Into the shadows

Victoria Franklin – Conservation Graduate Trainee

Thanks to archaeologists and historians we know a lot about the people who lived and worked in the historic landscape, but less about the shape and ecology of the landscape. There have been a lot of theories by ecologists such as Frans Vera and George Peterken, who suggest that the landscape was fluid with more wood pasture rather than the closed canopy dense woodlands we’re more familiar with today.

Historic woodlands were a hub of life, providing fodder for livestock and materials for villagers, farmers, tanners, blacksmiths, carpenters, broom whittlers and charcoal makers. Trees were even a source for medicine, for example the bark of Pedunculate Oak Quercus robur was used as an antiseptic and Ash Fraxinus excelsior was steeped into tea and used to aid kidney problems. This eco-cultural hub seems a far cry from how we see woods today, often used as a place of tranquillity, for bird watching or to seek refuge from everyday life.

Over the past year I’ve been researching ‘Shadow Woods’ – areas where there was woodland in the past that is no longer there. These, now shadows of a former landscape, can be identified in a number of ways. As a starting point for the search, the Doomsday Book and historic Tithe and Enclosure maps can give an indication of how the landscape once looked. Researching old place and field names such as ‘Hagg’ meaning an area where trees were felled or ‘Hollin’ historically a word for Holly or browse, also give clues as to the location of previously wooded areas.

With permission from land managers, we followed up on potential sites by surveying for any ancient woodland indicator species, ground flora that has colonised over generations and gives an indication that the area has been continually wooded for a considerable length of time. These species will change from woodland to woodland and throughout the country, but include Bluebells Hyacinthoides non-scripta, Honeysuckle Lonicera periclymenum, Ramsons Allium ursinum, Wood sorrel ‎Oxalis acetosella, Early purple orchids Orchis mascula, Primroses Primula vulgaris and Climbing corydalis Ceratocapnos claviculata. These plants continue to flower long after the surrounding woodland has gone. The residual flora and soils in these spaces are irreplaceable.  

Primroses Primula vulgaris, Wood anemone Anemonoides nemorosa amongst bracken and Hawthorn Crataegus monogyna scrub. Copyright NYMNPA.
Primroses Primula vulgaris, Wood anemone Anemonoides nemorosa amongst bracken and Hawthorn Crataegus monogyna scrub. Copyright NYMNPA.

Early purple orchids Orchis mascula and Primroses Primula vulgaris, strong evidence that the area is a Shadow Woodland. Copyright NYMNPA.
Early purple orchids Orchis mascula and Primroses Primula vulgaris, strong evidence that the area is a Shadow Woodland. Copyright NYMNPA

Any remaining veteran and ancient trees were surveyed for signs of being worked, which gives another glimpse into the past history of the wood. Coppiced trees such as willow were cut at the base when they are relatively young and the wood was used to make fences and shelters. Pollarded trees were cut just above the trunk to provide timber and fodder for animals leaving the tree alive to produce more wood in future years. An historically pollarded tree can be identified by having multiple branches.

Historically coppiced Willow.. Copyright NYMNPA.
Historically coppiced Willow. Copyright NYMNPA.

Ancient and Veteran trees are home to a whole host of deadwood beetles, fungi, lichen mosses and plants that cannot live anywhere else. These trees, botanical indicators and the soil of ancient and shadow woods are irreplaceable micro-habitats that have taken generations to create, once lost they will be gone forever.

The Shadow Wood sites surveyed within the North York Moors National Park were all in upland locations, many in remoter areas with little human disturbance since they were worked woodlands. The majority of these sites have been classed as grassland or as scattered parkland with a small amount of ancient or veteran trees. This classification strengthens the idea that the historic landscape was often open wood pasture rather than closed canopy woodlands.  

The hope is that identified sites can be targeted for woodland creation in the North York Moors National Park, therefore continuing and restoring life in these magical habitats, that are not only home to some amazing species and important trees but are a little bit of folklore too.

Image of Shadow Woodland in the North York Moors. Copyright NYMNPA.
Shadow woodland in the North York Moors. Copyright NYMNPA.

The Shadow Woods project within the North York Moors National Park has only been possible due to the dedicated work of Professor Ian Rotherham. His book Shadow Woods: a search for lost landscapes and publication Shadow Woods and Ghosts Survey Guide by C. Handley and I. D. Rotherham have provided invaluable research into these almost lost landscapes.

