds of people from across the project area join us every season to help with plant control – their contributions allow us to control larger areas than would otherwise be possible and help us to push control operations further downstream and work towards eradication.
Dedicated volunteer Alan has logged hundreds of hours over the years controlling invasive plants on the Dee and the Don
Cat volunteered with us from 2020-2022 as a recent graduate and has since found employment in the conservation sector
Volunteers come in all forms – students and early stage careerists looking for experience to enhance employment prospects, people with time on their hands wishing to make a difference in their local area, retirees giving something back locally or enjoying the social interactions of volunteering – and many more besides. We look to provide safe and enjoyable volunteering activities with a purpose and are happy to have supported many to gain employment (with the project and elsewhere) and secure formal qualifications and skills for use in the future.
The Diageo team on a corporate volunteer day in Speyside
Dedicated Speyside volunteer Mark making full use of his pesticide application training
The final people ingredient to our plant control programme mix is that of landowners and land managers.
7. Landowners
Last but certainly not least – landowners. We work with landowners all the time as we need their permission to undertake any work but they are also integral to our long-term sustainable control strategy.
We aim to identify problem areas in a catchment then control infestations with a mix of staff, contractor and volunteer contributions (see all of the above) to improve the sites sufficiently to handover responsibility for future management back to landowners. By providing training, equipment, advice and practical support in the early years, we provide landowners with the tools they need to control and, ultimately, eradicate invasive species on and from their land.
Groundskeeper Davie from Gordon Castle Estate (left) working alongside volunteer Mark (middle) and Charles from the Spey Fishery Board (right)
There is no legal obligation on a landowner to remove invasive plants from their land – only to prevent the spread elsewhere. The reality is that often infestations are large and expensive to control and landowners may simply have neither the resources nor technical expertise or skills to complete control. By reducing the scale of the problem, removing barriers to action and simply asking landowners to participate and contribute, we have made significant progress.
We already have a number of landowners contributing to the project – including estates, organisations, farmers and businesses. Currently, over 60 voluntary landowner agreements are in place where landowners have agreed to take on responsibility for ongoing management of invasive plants on their land after initial support from the project. This approach has already allowed the project to move resources to new (downstream) sites with future management on early control locations delegated to landowners.
The key to success
And that’s our approach to people engagement within our landscape scale invasive plant control project. Identify the key elements, groups and individuals and look to bring them into a coordinated overall programme where they can see that their contributions are valuable and valued.
Volunteers, project staff and Perth and Kinross Council staff ready to tackle giant hogweed on the River Almond
Controlling invasive plants at this scale can seem an impossible and overwhelming task but we know that real progress is possible when you have clear goals, priorities, a proper plan and, most importantly, a collaborative effort. There are many different stakeholders involved in the project and this collective effort is what allows us to make progress.
Volunteers, in all their different forms, have contributed an incredible 23,750 hours to our plant control project so far – the equivalent of >16 staff working with us for one year! However, it’s not simply just about the time – it’s important to recognise what that time is achieving in terms of invasive plant control. This collective effort has helped us to bring 1,580km of riverbank under management for our target invasive species – the large majority of this total on an annual basis. To give some context, Edinburgh to London (in a straight line by air) is 534km – so, each year, we are managing a riverbank length equivalent to three trips between Edinburgh and London!
Thank you to everyone who has helped us so far – we hope you will continue to be involved in the future.
A rare sighting of ‘super-vole’. Photo credit: Alan Ross. Vole identity: unknown…
The American mink control project run by the Scottish Invasive Species Initiative has been operating for 6 years and so far has captured 673 mink across the north of Scotland. Each year over 300 volunteers monitor an extensive network of rafts and traps, collectively contributing over 103,000 hours since the project began. After 6 years of co-ordinated control, it is important to look back and ask how effective the mink control programme has been so that we can continue to reduce mink numbers and the impact this invasive species has on Scotland’s ecosystems and native biodiversity. My ongoing research at the University of Aberdeen, in collaboration with the Initiative, is helping to answer these questions by investigating how the past and current mink control efforts have helped native species recover.
