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View north from Hen Tor, July 2025
View north from Hen Tor, July 2025

The Guardian has today published a feature on the poor condition of Dartmoor's SSSIs. This followed a visit by the reporter to Willings Walls and Hentor Warrens Common. In the article below, Dartmoor Nature Alliance's Tony Whitehead gives more background on the sorry decline of this common ...


Willings Walls and Hentor Warrens Common lies in south west Dartmoor on the eastern slopes of the Upper Plym above Cadover Bridge. The land is owned by the National Trust, forming a large part of their Upper Plym Estate, and is part of the larger Shaugh Prior Commons (Common Land Unit 190).


It is protected by law as part of the South Dartmoor Site of Special Scientific Interest (SSSI), Unit 61, and the Dartmoor Special Area of Conservation (SAC). The inclusion of this land in the SAC was due to its internationally important blanket bog and heathland plant communities. However, as we shall see, these wildlife habitats are in their death throes on this common. This is a story of long decline driven almost entirely by wholly unsustainable grazing pressure, paid for by the taxpayer. It is a scandalous exemplar of everything that is wrong with Dartmoor’s common land.


The decline of heather


That  heather  was  full  of  the  wind  and  the light  of  the  moor,  the  searching  wind  and  piercing  light; it  had  bathed  in  moonlight  and  fed  upon  unpolluted  air;  its  roots  had  sucked  life  from  fragrant  peat.  It  was  the manna  of  the  wilderness.

John Trevena – Heather, 1908


When Ernest George Henham, writing as John Trevena, published his 'Dartmoor trilogy' in the early 1900s, heather would have been ubiquitous across much of Dartmoor’s common land. Up on the high ground, on the deepest peat, the nodding clustered purple flowers of cross leaved heath would have bloomed here and there amongst the mosses and asphodels of the blanket bogs, while around the drier peripheries, the small purple flowers of common heather, or “ling”, would have stood clumped in tall stands amongst bilberries.


Amongst the heather, there would have been sufficient grazing for grazing animals walked up to the commons along ancient droves in spring and walked back down off the hill in autumn.


Things were changing, though. From the late 18th century, Dartmoor had been subject to the attentions of those who saw opportunity on this most marginal of lands. Not long before Henham settled in Sticklepath to write his novels, new hardier breeds of sheep and cattle had arrived on the moor. Now, sheep, particularly the Scottish Blackface, could be left out on the commons year-round.


With good grass scarce in the late winter months, these sheep were able to survive by browsing the growing tips of the heather. For sure, it wasn’t ideal, but it was sufficient for a hardy animal. In small numbers, the heather community could withstand the nibbling. But the number of animals on the moor was on the rise.


In the late 1940s, as part of the national post-war drive for greater self-sufficiency, the Government introduced new subsidies to support food production. One such subsidy was targeted at areas deemed Less Favourable and Severely Disadvantaged. As the names suggest, these were for the most marginal of lands and included the English uplands, such as Dartmoor. For decades, taxpayer money was given to farmers in these areas to support their livestock operations.


With this, the UK Government and, from the 70s, the European Union encouraged livestock farming on Dartmoor to intensify.  For probably the first time, farmers could concentrate wholly on farming rather than having a range of jobs to bring in income.


The number of animals rose dramatically on Dartmoor through the 50s, 60s, and into the 70s. And with the rise, an associated practice also dramatically increased – burning. Known as “swaling” on Dartmoor, large areas were burning every spring, over and over again, to produce fresh growths of grass in spring for hungry mouths. Swaling has long been a controversial topic on Dartmoor; letters to the papers were commonplace, dating back to well before the last war, and early preservationists, such as Hansford Worth, had commented on its unsustainability in relation to the natural vegetation. But this was burning on a new scale. And, along with the heavy grazing, it was taking its toll on the heather.


Heavy repeated grazing stunts heather, which is compounded by trampling. Frequent burning, combined with heavy grazing, further increased the pressure. Also, on the deeper peats, the burning had another effect – it favoured the growth of Purple Moor Grass (Molinia caerulea), which soon became dominant at the expense of heathers. Additional pressures came from outbreaks of heather beetle, climate change, and air pollution (atmospheric nitrogen), but according to NE evidence (page 23 here), these were not driving the changes. 

Over large areas on the drier peripheral parts of the moor, heather-rich heathland was degrading to species-poor acid grassland, whilst on the blanket bogs, Molinia was impoverishing previously unique plant communities. The heather, the “manna of the wilderness” was dying out: all driven by grazing and burning.


Failed schemes and wasted public money


The concern for the ongoing loss of heather on Dartmoor throughout the 80s led in to English Nature carrying out a significant study of heather condition in 1993-94. A report was published, and a series of maps produced. The survey found that 63% of Dartmoor’s commons supported some heather cover, with half showing damage and a third of this showing severe damage.  