Water Environment Grant (WEG): Keeping life on the bank

Christopher Watt – River Esk WEG Project Officer

Creating and expanding riparian woodland is a large component of the current WEG* funded project in the Esk Catchment, in conjunction with improving farm infrastructure. Riparian woodland is defined as trees located on the natural banks of waterbodies such as rivers, canels, ponds and lakes. The presence of riparian woodland brings an array of environmental benefits such as carbon capture, regulation of water temperature, bank stabilsation and provision of resources for wildlife. Riparian woodland is important feature of the Esk and provides benefits to conservation focus species in particular Freshwater pearl mussel (Margaritifera margaritifera), but also Atlantic salmon (Salmo salar) and Sea trout (Salmo trutta).This is why tree-planting efforts have been prioritized with project distribution located in both the upper and lower parts of the catchment.

Existing riparian woodland along the Esk. Copyright Chris Watt, NYMNPA.

Riparian woodland creation has focused on introducing a mix of tree species to the bankside to enhance structure and composition. Species which have a tolerance for wet conditions and partial submergence such as alder, aspen, birch and willow make a significant contribution to the mix. Other species such as alder-buckthorn, hazel, hawthorn and oak add additional variety. Planting design has incorporated adding open spaces such as rides and glades into the new small scale woodland as these are valuable habitats in their own right. All new woodland projects have an emphasis on long-term management to maintain habitat function with actions such as deadwood retention, grass-margin establishment, coppicing, pollarding and recycling tree-guards included in management plans. The vision is for these small scale woodlands to stabilize banksides, intercept agricultural run-off and reduce sedimentation entering into the Esk, leading to improvements in water-quality. Monitoring will record physical and biological change through measures fixed-point photography, vegetation monitoring and species recording.

Despite the ongoing challenges of the Covid situation and fickle weather conditions, work has been progressing on the Esk catchment with 2,095 new trees planted with much assistance from land managers, staff and volunteers. Planting efforts will continue with the aim to have all 3,000 remaining trees in the ground by March. This will also be accompanied by the planting of 1,060m of new hedgerows, wetland creation and bank stabilization works. Along with the habitat creation and enhancement works, measures to improve farm infrastructure are continuing such as concrete yard renewal, installation of sediment traps and rainwater guttering. Combined these efforts seek to work at the farm-level and tackle pollution pathways from yard/field to river and lead to the improvement of water-quality of this special river.

Tree planting volunteers, Botton in Danby Dale. Copyright NYMNPA.

 All work carried out has been in line with current COVID restrictions and guidelines at the time. To keep up to date with the latest National Park situation in regards Covid-19 – see here.  

Esk winter landscape. Copyright Chris Watt, NYMNPA.

*WEG stands for Water Environment Grant which has been providing funding to improve the water environment in rural England. This has been part funded by the European Agricultural Fund for Rural Development.

The European Agricultural Fund for Rural Development: Europe investing in rural areas

 

The European Agricultural Fund for Rural Development: Europe investing in rural areas

Woodland enterprise

Raincliffe Wood Community Enterprise was set up back in 2016 to take on the management of Raincliffe, Forge Valley and Row Brow Woods near Scarborough. Their mission is to build a strong community enterprise that secures a safe and sustainable future for the woods while enhancing wildlife and community benefits.

 

They’ve been working ever since to restore these ancient woodlands to predominantly broadleaf with all the biodiversity benefits that brings to this important area. Part of it is a National Nature Reserve and the area also includes the Raincliffe & Forge Valley Woods Site of Special Scientific Interest (SSSI) because of its sequence of woodland types rich with botany, birds and other animals. The historic environment is also full of features related to past industry and endeavour such as charcoal platforms and a forge. The Community/Social Enterprise aspect means income generated through woodland management today is used to help make the ongoing management sustainable and also to provide associated activities such as improving access, increasing community involvement and providing education.

 

Recently the National Park Authority have been working with Raincliffe Wood Community Enterprise (RWCE) and others to carry out works in the woods to get rid of litter, keep access open, and tackle rhododendron. Have a look at the RWCE’s recent Working Together blog post to find out more and to keep up to date about future plans.

