Tag: forestry and forest management and arboriculture

The key to sustainable forests? Thinking globally and managing locally

Key takeaways:

  • Working forests, where wood products are harvested, are explicitly managed to balance environmental and economic benefits, while encouraging healthy, growing forests that store carbon, provide habitats for wildlife, and space for recreation.
  • But there is no single management technique. The most effective methods vary depending on local conditions.
  • By employing locally appropriate methods, working forests have grown while supporting essential forestry industries and local economies.
  • Forests in the U.S. South, British Columbia, and Estonia all demonstrate how local management can deliver both environmental and economic wins.

Forests are biological, environmental, and economic powerhouses. Collectively they are home to most of the planet’s terrestrial biodiversity. They are responsible for absorbing 7.6 billion tonnes of carbon dioxide (CO2) equivalent per year, or roughly 1.5 times the amount of CO2 produced by the United States on an annual basis. And working forests, which are actively managed to generate revenue from wood products industries, are important drivers for the global economy, employing over 13 million people worldwide and generating $600 billion annually.

But as important as forests are globally, the key to maximizing working forests’ potential lies in smart, active forest management. While 420 million hectares of forest have been lost since 1990 through conversion to other land uses such as for agriculture, many working forests are actually growing both larger and healthier due to science-based management practices.

The best practices in working forests balance economic, social, and environmental benefits. But just as importantly, they are tailored to local conditions and framed by appropriate regional regulations, guidance, and best-practice.

The following describes how three different regions, from which Drax sources its biomass, manage their forests for a sustainable future.

British Columbia: Managing locally for global climate change

British Columbia is blanketed by almost 60 million hectares of forest – an area larger than France and Germany combined. Over 90% of the forest land is owned by Canada’s government, meaning the province’s forests are managed for the benefit of the Canadian people and in collaboration with First Nations.

From the province’s expanse of forested land, less than half a percent (0.36%) is harvested each year, according to government figures. This ensures stable, sustainable forests. However, there’s a need to manage against natural factors.

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In 2017, 2018, and 2020 catastrophic fires ripped through some of British Columbia’s most iconic forest areas, underscoring the threat climate change poses to the area’s natural resources. One response was to increase the removal of stands of trees in the forest, harvesting the large number of dead or dying trees created by pests that have grown more common in a warming climate.

By removing dead trees, diseased trees, and even some healthy trees, forest managers can reduce the amount of potential fuel in the forest, making devastating wildfires less likely. There are also commercial advantages to this strategy. Most of the trees removed are low quality and not suitable for processing into lumber. These trees can, however, still be used commercially to produce biomass wood pellets that offer a renewable alternative to fossil fuels. This means local communities don’t just get safer forests, they get safer forests that support the local economy.

The United States: Thinning for healthier forests

The U.S. South’s forests have expanded rapidly in recent decades, largely due to growth in working forests on private land. Annual forest growth in the region more than doubled from 193 million cubic metres of wood in 1953 to 408 million cubic meters by 2015.

This expansion has occurred thanks to active forest product markets which incentivise forest management investment. In the southern U.S. thinning is critical to managing healthy and productive pine forests.

Thinning is an intermediate harvest aimed at reducing tree density to allocate more resources, like nutrients, sunlight, and water, to trees which will eventually become valuable sawtimber. Thinning not only increases future sawtimber yields, but also improves the forest’s resilience to pest, disease, and wildfire, as well as enhancing understory diversity and wildlife habitat.

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While trees removed during thinning are generally undersized or unsuitable for lumber, they’re ideal for producing biomass wood pellets. In this way, the biomass market creates an incentive for managers to engage in practices that increase the health and vigour of forests on their land.

The results speak for themselves: across U.S. forestland the volume of annual net timber growth 36% higher than the volume of annual timber removals.

A managed working forest in the US South

Estonia: Seeding the future

Though Estonia is not a large country, approximately half of it is covered in trees, meaning forestry is integral to the country’s way of life. Historically, harvesting trees has been an important part of the national economy, and the government has established strict laws to ensure sustainable management practices.

These regulations have helped Estonia increase its overall forest cover from about 34% 80 years ago to over 50% today. And, as in the U.S. South, the volume of wood harvested from Estonia’s forests each year is less than the volume added by tree growth.

Sunrise and fog over forest landscape in Estonia

Sunrise and fog over forest landscape in Estonia

Estonia has managed to increase its growing forest stock by letting the average age of its forests increase. This is partially due to Estonia having young, fast-growing forests in areas where tree growth is relatively new. But it is also due to regulations that require harvesters to leave seed trees.

Seed trees are healthy, mature trees, the seeds from which become the forest’s next generation. By enforcing laws that ensure seed trees are not harvested, Estonia is encouraging natural regeneration of forests. As in the U.S. South protecting these seed trees from competition for water and nutrients means removing smaller trees in the area. While these smaller trees may not all be suitable for lumber, they are a suitable feedstock for biomass. It means managing for natural regeneration can still have economic, as well as environmental, advantages.

Different methods, similar results

Laws, landownership, and forestry practices differ greatly between the U.S. South, British Columbia, and Estonia, but all three are excellent examples of how local forest management contributes to healthy rural economies and sustained forest coverage.

While there are many different strategies for creating a balance between economic and environmental interests, all successful strategies have something in common: They encourage healthy, growing forests.

Supporting a circular economy in the forests

Every year in British Columbia, millions of tonnes of waste wood – known in the industry as slash – is burned by the side of the road.

Land managers are required by law to dispose of this waste wood – that includes leftover tree limbs and tops, and wood that is rotten, diseased and already fire damaged – to reduce the risks of wildfires and the spread of disease and pests.

The smoke from these fires is choking surrounding communities – sometimes “smoking out entire valleys,” air quality meteorologist from BC’s Environment Ministry Trina Orchard recently told iNFOnews.ca.

It also impacts the broader environment, releasing some 3 million tonnes of CO2 a year into the atmosphere, according to some early estimates.

Slash pile in British Columbia

Landfilling this waste material from logging operations isn’t an option as it would emit methane – a greenhouse gas that is about 25 times more potent than CO2. So you can see why it ends up being burned.

In its Modernizing Forest Policy in BC, the government has already identified its intention to phase out the burning of this waste wood left over after harvesting operations and is working with suppliers and other companies to encourage the use of this fibre.

This is a very positive move as this material must come out of the forests to reduce the fuel load that can help wildfires grow and spread to the point where they can’t be controlled, let alone be extinguished.

The wildfire risk is real and growing. Each year more forests and land are destroyed by wildfire, impacting communities, nature, wildlife and the environment.

In the past two decades, wildfires burned two and a half times more land in BC than in the previous 50-year period. According to very early estimates, emissions from last year’s wildfires in the province released around 150 million tonnes of CO2 – equivalent to around 30 million cars on the road for a year.

Alan Knight at the log yard for Lavington Pellet Mill in British Columbia

During my recent trip to British Columbia in Canada, First Nations, foresters, academics, scientists and government officials all talked about the burning piles of waste wood left over after logging operations.

Rather than burning it, it would be far better, they say, to use more of this potential resource as a feedstock for pellets that can be used to generate renewable energy, while supporting local jobs across the forestry sector and helping bolster the resilience of Canada’s forests against wildfire.

I like this approach because it brings pragmatism and common sense to the debate over Canada’s forests from the very people who know the most about the landscape around them.

Burning it at the roadside is a waste of a resource that could be put to much better use in generating renewable electricity, displacing fossil fuels, and it highlights the positive role the bioenergy industry can play in enhancing the forests and supporting communities.

Drax is already using some of this waste wood – which I saw in the log yard for our Lavington Pellet mill in British Columbia. This waste wood comprises around 20% of our feedstock. The remaining 80% comes from sawmill residues like sawdust, chips and shavings.

Waste wood for pellets at Lavington Pellet Mill log yard

It’s clear to me that using this waste material that has little other use or market value to make our pellets is an invaluable opportunity to deliver real benefits for communities, jobs and the environment while supporting a sustainable circular economy in the forestry sector.

What is the carbon cycle?

What is the carbon cycle?

All living things contain carbon and the carbon cycle is the process through which the element continuously moves from one place in nature to another. Most carbon is stored in rock and sediment, but it’s also found in soil, oceans, and the atmosphere, and is produced by all living organisms – including plants, animals, and humans.

Carbon atoms move between the atmosphere and various storage locations, also known as reservoirs, on Earth. They do this through mechanisms such as photosynthesis, the decomposition and respiration of living organisms, and the eruption of volcanoes.

As our planet is a closed system, the overall amount of carbon doesn’t change. However, the level of carbon stored in a particular reservoir, including the atmosphere, can and does change, as does the speed at which carbon moves from one reservoir to another.

What is the role of photosynthesis in the carbon cycle?

Carbon exists in many different forms, including the colourless and odourless gas that is carbon dioxide (CO2). During photosynthesis, plants absorb light energy from the sun, water through their roots, and CO2 from the air – converting them into oxygen and glucose.

The oxygen is then released back into the air, while the carbon is stored in glucose, and used for energy by the plant to feed its stem, branches, leaves, and roots. Plants also release CO2 into the atmosphere through respiration.

Animals – including humans – who consume plants similarly digest the glucose for energy purposes. The cells in the human body then break down the glucose, with CO2 emitted as a waste product as we exhale.

CO2 is also produced when plants and animals die and are broken down by organisms such as fungi and bacteria during decomposition.

What is the fast carbon cycle?

The natural process of plants and animals releasing CO2 into the atmosphere through respiration and decomposition and plants absorbing it via photosynthesis is known as the biogenic carbon cycle. Biogenic refers to something that is produced by or originates from a living organism. This cycle also incorporates CO2 absorbed and released by the world’s oceans.

The biogenic carbon cycle is also called the “fast” carbon cycle, as the carbon that circulates through it does so comparatively quickly. There are nevertheless substantial variations within this faster cycle. Reservoir turnover times – a measure of how long the carbon remains in one location – range from years for the atmosphere to decades through to millennia for major carbon sinks on land and in the ocean.

What is the slow carbon cycle?

In some circumstances, plant and animal remains can become fossilised. This process, which takes millions of years, eventually leads to the formation of fossil fuels. Coal comes from the remains of plants that have been transformed into sedimentary rock. And we get crude oil and natural gas from plankton that once fell to the ocean floor and was, over time, buried by sediment.

The rocks and sedimentary layers where coal, crude oil, and natural gas are found form part of what is known as the geological or slow carbon cycle. From this cycle, carbon is returned to the atmosphere through, for example, volcanic eruptions and the weathering of rocks. In the slow carbon cycle, reservoir turnover times exceed 10,000 years and can stretch to millions of years.

How do humans impact the carbon cycle?

Left to its own devices, Earth can keep CO2 levels balanced, with similar amounts of CO2 released into and absorbed from the air. Carbon stored in rocks and sediment would slowly be emitted over a long period of time. However, human activity has upset this natural equilibrium.

