Tag: biomass energy

Latvia catchment area analysis

Panorama view of Latvian forest and road from above

Latvia is a heavily forested small country (about half the size of England), with 52% forest cover totalling 3.54 million ha (2.7 times bigger than the forest area in England and 11% bigger than the entire UK).

In its catchment area analysis report of the Baltic country, consultancy Indufor found:

  • Best management practice is driven by the State-owned sector with an increasing proportion of corporate owners improving management standards in the private sector
  • Markets are dominated by domestic saw-timber demand and pulpwood exports to neighbouring Scandinavia
  • Fuelwood, pellets and biomass are substantial and critical markets for low-grade fibre

Increasing forest area, carbon stored and no deforestation

There has been an increase of around 400,000 hectares (ha) of forest in Latvia since 2000. This is due to natural afforestation of abandoned agricultural lands and also to an improvement in forest inventory analysis in 2009 which provided a more accurate assessment of land use and forestry data. Since 2010, the forest area has increased by 55,000 ha. There is no evidence of deforestation.

Primary land use Latvia

Primary land use Latvia

There has also been a substantial increase in forest carbon or growing stock. This increased by 106 million cubic metres (m3) since 2000 (75% hardwood) and by 33 million m3 since 2010 (57% hardwood).

Increase in forest carbon

Increase in forest carbon

Limited hardwood markets

A proportion of the increase in hardwood volume in 2009 was due to the improvement of forest inventory calculations but also due to increased natural regeneration on unutilised land. The hardwood forest in Latvia and the Baltic region is quite different to that of the US South. In the Baltics there is prolific hardwood regeneration (birch, alder and aspen) which grows quite rapidly.

There are limited markets for structural timber, therefore hardwoods produce a lot of low-grade wood fibre. There are no domestic pulp markets in Latvia and only limited markets for panel board. Therefore, much of the low-grade wood fibre can only be used for firewood and biomass. The chart below shows a minor change in species composition from planted pine to naturally regenerated spruce and aspen – the most prolific regenerators in this region.

Varied species mix

Varied species mix

Planting and regeneration

State owned forests have a higher proportion of planted forest areas compared to the private sector where natural regeneration is preferred due to lower costs. Planting allows the owner to control the species mix, quality and growth. Whereas regeneration can be more of a lottery for both quality and species mix. As more corporate owners emerge, planting with improved stock may increase.

Restocking practice by ownership category

Restocking practice by ownership category

How the financial crisis impacted Latvian forests

Harvesting levels have been consistently below net annual increment since 2000. There have been some fluctuations in the annual allowable cut in State forests, particularly following the global financial crisis in 2008.

Harvesting in the private sector declined due to falling prices and sawnwood production dropped by 42% in 2009 compared to 2006. During that period, State-owned forest increased harvesting in order to support the industry in the absence of strong markets and private sector supply.

Post-recession, the harvesting balance returned and demand for wood products increased. The current surplus of growth compared to removals is around 5.5 million m3 p.a. or a growth drain ratio of 1.6.

Surplus of growth compared to removals

Surplus of growth compared to removals

Biomass and pulp prices

Increasing wood pellet exports have had limited impact on wood prices. The feedstock for this market (fuelwood & forest chip) has limited competition and therefore remains fairly stable.

Pulpwood markets are driven by export demand to Scandinavia and can be volatile as this market fluctuates. 2018 saw a substantial spike in pulpwood prices due to increased export demand as a response to a global increase in pulp and paper prices boosting Scandinavian production. This had a minor knock on effect on the domestic fuelwood markets.

Variation of low-grade wood prices with changing demand

Variation of low-grade wood prices with changing demand

An important part of this analysis is to look for evidence to evaluate Drax’s performance against its new forest commitments, some of which relate directly to these trends and data sets.

Pine forest in Latvia

Pine forest in Latvia

Below, the consultant summarises the evidence of biomass impacts against key metrics in the forest industry of Latvia.

Is there any evidence that wood-based bioenergy demand has caused changes in …

Forest area / forest cover

No impact. Both forest area and forest cover have increased during the last two decades. The main driver of the growing forest area has been the natural regeneration of agricultural lands that were left uncultivated during the Soviet regime.

Forest growing stock

No impact. Forest growing stock has steadily increased throughout the observation period.

The main driver for harvesting level is the roundwood demand from sawmills, panel mills and export. Wood-based bioenergy demand may increase thinnings and residue collection, but it is not as significant a driver for total harvests as the aforementioned. Exported pellets have accounted for approximately 10-14% of the total volume of annual harvests in recent years, depending on the assumed average dry densities of the harvested wood and pellets.

Harvesting levels

No impact / slight increasing impact. The national felling volume is only about 65% of the national forest increment. The total harvesting area has been declining, while the total harvested volume has increased in the past 20 years. This can be explained by the diminished share of thinnings and increased share of clear-cuts. A decline in both area and volume of fellings can be seen between 2002–2008 and 2010–2016.

The main drivers of harvesting levels are sawmill industry, panel industry and export demand. However, wood demand for energy purposes can still improve the overall income for the forest owner and therefore increase the total harvesting levels in private forests

Harvesting residue collection

Increasing impact. Most of the collected residues originate from clear-cuts in state forests. Most produced harvesting residues are left in situ, and they are not over-exploited.

Collection of wood residues from harvesting operations has been increasing for the last 15 years as a result of increased capacities and demand from heat and CHP plants. Latvia is increasingly relying on woody biomass for energy generation.

Forest growth / carbon sequestration potential

No apparent impact. The total forest area and growing stock have grown in the last decade.

According to Latvia’s National Forestry Accounting Plan 2021–2025, the forests are decreasing their GHG sequestration capacity. Even a low sequestration rate increases carbon storage, which explains the increases in forest growing stock and area. The decrease in GHG sequestration capacity is due to forest ageing, emissions from soils and the increased share of broadleaved forests, which have lower carbon accumulation capacity than conifers.

Removal of harvesting residues decreases carbon sequestration since the residues are an input to the soil carbon pool. However, the majority of the harvesting residues’ carbon is released to the atmosphere when the biomass decays, so the ultimate impact of harvesting residue collection is minimal if the collection is done on a sustainable level. The sustainability of the collection is determined by how the soil nutrient balance is impacted by collection. This is not accounting for the substitution effect that the harvesting residues may have, by, e.g. reducing the need to burn fossil fuels.

Aerial sight of warm, colorful autumn morning sunrise at forest covered picturesque river valley. Clear blue sky and high contrast shadows with magnificent reflections, breathtaking

Is there any evidence that wood-based bioenergy demand has caused changes to forest management practices …

Rotation lengths

No impact. The Law on Forests regulates minimum forest age and diameter for clear-cuts. The LVM and large-scale forest owners often conduct clear-cuts at minimum diameter, whereas smallholders tend to wait until roundwood prices are high. Due to the regulation, an increase of wood-based bioenergy demand has not shortened rotations.

