Tag: sustainability

Full year results for the twelve months ended 31 December 2021

RNS Number : 6410C
Drax Group PLC
24 February 2022

Twelve months ended 31 December20212020
Key financial performance measures
Adjusted EBITDA (£ million) (1)(2)398412
Continuing operations378366
Discontinued operations – gas generation2046
Net debt (£ million) (3)1,044776
Adjusted basic EPS (pence) (1)26.529.6
Total dividend (pence per share)18.817.1
Total financial performance measures from continuing operations
Operating profit / (loss) (£ million)197(156)
Profit / (loss) before tax (£ million)122(235)

Will Gardiner, CEO of Drax Group, said:

Drax Group CEO Will Gardiner

Drax Group CEO Will Gardiner

“2021 was a transformational year for Drax as we became the world’s leading sustainable biomass generation and supply company, whilst continuing to invest in delivering positive outcomes for the climate, nature and people.

“Over the past ten years Drax has invested over £2 billion in renewable energy and has plans to invest a further £3 billion this decade, supporting the global transition to a low-carbon economy. Our investment has reduced our emissions from power generation by over 95% and we are the UK’s largest producer of renewable power by output. We are proud to be one of the lowest carbon intensity power generators in Europe – a significant transformation from being the largest coal power station in Western Europe.

“We have significantly advanced our plans for bioenergy with carbon capture and storage (BECCS) in the UK and globally. By 2030 we aim to deliver 12 million tonnes of negative emissions and lead the world in providing a critical technology which scientists agree is key to delivering the global transition to net zero.”

Financial highlights

  • Adjusted EBITDA £398 million (2020: £412 million)
  • Strong liquidity and balance sheet – £549 million of cash and committed facilities at 31 December 2021
    • Expect to be below 2x net debt to Adjusted EBITDA by the end of 2022
  • Total dividend – 10% increase to 18.8 pence per share (2020: 17.1 pence per share)
    • Proposed final dividend of 11.3 pence per share (2020: 10.3 pence per share)

Strategic highlights

  • Acquisition of Pinnacle Renewable Energy Inc. for C$385 million (£222 million) (enterprise value of C$796 million)
  • Sale of Combined Cycle Gas Turbine (CCGT) generation assets for £186 million
  • Development of the world’s leading sustainable biomass generation and supply company
    • Supply – 17 pellet plants and developments across three major fibre baskets, production capacity of c.5Mt pa
    • 22Mt (c.$4.5 billion) of long-term contracted sales to high-quality customers in Asia and Europe
    • 14Mt of own-use sales through 2026
    • Generation – 2.6GW of biomass generation – UK’s largest source of renewable power by output
  • Development of BECCS in UK
    • East Coast Cluster – selected as one of two priority carbon capture and storage clusters
    • Government – BECCS included in Net Zero Strategy and Interim Bioenergy Strategy
    • Drax Power Station – planning application started, technology partner selected and FEED study commenced

Strategic outlook – growth plans aligned with global low-carbon growth

  • To be a global leader in sustainable biomass
    • Targeting 8Mt pa of production capacity and 4Mt pa of biomass sales to third parties by 2030
  • To be a global leader in negative emissions
    • Targeting 12Mt pa of negative CO2 – UK and international BECCS
  • To be a UK leader in dispatchable, renewable generation
    • Key system support role for biomass and expansion of Cruachan Pumped Storage Power Station
  • All underpinned by continued focus on safety, sustainability and biomass cost reduction
  • Investments totalling £3bn in period to 2030, fully funded through cash generation
    • Pellet production, UK BECCS and Cruachan expansion

Future positive – people, nature, climate

  • CO2 – >95% reduction in generation emissions since 2012 – sale of CCGT generation assets and end of commercial coal in March 2021 and closure in September 2022 following fulfilment of Capacity Market agreements
  • Sustainable biomass sourcing
    • Science-based sustainability policy compliant with current UK and EU law on sustainable biomass
    • Biomass produced using sawmill and forest residuals, and low-grade roundwood, which often have few alternative markets and would otherwise be landfilled, burned or left to rot, releasing CO2 and other GHGs
    • Significant increase in sawmill residues used by Drax to produce pellets – 57% of total fibre (2020: 21%)
    • 100% of woody biomass produced by Drax verified against SBP, SFI, FSC®(4) or PEFC Chain of Custody certification with third-party supplier compliance primarily via SBP certification
    • Glasgow Declaration launched at COP26 to establish a world-wide industry standard on biomass sustainability
  • People – Diversity, Equity and Inclusion – female representation in the UK business increased to 36% (2020:34%)
  • Governance – two new North America based Non-Executive Directors – Kim Keating and Erika Peterman

Operational review

Pellet Production – acquisition of Pinnacle, capacity expansion and biomass cost reduction

  • Adjusted EBITDA (including Pinnacle since 13 April 2021) up 65% to £86 million (2020: £52 million)
    • Pellet production up 107% to 3.1Mt (2020: 1.5Mt), with 1.2Mt sales to third parties and increased own-use
    • Total $/t cost of production down 7% to $143/t(5) (2020: $153/t(5))
  • Developments in US southeast (2021-22) – addition of c.0.6Mt of new production capacity
    • Completion of LaSalle and Morehouse plant expansions
    • Commissioning of Demopolis and first satellite plant (Leola)
    • Commencement of construction of second satellite plant (Russellville)
  • Further opportunities for growth and cost reduction – increased production capacity, sales to third parties, continued operational efficiencies and improvement, wider range of sustainable biomass and technical innovation

Generation – dispatchable renewable generation and system support services

  • UK’s largest generator of renewable power by output – 12% of total
  • Adjusted EBITDA from discontinued CCGT generation assets £20 million (2020: £46 million)
  • Adjusted EBITDA from continuing operations £352 million (2020: £400 million)
    • Biomass – 5% increase in generation less major planned outage on CfD unit (successfully completed November 2021), higher cost from historic foreign exchange hedging and system charges
    • Pumped storage / hydro – good operational performance
    • Strong portfolio system support role (balancing mechanism, ancillary services and optimisation)
    • Limited role for coal in H2 at request of system operator
  • Ongoing cost reductions to support operating model for biomass generation at Drax Power Station from 2027
    • Reduction in fixed cost base – end of commercial coal operations March 2021, closure September 2022
    • Third biomass turbine upgrade, delivering improved thermal efficiency and lower maintenance cost
    • Trials to expand range of lower cost sustainable biomass – up to 35% blend achieved in test runs on one unit
  • As at 21 February 2022, Drax had 20.4TWh of power hedged between 2022 and 2024 on its ROC and hydro generation assets at £70.2/MWh, with a further 0.9TWh equivalent of gas sales (transacted for the purpose of accessing additional liquidity for forward sales from ROC units and highly correlated to forward power prices) plus additional sales under the CfD mechanism
Contracted power sales 21 February 2022202220232024
ROC (TWh(6))10.96.92.4
ROC (£ per MWh)70.070.070.6
Hydro (TWh)0.2--
Hydro (£ per MWh)90.9--
Gas hedges (TWh equivalent)(7)0.50.4
Pence per therm105101
CfD(6/8) typical annual output c.5TWh and current strike price £118.5/MWh

Customers – renewable power under long-term contracts to high-quality I&C customers and decarbonisation products

  • Adjusted EBITDA of £6 million inclusive of impact of mutualisation changes and Covid-19 (2020: £39 million loss)
  • Continued development of Industrial & Commercial (I&C) portfolio
    • Focusing on key sectors to increase sales to high-quality counterparties supporting generation route to market
    • Energy services to expand the Group’s system support capability and customer sustainability objectives
  • Rebranding of the Haven Power I&C business to Drax Energy Solutions
  • Closure of Oxford and Cardiff offices as part of Small & Medium-Size (SME) strategic review and continuing to evaluate options for SME portfolio to maximise value and align with strategy