Raincliffe Woods - https://www.raincliffewoods.co.uk/

Planting for the future: Part Two

Alasdair Fagan – Woodland Creation Officer

In a previous blog I talked about the importance of collecting and growing on tree seed from the North York Moors and the benefits of a combined genetic approach to planting woodlands to provide them with the best chance of withstanding climate change impacts in the future.

It is now widely accepted that tree planting has a major part to play in helping to offset the emissions contributing to global warming. The UK is committed to reducing carbon emissions by 80% (compared to 1990 levels) by 2050. A recent study by The Crowther Lab of ETH Zurich suggests that a global effort to plant one trillion trees can have a huge potential to tackle climate change. 

The 25 year Environment Plan released in 2018 outlines governmental ambitions to plant 11 million trees in new woodlands by 2021 through national grant schemes such as Countryside Stewardship and the Woodland Carbon Fund administered and regulated by the Forestry Commission.

The sequestration of carbon is one huge benefit provided by trees, but planting trees can have numerous smaller scale advantages too including;

  • Significant benefits to biodiversity
  • Creation of a priority habitat
  • Reducing soil erosion
  • Reducing the flow of water downstream
  • Providing shelter to livestock and game

Which leads me onto Woodland Creation in the North York Moors …

Between 2000 and 2017, this National Park saw the planting of over 150 hectares of low density wood pasture/parkland and over 560 hectares of new native woodland; that equates to the planting of over 622,400 native trees!

Looking forward, we have ambitious targets to create 7,000 hectares of ‘environmentally positive’ new woodland over the next 100 years. This will mean we’d plant over 7 million trees! This will increase woodland cover from 23% to 25% of the National Park.

Skipster Hag - woodland creation project planted in 2012. Copyright NYMNPA.

But we’re not gung-ho about it. Every woodland creation proposal is carefully planned and there are many considerations to be examined and consultations to be carried out during the developmental stages of each individual project. Things to think about include:

  • Existing ecology and habitats
  • Existing archaeology and cultural heritage features and records
  • Current land sse
  • Soils
  • Woodland networks in the landscape
  • Public Access and Rights of Way
  • Landscaping impacts
  • Impacts on groundwater
  • Appropriate species
  • Provenance of seed/trees
  • Future impacts of Climate Change (ESC tool)
  • Tree pests and diseases (chalara, alder rust etc)
  • Land designations (e.g. SSSI, SAC, SPA)
  • Open Access Land
  • Parish Council
  • Inclusion on Public Register
  • Neighbouring landowners
  • Environmental Impact Assessment (if over 2 ha)
  • Services

Planting at Oakley Side, Danby - to extend existing native woodland. Copyright NYMNPA.

Rievaulx - planting to restore ancient wood pasture habitat. Copyright NYMNPA.

Shadow Woodland - woodland plants such as bluebells show us where woodlands used to exist. Copyright NYMNPA.

Each project has its own issues and individualities. Here are three examples of woodland creation projects over the last couple of years.

Cam House, Bilsdale

This woodland creation project in Bilsdale is a large planting scheme of over 15 hectares. There are 17,825 trees planted of 18 different species.

The site varies somewhat in terms of hydrology with some areas being particularly wet. These areas are planted with species that prefer wetter ground (willows and alder) but the majority of the site is planted as diverse oak and hazel woodland, with other species such as birch, holly, wild cherry and crab apple included to provide maximum climate change resilience and benefit for biodiversity.

Aspen has been included to further futureproof the woodland against potential issues such as climate change and disease, after consulting the ecological site classification software for the site. This is an online tool used to calculate what the suitability of particular tree species are to potential planting sites. The tool uses information such as soil wetness, soil PH, wind exposure and climate data to estimate how well trees will grow. It also usefully has a future projections function which is linked to the Met Office’s future climate data, which allows us to try to predict how a changing climate might alter the site and suitability for tree species – some will become less suited to the site and others will become more suitable, such as aspen.

Planting at Cam House, Bilsdale. Copyright NYMNPA.

 Ayton Banks

Ayton Banks is a site that is extensively covered in dense stands of bracken. The landowner’s primary objective for the planting is to sustainably control the bracken long term whilst creating a diverse woodland habitat. 8,610 trees were planted across 5.43 hectares using site appropriate native species such as oak, hazel, birch and rowan.

