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THE TRANSATLANTIC TRADE IN WOOD FOR ENERGY : A Dialogue on Sustainability Standards and Greenhouse Gas Emissions Savannah, Georgia October 2013

TRANSATLANTIC TRADE IN WOOD FOR ENERGY...StakeholderWorkshops—Improvingthe TransatlanticDialogue InOctober2012,severalCanadianpartnersworkingwith IEABioenergyTask40(InternationalSustainableBioenergy

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Page 1: TRANSATLANTIC TRADE IN WOOD FOR ENERGY...StakeholderWorkshops—Improvingthe TransatlanticDialogue InOctober2012,severalCanadianpartnersworkingwith IEABioenergyTask40(InternationalSustainableBioenergy

THE TRANSATLANTIC TRADE INWOOD FOR ENERGY:A Dialogue on Sustainability Standards and Greenhouse Gas Emissions

Savannah, GeorgiaOctober 2013

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Workshop participants on the field study tour in southeast Georgia.

BrianKittler

This workshop was convened by the Pinchot Institute for Conservation with support from the International

Energy Agency (IEA) Bioenergy Tasks 40 and 43. The Georgia Forestry Commission and Plum Creek Timber

Company led the organization of the workshop field tour. This event was made possible with generous

support from the Programme for the Endorsement of Forest Certification Programs (PEFC), the Sustainable

Forestry Initiative (SFI), IEA Bioenergy Executive Committee (IEA Bioenergy ExCo), E.On, MeadWestvaco

Company Foundation, and Weyerhaeuser.

Workshop proceedings are available at:www.Pinchot.org/pellets

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IntroductionIncreasing Trade, Increasing DialogueBioenergy represents nearly 80% of renewable energyproduced globally and the share of energy coming frombiomass is projected to remain high for the foreseeablefuture (IPCC, 2011). Desire to reduce fossil fuelconsumption and associated greenhouse gas emissions isdriving policy such as the European Union (EU) goal forproducing 20% of its electricity with renewable resourcesby 2020. A host of incentives and subsidies is acceleratingEuropean demand for biomass which is expected toamount to 37–44 million metric tons of wood pelletequivalents for co-firing by 2020 (Lamers et al., In Press).An expanding transatlantic trade in wood pellets is a directresult. In 2013, the US will export nearly 3 million bonedry tonnes of wood pellets. As much as 20 million tonnes isexpected to be imported by the EU by 2020,1 with at leastone projection suggesting that as much as 60 millionmetric tonnes of biomass—mostly wood pellets from thesoutheastern US and Canada—could be imported annuallyto the EU out just beyond 2030 (Joudrey et al., 2012).

Given this rapid growth in the use of wood for energy,sustainable sourcing is a core focus of discussions amongststakeholders. Both the energy and forest industries havelong engaged in conversations with society at largeconcerning the sustainability of their function to producematerial and energy resources for society. Many of thesediscussions have yielded improved understanding, newknowledge, and consensus visions, clarifying the way wethink about and perceive complex sustainability issues.

A global wood pellet trade necessitates a much broaderdiscussion about the design and implementation ofsustainability criteria if these criteria are to be effective.There is a clear need for public dialogue concerningemerging “sustainability criteria” or market standardsfocused on the methods by which forest biomass isproduced and procured by energy facilities, and the overall

greenhouse gas emissions effects of increased forest-basedenergy. Two workshops were recently convened to facilitatedialogue between stakeholders in key regions of the worldactive in the global trade in industrial wood pellets.

1

SavannahWorkshop FormatOctober 23–24, 2013

Blending classroom presentation anddiscussion with in-field learning offered aunique platform for improving the under-standing of biomass sustainability within theUS South. Five panel discussions explored:

1 Projected European biomass demand andthe supply response in the US

2 Sustainability of the southern forestresource and sustainability issues in theregions’ private forests

3 The need for easily measurable andeffective sustainability indicators

4 The need for parity between emergingsustainability policies from Europe andsustainability programs and practices inthe US

5 A focused debate on the accounting ofbiogenic and combustion emissions

The field tour focused on biomass supplychains in southeast Georgia, touring industrialand non-industrial timberlands and a pelletmill sourcing low-grade pulpwood from bothcertified and uncertified lands.

THE TRANSATLANTIC TRADE IN

WOOD FOR ENERGY:A Dialogue on Sustainability Standards and Greenhouse Gas Emissions

1 In 2013 the US is expected to export approximately 5.4 million green tonnes of wood pellets.

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Stakeholder Workshops—Improving theTransatlantic DialogueIn October 2012, several Canadian partners working withIEA Bioenergy Task 40 (International Sustainable BioenergyTrade) and IEA Bioenergy Task 43 (Biomass Feedstocks forEnergy Markets) and IEA Bioenergy ExCo facilitated adialogue in Quebec, Canada around the design andimplementation of sustainability criteria within the contextof Canada’s forests (IEA Bioenergy, 2013).2

To explore these issues within the context of the US, thePinchot Institute for Conservation and IEA BioenergyTasks 40 and 43 and IEA Bioenergy ExCo broughttogether more than 60 experts and stakeholders inSavannah, Georgia. Representing conservationorganizations, government agencies, universities, and theforest and renewable energy industries in nine differentcountries, the workshop was organized to exploresustainable forest management (SFM) and the design andimplementation of sustainability criteria within the contextof the world’s largest wood pellet producing region, thesoutheast US. This report summarizes the perspectives anddiscussions offered by participants in the Savannahworkshop. Major themes emerging include:

1.Sustainability is more than calculations of forestgrowth-to-drain.