Other financial information

  • Total operating profit from continuing operations of £197 million (2020: £156 million loss, including exceptional costs totalling £275 million principally in respect of the announced closure of coal operations)
  • Total profit after tax from continuing operations of £55 million including a £49 million non-cash charge from revaluing deferred tax balances following confirmation of UK corporation tax rate increases from 2023 (2020: loss of £195 million)
  • 2021 capital investment of £230 million (2020: £183 million) – continued investment in biomass strategy
  • 2022 expected capital investment of £230–250 million – £70-80 million maintenance, £20 million enhancements, £110-120 million strategic, (primarily biomass and BECCS), and £30 million other (primarily safety and systems)
    • Excludes any material investment in non-core Open Cycle Gas Turbine developments – continuing to evaluate options, including sale, but continue to invest as appropriate to fulfil obligations under the Capacity Market agreements and to maximise value from any sale. In the event of a sale Drax expects to recover any capital expenditure incurred during 2022, which could total up to £100 million
  • Group cost of debt below 3.5%
    • Refinancing of Canadian facilities (July 2021) with lower cost ESG facility following Pinnacle acquisition
  • Net debt of £1,044 million (31 December 2020: £776 million), including cash and cash equivalents of £317 million (31 December 2020: £290 million)
    • Expect net debt to Adjusted EBITDA below 2x by the end of 2022
Forward Looking Statements
This announcement may contain certain statements, expectations, statistics, projections and other information that are, or may be, forward-looking. The accuracy and completeness of all such statements, including, without limitation, statements regarding the future financial position, strategy, projected costs, plans, beliefs and objectives for the management of future operations of Drax Group plc (“Drax”) and its subsidiaries (the “Group”), are not warranted or guaranteed. By their nature, forward-looking statements involve risk and uncertainty because they relate to events and depend on circumstances that may occur in the future. Although Drax believes that the statements, expectations, statistics and projections and other information reflected in such statements are reasonable, they reflect the Company’s current view and no assurance can be given that they will prove to be correct. Such events and statements involve risks and uncertainties. Actual results and outcomes may differ materially from those expressed or implied by those forward-looking statements. There are a number of factors, many of which are beyond the control of the Group, which could cause actual results and developments to differ materially from those expressed or implied by such forward-looking statements. These include, but are not limited to, factors such as: future revenues being lower than expected; increasing competitive pressures in the industry; and/or general economic conditions or conditions affecting the relevant industry, both domestically and internationally, being less favourable than expected. We do not intend to publicly update or revise these projections or other forward-looking statements to reflect events or circumstances after the date hereof, and we do not assume any responsibility for doing so.

Results presentation and webcast arrangements

Management will host a webcast presentation for analysts and investors at 11:00am (UK Time) on Thursday 24 February 2022.

The presentation 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 7:00am (UK time) on Thursday 24 February 2022 for download at: https://www.drax.com/investors/announcements-events-reports/presentations/

Event Title: Drax Group plc: Full Year Results
Event Date: Thursday 24 February 2022
Event Time: 11:00am (UK time)
Webcast Live Event Link:  https://secure.emincote.com/client/drax/drax019
Conference call and pre-register Link: https://secure.emincote.com/client/drax/drax019/vip_connect
Start Date:  Thursday 24 February 2022
Delete Date:  Friday 24 February 2023
Archive Link:  https://secure.emincote.com/client/drax/drax019

 

For further information, please contact: [email protected]

View investor presentation 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

Global collaboration
is key to tackling
the climate crisis

Leaders from 40 countries are meeting today, albeit virtually, as part of President Joe Biden’s Leaders’ Summit on Climate. The event provides an opportunity for world leaders to reaffirm global efforts in the fight against climate change, set a clear pathway to net zero emissions, while creating jobs and ensuring a just transition.

Since taking office President Biden has made bold climate commitments and brought the United States back into the Paris Agreement. Ahead of the two-day summit, he announced an ambitious 2030 emissions target and new Nationally Determined Contributions. The US joins other countries that have announced significant reduction goals. For example, the EU committed to reduce its emissions by at least 55%, also South Korea, Japan and China have all set net-zero targets by mid-century.

Here in the UK, Prime Minister Boris Johnson this week outlined new climate commitments that will be enshrined in law. The ambitious new targets will see carbon emissions cut by 78% by 2035, almost 15 years earlier than previously planned. If delivered, this commitment which is in-line with the recommendations of the Climate Change Committee’s sixth carbon budget will put the UK at the forefront of climate action, and for the first time the targets include international aviation and shipping.

What makes climate change so difficult to tackle is that it requires collaboration from many different parties on a global scale never seen before. As a UK-North American sustainable energy company, with communities on both sides of the Atlantic, at Drax we are keenly aware of the need for thinking that transcends borders, creating a global opportunity for businesses and governments to work together towards a shared climate goal. That’s why we joined other businesses and investors in an open letter supporting the US government’s ambitious climate actions.

Collaboration between countries and industries

It’s widely recognised that negative emissions technologies will be key to global efforts to combat climate change.

At Drax we’re pioneering the negative emissions technology bioenergy with carbon capture and storage (BECCS) at our power station in North Yorkshire, which when up and running in 2027 will capture millions of tonnes of carbon dioxide (CO2) per year, sending it for secure storage, permanently locking it away deep under the North Sea.

Experts on both sides of the Atlantic consider BECCS essential for reaching net zero. The UK’s Climate Change Committee says it will play a major role in removing CO2 emissions that will remain in the UK economy after 2050 from industries such as aviation and agriculture that will be difficult to fully decarbonise. Meanwhile, a report published last year by New York’s Columbia University revealed that rapid development of BECCS is needed within the next 10 years in order to curb climate change and a recent report from Baringa, commissioned by Drax, showed it will be a lot more expensive for the UK to reach its legally binding fifth carbon budget between 2028 and 2031 without BECCS.

A shared economic opportunity

Globally as many as 65 million well-paid jobs could be created through investment in clean energy systems. In the UK, BECCS and negative emissions are not just essential in preventing the impact of climate change but will also be a key component of a post-Covid economy.

Government and private investments in clean energy technologies can create thousands of well-paid jobs, new careers, education opportunities and upskill workforces. Developing BECCS at Drax Power Station, for example, would support around 17,000 jobs during the peak of construction in 2028, including roles in construction, local supply chains and the wider economy. It would also act as an anchor project for the Zero Carbon Humber initiative, which aims to create the world’s first net zero industrial cluster. Developing a carbon capture, usage, and storage (CCUS) and hydrogen industrial cluster could spearhead the creation and support of tens of thousands of jobs across the Humber region and more than 200,000 around the UK in 2039.

Under the Humber Bridge

Additional jobs would be supported and created throughout our international supply chain. This includes the rail, shipping and forestry industries that are integral to rural communities in the US South and Western Canada.

A global company

As a British-North American company, Drax embodies the positive impact that clean energy investments have. We directly employ 3,400 people in the US, Canada, and the UK, and indirectly support thousands of families through our supply chains on both sides of the Atlantic. Drax is strongly committed to supporting the communities where we operate by investing in local initiatives to support the environment, jobs, education, and skills.

From the working forests of the US South and Western Canada to the Yorkshire and Humber region, and Scotland, we have a world-leading ambition to be carbon negative by 2030. At Drax, we believe the challenge of climate change is an opportunity to improve the environment we live in. We have reduced our greenhouse gas emissions by over 80% and transformed into Europe’s largest decarbonisation project. Drax Power Station is the most advanced BECCS project in the world and we stand ready to invest in this cutting-edge carbon capture and removal technology. We can then share our expertise with the rest of the world – a world where major economies are committing to a net zero future and benefiting from a green economic recovery.