Burning fossil fuel releases carbon that’s been sequestered in geological formations for millions of years, transferring it from the slow to the fast (biogenic) carbon cycle. This influx of fossil carbon leads to excessive levels of atmospheric CO2, that the biogenic carbon cycle can’t cope with.

As a greenhouse gas that traps heat from the sun between the Earth and its atmosphere, CO2 is essential to human existence. Without CO2 and other greenhouse gases, the planet could become too cold to sustain life.

However, the drastic increase in atmospheric CO2 due to human activity means that too much heat is now retained between Earth and the atmosphere. This has led to a continued rise in the average global temperature, a development that is part of climate change.

Where does biomass fit into the carbon cycle?

One way to help reduce fossil carbon is to replace fossil fuels with renewable energy, including sustainably sourced biomass. Feedstock for biomass energy includes plant material, wood, and forest residue – organic matter that absorbs CO2 as part of the biogenic carbon cycle. When the biomass is combusted in energy or electricity generation, the biogenic carbon stored in the organic matter is released back into the atmosphere as CO2.

This is distinctly different from the fossil carbon released by oil, gas, and coal. The addition of carbon capture and storage to bioenergy – creating BECCS – means the biogenic carbon absorbed by the organic matter is captured and sequestered, permanently removing it from the atmosphere. By capturing CO2 and transporting it to geological formations – such as porous rocks – for permanent storage, BECCS moves CO2 from the fast to the slow carbon cycle.

This is the opposite of burning fossil fuels, which takes carbon out of geological formations (the slow carbon cycle) and emits it into the atmosphere (the fast carbon cycle). Because BECCS removes more carbon than it emits, it delivers negative emissions.

Fast facts

  • According to a 2019 study, human activity including the burning of fossil fuels releases between 40 and 100 times more carbon every year than all volcanic eruptions around the world.
  • In March 2021, the Mauna Loa Observatory in Hawaii reported that average CO2 in the atmosphere for that month was 14 parts per million. This was 50% higher than at the time of the Industrial Revolution (1750-1800).
  • There is an estimated 85 billion gigatonne (Gt) of carbon stored below the surface of the Earth. In comparison, just 43,500 Gt is stored on land, in oceans, and in the atmosphere.
  • Forests around the world are vital carbon sinks, absorbing around 7.6 million tonnes of CO2 every year.

Go deeper

Alabama Cluster Catchment Area Analysis

The area of timberland in the Alabama cluster catchment area has remained stable over the last 20 years, increasing slightly from 4.08 million ha to 4.16 million ha, an increase of 79 thousand hectares.  This area represents 79.6% of the total land area in 2020, up from 78.1% in 2020.  The total area of forestland and woodland was 86% of the catchment area in 2020, with farmland making up 13% and urban areas 1%.  This land base can be considered to be heavily forested and dominated by timberland.

Figure 1: Land Use Type – Alabama cluster

The timberland area is classified by growth rate potential, capable of achieving a minimum of 0.57 m3/ha/year.  More than 95% of the timberland area is in private ownership.  This proportion has remained stable since 2000 as shown in Figure 2.

Figure 2: Timberland Ownership Profile – Alabama cluster

The total standing volume, the amount of carbon stored in the forest area, has increased by 115 million m3 since 2000 an increase of 30%. Most of this increase has occurred since 2010, with 90 million m3 added to the inventory since this time, reflecting the maturing age class of the forest resource as it passes through the peak growth phase.  Almost all of this increase has been in the softwood pine forest area, with a combined increase of 86 million m3 since 2010.  Pine saw-timber and chip-n-saw both increased by 46% since 2010 and pine pulpwood by 25% over the same period. Suggesting that the average tree size is getting larger as the forest matures.

Figure 3: Standing Volume by Product Class – Alabama cluster

One measure of the sustainability of harvesting levels is to compare average annual growth against removals.  This comparison gives a growth drain ratio (GDR).  Where removals are equal to or lower than growth (a GDR of 1 or more) this is a measure of sustainability, where the ratio falls below 1, this can indicate that harvesting levels are not sustainable in the long-term.  Figure 4 shows that all pine product classes have a positive GDR since 2010.  In particular the pine pulpwood GDR ratio is in excess of 2 suggesting that there is a substantial surplus of this product category.  By contrast, the hardwood GDR for both saw-timber and pulpwood are both lower than 1 suggesting that harvesting levels for hardwood species should be reduced until growth can recover.

Figure 4: Growth Drain Ratio by Product Class – Alabama cluster

Figure 5 shows the maturing age class of the forest area, charting the change in annual surplus and deficit in each product class.  The trend shows that harvesting of pine saw-timber from 2000 to 2008 represented a deficit of growth compared to harvesting removals.  This indicates an immature forest resource with a low quantity of forest categorised as saw-timber, therefore harvesting volume in mature stands outweighed the growth in mid-rotation stands.  As the forest aged, and more standing timber grew into the saw-timber category, the surplus of annual growth compared to removals increased.  Saw-timber growth in 2020 was 3 million m3 higher than in 2000.  The surplus of pine pulpwood has remained positive and has increased substantially from 3 million m3 in 2000 to 6.5 million m3 in 2020 despite harvesting levels increasing slightly over this period.

Figure 5: Annual Surplus/Deficit of Growth and Removal by Product Class – Alabama Cluster

Biomass demand began in 2008 at a very small scale, representing just 0.5% of total pulpwood demand in the catchment area.  From around 2013 it began to increase and reached peak in 2015 with a total demand of 724,000 tons of pulpwood in that year, representing 8.1% of total pulpwood demand in the catchment area.  After that time, demand for pulpwood declined as pellet mills switched to mill residuals.  The latest data on pulpwood demand shows that the biomass sectors made up just 2.8% of total pulpwood demand in 2020 with just over 216,000 tonnes of total demand.  This demonstrates that the biomass and wood pellet sector is a very small component of the market in this region and unlikely to influence forest management decision making, as shown in Figure 6.

Figure 6: Pulpwood Demand by Market – Alabama Cluster

Pine pulpwood stumpage prices have declined significantly since a peak in 2013, falling from an annual high of $9.46 when demand was strongest to just $4.12 in 2020 as demand for pine pulpwood declined in 2020.  Pine saw-timber prices have seen a similar decline from a high point in the early 2000’s to a plateau from 2011 onwards.  Saw-timber stumpage more than halved in value over this period from $49 per ton to $22 per ton.  This can have a significant impact on forest management objectives and decision making.

Figure 7: Stumpage Price Change by Product Category – Alabama Cluster

Detailed below are the summary findings from Hood Consulting on the impact of biomass demand on key issues in the Alabama cluster catchment area.

Is there any evidence that bioenergy demand has caused the following:

Deforestation?

No. US Forest Service (USFS) data shows that total timberland area has held steady and averaged roughly 4,172,000 hectares in the Alabama Cluster catchment area since Alabama Pellets-Aliceville started up in late-2012. More importantly, planted pine timberland (the predominant source of roundwood utilized by the bioenergy industry for wood pellet production) has increased more than 75,000 hectares (+4.9%) in the catchment area since Alabama Pellets’ startup in 2012.

A change in management practices (rotation lengths, thinnings, conversion from hardwood to pine)?

Inconclusive. Changes in management practices have occurred in the catchment area over the last two decades. However, the evidence is inconclusive as to whether increased demand attributed to bioenergy has caused or is responsible for those changes.

Clearcuts and thinnings are the two major types of harvests that occur in this region, both of which are long-standing, widely used methods of harvesting timber. TimberMart-South (TMS) data shows that the prevalence of thinnings temporarily increased in the Alabama Cluster market (from 2007-2013) due to the weakening of pine sawtimber markets. Specifically, challenging market conditions saw pine sawtimber stumpages prices decline from an average of $47 per ton from 2000-2006 to just over $23 per ton in 2011, or a roughly 50% decrease from 2000-2006 average levels. This led many landowners to refrain from clearcutting (a type of harvest which typically removes large quantities of pine sawtimber), as they waited for pine sawtimber prices to improve. However, pine sawtimber stumpage prices never recovered and have held between $22 and $25 per ton since 2011. Ultimately, landowners returned to more ‘normal’ management practices by 2014, with thinnings falling back in line with pre-2007 trends.

The catchment area has also experienced some conversion. Specifically, from 2000-2020, planted pine timberland increased more than 460,000 hectares while natural hardwood and mixed pine-hardwood timberland decreased a combined 390,000 hectares. Note that the increase in planted pine timberland and decrease in natural hardwood/mixed pine-hardwood timberland over this period were both gradual and occurred simultaneously. This suggests a management trend in which natural timber stands are converted to plantation pine following final harvest. It’s also important to note that there is little evidence that links these changes to increased demand from bioenergy, as this conversion trend begun years prior to the startup of Alabama Pellets and continued nearly unchanged following the pellet mill’s startup.

Diversion from other markets?

No. Demand for softwood (pine) sawlogs increased an estimated 12% in the catchment area from 2012-2020. Also, there is no evidence that increased demand from bioenergy has caused a diversion from other softwood pulpwood markets (i.e. pulp/paper). Also, even though softwood pulpwood demand not attributed to bioenergy is down 14% since Alabama Pellets-Aliceville’s startup in 2012, there is no evidence that increased demand from bioenergy has caused this decrease. Rather, the decrease in demand from non-bioenergy sources is due to a combination of reduced product demand (and therefore reduced production) and increased utilization of sawmill residuals.

An unexpected or abnormal increase in wood prices?

No. The startup of Alabama Pellets-Aliceville added roughly 450,000 metric tons of softwood pulpwood demand to the catchment area from 2012-2016, and this increase in demand coincided with essentially no change in delivered pine pulpwood (PPW) price over this same period. Ultimately, the additional demand placed on the catchment area following the startup of Alabama Pellets-Aliceville was offset by a decrease in demand from other sources from 2012-2016, and, as a result, delivered PPW prices remained nearly unchanged.

However, the Aliceville facility was shut down for a majority of 2017 due to the catastrophic failure of a key piece of environmental equipment, and this was followed by Alabama Pellets’ strategic decision to transition to residual-consumption only beginning in 2018, which eliminated more than 360,000 metric tons of annual softwood pulpwood demand from 2016-2018. Over this same period, softwood pulpwood demand from other sources also decreased nearly 360,000 metric tons. So, with the elimination of roughly 720,000 metric tons of annual softwood pulpwood demand from all sources from 2016-2018, delivered PPW prices in the catchment area proceeded to decrease more than 6% over this period. Since 2018, total softwood pulpwood demand has increased roughly 4% in the catchment area (due to increases in demand from non-bioenergy sources), and this increase that has coincided with a simultaneous 4% increase in delivered PPW price.

