WTT Blog Posts

The riparian invasion: salmonid friend or foe?

'Tis the season to bash balsam - if you don't know how to, check out the definitive guide from WTT chum, Theo Pike, for guidance! Timely then for a new blog focussing on invasive plants. Alex Seeney from the Centre for River Ecosystem Science (CRESS) at the University of Stirling, is battling with balsam and knotweed from a more academic angle, and below gives an overview of some his research to date. This valuable work is supported by Scottish Natural Heritage.

Some of the most diverse and complex habitat types in aquatic systems are found at the interface between terrestrial and aquatic communities – the riparian zone. These diverse, dynamic systems provide an ecologically important buffer between land and water, and as such they are of particular importance to the health and quality of the waterways they border.

knotweed invasive species INNS riparian river Seeney trout

The dynamic nature of riparian zones increases their susceptibility to invasion, particularly by non-native flora, which use river networks like blood vessels around the human body, spreading through river corridors and using these systems for both short and long distance dispersal. Invasion of the riparian zone by non-native flora is commonly perceived as a negative occurrence and has a sizeable economic impact, with an estimated £5.6 million spent in 2010 to control riparian Japanese knotweed (Fallopia japonica) in Great Britain.

It is also important to consider how these plants may affect salmonid fish, especially considering the high economic value of salmonids to angling and the status of the Atlantic salmon (Salmo salar) as a protected species in the UK. My aim is to tease apart the effects of invasive riparian plants from a range of environmental factors that affect salmonids, quantifying not only the direction, but also the size of these effects. In doing so, we might take a step towards justifying the large amount of funding that is currently being provided to treat these plants. Monitoring both aquatic and terrestrial invertebrate communities is also important, as both provide essential food sources for salmonids residing in streams and rivers. Changes in the physical and chemical composition of riparian plants may affect both invertebrate groups, altering the type and volume of these food sources entering the aquatic food web.

Whilst searching for field sites for my PhD project in early 2015, the height and depth of the previous year’s invasive plant stands were easy to see. The stands were often wider than the small tributary streams they bordered and as such, tracking the spread of these plants along river corridors is quite a simple process. However, relating the presence of invasive plant stands to hydrological processes and furthermore, to critically important terrestrial and aquatic invertebrate food sources, is more difficult. In order to help me achieve this, a range of samples have been collected over a 2 year fieldwork period during 2015-16.

Alex Seeney PhD fieldwork salmonid trout habitat invasive species river riparian

Field sites were selected based on suitable habitat for adult salmonid spawning and juvenile survival. Sites were located on small tributary streams, and were chosen in communication with fisheries trusts to ensure populations of Atlantic salmon and brown trout (Salmo trutta) in tandem with established stands of Himalayan balsam (Impatiens glandulifera) and Japanese knotweed. A pair of uninvaded control sites were located upstream from a pair of invaded treatment sites on each waterbody, giving a total of 24 sites across 6 rivers. Treatment sites were chosen under the criteria that invasive plant coverage must exceed a minimum of 50% (based on a visual assessment).

In order to monitor physical changes at sites, thalweg profiles (showing the main flow of the river) and cross-sectional riverbed profiles were recorded each year, in tandem with pebble counts to monitor changes in grain size diversity and distribution. Full depletion electrofishing surveys were carried out during summer 2015 and 2016, covering a minimum of 100m2 where possible at all sites. Weights and fork lengths were recorded for all Atlantic salmon and brown trout, and a small number at each site were anaesthetised and a gastric lavage (stomach flushing) was performed to assess diet composition. This procedure was regulated under Home Office licence (Home Office Project Licence PPL 70/8673).

invertebrate riverfly monitoring seeney trout INNS invasive species balsampitfall invertebrate INNS seeney trout

A full range of terrestrial (Malaise and pitfall traps) and aquatic (Surber and drift nets) invertebrate samples were taken during the summer of 2016 to assess the terrestrial and aquatic communities present at each site. These samples will be used to show how the abundance and diversity of both aquatic and terrestrial invertebrate communities (and therefore the availability of prey items for salmonids) differs between invaded and uninvaded sites. Furthermore, vegetation surveys were carried out at all sites during the summer of 2016, which will allow invasive coverage to be expressed on a continuous (as opposed to binary) scale.

The range of samples collected over the past 2 years provides an exciting opportunity to investigate how invasive riparian plants may be affecting juvenile salmonids on a fine scale. Stomach contents and invertebrate samples from both years will be used to assess how different salmonid age classes are utilising the available habitat and food sources between invaded and uninvaded sites. I also plan to use electivity indices to look for evidence of any preferential feeding habits, giving an insight into the effects of invasive riparian plants on species and age-specific groups of juvenile salmonids.

I would welcome any questions or comments, and hope to provide an update in the coming months once the bulk of these samples have been processed – over 50,000 invertebrate samples identified so far!