If we are to reach the targets set in Paris, global leaders must lock in this opportunity and make this the decade of delivery.

Full year results for the twelve months ended 31 December 2020

Water outlet into Loch Awe from Cruachan Power Station

Drax Group plc
(“Drax” or the “Group”; Symbol:DRX)
RNS Number : 2751Q

Twelve months ended 31 December20202019
Key financial performance measures
Adjusted EBITDA (£ million) (1)(2)412410
Continuing operations366371
Discontinued operations – gas generation4639
Cash generated from operations (£ million)413471
Net debt (£ million) (3)776841
Adjusted basic EPS (pence) (1)29.629.9
Total dividend (pence per share)17.115.9
Total financial performance measures
Coal and other asset obsolescence charges(239)-
Operating (loss) / profit (£ million)(156)48
Loss before tax (£ million)(235)(16)

Financial highlights

  • Adjusted EBITDA from continuing and discontinued operations up £2 million to £412 million (2019: £410 million)
    • Includes estimated impact of Covid-19 of around £60 million, principally SME customers
    • Strong performance in Pellet Production and Generation
  • Strong cash generation and balance sheet
    • 1.9 x net debt to Adjusted EBITDA, with £682 million of cash and committed facilities at 31 December 2020
    • New carbon-linked RCF, Eurobond and infrastructure facilities with maturities to 2030 and reduced cost of debt
  • Sustainable and growing dividend up 7.5% to 17.1 pence per share (2019: 15.9 pence per share)
    • Proposed final dividend of 10.3 pence per share (2019: 9.5 pence per share)

Operational highlights

  • Pellet Production – 7% increase in production, improved quality and 5% reduction in cost
  • Generation – 11% of UK’s renewable electricity, strong operations and system support performance
  • Customers – lower demand and an increase in bad debt provisions, principally SME customers
  • Sustainability – sale of gas assets, end of coal generation, CDP Climate A- rating (2019: C) and TCFD Supporter
Train carrying sustainably sourced compressed wood pellets arriving at Drax Power Station in North Yorkshire

Train carrying sustainably sourced compressed wood pellets arriving at Drax Power Station in North Yorkshire [click to view/download]

Will Gardiner, CEO of Drax Group said:

“Drax has supported its customers, communities and employees throughout the Covid-19 pandemic and I want to thank colleagues across the Group for their commitment and hard work over the last year. We have delivered strong results, a growing dividend for shareholders and excellent progress against our business strategy.

Drax Group CEO Will Gardiner

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

“Our focus is on renewable power. Our carbon intensity is one of the lowest of all European power generators. We aim to be carbon negative by 2030 and are continuing to make progress. We are announcing today that we will not develop new gas fired power at Drax. This builds on our decision to end commercial coal generation and the recent sale of our existing gas power stations.

“The proposed acquisition of Pinnacle Renewable Energy will position Drax as the world’s leading sustainable biomass generation and supply business, paving the way for us to develop bioenergy with carbon capture and storage (BECCS) – taking us even further in our decarbonisation.”

2021 outlook

  • Targeting carbon negative
    • No new gas generation at Drax Power Station, retain options for system support gas in next capacity auction
    • Completion of sale of existing gas generation (January 2021) and end of commercial coal (March 2021)
  • Progressing biomass strategy
    • Proposed acquisition of Pinnacle Renewable Energy Inc. (Pinnacle) – supports long-term options for third-party supply, BECCS and biomass generation
    • BECCS – commencement of DCO planning process, potential FEED study and clarity on regional clusters

Infographic: How BECCS removes carbon from the atmosphere

  • Operations
    • Major planned outage on CfD unit and continued impact of Covid-19 on SME customers
    • Strong contracted power sales (2021–2023) 24.4TWh at £48.5/MWh

Operational review

Pellet Production – capacity expansion, improved quality and reduced cost

  • Adjusted EBITDA up 63% to £52 million (2019: £32 million)
    • Pellet production up 7% to 1.5Mt (2019: 1.4Mt)
    • Reduction in fines (larger particle-sized dust)
    • Cost of production down 5% to $153/t(4) (2019: $161/t(4))
  • Cost reduction plan – targeting $35/t (£13/MWh(5)) saving vs. 2018 on 1.9Mt by 2022 – annual savings of $64 million
    • $28 million of run-rate savings from projects delivered 2019-2020
    • Low-cost fibre, LaSalle (improved rail infrastructure, woodyard and sawmill co-location) and HQ relocation
    • $36 million of additional run-rate savings to be delivered by end of 2022
    • Expansion of Morehouse plant completed Q4 2020
    • Expansion of Amite and LaSalle, increased use of low-cost fibre and improved logistics
  • Additional savings from $40 million investment in three 40kt satellite plants in US Gulf – commissioning from 2021, with potential for up to 0.5Mt – targeting 20% reduction in pellet cost versus current cost

 Power Generation – flexible and renewable generation

  • Adjusted EBITDA up 9% to £446 million (2019: £408 million)
    • Biomass generation up 5% to 14.1TWh (2019: 13.4TWh) – record CfD availability (Q2 2020 – 99.5%)
    • Good commercial availability across the portfolio – 91% (2019: 88%)
    • Strong contracted position provided protection from lower demand and reduction in ROC(6) prices
    • Includes £46 million from discontinued gas (2019: £39 million)
Water cooling tower at Drax Power Station

Water cooling tower at Drax Power Station [click to view/download]

  • System support (balancing mechanism, Ancillary Services and optimisation) of £118 million (2019: £120 million)
    • Hydro and gas – one-off hydro contracts in 2019, offset by higher demand for system support services in 2020
    • Lower level of biomass activity due to higher value in generation market
    • 2019 included benefit of buying back coal generation
  • Pumped storage / hydro – excellent operational and system support performance
    • £73 million of Adjusted EBITDA (Cruachan, Lanark Galloway schemes and Daldowie) (2019: £71 million)
Aqueduct supplying water into the reservoir at Cruachan pumped hydro storage plant in Scotland

Aqueduct supplying water into the reservoir at Cruachan pumped hydro storage plant in Scotland [click to view/download]

  • Coal – 8% of output in 2020 and short-term increase in carbon emissions – utilisation of coal stock by March 2021
  • Covid-19 – business continuity plan in place to ensure continued operation and two major outages completed

Customers – managing the impact of Covid-19 on SME customers

  • Customer service employeeAdjusted EBITDA loss of £39 million (2019: £17 million profit) inclusive of estimated £60 million impact of Covid-19
    • Reduced demand, MtM loss on pre-purchased power and increase in bad debt, principally SME customers
    • Continue to evaluate SME options to maximise value and alignment with strategy
  • Development of Drax Customers Industrial & Commercial portfolio – increased sales to high-quality counterparties providing revenue visibility, while supporting the Group’s flexible and renewable energy proposition
  • Renewable and energy services expand Group system support capability and customer sustainability objectives

Other financial information

  • Total operating loss from continuing operations of £156 million reflects:
    • £70 million MtM loss on derivative contracts
    • £239 million obsolescence charges, principally coal (includes £13 million associated with decision not to develop new gas generation at Drax Power Station)
    • £34 million of costs associated with coal closure (redundancy, pensions and site reparations), with annual run-rate savings once complete of c.£30-35 million
  • Total loss after tax of £158 million includes £18 million reduced valuation of deferred tax asset resulting from UK Government’s reversal of previously announced corporation tax rate change (adjusted impact of £14 million, 3.5 pence per share)
  • Capital investment of £183 million(7) – continued invest in biomass strategy, some delay into 2021 due to Covid-19
    • 2021 expected investment of £190-210 million (excludes proposed acquisition of Pinnacle), includes expansion of LaSalle and Amite pellet plants and satellite plant development
  • Net debt of £776 million, including cash and cash equivalents of £290 million (31 December 2019: £404 million)
      • 1.9 x net debt to EBITDA, with £682 million of total cash and total committed facilities
      • Expect around 2 x net debt to EBITDA by end of 2022 inclusive of proposed acquisition of Pinnacle

 


View complete full year report View investor presentation Listen to webcast

Burns Lake and Houston pellet plant catchment area analysis

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

The eigth report in a series of catchment area analyses for Drax looks at the fibre sourcing area surrounding two compressed wood pellet plants operated by Pinnacle.