On Willings Walls and Hentor Common, the maps showed large patches where heather was absent, slightly overgrazed and severely overgrazed on the lower slopes, with some overgrazing on the higher areas of bog. There was still some healthy heather on site, on the slightly more distant parts in the east and the north.


English Nature Heather Condition Survey 1993/4
English Nature Heather Condition Survey 1993/4
Key to Map Above
Key to Map Above

 This mirrors a similar study undertaken by National Trust in 1990.


NT Heather Condition Survey 1993 (source here). Purple areas are Heather.
NT Heather Condition Survey 1993 (source here). Purple areas are Heather.

Even though the surveys were revealing poor condition, all was not lost. The English Nature heather condition surveys paved the way for the very first agri-environment schemes. The novel idea was that instead of being paid by the taxpayer to produce livestock, the commoners could be paid to produce nature on protected sites such as SSSIs and SACs. In this way, the first Environmentally Sensitive Areas were declared in the mid-90s, and commoners started to sign up on the stipulation that, in return for payments, they reduced the number of grazing animals to allow the heather to recover.


The principle is excellent. The trouble is, the rates at which stocking densities were set were inevitably a negotiation between what commoners say they need for their farm businesses, and what nature needs. They were, and remain, a compromise. In the mid-90s, Hentor and all the commons could probably have benefited from a period of years without grazing or burning to allow for recovery. But that was not politically acceptable to farmers. So the grazing and burning continued, with some cash now paid to farmers and commoners to limit grazing.


Evidence on the ground in subsequent years suggested that the changes being made to moorland management were nowhere near sufficient for nature to recover. The heather continued to decline on Willings Walls and Hentor Common, and significantly so.  By 2003, the area of heather in reasonable condition had retreated further to the north. By 2006, the only area that qualified as “heathland” rather than grass moor occupied a small area at the far north of the common.


NT Heather Condition 2003 (source here). Purple Areas are Heather.
NT Heather Condition 2003 (source here). Purple Areas are Heather.

But all was not lost. By the end of the 2000s, the ESA schemes were giving way to new Higher Level Stewardship schemes. These were detailed taxpayer-funded agreements with the local commoners to deliver nature. The Willings Walls and Hentor Commoners Association signed up with a contract worth £1,423,933 to run for ten years from 2011 to 2021. The agreement's aim was to return the SSSI to favourable condition. 


The formal monitoring of SSSIs began in the 2000s, with each sub-unit assigned a condition status ranging from favourable to unfavourable, recovering, to declining, and at worst, destroyed. Two years into the HLS agreement in 2013, the Willings Walls and Hentor Unit 61 was formally surveyed, and although described as being “unfavourable”, it was classified as “recovering” because it was part of an agreed scheme, and thus there was a path to recovery.  


This, as it turns out, was an optimistic assessment. In 2015, four years into the agreement, and at the behest of the site’s owners, the National Trust, another survey was carried out (Boyce 2016). It’s a depressing read. The heather had continued to decline. In the one remaining patch of “heathland” in the north of the common, the heather had died off. On the grass moor, where the heather still clung on back in the 2000s, it had now largely disappeared. The author of the report wrote, with what feels like a heavy heart, “In those places where there is still some senescent ling {common heather}, the plants continue to be heavily over-grazed and it is only a matter of time before these last old bushes are lost.” 


On the higher areas, the blanket bog also remained in poor condition, dominated by acres of dense Molinia, still bearing the effects of burns from past decades. The only solace in the report was that some areas of wet heath seemed to be doing OK. Overall, though, the report describes a place where the key features for which the site is important, or at least could be important, had been lost or were fading into extinction. The scheme, in place to reverse the place's fortunes, was not working.


Despite this, and with five years more money received, in 2020 the commoners association asked about extending the agreement beyond its 2021 end date. In response, Natural England carried out a site check. On the dry heath they reported “High levels of stock (cattle and sheep) noted at time of visit and levels of dung also high across much of the habitats on the lower slopes. The range of indicator species is also generally poor and below thresholds with all stops failing to record the necessary range of species for the habitat in question.” On the wet heath, they reported  “Generally, the condition of these habitats is poor, with areas on the lower slopes and in the south of the common showing signs of high browsing pressure from stock.”  


After over two decades of publicly funded schemes and millions of pounds of taxpayers' money handed to commoners, the site was worse than when these schemes started. And grazing levels remained high. Rightly, NE refused to renew the scheme without changes. Despite negotiation, the necessary assurances were not forthcoming and the HLS agreement ended, and now, with no pathway to recovery Unit 61 was classified as Unfavourabe Declining.  What a sorry state of affairs for nature on a site, potentially, of international importance, but where the key features had almost entirely disappeared. Either grazed and burned out of existence or swamped by Molinia, itself the legacy of excessive burning.


The End?