The Scottish Invasive Species Initiative encompasses a large area in Scotland (over 1/3 of the mainland) and is only possible thanks to the collective efforts of a large network of people, including project and fishery board staff in addition to a vast network of volunteers. Over the years the project has collected data that provides key information to better control this invasive predator – helping to identify “hot spot” capture areas for example, where ongoing control is essential. However, there are still gaps in our knowledge that need to be filled to continue protecting Scotland’s ecosystems and contribute to ongoing and future research. To fill in these gaps, we need all the help we can get, particularly from our on-the-ground experts: the volunteers.
The Scottish Invasive Species Initiative project area
Going forward, we have two new opportunities available for existing and new volunteers: Mink ‘super-volunteers’ and the ‘Volenteers’. These opportunities will, respectively, help understand: (1) how effective we are in reducing mink numbers in Scotland and, (2) how these efforts have contributed to the recovery of one of the UK’s most affected species by mink predation: the water vole.
The American mink is an invasive non-native species which has a devastating effect on native wildlife
Water voles are the UK’s most rapidly declining mammal – predation by American mink is a major cause of their decline. Photo credit: Alan Ross
Mink ‘super-volunteers’
Mink super-volunteers will be the project’s eyes on the river and this role is suited for those interested in helping improve our ability to detect and remove invasive mink. Mink super-volunteers’ will provide key information to assess how invasive mink populations are changing year-to-year.
As with current mink volunteers, ‘super-volunteers’ would oversee monitoring rafts and traps but also collect additional data on when and where these checks occur – and whether a mink has been detected and/or captured and, equally as important, when it has not. No mink news is good news! Knowing how often mink are not detected or captured will help us understand where and why we have successfully reduced mink populations and to what extent.
A clay pad lifted out of a monitoring raft to check for prints
A mink has been detected!
To sign up please get in touch with your local Scottish Invasive Species Initiative officer. Once we have you set up with a mink raft, data will be recorded with your smartphone (or pencil and paper) and submitted through an on-line form or via email. Your monitoring rafts would be placed in a suitable spot within the project area .
Finally, super-volunteers will not exclusively be ‘mink-watchers’. As a super-volunteer you can also choose to develop your naturalist skills and learn how to identify signs of other amazing riparian species like the otter or water vole that might leave marks on or near your rafts. Do not hesitate to report any interesting signs you find!
‘Super volunteers’ can practice their ID skills and report any tracks found on their monitoring pad. These were left by a water vole!
You might also find tracks in the surrounding area – these tracks were left by an otter walking along the soft sand of the river bank
To be a mink super-volunteer you do not require any previous expertise in mink raft monitoring or species identification as we will provide training opportunities and material – absolutely anyone can join!
‘Volenteers’
The ‘Volenteers’ opportunity will be for those of you who are interested in looking beyond the ‘mink horizon’ of the project and want to help figure out how water voles and other species may have recovered following mink control. Water voles are the UK’s second largest native rodent (second only to the beaver!) and their populations experienced a decline of over 90% during the 20th century – largely due to predation by the American mink. They serve as ecosystem engineers, cycling the nutrients in the soil when they burrow and promoting vegetation growth. What’s not to like? Since mink control programmes started in the 21st century, water voles seem to have recovered in different locations, but we still do not know exactly by how much or why that is.
Water voles are the UK’s second largest (and possibly cutest) native rodent. Photo credit: Alan Ross
Volenteers will be the extra eyes (and legs) on the ground to help monitor where water voles are in Scotland. Volenteers will participate in periodic water vole surveys (monthly for the summer months or twice a year, for example), which consist of walking alongside a strip of waterway in search of signs indicating water vole presence – such as dropping latrines which they use to mark their territories. Surveys would take place in late-spring and throughout the summer and so gives a perfect reason to go on a nice hike in the warm Scottish weather looking for water vole signs (or see the beasts if you’re lucky!) with friends and family.
You can choose to survey locations near your patch or mink monitoring rafts (if you are a mink volunteer), or even choose to do one-off surveys further away when you go hiking in the summer. Unlike mink raft locations, water vole surveys can be within or outside the Initiative’s area, just make sure you let us know where and when you would be interested in surveying beforehand as it may be necessary to get permission from landowners.