Statistical analysis did identify a positive relationship between softwood biomass demand and delivered PPW price. However, the relationship between delivered PPW price and non-biomass-related softwood pulpwood demand was found to be stronger, which is not unexpected given that pine pulpwood demand not attributed to bioenergy has accounted for 94% of total pine pulpwood demand in the catchment area since 2012. Ultimately, the findings provide evidence that PPW price is influenced by demand from all sources – not just from bioenergy or from pulp/paper, but from both.

Furthermore, note that Alabama Pellets’ shift to residual-consumption only beginning in 2018 resulted in no increase in pine sawmill chip prices, as the price of pine sawmill chips in the Alabama Cluster catchment area rather decreased from 2018-2020, despite a more than 100,000-metric ton increase in pine sawmill chip consumption by the Aliceville mill over this period.

A reduction in growing stock timber?

No. From 2012 (the year Alabama Pellets started up) to 2020, total growing stock inventory increased an average of 2.6% per year (+22% total) in the Alabama Cluster catchment area. Specifically, inventories of pine sawtimber and pine chip-n-saw increased 41% and 40%, respectively, while pine pulpwood (PPW) inventory increased 25% over this same period.

A reduction in the sequestration rate of carbon?

No. US Forest Service (USFS) data shows the average annual growth rate of total growing stock timber in the Alabama Cluster catchment area increased from 6.0% in 2012 to 6.2% in 2020, suggesting that the sequestration rate of carbon also increased slightly over this period.

Note that the increase in overall growth rate (and therefore increase in the sequestration rate of carbon) can be linked to gains in pine timberland and associated changes with the catchment area forest. Specifically, growth rates decline as timber ages, so the influx of new pine timberland (due to the conversion of both hardwood forests and cropland) has resulted in just the opposite, with the average age of softwood (pine) growing stock inventory decreasing from an estimated 35.4 years of age in 2000 to 33.2 years of age in 2010 and to 32.2 years of age in 2020 (total growing stock inventory decreased from 41.9 to 41.0 and to 40.4 years of age over these periods).

An increase in harvesting above the sustainable yield capacity of the forest area?

No. Growth-to-removals (G:R) ratios, which compare annual timber growth to annual timber removals, provides a measure of market demand relative to supply as well as a gauge of market sustainability. In 2020, the latest available, the G:R ratio for pine pulpwood (PPW), the predominant timber product utilized by the bioenergy sector, equaled 3.26 (recall that a value greater than 1.0 indicates sustainable harvest levels).

Moreover, note that the PPW G:R ratio has increased in the catchment area since the Aliceville mill’s startup in 2012, despite the associated increases in pine pulpwood demand. In this catchment area, pine pulpwood demand from non-bioenergy sources decreased more than 860,000 metric tons from 2012 to 2020, and this decrease more than offset any increase in demand from bioenergy.

Impact of bioenergy demand on:

Timber growing stock inventory

Neutral. According to USFS data, inventories of pine pulpwood (PPW) increased 25% in the catchment area from 2012-2020, and this increase in PPW inventory can be linked to both increases in pine timberland and harvest levels below the sustainable yield capacity of the forest area. Specifically, pine timberland (both planted and natural combined) increased more than 185,000 hectares in the catchment area from 2012-2020. Over this same period, annual harvests of PPW were 65% below maximum sustainable levels.

Timber growth rates

Neutral. The average annual growth rate of total growing stock timber increased from 6.0% in 2012 to 6.2% in 2020 in the Alabama Cluster catchment area, despite pine pulpwood (PPW) growth rate decreasing from 15.1% to 12.5% over this period. However, this decrease in PPW growth rate was not due to increased demand attributed to bioenergy but rather to the aging of PPW within its product group and its natural movement along the pine growth rate curve. Specifically, USFS data indicates the average age of PPW inventory in the catchment area increased from an estimated 13.4 years of age in 2012 to 13.6 years of age in 2020.

Forest area

Neutral. In the Alabama Cluster catchment area, total forest (timberland) area remained nearly unchanged (decreasing only marginally) from 2012-2020. However, pine timberland – the predominant source of roundwood utilized by the bioenergy industry for wood pellet production – increased more than 185,000 hectares over this period, and this increase can be linked to several factors, including conversion from both hardwood and mixed pine-hardwood forests as well as conversion from cropland.

Specifically, the more than 185,000-hectare increase in pine timberland from 2012-2020 coincided with a roughly 197,000-hectare decrease in hardwood/mixed pine-hardwood timberland and a more than 8,000-hectare decrease in cropland over this period. Furthermore, statistical analysis confirmed these inverse relationships, identifying strong negative correlations between pine timberland area and both hardwood/mixed pine-hardwood timberland area and cropland in the catchment area from 2012-2020.

Wood prices

Negative/Neutral. Softwood pulpwood demand attributed to bioenergy increased from roughly 80,000 metric tons in 2012 (the year Alabama Pellets-Aliceville started up) to more than 655,000 metric tons in 2015 (the year biomass demand reached peak levels). However, this roughly 575,000-metric ton increase in softwood biomass demand coincided with essentially no change in delivered pine pulpwood (PPW) price – which averaged $26.40 per ton in 2012 and $26.39 per ton in 2015. Ultimately, the additional demand placed on this catchment area following the startup of Alabama Pellets-Aliceville was offset by a more than 680,000-metric ton decrease in demand from other sources over this same period, and, as a result, delivered PPW prices remained nearly unchanged. Also note that Alabama Pellets’ strategic shift to consume residuals only (a transition that begun in 2018 and had been completed by 2019) resulted in a nearly 480,000-metric ton decrease in softwood biomass demand in the catchment area from 2015 to 2020. Over this same period, softwood pulpwood demand from other sources decreased more than 180,000 metric tons. In total, softwood pulpwood demand from all sources decreased more than 660,000 metric tons from 2015 to 2020, and this decrease in demand resulted in delivered PPW prices decreasing 5% over this period.

Statistical analysis did identify a positive relationship between softwood biomass demand and delivered PPW price. However, the relationship between delivered PPW price and non-biomass-related softwood pulpwood demand was found to be stronger, which is not unexpected given that pine pulpwood demand not attributed to bioenergy has accounted for 94% of total pine pulpwood demand in the catchment area since 2012. Ultimately, the findings provide evidence that PPW price is influenced by demand from all sources – not just from bioenergy or from pulp/paper, but from both.

Markets for solid wood products

Positive. In the Alabama Cluster catchment area, demand for softwood sawlogs used to produce lumber and other solid wood products has increased an estimated 12% since 2012, and this increase in softwood lumber production has consequentially resulted in the increased production of sawmill residuals (i.e. chips, sawdust, and shavings) – by-products of the sawmilling process and materials utilized by Alabama Pellets to produce wood pellets.

Moreover, the increased availability of sawmill residuals and lower relative cost compared to roundwood (after chipping and other processing costs are considered) led Alabama Pellets to make a strategic shift to utilize residuals only for wood pellet production beginning in 2019. So, not only has Alabama Pellets benefited from the greater availability of this lower-cost sawmill by-product, but lumber producers have also benefited, as Alabama Pellets has provided an additional outlet for these producers and their by-products.

Read the full report: Alabama Cluster Catchment Area Analysis

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 can be found here

Enviva Cottondale pellet plant catchment area analysis

The Enviva Cottondale pellet mill has a production capacity of 760,000 metric tonnes of wood pellets annually. Raw material used by the mill includes a combination of roundwood, chips, and secondary residuals (i.e., sawdust and shavings), with pine accounting for 80‐90% of total feedstock. In October 2018, Hurricane Michael passed through the centre of the Cottondale catchment area, causing significant damage to the forest resource with more than 500,000 hectares (ha) of forestland destroyed and an estimated loss of 42 million m3of timber (equivalent to around 4 times the UK annual production of roundwood).

This event has had an impact on the data trends for forest inventory, growth and harvesting removals – as harvesting levels were increased to salvage as much timber as possible before it became unusable due to decay. This can be clearly seen in many of the charts below. However, these forest areas have been restored and now continue to grow, allowing the catchment area to return to its pre-hurricane trends in the medium term.

Forest Area 

The catchment area around Enviva’s Cottondale pellet mill includes 4.3 million ha of land, based on the historical feedstock sourcing patterns of the mill. Timberland represents 68.7% (2.95 million ha) of the total land area in the Cottondale catchment area, this has increased slightly since 2000 from 67.8% and can be considered to have remained stable over this time period.  There are also around 300,000 ha of woodland (associated with agricultural land) and around 800,000 ha of cropland and pastureland.  Forestry is the dominant land use in this catchment area (Figure 1).

Figure 1: Land area by usage

Planted pine represents 33% of the timberland area, natural pine 20%, with 10% mixed stands and the remainder being hardwood forest of which 94% is naturally regenerated (Figure 2).  The breakdown of forest type and species composition has remained relatively stable and largely unchanged over the last 20 years, in contrast to other parts of the US South where some natural pine stands have been converted to planted pine. The pine and mixed forest areas are actively managed and produce the majority of the timber harvest in the catchment area. Despite the large area of hardwood forest, management and timber production is limited. Much of this area is classified as bottomland hardwood located alongside rivers, streams, and creeks and in streamside management zones (SMZs), which restricts active management. In addition, the proportion of this catchment area located in Florida contains a large area of swampland, which is largely composed of hardwoods and cannot be actively managed for timber production and is recognised as having important ecological value.

Figure 2: Breakdown of forest type

Volume and Growth

The overall trend of volume and growth in the Cottondale catchment area is of a maturing forest resource and an increasing accumulation of standing volume, particularly in the larger forest product classes (saw-timber and chip-n-saw). Figure 3 shows that total standing volume increased by 64 million m3 from 2000 to 2018, with the largest increases in the pine saw-timber and chip-n-saw categories. In 2018, the devastating impact of Hurricane Michael caused a substantial reduction in the standing volume across every product category with the total standing volume being reduced by 42 million m3. This event has had a significant impact on the forest resource and is a primary cause of recent data trends.

However, the overall long-term trend in the catchment area is of maturing forest and increasing inventory. This should continue in the long-term once the impact of the hurricane damage has been managed and replacement forest areas begin to mature.

Figure 3: Standing volume by product category

Pine pulpwood inventory increased steadily by around 8 million m3 from 2000 to 2013, reaching a peak of 49 million m3. This then declined slightly to 46 million m3 in 2018 due to the maturing age class of the forest and pulpwood forest growing into the larger size class of chip-n-saw and saw-timber forest (Figure 4), in addition to an increase in pulpwood demand as biomass markets became operational and ramped up production. Following the hurricane in 2018, the pine pulpwood inventory dropped by more than 10 million m3. 

Replanting and reforestation of damaged areas will ensure that future pine pulpwood production will increase again once these forests start to mature.

In the period from 2000 to 2018 pine sawtimber standing volume increased by 41.5 million m3 (78%) and chip-n-saw by 19.6 million m3 (73%), indicating a maturing age class and a growing forest resource. The 2018 hurricane caused a reduction in standing volume in both of these product categories of 11.6 and 8 million m3respectively (12% and 17% of the 2018 volume). However, the increasing trend is likely to continue once the forest area recovers.