The wider Ayton Banks site is an historic Alum Works, now a Scheduled Monument. The proposals for woodland planting were carefully developed with the National Park Authority’s Historic Environment Team to ensure that none of the sensitive areas of the monument are influenced by the project.

Planting at Ayton Banks. Copyright NYMNPA.

 Howe End, Danby

This lowland planting project presented the perfect opportunity to work with volunteers and other groups due to its proximity to our National Park Centre at Danby, the ease of access and parking, and the cooperation of the landowner (who is a National Park Volunteer).

3,500 trees were planted over two months by a wide variety of volunteer groups as well as local primary school children, National Park staff and apprentices.

Planting at Howe End, Danby. Copyright NYMNPA.

If you have a potential Woodland Creation project in mind then please visit our website page for more information or contact me via the National Park Office 01439 772700 or by email.

Autumn delights

Gallery

This gallery contains 26 photos.

It’s UK Fungus Day today. There are many many different types of fungi – classifications and relationships are still being expounded by experts. Sometimes sparsity of knowledge can be intriguing but with fungi the more knowledge acquired the more fascination … Continue reading

Local communities

Alasdair Fagan – Woodland Creation Officer

My job here at the National Park Authority means that I get the opportunity to be out and about in the North York Moors and get to places that most don’t get the opportunity to see. These hidden places are special for all sorts of reasons, in particular I get the chance to see some extraordinary woodlands – I admit I might be a little biased.

Recently we were out monitoring a woodland planting project near Castleton which meant we had to trek through a small existing woodland to get there. This was a combination of well-developed riparian (wet) flood plain woodland along river margins, wet marshy grassland filled with flowering plants and ancient woodland remnants creeping up the valley sides including oak, birch, hazel, alder and willow. Many of the woodland spring flowers were still in bloom and the woods were a lush green and bursting with insect and bird life.

Ancient Semi Natural Woodland site. Copyright Alasdair Fagan, NYMNPA.

As we approached the edge of this woodland I noticed something wriggling in the grass – it was a slow worm! Coming across this legless lizard species (Anguis fragilis) was a first time for me. Obviously I wouldn’t usually pick up/disturb wildlife but in this case I took the opportunity to move the slow worm to the cover of an old iron sheet as they are quite high up on the menu for many predatory species (birds, adders, badgers etc.).

Slow worm - copyright Alasdair Fagan, NYMNPA.

On the way back as we ducked, scrambled and tramped back through the same woodland I almost tripped over what can only be described as a large mound of leaf litter on the edge of a clearing. As I looked a little closer I noticed that the surface of the mound was moving – it was alive with wood ants! I was surprised to see them here as. I previously worked in Scotland and had always associated wood ants with more northern forest habitats. But they were definitely wood ants and they are surely an indicator that this particular woodland is in good ecological health.

Close up of a Northern hairy wood ant. Copyright Alasdair Fagan, NYMNPA.

Northern Hairy Wood ants (Formica lugubris) are a species of wood ant found in Scotland and in only two areas in England – the Peak District and the North York Moors. They are a fascinating species – I’m no expert yet but here are a few facts about our internationally important Northern Hairy Wood Ants:

  • The Northern Hairy Wood Ant currently has a near-threatened conservation status.
  • Northern Hairy Wood Ants ‘farm’ sap-sucking aphids (that favour oak and birch) for their honeydew. They gently stroke the backs of the aphids which then produce the sugar rich liquid in exchange for protection, and the ants use it to feed their young.
  • The ants take specific roles in the aphid farming process including; ‘shepherds’ who collect the honeydew, ‘transporters’ that move the honeydew to their nest, ‘guards’ that protect their aphids from competitors, and ‘scouts’ that search out new aphid colonies.
  • They employ a polydomous (many homes) nesting strategy whereby they have a number of nest mounds which operate as a single colony. The founding of additional nests allows for the expansion of the colony allowing it to grow and capitalise on new foraging and feeding opportunities spreading out through suitable habitat. If a smaller outlying nest is attacked or in danger then it will be abandoned and the inhabitants will return to the central nest.
  • Similar to other ants foraging workers leave pheromone trails, to good nectar sites or to groups of aphids, which direct other foragers to these valuable resources. The trails can persist for months.
  • The nest mounds of Northern Hairy Wood ants provide accomodating habitat for other invertebrates too. These include a variety of beetle species as well as the Shining guest ant (Formicoxenus nitidulus). This ant species lives within wood ant nesting colonies, accepting food from the host species and establishing its own discrete nests inside hollow twigs within the larger nest, raising its own brood. The Shining guest ant is a species of conservation interest, a priority species of the UK Biodiversity Action Plan and listed as ‘vulnerable’ on the IUCN red list.