Whatever parlous state of nature on the common, the imperative of the commoners to graze remained. However, they were now running up against the law. As protected sites, any work carried out on a SSSI if it is potentially damaging, requires consent. On this common, those that had rights by dint of being “occupiers” – the National Trust’s tenants – needed consent to graze.  They applied and Natural England (rightly) refused. This then became the subject of a legal case, which is still ongoing. Natural England also threatened a “stop order” on the commoners to stop all grazing in winter.  Before the order was issued the commoners agreed to do this voluntarily.


However, the site remains in a state of decline.  Yet another detailed survey in 2023, by Natural England, documented the loss of dwarf shrubs over the site in the past decade. It stated “Continued heavy grazing on dwarf shrubs, particularly heather, when now at very low cover […] risks further reduction and potentially loss from at least parts of the unit as has happened in the acid grassland sample points.” In short, the heather was nearly gone.

Likewise, the 2025 NE Dartmoor SSSI assessment firmly put this SSSI unit as “unfavourable declining,” commenting, “Some areas within the unit were noted as intensively grazed and this could be driving the dominance of Molinia. Areas of eroding peat were frequently mentioned associated with animal disturbance and burning.”


There are a great many Dartmoor commons in poor condition, but this has to be, by any metric, one of the worst. This site warrants the title of an ecological dead zone.


What is to be done?


Hen Tor July 2025
Hen Tor July 2025

It is still possible to restore the nature of Dartmoor's commons through sympathetic management. But is it possible to achieve with Dartmoor's farming communities and England's nature regulator, as they are?


To understand this scandalous state of affairs, it’s necessary to understand a little about the governance of Dartmoor’s commons.


In short, in terms of land management, nothing happens on Dartmoor’s commons without consideration of commoners and their grazing rights. Even the landowners themselves have relatively little sway on what happens. Willings Walls and Hentor is owned by the National Trust, who are sympathetic to nature restoration and are involved in some peat restoration work. However, they cannot do anything that might interfere with common rights, unless they work out a deal, and that’s rarely easy.  Even the Ministry of Defence on the Dartmoor Ranges has to pay compensation to commoners for the live firing days because these interfere with grazing rights and livestock needs to be moved (not by the commoners you understand, the MoD does this through range clearers employed by Landmarc).  This will be the subject of a future article.  The National Park Authority?  Unfortunately they have absolutely no powers in respect of grazing.


There are actually only two bodies that can exert legal control on grazing on Dartmoor. One is Natural England. They can, as here on Hentor, refuse to issue consent to graze; but only on the SSSIs, and not to commoners who are not notified owner/occupiers...which rather limits their power. They can also issue a Stop Notice (as can other regulatory bodies) when damage is clear and proven. They have threatened this on Willings Walls and Hentor Common, but have so far not followed through.


Beyond this, NE’s only “power” is through advising on agri-environment schemes. And while grazing rates are set by NE, they are agreed through negotiation. Back in 2023 Natural England tried to make a stand, being clear that if they were to agree to HLS schemes being extended they would need to see significant changes to stocking rates.  The backlash was dramatic, and the politically driven Independent Review resulted in clipped wings and a climb down for NE.


Once rates are set in agreements, it’s also worth bearing in mind that monitoring what is happening on the ground is very challenging, especially in the remoter parts of Dartmoor’s commons. As NE stated in their evidence to the Fursdon Review (p29):


Dartmoor also has particular challenges that create resource demands, including a history of non-compliance, so some agreements have not been successful and in some cases, commons associations struggle to achieve internal consensus.


If everything was working as it should, the results would be there to see in the recovery of the heather.  We do not see that on the Dartmoor commons.


The other body that has legal powers is the Dartmoor Commoners Council. Their powers derive from the Dartmoor Act 1985, which established the Council as a result of a long-running campaign to bring some order to a place that had long suffered from a lack of regulation, and in particular had a very poor record on animal husbandry.


Under the Act, the Council is responsible for regulations that aim to manage grazing on the commons. In particular, in Regulation 9, the council can issue “limitation notices”:


Whenever the Council shall consider it expedient to prescribe the maximum number of any description of animal that any person may from time to time depasture on any unit of the commons (whether by reason of the quality of the pasturage or otherwise) the Secretary of the Council shall send a Limitation Notice in accordance with Section 5(2)(a) of the Act to the owner or tenant of that land and to each person registered in accordance with Section 7 of the Act as having rights to depasture on that unit of the commons specifying the common land so restricted, the period of the limitation and the maximum number and description of animals that an owner, tenant or other person may depasture on that unit of the commons for that duration and shall send a copy of each such notice to the Secretary of the Commoners' Association to whose area the restriction applies.


However, it has very rarely used these powers, and indeed in January this year, actually voted not to use them at this time.  


