Woody Biofuels: Past, Present and Future
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FAOSTAT-Forestry Definitions
FOREST PRODUCTS DEFINITIONS General terms FAOSTAT - Forestry JOINT FOREST SECTOR QUESTIONNAIRE Item Item Code Definition code coniferous C Coniferous All woods derived from trees classified botanically as Gymnospermae, e.g. Abies spp., Araucaria spp., Cedrus spp., Chamaecyparis spp., Cupressus spp., Larix spp., Picea spp., Pinus spp., Thuja spp., Tsuga spp., etc. These are generally referred to as softwoods. non-coniferous NC Non-Coniferous All woods derived from trees classified botanically as Angiospermae, e.g. Acer spp., Dipterocarpus spp., Entandrophragma spp., Eucalyptus spp., Fagus spp., Populus spp., Quercus spp., Shorea spp., Swietonia spp., Tectona spp., etc. These are generally referred to as broadleaves or hardwoods. tropical NC.T Tropical Tropical timber is defined in the International Tropical Timber Agreement (1994) as follows: “Non-coniferous tropical wood for industrial uses, which grows or is produced in the countries situated between the Tropic of Cancer and the Tropic of Capricorn. The term covers logs, sawnwood, veneer sheets and plywood. Plywood which includes in some measure conifers of tropical origin shall also be covered by the definition.” For the purposes of this questionnaire, tropical sawnwood, veneer sheets and plywood shall also include products produced in non-tropical countries from imported tropical roundwood. Please indicate if statistics provided under "tropical" in this questionnaire may include species or products beyond the scope of this definition. Year Data are requested for the calendar year (January-December) indicated. 2 Transactions FAOSTAT - Forestry JOINT FOREST SECTOR QUESTIONNAIRE Element Element Code Definition code 5516 Production Quantity Removals The volume of all trees, living or dead, that are felled and removed from the forest, other wooded land or other felling sites. -
Quality Wood Chip Fuel Depends on the Size of the Installation in Which It Is to Be Used: Pieter D
Harvesting / Transportation No. 6 The quality requirements for wood chip Quality wood chip fuel depends on the size of the installation in which it is to be used: Pieter D. Kofman 1 Small boilers (<250 kW) require a high quality wood fuel with a low moisture content (<30%) and a small, even chip with few, if any, Quality wood fuel depends mainly on: oversize or overlong particles. A • moisture content, low level of fungal spores is required. • particle size distribution, Medium boilers (250 kW<X<1 MW) • tree species, are more tolerant of moisture content (30-40%) and can handle a • bulk density, coarser chip than small boilers. • level of dust and fungal spores in the fuel, and Still, the amount of oversize and overlong particles should be • ash content. limited. A low level of fungal spores is required. Good quality wood chip fuel is produced by machines with sharp knives, with the ability to vary the size of chip produced to meet end-user specifications. Other Large boilers (>1 MW) are tolerant machines use hammers or flails to reduce particle size and produce hogfuel, of both moisture content (30-55%) and chip quality. The level of fungal which is unsuitable for use in small installations. Large installations can, spores can be higher because however, also have problems in handling and combusting hogfuel. For forest these installations usually take thinnings and other roundwood, chipping is the preferred option. their combustion air from the chip silo which reduces spore This note deals with wood chips only, even though there are other wood fuels, concentrations in and around the such as hogfuel, sawdust, firewood, peelings from fence posts, etc. -
SHELTON RESEARCH, INC. 1517 Pacheco St
SHELTON RESEARCH, INC. 1517 Pacheco St. P.O. Box 5235 Santa Fe, NM 87502 505-983-9457 EVALUATim OF LOW-EMISSION WOOD STOVES by I Jay W. Shelton and Larry W. Gay Shelton Research, Inc. P.O. Box 5235 ! 1517 Pacheco Street Santa Fe, New Mexico 87501 [ June 23, 1986 FINAL REPORT I OON1RACT A3-122-32 Prepared for CALIFORNIA AIR RESOURCES BOARD P.O. Box 2815 1102 Q Street Sacramento, California 95812 Shelton Research, Ince Research Report No. 1086 I, TABLE CF CDmN.rS la PAGE 1' 1 LIST Clii' T~S••••••••••••••••••••••••••••• I~ LIST OF FIGURES •••••••••••••••••••••••••••• ii r } 1. SlM'v1ARY AND CINa.,USICNS •••••••••••••••••••• 1 ~- 2. RE~T1rns•••••••••••••••••••••••••••• 3 ! 3. I N'IRmJCTI. rn••••••••••••••••••••••••••••••• 4 4. APPLIANCE AND FUEL SELECTirn••••••••••••••• 5 5. 'IEa-IN"I oo_, JI'IIDAOI. •••.•••••...•.•••••.•••. 14 Test cycles •••••••••••••••••••••••••••••• 14 Installation••••••••••••••••••••••••••••• 16 Stove Q?eration•••••••••••••••••••••••••• 16 Fuel Properties•••••••••••••••••••••••••• 16 Measursnent Methods •••••••••••••••••••••• 18 Data Acquisition and Processing•••••••••• 29 r; 6. RESlJI..,TS. • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • 30 J Introduction••••••••••••••••••••••••••••• 30 Units for Fmissions •••••••••••••••••••••• 30 E:x: tra Tes ts •• ., •• "•••••••••••••••••••••••• 30 Particulate Matter ••••••••••••••••••••••• 31 Oeosote•••••• ., •••••••••••••••••••••••••• 32 P.AII. ••••••••••• o • •••••••••••••••••••••••• 32 l NOx •••••••••• t.10••·········· ............. 32 .Amoonia and cyanide•••••••••••••••••••••• -
PITT Research Brief Pyrolysis