Northern hairy wood ant nest - if you look carefully you can just make out the well camouflaged orange/black coloured ants. Copyright Alasdair Fagan, NYMNPA.

The intricacies of woodland ecology are often complex and astounding. My job means I work on woodland planting and creation and by the very nature of the timespan of trees I know that I’m likely never to see these new woodlands in their future glory. Therefore it’s very important to me to keep a perspective, looking at woodlands at a landscape and spatial scale and considering woodlands over their likely lifetime. Woodland visits like this one are what inspire me to want to create new woodlands and plant more trees, to establish the woodlands of the future.

If you might be interested in creating woodland in the North York Moors and would like more information about opportunities please contact me or call on 01439 772700.

Updating the landscape

This is a good example of the time and effort it can take to change a landscape for the better.

The Trennet Bank Project was initiated back in 2013 (although the wish to do something here had existed for much longer than that). We’ve now achieved the major part of the planned work with the removal of conifers and the start of the gradual restoration of the site to moorland and native woodland.

Trennet Bank is on the eastern edge of Bilsdale West Moor, just west of the village of Chop Gate. Set on the top of the bank was Trennet Plantation, a 20 hectare 20th century conifer plantation (Sitka spruce and Lodgepole pine) planted on moorland in the late 70s/early 80s. Since then the plantation was identified as an inappropriate forestry development at this location in terms of landscape and environment. Because it was so high on the horizon it stood out on the skyline from a number of vantage points and because it was surrounded on three sides by important moorland (designated Site of Special Scientific Interest, Special Protection Area, Special Ara of Conservation) it was isolated from other woodland. In fact it stuck out like a sore thumb.

In addition, there was no future as a working plantation (plant-grow-fell) as it had become uneconomic to manage and harvest the timber, because of its location. So the trees would eventually start to be blown over leaving very little ground vegetation and therefore this would lead to erosion.

From a National Park Authority point of view Trennet Bank Plantation provided an ideal example of where to put into practice the North York Moors Management Plan policy – The removal of plantations from inappropriate sites will be supported where this will deliver landscape enhancement or other environmental benefits.

What happened…

The first requirement was the creation of a temporary access route from the plantation on the hillside down to the farm below and then onto the main road. This was a more achievable alternative to trying to take the trees up over the designated moorland. It meant building up the existing track including the provision of a new bridge so that the route could be used by timber lorries, and by machinery accessing the site to fell the trees. Subsequently once the conifer removal was completed the track was reinstated to ensure it was suitable for continued farm use. During and after the work, farm stock had to continue to be managed with fencing and gates, to allow the farm to function.

To remove the conifers a felling licence was required from the Forestry Commission. A felling licence requires a commitment to replant so there is no net loss of woodland. As the idea for Trennet Bank was to remove the existing woodland, the subsequent native woodland and wood pasture planned for the site wouldn’t amount to the required 20 hectares. Mark Antcliff, Woodland Officer, undertook the challenge to establish enough alternative planting sites in the wider area to ensure there was no let loss. In all, nearly 36 hectares of new compensatory woodland was established including on the plantation site and also in other appropriate locations such as bracken dominated moor edge, thanks to willing landowners and land managers.

With the access route improved and the felling licence in place the removal of timber started in the summer of 2015, and was completed by November 2016. The timber was of reasonable quality because the trees were over 30 years old and so could be sold on with some of the money made covering some of the costs entailed. The work also created large amounts of brash, some of which remains on the site to decay naturally and some of which was removed to be used as biomass.

In the winter of 2016/17 part of the felled site was replanted with oak and hazel, leaving the remainder (80% of the site) to naturally revert to heath and mire. The planted trees will need to be managed over the next three years to ensure they become established.