This means that on the one hand we have one regulatory body with limited powers, Natural England, that, especially after the Fursdon review, is unwilling to use them, and on the other hand, another regulatory body, the Commoners Council, that is actively NOT using its powers.


This leaves just one thing that controls grazing on Dartmoor, and that’s the allocation of rights. The number of animals any commoner can graze is limited in law to the number set under the 1965 Commons registration act. The significant problem with this, however, is that the 1965 Act did not attempt to establish sustainable limits. Commoners submitted their numbers, and these were then fixed in various commissions over the ensuing years. If you add up all the numbers for any one common the number is huge.  Of course few actively graze the commons nowadays, there are probably under 200 commoners, and few of those use all their rights. But they could do so if they wished.  Even at current levels, on commons with live agreements, the numbers are still causing damage and preventing recovery.


The death of nature?


The death of nature on Willings Walls and Hentor reveals multiple failures.  Like much of Dartmoor, it illustrates the scale of post-war agricultural policy failure, which used public money to drive stocking levels way beyond sustainable limits —a legacy that nature still bears. More tragically, it also reveals the complete failure of agri-environment schemes to restore nature on Dartmoor. 


It is right that public money is used to support nature’s restoration, because the public benefits are enormous. And schemes can work, as we know from other places in England - the recovery of Cirl Buntings in Devon, for instance, is wholly due to public money invested in farming and well spent. But on Dartmoor, the potential of schemes to deliver change has always been compromised in negotiations with the commoning community.  


Although the schemes have brought grazing rates down from the historic highs of the 80s and 90s, compromise has always meant the numbers are never low enough. For instance, on the huge Forest of Dartmoor common, the agreed-upon rates allow an average of 0.52 ewes per hectare (data from stocking rates provided through EIR request).  In a Natural England 2020 Study of 25 years of schemes in the Lake District, habitat response was universally good only up to 0.4 ewes/ha. 


Indeed, the results are there to see – if the levels had been right, with the right numbers of animals grazing at the right times of year, we would have seen the heather recover.  At Willings Walls and Hentor, as elsewhere we have not, and worse, the decline has merely continued.


The compromises are born of powerful vested interests that put grazing rights before nature. The Dartmoor Commoners’ Council was established in 1985 specifically to address the mismanagement of the commons, particularly to tackle animal husbandry and intra-commons disputes. It was at the time novel, and for a while, may have worked in the true interests of the health of the commons. Sadly, it appears to have become little more than a trade organisation for some in the commoning community. What should be an independent public body, using its powers appropriately, has instead become a reactionary organisation working against the changes necessary for nature to start recovering.


Sadly, we also have a compromised regulator. We have seen above what happened when NE tried to make a stand in 2023.  On a neighbouring common, Penn and Stall Moor, local NE officers could not be sure, following a Habitats Regulation Assessment in 2023, that proposed works that were part of an HLS agreement would not cause continuing damage. NE directors waved it through.


It often feels, from the outside, that the local NE approach post-Fursdon is primarily to facilitate commoning and farming, and any benefits to nature are a fortuitous side effect. This is despite the huge weight of their own evidence on the causes and solutions to nature's decline (the aspect of land management that NE are supposed to enable and regulate).


The result of all this is a landscape governed not by ecological needs, but by a deeply entrenched status quo and defence of grazing interests, coupled with a waste of public money. The glacial progress of the new Dartmoor Land Use Management Group does nothing to give any confidence that this is not the case.


If Dartmoor is to have a future rich in nature and restored protected sites, its governance must be reimagined from the ground up. That means giving Natural England the confidence to act decisively when nature is in decline. It means reforming the Dartmoor Commoners’ Council so that it serves the public interest, not just one stakeholder group. It means putting ecological science at the heart of decision-making, rather than burying it beneath negotiation and compromise. And it means creating real consequences when public funds fail to deliver public goods. Restoration is possible, but we need payment by results. 


The lessons from Willings Walls and Hentor are clear: nature recovery cannot happen without reform and a fundamental change of attitude. Without it, the decline will continue—not just here, but across the moor. And we will look back, years from now, and wonder how we ever thought it acceptable to let a national treasure be eaten and burned to death on our watch.


We need bold change. Because Dartmoor deserves better.


 
 
 

Tony Whitehead



The deep peats of Dartmoor’s Commons support internationally important areas of blanket bog. However, they are in a much diminished condition. Last month, Natural England published new assessments that described this habitat as being in unfavourable condition and, in some cases, in decline.


The key reason for this poor condition is the degraded state of the peat on Dartmoor. It has suffered historical cutting and drainage, military activity, and, for decades, intensive burning (known as “swaling” on Dartmoor) tied to managing land to support high numbers of livestock, both cattle and sheep. This resulted in a drop in the water table across the high moor and the drying and erosion of the peat.