Thinnings

Increasing impact in naturally afforested former agricultural lands. No impacts on thinnings overall. The total harvested area has been declining, while the total harvested volume has increased in the past 20 years. This can be explained by the diminished share of thinnings, due to existing forest age structure, and increased share of clear-cuts. Most of the harvesting residues are collected from clear-cuts.

There is an increased demand for small diameter wood and harvesting/processing residues overall.

The increased demand for small-diameter hardwood has increased harvesting in previously unmanaged afforested agricultural lands, which usually overgrow with broadleaved trees. These kinds of lands are usually otherwise not significant for forest management.

Conversion from hardwood to softwood

No impact. No indication of hardwood conversion to softwood was found. Instead, pine forests are decreasing due to the favouring of natural regeneration, which usually results in spruce or broadleaved forests in nutrient-rich and/or wet soils.

Is there any evidence that wood-based bioenergy demand has impacted solid wood products markets …

Diversion from other wood product markets

No apparent impact. Production of sawnwood and wood-based panels have increased or remained steady, i.e. no evidence of diversion.

Several interviews confirmed that sawlogs are not processed for other products besides sawnwood and wood-based panels.

Wood prices

No apparent impact. Prices of all wood assortments increased in 2017–2018, most notably the prices of pulpwood. This was due to difficult harvesting conditions and increased demand for pulpwood in Finland and Sweden, because of high market pulp prices. Pulpwood prices returned to pre-surge levels in 2019. Fuelwood prices also increased temporarily, but at a much more moderate rate. The main driver for fuelwood price increases was the surge of pulpwood prices.

Read the full report Catchment Area Analysis in Latvia. A 2017 interview with Raul Kirjanen, CEO of Graanul Invest, a wood pellet supplier of Drax operating in Latvia, can be read here. Read how Drax and Graanul work with NGOs when concerns are raised within our supply chain here.

This is part of a series of catchment area analyses around the forest biomass pellet plants supplying Drax Power Station with renewable fuel. Others in the series include: Georgia Mill, ChesapeakeEstoniaMorehouse Bioenergy and Amite Bioenergy.

Changing forest structure in Virginia and North Carolina

Photos: Roanoke Rapids area near the North Carolina, Virginia border, courtesy of Enviva.

Forest owners have responded to the recovery in pine saw-timber markets, since the global financial crisis of 2008, by planting more forest and investing more in the management of their land. The same period has witnessed increased demand from the biomass sector which has replaced declining need for wood from pulp and paper markets.

The area of timberland (actively managed productive forest) has increase by around 89,000 hectares (ha) since 2010. This change is due to three important factors: new planting on agricultural land; the planting of low-grade self-seeded areas with more productive improved pine; and the re-classification by the US Forest Service (USFS) of some areas of naturally regenerated pine from woodland to timberland.

The 2018 data shows that pine forest makes up 46% of the timberland area, of which 61% is planted and the remainder naturally regenerated. Hardwoods cover 43% of the timberland area, with 93% of this naturally regenerated. The remaining area is mixed stands.

Composition of timberland area

Since 2000 there have been some significant changes in the composition of the timberland area with a transition from hardwood to softwood. Pine has increased from 39% of the total area in 2000 to 46% in 2018 and hardwood has decreased from 50% to 43% over the same period.

All pine areas have increased since 2000 with naturally regenerated pine increasing by 13,000 ha and planted pine by 340,000 ha since 2000. Mixed stands have declined by 6,500 ha as some of these sites have been replanted with improved pine to increase growth and saw-timber production.

The biggest change has been in the hardwood areas where there has been a decline of around 314,000 ha, despite the total area of timberland increasing by 31,000 ha.

Change in forest type

This change has been driven by private forest owners (representing 91% of the total timberland area), seeking to gain a better return on investment from their forest land.

Hardwood markets have declined since the 2008 recession and demand for hardwood saw-timber has not recovered. Demand for pine saw-timber has rebounded and is now as strong as pre-crisis.

Pine also offers much faster growth rates and higher total volumes in a much shorter time frame (typically 25-35 years compared to 75-80 years for hardwoods).

The decision to change species is similar to a farmer changing their agricultural crops based on market demand and prices for each product. Where forests are managed for revenue generation then it is reasonable to optimise the land and crop for this objective. This can be a significant positive, from a carbon perspective more carbon is sequestered in a shorter time frame and more carbon is stored in long term wood products, if the quantity if saw-timber is increased.

Increased revenue generation also helps to maintain the forest area (rather than conversion to urban development, agriculture or other uses).

A potential negative is the change in habitat from a pure hardwood stand to a pure pine stand, each providing a different ecosystem and supporting a different range of flora and fauna. There is no conclusive evidence that one forest type is better or worse than the other; there is a great deal of variety of each type.

Some hardwood forests are rich in species and biodiversity, others can be unremarkable. The key is not to endanger or risk losing any species or sensitive habitat and to ensure that any conversion only occurs where there is no loss of biodiversity and no negative impact to the ecosystem.

It is not clear whether all of the lost hardwood stands have been directly converted to pine forests, some hardwood stands may have been lost to other land uses (urban and other land has increased by 400,000 ha). Some may have been directly converted to pine by forest owners encouraged by the increase in pine saw-timber demand and prices.

Whatever the primary driver of this change it is clearly not being driven by the biomass sector.

Change in forest type – timing

The chart above demonstrates that the biggest change, loss of hardwood and increase in planted pine, occurred between 2000 and 2012, prior to the operation of the pellet mills. Since 2012, there has been no significant loss of natural hardwood and only a small decline in planted hardwood.

Read the full report: Catchment Area Analysis of Forest Management and Market Trends: Enviva Pellets Ahoskie, Enviva Pellets Northampton, Enviva Pellets Southampton (UK metric version). Explore Enviva’s supply chain via Track & Trace. This is part of a series of catchment area analyses around the forest biomass pellet plants supplying Drax Power Station with renewable fuel. The series includes: Estonia, Morehouse Bioenergy, Amite Bioenergy, and the Drax forestry team’s review of the Chesapeake report on Enviva’s area of operations.

The UK needs negative emissions from BECCS to reach net zero – here’s why

Early morning sunrise at Drax Power Station

Reaching the UK’s target of net zero greenhouse gas emissions by 2050 means every aspect of the economy, from shops to super computers, must reduce its carbon footprint – all the way down their supply chains – as close to zero as possible.