Surveying for water voles in the Cairngorms
Water vole surveys take place in late spring and summer
These surveys are a fantastic way to develop field and species identification skills, help an iconic Scottish species and spend time in nature. As with Mink super-volunteers, there is no need to have previous experience with these kinds of surveys. We will provide the training and guidance necessary to make sure you excel in the art of voling. If you are interested in water vole survey training, going out on practice surveys, or wanted to try it out before signing up let us know and we can arrange something for you.
How to sign up?
If you are looking to sign up or have any questions, do not hesitate to get in touch with me (Albert) or any other wonderful member of the Scottish Invasive Species Initiative using the contact details below. Or, if you know of someone who would be interested in participating, please send them this post (add some cute vole pictures, works a treat) and get them signed up too!
Fancy signing up as a ‘volenteer’? Contact Albert using the details below! You can do vole surveys near where you live or in more remote locations.
You can choose whether to be Mink super-volunteer, a Volenteer, or both, which by my naming convention would make you a Super-volenteer (now we’re talking)! If you have any doubts then do consider just giving it a go – you won’t know how rewarding this can be until you try!
Get in touch with your local Project Officer to sign up as a mink ‘super-volunteer’
Anyone in the project area can sign up as a mink volunteer – no experience necessary, all training and equipment provided!
We hope that these opportunities will help bring you and communities feel closer to nature and, together, help us better understand and protect our biodiversity.
Together we can help safeguard Scottish fauna and flora against invasive species in a rapidly changing climate. And who knows, maybe we can find the answer to the overarching question: how many mink is too many mink?
Contact details
Water vole surveys: To sign up as a volunteer for water vole surveys, contact Albert Bonet Bigata: a.bonetbigata.22@abdn.ac.uk
Mink volunteers: To sign up as a mink volunteer, contact your local Scottish Invasive Species Initiative Project Officer. All contact details are available on our website – if you are unsure who to speak to you can email us at: sisi@nature.scot
In 2023 the Scottish Invasive Species Initiative received support from Moray Council and the Ian and Clare Mattioli Charitable Trust to tackle invasive species in the Spey, Findhorn and Lossie catchments. This allowed us to trial a new method of chemical application and make rapid progress on significant giant hogweed and Japanese knotweed infestations, which would otherwise have taken several years to tackle. Find out more about these innovative methods in the blog below, written by Project Officers Karen and Elise.
Elise and intern Sarah forge a path into a mature giant hogweed stand on the lower Lossie
Merging walls of Japanese knotweed at Middle Brae beat on the Spey
Here on the rivers Findhorn, Lossie and Spey we are no strangers to large infestations of giant hogweed and Japanese knotweed, especially in lower areas of the catchments. As we work towards bringing many of our sites under control, we cannot help but cast nervous glances at the strongholds of invasive plants further downstream. Towering, dense forests of giant hogweed and tangled, impassable walls of Japanese knotweed await, daring us to even look in their direction with a knapsack. The thought of beginning to tackle these bastions for the first time is a daunting one.
But worry not dear friends, ‘tankfully’ there is a solution! In the expansive flowering fields of invasive plants, the peace and quiet was about to be broken by the sounds of ‘engine-uity’. Armed with determination, herbicide, a pressurised sprayer and, in some areas, a tractor-mounted cage, we embarked on a mission to reclaim the land for native species. Join us in this green adventure, where we turned the tide against an ocean of invasives!
Sarah, Elise and Bob after tackling a difficult infestation of giant hogweed in a scrapyard in the Findhorn catchment.
Sprouting the Plan In many places, we face expansive areas of dense interlocking Japanese knotweed and giant hogweed plants, often towering over our heads, smothering native biodiversity, and making access for effective control difficult. Traditional control methods via knapsack or stem injectors would require significant people power, time and would often mean that our control efforts would be limited to the outskirts of the densest stands, requiring a few years before we were finally able to meet in the middle.