This drop in the water table has also changed the vegetation's nature. Peat-forming sphagnum mosses are a vital component of any blanket bog. But they can only thrive in waterlogged conditions when the water table is at or very near the surface. Once it drops, they lose their competitive edge to deeper-rooted plants still able to access water. This is where the Purple Moor Grass, Molinia, comes in.


Molina is a perfectly natural component of a healthy bog. However, it is balanced with other species. Once the peat degrades, the Molinia is given an advantage; its roots are able to reach down to the lowered water table, which other plants cannot reach. Not only that, when a blanket bog is regularly burned, the sphagnum is irreparably damaged.  Like most grasses, Molinia thrives after fires – it regrows from its base into a space now cleared of competitors.


As if this isn’t enough encouragement, animals graze around the Molinia, further removing competition.  The palatability of Molinia is something we’ll return to in a moment. The icing on the cake for Molinia was, from the 80s, the huge increase in atmospheric nitrogen – in short, it started to rain fertiliser on Dartmoor, a final boost for the grass.


On the peripheries of the high moor, high livestock numbers in the 80s and 90s may have suppressed the Molinia’s vigour for a while in the days when favourable subsidies supported numbers of animals way in excess of sustainable limits.  Cattle and ponies will eat the grass, but it is only palatable in Spring; its nutritional value declines rapidly as it dies off in autumn (it is a deciduous grass). They will also trample it. However, the central and more inaccessible parts of the high moor may have long been dominated by the knee-deep tussocks so well known by hikers – archival photographs suggest this.


From the 2000s, much-needed controls on the excessive grazing, combined with a fall in stock numbers post foot and mouth, may have allowed the Molinia to become more vigorous, but by this time, the plant's hold was established.  This is an important point – the plant did not suddenly gain dominance due to a fall in livestock numbers, as some on Dartmoor have it – often those with a vested interest in increasing grazing.  Its rise to dominance has been a much longer process, and is a symptom of degraded peat.


Fortunately, the symptom points to the cure. Raising the water table and restoring the peat is the only way to restore the blanket bogs and restore balance to the system, where Molinia is in healthy balance with other plants.  In this way, the habitat can be returned to favourable condition, with all the societal benefits that flow from healthy bogs - carbon sequestration, flood control, clean water, etc. Rewetting the peat will, of course, also increase the peat’s resilience to wildfire. The South West Peat Partnership is doing some great work on Dartmoor in this respect.


Crucially and perhaps controversially, livestock have no useful purpose in restoring and maintaining Dartmoor’s blanket bogs.  Some argue that cattle on the high moor in Spring and Summer can be used to suppress the Molinia.


First, there’s the simple point that even if grazing was useful, the cattle to do this are probably not available, and even if they were, there are practical problems about how commoners can keep cattle on the high moor. I imagine nothing more galling than to take a herd to the central high moor to find the animals back at the moor gate the following day because that’s where all the nice grass is!  Remember that the central parts of moor are very poor grazing land because the vegetation underpinned by the peat lacks the minerals necessary for a healthy diet.


Second, cattle grazing Molinia might cause more damage than they cure by trampling sphagnum and other plants that survive in places beneath it. If you look at the Molinia-dominated parts of the moor, on many of the slopes, it is something of a monoculture, but on the flatter, still-wet bits, you will often find cotton grass and moss around the Molinia, just awaiting restoration to flourish and spread. 



In relation to trampling, we also need to consider the potential damage caused by commoners accessing their herds using 4WD vehicles and quad bikes (note that the peat restoration teams deliberately use low ground pressure, wide track machines to avoid damage).


Third, perhaps also controversially, while awaiting restoration, the Molinia can still provide a valuable role even where it is dominant. It protects the underlying peat from exposure to the atmosphere, and it may slow the flow of water off the moor. It’s not ideal, but it’s not useless either.


Given this, it’s high time we looked again at the role of commoners in relation to the restoration of the blanket bogs.  Currently, they are paid through Higher Level Stewardship to graze Molinia-dominated areas.  For the above reasons, this may not be necessary. What we need to do is rewet the bogs. Without this, to be blunt, grazing the Molinia will achieve nothing. Then, once rewetted, we need to maintain the restored area, but here again, grazing is unnecessary, as a recently published Natural England report on the favourable condition of blanket bogs stated (my emphasis): 


Large areas of the English uplands, including areas of blanket bog, are subject to livestock grazing. There are fewer grazing animals now than before headage payment subsidies ended in 2005. Future trends in livestock numbers are uncertain but grazing management is not required to maintain blanket bog, so further reduction or cessation of grazing is not a threat to this habitat.


The suggestion, therefore, is to stop paying for grazing the Molinia through Higher Level Stewardship and instead direct the money towards providing opportunities for commoners to become more involved in the peat restoration work. We need to level up the amount we are doing, which requires materials, knowledge of the land, and willing hands with practical skills. There’s also a role possibly in the aftercare of the works – dams built to hold back water need checking and maintenance.