POTENTIAL PFAS DESTRUCTION TECHNOLOGY: PYROLYSIS AND GASIFICATION In Spring 2020, the EPA established the PFAS Innovative Treatment Team (PITT). The PITT was a multi-disciplinary research team that worked full-time for 6-months on applying their scientific efforts and expertise to a single problem: disposal and/or destruction of PFAS- contaminated media and waste. While the PITT formally concluded in Fall 2020, the research efforts initiated under the PITT continue. As part of the PITT’s efforts, EPA researchers considered whether existing destruction technologies could be applied to PFAS-contaminated media and waste. This series of Research Briefs provides an overview of four technologies that were identified by the PITT as promising technologies Figure 1. Biosolids beneficial use. for destroying PFAS and the research underway by the readily available, cost effective, and produce little to no EPA’s Office of Research and Development to further hazardous residuals or byproducts. Pyrolysis and explore these technologies. Because research is still gasification have been identified as promising needed to evaluate these technologies for PFAS technologies that may be able to meet these destruction, this Research Brief should not be considered requirements with further development, testing, and an endorsement or recommendation to use this demonstrations. technology to destroy PFAS. Background Pyrolysis/Gasification: Technology Overview Pyrolysis is a process that decomposes materials at Various industries have produced and used per- and moderately elevated temperatures in an oxygen-free polyfluoroalkyl substances (PFAS) since the mid-20th environment. Gasification is similar to pyrolysis but uses century. PFAS are found in consumer and industrial small quantities of oxygen, taking advantage of the products, including non-stick coatings, waterproofing partial combustion process to provide the heat to materials, and manufacturing additives. -
Mean Annual Volume Increment of Selected Industrial Species
Forestry Department Food and Agriculture Organization of the United Nations Forest Plantations Thematic Papers MEAN ANNUAL VOLUME INCREMENT OF SELECTED INDUSTRIAL FOREST PLANTATION SPECIES Based on the work of Luis Ugalde and Osvaldo Pérez Consultants Edited by D. J. Mead April 2001 Forest Resources Development Service Working Paper FP/1 Forest Resources Division FAO, Rome (Italy) Forestry Department 2 Disclaimer The Forest Plantation Thematic Papers report on issues and activities in forest plantations as prepared for FRA 2000. These working papers do not reflect any official position of FAO. Please refer to the FAO website (http://www.fao.org/forestry) for official information. The purpose of these papers is to provide early information on on-going activities and programmes, and to stimulate discussion. Comments and feedback are welcome. For further information please contact: Mr. Jim Carle, Senior Forestry Officer (Plantations and Protection), Forest Resources Development Service Forest Resources Division Forestry Department FAO Viale delle Terme di Caracalla I-00100 Rome (Italy) e-mail: [email protected] For quotation: FAO (2001). Mean annual volume increment of selected industrial forest plantation species by L Ugalde & O Pérez. Forest Plantation Thematic Papers, Working Paper 1. Forest Resources Development Service, Forest Resources Division. FAO, Rome (unpublished). 3 ABSTRACT This paper provides a global overview of forest plantation growth rates, with a particular focus on mean annual volume increment (MAI) of the main species planted in developing countries. Documented growth data from both trials and plantations is presented, and the difficulty of translating trial data to commercial scale is highlighted. The main technical issues and pitfalls relating to MAI measurement and the preparation and growth models used are included. -
Tree Care Handbook
Minnesota SWCD Forestry Association Tree Handbook Dear Tree Planter. With headlines reporting the continuing deforestation of the tropical rain forest, one may ask the question: Are America’s forests in danger of disappearing? Because people such as yourself practice reforestation, our forested acres are actually growing in size. About one-third of the United States, or 731 million acres is covered with trees. That’s about 70 percent of the forest that existed when Columbus discovered America. Almost one third of this is set aside in permanent parks and wilderness areas. Minnesotans’ have planted an average of 12 million trees annually; enough trees to cover over 15,000 acres per year. Good land stewards are planting trees for many good reasons. The results of their efforts can be seen in reduced soil erosion, improved air and water quality, healthy forest industries, enhanced wildlife habitat and generally a more attractive surrounding for us to live in. Aspen has become the most prominent tree in Minnesota’s forests. After clearcutting, aspen regenerates readily by sprouting from its root system or by drifting seeds onto disturbed sites. Most of the other major species in Minnesota need some help from tree planters to ensure that they make up a part of the new forest. The following pages will help explain how to plant and care for a tree seedling. There is a section on the general characteristics and planting requirements of the tree and shrub species commonly planted for conservation purposes in Minnesota. The professionals working in conservation throughout Minnesota thank you for planting, nurturing and wisely using one of Minnesota’s greatest treasures its renewable trees. -