This part of interior British Columbia (BC) is unique in the Drax supply chain. Forest type, character, history, utilisation, natural challenges, logistics, forest management and planning are all very different to the other regions from which Drax sources biomass. Recently devasted by insect pest and fire damage, Arborvitae Environmental Services has produced a fascinating overview of the key issues and challenges that are being experienced in this region.

Figure 1: Catchment area map of the region [Click to view/download]

A positive response to natural disasters

Like the entire BC Interior, the area has suffered a devastating attack of Mountain Pine Beetle (MPB) damage over the last 20 years which has completely dominated every forest management decision and action. Within the catchment area, the MPB killed an estimated 157 million cubic metres (m3) between 1999 and 2014, representing 42% of the estimated 377 million m3 of total standing timber in the catchment area in 1999.  In addition, severe wildfires in 2018 burned an estimated 7.1 million m3.

These natural events have had a devastating impact on the forest resource. Harvesting increased significantly to utilise the dead and dying timber as lumber in sawmills whilst it was still viable.

Net carbon emissions in Canada’s managed forest: All areas, 1990–2017; illustrates that the impact of fires and insect damage have been far more significant, by hectares affected, than forestry activity; Chart via Natural Government of Canada

The Pinnacle pellet mills at Burns Lake and Houston were established alongside the sawmills to utilise the sawmill residues as there were no other viable markets for this material. These sawmills draw fibre from a large distance, up to 300 miles away. Therefore, the size of the catchment area in this piece of analysis is determined by the sourcing practices of the sawmills rather than the economic viability of low grade roundwood transport to the pellet mill (see Figure 1).

Damage to pine trees by Mountain Pine Beetle (MPB)

Utilising forest residues

The two mills producing high-density biomass pellets have provided an essential outlet for residue material that would otherwise have no other market and until very recently were supplied almost entirely by mill residuals. As the quantity of dead and dying timber has reduced and sawmill production has declined, the pellet mills are beginning to utilise more low-grade roundwood and forest residues (that are otherwise heaped and burned at roadside following harvest) to supplement the sawmill co-products.

Primarily State owned managed forests

The total land area in the catchment for Burns Lake and Houston is 4.47 million hectares (ha) of which 3.75 million ha is classed as forest land, 94% of the catchment area is public land under provincial jurisdiction. The provincial forest service is responsible for all decisions on land use and forest management on public land, in consultation with communities and indigenous groups, determining which areas are suitable for timber production and which areas require protection. Approximately 34% of the catchment area is not available for commercial timber harvesting because it is either non-forested or it has low productivity, and other operational challenges, or it is protected for ecological and wildlife reasons.

The Chief Forester for the province sets the Annual Allowable Cut (AAC) which determines the quantity of timber that can be harvested each year. Ordinarily this will be based on the sustainable yield capacity of the working forest area, but in recent years the MPB damage has necessitated a significant increase in AAC to facilitate the salvage of areas that have been attacked and damaged (see Figure 2).

Figure 2: Changes in Annual Allowable Cut 1980 to 2018 (Source: Nadina District FLNRORD) [Click to view/download]

The catchment area is in the Montane Cordillera ecozone and the Canadian Forest Service reports that between 1980 and 2017, the area of forest in the ecozone declined from 31,181,000 ha to 31,094,000 ha, a decline of 87,000 ha or 0.28 % of the forest area. Deforestation in the catchment area was estimated at 300 ha per year. Most deforestation in the ecozone occurred because of conversion to agriculture, as well as other contributing factors, such as mining, urban expansion and road construction (including forest roads).

The forest area is dominated by coniferous species (see Figure 3) predominantly lodgepole pine, spruce and fir (90% of the total area), with hardwood species (primarily aspen) making up just 8% of the total area.

Figure 3: Species composition of forest land in the catchment area.

Managing beetle damaged areas

The annual harvest volume was at a peak in the early part of the last decade at over 12 million m3 in 2011. This has now declined by around 4.5 million m3 in 2019 (see Figure 4) as the beetle damaged areas are cleared and replanted. The AAC and harvesting levels are expected to be reduced in the future to allow the forest to regrow and recover.

Figure 4: Annual change in harvest volume of major species

Future increases in forest growth rates

Historically, the forest area has naturally regenerated with self-seeded stands reaching a climax of mature pine, spruce, and Abies fir mixtures.  As the forest matured, it would often be subject to natural fires or other disturbance which would cause the cycle to begin again. Following the increase in harvesting of beetle damaged areas, many forests are now replanted with mixtures of spruce and pine rather than naturally regenerated. This is likely to lead to an increase in forest growth rates in the future and a higher volume of timber availability once the areas reach maturity (see Figure 5).

Figure 5: Forecast of future volume production

Timber markets in the catchment area are limited in comparison to other regions like the US South.  The scale of the landscape and the inaccessible nature of many of the forest areas limit the viability of access to multiple markets. Sawmills produce the highest value end-product and these markets have driven the harvesting of forest tracts for many years. Concessions to harvest timber are licensed either by volume or for a specific area from the provincial forest service. This comes with a requirement to ensure that the forest regrows and is appropriately managed after harvesting.

There are no pulp mills within the catchment area and limited alternative markets for the lowest grades of roundwood or sawmill residuals other than the pellet mills; consequently, the pellet mills have a close relationship with the sawmills.

Wood price trends

Prices for standing timber on public land are determined by the provincial government using results from public timber sales and set according to the species and quality of timber produced (from the highest-grade logs through to forest residuals). The lack of market diversity and challenging logistics mean that there is little competition for mill residuals and low-grade fibre. The price differential in end-product value between sawtimber and wood pellets ensures that fibre suitable for sawmill utilisation does not get processed by the pellet mill. A very small volume of larger dimension material can end up in a low value market when there are quality issues that limit the value for sawtimber (e.g. rotten core, structural defects) but this represents a very small proportion of the supply volume. There is no evidence that pellet mills have displaced other markets within this catchment area.

Read the full report: Catchment Area Analysis: Pinnacle Renewable Energy’s Burns Lake & Houston Mills.

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

New ESG RCF and Financing Update

Landscape of trees in autumn Where: Cruachan Power Station, Scotland
RNS Number: 8002F
Drax Group PLC (Symbol: DRX)

Drax is pleased to announce that it has completed the refinancing of its revolving credit facility.

The new £300 million facility (“the Facility”) matures in 2025, with an option to extend by one year(1). The Facility replaces the current RCF which matures in 2021 and provides increased liquidity, enabling the full facility to be drawn as cash (the previous facility restricted cash drawn to support liquidity to £165 million). The Facility is currently undrawn for cash.

The Facility has a customary margin grid referenced over LIBOR, which reflects a small reduction in cost versus the current RCF and includes an embedded ESG component which adjusts the margin based on Drax’s carbon intensity measured against an annual benchmark.