2.There is a lack of clear understanding about howpellet demand may affect forest management,frustrating all stakeholders and raising questionsabout the sustainability of wood pellet exportmarkets.

3. If the export market for pellets is to expand,European sustainability criteria need to be translatedto the North American context for successfuldeployment.

4.There is a need to reconcile the intent behind theEuropean Commission’s prohibition of biomass fromwetlands with the legally permissible logging ofcertain wetlands in the US.

5.There is emerging agreement around the need toaccount for biogenic carbon and combustionemissions and principles to do so, but expectationsvary significantly.

2

Savannah workshop panelists discuss biodiversity conservation strategies for the South.

BrianKittler

2 The Quebec Workshop summary report is available here: http://www.ieabioenergy.com/publications/the-science-policy-interface-on-the-environmental-sustainability-of-forest-bioenergy/

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BackgroundA Desire to Find Common GroundThe transatlantic trade in wood pellets is of strategicimportance for all countries involved. While Europe couldtechnically produce more of its own biomass, it would comeat much higher prices than if resources are sourced from theUS and Canada. Both of these exporting nations see anopportunity for economic growth but the context is quitedifferent. For Canada, pellet export markets are sourcedfrom mill residues associated with the removal of beetle-killed forests in British Columbia and may possibly besourced from forest industry in the eastern provinces,virtually all of which occurs in the context of largely publiclyowned and certified forests. In the US, wood pellet exportsoffer private landowners additional outlets for low-gradewood, providing an additional revenue source and reducingthe incentive for conversion to non-forested land uses.

Europe and the US share common interests in establishinga substantial trade in wood for energy; this suggests thereare strong incentives for identifying sustainability criteriaapproved by all parties. Yet, there is tension between

European expectations for sustainability criteria and therealities of what may constitute measurable and meaningfulcriteria for the US. There is a sense that greater internationalcooperation is necessary to ensure that sustainability criteriado not inadvertently erect barriers to trade or allowunacceptable environmental impacts.

At present, the policy environment around sustainabilitycriteria is opaque. Belgium is the only EU member statethat requires by law that biomass for energy must beproduced sustainably. Since 2010, the EuropeanCommission (EC) has been considering binding criteriathat would essentially set sourcing requirements forEuropean buyers. It is however appearing increasinglyunlikely that any mandatory criteria will be introducedwithin the next 1-2 years. Given this uncertain policyenvironment, EC member states such as the Netherlandsand Denmark are considering their own country-levelrequirements. These proposals follow recent action takenby the United Kingdom (the single largest source of woodpellet demand) to propose sustainability criteria andbiomass procurement requirements that will go intoeffect April 2014.

3

A representative from one of the world’s largest privately held power utilities converses with a forester working withone of the largest private landowners in the US.

BrianKittler

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All of these efforts focus on requirements for sustainableforest management and third-party verification. Otherelements of proposed frameworks include requirements for:

� Documenting minimum GHG emission reductions

� Avoiding biomass from areas of “high biodiversity”

� Avoiding biomass from wetlands (as defined bythe EU)

� Maintaining or increasing carbon stocks of sourceregions

� Documenting biomass chain-of-custody from theforest to the end consumer

� Verifying via a third party that biomass is “legaland sustainable”

The Savannah workshop sought to begin to clarify whetherexisting forest management and biomass procurementpractices being used in the region satisfy the intent ofexisting and proposed sustainability criteria.

Context of the Southern Forest SystemWorkshop participants saw first-hand what makes thesoutheastern US such a diverse region in forest type,ownership and culture. Almost 90% of the forestland (200million acres) in the 13-state southern region is privatelyowned and governed by a complex mix of market forces,regulations, and voluntary incentive programs.

The region is a major player from a global fiber supplyperspective; more than 60% of US timber is produced inthis region of the number one timber-producing nation.The USDA Forest Service states that the region couldsupport as much as a 40% increase in timber productionfrom 2006–2007 levels (Wear & Greis, 2013).

However, it is important to acknowledge that only 17%of forests in the South are certified to a sustainable forestmanagement standard. More than 53% of all acresenrolled in the American Tree Farm System (ATFS) arelocated in the South, and the region also has the largestconcentrations of SFI certified lands in the US. TheForest Stewardship Council (FSC) has a relatively smallamount of certified land in the region.

The industrial forest estate of the South includes around40 million acres of intensively managed and highlyproductive native pine plantations, most of which arelocated in the coastal plain—the region of focus for theworkshop study tour. While the growth in new plantationacreage has leveled off in most southern states in recentyears, the USDA Forest Service speculates that theplantations may increase by 7–27 million acres by 2050(Wear & Greis, 2013).

While a mix of market forces would shape such anexpansion, workshop presenters surmised that an increase inplantations would be linked to increased demand for pinepulpwood for wood pellets. That said, the projected futureloss of natural forests in the region is forecasted by at leastone presenter to be only marginally associated with woodpellet demand, contrasting with concerns expressed by someenvironmental interests participating in the dialogue.

Forest loss to suburban development is perhaps themajor sustainability issue facing the region, and the nation’sforests. Forest conversion is a major contributing factor forwhy in just a few decades US forests could transition fromcurrently sequestering 12% of US CO2 emissions tobecoming a net source of emissions themselves (USDAForest Service, 2012).3 The loss of natural forests is of greatconcern from a carbon management perspective, as theregion’s intact natural forests are generally more carbondense than its plantation forests. It should be noted,however, that due to intensive investments in silviculture,

4

BrianKittler

Longleaf Pine habitat in the foreground, adjacent to denselyplanted Loblolly Pine in the background.

