Biodiversity Net Gain

One of the aims of the Government’s 25-year Environment Plan, is to “leave the environment in a better state than we found it”. One way the Government hope to achieve this is found in the Environment Act which, from late 2023 will require developers to contribute at least 10% net gain in biodiversity on their development land. This biodiversity value can include actions such as creating habitats and nature reserves on nearby land.  

Developers must set out how their net gain will be achieved as part of their planning application. Whilst they are encouraged to provide net gain on site if possible, many will have to either purchase land to create/improve habitat or pay someone to establish it for them. For farmers and landowners this represents an opportunity to create more income from unprofitable areas of land (as well as productive areas) and can complement the holding’s areas of productive farming. There is also the potential for synergy with other areas of diversification such as sporting or tourism. The downside is land will be locked up for at least 30 years. These conservation covenants will run with the land, creating binding targets and obligations on whoever buys or inherits the land. 

The biodiversity net gain (BNG) that developers require, and landowners will create, is represented by ‘biodiversity units’ calculated via the Biodiversity Metric 3.1. This will provide the common standard required for quality assurance for purchasers and regulates exactly what the provider is required to do. It is interesting to see how BNG interacts with other environmental schemes such as ELMS. It is generally understood that benefits can ‘stack’ as long as the same outcomes are not double counted. The British Standards Institution’s guidance, BS 8683, defines this as not paying for something that would happen anyway, whereas DEFRA simply say they will not pay for the same thing twice. The latter statement suggests more leeway and that the by-product of one scheme may be sold separately to the initial action e.g. creating woodland for biodiversity then selling the carbon sequestered as credits. In this instance you are not selling the carbon itself twice as you are being paid to create/improve habitat rather than sequestering carbon, making use of all revenue streams available from taking land out of production. This would make sense as it would encourage the overall uptake of landowners willing to take part. 

There are two main options, habitat creation and habitat enhancement/restoration. These will involve actions such as planting woodland, sowing wildflower meadow, creation of wetlands and ponds, hedgerows, tree lines, scrub belts and grassland verges. All habitats must be secured for at least 30 years. 

 The Environment Act also introduces provisions to implement a Local Nature Recovery Strategy. This will support the delivery of biodiversity net gain by putting a duty on local authorities to map and record areas with potential for creating or improving habitat and other environmental goals. This will involve mapping valuable existing areas, making specific proposals for improvement and agreeing priority areas and outcomes for evidence based, locally led plans. These may then be used to offset developers’ projects.  

Example of calculating a site’s biodiversity units 

Calculating original site’s baseline 

There are several factors and multipliers involved in calculating the units a site will lose or gain including area, distinctiveness, condition, strategic significance, impact of development, time to reach desired level, difficulty of establishment, risk and proximity to development site. The higher the development site’s biodiversity, the more habitat will be lost from the development and in turn required from off-site projects to make up a 10% net gain. This process will discourage new development on sites of high biodiversity.  

First the original baseline of the area to be developed is established. Then the impact of the developmental actions and any existing habitat lost are calculated and subtracted from the baseline. After the developer has established the on-site losses, they must try to deliver on-site gains. Where this does not reach 10% net gain, they must look for off-site schemes.  

Unit Calculations for Offsite creation/enhancement 

  • Establish Offsite Baseline 

The area in ha or km for rivers is worked out. There is no specific minimum or maximum size but under a certain threshold it would simply not be worth it. Local authorities are in the process of creating areas of strategic significance. If the location of a site is within such an area it receives a 15% boost to the number of units generated. If it is considered to be in a desirable location but not within an official strategic site it may receive a 10% boost subject to the Local Authority’s agreement.  

Every habitat is given a distinctiveness score between 0 and 8 based on its rarity, proportion in SSSIs and its UK Priority status. This is multiplied by the area. 

This is combined with the condition of the existing habitat (or proposed habitat) ranging from x1 (Poor) to x3 (good). Certain habitats like cereal crops are automatically classed as poor. 

This creates the starting point for the number of units available. 

As an example, 2 ha of arable would generate:  

2 (Area) x 2 (‘Low’ Distinctiveness) x 1 (Condition) x 1 (‘Low’ Strategic Significance) = 4 Units 

  • Account for Loss of existing habitat 

The impact of enhancing a site (as it will have some habitat value already) must be calculated and subtracted from the final figure. This is the area before enhancement or having new habitat created upon it.  

  • Account for Gain of created/enhanced habitat 

The created/enhanced habitat value must be calculated, as when establishing the baseline, but using the new type of habitat or new condition scores with the following multipliers: 

Spatial risk – The distance of the new site to the developer’s site will negatively impact the amount of usable units by 25% if in a neighbouring Local Authority area and 50% if further afield.  

