Modified Grassland BNG Units
Low
Grassland
Widespread across lowland Britain, especially in improved farmland and amenity grasslands


Trusted by Developers and Landowners
What are Modified Grasslands?
Modified grassland is species-poor vegetation, usually with fewer than nine species per square metre. It is dominated by vigorous grasses and clovers on nutrient-enriched soils. The habitat is typically created by agricultural improvement, through reseeding, slurry, and heavy grazing or frequent mowing.

Why It Matters for BNG
Modified grassland offers a practical baseline habitat for uplift. Enhancement to higher condition neutral grassland satisfies metric requirements and aligns with long term management plans for development sites.
Landowners can transition improved fields into higher value grassland through nutrient reduction and revised cutting schedules. This shift creates dependable BNG supply with limited capital input.
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Where Does It Grow?

Modified grassland is common across farmland and developed areas, including:
• Intensively managed pastures dominated by rye-grass and white clover
• Amenity grasslands such as parks, sports pitches, and road verges
• Margins and set-aside fields where nutrient levels remain high
Soil Preferences
Occurs on fertile, neutral soils enriched by long-term nutrient inputs.
How New Modified Grassland Is Created
Modified grassland is not normally created deliberately within BNG projects, as it is a low-distinctiveness habitat that delivers little ecological uplift.


How Existing Modified Grassland Is Improved
Modified grassland can be improved through changes in management that gradually reduce soil fertility and allow a more diverse sward to establish. Key measures include:
Inputs
• Cease reseeding and herbicide use to allow natural regeneration
• Reduce nutrient inputs by ending fertiliser and slurry applications
• Introduce hay cutting with removal of arisings to lower soil fertility
• Plug planting or spreading green hay from species-rich meadows where seedbanks are depleted
Management
• Light aftermath grazing to vary sward height and open gaps for herbs
• Rotational cutting or grazing to avoid uniform structure
• Controlling scrub encroachment without eliminating valuable edges
Landscape
• Establish buffer strips to reduce nutrient run-off from adjacent farmland
• Target improvements near existing species-rich grasslands to encourage colonisation
• Link improved sites with wider habitat networks to increase resilience
With time and sustained management, modified grassland can transition into Other Neutral Grassland in good condition, a habitat of medium distinctiveness and higher biodiversity value.
Target Condition
Modified Grassland in good condition is defined by reduced nutrient levels, varied sward structure, and the presence of wildflower species beyond rye-grass and clover. This reflects an active transition towards semi-natural grassland.


The BNG Value of Modified Grasslands
• Distinctiveness: Low
• Condition Potential: Limited; primarily valued as a baseline for enhancement
• Habitat Connectivity: Provides only weak ecological linkage, but can act as a stepping stone if improved
• Climate Services: Stores some carbon in soils and provides forage, but far less than semi-natural alternatives
Species Typical of Modified Grasslands
🌱 Flora
• Perennial rye-grass (Lolium perenne)
• Yorkshire fog (Holcus lanatus)
• Cocksfoot (Dactylis glomerata)
• White clover (Trifolium repens)
Occasional dock (Rumex spp.) and nettle (Urtica dioica) in enriched areas.
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Frequently Asked Questions
What is Modified Grassland?
This refers to grassland that has been heavily managed, often with fertilizer and intensive cutting/grazing, resulting in low species diversity (e.g., intensive agricultural fields or amenity lawns).
How is BNG measured here?
Due to its low inherent value, it usually scores a very low distinctiveness and condition (often Poor), meaning a large biodiversity uplift can be demonstrated if it is enhanced or converted.
How can I achieve BNG?
This habitat is a prime target for BNG Creation or high-level Enhancement to a higher-value type, such as Lowland Meadow, Lowland Mixed Deciduous Woodland, or Scrub.
What is the BNG target condition?
The target is rarely to enhance Modified Grassland itself but to convert it into a target habitat type (e.g., aiming for a Moderate condition of a newly created Lowland Meadow).
What management is required?
Depends entirely on the target habitat. For conversion to meadow, a multi-year program of nutrient-stripping cuts and removals is necessary, followed by annual hay-cutting.
Exploring Other Habitats?

Rural Tree
Rural trees are individual trees located in the open countryside that do not form part of woodland, hedgerow or wood-pasture habitats. They include isolated field trees, parkland trees, scattered trees in paddocks, and trees along rural roadsides or watercourses where they are not part of a continuous linear feature.
Ancient and veteran trees in rural locations are also recorded under this habitat type and are additionally flagged as irreplaceable habitat, meaning impacts should be avoided wherever possible.

Upland Mixed Ashwood
Upland mixed ashwoods are species-rich broadleaved woodlands found on base-rich soils in upland landscapes. They are typically dominated by ash, though locally oak, birch, wych elm, rowan, small-leaved lime or hazel may be prominent depending on site conditions.
These woodlands often develop on limestone and other calcareous substrates, including steep slopes, ravines, flushes and rocky outcrops. Many upland mixed ashwoods are ancient woodland, while others represent long-established secondary woodland that retains strong ecological continuity.
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Ponds (Non-Priority Habitat)
Non-priority ponds are small standing waterbodies, generally up to two hectares in size, that do not meet the priority pond criteria but still function as semi-natural freshwater habitats. Non-priority ponds include many farm ponds, estate ponds, attenuation ponds with natural features, and older field ponds that support aquatic and marginal vegetation but lack the exceptional species assemblages required for priority status.
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