In summary, the restoration of Dartmoor’s blanket bogs is vital and dependent on rewetting.  Grazing has no role in restoration and maintenance, but there are new opportunities for the profitable involvement of the local commoning community and others.


 
 
 

Tony Whitehead



Without so much as a whisper publicly, Natural England this week updated its assessment of Dartmoor’s protected sites, the three big Sites of Special Scientific Interest (SSSIs) that cover Dartmoor's commons. The new assessments covered 22,494ha - 24% of the whole National Park - and are based on an extensive survey by Natural England in 2024. 


It is not a pretty picture. 


To summarise, every designated feature assessed is in unfavourable condition, with the exception of two tiny “soakaways” in East and North Dartmoor. That’s all Dartmoor’s blanket bogs, wet heaths, and dry heaths. And worse still, many are declining in condition. 


Regarding the individual SSSI units (subdivisions of the whole), if you look at those newly assessed only 26ha of 22,494ha are in favourable condition. If you compare that with the previous assessments of those same units, that’s a significant drop from a still dismal 914ha  in favourable condition. Notably, the land area in unfavourable declining condition has doubled from 1,527ha to 3,178ha.


You can read the assessments for the designated features and the units of each SSSI here, here and here.  


Despite many millions of pounds of public investment in Dartmoor over the past three decades, Dartmoor’s commons remain in appalling condition. This begs two crucial questions - what exactly has the taxpayer paid for? And secondly, with agri-environment schemes (Higher Level Stewardship) currently being extended, what are we going to be paying for? 


At the inaugural meeting of the new Dartmoor Land Use Management group in January, a local Natural England Officer said that NE would “very shortly be communicating with HLS agreement holders, offering two-year extensions to current agreements subject to some potential ‘tweaks’ to management plans".


Potential tweaks? Given the appalling state of the commons, it would not be unreasonable to demand a little more than possible “tweaks” to schemes that have so singularly failed to deliver more nature, and in many cases simply paid for decline. Surely we should be asking for wholesale reform?  


Or perhaps we should not be paying any more taxpayers’ money to Dartmoor commons schemes that have so obviously failed, and spend it instead where it could make a genuine difference.


To be clear - this is not a criticism of all agri-environmnet schemes per se or of ambitious farmers that use the investment wisely to deliver for nature.  We know that many farmers on Dartmoor are keen for change - support for the Central Dartmoor Landscape Recovery scheme is an example. But the fact remains, that the taxpayers must see a return on their investment and begin to see nature restored rather than in decline. 


With these questions in mind, here’s a background and summary of the assessments. 


Background


The majority of Dartmoor’s common land is notified as Sites of Special Scientific Interest (SSSI). The first designations of SSSI on Dartmoor were in 1952 with further designation in 1976. The current suite of SSSIs were designated in 1987 and 1989 with renotification and extension of the original sites under the Wildlife and Countryside Act, 1981.


SSSI selection is based on the presence of the particular features of interest. It operates on a principle of establishing a network of sites representing in total those parts of Great Britain in which the features of nature are most highly concentrated or of highest value. 


These large upland SSSIs recognised the importance of Dartmoor’s blanket bogs and heathland, based on a national listing of ‘near natural’ or semi-natural’ special sites first developed in 1947. The rationale for notification was to notify a large area to include examples of vegetation types that are distinct from other parts of Britain.


The vegetation of Dartmoor is of particular interest for its extensive areas of internationally important blanket bog and some of the best areas of wet heath in England. These wet and predominantly western communities occur alongside equally important dry heath.


There are three SSSIs covering the commons: 


East Dartmoor SSSI (211.36 ha) was first notified in 1976 and notified under the 1981 Act in 1987 with amendments to the boundary including extensions and deletions.


South Dartmoor (9,668.2 ha) was notified in 1952, revised in 1976 and notified under the 1981 Act in 1989, with amendments to the boundary including extensions and deletions. The SSSI name has been changed from Central South Dartmoor. The site now includes High-house Waste, formerly part of Hawn's Wood and High House Moor SSSI (now Dendles Wood SSSI). Part of the site notified initially in 1951 has since been re-notified as part of the Holne Woodlands SSSI.


North Dartmoor (13,413 ha) was notified in 1952, revised in 1976 and notified under the 1981 Act in 1989, with amendments to the boundary including extensions and deletions. The extensions include the formerly separate Gidleigh Common SSSI and Black Tor Copse Forest Nature Reserve.


Monitoring SSSI Condition


SSSI condition was not objectively assessed when the Dartmoor SSSIs were notified in the 1950’s. Selection was based on the presence of key features rather than their condition. 


At the time of the notification under the Wildlife and Countryside Act in the 1980s, it was recognized that a large proportion of the Dartmoor's SSSIs supported degraded examples of habitat. However, these were the best examples available and were sufficiently intact to be of special interest. A potential for recovery was recognised.


