What Are Moors in England? A Look at the Landscape

Moors are open, treeless upland landscapes defined by acidic soils, low-growing vegetation, and persistent wind and rain. They cover roughly a tenth of England’s land area, stretching across the Pennines, the North York Moors, Exmoor, Dartmoor, and parts of the Lake District. What looks like untouched wilderness is actually a landscape shaped by thousands of years of human activity, and one that sits at the center of fierce debates about carbon storage, wildlife conservation, and public access.

What Makes a Moor a Moor

There is no single geological recipe for a moor. The common thread is an exposed upland terrain where thin, nutrient-poor soils and a wet, cool climate prevent trees from establishing. Dartmoor, the largest granite moorland in southern England, covers about 625 square kilometers at elevations between roughly 300 and 620 meters, its rolling plateau punctuated by granite outcrops called tors and cut by river valleys up to 200 meters deep along its edges.1Elsevier. The granite tors of Dartmoor, Southwest England: rapid and recent emergence revealed by Late Pleistocene cosmogenic apparent exposure ages The Pennine moors, by contrast, sit on millstone grit and limestone, and the North York Moors on sandstone. What unites them is what happens at the surface: waterlogged conditions slow the breakdown of dead plant material, and over centuries that half-decomposed matter builds up into peat, sometimes meters thick.

The distinction between a “moor” and a “heath” sometimes confuses people. In everyday English, the two words overlap heavily. Broadly, “heath” tends to describe lowland areas with dry, sandy soils and heather cover, while “moor” usually refers to higher ground with wetter, peatier soils. In practice, many landscapes grade from one into the other, and the terms get used interchangeably in local place names. What matters ecologically is the combination of altitude, rainfall, drainage, and soil chemistry, not the label.

The Plants That Define the View

If you have ever driven through the Peak District or across Dartmoor, the dominant visual impression is a carpet of low, scrubby vegetation in shades of brown, green, and purple. The signature plant is heather, particularly common heather (Calluna vulgaris) and bell heather (Erica cinerea). In wetter hollows, you find cotton grasses, sphagnum mosses, and bilberry. On drier ridges, bracken and gorse can muscle in. The absence of trees is striking, especially compared to the wooded valleys just downhill, and it is mostly a consequence of human clearance stretching back to the Bronze Age and sustained by grazing and burning ever since.

These plants are remarkably well adapted to disturbance. A recent assessment of UK heath and mire species found that 97 percent of the plants examined carry some form of fire-adaptive trait, whether that means the ability to resprout from roots after burning, seeds that survive fire in the soil, or the capacity to colonize newly burned ground from wind-dispersed seed.2PubMed Central. Adaptive plant traits under anthropogenic burning regimes: A database for UK heath and mire plant species That is not a coincidence. Moorland vegetation has been living with fire, both natural and human-set, for so long that plants lacking fire resilience were filtered out long ago. The landscape looks sparse and fragile, but the plant community is tougher than it appears.

Sphagnum mosses deserve special mention because they are the engine of peat formation. These small, sponge-like plants hold enormous quantities of water and, as they grow, their lower layers die and compact into peat rather than fully decaying. A long-running experiment on English peatland found that sphagnum species were more common on plots that received short-rotation prescribed burns than on plots left unburned for longer periods.3PubMed Central. Impacts of prescribed burning on Sphagnum mosses in a long-term peatland field experiment That result surprised some conservation advocates who expected all burning to harm mosses, and it feeds into a wider argument about how moorlands should be managed.

Moorland Wildlife

English moors are among the most important habitats in Europe for ground-nesting birds. The open landscape with minimal tree cover suits species that nest on the ground and rely on long sightlines to spot approaching predators. Golden plover, curlew, lapwing, red grouse, skylark, meadow pipit, and snipe all breed on moorland in significant numbers. Several of these species are in steep decline nationally, which makes the moors’ role as a remaining stronghold even more significant.

What controls bird populations on moorland is a contentious question. An eight-year field experiment in northern England found that legally controlling foxes and carrion crows led to an average threefold increase in breeding success for lapwing, golden plover, curlew, red grouse, and meadow pipit. Breeding numbers of those species grew by at least 14 percent per year where predators were controlled, while they declined by at least 17 percent per year where predator control was absent.4Journal of Applied Ecology. Changes in breeding success and abundance of ground-nesting moorland birds in relation to the experimental deployment of legal predator control A separate study on a Scottish grouse moor tracked what happened when active management ceased: golden plover, lapwing, curlew, and red grouse all declined, while carrion crow numbers climbed.5Ibis. The direct and indirect effects of predation by Hen Harriers Circus cyaneus on trends in breeding birds on a Scottish grouse moor