Code of Practice for Wood Processing Facilities (Sawmills & Lumberyards)
CODE OF PRACTICE FOR WOOD PROCESSING FACILITIES (SAWMILLS & LUMBERYARDS) Version 2 January 2012 Guyana Forestry Commission Table of Contents FOREWORD ................................................................................................................................................... 7 1.0 INTRODUCTION ...................................................................................................................................... 8 1.1 Wood Processing................................................................................................................................. 8 1.2 Development of the Code ................................................................................................................... 9 1.3 Scope of the Code ............................................................................................................................... 9 1.4 Objectives of the Code ...................................................................................................................... 10 1.5 Implementation of the Code ............................................................................................................. 10 2.0 PRE-SAWMILLING RECOMMENDATIONS. ............................................................................................. 11 2.1 Market Requirements ....................................................................................................................... 11 2.1.1 General .......................................................................................................................................... -
CO2 REMOVAL from WOOD GAS Dahiru Rufai Ahmed
FACULTY OF TECHNOLOGY CO2 REMOVAL FROM WOOD GAS Dahiru Rufai Ahmed Master’s Thesis Master’s Degree Programme (BCBU) Environmental Engineering September 2013 1 UNIVERSITY OF OULU Abstract Thesis Faculty of Technology Department Degree Programme Department of Process and Environmental Master’s Degree Programme (BCBU) in Engineering Environmental Engineering Author Supervisor Dahiru, Rufai Ahmed Tanskanen, J., Professor Title of the thesis CO2 Removal from Wood Gas Study option Type of the thesis Submission date Number of pages Sustainable Energy Master’s Thesis 11th September, 2013 94 + 4 Appendix Abstract Gasification is considered as one of the most attractive conversion technologies, because the product gas from the process serves as a building block for several industrial applications. However, the use of biomass as a fuel in the gasification process offers a carbon neutral fuel that will alleviate the continuing use of fossil fuels sources. This study was done to evaluate the possible applications of syngas originating from biomass gasification, as a follow up to the earlier biomass gasification research of the HighBio project. The syngas from the gasification process is generally produced in a gasifier. An overview of the different type of gasifiers for biomass gasification that include updraft, downdraft, crossdraft, entrained-flow and plasma gasifiers was presented. The syngas can be utilized in the generation of power, heat, fuels and chemicals. A detailed overview of the promising applications of the syngas in Fischer-Tropsch synthesis, hydrogen production, ammonia synthesis, hydroformylation of olefins, and syngas fermentation was also given. However, for these applications, a high degree of treatment and conditioning of the syngas is required. -
Wood Products: Thermal Degradation and Fire
Wood Products: Thermal Degradation and off. The hemicelluloses and lignin components are pyrolyzed in the ranges 200-300°C and 225-450 °C, Fire respectively (see Wood, Constituents of). Much of the acetic acid liberated from wood pyrolysis is attributed Wood is a thermally degradable and combustible to deactylation of hemicellulose. Dehydration reac material. Applications range from a biomass provid tions around 200°C are primarily responsible for ing useful energy to a building material with unique pyrolysis of hemicellulose and lignin and results in a properties. Wood products can contribute to unwant high char yield for wood. Although cellulose remains ed fires and be destroyed as well. Minor amounts of mostly unpyrolyzed, its thermal degradation can be thermal degradation adversely affect structural pro accelerated in the presence of water, acids, and oxygen. perties. Therefore, knowledge of the thermal degrad As the temperature increases, the degree of poly ation and fire performance of wood can be critical in merization of cellulose decreases further, free radicals many applications. Chemical treatments are available appear, and carbonyl, carboxyl, and hydroperoxide to improve fire performance characteristics. groups are formed. Bryden (1998) assumed tar under- goes cracking to lighter gases and repolymerization to char while streaming through the hot charred residue. Overall pyrolysis reactions are endothermic due to 1. Thermal Degradation decreasing dehydration and increasing CO formation As wood reaches elevated temperatures, the different from porous char reactions with H2O and CO2 with chemical components undergo the thermal de- increasing temperature. During this “low-temperature gradation that affects the performance of wood. The pathway” of pyrolysis, exothermic reactions of ex- extent of the changes depends on the temperature level posed char and volatiles with atmospheric oxygen are and length of time under exposure conditions. -