But as the country transforms, one thing is certain: demand for electricity will remain. In fact, with increased electrification of heating and transport, there will be a greater demand for power from renewable, carbon dioxide (CO2)-free sources. Bioenergy is one way of providing this power without reliance on the weather and can offer essential grid-stability services, as provided by Drax Power Station in North Yorkshire.

Close up of electricity pylon tower

Close up of electricity pylon tower

Beyond just power generation, more and more reports highlight the important role the next evolution of bioenergy has to play in a net zero UK. And that is bioenergy with carbon capture and storage or BECCS.

A carbon negative source of power, abating emissions from other industries

The Committee on Climate Change (CCC) says negative emissions are essential for the UK to offset difficult-to-decarbonise sectors of the economy and meet its net zero target. This may include direct air capture (DAC) and other negative emissions technologies, as well as BECCS.

BECCS power generation uses biomass grown in sustainably managed forests as fuel to generate electricity. As these forests absorb CO2 from the atmosphere while growing, they offset the amount of COreleased by the fuel when used, making the whole power production process carbon neutral. Adding carbon capture and storage to this process results in removing more CO2 from the atmosphere than is emitted, making it carbon negative.

Pine trees grown for planting in the forests of the US South where more carbon is stored and more wood inventory is grown each year than fibre is extracted for wood products such as biomass pellets

Pine trees grown for planting in the forests of the US South where more carbon is stored and more wood inventory is grown each year than fibre is extracted for wood products such as biomass pellets

This means BECCS can be used to abate, or offset, emissions from other parts of the economy that might remain even as it decarbonises. A report by The Energy Systems Catapult, modelling different approaches for the UK to reach net zero by or before 2050, suggests carbon-intensive industries such as aviation and agriculture will always produce residual emissions.

The need to counteract the remaining emissions of industries such as these make negative emissions an essential part of reaching net zero. While the report suggests that direct air carbon capture and storage (DACCS) will also play an important role in bringing CO2 levels down, it will take time for the technology to be developed and deployed at the scale needed.

Meanwhile, carbon capture use and storage (CCUS) technology is already deployed at scale in Norway, the US, Australia and Canada. These processes for capturing and storing carbon are applicable to biomass power generation, such as at Drax Power Station, which means BECCS is ready to deploy at scale from a technology perspective today.

As well as counteracting remaining emissions, however, BECCS can also help to decarbonise other industries by enabling the growth of a different low carbon fuel: hydrogen.

Enabling a hydrogen economy

The CCC’s ‘Hydrogen in a low-carbon economy report’ highlights the needs for carbon zero alternatives to fossil fuels – in particular, hydrogen or H2.

Hydrogen produced in a test tube

Hydrogen produced in a test tube

When combusted, hydrogen only produces heat and water vapour, while the ability to store it for long periods makes it a cleaner replacement to the natural gas used in heating today. Hydrogen can also be stored as a liquid, which, coupled with its high energy density makes it a carbon zero alternative to petrol and diesel in heavy transport.

There are various ways BECCS can assist the creation of a hydrogen economy. Most promising is the use of biomass to produce hydrogen through a method known as gasification. In this process solid organic material is heated to more than 700°C but prevented from combusting. This causes the material to break down into gases: hydrogen and carbon monoxide (CO). The CO then reacts with water to form CO2 and more H2.

While CO2 is also produced as part of the process, biomass material absorbs CO2 while it grows, making the overall process carbon neutral. However, by deploying carbon capture here, the hydrogen production can also be made carbon negative.

BECCS can more indirectly become an enabler of hydrogen production. The Zero Carbon Humber partnership envisages Drax Power Station as the anchor project for CCUS infrastructure in the region, allowing for the production of ‘blue’ hydrogen. Blue hydrogen is produced using natural gas, a fossil fuel. However, the resulting carbon emissions could be captured. The CO2 would then be transported and stored using the same system of pipelines and a natural aquifer under the North Sea as used by BECCS facilities at Drax.

This way of clustering BECCS power and hydrogen production would also allow other industries such as manufactures, steel mills and refineries, to decarbonise.

Lowering the cost of flexible electricity

One of the challenges in transforming the energy system and wider economy to net zero is accounting for the cost of the transition.

The Energy Systems Catapult’s analysis found that it could be kept as low as 1-2% of GDP, while a report by the National Infrastructure Commission (NIC) projects that deploying BECCS would have little impact on the total cost of the power system if deployed for its negative emissions potential.

The NIC’s modelling found, when taking into consideration the costs and generation capacity of different sources, BECCS would likely be run as a baseload source of power in a net zero future. This would maximise its negative emissions potential.

This means BECCS units would run frequently and for long periods, uninterrupted by changes in the weather, rather than jumping into action to account for peaks in demand. This, coupled with its ability to abate emissions, means BECCS – alongside intermittent renewables such as wind and solar – could provide the UK with zero carbon electricity at a significantly lower cost than that of constructing a new fleet of nuclear power stations.

The report also goes on to say that a fleet of hydrogen-fuelled power stations could also be used to generate flexible back-up electricity, which therefore could be substantially cheaper than relying on a fleet of new baseload nuclear plants.

However, for this to work effectively, decisions need to be made sooner rather than later as to what approach the UK takes to shape the energy system before 2050.

The time to act is now

What is consistent across many different reports is that BECCS will be essential for any version of the future where the UK reaches net zero by 2050. But, it will not happen organically.

Sunset and evening clouds over the River Humber near Sunk Island, East Riding of Yorkshire

Sunset and evening clouds over the River Humber near Sunk Island, East Riding of Yorkshire

A joint Royal Society and Royal Academy of Engineering Greenhouse Gas Removal report, includes research into BECCS, DACCS and other forms of negative emissions in its list of key actions for the UK to reach net zero. It also calls for the UK to capitalise on its access to natural aquifers and former oil and gas wells for CO2 storage in locations such as the North Sea, as well as its engineering expertise, to establish the infrastructure needed for CO2 transport and storage.

However, this will require policies and funding structures that make it economical. A report by Vivid Economics for the Department for Business, Energy and Industrial Strategy (BEIS) highlights that – just as incentives have made wind and solar viable and integral parts of the UK’s energy mix – BECCS and other technologies, need the same clear, long-term strategy to enable companies to make secure investments and innovate.

However, for policies to make the impact needed to ramp BECCS up to the levels necessary to bring the UK to net zero, action is needed now. The report outlines policies that could be implemented immediately, such as contracts for difference, or negative emissions obligations for residual emitters. For BECCS deployment to expand significantly in the 2030s, a suitable policy framework will need to be put in place in the 2020s.

Beyond just decarbonising the UK, a report by the Intergovernmental Panel on Climate Change (IPCC) highlights that BECCS could be of even more importance globally. Differing scales of BECCS deployment are illustrated in its scenarios where global warming is kept to within 1.5oC levels of pre-industrial levels, as per the Paris Climate agreement.