Drone survey photos show extensive stands of Japanese knotweed dominating a riparian woodland in the Spey catchment. The knotweed is visible as dense clumps of green foliage around the trees and on open ground, covering an expansive area. If left untreated these stands will continue to spread.
We are left pondering how many hours will be spent bashing a path through the undergrowth with a fully laden knapsack? How many dauntless volunteers will disappear into the fray and will the biscuits we offer be enough to tempt them out again? And perhaps most importantly, how effective will our efforts be against such mature and overwhelmingly huge stands?
While there are many factors against us, there are also some crucial advantages on these sites, namely good track access, large areas of invasive non-native plants growing away from the river, and land managers who are supportive of new and innovative strategies. So, we hatched a plan that was as ambitious as it was ‘engine-ious’.
The motorised spray tank set up in a the back of a trailer
We turned to the newest weapon in our armoury; a motorised spray tank normally used by a local estate for controlling hill fires, with a capacity of 400 litres, a 50-metre hose and a lance that can spray up to 10 metres! With the tank safely loaded into our trailer and filled with the standard glyphosate and water mixture we’d use in our knapsacks (Roundup ProVantage at 2% concentration), we set off down the aforementioned access tracks to introduce the invasive plants of Moray to our formidable new weapon.
We quickly settled on a strategy and established that a team of three was optimal; with one team member staying in the trailer to keep an eye on the engine and to feed the hose out to the operators on the ground; another team member managing the hose between the trailer and the lance, ensuring it didn’t get snagged or tangled; and the last team member handling the business end and operating the lance. Working together we were able to achieve a very fine level of control with the sprayer to minimise off-target application. Using this approach our staff, volunteers, and groundskeepers were able to operate the power sprayer safely.
Project Officer Elise operates the sprayer while Bob (Director of the Findhorn, Nairn & Lossie Rivers Trust) operates the engine and hose
Rivers Lossie and Findhorn
We started the season by tackling infestations of giant hogweed on the lower Lossie and Findhorn. These areas were dominated by mature plants that were well on the way to flowering – if not flowering already. On top of that, there was also a heatwave to deal with, which would have further ‘sapped’ operators’ energy and could have proved limiting if using heavy knapsack sprayers. However, armed with the tank, we were able to travel light, with operators only carrying saws to cut their way into thickets to reach flowering heads before spraying their way out with the tank’s powerful lance. The increased range of this lance meant large areas were covered quickly and efficiently. It also meant that plants growing in areas that would be hard to access with a knapsack were given no respite as we were able to find safe vantage points and use our new-found range to sufficiently douse them with spray. Seeing the amount of ground that three or four of us were able to cover in a day was incredible – but we were hardly complaining!
Deploying the power sprayer on a dense stand of giant hogweed on the lower Lossie
Tackling Japanese knotweed on the Upper Lossie – Elise operates the power sprayer while volunteer Robert manages the hose
Later in the year the tank had another chance to shine in the fight against previously untreated Japanese knotweed. Well-established knotweed tends to grow in large, dense stands which form thick canopies of leaves, making them ideal targets for the tank. Using the same techniques we had perfected during our days treating giant hogweed, we marched into battle against the Japanese knotweed on the Lossie. In some areas we were faced with solid walls of knotweed as well as smaller isolated clumps. To use the tank on these small sections would have been irresponsible as it would run the risk of off-target application. However, rather than just leaving these sections untreated, we instead turned to a hybrid method of treatment and tackled it the old-fashioned way, with team members working with knapsacks in tandem with the tank.
Sprawling fields of knotweed dominate areas of the lower Lossie
Elise and Sarah fully kitted up and ready to tackle Japanese knotweed!
This goes to show that every site is different, and varying abundance and distribution of invasive plants require different combinations of treatment methods, as we were about to find out on the Spey.
River Spey
A Japanese knotweed stand (field!) on the Spey – an infestation this large would take years to tackle with a knapsack sprayer
Drone photos show the extensive coverage of Japanese knotweed at the Middle Brae beat on the Spey
In the lower Spey catchment, this year’s focus with the tank was solely on untouched Japanese knotweed stands. After identifying suitable sites, we approached it in the same way as on the Findhorn and Lossie in the first instance – on foot. This was the best approach where Japanese knotweed was growing in dense but narrow stands along both sides of an estate track.