Difficulty of creation and time – The time it takes for enhancement or creation of a habitat to reach its desired potential will impact units with up to a 70% reduction if it takes 30 years or longer. The higher the difficulty will reduce the value by up to 10%. 

Example – If the above arable site was used to create Gorse Scrub: 

2 (Area) x 4 (‘Medium’ Distinctiveness) x 3 (‘Good’ Condition) = 24 

x 1 (‘Low’ Strategic Significance) = 24 

x 0.7 (Remoteness: 10+ years to establishment) x 1 (‘Low’ Difficulty of creation)  

x 1 (Spatial Risk: Within same LPA) 

= 16.8 Units minus: 4 (Baseline Units Lost) 

Units created = 12.8 

It is worth noting the benefits of enhancing existing land rather than creating new habitat. More units may be produced via enhancement even if the habitat is a more ‘common’ one than a newly created ‘rare’ habitat. This is because the loss of existing habitat that must be factored in before a new one is created. Enhancement does not have this issue, potentially resulting in more of a net gain. 

The type of habitat, whether created or enhanced must be carefully considered as factors such as time taken to establish will drastically affect the number of units produced. The land manager must also consider how BNG complements the rest of the business. Whilst it may seem simpler to sell land to developers and let them create habitat for themselves, retaining the land allows one to sell BNG units and continue farming to an extent (depending on the type of habitat created/enhanced) thus allowing the landowner to make the most of their ‘natural capital’. 

Developers/Purchasers of credits 

  • Before development begins, you must submit a biodiversity net gain plan to be approved by a planning authority. 
  • This plan will show how the net gain target will be achieved and how the biodiversity value has been calculated. If the development has been permitted under a development order, such as permitted development rights then it does not need a biodiversity net gain plan. 
  • The Biodiversity value must be calculated using the DEFRA biodiversity metric. DEFRA have proposed an outline tariff of £9,000 to £15,000 per biodiversity unit. 
  • The ‘net gain’ will be calculated by estimating the pre-development biodiversity value (at the time of planning application submission) and deducting it from the post-development biodiversity value. 
  • The post-development value may include biodiversity only realised years in the future if it is a long-term project. To do this the enhancement must firstly be secured under a planning condition/planning obligation/conservation covenant. Secondly, be significant and lastly be maintained for at least 30 years after completion of the development. 
  • Biodiversity value may include off-site options such as purchasing ‘biodiversity credits’ or contributing to a habitat registered on the Government’s proposed ‘biodiversity gain register’. 

Contact us for help acquiring suitable land that matches your offsetting needs. 

Land Owners/Vendors 

If you have land that may be suitable for the ‘biodiversity gain register’ then contact us to discuss your options and help you with the next stage. You would need to register/work out: 

  • The location and area of the land; 
  • The works to be carried out on the land and the habitat enhancement to be achieved by them; 
  • Information about the habitat of the land before the commencement of those works; 
  • The person who applied to register the land and (if different) the person by whom the requirement to carry out the works or maintain the habitat enhancement is enforceable; 
  • Any development to which any of the habitat enhancement has been allocated; 
  • The biodiversity value calculated using the Biodiversity Metric tool.

Contact us for our welcome pack which explains how we can complete a free desktop assessment and Biodiversity Metric 3.1 calculation for you.

Biodiversity value 

DEFRA have proposed an outline tariff of £9,000 to £15,000 per biodiversity unit hoping to make it attractive to sellers by determining not to use compensatory or income foregone models of remuneration.  It has been mooted that they may fetch £20,000 or higher per unit. However it will depend on a case by case basis. An example of a high paying habit would be a hectare of arable used to create gorse scrub producing 6.4 units, subject to a variety of factors. This could potentially make up a payment of £96,000 or £1,295/acre per annum for 30 years. Putting one hectare of modified grassland into lowland meadow would yield a net 8.25 units in optimal conditions (distance, within a formally identified area etc.) This would result in £123,750 or £1,669/acre per annum for 30 years. 

What we can do for you: 

  • Biodiversity Net Gain has become a requirement now the Environmental Bill 2021 is ratified. Please register your interest with us now to take advantage of Biodiversity Net Gain schemes as they progress.  
  • We can advise on suitability of areas for Biodiversity Net Gain.  
  • Our surveying team will calculate the potential Biodiversity Units using the DEFRA Biodiversity Metric 3.1, created by the actions you will undertake on your land.  
  • For those looking to acquire Biodiversity units we can add you to our register and match you to a site that suits your requirements and location.  
  • For our user guide on Biodiversity net gain email us for our welcome pack
Alasdair Squires

Alasdair Squires

01392 823935