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annual accumulations of carbon in plantation systems aretypically greater than in natural forests.

The USDA Forest Service predicts that the region couldlose from 11 to 23 million acres of forest by 2060, with thegreatest loss occurring in the Piedmont region when forestproducts markets are weak and development pressuresstrong. To the industry, bioenergy demand (including pelletexports) represents the most significant new market forforest products in the region (Wear & Greis, 2013). Newmarkets for low-grade roundwood create new opportunitiesfor landowners and foresters seeking to improve foreststands. This view was confirmed during the field tour; theindustrial landowners participating in the dialogue notedthat pellet markets allow them to generate revenue fromthinning pine plantations.

Across the South, forest industry-owned timberlandis relatively small in comparison to land owned by

non-industrial private forest (NIPF) landowners, whocontrol two-thirds of forests in the region. These NIPFlands also grow a significant portion of the region’s forestproducts for the forest economy and provide valuablewildlife habitat. More than 60% of the region’s NIPFlands are 100 acres or more in size, meaning that amajority of NIPF lands are capable of generating abiomass supply. Yet, workshop participants were quickto note that only 3% of NIPF landowners in the regionhave a written forest management plan, and only 13%have received forest management advice (Wear & Greis,2013).4 Likewise, many of the landowners considerincome generated through harvesting as only asecondary ownership objective, with many landownersproviding valuable wildlife habitat (Butler, 2008). Thisdiverse population has equally diverse managementobjectives for their forest land, and there is a relativelylow level of interest in enrolling in programs likeforest certification.

5

Southeast Georgia Study Area

The field tour in southeast Georgia was a unique opportunity to explore a location of significant interest tothe wood pellet sector. This sub-region located on the coastal plain has over 7 million acres of forest, 89%of which is privately owned. The majority (61%) is comprised of trees 25 years old or younger, with fastgrowing pine species comprising 57% of the total volume. Currently, more trees are being grown annuallythan harvested, with pines dominating removals. From 1995—2009 just over half of removals in theworkshop study area were pulpwood and 36% was sawtimber. There are over 110 wood-using industrialfacilities in the workshop study area, many of which are certified, sourcing certified and non-certified fiberin their supply chains, and documenting chain-of-custody with Georgia’s load tracking system.

In the region, there are approximately 125,000 acres of non-industrial private forest (NIPF) land enrolled inthe Forest Stewardship Program. There are over 2.2 million acres of land certified by SFI in Georgia, muchof which is likely located in southeast Georgia. In addition the American Tree Farm System has 790,000acres of NIPF land enrolled in 26 counties in southeast Georgia. The reach of SFI is extended through FiberSourcing, a third-party verified program in which wood-using facilities implement a variety of activitiesincluding logger education and training programs. There are over 650 registered Master Loggers within 75miles of Waycross, Georgia, where the Georgia Biomass export pellet plant is located. There is also onelandowner in this area certified by the Forest Stewardship Council (FSC) with over 25,000 acres certified.Some wood-using facilities also use FSC Controlled Wood.

3 Emissions associated with wildfires and tree mortality in the western US and forest loss in the east are cited as reasons for this projectedtrend. Note that this forecasted future is based on national USDA Resource Planning Act (RPA) assessment projections from 2010. Sincethe RPA assessment, USDA has noted that the downturn in US housing markets likely means additional carbon storage in forestsassociated with reduced removals.4 It should be noted that NIPF owners with larger acreages are much more likely than smaller acreage owners to have receivedmanagement advice and/or have a written management plan.

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Themes Emerging fromthe Dialogue1. Key Theme—Sustainability is more than acalculation of growth-to-drain ratio at a fixedpoint in time.

Workshop participants recognized that the South hasgarnered attention from pellet buyers because:

� Southern forests are very productive.

� At the regional level, growth exceeds removals.

� The location is advantageous from a logisticsperspective (e.g. port access).

� Changes in the region’s pulp and paper sector appearto be creating opportunities to utilize relativelyinexpensive low-grade roundwood, with would-bepellet producers seeking out areas where loggingcapacity and landowner relationships now lacklocal markets.

While participants generally concluded these points areimportant factors for why the market is locating in theregion, discussion centered on whether sustainability shouldbe measured by growth-to-drain ratios or should includeother measures. There are new opportunities for additionalwood-using industries in some places, while in others;demand for low-grade pulpwood continues to be strong,even without demand from energy markets. In these places,the growth-to-drain ratio may already be even or declining.Still, participants generally recognized that there are places on

the landscape capable of accommodating new wood pelletoperations, at least from a growth-to-drain perspective.

Others emphasized that while growth-to-drain ratios asmeasured by forest inventory statistics are a convenient wayto understand what is happening at a fixed point in time, thisapproach offers an incomplete view of sustainability overtime.5 There was a sense that more nuanced sustainabilityconcepts must be brought into the conversation.