Alex (alex.seeney@stir.ac.uk or @AlexSeeney)

Can watercress farming directly impact fish communities in chalk streams?

Asa White gets to call wading around in the Bourne Rivulet work! Our research interests in chalk streams have some parallels. While I am curious as to how a colourless, odourless gas (methane) contributes to the fuelling of their food webs, Asa is trying to understand how an equally invisible chemical is affecting invertebrate and fish life. Here, he outlines his research plans and offers up the experience of electric fishing - read on! 

Watercress is native to the chalk streams of southern England, and has been harvested for millennia. In the early 19th century, the advent of the railway made commercial production viable for the first time. A growing London market supplied by trains (the famous ‘Watercress Line’ being one) led to an explosion in the number of watercress farms throughout the south of England. Historically, watercress was grown in gravel beds irrigated by water diverted from chalk streams, but hygiene concerns now oblige growers to irrigate their beds using fresh water abstracted from boreholes. In both instances, the water used to irrigate the beds is discharged into adjacent chalk streams. 

Today, much watercress farming is highly mechanised, with modern practices allowing for year-round production. A number of large-scale modern watercress farms now house washing and packing facilities for the watercress farmed onsite in addition to imported salad leaves. Abstracted water is used to rinse the crop prior to packing, with the spent water returned to the chalk stream. Typically it is first filtered through screens and channelled into settlement ponds or through watercress beds to reduce sediment load before discharge. While sediment is often effectively treated, there is growing concern that the mechanical abrasion of watercress and other salad leaves during the washing process - and to a lesser extent during the harvesting of watercress - induces the release of phenethyl isothiocyanate (PEITC) into the receiving water course.

Watercress possesses the glucosinolate-myronase system; regarded as the classic defence against herbivorous organisms. Damage to watercress tissue initiates the synthesis of PEITC, the compound which gives watercress its hot peppery taste. While pleasing to many human consumers, myself included, PEITC has unsurprisingly been shown to be toxic to a number of aquatic and terrestrial invertebrates. A number of surveys by the Environment Agency have demonstrated altered invertebrate communities downstream of watercress farm outflows. Some expected taxa were found to be absent, along with a significant depletion in a staple year-round component of salmonid diets, Gammarus shrimp. While the impact on invertebrates has been documented, until now the effect of watercress farming on fish populations hasn’t received attention.

Asa White PhD research Brighton watercress salmonid

My research at the University of Brighton comprises three main elements. Firstly, using electric fishing surveys around three watercress farms over two years, I am ascertaining whether discharges are having a population-level impact on fish communities. Secondly, at the same sites, I am surveying habitat suitability for salmonids in terms of the physical habitat and prey species abundances. Lastly, I am running laboratory ecotoxicology experiments to study the effects of PEITC on fish. The aim of the research is understand what effect, if any, watercress farming is having on fish populations. Should a negative impact be uncovered, then mitigation strategies to lessen the impacts could be developed to ensure that fish populations in chalk stream headwaters flourish. 

It is well-known that early life stages of fish are particularly sensitive to pollutants. With salmonids and bullhead spawning in the upper reaches of chalk streams where watercress farming typically occurs, there is a very real potential for developing embryos to be exposed to PEITC. To assess the impact of PEITC exposure, I am running a series of ecotoxicology experiments on fish eggs in the laboratory.  Brown trout are the main focus due to their high value within chalk stream ecosystems, but I have plans to experiment with grayling and at least one cyprinid species.  Last October I exposed brown trout eggs to a range of PEITC concentrations throughout embryonic development. I am currently repeating the experiments using photoperiod eggs obtained this March that I am expecting to hatch around the end of April. If the results from the first experiment are accurately replicated, then I have a very strong dataset for publication. Watch this space!    

My study sites are located around three watercress farms and include sites immediately upstream and downstream of discharges at each farm for direct comparison. To investigate the downstream extent of perturbations caused by discharges, each farm has two further sites, one approximately 500m and another between 1km and 1.5km downstream.  One of the farms is on The Bourne Rivulet, a tributary of The Test in Hampshire, and is owned by VItacress Salads Ltd, a company which has generously part-funded the research through the Vitacress Conservation Trust. This reach boasts a very well-regarded wild trout fishery made famous by Harry Plunket Greene in his 1924 book on fly fishing Where the Bright Waters Meet. A further two farms in Dorset complete the sites; one on the River Frome and the other on the River Crane, a tributary of the River Stour. Both of these farms are located on SSSI perennial chalk river headwaters. So far I have surveyed these sites during spring and autumn in 2016, and I will return to survey them again this year.

The electric fishing at each site is carried out over 100m runs using a standard three run depletion method.  The catch is identified to species level and the standard length and weight of each individual recorded before being returned to the river unharmed. It is important to tease out whether any differences in trout numbers seen downstream of watercress farm discharges are related to the discharge or merely a function of the prevailing conditions such as substrate type, hydrology, plant cover, geographic location etc. I’m addressing this by using detailed habitat surveys fed into HABSCORE software. HABSCORE outputs an estimate of expected salmonid abundances for the given physical habitat, which can then be compared to the actual abundances found during electric fishing.