In stark contrast, the next site was 220 meters in width and featured towering knotweed wall to wall, broken only by a couple of tracks and natural breaks between the mature stands that were increasingly merging together after years of unchecked growth. We looked to elevate our approach – literally – with a tractor mounted cage to provide us with the advantage of height to spray beyond the initial wall of knotweed without having to enter it on foot. Luckily, we had a supportive land manager with a skilled groundskeeper and his tractor who came to our aid.
Project Officer Karen in the mounted cage
Spey bailiff Doug operates the power sprayer from the cage with fall arrester, helmet and filter mask for safety
This came with a new level of safety considerations but armed with a helmet and fall arrester for the person manning the cage, high visibility clothing and a thorough risk briefing for everyone involved, as well as experienced operators, we took our control to new heights.
Karen operates the lance on a large clump of Japanese knotweed while Elise manages the hose
Even from the cage, the centre of the largest clumps could not be reached and will need to be tackled next year
The trailer was hooked up to the tractor where the tank was manned by a team member, the hose was secured over the cab and fed into the cage where a member of staff was utilising the pressurised lance to spray as far across the top of the knotweed expanse as possible. Some of the natural breaks between Japanese knotweed stands meant that these could be tackled from a number of angles, although the centre of some of the largest expanses remained out of reach even from the cage. In just one treatment season, this approach allowed us to nearly eliminate smaller, isolated stands and greatly reduced the extent of the larger, merging areas of growth. This was particularly important in mixed sites, where the reduction of Japanese knotweed will improve the efficiency of giant hogweed control in following years.
Doug and Karen with the tractor
Success – Japanese knotweed dies off on the middle Brae beat after one round of treatment
Last but knot least
The humble knapsack will always have a place in the battle against invasive plants, but we cannot be afraid to think outside the box when faced with challenging sites. Collaboration often provides new opportunities to explore innovative control methods and bring together the different skillsets necessary to make them a reality.
The support we received from Moray Council and the Ian and Clare Mattioli Charitable Trust has made this work possible and enabled us to hire the specialized equipment required for this new method. This has allowed us to make rapid progress on really badly infested sites by covering significantly more ground, saving countless hours and ultimately being more efficient than would ever have been possible using only traditional spraying strategies. It is tricky to give exact figures as spraying on foot can be so variable, but we would estimate that using the spray tank we were able to cover 10-15 times more ground than one person could cover using a backpack sprayer in the same time period.
Sarah, Elise, Bob and volunteer Ivan triumphant after a hot day spraying giant hogweed on the Findhorn
Volunteer Teresa, Spey Bailiff Doug, Groundkeeper Davie and Project Officer Karen in the tractor cage
Having visited the sites a few weeks after treatment we are delighted with the results so far. When faced with infestations this significant the problem can often seem overwhelming, even hopeless – but take heart that there is always a solution, even on the most difficult sites!
Karen and Sophie from Moray Council on a site visit. The dead brown stems behind them, stretching into the distance, show the expanse of Japanese knotweed treated on site.
A special thanks goes to Moray Council and the Ian and Clare Mattioli Charitable Trust for supporting the funding of this control work. Thank you also to Kellas Estate for access to the spray tank, Gordon Castle Estate for providing the tractor and their groundskeeper – and in particular for their support and confidence in us.
As always, we couldn’t have done this without our stalwart volunteers, committed partner staff and David Mitchell with his tireless skill navigating the tractor through the knotweed jungles.
The Scottish Invasive Species Initiative is a partnership project funded by The National Lottery Heritage Fund & NatureScot (2017-2023) and the Scottish Government’s Nature Restoration Fund, managed by NatureScot (2023-2026).
NatureScot employees are allocated one day per year to spend on a volunteering opportunity or activity of their choosing. In August 2023, Liz Colmer and a group from the Inverness office chose to spend their day with us and joined Project Officer Trudi on the banks of the River Beauly to tackle Himalayan balsam – an invasive non-native species. The gang cleared a woodland area, helping to preserve the native flora found there and prevent this highly invasive plant from reinfesting the riverbanks.