Participants discussed how biodiversity conservation, waterresource protection, and other tenets, of sustainable forestmanagement are deeply-held values among a diversity ofinterests in the US South, as well as among internationalstakeholders. Local plans for expanded manufacturingcapacity must consider the effects of protecting these valuesas they are assessing the sustainable level of wood supplywithin their expected procurement areas. As a way of doingso, some advocated for risk-based and spatially explicitassessments of pellet mill supply chain sustainability,evaluating:

� Standing inventory excluding areas of high bio-diversity value (i.e. areas with known occurrencesof rare, threatened, or endangered species)

� Current volumes and end-uses

• Certified volumes

• Non-certified volumes that could be mixed withcertified volumes through SFI Fiber Sourcing andFSC Controlled Wood

� Landowner likeliness to harvest

� Assumptions about future land-use change

� Projections for sawtimber and pulpwood markets

� Projected changes in forest and wood productcarbon stocks

2. Key Theme—There is a lack of clearunderstanding of how pellet demand may affectforest management. This uncertainty frustratesall stakeholders and raises questions about thesustainability of the pellet export sector.

A considerable amount of discussion speculated on howpellet demand might influence forest management.Landowners and foresters pointed to new opportunities toutilize material from pre-commercial thinning and harvestresidues that could enhance silvicultural options.

6

BrianKittler

Growth rings show the region’s productive capacity.

5 The cyclical nature of timber and pulp markets has caused growth-to-drain ratios to briefly drop below a 1:1 ratio for a few short timesin the past, but overall regional carbon stocks have strongly increased over the past 50 years. Still, USDA Forest Service projections (Wear& Greis, 2013) suggest future loss of regional forest carbon associated with urbanization.

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Representatives from existing wood using industriesexpressed that some competition may not be a bad thingfor forest sustainability, but that the apparent scale andrapid pace of growth in pellet demand is of concern.

Some speculated that a high level of demand would seehigher volumes of material removed during biomassharvests, necessitating biomass harvesting best managementpractices (BMPs) as a precautionary safeguard. While stillothers noted that the pellet market, given its reliance onrelatively low value fiber, is having little impact on forestmanagement, particularly the integrated harvestingoperation that is commonplace in this region. Conversionof natural forests to plantation forests is of major concernfor some and another instance where the relationship tobioenergy demand is unclear.

Empirical evidence suggests that landowners do respond tomarket signals. Historical examples of this include a spikein tree plantings in the region occurring as sawtimber pricesincreased, and the strong association that exists betweenforest product markets and tree age class. These historicaldata and relationships have been used to model futureconditions. The range of futures presented at the workshopsuggests significant uncertainty in how demand from pelletmarkets might actually affect existing market structures andforest management decisions. Some relayed anecdotes ofdirect competition, or fear of competition, between pelletsand traditional markets, while others saw a morecomplementary relationship in the future.

A recently completed multi-year research effort led by theUSDA Forest Service known as the Southern Forest Futures

Project found that regional prices for pulpwoodroundwood could be affected by energy demand in thefuture, but the study found significant uncertainty onwhen and to what extent. While fraught with uncertainty,long-range regional projections do not show changes inmarkets until aggregate demand increases to a certainthreshold volume. Forecasts completed in association withthe Southern Forest Futures Project suggest that priceswould likely rise when the combined pulpwood gradebiomass demand for domestic consumption and exportsgrows to utilize 45–54 million green tonnes (23–27million tonnes of pellet equivalent). Such price increaseswould likely lead to market restructuring, and dis-placement of some users (Wear & Greis, 2013). Manyagreed there likely would be observable changes in forestmanagement and market structure well before somethreshold of aggregate demand were to be reached.

In addition to a volume of demand (45–54 million greentonnes) that could shift market structures, the SouthernForest Futures Project also speculates that this level ofdemand may be realized around 2030. In 2013, the US willexport approximately 5.4 million tonnes of biomass (2.7million tonnes of pellets) of biomass. Information shared atthe workshop forecasts exports from the region to grow to5.6 million tons of wood pellet by 2020. Other analysissuggests more rapid growth, since another 5.4 milliontonnes of biomass (2.7 million tonnes of pellets) of capacityis projected to come online over the next two years (ArgusGroup, 2013). Still, reaching 45–54 million green tonnesper year would require significant acceleration of growthin both US domestic consumption and exports beyondcurrent levels.

3. Key Theme—If the export market forpellets is to expand, European sustainabilitycriteria need to be translated to the NorthAmerican context for successful deployment.

Participants suggested that the process for defining effective,measurable, and outcome-based sustainability criteriainclude robust dialogue between the US and Europe. Anassociated challenge would be reconciling preferences forthird-party verification of sustainability practices with theownership patterns and culture of the South.

It is clear that requiring a high percentage of SFM certifiedfiber in wood pellet exports will be a challenge, as only17% of forested lands in the South are certified. Therewas a general sense among workshop participants thatin addition to forest management and chain-of-custodycertifications there are other potentially applicablepathways to meeting sustainability requirements, possiblyutilizing a risk-based approach. Requirements for forest

7

BrianKittler

Loblolly Pine plantation thinning visited on the field study tour.

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management certification were generally viewed asunrealistic given the lack of certified land and thatbiomass is a low-value forest product relative to otherproducts removed. Still, some felt that options exist toincrease the share of certified lands in the region andthat energy markets have a role in doing so. During theworkshop an NIPF landowner may have best summedup the issue when he quipped, “show me the money,”suggesting that he would participate in a given marketor sustainability program if presented with a clearfinancial motive.

Some suggested that the process of reconciling Europeanexpectations with on-the-ground realities in the Southpresents opportunities for innovations. Ideas included:

� Expanded use of group certification via forestmanager certification for both FSC and ATFS.However, with only a few foresters in the workshopstudy area presently offering this service, some saw aneed for supply chain investment by pellet millsand/or pellet buyers.