Figure 4: Standing volume by product category

The growth drain ratio (GDR) is the comparison of average annual growth to removals (typically harvesting), where the growth exceeds removals the GDR will be in excess of 1 and this is considered sustainable, where removals exceed growth then the GDR will be less than 1 and this is not sustainable if maintained in the long-term – although in the short-term this can be a factor of large areas of mature forest with low growth rates and high rates of harvesting, short periods of high demand for a particular product or salvage harvesting after a natural disturbance. The GDR should be considered over a longer time period to ensure it reflects the long-term trend. In the period from 2003 to 2020 the combined GDR for pine products averaged 1.52 with a high of 1.84 and a low of 1.08 (Figure 5).

Figure 5: Growth to drain ratio by product category

The maturing forest resources can be clearly seen from the growth to removals data for each product category. Average tree sizes getting larger and more pulpwood class stands moving into the larger saw-timber and chip-n-saw categories. This trend can be seen by comparing the data values from 2003 and 2018 where saw-timber average annual growth increased by 90% (1.6 million m3), and removals by 41% (0.98 million m3).  Chip-n-saw growth increased by 73% (1.3 million m3) whilst removals increased by 160% (1.9 million m3). Pulpwood growth decreased by 7.5% (0.4 million m3) whilst removals increased by 63% (1.6 million m3).  Over this time period the total annual surplus of pine growth compared to removals averaged 3.7 million m3 per year (Figure 6).

Figure 6: Pine growth and removals by product category and year

Hardwood saw-timber and pulpwood removals declined by 20% and 40% respectively between 2000 and 2018, whilst growth increased by 23% for hardwood saw-timber and declined by 16% for hardwood pulpwood. The average annual hardwood surplus over this time period was 1.5 million m3 per year (Figure 7).

Figure 7: Hardwood growth and removals by product category and year

Despite a short-term imbalance in some product categories, the overall surplus of pine growth compared to removals has remained strong, with an average of 3.3 million m3 between 2000 and 2020, which includes the increased salvage harvesting in 2018 (Figure 8).

Figure 8: Cumulative annual surplus of growth compared to removals

Wood Prices

Stumpage price is the value paid to the forest owner for each category of product at the time of harvesting. The variation in prices in the Cottondale catchment area has been significant and shows some interesting trends. The higher value pine products (saw-timber and chip-n-saw) began with high stumpage values in 2000, as markets were strong for construction and furniture grade timber and supply limited at that stage due to the young age class and predominance of pulpwood stands at that time.  In 2008, following the global economic crisis and the crash in housing and construction markets, saw-timber prices declined substantially reaching a low of $23 per ton, a 47% decline from the 2000 price. This stumpage price has never recovered, despite an improvement in the economy and an increase in housing starts and demand for structural timber. The reason for the continued deflated saw-timber stumpage price is a substantial surplus of supply in this catchment area.  As the forest area has matured and more saw-timber grade stands are available, markets have been able to satisfy demand without an increase in price.

Pine pulpwood prices at Cottondale were lower than the US South-wide average in 2000 and remained relatively low until around 2013. A reduction in saw-timber production, and consequent reduction in mill residuals, due to the recession of 2008, led to a shortage of pulp mill feedstock and increased harvesting of pulpwood stands. This caused an increase in pine pulpwood stumpage values alongside an overall increase in demand as biomass and pellet markets began production around this time. The data shows a short-term spike in pine pulpwood stumpage prices in 2013-14, but this returned to a more normal trend as more saw-timber residues became available and pulpwood stumpage values have been around $10-11 per ton since 2015 (Figure 9).

Figure 9: Variation in stumpage value over time

Biomass demand 

Biomass demand in the Cottondale catchment area began in 2008 and has averaged around 800 thousand m3per year since that time with a high of just over 1 million m3 in 2013 to 2015 and a low of 200 thousand m3 in 2008. Other pulpwood markets have had an average annual demand of 3.97 million m3 between 2000 and 2020 with a high of 4.76 million m3 in 2018 and a low of 3.2 million m3 in 2009.  In 2020 the biomass market represented 16% of the total pulpwood demand in the Cottondale catchment area (Figure 10).

Figure 10: Total pulpwood demand

Forest Management

The average size of clear-cut harvesting sites from 2000 to 2020 has been 47 ha, ranging from 38 ha up to 56 ha. The average size of thinning sites has been 65 ha, ranging from 55 ha up to 76 ha. When isolating the period from 2000 to 2010 and 2011 to 2020, the averages and range remain very similar, suggesting that there has been no significant change in harvesting coupe size over this period.

Figure 11: Average size of harvesting sites

The impact of biomass and wood pellet demand on the key metrics in this catchment area are considered below. This is a summary of Hood Consulting’s view on the trends and impacts in the Cottondale catchment area.

Is there any evidence that bioenergy demand has caused the following:

Deforestation?

No. US Forest Service (USFS) data shows a 55,166-hectare (+1.9%) increase in the total area of timberland in the Enviva Cottondale catchment area since the Enviva Cottondale pellet mill commenced production in 2008. Furthermore, a strong positive relationship was identified between biomass demand and timberland area, suggesting that the increase in timberland area since 2008 can be linked, to a degree, to increased demand attributed to bioenergy.

A change in management practices (rotation lengths, thinnings, conversion from hardwood to pine)?

Inconclusive. Changes in management practices have occurred in the catchment area over the last two decades. However, the evidence is inconclusive as to whether increased demand attributed to bioenergy has caused or is responsible for these changes.

Clearcuts and thinnings are the two major types of harvests that occur in this region, both of which are long-standing, widely used methods of harvesting timber. TimberMart-South (TMS) data shows that thinnings accounted for 63% of total reported harvest area in the Cottondale market from 2005-2011 but only 39% of total harvest area reported from 2012-2020. Specifically, the decreased prevalence of thinning since 2012 can be linked to the strengthening of pine pulpwood markets and concurrent weakening of pine sawtimber markets beginning in the mid-2000s.

Prior to the bursting of the US housing bubble in 2006, timber management in this market had been driven to a large degree by pine sawtimber production. However, challenging market conditions saw pine sawtimber stumpages prices decline more than 40% from 2006-2011. At the same time, pine pulpwood markets started to strengthen, with pine pulpwood stumpage prices increasing more than 50% from 2006-2010. So, with sawtimber markets weakening and pulpwood markets strengthening, the data suggests that many landowners decided to alter their management approach (i.e. to take advantage of strong pulpwood markets) and focus on short pulpwood rotations that typically do not utilize thinnings.

Bioenergy has had an impact on this market by adding an average of roughly 680,000 metric tons of additional pine pulpwood demand to this catchment area annually since 2008. However, bioenergy has accounted for only 17% of total softwood pulpwood demand in this market since Enviva Cottondale’s startup. Ultimately, the shift in management approach that occurred in this market can be more closely linked to other factors, such as increased softwood pulpwood demand from non-bioenergy sources (i.e. pulp/paper) as well as the weakening of pine sawtimber markets.

Diversion from other markets?

No. Demand for softwood (pine) sawlogs increased an estimated 23% in the Cottondale catchment area from 2008-2020. Also, there is no evidence that increased demand from bioenergy has caused a diversion from other softwood pulpwood markets (i.e. pulp/paper), as softwood pulpwood demand not attributed to bioenergy has increased 25% since the Cottondale mill’s startup in 2008.

An unexpected or abnormal increase in wood prices?

Inconclusive. The startup of Enviva Cottondale added more than 900,000 metric tons of softwood pulpwood demand to the catchment area from 2008-2013, and this increase in demand coincided with a 28% increase in the delivered price of pine pulpwood (PPW) – the primary roundwood product consumed by the Enviva Cottondale mill. However, since 2013, delivered PPW prices have held flat, despite biomass-related softwood pulpwood demand falling to an average of roughly 635,000 tons per year since 2016, down more than 40% compared to 2013 peak levels. (Note the decrease in roundwood consumption was due to a higher utilization of secondary residuals). It’s also important to point out that the roughly 410,000-metric ton decrease in softwood biomass demand from 2013 to 2020 was offset by a roughly 455,000-metric ton increase in softwood pulpwood demand from other sources.

Statistical analysis did identify a positive relationship between softwood biomass demand and delivered PPW price. However, that relationship was found to be relatively weak. The relationship between delivered PPW price and softwood pulpwood demand from other sources was found to be much stronger, which was not unexpected to find given that softwood pulpwood demand not attributed to bioenergy has accounted for 83% of total softwood pulpwood demand in the catchment area since 2008.

Furthermore, there is some evidence linking the increase in pine sawmill chip prices to increased consumption of secondary pine residuals by Enviva Cottondale. Specifically, consumption of secondary pine residuals by Enviva Cottondale more than doubled from roughly 213,000 metric tons in 2012 to nearly 490,000 metric tons in 2016, and this increased consumption of pine residuals coincided with a nearly 20% increase in the price of pine sawmill chips. However, increased consumption of residuals by the bioenergy sector was only one of several contributing factors that can be linked to the increase in pine sawmill chip prices. Increased consumption of pine residuals by the pulp/paper industry also contributed to higher pine sawmill chip prices. In addition, there is a strong linkage between pine sawmill chip prices and softwood lumber production. Specifically, the increase in softwood lumber production that begun in the early-to-mid-2010s consequently resulted in the increased production of secondary residuals, and the increased availability of this lower-cost material led to greater competition and ultimately higher pine residual prices.

A reduction in growing stock timber?

No. From 2008 (the year Enviva Cottondale commenced production) up until Hurricane Michael struck in late-2018, total growing stock inventory increased an average of 1.8% per year (+19% total) in the Cottondale catchment area. Specifically, inventories of pine sawtimber and pine chip-n-saw increased 58% and 28%, respectively, while pine pulpwood (PPW) inventory decreased 4% over this same period.

However, note that the decrease in pine pulpwood inventory from 2008-2018 was not due to increased demand from bioenergy or increased harvesting above the sustainable yield capacity of the forest area, as annual growth of pine pulpwood exceeded annual removals every year throughout this period. Rather, this slight decrease in PPW inventory levels is more a reflection of the aging of the catchment area forest and the movement of stands classified as pulpwood to stands classified as chip-n-saw.

A reduction in the sequestration rate of carbon?

No. US Forest Service (USFS) data shows the average annual growth rate of total growing stock timber in the Cottondale catchment area decreased from 5.9% in 2008 to 5.2% in 2020, suggesting that the sequestration rate of carbon also declined slightly over this period. However, there is little evidence to suggest that increased demand attributed to bioenergy is responsible for this change.