Using standard three minute kick and sweep sampling, the invertebrate fauna is being surveyed to see if the abundance of suitable prey species for fish is present. In addition, I am using biotic indices to assess whether the invertebrate assemblages indicate that the sites are impacted by pollution. Should fish populations be found to be altered below watercress farm discharges, we can then begin to ask ‘are differences in expected fish populations driven by changes in prey availability, lack of suitable habitat or a direct effect of PEITC in discharge water – or a combination of these factors?’

So far I have enjoyed data collection in the field for two seasons, and have been very fortunate to have been blessed with fine weather. The main catch from these chalk streams is naturally brown trout and bullhead with the occasional eel. However, the downstream site on the Frome has proved to hold a diverse range of species. I pulled out a magnificent grayling on my last visit, along with pike, stone loach, minnow, perch and brook lamprey. One of the joys of electric fishing is one never really knows what one is going to find, and if it is in the run, it will come to you! My survey work would be impossible without the help of volunteers. Students from the Aquaculture and Fisheries department at Sparsholt College inevitably turn out to be real gems, bringing with them lots of experience. However, I always train any volunteer who hasn’t had electric fishing experience and they soon get the hang of it. I’m always on the lookout for volunteers, so if any readers of this blog would like to try their hand at electric fishing and habitat surveying, I would be delighted to hear from you!  

Asa White (A.White2@brighton.ac.uk)

Little weirs and little fishes

Jeroen Tummers has been wrestling with more holistic fish passage solutions during the course of his PhD with Dr Martyn Lucas at Durham University (Martyn gave us a few comments about this project on a previous WTT Blog). But below, we hear from Jeroen himself, about his valuable contribution.  

One of the most important components in restoring impacted river systems, given their linear nature, is to reconnect habitat patches separated by obstacles to free movement. Fishes rely on free access to habitat upstream, and downstream, in a river system to spawn, for feeding, or for finding refuge. Since the presence of these three functional habitat types can change both spatially and temporally, it is important that free access is retained.

But movement between these habitats can be severely hindered by man-made in-stream structures. It is generally agreed that high-head structures like dams have a profound effect on the survival and sustainability of fish assemblages. However, what about low-head structures? Each individual low-head structure might have a lower impact but as they are much more abundant, their combined fragmentation effect may be even greater. How much more abundant these low-head obstructions are compared to high-head ones is not well known, but this is currently being analysed across Europe for the AMBER project (Adaptive Management of Barriers in European Rivers), which I currently work on. Driven by national and international legislation, such as the EU Water Framework Directive (WFD), obstructed surface waters must be reconnected so that fishes may move freely up and down the river.

Jeroen tummers phd wtt blog

 

 

 

 

 

 

 

 

An example of a formerly fragmented river system is the River Deerness, which I studied during my PhD, and which was failing WFD classification for fish because of a lack of connectivity. At the start of my studies, eight obstacles to fish movement were present in the catchment, of which - over the course of two years - six were either completely removed or modified by provision of a fishway, to facilitate both up- and downstream fish passage. The aims of my study were to evaluate how effective these different solutions were for mitigating river habitat fragmentation for a range of fish species and age groups.

I used a combination of approaches, including capture-mark-recapture of a wide range of fish age groups: for smaller individuals a Visible Implant Elastomer (VIE) was used as mark; larger fish were tagged with a Passive Integrated Transponder (PIT), allowing individual recognition in following recapture surveys. This was conducted in 20m zones directly up- and downstream of each obstruction, before and after its removal or modification. For young-of-the-year (YOY) fish, VIE markings were site, zone and survey session specific, allowing for in-depth analysis of spatial behaviour of very young fish in the context of habitat fragmentation, an approach rarely used before.

Results showed quantitative, medium-term evidence of increased dispersal of smaller, more sedentary species (e.g. European bullhead, Cottus perifretum) as well as of larger, more mobile fishes (e.g. brown trout, Salmo trutta) past each of the restored sites, but not at the two unmodified control structures. It is worth highlighting that YOY trout showed increased upstream as well as downstream dispersal rate over modified or removed structures relative to unmodified control sites as well, with similar good quality habitat available at all sites. Young trout suffer from competition for food and space in a population which reaches carrying capacity, a situation which may be exacerbated close to a barrier. My results demonstrate that as soon as a reach is reconnected by barrier removal or modification, these young fish can disperse up- and downstream to areas of lower density with less competition. 