Drax has also agreed a change to the Group’s £35 million term-loan facility, maturing in 2022, in order to simplify its capital structure. This facility will now rank as senior, previously super senior.

Drawing of previously agreed infrastructure facility

On 14 September 2020, Drax confirmed that it had agreed a new infrastructure term-loan agreement (the “Agreement”) that provided committed facilities of approximately £160 million with a range of maturities between 2024 and 2030(2). These facilities extended the Group’s maturity profile while also reducing the cost of debt. Drax has now drawn £28 million(2), with the balance to be drawn by February 2021.

The Agreement also included an option for a further £75 million. Under this option Drax has now agreed £53 million maturing in 2028, which will be drawn in December 2020.

Proceeds from Euro denominated bond issue and utilisation

On 4 November 2020, Drax issued €250 million of Euro denominated senior secured notes which mature in 2025. The effective Sterling-equivalent interest rate is 3.24% per annum.

The proceeds from this issuance, along with existing cash flows, are being used to redeem the Group’s £350 million 2022 Sterling bond and £125 million ESG term-loan facility.

The notes extend the Group’s debt maturity profile and reduce the overall cost of debt to approximately 3.7%.

Summary of Group debt structure at 19 November 2020

InstrumentMaturityDescription
Infrastructure facilities (2019)2024-2029£375m
Infrastructure facilities (Sept 2020)2024-2030approx.£160m (2) (£28m (2) drawn)
Infrastructure facilities (Nov 2020)2028£53m
Bonds2025$500m
Bonds2025€250m
RCF2025£300m (undrawn for cash)
Index-linked term-loan2022£35m

Enquiries:

Drax Investor Relations: Mark Strafford

+44 (0) 7730 763 949

Media:

Drax External Communications: Selina Williams

+44 (0) 7912 230 393

Website: www.drax.com

END

Georgia Mill Cluster catchment area analysis

Forest in LaSalle catchment area

The seventh report in a series of catchment area analyses for Drax looks at the fibre sourcing area surrounding a number of compressed wood pellet plants operated by Georgia Biomass (now owned by Enviva) and Fram Renewable Fuels.

The evidence found in the report by Hood Consulting shows a substantial increase in forest inventory (stored carbon) and a relatively stable forest area. However, with continued pressure from urban development, future losses of timberland area are possible.  Despite this, increasing growth rates can maintain and improve wood supply and carbon stock for the foreseeable future.

Increasing forest growing stock and carbon sequestration

The overall inventory of growing stock in the catchment area has increased by 63 million cubic metres (m3) between 2000 and 2018, a growth of 19.3%.  All of this increase has been in the pine area, which increased by nearly 68 million m3, whereas the hardwood species decreased in volume by 4.5 million m3. Overall, the inventory volume split by species in 2018 was 72% to 28% softwood to hardwood. The breakdown by product category is shown in Figure 3 below.

Figure 1: Change in growing stock by major product category and species (USFS)

The pine saw-timber and chip-n-saw product categories, larger dimension and higher value material, showed the largest increase in inventory, whereas pine pulpwood decreased in total volume.  The most substantial change occurred from 2010 to 2018, where pulpwood went from an increasing trend to a decreasing trend and saw-timber increased in volume much more rapidly – this is shown in Table 1 and Figure 2 below.

Change (cubic metres (m3))Pine SawtimberPine Chip-n-sawPine PulpwoodHardwood SawtimberHardwood PulpwoodTotal
2000-201851,301,62822,277,139-5,835,2301,211,110-5,657,11463,297,533
2000-201014,722,99512,707,6745,262,192-3,740,507-5,76989923,182,455
2010-201836,578,6329,569,465-11,097,4224,951,618112,78440,115078
Table 1: Change in growing stock volume by major product category (USFS)

These changes are likely to reflect an increasing age class in the catchment area, with younger stands of pine (previously classed as pulpwood), growing into a larger size class and being reclassified as saw-timber.  This means that the volume of saw-timber availability in future will be significantly higher, but pulpwood availability will be diminished.  For pellet mill markets any loss in pulpwood availability can be compensated by an increase in sawmill residue production if market demand is maintained or increased.

Figure 2: Change in growing stock by major product category and species (USFS)

Growth rates for both softwood and hardwood species have been increasing since 2000 as shown in Figure 3 below. Softwood growth has increased by 18.5% since 2000 and hardwood by 1.4%. The improved softwood growth rate probably resulted from increased investment in the management of pine forests, the superior quality of seedlings and better management practice (ground preparation, weed control, fertilisation etc.). This is a very positive trend for the sequestration rate of carbon and also for providing landowners with the potential to increase revenue per hectare and encourage the retention and improved management of forests, rather than converting to other land uses. The Georgia catchment area is likely split between passive owners that do not actively manage, where growth rates are slower or decline and the incentive to convert land is greater, and owners that actively manage to improve growth and quality, increasing revenue and maintaining productive forest.  There is likely to be a much greater differential in growth rate between these two management approaches than reflected by the trend in Figure 3, highlighting the importance of active management for carbon abatement.

Average annual growth rate per hectare (USFS)

Figure 3: Average annual growth rate per hectare (USFS)

Stable forest area

At a macro scale, the distribution of land use categories has remained relatively stable since 2000, with no apparent major shifts in land use. The timberland area around the seven mills has decreased by around 135 thousand hectares (ha) between 2000 and 2018 (2.3% of the total land area), whilst the area of arable and urban land increased by 98 thousand (1.7% of total area) and 158 thousand (2.7% of total area) ha respectively.  In 2018, timberland represented 67% of total land area and all forest and woodland 80% of total area, down from 69% and 82% respectively in 2000 (Figure 1).

Change in land use category (USDA)

Figure 4: Change in land use category (USDA)

Looking at this change in land use more closely, the timberland area shows the most pronounced decline between 2010 and 2018, a drop of 117 thousand ha. The largest change in other land use categories over this period was an increase of 97 thousand ha in urban and other land, suggesting that a large proportion of the timberland area has been converted to urban areas.

LaSalle Bioenergy forest area

The most significant change in agricultural land occurred prior to 2010, when the timberland area remained relatively stable, this change appears to have involved the transition of pastureland to arable crops. There may also have been some reclassification of forest and woodland types, with a decrease in the area of woodland and an increase in forestland during the period between 2000 and 2010 (Table 2).

Change (hectares (ha))TimberlandOther ForestlandArable CroplandWoodlandPasturelandUrban & Other Land
2000-2018-135,19570,07398,436-77,904-113,725178,315
2000-2010-18,53953,15073,243-73,077-95,63060,852
2010-2018-116,65616,92225,193-4,827-18,09697,463
Table 2: Timing of land use change in Georgia catchment area (USDA)

These trends are also clear and apparent in Figure 3 below which shows the sharp decline in timberland area, albeit small in absolute area relative to the total catchment area size, and the steady increase in urban land.  Georgia ranks 8th in the list of US States and territories by total population with 10.6 million and 17th by population density at 184 per square mile (mi2) compared to just 63 per mi2  in Mississippi where Drax’s Amite Bioenergy (ABE) pellet plant is located and 108 per mi2 in Louisiana where the Morehouse Bioenergy (MBE) and LaSalle Bioenergy (LBE) mills are located (US Census Bureau). This population pressure and increased development can lead to more forest loss and land use change.

Trends in major land use categories (USDA)

Figure 5: Trends in major land use categories (USDA)

Drax’s suppliers in the Georgia catchment area have made a commitment not to source wood from areas where land use change is taking place. This commitment is monitored and verified through the Sustainable Biomass Program (SBP) certification process that is maintained by each mill.  Any land use change in the catchment area is likely to be a result of prevailing economic drivers in the region rather than due to actions being taken by the pellet producers.