The objective assessment of SSSI condition, referred to as Common Standards Monitoring (CSM), was introduced in 1998 (JNCC 2004). Natural England is responsible for assessing the condition of all SSSIs using CSM.


Using the CSM methodology, Natural England produces a Monitoring Specification (aka Favourable Condition Tables), which sets the attributes and targets used to assess the current state of each designated site feature. 


On Dartmoor the designated features of the SSSI are: Blanket Bogs and Valley Bogs, Wet Heaths, Acid Grassland, Subalpine Dwarf Shrub Heath, Soakaways and Sumps and Short Sedge Acidic Fen. 


The Monitoring Specifications for the three Dartmoor SSSIs can be found here:



The data collected through CSM surveys then defines the following categories, which are used to describe the condition of the SSSI:  


Favourable - The designated feature is being adequately conserved.


Unfavourable recovering - The feature is not yet fully conserved but the necessary actions to achieve favourable condition have either been identified and recorded, or at least one action underway or no actions behind schedule


Unfavourable no change -  The feature is not being conserved. It will not reach favourable condition unless there are changes to the management or external pressures. The longer the feature remains in this poor condition, the more difficult it will be, in general, to achieve recovery. 


Unfavourable declining - The feature is not being conserved and will not reach favourable condition unless there are changes to management or external pressures. The feature condition is becoming progressively worse. The longer the feature remains in this poor condition, the more difficult it will be, in general, to achieve recovery. 


In addition to detailing the site's condition using the above categories, CSM also identifies the pressures and threats to designated features evident in the collected data.  These are those things driving a designated feature into unfavourable condition. 


In the 2024 Dartmoor survey, “Whole feature assessments” were introduced to assess the condition of designated features (eg Blanket Bogs etc) across the whole of the SSSIs. 


The Results


The following summarises the condition of each key feature: 


Table 1: Condition of SSSI Designated Features:

SSSI

Designated Feature

Condition 2024

South Dartmoor SSSI

Acid Grassland

Unfavourable Declining

North Dartmoor SSSI

Acid Grassland 

Unfavourable No Change 

East Dartmoor SSSI

Acid Grassland / Dry Heath Mosaic

Unfavourable Declining

East Dartmoor SSSI

Blanket and Valley Bogs

Unfavourable Declining

North Dartmoor SSSI

Blanket and Valley Bogs

Unfavourable No Change 

South Dartmoor SSSI

Blanket and Valley Bogs

Unfavourable Declining

East Dartmoor SSSI

Short Sedge Acidic Fen

Unfavourable No Change 

North Dartmoor SSSI

Short Sedge Acidic Fen

Unfavourable No Change 

South Dartmoor SSSI

Short Sedge Acidic Fen

Unfavourable Declining

East Dartmoor SSSI

Soakaway and Sump

Favourable

North Dartmoor SSSI

Soakaway and Sump

Favourable

South Dartmoor SSSI

Soakaway and Sump

Unfavourable Declining

East Dartmoor SSSI

Subalpine dwarf shrub heath

Unfavourable Declining

North Dartmoor SSSI

Subalpine dwarf shrub heath

Unfavourable No Change 

South Dartmoor SSSI

Subalpine dwarf shrub heath

Unfavourable Declining

East Dartmoor SSSI

Wet Heath

Unfavourable Declining

North Dartmoor SSSI

Wet Heath

Unfavourable No Change 

South Dartmoor SSSI

Wet Heath

Unfavourable Declining


In terms of whole features, only the very small soakaways and sumps in East and North Dartmoor were found to be in Favourable Condition. 


Every other designated feature is in unfavourable condition, which means that “the feature is not being conserved” and “It will not reach favourable condition unless there are changes to the management or external pressures.”


Ten features are in declining condition, which means their condition is becoming progressively worse, and “the longer the feature remains in this poor condition, the more difficult it will be, in general, to achieve recovery.” 


Comparison by Unit with Previous Condition


The assessment also looked at individual SSSI - subdivisions of the whole SSSIs.  There’s much to look at here, and we’ll come back to this.  Looking at individual units and knowing their area allows us to compare the current condition with the previous condition. The latest assessments included all units across all three SSSI’s with the exception of North Dartmoor Unit 91, Blackator Copse and South Dartmoor Unit 3 Foxtor Mire. 


Of the total area assessed, only three units, amounting to 26ha were found to be in Favourable Condition. Overall the area of units in favourable condition has fallen from 914ha previously. Notably, the area of land in unfavourable declining condition has increased from 1,527ha to 3,178ha.


Pressures


The table below summarises the key pressures. 


The first thing to note is how many times overgrazing is listed as a pressure. It is clear that this still remains a key issue for Dartmoor. Alongside this, undergrazing is listed on a number of occasions, where it is linked to the dominance of the Purple Moor Grass, aka “Molinia”. 