The reduction in overall growth rate (and therefore reduction in the sequestration rate of carbon) is more a reflection of the aging of the catchment area forest. Specifically, growth rates decline as timber ages, and this is exactly what USFS data shows in the Cottondale catchment area, with the average age of growing stock timber increasing from less than 44 years of age in 2008 to nearly 46 years of age in 2020.

An increase in harvesting above the sustainable yield capacity of the forest area?

No. Growth-to-removals (G:R) ratios, which compare annual timber growth to annual timber removals, provides a measure of market demand relative to supply as well as a gauge of market sustainability. In 2020, the latest available, the G:R ratio for pine pulpwood (PPW), the predominant timber product utilized by the bioenergy sector, equaled 1.26 (recall that a value greater than 1.0 indicates sustainable harvest levels).

Note, however, that the PPW G:R ratio averaged 1.57 in the catchment area from 2013-2017 before falling to 1.20 in 2018 and averaging 1.27 since. This notable drop in 2018 was due to a nearly 35% increase in PPW removals (due to Hurricane Michael). It’s also important to note that while annual removals have moved back in line with pre-Michael levels since 2019, this lower PPW G:R ratio is likely reflective of the new norm (at least over the midterm). Hurricane Michael destroyed an estimated 22% of total pine pulpwood inventory in the Cottondale catchment area, and this loss in inventory will be reflected in reduced growth until the destroyed forests regenerate. However, in spite of this loss, adequate PPW inventory levels still remain and sustainable market conditions are expected to persist moving forward.

Timber growing stock inventory

Neutral. According to USFS data, inventories of pine pulpwood (PPW) decreased 25% in the catchment area from 2008-2020. However, this substantial decrease was due to Hurricane Michael, which destroyed nearly 520,000 hectares of catchment area timberland when it hit the Florida panhandle in late-2018. Prior to this event occurring, PPW inventory levels had held relatively steady, decreasing slightly but averaging 47.2 million m3 in the catchment area from 2008-2018. However, the destruction caused by Hurricane Michael resulted in the immediate loss of more than 10.3 million m3 of PPW inventory, or a 22% decrease compared to pre-hurricane levels.

Moreover, the slight decrease in PPW inventory levels that did occur from 2008-2018 was not due to increased demand from bioenergy. Typically, a reduction in inventory is linked to harvest levels above the sustainable yield capacity of the forest area, but in the Cottondale catchment area, annual growth of PPW exceeded annual removals every year throughout this period. Ultimately, the decrease in PPW inventory from 2008-2018 can be more closely linked to decreased pine sawtimber production beginning in the early to mid-2000s. Specifically, annual removals of pine sawtimber decreased 28% from 2003-2014, and the reduction in harvest levels over this period translated to a reduction in newly-re-established pine stands and ultimately the slight reduction in PPW inventory levels that occurred in the mid-to-late 2010s.

Timber growth rates

Neutral. Overall, timber growth rates declined slightly in the catchment area from 2008 (the year Enviva Cottondale commenced operations) through 2020. However, this decrease in timber growth rates was not due to increased demand attributed to bioenergy but rather to the aging of the catchment area forest. Specifically, USFS data shows the average age timber inventory in the Cottondale catchment area increased from an estimated 43.6 years of age in 2008 to 45.7 years of age in 2020.

Forest area

Positive. In the Enviva Cottondale catchment area, total forest area (i.e. timberland) increased more than 55,100 hectares (+1.9%) from 2008 through 2020, and this increase can be linked to several factors, including increases in softwood pulpwood demand (from both bioenergy and other sources) as well as conversion from farmland.

Specifically, the more than 55,100-hectare increase in catchment area timberland from 2008-2020 coincided with a 1.1-million metric ton increase in annual softwood pulpwood demand (roughly half of which was attributed to bioenergy). While statistical analysis identified moderately strong positive relationships between timberland area and both softwood biomass demand and non-bioenergy-related softwood pulpwood demand, a strong positive correlation was found between timberland and total softwood pulpwood demand – suggesting that the increases in timberland since 2008 can be attributed, in part, to the increase in total softwood pulpwood demand (from both bioenergy and other sources).

The more than 55,100-hectare increase timberland from 2008-2020 also coincided with a roughly 75,000-hectare decrease in farmland (i.e. cropland, woodland, and pastureland) over this period. Specifically, the catchment area experienced a roughly 31,800-hectare loss in cropland, 8,900-hectare loss in pastureland, and 34,300-hectare loss in woodland from 2008-2020. Furthermore, statistical analysis confirmed this inverse relationship, identifying a strong negative correlation between timberland and farmland in the Cottondale catchment area.

Wood prices

Negative / Positive. Total softwood pulpwood demand attributed to bioenergy in the Cottondale catchment area increased from zero tons in 2007 (the year prior to Enviva Cottondale’s startup) to over 1.0 million metric tons in 2013. Over this same period, the price of delivered pine pulpwood (PPW) – the predominant roundwood product utilized by Enviva Cottondale for wood pellet production – increased 42% (from $21.06 per ton in 2007 to $29.82 per ton in 2013).

However, the apparent link between increased softwood biomass demand and increased delivered PPW price is only loosely supported by statistical analysis, which identified a relatively weak positive relationship between these two variables. Furthermore, delivered PPW price has remained nearly unchanged in the catchment area since 2013, despite softwood biomass demand declining and averaging roughly 577,000 metric tons per year since 2016. (Note that the roughly 410,000-metric ton decrease in softwood biomass demand from 2013-2020 was offset by a roughly 455,000-metric ton increase in softwood pulpwood demand from other sources). Ultimately, the increase in delivered PPW prices in the catchment area can be linked to increased demand for softwood pulpwood from all sources, and roughly half of the 1.2-million metric ton increase in softwood pulpwood demand since 2007 can be attributed to bioenergy.

However, it’s also important to note that the increase in bioenergy-related wood demand has been a positive for forest landowners in the Enviva Cottondale catchment area. Not only has bioenergy provided an additional outlet for pulpwood in this market, but the increase in delivered PPW price resulting from increased softwood pulpwood demand from bioenergy has transferred through to landowners in the form of higher PPW stumpage prices. Specifically, over the six years prior to Enviva Cottondale’s startup, PPW stumpage price – the price paid to landowners – averaged roughly $7.40 per ton in the Cottondale catchment area. However, since 2010, PPW stumpage prices have averaged more than $11.15 per ton, representing a more than 50% increase compared to pre-mill startup levels.

Markets for solid wood products

Positive. In the Enviva Cottondale catchment area, demand for softwood sawlogs used to produce lumber and other solid wood products increased an estimated 23% from 2008-2020. This increase in softwood lumber production has consequentially resulted in an increase in sawmill residuals (i.e. chips, sawdust, and shavings) – by-products of the sawmilling process and materials utilized by Enviva Cottondale to produce wood pellets.

Specifically, softwood sawlog demand has increased more than 16% in the catchment area since 2014, and this increase in demand has coincided with a nearly 60% increase in pine residual purchases by Enviva Cottondale. (Note that pine residuals constituted 25% of total raw material purchases by Enviva Cottondale in 2014 but 41% of total raw material purchases in 2020). So, not only has Enviva Cottondale benefited from the greater availability of this sawmill by-product, but lumber producers have also benefited, as Enviva Cottondale has provided an additional outlet for these producers and their by-products.

Read the full report: Enviva Cottondale pellet plant catchment area analysis

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 can be found here

At the heart of the energy transition

Tree nursery in Mississippi

Will Gardiner opened the second day of the Chatham House Energy Transitions conference. Watch his keynote address below or scroll down the page to read his speech in full.

The energy transition is central to our purpose of enabling a zero carbon, lower cost energy future.

Drax has been at the heart of Britain’s energy system for decades. And we have played a key role in the decarbonisation of the power sector: Drax Power Station in Selby, North Yorkshire, is the UK’s largest power station and Europe’s largest decarbonisation project. Cruachan, our Scottish Pumped Storage facility is a key complement to Britain’s ever increasing supply of offshore wind.

Our transition from coal to biomass has allowed us to reduce our greenhouse gas emissions by over 80% while providing clean and flexible energy to millions of homes and businesses across the UK. This month saw the end of commercial coal generation at Drax power station – a milestone in the history of our company and of the UK economy, too.

But the scale of the climate crisis means that we cannot stop here.

Which is why we have committed to a world-leading ambition to be carbon negative by 2030.

We will achieve this by making a transformational investment in bioenergy with CCS, or BECCS, which will enable us to permanently remove carbon emissions from the atmosphere while continuing to supply the renewable electricity that millions of British homes and businesses depend upon.

Water outlet into Loch Awe from Cruachan Power Station

Water outlet into Loch Awe from Cruachan Power Station

Today, we are pioneering BECCS at Drax Power Station as part of the Zero Carbon Humber Cluster, a coalition of diverse businesses with one ambition: to create the world’s first net zero emissions industrial cluster.

The benefits are enormous

BECCS is a vital technology in the fight against climate change. Expert bodies such as the Climate Change Committee here in the UK and the IPCC at a global level are clear that we need negative emissions technologies including BECCS to reach net zero, and BECCS is central to the UK and Europe’s decarbonisation plans.

As the world’s largest, and most experienced, generator and supplier of sustainable bioenergy there is no better place to pioneer BECCS than at Drax. The economic, social and environmental benefits are enormous.

BECCS at Drax will permanently remove millions of tonnes of carbon from the atmosphere and help heavy industry in the UK’s largest emitting area decarbonise quickly and cost effectively;

It will enable the creation of tens of thousands of green jobs in the North of England, levelling up the economy and delivering a green recovery from the Covid crisis;

And it will put the UK at the forefront of global efforts to develop carbon removal technology in this, the year that we host COP26 in Glasgow.

The scale of the climate crisis means that we cannot stop here.

A proven technology

We know that BECCS works and that the technology is available now. Looking at cost projections from the CCC, we also know that it is the best value negative emissions technology.

Engineer at BECCS pilot project within Drax Power Station

Engineer at BECCS pilot project within Drax Power Station

We have already successfully run two BECCS pilots at the power station. In 2019 we demonstrated that we can capture CO2 from a 100% biomass feedstock. And in 2020, we began a second pilot working with Mitsubishi Heavy Industries to further enhance the potential for delivering negative emissions.

We aim to deploy BECCS at scale by 2027. To that end, earlier this month, we kickstarted the planning process for our proposals to build our first BECCS units, marking a major milestone in the project and putting us in a position to commence building BECCS as soon as 2024.

The support we need

Drax Power Station has a proud history of transformation. And today we are making rapid progress in further decarbonising our operations and making bold commitments about our future.

The core of our successful decarbonisation has been a close partnership with government. And it is this partnership that will make BECCS a reality and enable the multiple benefits that come with it. An effective negative emissions policy and regulatory framework from government will enable further investments from companies such as Drax.

We believe it is possible for such a policy framework to emerge in the coming months.

With COP26 later this year, making that policy commitment will allow us to accelerate our own decarbonisation journey and support the industries of the future here in the UK.