On Wednesday 9 August, myself and some NatureScot colleagues; Megan, Cat, Lucie, Kat and Susi and Susi’s daughter Lucy met at the Beauly Fisheries Office to meet with Trudi Clarke, Scottish Invasive Species Initiative Project Officer – Cromarty, Ness & Beauly catchments.
We were meeting to go Himalayan balsam bashing. This opportunity was organised by Susi Hodgson and advertised on the NatureScot intranet. I have often wondered what I would do with a volunteer day and so when this opportunity to help in my local area appeared, I couldn’t pass it up.
A short way from the Lovat Bridge, in some riparian woodland by the River Beauly, was our location. As we were walking in, we spotted a roe deer bounding across the field and Trudi spotted a kingfisher a bit later.
We started with a brief introduction from Trudi; Himalayan balsam is an invasive species, it spreads fast, dominating and blocking the light of other native plants and its shallow roots do not help to prevent soil erosion along the banks of the river. She explained that the plant is non-toxic and the technique for pulling it out by the root and placing it in piles, or over the branches of trees, so that the roots dry out and it can no longer spread. It is best to pull it at this time of year before it goes to seed, as the seed pods can scatter quite explosively and are responsible for the invasive element of this annual plant.
At first inspection, there didn’t look to be much Himalayan balsam by the river (due to success of previous years’ bashing efforts) but it wasn’t long before we found vast areas of it deeper into the woodland. The plant is easy to pull out, however, it was growing at all different heights so involved stooping. It was hard work but immensely satisfying seeing the areas we had cleared and the space and light it created for the other plants.
Once pulled, hanging Himalayan balsam on tree branches helps to dry out the roots of the plant
This ensures the plant dies off and does not re-root
It was great to be outside, working alongside colleagues and I enjoyed the smell of water mint, which was growing alongside the Himalayan balsam in places, and will no-doubt now flourish without being shaded out by the invasive invader we’d spent the day removing.
Would you be interested in joining us for a balsam bashing volunteer day in 2024? Get in touch! These volunteer days are held all across our project area (including Highland/Eastern Perthshire, Angus, Aberdeenshire, Moray and northern Highlands) in July and August. Contact: sisi@nature.scot for more information.
The Scottish Invasive Species Initiative was delighted to have Tony Martin of the Waterlife Recovery Trust attend and present at our recent project conference in Aviemore. Tony leads work which controls and is close to eradicating the American mink from a sizeable chunk of East Anglia using volunteers and an extensive network of smart traps. In this blog he tells us about this work and offers his thoughts and ambitions for a “mink free GB”. The Waterlife Recovery Trust approach to things is in some ways very different to ours in the north of Scotland but there are, of course, many similarities. We share the same objective of delivering American mink control at landscape scale working with volunteers and communities – and it’s always good to hear of different tactics and to share knowledge and experience to learn and improve as we go along. We look forward to seeing how the project progresses over the coming years.
Despite decades of trapping costing millions of pounds, American mink remain firmly established in Britain’s countryside from the south coast of England to the north of Scotland. It’s hardly surprising, therefore, that few people would give any credence to the idea that mink could be entirely eradicated from this rather large island of ours. It’s a completely barking mad concept, obviously.
I had the privilege of leading the rodent eradication project on the sub-Antarctic island of South Georgia – an equally preposterous concept. Who in their right mind would believe it possible to eliminate every single one of the millions of rodents on this huge, mountainous, glacier-riven island, a thousand miles from anywhere, with no roads or access by air? But we did it, and in so doing I learned an important lesson – that it’s foolish to dismiss even the daftest idea without giving it proper consideration. Might mink eradication in Britain be possible, after all? Would it not be worth carrying out a trial to discover if it might be feasible?
Pest eradications can only work if the area to be ‘treated’ cannot be readily re-invaded. Usually the barrier to re-invasion is the sea, which is why small islands lend themselves to this process. But a meaningful trial of mink eradication would need to cover a very large area (5,000 sq km, say), and there are no islands of a suitable size with mink on them in Britain. Even Lewis is less than 2,000 sq km in extent. The next best thing might be a large peninsula, with effort put in place to stop re-invasion from its landward side. I live in East Anglia, which happens to be a large peninsula, sort of…..