� Augmenting the outreach, education, and trainingaspects of SFI’s Fiber Sourcing program to includeadditional provisions if the procurement area is foundto have a measured risk of not meeting Europeansustainability criteria.

� Devising statistically valid third-party verification,inspection, or monitoring protocols to verifycompliance with European market standards at aregional- or supply area-level in a similar mannerto how voluntary BMP compliance is monitoredby states.

� Expanded utilization of FSC’s Controlled Woodprogram in the region, with augmentation asnecessary to address additional sustainabilitymeasures required by Europe.

� Expanded use of biomass harvesting guidelines suchas South Carolina’s Biomass BMPs.

� Leveraging state administrative capacity to deployprivate funding from pellet buyers through programslike the Forest Stewardship Program for targetedexpansion of forest stewardship plans in theprocurement areas of pellet mills.

Among these suggestions, the idea of a risk-based approach,e.g. regional or supply chain level risk assessments came upmore than once from both European regulators and buyers.This concept was discussed in association with the UK’sCentral Point of Expertise on Timber Procurement (CPET)and again with the Sustainable Biomass Partnership (SBP— formerly the Industrial Wood Pellet Buyers), a coalitionof seven European power companies.

CPET provides practical advice on implementation of theUK’s biomass sustainability criteria, CPET is activelyseeking to understand US systems of wood procurement.For pellets in the South, CPET is largely about the“Category B” evidence route for demonstrating sustainablefiber procurement. Category A is a straightforward defaultto sourcing with SFM certification, with wood needing toinclude at least 70% certified (i.e. “sustainable”) to 30%non-certified content (but “legal”) in order to demonstratethat supplies are both “legal and sustainable.” While notrequiring certification, Category B appears to be quiterigorous in calling for “equivalent evidence” as Category A,(i.e. at least 70% determined by CPET as being from“sustainable” origins, with 100% “legal”).

CPET is actively seeking to understand what may qualify asevidence for compliance with Category B for wood pelletsoriginating in the Southeast US, and has indicated thatsuch an assessment may include state if not county levelstudy. At the workshop, several US programs were discussedas potential means to comply with aspects of Category B,but it is clear that additional consideration of theseapproaches is necessary.

Some participants wondered whether state-level periodicmonitoring of BMP compliance should be explored inrelation to CPET’s expectations for third-party verification,and if need be, might state monitoring programs change tomeet this requirement. Other participants wondered ifthird-party verification is really necessary (and feasible) atthe level of the pellet mill supply chain. The concept ofsupplier risk-based assessments for each principle and

8

BrianKittler

A timber harvest load ticket used to track harvested woodin Georgia’s fiber market.

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criteria listed in Category B was also discussed, withworkshop participants wondering how such a risk-assessment might compare with the type of risk assessmentdescribed above in Key Theme 1 (see page 6).

Other things being evaluated by CPET include a mix of:� Forest management plans (participation in the Forest

Stewardship Program, for instance)

� Implementation of BMPs

� Contractor training, and specifically trainingssponsored by facilities using SFI Fiber Sourcing

� Supply area risk assessments, looking at a range ofissues, including controls for minimizing harm toecosystems, maintaining forest productivity, andensuring ecosystem health and vitality

� FSC Controlled Wood and PEFC Avoidance ofControversial Sources

4. Key Theme—There is a need to reconcilethe intent behind the European Commission’sprohibition of biomass from wetlands with thelegally permissible logging of certain wetlandsin the US.Proposed criteria from the European Commission suggesta prohibition of biomass sourced from wetlands. This isassumed to be due to the ecological value of wetlands in

providing biodiversity, water quality, and carbon storage.A few issues surfacing in discussions illustrate a need forclarifying the intent of this criterion:

� There appears to be no universally accepteddefinition of wetlands (in part because there aremany types), making a prohibition problematic in itsimplementation, especially given that some wetlanddesignations are somewhat subjective.

� It is legal to practice silviculture in wetlands in theUS, meaning that logging of forested wetlands ispermitted as long as wetland hydrology and existinglaws requiring best management practices (BMPs) formaintaining water quality and protecting endangeredspecies are abided by.

� Some wetlands that were previously drained andconverted to agriculture and later pine plantationscontribute important volumes of fiber. Yet, drainingof additional lands is prohibited under the “swampbuster” provisions of the Clean Water Act. Theregeneration of Loblolly pine in Southern forestsrequires no major drainage activities.

The South is the most biodiverse region of the US, andmuch of this diversity occurs in bottomland hardwoodforested wetlands, most of which are privately owned. Ofkey conservation concern are relict older age bottomlandsystems that are quite rare. While pine plantations typicallyhave lower biodiversity value as compared to bottomland

9

CPET Category B Requirements

1.Third-party verification of items 2, 3 and 4 below

2.Demonstrate Chain-of-Custody/traceability in the supply chain to the forest source for 70% ofmaterial, where 70% must be legal and sustainable, with balance being legal)

3.Demonstrate the harvested fiber complies with applicable laws

4.Demonstrate the site-specific sustainability of the source of 70% of harvested fiber, includingthird-party verification of this sustainability

a. A locally applicable definition of sustainability is required

b. Specific requirements for how the definition was developed (multi-stakeholder process etc.)

c. Overall forest management principles and criteria to:

i. Minimize harm to ecosystems

ii. Maintain forest productivity

iii. Ensure forest ecosystem health and vitality

iv. Maintain biodiversity

v. Include social criteria

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systems, environmental interests have expressed concernthat pellet demand would not be constrained to plantationforests and would spill over into wetland forests. Others feltthat risks to areas of high conservation value are adequatelymitigated through existing law—such as the FederalEndangered Species Act and Federal Clean Water Act—and procurement practices such as using SFI’s Forestsof Exceptional Conservation Value and/or FSC’s HighConservation Value Forests and CPET’s procurement rules.Under these programs, ecological communities andspecies at risk of becoming endangered—rather than justendangered species—must be located and associated landsspecifically managed for these communities and species.