Establishing wood pasture on Trennet Bank. Copyright NYMNPA.

Lessons learnt for other potential large scale projects…

  • This turned out to be a major project for one Woodland Officer, with occasional assistance. A project of this scale and complexity would be helped by having a project manager on the ground.
  • Unavoidably the project relies on the good will and co-operation of landowners and tenants. It just couldn’t have happened otherwise.
  • In all, because of the complexity of the project, seven different agreements were required to be brokered by the Authority.

In the end a lot of time and resource was spent over a number of years, and as a result the landscape and environment of this part of the North York Moors has been significantly enhanced.

Planting for the future

Alasdair Fagan – Woodland Creation Officer

I believe that most people like the idea of trees being planted – as long as they are in the ‘right place’. Small, negligible seeds unfurling to create little, delicate saplings growing on and upwards into woody giants that dominate a landscape.

But why would we purposefully plant trees?  Here are some of the benefits that tree planting/woodland creation can provide.

Habitat

Each individual tree provides a habitats. Wooded habitats are some of the most diverse habitats in England; with many birds, mammals, insects and plants specialising in woodland environments these habitats are critical for biodiversity. Creating even small areas of woodland has the potential to greatly increase the number of species in almost any landscape.
Lesser? redpoll (woodland/wetland bird). Copyright Liz Bassindale, Howardian Hills AONB.

Lesser? redpoll  – this RSPB Red status bird has suffered severe population declines in the UK. It relies on wet woodland species like birch and alder.

Connectivity

It is important to look at woodlands from a landscape scale. Connectivity is the word used to evaluate how connected/joined up otherwise isolated fragments of habitat are. It is always a big advantage for tree planting if it helps to connect existing woodland areas and so allows woodland species to move freely across the landscape.

Newly planted woodland near Skipster Hagg Woods. Copyright NYMNPA.

Newly planted woodland near Skipster Hagg Woods, Appleton le Moors. The word Hagg suggests the land here has long been wooded. This new planting is an extension of an existing native woodland, which should improve connectivity through the landscape.

Water quality and retention

It is now widely accepted that planting trees and woodlands has benefits for the management of water catchments. Woodland filters sediment and nutrient run off from the land if planted between the source and a watercourse, and so can greatly improve water quality. Also when trees are planted along a river catchment they can help to slow down the flooding effects of heavy rainfall events by increasing the porosity of the soil. Water is more readily absorbed into the soil, thanks to the roots of trees, before being released into water courses of the catchment.

Bank stabilisation

Just as trees can slow down the movement of water they can also minimise the movement of landforms. The roots of trees help bind and stabilise river banks and hill sides. Trees hold landforms together minimising erosion and the displacement of soil, the effects of which can in some cases be devastating.

Small scale riparian woodland planting. Copyright NYMNPA.

Small scale riparian woodland planting in the Esk Catchment. The opposite bank is slumping and loosing soil resource into the water. 

Shelter

Trees and woodland copses carefully located on a holding can provide useful shelter for livestock and gamebirds. It has been demonstrated that shelter provided by trees has resulted in significant reductions in cold, wet and windy weather lamb losses.
Highland Cattle on Levisham Estate. Copyright Ami Walker, NYMNPA.

Highland Cattle on Levisham Estate taking advantage of the the woodland cover on a hot day.

Climate Change

One of the causes of climate change is the release of greenhouse gases (e.g. carbon dioxide) into the earth’s atmosphere trapping heat. Trees produce energy to live and grow by using sunlight to convert water and carbon dioxide through photosynthesis; a process which produces oxygen. So trees are using up Carbon Dioxide, storing carbon and generating essential oxygen.

Amenity 

As well as providing a land management tool, the presence of trees and woodlands can have positive impacts on the health and wellbeing of people. Trees and woodland are intrinsic to many landscapes, particularly so in the North York Moors. Woodlands provide amenity value as local cultural assets that can last for generations if looked after properly. Imagine the feeling of personal achievement in planting a new woodland that will grow and mature into the future, making a living mark on an evolving landscape beyond the constraints of a human lifetime.

View from Chimney Bank down into Rosedale. Copyright NYMNPA.

View from Chimney Bank down into Rosedale. Trees in the right place can really compliment the landscape and add amenity value from notable viewpoints.