Increasing demand and surplus forest growth

Strong markets are essential for ensuring that forests are managed and restocked to optimum benefit, sawlog markets are particularly important as this is highest revenue stream for forest owners. Figure 6 shows the trend in market demand for each major product category since 2000 and demonstrates the recent increase in softwood sawlog demand as the US economy (particularly housing starts) recovered from the global recession at the end of the last decade. Softwood pulpwood demand increased through the 2000s but has remained relatively stable since 2011, with the exception of a peak during 2018 which resulted from an increase in volume generated by salvage operations after hurricane Michael.

Figure 6: Demand for wood products (USFS, TMS)

Figure 6: Demand for wood products (USFS, TMS)

The comparison of average annual growth and removals in the Georgia catchment area is much more tightly balance than in Drax’s other supply regions, as shown in Figure 7. Since 2000 the average annual surplus of growth has been around 3.6 million m3 with both demand and growth increasing in recent years.

Figure 7: Average annual growth, removals and surplus (USFS)

Figure 7: Average annual growth, removals and surplus (USFS)

As shown in Figures 2 & 3, growth rates are strong and inventory is increasing, this is not a problem in the Georgia area.  The relatively small surplus, as compared to other catchment areas in the US South, is due to the higher concentration of wood fibre markets and the more intense forest industry activity in this region.  As of July 2020, there were over 50 major wood-consuming mills operating within the Georgia catchment area and an additional 80+ mills operating within close proximity, overlapping the catchment area.  Total pulpwood demand in 2019 was 12.9 million tons, of which approximately 87% was attributed to non‐bioenergy‐related sources (predominantly pulp/paper) and 13% was attributed to the bioenergy sector.  Given the bio-energy sector’s low ranking position in the market (with the lowest ability to pay for fibre), combined with the relatively small scale in demand compared to the pulp and paper industry, the influence of biomass markets can be considered to be minimal in this region, particular when it comes to impacts on wood prices and forest management practice.

Wood price trends

Pine sawtimber prices suffered a significant decline between 2000 and 2010, dropping almost $21 per ton as a result of the global financial crisis and the decline in demand due to the collapse in housing markets and construction (Table 3).  Since 2010 pine sawtimber has remained relatively stable, with some minor fluctuations shown in Figure 8 below.

Change ($/ton)Pine SawtimberPine Chip-n-sawPine PulpwoodHardwood SawtimberHardwood Pulpwood
2000-2019-$20.92$15.14$5.95$12.55$4.70
2000-2010-$20.92-$21.41$2.11$11.25$5.67
2010-2019$0.00$6.27$3.84$1.30-$0.97
Table 3: Stumpage price trends (TMS)

Pine pulpwood prices have been on a generally increasing trend since 2000, with a more significant increase since 2011.  This increase does not reflect an increase in demand or total volume, which has remained relatively stable over this period, but a shifting of the geographic distribution of the market with some new mills opening and old mills closing, resulting in increased competition in some localised fibre baskets and leading to an overall increase in stumpage price.

Figure 8: Stumpage price trends (TMS)

Figure 8: Stumpage price trends (TMS)

Figure 9 below shows that, with the exception of the hurricane salvage volume in 2018, pulpwood removals have declined or remained relatively stable since 2010, whereas pulpwood stumpage prices increased by 41% from 2010 to 2018.

Figure 9: Pulpwood demand and stumpage price (USFS, TMS)

Figure 9: Pulpwood demand and stumpage price (USFS, TMS)

Comparing this stumpage price trend with other catchment areas of the US South (Figure 10), where Drax sources wood pellets, the Georgia area is on average 35% higher than the next highest area (Chesapeake) and 87% higher than the lowest cost area (Amite Bioenergy in Mississippi).  This price differential is predominantly due to the scale of demand and availability of surplus low-grade fibre.

Figure 10: Comparison of pine pulpwood stumpage prices in Drax supply areas US South (TMS)

Figure 10: Comparison of pine pulpwood stumpage prices in Drax supply areas US South (TMS)

Hood Consulting summary of the impact of the seven pellet plants on key trends and metrics in this catchment area.

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

Deforestation?

No. US Forest Service (USFS) data shows a 108,130-hectare (-2.6%) decrease in total timberland in the Georgia catchment area since Georgia Biomass’ first full year of production in 2012. Specifically, this loss in total area of timberland coincided with a more than 21,000-hectare increase in cropland/pastureland and a more than 73,000-hectare increase in urban land and land classified as having other uses.

However, there is little evidence to suggest that increased wood demand from the bioenergy sector has caused this decrease in total timberland. Furthermore, pine timberland – the primary source of roundwood utilized by the bioenergy industry – has increased more than 17,000 hectares in the catchment area since 2016.

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

No. Changes in management practices have occurred in the catchment area over the last two decades. However, there is little evidence to suggest that bioenergy demand, which accounts for roughly 10-14% of total pulpwood demand (and only 5-7% of total wood demand in the catchment area), 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 67% of total reported harvest area in the southeast Georgia market from 2000-2010, but only 43% of total harvest area reported from 2012-2019. Specifically, this downward shift was initiated by the bursting of the US housing bubble in the mid-2000s and had been completed by the early 2010s. We’d like to note that this shift coincided with a nearly 50% decrease in pine sawtimber stumpage price from 2006-2012. This is important because the strength of pine sawtimber markets had been a driving force behind timber management decisions in this region in the early and mid-2000s.

Also, contributing to the decreased prevalence of thinnings was the strengthening of pine pulpwood markets in the mid-2000s, as pine pulpwood stumpage prices increased more than 40% in the Georgia catchment area from 2003-2008. So, with sawtimber markets continuing to weaken and pulpwood markets doing just the opposite, the data suggests that many landowners decided to alter their management approach (to take advantage of strong pulpwood markets) and focus on short pulpwood rotations that typically do not utilize thinnings.

Ultimately, the shift in management approach that occurred in this market can be linked to the weakening of one type of timber market and the strengthening of another. In the early and mid-2000s, timber management was focused on sawtimber production – a type of management that utilizes thinnings. However, for more than a decade now, this market has been driven to a large degree by the pulp/paper industry, with a significant portion of the timber management in this area focused on short pulpwood rotations.

Diversion from other markets?

No. Demand for softwood (pine) sawlogs increased an estimated 39% in the Georgia catchment area from 2011-2019. Also, increased bioenergy demand has caused no diversion from other pulpwood markets (i.e. pulp/paper), as pulpwood demand not attributed to bioenergy held steady and remained nearly unchanged from 2012-2017 before increasing in 2018 and 2019 due to the influx of salvage wood brought about by Hurricane Michael.

We’d like to make special note that increased demand for softwood sawlogs since 2011 has not resulted in a full pine sawtimber (PST) stumpage price recovery in this market. Reduced demand for softwood sawlogs in the late 2000s and early 2010s resulted in oversupply, and this oversupply has remained, despite increased demand the last 6-8 years. As a result, PST stumpage prices have held steady and averaged roughly $30 per ton in the catchment area since 2013 – down approximately 35% from the 2000-2006 average of more than $46 per ton, but up roughly 15% from the 2011-2012 average of approximately $26 per ton.

An unexpected or abnormal increase in wood prices?

No / Inconclusive. The delivered price of pine pulpwood (PPW) – the primary roundwood product consumed by both Georgia Biomass and Fram – increased 26% in the Georgia catchment area over the six years directly following the startup of Georgia Biomass, increasing from $29.16 per ton in 2011 to $36.63 per ton in 2017. And while this 26% increase in delivered PPW price coincided with a roughly 1.1 million metric ton increase in annual pine pulpwood demand from Georgia Biomass and Fram, total demand for pine pulpwood (from both bioenergy and other sources) actually decreased 7% over this period. Moreover, evidence suggest that this increase in PPW price is more closely linked to changes in wood supply, specifically, the 9% decrease in PPW inventory from 2011-2017.