The study is innovative because it combines multiple approaches to evaluate the effectiveness of a range of fish passage solutions, in both up- and downstream direction, in a fragmented system for fishes with poor and good swimming capacity (bullhead and brown trout, respectively) following a before/after intervention method. It also shows that conventional techniques used to evaluate a given fish passage solution, such as sporadic semi-quantitative electric fishing surveys downstream and upstream of a (modified or removed) obstruction, may not be very effective. We have published part of this work in the journal, Science of the Total Environment, available here.

It is hoped that in years to come, in addition to an increase in abundance and area of occurrence of species already present in the Deerness, Atlantic salmon (Salmo salar) may also return to spawn, as habitat suitable for redds is available throughout much of the middle and upper Deerness. Salmon has been almost absent in the last few decades in the greater Wear catchment, but is now on the increase in the main river. So hopefully, this work will help river managers like the Wear Rivers Trust to make better informed decisions on how to deal with obstructions on fragmented systems.

Jeroen (j.s.tummers@durham.ac.uk)

Land and lake interconnectedness

On a day-to-day basis, most of my time as WTT Research & Conservation Officer is devoted to river habitats, but in my academic role at the Lancaster Environment Centre, lakes are a long-standing focus of my aquatic ecology research. A Natural Environment Research Council grant allowed a colleague from Cambridge and I to convene a workshop with scientists from Canada, the USA and Sweden, with common interests in how lake food webs may be fuelled by subsidies from the land. The output from that meeting is a recently published synthesis based upon data from ~150 northern lakes. Most of the planet's freshwater lakes and rivers that we associate with various ecosystem services, like fisheries and water supply, are found in the northern hemisphere, a region that is changing rapidly in response to human activity intertwined with shifting climatic trends.

The classical view of lake food webs is that of algae produced via photosynthesis forming the food base for zooplankton (such as water fleas or Daphnia) that is then munched by fish. We do not contest this because algae are typically a very high quality diet, and many lakes contain plentiful algae. However, in lakes that do not contain adequate supplies of such a resource, or during winter when it is less available or completely unavailable, then organic matter from the land, derived from the breakdown of terrestrial plants, can still be used via intermediary bacteria. And this situation is more common than you might imagine.

Our team used stable isotope techniques as natural ‘tracers’ of diet and analysed over 550 zooplankton samples from lakes across a range of conditions from the boreal zone to the sub-tropics. In half of the zooplankton samples, these tiny animals comprised at least 42% terrestrially-derived material. In some instances, terrestrial food sources accounted for up to 83% of total zooplankton biomass.

By concurrently investigating how physical characteristics of the land draining into lakes influenced the observed terrestrial subsidies in the lake food webs, we could identify certain key determinants. Differences in tree cover, vegetation density, soil carbon concentrations, lake area, and lake perimeter can all potentially impact upon the amount of terrestrial matter available to aquatic life.

These widespread findings further highlight the interconnectedness of ecosystems. But they also convey an important message for those tasked with conserving and managing freshwater resources. We must understand how landscape changes, such as forest clearing or reinstatement, or agricultural practices, impact upon lakes that they adjoin or are linked to via river networks.

What does this mean for trout? Well, trout are renowned for their ability to maintain higher populations than we might expect for a given stretch of river or area of lake. That is because they can and do readily tap into food resources from ‘outside’ of the waterbody, i.e. daddy long-legs or heather flies, worms, even cicadas, mice and lemmings. However, if some of their ‘aquatic’ food is already heavily subsidised by terrestrial matter, then it is even more important for us to consider sensitive land management beyond a riparian buffer strip.

The full article for those that are brave, is available open access here: http://advances.sciencemag.org/content/3/3/e1601765

Impacts of low flows on salmonid river ecosystems

In the first of a new series from students actively involved in research relevant to wild trout, Jessica Picken from Queen Mary University of London summarises the aims of her PhD working with the Game & Wildlife Conservation Trust and with CEFAS.

Climate change is considered to be the most critical disturbance imposed on natural systems on a global scale. Climate models predict that average temperatures in the UK will increase over the course of the next 50 years with the greatest warming in the south of England during summer months, and that annual average precipitation will reduce. However, the reduction in precipitation is expected to be more pronounced during summer than winter, whereas extreme winter precipitation is expected to become more frequent. In other words, there is likely to be an overall shift towards drier summers but wetter winters.

River itchen jess pickens qmul gwct cefasFlow regime is widely recognised to be the master variable controlling a number of key riverine processes, including levels of dissolved oxygen, sediment transport and deposition, water quality, and habitat type and distribution. These processes in turn influence the spatial and temporal distribution and abundance of critters! Chaotic variability in river discharge (due to climate variations) can adversely affect migratory and resident salmonids at different stages of their life-history. However, in the relatively more stable chalk streams of southern England, drought and associated low river discharges (often exacerbated by human influences such as abstraction, flow regulation and land use), are thought to be the biggest threat. In the future, chalk streams are likely to suffer from periods of intense summer drought more frequently, with potentially disastrous implication for their fish populations.