5. Key Theme—There is emerging agreementaround the need to account for biogenicand combustion carbon emissions and theprinciples to do so, but expectations varyfrom stakeholder to stakeholder.The last three years have seen increased debate and scientificresearch into the climate effects of forest bioenergy. Thereappears to be increasing agreement, at least among thoseparticipating in this workshop, that forest bioenergy hasdefinite greenhouse gas mitigation benefits as compared tofossil fuel alternatives, but in the workshop there was adisagreement over whether there is a time lag (or carbondebt) before those benefits are realized. Presenters at theworkshop synthesized findings from the majority of biogeniccarbon accounting studies completed over the last twodecades. The overwhelming majority of these studies find

that compared to fossil fuel energy systems, forest bioenergyhas greenhouse gas mitigation benefits in the long run.

The majority of studies find these benefits beginningto accrue 30–50 years after the start of the system, butpayback periods in these studies vary from virtuallyimmediate (within two years), to quite long into the future,with the timing depending heavily on assumptions,methods, and regional differences, but also on severalcomponents of forest bioenergy systems (e.g. feedstock typeand origin, energy technology, fossil fuel replaced, etc.).

With the carbon debt question occupying significantattention in recent years, one perspective underscoredduring the workshop is that while the greenhouse gasprofile of forest bioenergy is extremely important, it isnot the sole metric by which bioenergy should be judgedas sustainable or not. Moreover, some cautioned that thereis a need to differentiate between sustainability criteriafor carbon management and sustainability criteria forsustainable forest management, suggesting that these donot always necessarily go hand-in-hand. There is a needto differentiate between carbon accounting and other areasof sustainability (e.g. wetlands, biodiversity) in order toidentify potential tradeoffs between carbon and othercomponents of sustainability.

Beyond these basic points of understanding, the dialoguehighlighted areas where stakeholders diverge and convergein their views.

BrianKittler

A non-industrial private forest parcel in Wayne County, Georgia.

10

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Convergent ideas and principles:� Policy should not be based on modeling alone.

Stakeholder vetting is important, as is scientificdebate.

� Policy options for controlling greenhouse gasemissions vary (e.g. greenhouse gas calculators andemissions default units, system-wide performancestandards, regulation of acceptable and non-acceptable feedstocks, ignore the issue, incentivizecertain energy systems to be developed) and theselection of policy options will incentivize what sortof energy system is ultimately deployed.

� Best practices or performance standards for bioenergy(forest management practices, energy technologies,forest types, etc.) could be developed to emphasizebioenergy systems with greater potential forgreenhouse gas mitigation benefits.

• Sustainable forest management is fundamental.

• In the South there may be opportunities to increaseplanting density of plantations and use pre-commercial thinnings for biomass.

• Using marginal and unused land for feedstockproduction generally creates immediate net carbonbenefits.

• Utilizing mill residuals and logging residues accruecarbon/climate benefits quickly.

� Concerning the math of carbon accounting, areas ofagreement include:

• Accounting is incomplete if emissions and re-sequestration within the forest sector are ignored,and if net changes in energy and material stocks arenot properly examined. Policy needs to reflect this.

• The construction of baseline scenarios should bebased on real-world data on actual forestmanagement patterns and economics, referencefossil fuel energy systems, as well as underlyingtransport systems for both bioenergy and referencefossil-based energy scenarios. Getting the baselineright is key to determining the time lag until netgreenhouse gas emission benefits are achieved.

• There is emerging consensus within the scientificcommunity that determining the overall climatemitigation potential of bioenergy requires goingbeyond mere carbon accounting, i.e. incorporatingassessments of the albedo effect and climatedynamics (e.g. pulse emission responses).

Divergent ideas and principles:� There is disagreement over whether any delay in the

timing of climate mitigation benefits (even short-term delays) should be considered acceptable, even inareas where overall forest carbon stocks are positiveand increasing, and can be forecasted to do so intothe future.

� There is lack of agreement around the acceptablelength of payback periods, with some objecting to theconcept of a carbon debt because they believe it doesnot accurately credit landowners with past andcontemporaneous actions taken to regrow foreststocks.

� While participants agreed that getting baseline andreference scenarios accurately defined is of centralimportance, opinions varied with regards to baselineforest management futures (e.g. wood is harvested,used for pulp, and replanted, or wood is harvested forpulp and land is converted to other uses, or woodremains growing for several more years, etc.).

� There is disagreement over how to evaluate theeconomic effects of bioenergy demand at a regionalscale and the resultant greenhouse gas emissionseffects from the forest energy sector. Some studieshave largely ignored future market effects on plantingrates and forest management activity with increasedenergy demand. Others attempting to integrate theeconomics of bioenergy demand find that bioenergydemand in the South might contribute to alandscape-level management response (more acresplanted, acres managed more intensively, less acresconverted to other uses) that offers greenhouse gasmitigation benefits.

� Perspectives and definitions matter, as one’s residuemay be another’s roundwood.

� Stakeholders have varying perspectives regarding therole forest certification systems play, or could play, inincentivizing climate-friendly bioenergy.