This is interesting because it can be argued that the Molinia dominance is a symptom of the degraded condition of the peat. However, grazing could be part of the solution - but as is known, there are questions about getting cattle into the right places to do this work in the periods when it is palatable. 


“Weeds and inappropriate species” is also mentioned on a number of occasions. This is often related to gorse and bracken, but also to the spread of young conifers that have “escaped” from the large plantations. This is also interesting - gorse and bracken can be important in themselves, as nurseries for scrub and woodland development.  Or in the case of bracken, as an important habitat in itself for some butterflies and for birds such as Whinchat.  But the point is, that in excess these can indeed impact on key features, and this needs careful consideration. 


Lastly, note that “managed burning” (“swaling”) is recorded as a pressure on the dwarf shrub heath in south Dartmoor. As said elsewhere, swaling is a significant issue for the future of Dartmoor's wildlife and habitats.


Table 2: Pressures on SSSI Designated Features 

SSSI

Designated Feature

Condition 2025

Pressure

South Dartmoor SSSI

Acid Grassland

Unfavourable Declining

Land management – Over grazing should be recorded as a pressure for this interest feature.


Land management (scrub encroachment and inappropriate species) should be recorded as a pressure for this interest feature.

North Dartmoor SSSI

Acid Grassland 

Unfavourable No Change 

Land Management – Over grazing should be monitored and recorded as a pressure for this interest feature

East Dartmoor SSSI

Acid Grassland / Dry Heath Mosaic

Unfavourable Declining

Land management – Over grazing and Weeds / Inappropriate species would be recorded as a pressure for this habitat if it was a feature of the SSSI. 

East Dartmoor SSSI

Blanket and Valley Bogs

Unfavourable Declining

Land management, in particular over and under grazing, should be recorded as a pressure for the blanket bog interest feature.

North Dartmoor SSSI

Blanket and Valley Bogs

Unfavourable No Change 

Land Management – Over and Under grazing should be included as a pressure

South Dartmoor SSSI

Blanket and Valley Bogs

Unfavourable Declining

Land management, in particular over and under grazing, should be recorded as a pressure for the blanket bog interest feature.

East Dartmoor SSSI

Short Sedge Acidic Fen

Unfavourable No Change 

Land management – Weeds / Inappropriate species and under grazing should be recorded as a pressure.  

North Dartmoor SSSI

Short Sedge Acidic Fen

Unfavourable No Change 

Land management – Weeds / Inappropriate species should be recorded as a pressure

South Dartmoor SSSI

Short Sedge Acidic Fen

Unfavourable Declining

Land management – Weeds / Inappropriate species should be recorded as a pressure.


Land management -Over grazing should be recorded as a pressure for this interest feature.

East Dartmoor SSSI

Subalpine dwarf shrub heath

Unfavourable Declining

Land management – over grazing and Weeds / Inappropriate species will be recorded as pressures to achieving favourable condition for subalpine dwarf shrub heath interest feature.

North Dartmoor SSSI

Subalpine dwarf shrub heath

Unfavourable No Change 

Land management – Over grazing should be recorded as a pressure for subalpine dwarf shrub heath.

South Dartmoor SSSI

Subalpine dwarf shrub heath

Unfavourable Declining

Land management – over grazing and Fire – Managed burning will be recorded as pressures to achieving favourable condition for subalpine dwarf shrub heath interest feature.

East Dartmoor SSSI

Wet Heath

Unfavourable Declining

Land management – Over Grazing should be recorded as a pressure for this interest feature.

North Dartmoor SSSI

Wet Heath

Unfavourable No Change 

Land management- over grazing should be recorded as a pressure for this interest feature.

South Dartmoor SSSI

Wet Heath

Unfavourable Declining

Land management – Over and Under Grazing should be recorded as a pressure for this interest feature.


Conclusions


This is the briefest summary of the data - there is much more to return to, not least further analysis of the condition of individual site units. 


These assessments of 'protected' sites have revealed their appalling condition. In many places, the trend is one of decline. 


The pressures listed reveal clearly that grazing remains a key issue. In many places, the evidence from Natural England shows that overgrazing continues to hold back recovery, particularly of heathland. In others, lack of grazing, especially by cattle, is allowing the Purple Moor grass on blanket bogs to further flourish on areas suffering the historic eroding effects of excessive burning and overgrazing. 


Over twenty years, millions of pounds of public money have been invested in restoring Dartmoor’s commons, and it has produced no change whatsoever, and in some places it’s got worse. What’s particularly galling is that we know, elsewhere, investing in nature restoration can deliver. 


We are in a nature and climate crisis. Dartmoor should be playing its part - but these shameful results show how much we need to start putting nature first in this special and much-loved landscape. And think very carefully how public money, our money, is invested in this place. 


We cannot keep funding failure.


 
 
 

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