A meeting of interested parties in Sept 2019 confirmed enthusiasm for a landscape-scale mink eradication trial involving many tens of partner organisations, and the Waterlife Recovery East (WRE) project was born. So far, so promising, but how could we collectively do so much better than the very many organisations up and down the country that had been trapping mink for decades and doing little more than holding back the tide in most places? The answer was in four parts, though we didn’t know that at the beginning.
A female mink in a trap.
The first part was easy – increasing collaboration and cooperation. A Steering Group of key stakeholders was set up and has continued to meet quarterly. The Steering Group discusses and agrees matters such as methodology, Best Practices, fund raising and strategy, ensuring a consistent, effective, safe and humane way of removing mink across the region. The second part was establishing the scientific basis for the strategy. To be successful, the project would need to be adaptive – continuously learning and improving as evidence dictated. That evidence would come from close examination of the mink caught, and from keeping a close eye on changes in the Catch Per Unit Effort (CPUE), a proxy for mink abundance – number of mink caught per thousand trap nights, to aid targeting of traps and volunteer effort. To that end, every mink caught would need to be measured, weighed, DNA sampled (the tip of an ear is sufficient) and teeth taken to determine age.
The third and fourth factors were to do with the practical process of mink removal. Aerial spreading of toxic bait, as used in many pest eradication campaigns worldwide (including on South Georgia) was not practical for many reasons, and trapping was the next best option. The question was whether we could find ways to improve the efficacy of trapping to the extent that literally every mink could be captured, while at the same time avoiding harming the good guys – the native wildlife we seek to protect. The two elements we focused on were (a) making trapping far less labour intensive than hitherto, and (b) increasing the probability that a mink near a trap would be enticed to enter it.
An adult male mink about to enter the trap on a raft, having circumvented the water vole excluding wall around the entrance.
We tackled the first problem by taking advantage of electronic boxes that alert the trapper when a trap door closes; we call them Remote Monitoring Devices (RMDs). These boxes (one per trap, turning it into a ‘smart’ trap) use the cellular phone system to send alerts by email and text message with 100% reliability, and their use means that a trap visit need only be made when there’s a high probability of an animal being in the trap, rather than daily. This reduces labour (and often fuel) by up to 98%. These huge efficiency gains mean that traps can be active 24/7/365 at every site, other than when temporary retreat is demanded by flash flooding, and that’s crucial. Trapping effort per location is far greater than is normally achieved with a traditional raft fitted with a clay pad to detect mink footprints. We detect mink by catching them, rather than by looking for their footprints.
The second issue was approached by recognising what every mink trapper knows – that a second mink will often follow a first mink into a trap, within days or even hours. They do so because of the scent left by the first animal, and that eye-watering scent mostly comes from glands either side of the anus. We now harvest that eau de mink from every animal captured, carefully expressing it, drop by noxious drop, onto roll-your-own cigarette filters. The filters are then stored in a freezer until used as scent bait in our traps, suspended above the treadle inside a hollow practice golf ball. And they work – there’s now plenty of evidence to show that mink are drawn into traps by following this scent to its source.
This adult female mink was obsessed with the scent in the practice golf ball.
So far, so good, but back to the eradication trial – how could the test area (termed the ‘Core Area’) be isolated from the rest of Britain, stopping mink immigration from untrapped areas? The answer was to use East Anglia’s natural defence – the sea – to prevent incursion from the north and east, and to establish a 60 km-wide ‘Buffer Zone’ of traps to stop inward movement from the west and south (see Map 1). The Core Area comprises a large number of contiguous river catchments covering the central and eastern portions of Norfolk and Suffolk, totalling 5,853 sq km, while the Buffer Zone covers 10,423 sq km. Together, they amount to 12.5% of England.
Map 1: The Waterlife Recovery East project area in East Anglia, covering the counties of Norfolk, Suffolk, Essex and Cambridgeshire. The Core Area covers 5,833 sq km and the Buffer Zone amounts to a further 10,423 sq km. Together, they comprise 12.5% of England.