BECCS in context

But we know that there is no silver bullet solution to tackling climate change.

Negative emissions technologies such as BECCS will be needed alongside others, for example more renewables, electric vehicles, energy storage, energy efficiency and hydrogen.

BECCS will enable us to permanently remove carbon emissions from the atmosphere while continuing to supply the renewable electricity that millions of British homes and businesses depend upon.

BECCS complements – and does not – and should not – substitute for ambitious decarbonisation plans. Technologies such as BECCS have a clear and unique role to play by helping harder to abate sectors such as heavy industry, aviation and agriculture – decarbonise.

This is critically important if we are to meet our legally binding 2050 net zero target. The CCC estimates that 51m tonnes of CO2 will need to be captured via BECCS to meet net zero.

Sustainability at our core

We know that BECCS can only make a meaningful contribution to tackling climate change if the bioenergy is sustainably sourced. This has been fundamental to Drax’s transition from coal to biomass, and it remains fundamental as we progress our plans for BECCS.

Infographic showing how BECCS removes carbon from the atmosphere

Biomass, as the UK Government has stated, is one of our most valuable tools for reaching net zero emissions. So we need the right framework to ensure it is sourced sustainably.

As the world’s largest bioenergy producer and generator, we recognise our responsibility to be the world leaders in sustainability, too.

At Drax, we have invested in world leading policies, tools and expertise to ensure that our biomass is sustainably sourced. We go beyond regulatory compliance and have set up an Independent Advisory Board, Chaired by the UK Government’s former Chief Scientific Advisor, to help us and challenge us on sustainable biomass and its role in Drax’s transition to net zero.

front cover of 'Responsible sourcing' PDF

[click to read]

Thanks to our independent catchment area analyses, we know more about the forests we source from than ever before. We know and can demonstrate how demand for biomass can support healthy forests. For example, in the South East US where Drax sources most of its biomass, there is more than double the carbon stored in forests than there was 50 years ago.

A partnership with our stakeholders

The purpose of today’s session is to discuss all these issues and more. Our aim is clear: to enable a successful energy transition.

At Drax we stand ready to invest hundreds of millions of pounds to scale up BECCS technology;

To put the UK at the forefront of global efforts to reach net zero emissions;

And to help create tens of thousands of green jobs in the North of England.

But I want your help in making BECCS as sustainable and successful as it can be.

We know and can demonstrate how demand for biomass can support healthy forests.

Thank you very much for listening and I wish you a good and constructive session tackling this critical global challenge.

Will Gardiner delivered this keynote address at Energy Transitions 2021.

The video of Will’s speech can be watched in full here and with subtitles here.

Proposed Acquisition of Pinnacle Renewable Energy Inc. – a major international supplier of sustainable biomass

This announcement contains inside information

RNS Number: 2805O
Drax Group PLC
(“Drax”, “the Group”, “Drax Group”, “the Company”; Symbol: DRX)

Drax is pleased to announce that it has signed an agreement (the “Acquisition Agreement”) with Pinnacle Renewable Energy Inc. (PL.TO) (“Pinnacle”), providing for the acquisition by Drax Canadian Holdings Inc., an indirect, wholly-owned subsidiary of Drax, of the entire issued share capital of Pinnacle (the “Acquisition”). The Acquisition will be implemented by way of a statutory plan of arrangement in accordance with the laws of the Province of British Columbia, Canada, at a price of C$11.30 per share (representing a premium of 13% based on the closing market price as at 5 February of C$10.04 per share and valuing the fully diluted equity of Pinnacle at C$385 million (£226 million(1)), with an implied enterprise value of C$741 million, including C$356 million of net debt(2)). The Acquisition, which remains subject to Drax and Pinnacle shareholder approval, court approval, regulatory approvals and the satisfaction of certain other customary conditions, has been unanimously recommended by the board of Pinnacle and has the full support of Pinnacle’s major shareholder, affiliates of ONCAP (which, together hold shares representing approximately 31% of Pinnacle’s shares as at 5 February 2021). Completion is expected to occur in the second or third quarter of 2021.

The Board believes that the Acquisition advances Drax’s biomass strategy by more than doubling its biomass production capacity, significantly reducing its cost of biomass production and adding a major biomass supply business underpinned by long-term contracts with high-quality Asian and European counterparties. The Acquisition positions Drax as the world’s leading sustainable biomass generation and supply business alongside the continued development of Drax’s ambition to be a carbon negative company by 2030, using Bioenergy Carbon Capture and Storage (BECCS).

Highlights

  • Compelling opportunity to advance Drax biomass strategy
    • Adds 2.9 million tonnes of biomass production capacity
    • Significantly reduces Drax average cost of production(3)
  • Increased global reach and presence in third-party markets
    • C$6.7 billion of contracted sales to counterparties in Asia and Europe
    • 99% of capacity contracted through to 2026, significant volumes contracted post 2027
  • Strong return on investment
    • Cash generative with 2022 EBITDA consensus of C$99 million
    • Expected returns significantly ahead of Drax’s WACC
    • Funded from cash and existing agreements
  • Reinforces sustainable and growing dividend

The world’s leading sustainable biomass generation and supply business

  • Drax and Pinnacle combined
    • 17 pellets plants, three major fibre baskets, four deep water ports
    • 4.9Mt capacity from 2022 – 2.9Mt available for self-supply
    • 2.6GW of renewable biomass generation, with potential for BECCS
  • Global growth opportunities for sustainable biomass

Commenting on today’s announcement Will Gardiner, Chief Executive Officer of Drax, said:

“I am excited about this deal which positions Drax as the world’s leading sustainable biomass generation and supply business, progressing our strategy to increase our self-supply, reduce our biomass production cost and create a long-term future for sustainable biomass.

Drax Group CEO Will Gardiner

Drax Group CEO Will Gardiner in the control room at Drax Power Station [Click to view/download]

“We expect to benefit greatly from Pinnacle’s operational and commercial expertise, and I am looking forward to what we can achieve together.

“It will pave the way for our plans to use Bioenergy with Carbon Capture and Storage (BECCS), and become a carbon negative company by 2030 – permanently removing millions of tonnes of carbon dioxide from the atmosphere each year. Negative emissions from BECCS are vital if we are to address the global climate emergency whilst also providing renewable electricity needed in a net zero economy, supporting jobs and clean growth in a post-COVID recovery.”

Duncan Davies, Chief Executive Officer of Pinnacle, said:

“Pinnacle’s Board of Directors has unanimously determined that the transaction represents the best course of action for the company and its shareholders. On closing, the transaction will deliver immediate, significant and certain cash value to our shareholders. At the same time, the combination of Pinnacle and Drax will create a global leader in sustainable biomass with the vision, technical expertise and financial strength to help meet the growing demand for renewable energy products, which is exciting for our employees, customers and others around the world.”

Drax’s sustainable biomass strategy

Sustainable biomass has an important role to play in global energy markets as a flexible and sustainable source of renewable energy, as well as having the potential to deliver negative emissions. Drax believes that the Acquisition accelerates the Group’s strategic objectives to increase its available self-supply of sustainable biomass to five million tonnes per annum (Drax currently operates 1.6 million tonnes of capacity with 0.4 million tonnes in development) and reduce the cost of biomass to £50/MWh(4) by 2027. Through the delivery of these strategic objectives Drax aims to create a long-term future for sustainable biomass, including third-party supply, BECCS and merchant biomass generation.

Employee at Morehouse BioEnergy in Louisiana

Employee at Morehouse BioEnergy in Louisiana

The Group’s enlarged supply chain will have access to 4.9 million tonnes of operational capacity from 2022. Of this total, 2.9 million tonnes are available for Drax’s self-supply requirements in 2022 (increasing to 3.4 million tonnes in 2027). Drax aims to increase the level of third-party sales and further expand its capacity to meet its target of five million tonnes of self-supply by 2027.

Drax believes that the Acquisition is highly complementary to the Group’s other long-term strategic options for biomass. Once optimised, the enlarged group’s biomass supply chain will support Drax’s own generation requirements, including the potential development of BECCS, whilst also serving the growing biomass markets in Europe and Asia via long-term off-take agreements.

A major producer and supplier of good-quality, low-cost sustainable biomass

Pinnacle, which is listed on the Toronto Stock Exchange, operates 2.5 million tonnes of biomass capacity at sites in Western Canada and the Southeastern US, with a further 0.4 million tonnes of capacity in development (commissioning in 2021). Investment in this new capacity is expected to be substantially complete in the first half of 2021. Once the new capacity is commissioned, Pinnacle’s nameplate production capacity is expected to increase to 2.9 million tonnes per annum.

Pinnacle has ownership of c.80% of this nameplate capacity, with the remaining c.20% co-owned with its forestry industry joint venture partners, ensuring strong commercial relationships and shared interests in security of supply. Pinnacle has sales and marketing rights to 100% of the output from all sites.

Pinnacle is a key supplier of wood pellets for Drax and other third parties in Asia and Europe, with C$6.7 billion of contracted third-party sales (including sales to Drax).

Westview terminal, Canada

Wood pellets loaded onto vessel at Westview Terminal, British Columbia

Through scale, operational efficiency and low-cost fibre sourcing, Pinnacle is currently produces biomass at a lower cost than Drax, with a like-for-like 2019 production cost of US$124/tonne(3), compared to Drax’s 2019 production cost of US$161/tonne(3). The pro forma 2019 production cost for the combined business is US$141/tonne.

Pinnacle’s lower cost partially reflects the use of high levels of low-cost sawmill residues. British Columbia has a large and well-established commercial forestry industry, which has in recent years seen increased harvest levels, in part associated with management of a pine beetle infestation, producing good levels of residue material availability for the production of biomass. This infestation has now run its course and alongside other influences on the forest landscape, including wild-fire, is resulting in a reduction in the annual harvest and sawmill closures. The industry is adjusting to this with some production curtailment as well as developing approaches to fibre recovery and use which is expected to result in some increase in fibre costs.

Since 2017, the Sustainable Biomass Program has conducted annual audits of each of Pinnacle’s operational sites, allowing Drax to ensure, through its diligence, that the material that it purchases from Pinnacle is in line with its sustainability standards.

Drax is committed to ensuring best practice in health and safety, operational efficiency and sustainability across the enlarged group and intends to invest accordingly to deliver this outcome.

Drax is committed to ensuring that its biomass sources are compliant with Drax’s well-established responsible sourcing policy and Drax expects to invest in, adapt and develop sourcing practices to ensure compliance with Drax’s policies to deliver both Drax’s biomass strategy and positive forest outcomes.

A large and geographically diversified asset base

Pinnacle has ownership interests in ten operational plants and one in development (commissioning 2021), six of which are operated through joint venture arrangements, providing access to nameplate production capacity of 2.9 million tonnes per annum.