Beyond birds, moors support populations of mountain hare, adder, common lizard, and in some areas, the elusive ring ouzel, sometimes called the “mountain blackbird.” Dartmoor’s semi-wild pony herds are themselves a conservation tool: their grazing and trampling reduces the dominance of purple moor-grass (Molinia caerulea), a tough, tussock-forming species that can shade out heather if left unchecked. Trials using salt blocks to concentrate pony activity in specific areas showed clear reductions in moor-grass cover and an increase in heather seedling germination.6Conservation Evidence Journal. Using Dartmoor ponies in conservation grazing to reduce Molinia caerulea dominance and encourage germination of Calluna vulgaris in heathland vegetation on Dartmoor, UK

A Landscape Shaped by People

One of the biggest misconceptions about English moors is that they are natural wilderness. They are not. Most moorland was forested after the last ice age, covered in birch, oak, and hazel. Clearance began in the Neolithic period and intensified through the Bronze Age, when communities burned and felled trees to create pasture for livestock. Once the trees were gone, grazing animals, burning, and the wet, acidic conditions prevented regrowth. The open moor we see today is, in ecological terms, an artifact of human land use maintained over millennia.

That history explains a paradox. Moorland is sometimes described as “degraded” because it has lost its original tree cover, yet it is also classified as a priority habitat under UK and European conservation law because of the specialized species it now supports. Both things are true. The landscape was created by removing something (forest), but in the thousands of years since, a distinct ecological community has developed that would itself be lost if the moor were simply allowed to revert to woodland. This tension between rewilding advocates who want to see trees return and conservationists who want to protect open moorland habitats is one of the liveliest arguments in British ecology.

Grouse Moor Management and Its Critics

A substantial proportion of English upland moorland is managed for driven grouse shooting, an industry with deep cultural roots in northern England and Scotland. Management typically involves rotational heather burning, where small strips of older heather are set alight on a cycle of roughly 8 to 15 years, creating a patchwork of different-aged heather stands. Young heather provides nutritious food for red grouse; older, taller heather provides nesting cover. Alongside burning, gamekeepers control predators like foxes and stoats and maintain drains and tracks.

The effect on bird populations is measurable. One large-scale comparison found that grouse moors carried out rotational burning over about a third more area than non-grouse moors, and this burning was associated with higher densities of red grouse and golden plover, though meadow pipit densities were lower. Predator control and heather burning each had statistically separate effects on red grouse numbers.7Journal of Applied Ecology. The effect of management for red grouse shooting on the population density of breeding birds on heather‐dominated moorland Proponents of grouse shooting argue that without the economic incentive the sport provides, estates would abandon active moorland management, and bird populations would crash as predators went unchecked.

Critics counter that the burning damages peat, releasing stored carbon, and that predator control sometimes extends illegally to protected raptors like hen harriers and peregrine falcons. The persecution of raptors on grouse moors is well documented by conservation organizations and remains a serious enforcement problem, though it is not endorsed by any shooting body. The debate is genuinely polarized: environmental groups such as the RSPB and conservation scientists point to carbon loss and raptor killing as unacceptable costs, while moorland managers and some ecologists argue that the alternative, unmanaged moors with no burning, no grazing control, and no predator management, produces worse outcomes for many vulnerable species. The evidence, as the studies above suggest, supports elements of both positions, which is precisely why the argument refuses to settle.

Carbon, Peat, and Climate

English peatlands, including moorland bogs, store an enormous quantity of carbon, locked into partially decomposed plant material built up over thousands of years. Healthy, waterlogged peat acts as a carbon sink, slowly absorbing carbon dioxide from the atmosphere. Damaged or drained peat does the opposite: it dries out, begins to decompose aerobically, and releases its stored carbon as CO₂. Research on restored peatlands shows that carbon dioxide is the most significant component of long-term climate impact. On average, rewetted open peatlands store around 534 kilograms of carbon per hectare per year, while drained peatland can lose over a tonne of carbon per hectare annually through peat decomposition.8PubMed Central. Peatland restoration pathways to mitigate greenhouse gas emissions and retain peat carbon

These numbers matter because England’s upland peat is in poor condition. Centuries of drainage for agriculture, overgrazing, air pollution, and more recently, infrastructure construction have left much of it eroding. Even supposedly benign interventions carry costs. A study of wind farm construction on a blanket peat catchment in Scotland found that building access roads and turbine foundations elevated dissolved organic carbon concentrations in nearby streams by 2 to 5 milligrams per liter compared to undisturbed streams, and suspended sediment concentrations spiked to four or five times background levels during peak rainfall. The additional carbon lost from the disturbed catchment was estimated at 5 grams per square meter.9Mires and Peat. Effects of Wind Farm Construction on Concentrations and Fluxes of Dissolved Organic Carbon and Suspended Sediment From Peat Catchments at Braes of Doune, Central Scotland The irony of damaging a carbon store to build renewable energy infrastructure has not been lost on critics, though the long-term carbon math generally still favors the turbines over fossil fuels.