We are studying three carrier streams of the River Itchen where complete control of the flow is achieved by altering sluice gates at the top of each stream. During the summer, the sluice gates will be lowered in order to experimentally induce low flow conditions. Each stream will experience a four week low flow treatment, reduced by 90%, 45%, or not altered (as a control). The following summer, the individual streams will be subject to a different flow treatment so that at the end of the three years, each stream will have experienced all the different flow treatments.

Samples of the riverflies and other invertebrates  will be collected from each stream throughout the year to enable any response in fish food to be identified, in terms of species composition and density. Salmonid stomachs will be flushed to determine their diet, and to enable the construction and assessment of food webs in each stream under each treatment. It is possible that reduced flow may result in the loss of certain habitat types that are required by some invertebrates (e.g. decreases in stoneflies may occur where fast flowing habitats are lost) which, in turn, will affect salmonid diet as they respond to the change in prey availability by becoming increasing reliant on alternative food sources. We may see a shift in stream food web dynamics under different low flow conditions.

The movement and behaviour of salmonids may also change in response to reduced food availability, with fish increasing their foraging range to seek out food of a better quality or more suitable instream habitat. However, salmonid movement may be restricted due to the reduced amount of available habitat during the low flow period which could cause and increase in foraging competition due to fish density increases. To help me tease all this apart, I will monitor behavioural responses using Passive Integrated Transponder (PIT) tags inserted into individual fish to monitor habitat choices of salmonids before, during and after flow reduction in all three streams.

Results from this three year project will increase our understanding of the impact of short term summer drought events, which is vital to safeguard salmonid populations in these streams and to define future catchment and water resource management strategies for the south of England.

If you have any questions or comments, I would love to hear from you, and I hope to reappear on these pages to update you as the project unfolds.

Jessica (j.picken@qmul.ac.uk, or @jesspicken)

Fishing and family holidays for 2017 in the WTT auction

Fishing and family holidays in 2017 in the WTT auction

Short, grey days and limited fishing opportunity over Christmas and New Year tends to make me think of summer holidays.  As I write the lot descriptions for the WTT’s annual fundraising auction,  especially the ‘fishing overseas’ section,  I can dream about travelling to exotic rivers to fish in warm sunshine.  This year, it occurred to me that many of the ‘overseas’ lots could be combined family holidays, and perhaps some advance notice might be useful to aid planning.

This blog post describes some of the lots in Europe and the UK that could easily be combined with a holiday with the family or non-fishing partner. Watch out for the next blog post with fishing holidays further afield: Iceland, the Bahamas, Argentina and Zimbabwe

The chalk streams of Normandy provide excellent trout fishing, and mix well with fine food and visits to historic towns and beaches. Check out lots on the famous and historic Fario Club beats on the Rouloir and Fario Club members' beats on the Andelle. Previous winners of these lots have enjoyed the hospitality and good company of Laurent Sainsot, an Anglophile trout fisherman and tremendous WTT supporter (below left).

Near the Cote D’Azur, Tony Mair will take you on a walk (more of scramble, but perfectly safe …) to the bottom of the Verdon Gorge to fish the clear blue river between towering cliffs. Tony lives locally and will collect you from Nice.  A stunning location and a good break from the beach (below right).

Fario

Verdon

 

 

 

    

 

 

 


If cooler climes and mountains are more your idea of fun, you could include a day with Chris Hendriks fishing for trout and grayling in rivers large and small in the Tyrsil area of Norway.

Chris is a leading light in the European tenkara community but you may fish conventionally if you wish – all you need bring are your waders as he can supply the rest. There are some lovely comfortable cabins nearby. (below left).

Trysil

 

 

 

 

 

 

 

 



For sun and mountains, you can’t beat the Spanish Pyrenees.  There is some fantastic trout fishing here, but you need to know where to go, and how to get access through the complexity of permits, licences and private roads. Ivan Tarin and his guiding team will look after you not just in terms of fishing, but share with you the local Spanish food, wine and culture. A week in the High Pyrenees in midsummer might also appeal to a non fishing partner who is well catered for if they enjoy walking, wildlife, history and the culture of this beautiful area.  

High Pyrenees     Pyrenees lodge

 

 

 

 

 

 

 

 


Within the UK, we have some new lots this year that would combine beautifully with a holiday.

Pembrokeshire has a stunning coastline and is rich in birdlife and wild flowers. It also has some very good fishing both in the sea for bass and pollock, and, course, sea trout. Generous supporter Tony Richards has a cottage in Newport and a family member on the committee of the Nevern Angling Association. Thanks to him, we can offer a week in his cottage and a week's fishing ticket for two anglers on this excellent (but little known) sea trout river.