Seven of Pinnacle’s sites are in British Columbia (1.6 million tonne nameplate capacity) and two are in Alberta (0.6 million tonne nameplate capacity). All of these sites have rail lines to ports at either Prince Rupert or Vancouver, both accessing the Pacific Ocean, providing routes to Asian and European markets.

Pinnacle also operates a US hub at Aliceville, Alabama (0.3 million tonne nameplate capacity) and is developing a second site in Demopolis, Alabama (0.4 million tonne nameplate capacity), which Pinnacle expects to commission in 2021. Pinnacle’s total operational and development nameplate capacity in the US is 0.7 million tonnes.

Pinnacle’s US sites are close to Drax’s existing operations in the Southeastern US and will utilise river barges to access the Port of Mobile and barge-to-ship loading, reducing fixed port storage costs.

Forest in LaSalle catchment area

Working forest in LaSalle BioEnergy catchment area, Louisiana

All production sites are located in areas with access to fibre and are able to operate with a range of biomass material from existing commercial forestry activities, including sawmill residues, pre-commercial thinnings and low-grade wood. Combined with a geographic spread of production capacity and access to three separate export facilities, Pinnacle benefits from operational and sourcing flexibility, further enhancing Drax’s security of supply.

Further information is set out in Appendix 1 to this announcement.

Long-term biomass revenues with access to Asian and European markets

Pinnacle has contracted sales of C$6.7 billion, with high-quality Asian and European counterparties (including Drax). This equates to 99% of its current production capacity contracted to third parties through 2026 and a significant volume contracted in 2027 and beyond, providing long-term high-quality revenues.

Vessel carrying biomass pellets at Westview Terminal, British Columbia

Pinnacle has been supplying biomass to Europe since 2004. The location of the majority of Pinnacle’s production capacity in Western Canada, with access to the Pacific Ocean, provides a strong position from which to serve the growing demand for biomass in Asian markets. In 2018 and 2019, Pinnacle entered into 12 new long-term contracts in Japan and South Korea, totalling over 1.3 million tonnes per annum, valued at C$4.6 billion, with most contracts commencing between 2021 and 2023. The average contract duration is nine years, with certain contracts extending significantly beyond this point. Contracts typically operate on a take-or-pay basis.

Global growth opportunities for sustainable biomass

The global biomass wood pellet market has a broad range of providers that are expected to expand their production capacity, including operators such as Enviva, Graanul Invest, Pinnacle, An Viet Phat, Fram and SY Energy.

The market for biomass wood pellets for renewable generation in Europe and Asia is expected to grow in the current decade, principally driven by Asian demand(5). Drax believes that increasingly ambitious global decarbonisation targets, the need for negative emissions and an improved understanding of the role that sustainably sourced biomass can play will result in continued robust demand.

Aerial photo of biomass storage domes, Drax Power Station

Train pulling biomass wagons, storage domes and wood pellet conveyor system Drax Power Station, North Yorkshire

As a vertically integrated producer and consumer of sustainable biomass Drax is differentiated from its peers and well positioned to deliver supply chain efficiencies and an expanded range of sustainable biomass materials for own-use and third-party sales.

Through its expanding lower cost supply chain, expertise in biomass generation and enhanced global footprint, Drax believes that there will be opportunities to work with other companies and countries in developing their own biomass-enabled decarbonisation strategies.

Strong return on investment

The Acquisition is expected to be cash generative and represent an attractive opportunity to create significant value for shareholders, with expected returns significantly in excess of the Group’s weighted average cost of capital.

The addition of long-term contracts with high-quality counterparties in growing international biomass markets will reduce the Group’s relative exposure to commodity prices, in line with the Group’s objective to improve earnings quality and visibility.

In total, the Acquisition increases access to lower cost biomass by a further 2.9 million tonnes after the commissioning of the Demopolis plant in 2021. The price paid for this capacity is consistent with the previously outlined strategy to invest in the region of c.£600 million to deliver Drax’s plans for five million tonnes of self-supply capacity and a biomass cost of £50/MWh by 2027.

For the year ended 27 December 2019, Pinnacle generated Adjusted EBITDA(6) of C$47 million from pellet sales of 1.7 million tonnes.

Pinnacle’s 2019 performance was impacted by fire at its Entwistle plant, reduced rail access due to rail industrial action and weather disrupted forestry activity. At the same time Pinnacle experienced regional Canadian sawmill closures, resulting in some reduction in sawmill residues and an increase in provincial fibre prices.

Fibre diversification and the development of a second hub in the Southeastern US is expected to partially mitigate the risk of fibre price rises.

Taking these factors into account, alongside the commissioning of new capacity and the commencement of Asian supply contracts, Pinnacle’s 2022 consensus EBITDA is C$99 million, increasing to C$126 million in 2023 (Bloomberg).

The Acquisition strengthens the Group’s ability to pay a sustainable and growing dividend. Drax does not expect the Acquisition to have any impact on its expectations for the final dividend payment for 2020.

Financing the Acquisition

The Acquisition is expected to be funded from cash and existing agreements. On 15 December 2020 the Group issued a trading update which noted cash and total committed liquidity of £643 million at 30 November 2020. Following the completion, on 31 January 2021, of the sale of four gas power stations, previously announced on 15 December 2020, the Group received cash of £188 million, being the agreed purchase price consideration of £164 million and £24 million of customary working capital adjustments.

Net debt to Adjusted EBITDA(7) in 2021 is expected to be above Drax’s long-term target of around 2 times immediately after completion of the Acquisition but is expected to return to around this level by the end of 2022.

Management of foreign exchange exposure

The Acquisition price will be paid in Canadian dollars. Pinnacle’s existing contracts with Drax and third parties are denominated in Canadian and US dollars and Drax expects to manage any exposure within its foreign exchange processes.

Drax’s policy is to hedge its foreign currency exposure on contracted biomass volumes over a rolling five-year period. This has given rise to an average foreign exchange rate hedge around 1.40 (US$/GBP£).

Sustainable sourcing

Sustainably sourced biomass is an important part of UK and European renewable energy policy. The renewable status of sustainably sourced biomass is based on well-established scientific principles set out by the Intergovernmental Panel on Climate Change and reflected in the European Union’s (EU) second Renewable Energy Directive and the UK Renewables Obligation.

Drax maintains a rigorous approach to biomass sustainability, ensuring the wood fibre it uses is fully compliant with the UK’s mandatory standards as well as those of the EU.

British Columbia, near Barriere, North Thompson River, aspen trees, dead pine trees behind infected with pine bark beetle (aka mountain pine beetle)

Dead pine trees in background, infected with mountain pine beetle, British Columbia

Drax recognises that the forest landscape in British Columbia and Alberta is different to commercially managed forests in the Southeastern US. Working in partnership with eNGO Earthworm, Drax has a good understanding of the considerations associated with sourcing residues from harvesting of primary forest and the particular characteristics of the forests in British Columbia and Alberta. In line with its responsible sourcing policy, Drax will work closely with eNGO partners, Indigenous First Nation communities and other stakeholders, and invest to deliver good environmental, social and climate outcomes in Pinnacle’s sourcing areas.

Operational efficiencies, improvements and savings

The strong financial returns associated with the Acquisition are not dependent on synergy benefits, but the Group has identified areas for potential operational improvements and efficiencies, and opportunities to invest across the supply chain to achieve consistent standards and improve outputs across the enlarged group.

Portfolio optimisation

Drax aims to leverage Pinnacle’s trading capability across its expanded portfolio. Drax believes that the enlarged supply chain will provide greater opportunities to optimise the supply of biomass from its own assets and third-party suppliers.

With existing plans to widen of the Group’s sustainable biomass fuel mix to include a wider range of lower cost sustainable biomass materials, Drax expects to create further opportunities to optimise fuel cargos for own use and third-party supply.

Logistics optimisation

Drax believes that the transport and shipping requirements of the enlarged group will provide greater opportunities to optimise logistics, with delivery of cargos to a counterparty’s closest port, reducing distance, time, carbon footprint and cost.

Enhanced security of supply

Control of Drax’s biomass supply chain, with geographically diverse production and export facilities, is expected to enhance security of supply, further mitigating the risk of supply interruptions thereby resulting in improved reliability and a reduced risk of supply interruption.

Combined expertise

Drax believes that there will be opportunities to share best practice and drive improved production performance across the enlarged group by leveraging combined expertise in the production of good-quality, low-cost pellets across the enlarged supply chain.

Drax also expects to leverage Pinnacle’s experience in developing and managing third-party off-take agreements alongside its existing commercial and trading capabilities to develop new agreements for supply to third-parties.

Stronger counterparty credit

Drax has a stronger credit rating, which could enable Pinnacle to develop its supply capability and contracts in Asian and European markets beyond its current position.

Reduced cost of debt

Drax’s average cost of debt is lower than Pinnacle’s giving rise to potential future savings.

Corporate cost savings

Drax expects to derive typical corporate cost savings associated with the Acquisition and delisting from the Toronto Stock Exchange.

Shareholder approvals

The Acquisition constitutes a Class 1 transaction under the Listing Rules. As a consequence, completion of the Acquisition is conditional on the Acquisition receiving the approval of Drax shareholders. A combined shareholder circular and notice of general meeting will be posted to shareholders as soon as practicable.

Among other things, the Acquisition is also conditional upon the approval of the Acquisition by Pinnacle’s shareholders, the approval of the Supreme Court of British Columbia, certain antitrust and other regulatory approvals other customary conditions.

A summary of the terms of the Acquisition Agreement is set out in Appendix 2 to this announcement.

Drax’s board has unanimously recommended that Drax’s shareholders vote in favour of the Acquisition, as each of the Drax directors that hold shares in Drax shall do in respect of their own beneficial holdings of Drax’s shares, representing approximately 0.17 per cent. of the existing share capital of Drax as at 5 February 2021, being the last business day prior to the date of this announcement.

Pinnacle’s board has unanimously recommended that Pinnacle’s shareholders vote in favour of the Acquisition at the Pinnacle General Meeting, as the Pinnacle directors (and certain current and former members of Pinnacle management that hold shares in Pinnacle) shall do in respect of their own beneficial holdings of Pinnacle’s shares, representing approximately 4.75 per cent. of the existing share capital of Pinnacle as at 5 February 2021, being the last business day prior to the date of this announcement.

In addition to the irrevocable undertakings from Pinnacle directors described above, Drax has also received an irrevocable undertaking from affiliates of ONCAP (which, together, hold shares representing approximately 31% of Pinnacle’s shares as at 5 February 2021 (being the last business day prior to the date of this announcement)) to vote in favour of the Acquisition at Pinnacle’s General Meeting.

Other

Drax issued a trading update on 15 December 2020 outlining its expectations for 2020 and expects to announce its full year results for the year ended 31 December 2020 on 25 February 2021.