However, there is evidence that links increased demand from the bioenergy sector to an increase in secondary residual (i.e. sawmill chips, sawdust, and shavings) prices. Specifically, the price of pine sawmill chips – a residual feedstock utilized by the bioenergy industry for wood pellet production – held steady and averaged approximately $26 per ton in the Georgia catchment area from 2008-2012. However, from 2012-2016, pine sawmill chip prices increased more than 15% (to $29.55 per ton in 2016). This increase in price coincided with annual pine residual feedstock purchases by Georgia Biomass and Fram increasing from roughly 325,000 metric tons to nearly 1.0 million metric tons over this period. However, note that pine sawmill chip prices have held steady and averaged roughly $29.50 per ton in the catchment area since 2016, despite further increases in pine secondary residual purchases by Georgia Biomass and Fram (to more than 1.2 million metric tons in 2019).

Ultimately, the data suggests that any excess supply of pine secondary residuals in the catchment area was absorbed by the bioenergy sector in the early and mid-2010s, and the additional demand/competition placed on this market led to increased residual prices. However, the plateauing of residual prices since 2015 along with the continued increase in secondary residual purchases by Georgia Biomass and Fram further suggest that an increasing percentage of secondary residual purchases by the bioenergy sector is sourced from outside the catchment area. Specifically, Fram confirmed this notion, noting that 35-40% of its secondary residual purchases come from outside the Georgia catchment area (from six different states in the US South).

A reduction in growing stock timber?

No. Total growing stock inventory in the catchment area increased 11% from 2011 through 2018, the latest available. Specifically, over this period, inventories of pine sawtimber and chip-n-saw increased 35% and 13%, respectively. However, pine pulpwood inventory decreased 11% from 2011-2018.

Note that the decrease in pine pulpwood inventory was not due to increased demand from bioenergy (or other sources) or increased harvesting above the sustainable yield capacity of the forest area – as annual growth of pine pulpwood has exceeded annual removals every year since 2011. Rather, this decrease can be linked to the 24% decline in pine sawtimber removals that occurred from 2005-2014 (due to the bursting of the US housing bubble and Great Recession that followed). In this region, timber is typically harvested via clearcut once it reaches maturity (i.e. sawtimber grade), after which the stand is reestablished, and the cycle repeated. However, with the reduced harvest levels during this period also came a reduction in newly reestablished timber stands – the source of pine pulpwood. So, with less replantings occurring during this period, inventories of pine pulpwood were not replenished to the same degree they had been previously, and therefore this catchment area saw a reduction in pine pulpwood inventory levels.

However, according to the US Forest Service, annual removals of pine sawtimber have increased 50% in the Georgia catchment area since 2014, which would suggest higher clearcut levels and increased stand reestablishment. TimberMart-South data also supports this assertion, as clearcut harvests have constituted approximately 60% of the total harvest area reported to TimberMart-South in this region since 2014, compared to 40% from 2005-2014. Ultimately, these increases in clearcut (and stand reestablishment) levels may not be reflected in increased pine pulpwood inventory levels in the short term – as it can take more than 10 years for a pine seedling to become merchantable and reach the minimum diameter requirements to be classified as pulpwood. However, adequate supply levels are expected to remain in the meantime. Furthermore, pine pulpwood inventory levels are expected to increase in the mid-to-long terms as a result of the increased harvest levels and stand reestablishment levels that have occurred in the catchment area since 2014.

A reduction in the sequestration rate of carbon?

No / Inconclusive. US Forest Service data shows the average annual growth rate of total growing stock timber has remained nearly unchanged (holding between 6.0% and 6.1%) in the catchment area since 2011, which would suggest that the sequestration rate of carbon has also changed very little in the catchment area the last 8-10 years. However, the 11% increase in total growing stock inventory since 2011 does indicate that total carbon storage levels have increased in the Georgia catchment area since Georgia Biomass commenced operations in this market.

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 harvests, provides a measure of market demand relative to supply as well as a gauge of market sustainability. In 2018, the latest available, the G:R ratio for pine pulpwood, the predominant timber product utilized by the bioenergy sector, equaled 1.06 (a value greater than 1.0 indicates sustainable harvest levels). Note, however, that the pine pulpwood G:R ratio averaged 1.44 from 2012-2017. The significant drop in 2018 was due to a 31% increase in removals (due to Hurricane Michael) and is not reflective of the new norm. Specifically, pine pulpwood removals are projected to be more in line with pre-2018 levels in 2019 and 2020, and so too is the pine pulpwood G:R ratio.

Timber growing stock inventory

Neutral. According to USFS data, inventories of pine pulpwood decreased 11% in the catchment area from 2011-2018. However, that decrease 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 this case, annual growth of pine pulpwood exceeded annual removals every year during this period.

Ultimately, the decrease in pine pulpwood inventory from 2011-2018 can be linked to decreased pine sawtimber production beginning in the mid-2000s. Specifically, annual removals of pine sawtimber decreased 24% from 2005-2014, and the reduction in harvest levels during this period meant fewer new pine stands were reestablished, and that has led to the current reduction in pine pulpwood inventory. (Note that the decrease in pine sawtimber removals from 2005-2014 was mirrored by a 27% increase in pine sawtimber inventory over this same period). However, USFS data shows that annual removals of pine sawtimber have increased 50% in the Georgia catchment area since 2014, which suggests that pine pulpwood inventory levels will start to increase in the catchment area due to increased harvest levels and the subsequent increase in stand reestablishment levels.

Timber growth rates

Neutral. Timber growth rates have increased for both pine sawtimber and pine chip-n-saw but decreased slightly for pine pulpwood in the catchment area since 2011. Evidence suggests that this decrease in pine pulpwood growth rate is not due to increases in bioenergy demand, but rather linked to changes in diameter class distribution and indicative of a forest in a state of transition, where timber is moving up in product class (i.e. pine pulpwood is moving up in classification to pine chip-n-saw).

Forest area

Neutral. In the Georgia catchment area, total forest area (timberland) decreased more than 115,000 hectares (-2.8%) from 2011 through 2018. Note that this decrease coincided with a roughly 19,000-hectare increase in cropland and 93,000-hectare increase in urban land and land classified as having other uses.

Specifically, pine timberland, the primary source of roundwood utilized by the bioenergy industry, decreased over 34,000 hectares from 2011-2016. However, from 2016-2018, pine timberland stabilized and rather increased more than 17,000 hectares in the catchment area (or a net decrease of roughly 17,000 hectares from 2011-2018). Ultimately, there is little evidence that the decrease in pine timberland from 2011-2016 or increase since 2016 is linked to increased bioenergy demand. Rather, the overall decrease in pine timberland since 2011 appears to be more closely linked to the relative weakness of pine sawtimber markets in the Georgia catchment area and the lack of return from sawtimber.

Wood prices

Positive / Negative. Intuitively, an increase in demand should result in an increase in price, and this is what the data shows in the Georgia catchment area as it relates to increased biomass demand from Georgia Biomass and Fram and the prices of the various raw materials consumed by these mills. Specifically, the 1.4-million metric ton increase in softwood pulpwood demand attributed to Georgia Biomass and Fram coincided with a 20% increase in delivered pine pulpwood price and a 10-15% increase in pine chip prices from 2011-2015. Since 2015, biomass demand has held relatively steady, and, overall, so too have delivered pine pulpwood and pine chip prices. The apparent link between increased bioenergy demand and increased pine raw material prices is supported further by statistical analysis, as strong positive correlations were found between softwood biomass demand and both delivered pine pulpwood and pine chip prices. However, note that biomass demand alone is not responsible for these changes in prices, as softwood biomass demand accounts for only 10-15% of total softwood pulpwood demand in the catchment area. Rather, the prices of these raw materials are impacted to a larger degree by demand from other sources (i.e. pulp/paper), which accounts for 85-90% of total softwood pulpwood demand in the Georgia catchment area.