The National Park Authority is looking for landowners and partners to create new woodland across the North York Moors. Funding is available for deciduous woodland planting projects of 1 hectare (2.5 acres) and above; the funding can cover the total costs of planting and establishment. If you are interested and would like more information please contact me by email or ring me on 01439 772700.

Letter from Scotland

Sam Jones – previous River Esk Project Student

I still recall the morning as, fresh-faced and hopeful, I sat in the back of a bus trundling along country roads towards the North York Moors. As we turned a corner and crested a ridge I was gifted my first view of the National Park and I could feel butterflies in my stomach, this would be my first real job in conservation. This was the start of my life serving the environment as I saw it then (and still do now I suppose). That was about four years ago, things have moved on quite a bit since then.

I worked for the National Park Authority on a year in industry placement back in my third year of University assisting with the Esk Pearl Mussel Salmon Recovery Project lead by Simon Hirst aimed at conserving the remaining Freshwater pearl mussel population in the River Esk. It was a wonderful and varied experience.

At the end of my time I spent a week wading through ocherous becks in the very upper reaches of the Murk Esk. I was rather cheekily using my last few weeks working at the National Park to collect data for my upcoming final year project. I collected samples of upland invertebrates from becks through moorland and coniferous woodland to test the effects of acidification on aquatic life, and to see how the impacts of acidic moorland and plantation woodlands compare. My project has now been published although you need journal access to see the whole thing. Simon has asked me for a basic summary of my findings and conclusions – so here goes…

I used aquatic invertebrates as indicators of environmental degradation. It’s well recognised that moorlands and uplands can have acidification issues, and the North York Moors may well be one of the most extreme areas for it in the UK with its nearby zones of industry. Acid issues have been recorded in local becks in the past, including severe fish kills. However my results were a little surprising. Originally I thought that plantation woodland, being the newer and least natural habitat (compared to moorland which is also man-made habitat), and having less ability to slow down and buffer the incoming water, would have a much more degraded community. However, my results showed significantly more acid sensitive species living in the woodlands than the moorland. This was despite the fact that previous studies had recorded lower pH values (i.e. more acidic) in plantations than in moorlands. I think that the reason for this is the woodlands provide a more diverse and richer freshwater environment for the invertebrates to live in. This is a good sign as it shows that the conifer plantation woodland, that so much of our countryside is dominated by, may not have such a bad effect on aquatic life as once assumed. The aquatic communities were also generally healthier than would have been expected given the severe acidification. I think this shows that the species of invertebrates living in the uplands of the North York Moors are well adapted for highly acid conditions and that, despite the seemingly poor chemical results, life in the upland becks is thriving.

What happened next? After I graduated from the University of York I went on to work for Natural England, the Environment Agency and now I’m part of an ecological consultancy. I’ve come full circle, and recently I was lucky enough to get accepted for a PhD up in Inverness studying Freshwater pearl mussels. Apparently they needed someone with more waders and bucket experience than lab experience, and I fitted the bill.

Scotland is one the great bastions of the Freshwater pearl mussels with populations of tens of thousands in numerous rivers and multiple populations with favourable age structures and reproductive ability (unlike in the Esk sadly). As such, my PhD is to study these populations and monitor them using traditional methods. However the focus of the investigation is to allow comparison of conventional survey methods with new eDNA techniques. Environmental DNA (eDNA) is a method of monitoring species or habitats using the DNA that is freely found in the environment. All organisms living in an environment discard DNA, whether through waste, dead cells, carcasses, etc. and this can be picked up in trace amounts in water, soil, and even air. With Freshwater pearl mussels the hope is that DNA markers and techniques can be designed to allow detection of small or isolated populations of pearl mussels in rivers simply from a scoop of river water downstream of these prospective populations. There is also potential that the techniques could be used to monitor the size, health and population structure of these populations and perhaps even help identify sub species or genetically distinct populations. Whether this is possible or not, the possibility of cheaper and easier monitoring of pearl mussels fundamentally helps with conservation efforts.

I’m hoping to be able to keep Simon and the Esk Project up to date with our findings and perhaps provide some new information and techniques that may help the Esk’s own struggling mussels over time.

Anyway, that’s my little summary of things. I hope you guys found this interesting.

Thanks for reading, and keep on supporting the National Park,

Sam