Enquiries:

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

Media:

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

Royal Bank of Canada (Financial Adviser and Joint Corporate Broker):

+44 (0) 20 7653 4000
Peter Buzzi
Mark Rushton
Evgeni Jordanov
Jonathan Hardy
Jack Wood

Acquisition presentation meeting and webcast arrangements

Management will host a webcast for analysts and investors at 9:30am (UK Time), Monday 8 February 2021.

The webcast can be accessed remotely via a live webcast link, as detailed below. After the meeting, the webcast recording will be made available and access details of this recording are also set out below.

A copy of the presentation will be made available from 7am (UK time) on 8 February 2021 for download at: https://www.drax.com/investors/results-reports-agm/#investor-relations-presentations

Event Title:
Drax Group plc: Proposed Acquisition of Pinnacle Renewable Energy Inc

Event Date:
9:30am (UK time), Monday 08 February 2021

Webcast Live Event Link:
https://secure.emincote.com/client/drax/drax010

Start Date:
9:30am (UK time), Monday 08 February 2021

Delete Date:
Monday 27 December 2021

Archive Link:
https://secure.emincote.com/client/drax/drax010

Important notice

The contents of this announcement have been prepared by and are the sole responsibility of Drax Group plc (the “Company”).

RBC Europe Limited (“RBC”), which is authorised by the Prudential Regulation Authority (the “PRA”) and regulated in the United Kingdom by the Financial Conduct Authority (“FCA”) and the PRA, is acting exclusively for the Company and for no one else in connection with the Acquisition, the content of this announcement and other matters described in this announcement and will not regard any other person as its clients in relation to the Acquisition, the content of this announcement and other matters described in this announcement and will not be responsible to anyone other than the Company for providing the protections afforded to its clients nor for providing advice to any other person in relation to the Acquisition, the content of this announcement or any other matters referred to in this announcement.

This announcement does not constitute or form part of any offer or invitation to sell or issue, or any solicitation of any offer to purchase or subscribe for, any shares in the Company or in any entity discussed herein, in any jurisdiction nor shall it or any part of it nor the fact of its distribution form the basis of, or be relied on in connection with, any contract commitment or investment decision in relation thereto nor does it constitute a recommendation regarding the securities of the Company or of any entity discussed herein.

RBC and its affiliates do not accept any responsibility or liability whatsoever and make no representations or warranties, express or implied, in relation to the contents of this announcement, including its accuracy, fairness, sufficient, completeness or verification or for any other statement made or purported to be made by it, or on its behalf, in connection with the Acquisition and nothing in this announcement is, or shall be relied upon as, a promise or representation in this respect, whether as to the past or the future. RBC and its respective affiliates accordingly disclaim to the fullest extent permitted by law all and any responsibility and liability whether arising in tort, contract or otherwise which it might otherwise be found to have in respect of this announcement or any such statement.

Certain statements in this announcement may be forward-looking. Any forward-looking statements reflect the Company’s current view with respect to future events and are subject to risks relating to future events and other risks, uncertainties and assumptions relating to the Company and its group’s and/or, following completion, the enlarged group’s business, results of operations, financial position, liquidity, prospects, growth, strategies, integration of the business organisations and achievement of anticipated combination benefits in a timely manner. Forward-looking statements speak only as of the date they are made. Although the Company believes that the expectations reflected in these forward looking statements are reasonable, it can give no assurance or guarantee that these expectations will prove to have been correct. Because these statements involve risks and uncertainties, actual results may differ materially from those expressed or implied by these forward looking statements.

Each of the Company, RBC and their respective affiliates expressly disclaim any obligation or undertaking to supplement, amend, update, review or revise any of the forward looking statements made herein, except as required by law.

You are advised to read this announcement and any circular (if and when published) in their entirety for a further discussion of the factors that could affect the Company and its group and/or, following completion, the enlarged group’s future performance. In light of these risks, uncertainties and assumptions, the events described in the forward-looking statements in this announcement may not occur.

Neither the content of the Company’s website (or any other website) nor any website accessible by hyperlinks on the Company’s website (or any other website) is incorporated in, or forms part of, this announcement.

Appendix 1

Pinnacle Production Capacity

PlantLocationStatusCommissioningNameplate Capacity (Mt)Pinnacle Ownership (%)
Williams LakeBC, CanadaOperational20040.2100%
HoustonBC, CanadaOperational20060.230%
ArmstrongBC, CanadaOperational20070.1100%
MeadowbankBC, CanadaOperational20080.2100%
Burns LakeBC, CanadaOperational20110.4100%
LavingtonBC, CanadaOperational20150.375%
SmithersBC, CanadaOperational20180.170%
EntwistleAlberta, CanadaOperational20180.4100%
AlicevilleAlabama, USAOperational20180.370%
High LevelAlberta, CanadaOperational20200.250%
DemopolisAlabama, USADevelopmentEst. 20210.470%
Total2.980%

Capacity by fibre basket in 2021

LocationNameplate Capacity (Mt)Pinnacle Ownership (%)
BC, Canada1.684%
Alberta, Canada0.683%
Alabama, USA0.370%
Total2.582%

Capacity by fibre basket in 2022

LocationNameplate Capacity (Mt)Pinnacle Ownership (%)
BC, Canada1.684%
Alberta, Canada0.683%
Alabama, USA0.763%
Total2.981%

Across its business Pinnacle employs 485 employees, principally in the operation of its assets.

Appendix 2

Principal terms of the Acquisition Agreement

The following is a summary of the principal terms of the Acquisition Agreement.

Parties and consideration

The Acquisition Agreement was entered into on 7 February 2021 between Drax, Drax Canadian Holdings Inc., (an indirect wholly-owned subsidiary of Drax) (“Bidco”) and Pinnacle. Pursuant to the Acquisition Agreement, Bidco has agreed to acquire all of the issued and outstanding shares in Pinnacle and, immediately following completion, Pinnacle will be an indirect wholly-owned subsidiary of Drax. The Acquisition will be implemented by way of a statutory plan of arrangement in accordance with the laws of the Province of British Columbia, Canada.

Conditions

Completion under the Acquisition Agreement is subject to, and can only occur upon satisfaction or waiver of, a number of conditions, including:

(a) the approval of the Acquisition by Drax shareholders who together represent a simple majority of votes cast at a meeting of Drax shareholders;

(b) the approval of the Acquisition by Pinnacle shareholders who together represent not less than two-thirds of votes cast at a meeting of Pinnacle shareholders;

(c) an interim order providing for, among other things, the calling and holding of a meeting of Pinnacle shareholders and a final order to approve the Arrangement, each having been granted by the Supreme Court of British Columbia;

(d) no material adverse effect having occurred in respect of Pinnacle;

(e) in the event that the Competition and Markets Authority (the “CMA”) has requested submission of a merger notice or opened a merger investigation, the CMA having issued a decision that the Acquisition will not be subject to a Phase 2 reference or the period for the CMA considering a merger notice has expired without a Phase 2 reference having been made;

(f) either the receipt of an advance ruling certificate or both the expiry, termination or waiver of the applicable waiting period under the Competition Act (Canada) and, unless waived by Drax, receipt of a no-action letter in respect of the Acquisition from the Commissioner of Competition;

(g) the expiry or early termination of any applicable waiting period (and any extension of such period) applicable to the Acquisition under the Hart-Scott-Rodino Antitrust Improvements Act of 1976 (US); and

(h) the receipt a third party consent

In addition, Drax has the unilateral right not to complete the Acquisition where registered Pinnacle shareholders representing more than five per cent. of the outstanding share capital of Pinnacle duly exercise their dissent rights.

If any of the conditions are not satisfied (or waived) by 7 September 2021, either party can terminate the Acquisition Agreement.

Non-solicitation

Prior to obtaining approval from their respective shareholders in relation to the Acquisition, each of Drax and Pinnacle are prohibited from soliciting from any third party any acquisition proposal (relating to 20 per cent. or more of their shares or their group’s assets). However, if prior to obtaining Drax shareholder approval, Drax receives an unsolicited bona fide proposal in respect of 50 per cent. or more of its shares or all or substantially all of the assets of the Drax group and which the Drax board considers would result in a transaction that is more favourable to Drax shareholders from a financial perspective than the Acquisition (a “Drax Superior Proposal”), it may engage in discussions in relation to such Drax Superior Proposal in accordance with the terms of the Acquisition Agreement. Similarly, if prior to obtaining Pinnacle shareholder approval, Pinnacle receives an unsolicited bona fide proposal in respect of 100 per cent. of its shares or all or substantially all of the assets of the Pinnacle group and which the Pinnacle board considers would result in a transaction that is more favourable to Pinnacle shareholders from a financial perspective than the Acquisition (a “Pinnacle Superior Proposal”), it may engage in discussions in relation to such proposal in accordance with the terms of the Acquisition Agreement.

Termination fees payable to Pinnacle

Drax has agreed to pay a break fee of C$25 million to Pinnacle if the Acquisition Agreement is terminated as a result of:

(a) the Drax board withholding, withdrawing or adversely modifying its recommendation that Drax shareholders approve the Acquisition;

(b) the Drax board authorising Drax to enter into any definitive agreement (other than a confidentiality agreement) in respect of a Drax Superior Proposal;

(c) the Drax board terminating the Acquisition Agreement in response to any intervening event that was not known to the Drax board as of the date of the Acquisition Agreement;

(d) Drax breaching its non-solicitation obligations set out in the Acquisition Agreement; or

(e) completion not occurring by 7 September 2021 or a failure to obtain Drax shareholder approval and, in each case, an acquisition of 50 per cent. of Drax’s shares or assets (subject to certain exceptions) is is made or announced prior to the Drax shareholder approval having been obtained and any such acquisition is consummated (or a definitive agreement is entered into in respect of the same) within 12 months of termination.

In addition, Drax has agreed to pay Pinnacle an expense fee of C$5 million in the event that the Acquisition Agreement is terminated as a result of a failure to obtain Drax shareholder approval. The expense fee shall not be payable in the event that the break fee is also payable.

Termination fees payable to Drax

Pinnacle has agreed to pay a break fee of C$12.5 million to Drax if the Acquisition Agreement is terminated as a result of:

(a) the Pinnacle board withholding, withdrawing or adversely modifying its recommendation that Drax shareholders approve the Acquisition;

(b) the Pinnacle board authorising Pinnacle to enter into any definitive agreement (other than a confidentiality agreement) in respect of a Pinnacle Superior Proposal;

(c) the Pinnacle board terminating the Acquisition Agreement in response to any intervening event that was not known to the Pinnacle board as of the date of the Acquisition Agreement;

(d) Pinnacle breaching its non-solicitation obligations set out in the Acquisition Agreement; or

(e) completion not occurring by 7 September 2021 or a failure to obtain Pinnacle shareholder approval and, in each case, an acquisition of 50 per cent. of Pinnacle’s shares or assets (subject to certain exceptions) is made or announced prior to the Drax shareholder approval having been obtained and any such acquisition is consummated (or a definitive agreement is entered into in respect of the same) within 12 months of termination.