Dinas head

The Hebrides has quiet, sandy beaches and turquoise seas that are the envy of many Caribbean tourist boards. The fishing is for salmon, sea trout and wee brownies in the hill lochs. This year, we can offer a week in a cottage on Loch Fincastle on the Borve Estate of South Harris, including fishing in the tidal loch for salmon and sea trout. The cottage is short drive from the famous Scarista and Luskentyre beaches. 

fincastle    south harris

 

 

        

 

 

 

 

 

Full details of all these lots will be on the website and in the catalogue in early February. If you are not yet a WTT member please contact Christina and she will send you a printed copy of the catalogue office@wildtrout.org or call on 02392 570985. 

If you would like more detail now, contact me on dashton@wildtrout.org

 

Mike Blackmore: moving house, getting sick and still getting projects delivered

As a follow on from Mike Blackmore’s ‘Mad March’ blog, this is what he has been up to recently, or rather this blog post is about the challenges of moving house, getting sick and still getting projects delivered!  
You can read more about some of the projects Mike has been delivering in our Autumn Newsletter

Mike is the WTT Conservation Officer for the South and West. 

Mike says:

Between the end of August and November I have 

  • ·         Spent 42 days in-river delivering habitat enhancement/restoration projects plus 17 days out doing some other kind of away from the office activity (site visits, meetings etc.)
  • ·         I’ve worked on 16 different projects in 10 rivers across 4 counties with 3 EA offices, 2 Wildlife Trusts and 2 Rivers Trusts.

My waders are all trashed, my chainsaw needs serious TLC, the van needs a good power wash and a service and I needSt James Leat a holiday. Unfortunately, all of these have had to wait because midway through the Dever project we moved out of our house and into temporary accommodation, putting everything into storage whilst we awaited exchange of contracts for our new property.

In an attempt to make things easier for ourselves, Lotte and I rented a self-catered cottage for the second week of the Dever project (to reduce stress levels and commute distance). Cue Noro virus, violent sickness, 48 hours without food or sleep and literally using a stick to hold myself up whilst directing the diggers on site. Didn’t reduce stress levels but I did shed a few pounds!

 

After the Dever project I attempted setting up a temporary office in my parents garden room only to discover that mobile reception and internet in their corner of Somerset is powered by druidic chanting, steam and wishful thinking.

Otter PVThe next attempt at an office was my parents in-law’s campervan which despite being parked on a steep driveway and containing a purely ornamental electric heater, did have power and 21st century telecommunications. However, late on a Thursday evening I was informed that the campervan was going away to make space for builders that were coming next week. Attempt 3 at an office space was at my sister’s house which during the day contains her sleeping nightshift-working husband and a small dog that, despite being very cute, enjoys tearing lumps out of my spaniel.

 

We’ve now finally arrived in our new house and I’ve got a chance to catch up on report writing and such. It’s just dawned on me that I have three months to get four projects up and running for March I’d better crack on. Maybe I’ll take that holiday in May!

An enthusiastic response from Yorkshire

You may have seen via the WTT news pages or via Twitter that we were awarded a grant from Yorkshire Water’s Biodiversity Enhancement Fund which is part of their Blueprint for Yorkshire.

According to Yorkshire Water: The Wild Trout Trust secured funding to deliver projects across multiple locations within the Yorkshire Water operating area. Projects focused on work to restore, improve and maintain becks, rivers and wetlands. This work is in line with the government’s Catchment Based Approach plans for river management and is in in partnership with the EA, the Rivers and Wildlife Trusts, and local community groups. The proposal also focused on enhancing volunteer’s practical skills in order to enable them to apply learnt techniques on other nearby sites and create a network of environmental stewardship groups for the future.  

This proposal was successful because the project benefits BAP species and habitats as well as focusing on mitigating the impact of YWS neighbouring assets. The emphasis of the project on upskilling local groups was also valued.

Obviously improving habitat is key to the aims of the WTT but our impact is all the greater because of engagement and collaboration with grass roots organisations, and these Yorkshire Water funded ‘habitat demo days’ were my first opportunity to lead workshops on my local patch.

After discussions with Don Vine at Yorkshire Wildlife Trust, Pete Turner at Environment Agency (of course), Craig Best at the National Trust, and Nick Chuck of Bingley Angling Club, I settled on two small tributaries of the Aire (Howgill & Granby becks) within the grounds of East Riddlesden Hall, opposite Marley Sewage Treatment Works. As a part of the agreement with Yorkshire Water, some of the funding will be used to create a semi-permanent wetland (planned by Yorkshire Wildlife trust) which will contribute to natural flood management via water storage. As an example of some of the leveraged funding achieved, the Environment Agency have funded the livestock exclusion fencing along Granby Beck which ensured that all our instream habitat works were protected and the benefits realised more quickly.

My reasons for choosing this site were numerous, but spawning habitat is relatively rare on the mainstem Aire and hence looking after the numerous but all too commonly abused small tributaries, the capillaries of the river network, is very important if we want self-sustaining, resilient wild trout populations. There is the added advantage that it is relatively easy to demonstrate various restorative intervention techniques on small tribs that are scalable, and then let volunteers get stuck in both literally and practically.