Restoring Eroded Moorland

Across the Pennines and the Peak District, large-scale restoration projects are underway to repair eroded blanket peat. The damage is visible from the air: networks of gullies, some several meters deep, cut through the peat like drainage channels, carrying dissolved carbon and sediment into rivers. The approach to healing these gullies borrows from what the peat does naturally. Studies of how eroded gullies recover on their own have identified a two-phase process: first, common cottongrass colonizes the bare peat as a pioneer, stabilizing the surface; then a second wave of up to six additional species moves in, establishing either wet bog or dry heath vegetation depending on local conditions.10Mires and Peat. Geomorphological Controls on the Re-Vegetation of Erosion Gullies in Blanket Peat: Implications for Bog Restoration

Restoration teams mimic and accelerate this natural sequence. They block drainage ditches with small dams made of peat, stone, or heather bales to raise the water table. They spread locally harvested sphagnum moss fragments onto bare peat. They seed cottongrass and apply lime and fertilizer to give plants a foothold on surfaces too acidic and nutrient-poor for quick establishment. The work is labor-intensive and expensive, but the results are encouraging in areas where projects have had a decade or more to mature. Rewetted peat stops crumbling, starts accumulating new plant material, and reduces the brown, carbon-laden water that otherwise flows into reservoirs, a practical benefit that helps justify the cost to water companies who co-fund many of these schemes.

The Fight for Access

English moors played a pivotal role in the history of public access to the countryside. For centuries, vast tracts of upland were privately owned and managed as grouse moors or sheep pasture, and walkers who strayed onto them could be prosecuted for trespass. Frustration with this situation boiled over on 24 April 1932, when a group of 400 to 600 young workers from Manchester and Sheffield, led by 20-year-old Benny Rothman, staged a mass trespass on Kinder Scout, the highest point in the Peak District. Six walkers were arrested and five were sentenced to jail terms of between two and six months.11British Online Archives. Right to Roam: The Kinder Mass Trespass of 1932

The Kinder trespass did not immediately change the law, but it became a rallying symbol. The National Parks and Access to the Countryside Act of 1949 created the Peak District as England’s first national park, and eventually the Countryside and Rights of Way Act of 2000 established a legal right to walk on mapped open land, including most moorland. Today, you can walk freely across the vast majority of English moors without permission. The cultural memory of the access struggle runs deep in northern England, where moorland walking is not just recreation but a point of regional identity.

What It Feels Like on the Ground

Reading about moors in the abstract misses something essential: the sensory experience. Moorland is one of the few landscapes in densely populated England where you can stand and see no buildings, no roads, and no trees in any direction. The sound environment is wind, the call of curlews (a haunting, bubbling trill), and in summer, the go-back-go-back alarm call of red grouse exploding from the heather at your feet. The ground underfoot is uneven and often soggy, ankle-deep in sphagnum in the wetter areas, crunchy with dried heather stems on the ridges. In August, the heather blooms and the moors turn purple across entire horizons.

The weather is a defining feature. Upland moors receive far more rainfall than lowland England, and conditions can shift from sunshine to driving rain and low cloud in minutes. Exposure is real: the Pennine Way, a long-distance trail that follows the spine of England’s moorland, has a reputation for testing experienced walkers with navigation challenges in poor visibility. The combination of featureless terrain and sudden fog has caught out many hikers over the years. For those willing to deal with the conditions, the reward is a landscape unlike anything else in England, vast, open, and profoundly quiet.

Moorland in Literature and Imagination

English moors have shaped the cultural imagination far beyond their physical boundaries. Emily Brontë’s “Wuthering Heights” is inseparable from the West Yorkshire moors above Haworth, where the wild, windswept landscape mirrors the emotional extremes of the novel. Arthur Conan Doyle set “The Hound of the Baskervilles” on Dartmoor, exploiting the moor’s fog, bogs, and isolation to create an atmosphere of menace. The moors in these stories are rarely neutral backdrops; they function as characters, hostile or liberating depending on the author’s purpose.

This literary tradition has practical consequences. It draws millions of visitors to moorland national parks each year, supporting rural economies but also creating pressure on fragile habitats. Footpath erosion on popular routes like the Pennine Way or the Haworth moor walks has required extensive and costly repair work, often using stone pitching or recycled materials laid by hand. The tension between access and preservation is a recurring theme in moorland management, and it rarely has a clean resolution. The moors endure, as they have for centuries, shaped by the competing demands of the people who walk them, manage them, study them, and fight over their future.