Another question was how we would define trial success. Would an absence of mink in the area for a day suffice? Or for a week or a year? And how would we know if that had been achieved? We can’t expect to mobilise East Anglia’s entire population to look for mink on a particular night, let alone every night for a year. Furthermore, perhaps it’s not necessary to remove every mink – eradication would inevitably ensue if mink remained, but all of one gender, or if reproduction stopped. In the end, the decision was made to define trial success as the lack of evidence of reproduction over a 12-month period despite substantial search effort. We could never expect to prove that no reproducton had occurred, no more than we can prove that the Loch Ness Monster is a myth. But we would expect even one mink family to come to our attention, either through a report from a member of the public (as frequently happens from far and wide – a live sighting or a roadkill) or by way of the capture of a very young mink or a lactating female.
With funding from Natural England, water companies, Internal Drainage Boards (IDB) and private donors, and the participation of many hundreds of volunteers, reserve wardens, IDB staff etc, a comprehensive network of electronically-monitored traps was set up across East Anglia during 2020 and 2021, in both the Core Area and Buffer Zone. The average trap density across the Core Area was just one per 18 sq km. Catches were high initially, as was catch per unit effort (CPUE), but both rapidly diminished (see Figures 1 and 2). We found that, on average, CPUE dropped by some 70% each year, which means that fewer than 1% would remain after just 4 years.
Figure 1: Number of mink captured per year in the Buffer Zone and Core Area. The catches peaked in 2021, when a large number of new traps was deployed (and remain in place).
Figure 2: Catch per Unit Effort (CPUE) by year in the Buffer Zone and Core Area. This is the number of mink caught per thousand trap nights, and is a good proxy for mink abundance. The value for the Core Area in 2023 indicates that, on average, an active trap catches one mink per 30 years of operation.
So,the big question: is mink eradication feasible on a landscape scale in England? Remarkably, the tentative answer is ‘Yes, it is’. We almost reached the point of zero reproduction in the Core Area in 2022, before belatedly hearing of an unconfirmed but persuasive sighting of a single mink family in eastern Norfolk. The 2023 breeding season has, though, come and gone with no evidence of mink reproduction despite many thousands of hours of sighting effort, and over 106,000 trap nights of catch effort. We’re not quite ready to declare the trial to be over, but that will happen if no evidence of breeding in 2023 comes to light very soon. The occasional mink does turn up in a trap, but the genetic evidence indicates these are probably immigrants that have found their way in to the Core Area along the coast. We are now in little doubt that the eradication of American mink is entirely feasible in England, and almost certainly in Wales, too. What’s more, this could be achieved within no more than five years of setting up a smart trap network, and substantially through the efforts of trained volunteers.
With the mink gone, water voles are now becoming a nuisance – forever setting off our traps.
So, what about Scotland? Is mink eradication feasible here? Although there are certainly greater challenges (lower density of people to visit traps, poor to no mobile coverage in some areas, access difficulties in winter, waterways in spate after heavy rains among them), and costs would be greater per unit area in consequence, I suspect that Scottish ingenuity and determination would win through in most mainland regions. The west coast and western isles do pose huge difficulties, though, and I’m unsure whether all mink could be removed from this vast and complex area with existing technology and methodology. There are two new tools on the horizon that may help in even these remote and windswept places, though. Firstly, a satellite-linked RMD is likely to be available within a year, so traps in even the most remote spots can then be electronically monitored. Secondly, a synthetic version of mink lure should soon be available, closely mimicking the real thing, but dispensed from handy containers which every trapper can carry in their kit. Together, these two innovations should bring a mink-free Scotland that bit closer.
I sign off from a train to Oban. I have been invited to Lismore and Mull this week, with a view to seeing if smart traps can enhance the efficiency of trapping mink in western Scotland, as they have in England. Mink are threatening to force the closure of an organic, free-range poultry business on Lismore, so the stakes are high. I very much look forward to what I’m sure will be an educational and enjoyable visit for this resident of the flat Fenlands of Cambridgeshire.