BECCS has the potential to play a vital role in power generation, creating a hydrogen economy and offsetting other emissions. As it continues to progress, it is becoming increasingly effective and cost efficient, offering a key component of a net zero UK.

Learn more about carbon capture, usage and storage in our series:

Responsibility, wellbeing and trust during the COVID-19 outbreak

Engineers in PPE working at Drax Power Station

We are living through unprecedented times. Coronavirus is having far reaching effects on all industries not just here in the UK, but around the world. At Drax, we take our responsibilities as a member of critical national infrastructure and as an essential service provider very seriously. We are committed to maintaining a continuous, stable and reliable electricity supply for millions of homes and businesses in the UK.

The wellbeing of our people

Firstly, I’d like to thank our employees, contractors, supply chain workers and their families as well as the communities in the UK and US in which we operate, for their fantastic support and continued hard work during these difficult and uncertain times. Our employees’ health and wellbeing are vital, and we’re working hard to ensure we are supporting them with both their physical and mental health, whether working at home or at one of our sites.

Engineer maintaining equipment in Drax Power Station

Engineer maintaining equipment in Drax Power Station [Click to view/download]

Across all our sites we are have implemented strategies to reduce the chances of people spreading the virus and have operational plans in place to ensure continued delivery of power into the grid.

Power station resilience

At Drax Power Station, the UK’s largest power station, largest decarbonisation project in Europe and biggest source of renewable power into the national grid, we have arranged for the separation of key operational teams and employees so that they are physically distanced from each other. We have moved as many employees as possible to work from home, so that there are fewer people in our workplaces reducing the risk of the spread of infection, should it arise. We have strict controls on visitors to the site and on our contractors and suppliers. Our resilience teams are working well and we have contingency plans in place to manage risks associated with colleague absences.

We have closed the visitor centres at Cruachan pumped storage hydro power station and Tongland hydro power station in Scotland, as well as at Drax Power Station in North Yorkshire. We have also stopped all but critically important travel between our sites.

Our supply chain

Sustainable biomass wood pellets destined for Drax Power Station unloaded from the Zheng Zhi bulk carrier at ABP Immingham [Click to view/download]

It is vital we maintain a resilient supply chain for the sustainably sourced biomass wood pellets required to produce electricity at Drax Power Station, the country’s largest power station. We’re working closely with our suppliers in the US and Europe to maintain biomass supplies as well as with rail and port infrastructure in the US and UK to ensure continuity of supply.

Just last week Associated British Ports (ABP) and Drax received and unloaded the largest ever shipment of sustainable biomass to arrive at the Port of Immingham in the UK’s Humber region. The vessel transported 63,907 tonnes of Drax’s wood pellets from the US Port of Greater Baton Rouge in Louisiana. The consignment supplies Drax Power Station with enough renewable fuel to generate electricity for 1.3 million homes.

Our three wood pellet manufacturing plants are running well, with US authorities classifying our employees as key workers. The same is the case for our rail freight partners on both sides of the Atlantic. In the UK, GB Railfreight recognises the strategic importance of biomass deliveries to Drax Power Station.

Our customers

Businesses – both large and small – are feeling the economic effects of this virus. Our employees involved with the supply of electricity, gas and energy services to organisations are working hard to support them. More information can be found via these links:

We are working closely with BEIS, HM Treasury and our trade associations to explore how government and industry can further support business through this challenging time. Organisations facing financial difficultly can access the unprecedented level of support already announced by the Chancellor, Rishi Sunak via:

Drax employee in high visibility clothing on the telephone

Drax employee in high visibility clothing on the telephone [Click to view/download]

Leadership

Our Executive Committee is meeting regularly via video conference to discuss our contingency planning as the situation changes. We are working closely with the UK, US state and Canadian governments, National Grid and Ofgem to ensure that we remain up to date with the latest advice and that we are prepared for any further escalation.

This is an unprecedented time for the UK and the world. Rest assured that Drax’s critical national infrastructure and essential service operations, as well as its employees, are working hard 24/7 to make sure individuals, families, businesses and organisations are supplied with the vital electricity needed to keep the country running.

Estonia catchment area analysis

View from Suur Munamagi over forest landscape in South Estonia.

Estonia is a heavily forested country with a mature forest resource that has been neglected over many years due to political and ownership changes. Management of state and corporate owned forests is now good, but some small privately-owned areas of forest are still poorly managed.

Despite this, both the forest area and the growing stock have been increasing, largely due to new planting and the maturing age class of existing forest.

Forest area has increased from 49% to 52% of the total land, increasing by more than 118 thousand hectares since 2010.

Land use in Estonia

Land use in Estonia [click to view/download]

Over the same period the growing stock increased by 52 million m3, with 60% of this growth in softwood and 40% in hardwood species. The data shows a slight decline in 2018 but this is due to a sampling error and the growing stock is thought to have been maintained at 2017 levels (this should be rectified in the 2019 data when available).

Change in forest growing stock – Estonia

Change in forest growing stock – Estonia [click to view/download]

The forests of Estonia have been going through a period of restitution since the 1990s. Land that had been taken into state ownership during Soviet rule has been given back to private owners. This process was complex and lengthy and limited active management in the forest during this time.

Since 2008, harvesting and management has increased. Private and corporate forest owners have been harvesting forest that had been mature and ready for clear felling. The longer-term harvesting trend has been considerably lower than annual growth (increment) and the maximum sustainable harvesting level, as shown on the chart below.

Annual increment and harvesting levels

Annual increment and harvesting levels [click to view/download]

In 2018 harvesting reached an all time high at just over 14 million m3 and just under the maximum threshold. It is expected to remain at this level as more forest matures and enters the cycle of harvest and regeneration.

Clear cutting (regeneration felling) is the largest operation by volume but thinning (maintenance felling) is the largest by area.

This indicates a forest landscape in balance, with widespread thinning to produce more sawlog trees and a large volume of clear cuts in the mature stands to make way for the next generation of forests.

Reforestation in Estonia. * Note: Since 2014 it has not been compulsory for private and other forest owners to submit reforestation data. [Click to view/download]

Reforestation in Estonia. * Note: Since 2014 it has not been compulsory for private and other forest owners to submit reforestation data. [Click to view/download]

Planting of seedlings is the most common form of regeneration. However, some native hardwood species are strong pioneers and naturally regenerate among the spruce and pine stands. This has led to a change in the species composition of some forests with an increase in hardwoods, although this is relatively small scale and only prevalent among some small private owners that do not invest in clearing unwanted regeneration.