� Some felt that SFM certification standards shouldinclude greenhouse gases in a meaningful way. Othersfelt that this should be held off until a properframework for accounting is fully agreed upon.

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Conclusion

The Savannah workshop was a unique opportunity tobring together a broad spectrum of stakeholders to evaluatesustainability issues—particularly biomass sourcingoptions—at a critical moment in the development of theglobal wood pellet trade.

A key objective was to increase the collective understand-ing of sustainable procurement options already in use inthe South and how these systems match up to Europeandemand. Connections among participants werestrengthened for future cooperation in hopes ofestablishing meaningful sustainability criteria. Theseconnections are key to informing ongoing processessuch as the deliberations of the Sustainable BiomassPartnership and governmental bodies throughout Europeand North America.

Key points of discussion highlighted the need to:� Expand our understanding of sustainability concepts

beyond simple growth-to-drain calculations

� Clarify understanding of how pellet demand mayaffect forests and forest products markets inthe future

� Negotiate scientifically robust and effective Europeansustainability criteria (third-party verification,risk assessment and mitigation, etc.) and developprocedures for satisfying these criteria within the US

� Continue the dialogue around biogenic andcombustion emissions with a focus on (1) enhancingscientific understanding of the complexities involved,and (2) analyzing intended and unintendedconsequences of policy and regulatory options

Substantial common ground was established among thediversity of organizations and individuals participating.There is an active interest from all parties in follow-ondialogue that would allow remaining differences to beaddressed and workable solutions found. Some of theparticipants who were most doubtful about the feasibilityof addressing European concerns over sustainable sourcingprior to the workshop, from both Europe and the US,were subsequently among those expressing the strongestreassurance that practical solutions can be found. Severalin attendance recommended follow on discussions toresolve remaining issues, including a repeat of such anevent in a year’s time. Stakeholders identified a commonpurpose in identifying meaningful criteria so that buyershave reliable assurance that standards are being met,sellers have viable markets, and the public gets renewableenergy without harming the environment.

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Workshop participants from the US and Europe learning how fiber moves to market in the Coastal Plain of Georgia.

BrianKittler

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“Sustainability is a prerequisite for the use and further growth of solid woody biomass in energy

applications. This event was a unique opportunity for energy, forestry, and conservation interests in the

United States and Europe to examine the opportunities and challenges for the energy industry to

contribute to the sustainability of a renewable resource in the southeast US.”—Volker Türk, Manager Corporate Responsibility, E.ON Climate & Renewables

“Certainly I got updated on evolving policy in the EU. But even more importantly, I met key governmentand industry personnel from both sides of the Atlantic, and started what have already become constructiverelationships.”

—Ben Larson, Manager Agriculture Program, National Wildlife Federation

“This event has made an outstanding contribution to the much needed dialogue among stakeholders

engaged in and concerned about trans-Atlantic trade in wood pellets for energy. It was a necessary follow-

on from a dialogue between North Americans and Europeans initiated in Quebec in 2012. The indoor

sessions provided ample opportunity to dive deeply into controversial and technical details regarding the

forest sector in the southern US and to collectively gain new levels of understanding about timber supply,

private and industrial landowner approaches to sustainable forest management, and ways in which land

use and conservation and forest products markets might be impacted by European demand for wood

pellets. The field tour gave European colleagues a first-hand look at management of privately-owned

southern pine plantations and an opportunity to speak directly with industrial foresters and an award

winning, well-respected southeast Georgia farmer and forest landowner. The field tour translated abstract

concepts discussed indoors into something first-hand and real—we saw sustainably managed forests that

have been owned and managed for multiple uses over several generations by honest and hard-working

people who have to make a living off the land and who care deeply about conservation of the land and

the region’s forests. The Quebec and Savannah events must be continued as there are many controversial

issues that need to be resolved through intense debate and discussion before we find ‘common ground’ on

what constitutes sustainable forest management for bioenergy and fair and equitable governance systems

to ensure conservation of our forests and mitigation of climate change.”—C. Tat Smith, Univeristy of Toronto and IEA Bioenergy Task 43

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Testimonials from Participantsin the Savannah Workshop

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Works CitedButler, B. J. (2008). Family Forest Owners of the UnitedStates, 2006. Gen. Tech. Rep. NRS-27. . Newtown Square,PA:: U.S. Department of Agriculture, Forest Service,Northern Research Station. 72 p.

IEA Bioenergy. (2013). The Science-Policy Interface on theEnvironmental Sustainability of Forest Bioenergy: AStrategic Discussion Paper. IEA Bioenergy: ExCo:2013:03.IPCC. (2011). IPCC Special Report on Renewable EnergySources and Climate Change Mitigation. New York:Cambridge University Press. Retrieved fromhttp://srren.ipcc-wg3.de/report

Joudrey, J., McDow, W., Smith, T., & Larson, B. (2012).European Power from U.S. Forests: How Evolving EUPolicy is Shaping the Transatlantic Trade in Wood Biomass.Washington, DC: Environmental Defense Fund.

Lamers, P., Hoefnagels, R., Junginger, M., Hamelinck, C.,& Faaij, A. (In Press). Global Solid Biomass Trade forEnergy by 2020: An Assessment of Potential ImportStreams and Supply Costs to North-West Europe UnderDifferent Sustainability Constraints. Global ChangeBiology Bioenergy.

Stewart, I. (2013). Energy and Commodity PriceBenchmarking and Market Insights: US Biomass Supplyin 2013 and Beyond. Argus Media.