Sixteen people attended each of two consecutive Saturday workshops at East Riddlesden Hall. Participants came from a variety of sources but I was blown away by the fact that representatives from nine different angling clubs attended, including Appletreewick, Barden & Burnsall Angling Club, Skipton Angling Association, Bradford City Angling Association, and even as far afield as Knaresborough Anglers Club. There was also a volunteer team from ComputerShare but from the degree of energy and enthusiasm, you’d never have guessed that they were office/desk-bound for the majority of the week! They appeared genuinely proud of their achievements and new found skills. One of the most gratifying moments for me was overhearing two committee members from an angling club on another catchment, stood next to one of the pinch-point interventions, discussing exact locations where they could apply such a measure on one of their own waters. Bingo!

I created a social media summary via Storify, here. Some of the take home facts and figures from the two days at East Riddlesden, and a similar demo day run by colleague Gareth Pedley with Caitlin Pearson of Yorkshire Dales Rivers Trust on Skeeby Beck, are summarised in the infographic below.

Please contact me if you have ideas for similar workshops or practical visits that could be considered for support under our partnership with Yorkshire Water.

Diving in on the Dever

It is incredibly difficult to drag our Conservation Officer for the South & West, Mike Blackmore, out of the river (where we know he prefers to be). Therefore, in order not to distract him from his valuable work before the end of the ‘in-river’ season, we asked Kris Kent to update us on work to restore the River Dever. Kris has been fly fishing and trotting for brown trout and grayling for over 20 years in the UK, Europe and Scandinavia. He is PR Officer for the Grayling Society and helps WTT with our online communications and events. (WTT Director: he’s also a bloody good egg – thank you, Kris, for all your help).

I was between jobs so I emailed Shaun Leonard, Wild Trout Trust Director, to see if there was anything I could help out the Wild Trout Trust with.  I was thinking of a little light administration, spreadsheets, reports or the like.  Within a few minutes Shaun called me on the mobile.  “Did I fancy helping out Mike Blackmore with a project he was working on?”  I said “Why not.”  Shaun suggested I call Mike to make the necessary arrangements.  Mike seemed a little bewildered by the fact that I was going to be helping out but he suggested that I start the following Tuesday and filled me in on the logistics.

In Guildford on business and on my way back to home in Lambourn, I realised I would be passing close by the project site, so I popped by to make sure I knew where I would be going the following week.  I pulled off the narrow lane that skirted the river by the pretty little church of Saint Michael and All Angels. Mike’s white VW Transporter was parked up by the stables so I knew I must have been in the right place.

Mike Blackmore Wild Trout Trust river restoration conservation

Saint Michael and All Angels, and the team working hard

I decided to take a quick stroll along the river and see if I could find Mike and the team and see what was going on.  It didn’t take me long to find them.  Mike and Jonny, the Keeper, were being ably supported by volunteers from Sparsholt College.  They looked a little confused as I strode down the path in suit and brogues!

Mike walked me down the river explaining the background to the project, the problems being addressed and the plan for the project.  The Environment Agency had identified this reach of the Dever as being an ideal opportunity to undertake a major habitat restoration project with the Wild Trout Trust as part of the Test and Itchen Restoration Strategy. Following engagement and planning with the riparian owners and the team that run and maintain the fishery (Fishing Breaks), a project was pulled together.  The project was funded by the owners, the Environment Agency and a donation from a WTT partner, Springwise, through an initiative called 1% for the Planet by which environmentally-minded businesses can donate 1% of their turnover for work to improve our natural environment. Fishing Breaks also provided skilled labour in the form of River Keeper, Jonny Walker.

This section of the Dever was suffering from a number or problems.  Impoundments meant that long sections lacked significant flow and had led to siltation of the spawning gravels, uniformity of habitat, and tall, vertical banks.  It was overwide in many places and had been artificially straightened. The uniform habitat was limiting biodiversity and, whilst there was a reasonable head of wild trout and grayling, the lack of suitable spawning habitat was hindering recruitment and a lack of refuges meant that fish (particularly juveniles) were vulnerable to predation.

The project had two phases. Week one focused on opening up the canopy in strategic places to let more light in and aid weed and marginal plant growth.  The wood generated would then be used to create flow deflecting woody habitat features.  Woody mattresses and hinged bankside trees would create fish refuges and trap silt, providing additional marginal habitat. Together these would help narrow the channel, increase flow, scour gravels and create a more sinuous, meandering channel.

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Creating a woody mattress, and the plant required for 'dig and dump'

In week two, the heavy plant would arrive. This would enable the team to do some ‘dig and dump’.  Pools would be dug out with the waste materials from that process used to create marginal berms that pinch the channel and accelerate flow. Then, new gravels would be introduced to make the new pools more hospitable for fish and provide spawning opportunities at the tail of each pool. Additional riffles would also be created to further diversify habitat. Sections of tall, steep bank would be re-profiled to improve floodplain connectivity, improve marginal habitat and provide easier access for anglers.