Species mix in Estonian forests [Click to view/download]

Species mix in Estonian forests [Click to view/download]

Markets and prices for forest products

Sunrise and fog over forest landscape in Estonia

Sunrise and fog over forest landscape in Estonia

Pulpwood markets are limited in Estonia and this material has been historically exported to neighbouring Finland and Sweden. Export demand has had a significant impact on prices as can be seen in a spike in 2018 when demand was at its strongest.

The forest industry has been dominated by sawmills and panel board mills. Demand and production in this sector has been increasing and this has kept prices high. There is a substantial differential between sawlog and pulpwood pricing.

Comparison of sawlog and pulpwood prices [click to view/download]

Comparison of sawlog and pulpwood prices [click to view/download]

The pellet industry developed due to the abundance of low-grade fibre available domestically. This included sawmill and forest residues, as well as low grade roundwood from thinnings and clear cuts. Drax’s suppliers use a combination of these feedstock sources as shown below.

Drax feedstocks from Estonia 2018 [click to view download]

Sunrise through forest in Estonia

Sunrise through forest in Estonia

Summary of key questions addressed in the analysis:

Impacts of wood-based bioenergy demand to forest resources:

Forest area / forest cover

No negative impact. Regardless of increasing domestic biomass utilisation for energy and exports, forest area has increased due to afforestation programmes. Forest cover is not as high as forest area, due to temporarily un-stocked area after clear-cut. Despite this, forest cover has continuously increased from 2010–2018.

Growing stock

No negative impact. The total forest growing stock has been increasing for the last two decades. In 2018 the growth slowed or halted (official statistics show a decrease, but this is due to sampling error). In 2018 there was record-high wood demand from Finland, which was driven by high global pulp prices motivating maximal pulp production. This increased harvests to a previously unseen level.

Harvesting levels

Slight increasing impact. During 2004–2011, harvesting levels in Estonia were less than half of the estimated maximum sustainable level. This resulted in an increase in the maximum sustainable harvesting level for the 2011–2020 period. In 2018, the harvesting volumes were at the maximum sustainable level. The main drivers increasing the harvesting volumes have been increased sawmill capacity and production, high demand for pulpwood in Finland and Sweden and improved demand for energy wood. This was a temporary peak and demand has already slowed. Softwood lumber prices have decreased significantly in Europe due to an abundance of wood supply from Central Europe, which has been created by widespread bark beetle and other forest damages. Global pulp prices have also decreased to below 2017 prices.

Forest growth / carbon sequestration potential

Ambivalent impact. The annual increment has grown throughout the 2000–2018 period. Increased fuelwood price has enabled forest management in some of the alder forests that were completely unutilised in the past. Thinnings, both commercial and pre-commercial, accelerate long-term volume growth in forests, leading to increased carbon sequestration. Removal of harvesting residues decreases carbon sequestration since the residues are input to the soil carbon pool. However, the majority of the harvesting residues’ carbon is released to the atmosphere when the biomass decays, so the ultimate impact of harvesting residue collection is minimal if the collection is done on a sustainable level. The sustainability of the collection is determined by how the soil nutrient balance is impacted by collection. This is not accounting for the substitution effect that the harvesting residues may have, by e.g. reducing the need to burn fossil fuels. Utilisation of sawmill by-products does not directly impact forests’ carbon sequestration potential, but it can increase harvesting through improved sawmill overall profitability.

Impacts of wood-based bioenergy demand to forest management practices:

Rotation lengths

Neutral. Forest law regulates minimum forest age for clear-cuts. According to interviews, Riigimetsa Majandamise Keskus (RMK – the Estonian state forest company), often conducts the final felling at the minimum age. Due to the regulation, an increase of wood-based bioenergy demand has not shortened rotations at least in state-managed forests. In forests that are older than the minimum final felling age, sawlog price is a more important driver for final-felling decisions than wood-based bioenergy demand.

Thinning

Increasing impact. The increase of bioenergy demand has increased the demand for small-diameter hardwood, which in turn has increased thinnings in previously unmanaged forest stands. This will increase the availability of good quality sawlogs and will also accelerate the carbon sequestration (tonnes/ha/year) of the forests. However, the total forest carbon stock (tonnes/ha) will be reduced; in unmanaged (e.g. no thinnings) mature stands, the carbon stock is larger than in managed stands of similar age. The carbon stock of a thinned stand will remain below that of an unthinned stand regardless of post-thinning accelerated growth.

Conversion from hardwood to softwood

Neutral. No indication of hardwood conversion to softwood was found.

Impacts of wood-based bioenergy demand to solid wood product (SWP) markets:

Diversion from other wood product markets

Neutral. Production of sawnwood, wood-based panels, pulp and paper products have increased or remained steady, i.e. no evidence of diversion.

Wood prices

Slight increasing impact. During 2017–2018, the price of all roundwood assortments increased notably. The increase was strongest in pulpwood assortments, especially those that are not further processed domestically but are exported to mainly Finland and Sweden. Finnish demand for pulpwood was at a very high level in 2018. This was a temporary trend, however, and prices and demand have since decreased. The price increase for fuelwood was less dramatic, no sharp increases are observed. According to interviews, pellet production was the most important driver of fuelwood prices.

Read the full report: Catchment Area Analysis in Estonia. A 2017 interview with Raul Kirjanen, CEO of Graanul Invest, a wood pellet supplier of Drax operating in Estonia, can be read here. Read how Drax and Graanul work with NGOs when concerns are raised within our supply chain here.

Read more about how bioenergy has no negative impact on Estonia’s forest resources here.

This is part of a series of catchment area analyses around the forest biomass pellet plants supplying Drax Power Station with renewable fuel. Others in the series include: Georgia Mill, Latvia, Chesapeake and Drax’s own, other three mills LaSalle BionergyMorehouse Bioenergy and Amite Bioenergy.

End of coal generation at Drax Power Station

Coal picker, Drax Power Station, 2016

Drax Group plc
(“Drax” or the “Group”; Symbol:DRX)
RNS Number : 2747E

Following a comprehensive review of operations and discussions with National Grid, Ofgem and the UK Government, the Board of Drax has determined to end commercial coal generation at Drax Power Station in 2021 – ahead of the UK’s 2025 deadline.

Commercial coal generation is expected to end in March 2021, with formal closure of the coal units in September 2022 at the end of existing Capacity Market obligations.

Will Gardiner, Drax Group CEO, said:

“Ending the use of coal at Drax is a landmark in our continued efforts to transform the business and become a world-leading carbon negative company by 2030. Drax’s move away from coal began some years ago and I’m proud to say we’re going to finish the job well ahead of the Government’s 2025 deadline.

“By using sustainable biomass we have not only continued generating the secure power millions of homes and businesses rely on, we have also played a significant role in enabling the UK’s power system to decarbonise faster than any other in the world.