USDA Forest Service. (2012). Future of America’s Forestand Rangelands: Forest Service 2010 Resources PlanningAct Assessment. Gen. Tech. Rep. WO-87. Washington,DC.: USDA Forest Service.

Wear, D. N., & Greis, J. G. (2013). Southern ForestFutures Project: Tec hnical Report. (SRS-GTR-178).Ashville, NC: USDA Forest Service, SouthernResearch Station.

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Participant ListBob AbtProfessor of Forest Resource EconomicsNorth Carolina State [email protected]

Ken ArneyDeputy Regional ForesterUSDA Forest Service, Southern [email protected]

Chris ArthersEssent [email protected]

Nadine BlockSustainable Forestry [email protected]

Jessica BrooksDeputy DirectorUS Industrial Pellet [email protected]

Thomas BuchholzSpatial Informatics [email protected]

Todd BushVP Sales and MarketingGreen Circle Bio [email protected]

David CarrGeneral CounselSouthern Environmental Law [email protected]

FG Courtney-BeauregardManager, Southeast Sustainable

BioenergyNational Wildlife [email protected]

Virginia DaleDirector, Center for Bioenergy

SustainabilityOak Ridge National [email protected]

Wade DubeaState ForesterLouisiana Department of [email protected]

Judy DunscombSenior Conservation ScientistThe Nature [email protected]

Gustaf EgnellAssociate professorSwedish University of

Agricultural [email protected]

Bob EmorySouthern Timberlands Environmental

Affairs [email protected]

Jason EvansEnvironmental Sustainability AnalystUniversity of [email protected]

Zander EvansForest [email protected]

Rob FarrisState ForesterGA Forestry [email protected]

Bob FleddermanManager, Emerging [email protected]

Emily [email protected]

Uwe [email protected]

Chris GalikSenior Policy AssociateDuke [email protected]

Seth GintherExecutive DirectorUS Industrial Pellet [email protected]

Chun Sheng GohUtrecht [email protected]

Michel GroeneveldCommercial Project Manager BiomassE.ON Climate & [email protected]

Bo HektorFirst Bioenergy [email protected]

Richard HessDirectorIdaho National Laboratory/Energy

Systems & Technologies [email protected]

Jacob JacobsonEngineerIdaho National [email protected]

Jennifer JenkinsClimate Change Division, Office of

Atmospheric ProtectionUS [email protected]

Michael JostromDirector Renewable ResourcesPlum Creek Timber [email protected]

Martin JungingerUtrecht [email protected]

Christian KammerTechnical OfficerPEFC [email protected]

Brian KittlerProject DirectorPinchot Institute for [email protected]

Keith KlineSenior Research StaffOak Ridge National [email protected]

Patrick LamersUtrecht [email protected]

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Stanley LanceyEconomistAmerican Forest & Paper [email protected]

Fanny-Pomme LanguePolicy DirectorAEBIOM - European

Biomass [email protected]

Ben LarsonAgriculture Program ManagerNational Wildlife [email protected]

Dan LenRegional Woody Biomass CoordinatorUSDA Forest Service, Southern [email protected]

Jonathan LoweryHarvest Scheduling ManagerThe Westervelt [email protected]

Leitre [email protected]

Julian MatzenbergerResearcher, Energy Economics GroupVienna Univ. of [email protected]

Nathan McClureChief ForesterGeorgia Forestry [email protected]

Reid MinerVice [email protected]

Asger OlesenEuropean [email protected]

Olle OlssonResearch FellowStockholm Environment [email protected]

Carlton OwenU.S. Endowment for Forestry

and [email protected]

David ParéRessources Naturelles [email protected]

Barry ParrishGeorgia [email protected]

Richard PeberdyVice-President, SustainabilityDrax Biomass International [email protected]

Luc PelkmansProject [email protected]

Stephen PrisleyAssociate Professor, Forest

Inventory & GISVirginia [email protected]

Jörgen RansmarkStrategistE.On [email protected]

David RefkinGreenPath Sustainability [email protected]

Matthew RudolfRegional Director, AmericasRSB Services [email protected]

Guy SabinSouth Carolina Forestry [email protected]

V. Alaric SamplePresidentPinchot Institute for [email protected]

Peter-Paul SchouwenbergSenior Officer Regulatory &

Corporate [email protected]

Robert SimpsonPresident & CEOGreenWoodGlobal Consultiing, [email protected]

Tat SmithUniversity of [email protected]

Inge StupakAssociate ProfessorUniversity of [email protected]

Volker TürkManager, Corporate ResponsibilityE.ON Climate & [email protected]

Mieke VandewalPCU [email protected]

DaveWearUSDA Forest ServiceSouthern Research [email protected]

ElizabethWoodworthDirector of Marketing,

Communications and SustainabilityEnviva [email protected]

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About the Pinchot Institute for ConservationThe mission of the Pinchot Institute is to strengthenforest conservation thought, policy and action bydeveloping innovative, practical, and broadly supportedsolutions to conservation challenges and opportunities.Pinchot Institute accomplishes this through nonpartisanresearch, education and technical assistance on key issuesinfluencing the future of conservation and sustainablenatural resource management.

About IEA BioenergyIEA Bioenergy is an organisation set up in 1978 by theInternational Energy Agency (IEA) with the aim ofimproving cooperation and information exchangebetween countries that have national programmes inbioenergy research, development and deployment.

Savannah workshop participants.

BrianKittler

© 2014 Pinchot Institute for Conservation

Designed by Judith Barrett Graphics, Alexandria, Va.

Printed by HBP, Falls Church,Va.

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