Hardwood-Distillation Industry
HARDWOOD-DISTILLATION INDUSTRY No. 738 Revised February 1956 41. /0111111 110 111111111111111111 t I 1, UNITED STATES DEPARTMENT OF AGRICULTURE FOREST PRODUCTS LABORATORY FOREST SERVICE MADISON 5, WISCONSIN. In Cooperation with the University of Wisconsin 1 HARDWOOD-DISTILLATION INDUSTRY— By EDWARD BEGLINGER, Chemical Engineer 2 Forest Products Laboratory, — Forest Service U. S. Department of Agriculture The major portion of wood distillation products in the United States is obtained from forest and mill residues, chiefly beech, birch, maple, oak, and ash. Marketing of the natural byproducts recovered has been concerned traditionally with outlets for acetic acid, methanol, and charcoal. Large and lower cost production of acetic acid and methanol from other sources has severely curtailed markets formerly available to the distillation in- dustry, and has in turn created operational conditions generally unfavor- able to many of the smaller and more marginal plants. Increased demand for charcoal, which is recovered in the largest amount as a plant product, now provides a compensating factor for more favorable plant operation. The present hardwood-distillation industry includes six byproduct-recovery plants. With the exception of one smaller plant manufacturing primarily a specialty product, all have modern facilities for direct byproduct re- covery. Changing economic conditions during the past 25 years, including such factors as progressively increasing raw material, equipment, and labor costs, and lack of adequate markets for methanol and acetic acid, have caused the number of plants to be reduced from about 50 in the mid- thirties to the 6 now operating. In addition to this group, a few oven plants formerly practicing full recovery have retained the carbonizing equipment and produce only charcoal. -
Sustainability Report for Georgia's Forests
Executive Summary Georgia’s forests are being sustainably managed to meet the numerous needs of our state today. To ensure our forests will continue to meet the needs of present generations and the projected demands for future generations, many challenges must be addressed. Forest sustainability is dependent on both environmental and economic sustainability. A challenge to either element is a challenge to both elements. Success will depend on proactive decisions by our state leaders and the entire forestry and conservation communities addressing a myriad of forestry-related issues. Georgia boasts more than 24 million acres of forestland. Georgia’s forest inventory volumes are at an all-time high. We have 49 percent more cubic feet of wood growing in Georgia than we did 40 years ago. However, the state’s population is increasing at a record rate. Urbanization continues to be a threat to forest sustainability. Further, recent increases in population and changing land-use patterns have made ongoing forest management more difficult in some areas of the state. These and other trends threaten forest sustainability and the numerous economic, environmental, and social benefits that our forests provide. This report describes both forestland (all forests including those not available for commercial harvest – 24.6 million acres) and timberland (all forests that are available for commercial harvest – 23.9 million acres). (GFC 2016) Georgia’s forest area has remained stable over the past 50 years at about 24 million acres. Approximately 91 percent of this acreage is privately owned, giving Georgia more privately-owned acres of timberland than any other state in the nation. -
Regulation on Forest Products Processing and Marketing
Forestry Development Authority Regulation No. 112-08 Regulation on the Forest Products Processing and Marketing WHEREAS, the National Forestry Reform Law of 2006 establishes a transparent framework, for the use, management and protection of forest resources that balances the commercial, community, and conservation priorities of the Republic; and WHEREAS, the economic potential of processed wood products has not been appreciated, there has been too much exportation of crude round logs with evidence of low percentage of primary processed wood for both domestic and export market, no value-added wood product, low recovery rate of wood processing industry, problem of waste disposal; and WHEREAS, industrialization of the wood industry in general and the processing of wood into secondary/value-added products in particular are essential elements for the realization of the potential sustainable utilization of Liberia‘s forest resources; and WHEREAS, sustainable utilization of forest resources concept is not only to maintain the value of forest resources, but rather it also has a huge potential for creating employment, income and wealth for the Liberia populations; and WHEREAS, local small-scale wood enterprises are not fully capacitated and unregulated which in essence has resulted into unsustainable use and marketing of wood products, wastage of wood products, constant exposure of wood products to deteriorating agents; and WHEREAS, the lack of standard units of measurement for Liberia domestic wood market and unregulated import of wood products,