“Having pioneered ground-breaking biomass technology, we’re now planning to go further by using bioenergy with carbon capture and storage (BECCS) to achieve our ambition of being carbon negative by 2030, making an even greater contribution to global efforts to tackle the climate crisis.

“Stopping using coal is the right decision for our business, our communities and the environment, but it will have an impact on some of our employees, which will be difficult for them and their families.

“In making the decision to stop using coal and to decarbonise the economy, it’s vital that the impact on people across the North is recognised and steps are taken to ensure that people have the skills needed for the new jobs of the future.”

Coal in front of biomass storage domes at Drax Power Station, 2016

Coal in front of biomass storage domes at Drax Power Station, 2016

Drax will shortly commence a consultation process with employees and trade unions with a view to ending coal operations. Under these proposals, commercial generation from coal will end in March 2021 but the two coal units will remain available to meet Capacity Market obligations until September 2022.

The closure of the two coal units is expected to involve one-off closure costs in the region of £25-35 million in the period to closure and to result in a reduction in operating costs at Drax Power Station of £25-35 million per year once complete. Drax also expects a reduction in jobs of between 200 and 230 from April 2021.

The carrying value of the fixed assets affected by closure was £240 million, in addition to £103 million of inventory at 31 December 2019, which Drax intends to use in the period up to 31 March 2021. The Group expects to treat all closure costs and any asset obsolescence charges as exceptional items in the Group’s financial statements. A further update on these items will be provided in the Group’s interim financial statements for the first half of 2020.

As part of the proposed coal closure programme the Group is implementing a broader review of operations at Drax Power Station. This review aims to support a safe, efficient and lower cost operating model which, alongside a reduction in biomass cost, positions Drax for long-term biomass generation following the end of the current renewable support mechanisms in March 2027.

While previously being an integral part of the Drax Power Station site and offering flexibility to the Group’s trading and operational performance, the long-term economics of coal generation remain challenging and in 2019 represented only three percent of the Group’s electricity production. In January 2020, Drax did not take a Capacity Market agreement for the period beyond September 2022 given the low clearing price.

Enquiries

Drax Investor Relations:
Mark Strafford
+44 (0) 7730 763 949

Media

Drax External Communications:
Ali Lewis
+44 (0) 7712 670 888

 

Website: www.drax.com/uk

END

How biomass wood pellet mills can help landowners grow healthy forests

Working Forests US South

International Paper’s pulp and paper mill, located in the Morehouse parish of Louisiana, had been in operation since 1927 and was once the largest employer in the area. However, as a result of the global recession of 2008, the company was forced to lay off over 550 employees and shut the facility. Other mills in the area have also reduced production including Georgia Pacific which let go around 530 people at its Crossett, Arkansas plant 18 miles to the north of Morehouse in 2019.

For an area dominated by forests, such as Northern Louisiana and Southern Arkansas, this decline in traditional markets came as a serious blow. It’s a region where a healthy market for wood products is vital for the local economy and, in turn, the health of the region’s forests. Luckily other wood product manufacturers and industries have since began to fill the gap.

Engineers in front of wood pellet storage silos at Drax's Morehouse BioEnergy biomass manufacturing facility in northern Louisiana

Engineers in front of wood pellet storage silos at Drax’s Morehouse BioEnergy biomass manufacturing facility in northern Louisiana

Drax Biomass has opened a mill in Morehouse parish that uses some of the the low-grade wood previously used to supply the paper industry to produce compressed wood pellets, which are used to generate renewable electricity in the UK.

Commissioned in 2015, the plant employs 74 people and can produce as much as 525,000 metric tonnes of biomass pellets a year. This makes it an important facility for local employment and the wood market in the region. However, to ensure it is positively contributing to the area and its environment, the demand for wood must be sustainably managed.

Morehouse BioEnergy sources low-grade wood from a catchment area that covers a 60-mile radius and includes 18 counties in Arkansas and four in Louisiana.

As Drax Biomass doesn’t own any of the forests it sources wood products from, it regularly examines the environmental impact of its pellet mills on the forests and markets in which it operates. The aim is to ensure the biomass used by Drax to generate 12% of Great Britain’s renewable electricity is sustainably sourced and does not contribute to deforestation or other negative climate and environment impacts.

A new report by forestry research and consulting firm Forisk evaluates the impact of biomass pellet demand from Morehouse BioEnergy on the forests and wood markets within the mill’s catchment area.

Map of pulpwood-using mills near Morehouse timber market

Map of pulpwood-using mills near Morehouse timber market

It found that biomass demand in the region does not contribute to deforestation, nor increase forest harvesting above a sustainable level. Overall, growth of the region’s pine timberland, which supplies Morehouse BioEnergy, continues to exceed removals, pointing to expanding forest carbon and wood inventory.

Annual growth compared to harvesting removals

Annual growth compared to harvesting removals

Growing forests and increasing timber stocks

The study focuses on timberland – working forests – in the plant’s sourcing area, which the US Forestry Service categorises as productive land capable of providing timber on an industrial scale.

The timberland here is made up of 63% softwood trees, which includes pines, and 37% hardwoods such as oak. Pellet manufacturing as a whole (including other pellet producers in the area), accounts for only 6% of the demand for wood products in the region. Of that, Morehouse BioEnergy contributes to 4% of total pellet demand.

Total area of timberland

Total area of timberland

Lumber – such as sawtimber – makes up the bulk of demand for wood products, accounting for 46% of total demand, largely as a result of its high market value and landowners’ aims to extract maximum revenue from their pine stands.

However, the less valuable wood – parts of trees that are misshapen, too short or thin to be used for lumber – can be sold at a lower price to biomass pellet mills. This wood might previously have been sold to paper and pulp mills exclusively, but with International Paper’s departure, Morehouse BioEnergy now fills a part of that role.

Total volume of growing stock on timberland

Total volume of growing stock on timberland

Maintaining healthy markets for both high and low-value wood is key to enabling landowners to reforest areas once they have been harvested in the knowledge it will provide a valuable return in the future. Ultimately, however, the way forests are maintained depends on the individual landowners and how they want to use their land.

The advantages of corporate ownership

Morehouse BioEnergy’s catchment area covers 28,000 square kilometres of timberland, within which 96% of the timber is privately owned. While some of that is owned by families with small patches of productive land, 54% is held by corporate owners. This includes businesses such as real estate investment trusts (REITs) and timber investment management organisations (TIMOs), which advise institutional investors on how to manage their forest assets.

This high percentage of corporate ownership influences forest management and replanting, as owners look to maximise the value of forests and seek to continue to generate returns from their land.