On the other hand, it’s also important to note that the increase in bioenergy-related wood demand has been a positive for forest landowners in the Georgia catchment area. Not only has bioenergy provided an additional outlet for pulpwood in this market, but the increase in pulpwood prices as a result of increased pulpwood demand has transferred through to landowners (improved compensation). Specifically, since 2015, pine pulpwood (PPW) stumpage price – the price paid to landowners – has averaged more than $17 per ton in the Georgia catchment area. This represents a 70% increase over the approximately $10 per ton averaged by PPW stumpage in the catchment area over the last five years prior to Georgia Biomass’ startup in 2Q 2011.

(Note: Pine pulpwood stumpage prices are notably higher in the Georgia catchment area due to a much tighter balance in supply and demand (in comparison to most other markets across the US South). For instance, in all other areas across the US South2, PPW stumpage prices have averaged less than $9 per ton since 2015, or roughly half that of prices in the Georgia catchment area).

Markets for solid wood products

Positive. In the Georgia catchment area, demand for softwood sawlogs used to produce lumber and other solid wood products increased an estimated 39% from 2011-2019, and by-products of the sawmilling process are sawmill residuals – materials utilized by Georgia Biomass and the Fram mills to produce wood pellets. With the increased production of softwood lumber, so too has come an increase in sawmill residuals, some of which have been purchased/consumed by Georgia Biomass and Fram. Not only have these pellet producers benefited from the greater availability of this by-product, but lumber producers have also benefited, as the Georgia Biomass and Fram mills have provided an additional outlet for these producers and their by-products.

Read the full report: Georgia Biomass 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 include: ChesapeakeEstonia, Latvia and Drax’s own, other three mills LaSalle BionergyMorehouse Bioenergy and Amite Bioenergy.

LaSalle catchment area analysis

LaSalle Bioenergy Pellet Plant

The wood supply catchment area for Drax’s LaSalle BioEnergy biomass pellet plant in mid-Louisiana is dominated by larger scale private forest owners that actively manage and invest in their forest for saw-timber production. Eighty-three per cent (83%) of the forest is in private ownership and 60% of this area is in corporate ownership.

The Drax Biomass pellet mill uses just 3.2% of the roundwood in the market and therefore has limited impact or influence on the overall trends. By contrast, the pulp and paper industry consumes 74% of the total pulpwood demand as the most dominant market for low grade fibre.

Forest in LaSalle catchment area

Forest in LaSalle catchment area

The catchment area has seen an increase in total timberland area of 71 thousand hectares (ha) since 2008, this is primarily due to planting of previously non-stocked land. Hardwood areas have remained stable but planted pine has increased, replacing some of the naturally regenerated mixed species areas. The data below shows that deforestation or conversion from pure hardwood to pine is not occurring.

Timberland area by management type

Timberland area by management type

The overall quantity of stored carbon, or the inventory of the standing wood in the forest, has increased by 7% or 32.6 million metric tonnes since 2008. This total is made up of a 49 million tonne increase in the quantity of pine and a 16 million tonne decline in the quantity of hardwood. Since the area of pure hardwood forest has remained stable, this decline is likely to be due to the conversion of mixed stands to pure pine in order to increase saw-timber production and to provide a better return on investment for corporate owners.

Historic area and timberland inventory

Historic area and timberland inventory

Forest in LaSalle catchment area

Forest in LaSalle catchment area

The growth-to-drain ratio and the surplus of unharvested pine growth has been increasing year-on-year from two million tonnes in 2008 to over five million tonnes in 2016.

This suggests that the LaSalle BioEnergy plant (which almost exclusively utilises pine feedstocks) has not had a negative impact on the growth-to-drain ratio and the surplus of available biomass.

The latest data (2016) indicates that the ratio for pine pulpwood is 1.54 and for pine saw-timber 1.24 and that this has been increasing each year for both categories.

Historic growth and removals by species

Historic growth and removals by species

Stumpage prices for all product categories declined between 2010 and 2011. This was followed by a peak around 2015-16 with the recovery in demand post-recession and prices then stabilised from 2016 to 2019. The data indicates that there has been no adverse impact to pine pulpwood prices as a result of biomass demand. In fact, pine pulpwood prices are now nearly 20% lower than in 2014 as shown on the chart below.

LaSalle BioEnergy market historic stumpage prices, USD$:tonne

LaSalle BioEnergy market historic stumpage prices, USD$:tonne

The character of the pine timberland is one of a maturing resource, increasing in the average size of each tree. The chart below chart shows a significant increase in the quantity of timber in the mid-range size classes, indicating a build-up of future resources for harvesting for both thinning and final felling for sawtimber production.

With balanced market demand, the supply of fibre in this catchment area should remain plentiful and sustainable in the medium term.

Historic pine inventory by DBH (diameter at breast height) class

Historic pine inventory by DBH (diameter at breast height) class

Forisk summary of the impact of LaSalle BioEnergy on key trends and metrics in this catchment area

Is there any evidence that bioenergy demand has caused …

Deforestation

No

Change in forest management practices

No

Diversion from other markets

Possibly. Bioenergy plants compete with pulp/paper and oriented strand board (OSB) mills for pulpwood and residual feedstocks. There is no evidence that these facilities reduced production as a result of bioenergy markets, however.

Increase in wood prices

No. There is no evidence that bioenergy demand increased stumpage prices in the market.

Reduction in growing stock of timber

No

Reduction in sequestration of carbon / growth rate

No

Increase in harvesting above the sustainable yield

No 

The impact of bioenergy on forest markets in the LaSalle catchment is …

Growing stock

Neutral

Growth rates

Neutral

Forest area

Neutral

Wood prices

Neutral

Markets for solid wood

Neutral to Positive. Access to viable residual markets benefits users of solid wood (i.e. lumber producers).

Forest in LaSalle catchment area

Forest in LaSalle catchment area

Read the full report: LaSalle, Louisiana Catchment Area Analysis. Read how a $15m rail link from LaSalle BioEnergy to the Port of Greater Baton Rouge helps Drax reduce supply chain emissions and biomass costs here. Take a 360 immersive experience and video tour of LaSalle BioEnergy.

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

£125 million ESG facility extended to 2025

Engineers in PPE high above Drax Power Station looking towards biomass wood pellet storage dome

RNS Number: 7379P
Drax Group plc
(“Drax” or the “Company”; Symbol: DRX)

Drax is pleased to announce that it has completed a three-year extension to the £125 million Environmental, Social and Governance (ESG) facility agreement entered into in July 2019. The contractual final maturity of the facility is 2025, further extending the profile of Drax’s existing facilities, which include maturities to 2029.

The ESG facility includes a mechanism that adjusts the rate of interest paid based on Drax’s carbon emissions against an annual benchmark, reflecting Drax’s continued commitment to reducing its carbon emissions as a part of its overall purpose of enabling a zero-carbon, lower cost energy future and an ambition to become carbon negative by 2030.

The average all-in interest rate during the first year of the extended facility is less than 2%. The Group’s overall cost of debt is less than 4% per annum.

Enquiries:

Drax Investor Relations: Mark Strafford

+44 (0) 7730 763 949

Media:

Drax External Communications: Ali Lewis

+44 (0) 7712 670 888

Website: www.drax.com

END