So I arrived at the beginning of week two and found the river already transformed. My job was to run around and help out with anything that needed doing, freeing up the professionals to focus on the important stuff.  After the digger had introduced the gravels into the new pools, I would follow on and rake them over, blending them in and tidying them up.

I helped peg in some woody debris as juvenile refuge habitat and I stacked up the leftover wood and piled up the brash ready to burn.  During week one, the team had created a new river bank along an over-widened section. During week two, I helped to back fill this area and translocate marginal plants to the new bank edge.

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Creating new bank

By the end of the week, I was exhausted, not being used to such manual work.  But the sense of achievement was almost overwhelming. Seeing the transformation from degraded to vibrant habitat gave me a huge sense of satisfaction and pride. And the fish loved it too.  Minutes after digging a new pool, the fish had already moved in and in one small pool we counted over twenty trout and grayling. I can’t wait to go back in six months or a year and see how the river has settled into its new setting.  The other thing I enjoyed was the sense of camaraderie, working together on such an important restoration project. I highly recommend it.

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A few of the team!

 

 

Easements on Eastburn

A number of my blog posts have featured Eastburn Beck. It’s my pet project because it is the first that I cut my teeth on after moving to Yorkshire, because I live overlooking its headwaters and hence it is a very easy and accessible site for me to monitor. It is also exciting because it has ably demonstrated the value of partnership working, and how with critical mass, relatively small habitat improvements are snowballing both up and downstream from the original work plans as word spreads; this is quite typical for projects that the WTT is involved with!

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Pre & post some weir notching we undertook on Eastburn Beck at Lyndhurst Wood. The channel width is narrower with more natural pool, riffle, and depositional features

To date, the project has involved me (WTT), the Environment Agency (via the powerhouse that is Pete Turner), Yorkshire Wildlife Trust, Bradford Environmental Action Trust, the Woodland Trust, Aire Rivers Trust, and Green Port Hull, as well as some very cooperative local land / structure owners. It has attracted a reasonable amount of media coverage too: Craven Herald, Keighley News, a colour spread in the Yorkshire Post magazine, and in Fieldsports magazine (the latter two instigated by top WTT chum, Andrew Griffiths). It was even the feature of Pete Turner’s first ever blog!

So, I can’t say that I’ve seen it through to completion – when can we truly say that a river or stream has been completely rehabilitated to a pristine condition with the number and diversity of stressors acting upon them nowadays? It’s a job for life! However, I can say that the Beck is slowly returning to some version of the right track and hopefully you can follow its continuing evolution through these blogs. Check out the green tabs at the bottom of this post which will link you via key words (connectivity, weirs etc).

I’m currently working on a fish easement for the shallow concrete sill of a road bridge next to a former mill. More connectivity issues – see the recent news item for how often these crop up in WTT Conservation Officer workloads. This particular phase of work has been supported by funding from Green Port Hull, via a grant awarded to Aire Rivers Trust & WTT. There are several kilometres of becks and trickles with reasonable to good quality spawning habitat availability above this obstruction, so it is a likely bottleneck on the system limiting trout population potential. It is not classified as main river but one still has to apply for consent to install any structures which might affect flow and perceived flood risk; in this case, North Yorkshire County Council were very cooperative.

Prior to any installation however, the scientist in me was keen to assess just how much of an obstruction this particular weir and culvert combo was. Cue a call to those good folk at Ribble Rivers Trust and in particular Mike Forty (another name you might recognise from a past blog on making connections). Mike carefully set up a pair of telemetry loops at the lower and upper end of the culvert, and then together we spent a day electrofishing to capture trout from upstream. A total of 25 fish were tagged with Passive Integrated Transponders (PIT-tags) and released into the pool immediately downstream of the weir. The premise is that these fish that have been displaced will attempt to return to their ‘preferred’ location upstream; there is a scientific basis for this – see Mike’s report.

The headlines are that 40% (10/25) of the trout were recorded as attempting to jump the weir, and of those there was a passage efficiency of 40%; in other words 40% (4/10) of the trout that attempted to get up and over the weir and into the shallow water in the culvert did eventually make it upstream. I say eventually, it took those 4 fish an average of >10 minutes to negotiate the culvert. Interestingly, it wasn’t the larger fish that made it either, so perhaps the depth of water was insufficient for those larger fish. Despite some difficulties with the study, including a flash flood of epic proportions (2nd highest level ever recorded – typical), Mike and I are in agreement that the structure is a considerable obstruction to fish passage, let along geomorphology!

Now that passage (or lack thereof) has been assessed prior to any interventions, I can proceed with installing some oak baffles and a baulk to focus flows and increase the depth across the sill, whilst providing slack water refugia en route for fish to recover if required. Watch this space for future updates. 

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