“In general, corporate owners are spending more money on silviculture and actively managing their timber stands,” explains Forisk Consulting Partner Amanda Lang. “They are investing more in fertiliser, their seedlings and harvest control on pine stands, because that leads to larger trees of a higher quality and more profit in the long run.” This is reflected in the higher growth rates found in the private sector, leading to faster rates of carbon sequestration.

Annual growth per hectare by owner type

Annual growth per hectare by owner type

Smaller private landowners, meanwhile, may have other objectives for their land like recreation and hunting, in addition to timber income. As a result, some owners may be less inclined to intensively manage their timber stands, forgoing fertilisation and competition control (due to cost) and might harvest on a less regular basis. Although these landowners may not be maximising the productivity of their timber resource to the same degree corporate owners do, their unique management often contribute to greater diversity on the landscape.

Demand and forest health

In 2018 the annual average price for a metric tonne of pine sawtimber in Morehouse BioEnergy’s catchment area was $25.71, down from a 10-year high of $31.60 in 2010. Similarly, pine pulpwood, from which biomass pellets are made, was valued at $7.75 per metric tonne in 2018, down from a 10-year high of $13 in 2010.

These low wood prices have caused many landowners to delay harvesting forests in hopes for a more lucrative wood price. As a result, pine timber inventories have grown across Morehouse BioEnergy’s catchment area. In 2010 the US Forest Service counted more than 167 million metric tonnes of pine inventory. By 2018 this had increased by more than 35% to reach 226 million.

Morehouse BioEnergy market historic stumpage prices, $/metric tonne

Morehouse BioEnergy market historic stumpage prices, $/metric tonne

The report suggests this price slump is an ongoing result of the 2008 recession, which greatly affected US house construction – one of the primary uses of sawtimber and many other types of wood products in the US. Some areas have already seen sawtimber prices increase as they recover from the recession, however, the report suggests this is not spread evenly on a national level.

The inventory overhang in Morehouse BioEnergy’s catchment area is expected to begin reversing in 2024 or 2025, as Lang explains: “We expect inventories to increase for a few more years and then start to decline. That said, inventories will remain higher than pre-recession levels.”

While high inventories suggest an abundant resource, lower inventory volumes are not indicative of declining or unhealthy forests. Rather, they can point to younger, growing forests that have recently been replanted, which will later grow to higher inventory volumes as they mature. Both suggest a healthy forestry industry in which landowners continue to reinvest in forests.

Overall, the analysis of the region points to healthy, growing forests and, importantly, a sustainable industry from which Drax can responsibly source biomass pellets. Ensuring the biomass used at Drax Power Station is sustainably sourced is crucial to its generation of renewable, carbon-neutral electricity, and in turn laying the path to negative emissions.

Read the full report: Morehouse, Louisiana Catchment Area Analysis. A short summary of its analysis and conclusions, written by our forestry team, can be read here. Explore every delivery of wood to Morehouse BioEnergy using our ForestScope data transparency tool.

Morehouse catchment area analysis

Working forest in southern Arkansas within the Morehouse catchment area

The forest area around the Drax Morehouse BioEnergy plant has a long history of active management for timber production. 96% of the forest owners are private and around half of these are corporate investors seeking a financial return from forest management. The pulp and paper (p&p) sector dominates the market for low grade roundwood with over 75% of the total demand. The wood pellet markets use only 6% of the roundwood, of which 4% is used by Morehouse.

Given the small scale of demand in the pellet sector, the extent of influence is limited. However, the new pellet markets have had a positive impact, replacing some of the declining demand in the p&p sector and providing a market for thinnings for some forest owners and a new off-take for sawmill residues.

Pine forest is dominant in this area with an increasing inventory (growing stock) despite a stable forest area. Active management of pine forests has increased the amount of timber stored in the standing trees by 68 million tonnes from 2006 to 2018.  Over the same period the hardwood inventory remained static.

Chart showing historic inventory and timberland area in Morehouse catchment

Historic inventory and timberland area in Morehouse catchment; click to view/download.

US Forest Service FIA data shows that the pine resource in this catchment area has been maturing, the volume of timber has been increasing in each size class year on year. This means that the volume available for harvesting is increasing and that more markets will be required to utilise this surplus volume and ensure that the long-term future of the forest area can be maintained.

Chart showing historic pine inventory by DBH Class

Historic pine inventory by DBH Class in Morehouse catchment; click to view/download.

This is reflected in the growth drain ratio – the comparison of annual growth versus harvesting. A ratio of one shows a forest area in balance, less than one shows that harvesting is greater than growth. This can be the case when the forest area is predominantly mature and at the age when clear cutting is necessary.

A growth drain ratio of more than one shows that growth exceeds harvesting, this is typically the case in younger forests that are not yet ready for harvesting and are in the peak growing phase, but it can also occur when insufficient market demand exists and owners are forced to retain stands for longer in the absence of a viable market.

Drax Morehouse plant

Drax’s Morehouse BioEnergy compressed wood pellet plant in northern Louisiana

This can have a negative impact on the future growth of the forest; limiting the financial return to forest owners and reducing the cumulative sequestration of carbon by enforcing sub-optimal rotation lengths.

The current growth drain ratio of pine around Morehouse is 1.67 with an average annual surplus of around 7 million metric tonnes. This surplus of growth is partly due to a decline in saw-timber demand due to the global financial crisis but also due to the maturing age class of the forest resource and the increasing quantity of timber available for harvesting.

Historic growth and removals of pine in Morehouse catchment (million metric tonnes)

YearGrowthRemovalsNet GrowthGrowth-to-Drain
200914.112960762411.1860124622.92694830041.26166145535
201014.580331100610.91819493463.662136166021.33541589869
201115.129903273610.72162297824.408280295451.41115792865
201215.357258404710.30755904395.049699360811.48990254039
201315.63898206189.701617808065.93736425371.61199733603
201415.91041518229.376564771556.533850410651.69682773701
201515.94235364499.669133266476.273220378431.64878828387
201616.43527840789.579357241816.855921165961.71569740985
201716.838075354610.1594737396.678601615681.65737672908
201817.770968348910.65938820047.111580148561.66716588371

The chart below shows the decline in pine saw-timber demand in the catchment area following the financial crisis in 2008. It also shows the recent increase in pulpwood demand driven by the new pellet mill markets that have supplemented the declining p&p mills.

Sawmills are a vital component of the forest industry around Morehouse, with most private owners seeking to maximise revenue through saw-timber production from pine forests.

As detailed in the table below, there are 70 markets for higher value timber products around this catchment area. These mills also need an off-taker for their residues and the pellet mills can provide a valuable market for this material, increasing the viability of the saw-timber market.

Operating grade-using facilities near Morehouse timber market

TypeNumber of MillsCapacityCapacity UnitsHardwood Roundwood At Mill From MarketSoftwood Roundwood At Mill From Market
Consumption, million green metric tonnes
Lumber6810538.8235294M m³1.737194320550.88604623042613.06745552335.69986977638
Plywood/Veneer2904M m³000.9617438725360.506109617373
Total701.737194320550.88604623042614.02919939586.20597939376

Pulp and paper mills dominate the low grade roundwood market for both hardwood and softwood. The pellet mill market is small with just 3 mills and therefore does not influence forest management decisions or macro trends in the catchment area. However, demand for wood pellet feedstock exceeds 1.5 million tonnes p.a. and this can provide a valuable market for thinnings and sawmill residues. A healthy forest landscape requires a combination of diverse markets co-existing to utilise the full range of forest products.

Operating pulpwood-using facilities near Morehouse timber market

TypeNumber of MillsCapacityCapacity UnitsHardwood Roundwood At Mill From MarketSoftwood Roundwood At Mill From Market
Consumption, million green metric tons
Pulp/Paper117634.86896M metric tons3.489826926741.192570970097.557287050371.66598821268
OSB/Panel62412.55M m³002.567325398621.19890681942
Chips178395.08999M metric tons2.938909722111.46484421365.287607151192.18745126814
Pellets31573.965975M metric tons002.078219858451.01128896402
Total346.428736648862.6574151836917.49043945866.06363526426

In its analysis, Forisk Consulting considered the impact that the new pellet mills including Morehouse BioEnergy have had on the significant trends in the local forest industry. The tables below summarise the Forisk view on the key issues. In its opinion, the Morehouse plant has had no negative impact.

Bioenergy impacts on markets and forest supplies in the Morehouse market

ActivityIs there evidence that bioenergy demand has caused the following?Explanation
DeforestationNo
Change in forest management practiceNo
Diversion from other marketsPossiblyBioenergy plants compete with pulp/paper and OSB mills for pulpwood and residual feedstocks. There is no evidence that these facilities reduced production as a result of bioenergy markets, however.
Increase in wood priceNoThere is no evidence that bioenergy demand increased stumpage prices in the market.
Reduction in growing stocking timberNo
Reduction in sequestration of carbon / growth rateNo
Increasing harvesting above the sustainable yieldNo

Bioenergy impacts on forests markets in the Morehouse market

Forest metric Bioenergy impact
Growing Stock Neutral
Growth Rates Neutral
Forest Area Neutral
Wood Prices Neutral
Markets for Solid Wood Neutral to Positive*
*Access to viable residual markets benefits users of solid wood (i.e. lumber producers).

Read the full report: Morehouse, Louisiana Catchment Area Analysis. An interview with the co-author, Amanda Hamsley Lang, COO and partner at Forisk Consulting, can be read here. Explore every delivery of wood to Morehouse BioEnergy using our ForestScope data transparency tool.

This is part of a series of catchment area analyses around the forest biomass pellet plants supplying Drax Power Station with renewable fuel. Others in the series include: ,

Others in the series include: Georgia MillEstonia, Latvia, Chesapeake and Drax’s own, other three mills LaSalle BionergyMorehouse Bioenergy and Amite Bioenergy.

Findings and Recommendations from the First Meeting of Drax’s Independent Advisory Board on Sustainable Biomass (IAB)

Sir John Beddington

Dear Will,

Findings and Recommendations from the First Meeting of Drax’s Independent Advisory Board on Sustainable Biomass (IAB)

The Independent Advisory Board on Sustainable Biomass provides this statement following its first meeting on Friday 15th November 2019.

Attendees: John Beddington (Chair), John Krebs (Deputy Chair), Virginia Dale, Sam Fankhauser, Elena Schmidt, Robert Matthews (Ex-Officio Member).

During the meeting, IAB members:

The IAB shares this summary of its findings and recommendations.

  • The IAB agreed that its role is to provide independent advice to Drax on its sustainable biomass policy and practice. IAB members will do this by scrutinising the science and evidence, informing Drax’s approach, and by providing independent feedback to Drax on how it can adopt best practices. In addition to holding two face to face meetings each year, the IAB agreed to hold two interim telephone meetings.
  • The IAB recommended Drax refer to “forest environment” not “natural environment” in its policy.
  • The IAB noted that the ten criteria Drax have outlined to reduce the carbon emissions of its biomass approach have been designed to reflect the findings of Forest Research’s Carbon Impacts of Biomass Consumed in the EU report (2018). The IAB found that the Drax criteria are an accurate interpretation of the report.
  • The IAB would like to explore how the science can further be developed with regard to the use of small, early thinnings and small roundwood, and consider how Drax’s policy might evolve.
  • The IAB and Drax discussed the possibility of developing some sub criteria for specific forest types.
  • The IAB suggested Drax could consider a “Restatement of the Evidence” academic review process to better understand, and draw alignment on, where there is scientific evidence on the sustainability of biomass.
  • The IAB suggested Drax should consider both a goal to continuously improve and consider the longer term implications of its policy commitments in light of potential climate changes.
  • The IAB emphasised that the way Drax operationalises its commitments will be critical. It stressed the importance of robustly exploring the counterfactuals to Drax’s biomass activities, highlighting the potential for trade-offs between climate and biodiversity outcomes as an area for more detailed review.
  • The IAB highlighted a number of considerations for Drax in its use of the Sustainable Biomass Program (SBP). It welcomed SBP’s adoption of a multi-stakeholder approach and suggested it will be important to scrutinise its evolution. It noted that, as Drax’s sustainability commitments go beyond SBP’s current criteria, Drax needs a strategy on how to evidence the compliance for these additional commitments.
  • The IAB expressed interest in learning about Drax’s long term vision. It noted that the ceasing of subsidies in 2027 will be a key milestone and highlighted its interest in exploring Drax’s strategy for managing this.

In future meetings with Drax, the IAB will further examine evidence of Drax’s approach, performance and impact against its commitments, to identify any changes that Drax may need to make. The IAB noted the following specific topics for further consideration:

  • Evidence relating to the impact of thinning a forest on carbon, pest control and fire risks;
  • How Drax operationalises its commitments, the counterfactuals of Drax’s biomass activities, and potential trade-offs between biodiversity and carbon outcomes;
  • Drax’s approach to biodiversity;
  • Drax’s long term vision including its plans for developing and scaling bioenergy with carbon capture and storage (BECCS) and its broader roadmap to net zero carbon emissions;
  • Drax’s evidencing for each of its climate related commitments;
  • Potential differences between the standards expected by stakeholders and local legal standards;
  • Water and soil management practices.

Yours sincerely,

Professor Sir John Beddington
Chair of the IAB

View/download the PDF version here