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A methodology and processes for assessment of the compliance of existing wood-based panel production plants with bat requirements

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Warianty tytułu
Języki publikacji
EN
Abstrakty
EN
All producers of wood-based materials should know to what extent their facility is in compliance with BAT (Best Available Techniques) requirements (Reference Document for the Production of Wood-based Panels, 2016). This paper presents a methodology with optimized procedures to evaluate the compliance of a facility with BAT requirements, verified using the example of an existing wood-based panel production plant. Model production of particleboard consumes 500,000 tonnes of wood (actual weight – LUTRO) annually; the largest shares are those of coniferous pulpwood with nearly 150,000 tonnes, sawdust with around 110,000 tonnes, and others. Approximately 400,000 m3 of raw particleboard is produced per year, of which about half is laminated. The company manufactures annually almost 22 million m2 of impregnated foil. There are 34 points at the plant where air emissions occur. During particleboard production, 27 types of hazardous waste and nine kinds of other waste are generated. The article is a brief overview of the subject matter and the results of research. The methodology comprises a set of theoretical analyses, results of controls on site, analyses and measurements, which are processed in 16 steps. In this article, we report the results of comparisons of the parameters of the monitored plant with the parameters of the best available technology. In the processes of production, drying and shredding of chips, the critical locations, or most demanding in terms of meeting the BAT requirements, are sawdust storage or sawdust handling, and the chip dryer. The drying of chips is the main source of air pollution and a potential source of odour. A wet electrostatic precipitator was implemented to minimize emissions from the dryer. Authorized emission measurement indicates an average PM value of 3.57 mg/m3 (with 17% O2), against a current emission limit of 20 mg/m3. The result of authorized measurement of TOC is 49 mg/m3, while the current emission limit is 300 mg/m3. The real values of the formaldehyde concentration measurements are low, below 0.76 mg/m3. The current emission limit for the sum of concentrations of formaldehyde, acetaldehyde, phenol and formic acid is 25 mg/m3. Thorough environmental management analysis of the compliance of the existing particleboard production plant has a positive impact on several environmental and economic solutions. Moreover, a series of measures and communication with competent environmental protection authorities are proposed.
Rocznik
Strony
117--129
Opis fizyczny
Bibliogr. 25 poz., rys., tab.
Twórcy
  • European Science and Research Institute, Zvolen, Slovakia
  • European Science and Research Institute, Zvolen, Slovakia
autor
  • Matej Bel University – Faculty of Natural Sciences, Banská Bystrica, Slovakia
Bibliografia
  • Act of the Slovak Republic no. 24/2006 Coll. on environmental impact assessment
  • Act of the Slovak Republic no. 39/2013 Coll. on integrated pollution prevention
  • Act of the Slovak Republic no. 569/2007 Coll. on geological works
  • Akyuz İ., Ozşahin Ş., Tiryaki S., Aydın A. [2017]: An application of artificial neural networks for modeling formaldehyde emission based on process parameters in particleboard manufacturing process. Clean Technologies and Environmental Policy 19 [5]: 1449-1458. DOI: 10.1007/s10098-017-1342-0
  • BAT conclusions [2015]: Commission implementing decision (EU) 2015/2119 of 20 November 2015 establishing best available techniques (BAT) conclusions, under Directive 2010/75/EU of the European Parliament and of the Council, for the production of wood-based panels
  • Directive 2010/75/EU [2010]: Directive of the European Parliament and of the Council of 24 November 2010 on industrial emissions. DOI: 10.3000/17252555.L_2010.334.eng
  • Esteves B., Martins J., Martins J., Cruz-Lopes L., Vicente J., Domingos I. [2015]: Liquefied wood as a partial substitute of melamine-urea-formaldehyde and ureaformaldehyde resins. Maderas Ciencia y Tecnologia 17 [2]: 277-284. DOI: 10.4067/S0718-221X2015005000026
  • Frąckowiak I., Warcok F., Bendowska R., Idziak A. [2014]: Possibilities of limiting formaldehyde content in particleboards to a level characteristic of natural wood. Drewno 57 [191]: 71-85. DOI: 10.12841/wood.1644-3985.077.05
  • Garcia R., Freire F. [2014]: Carbon footprint of particleboard: A comparison between ISO/TS 14067, GHG Protocol, PAS 2050 and Climate Declaration. Journal of Cleaner Production 66: 199-209. DOI: 10.1016/j.jclepro.2013.11.073
  • Gűler C., Sahin H., Yeniay S. [2016]. The potential for using corn stalks as a raw material for production particleboard with industrial wood chips. Wood Research 61 [2]: 299-306
  • Iritani D.R., Silva D.A.L., Saavedra Y.M.B., Grael P.F.F., Ometto A.R. [2015]: Sustainable strategies analysis through Life Cycle Assessment: A case study in a furniture industry. Journal of Cleaner Production 96: 308-318. DOI: 10.1016/j.jclepro.2014.05.029
  • Kim M.H., Song H.B. [2014]: Analysis of the global warming potential for wood waste recycling systems. Journal of Cleaner Production 69: 199-207. DOI: 10.1016/j.jclepro.2014.01.039
  • Klimek P., Wimmer R., Kumar Mishra P., Kudela J. [2017]: Utilizing brewer’s-spent-grain in wood-based particleboard manufacturing. Journal of Cleaner Production 141: 812-817. DOI: 10.1016/j.jclepro.2016.09.152
  • Knauf M. [2015]: Waste hierarchy revisited – an evaluation of waste wood recycling in the context of EU energy policy and the European market. Forest Policy and Economics 54: 58-60. DOI: 10.1016/j.forpol.2014.12.003
  • Ladomersky J. Hroncova E., Samešova D., Ladomerska Z., Stehlikova D. [2010]: Reduction of pollutants and malodorous substances emissions and expanding of preparation, drying and sorting of wood chips in the particleboard production in Bučina DDD, Zvolen. Report elaboration in accordance to Act No. 24/2006 Coll. On environmental impact assessment. Technical University in Zvolen, 148 pp. (+ appendices). In Slovak [unpublished]
  • Lykidis C., Grigoriou A., Barboutis I. [2014]. Utilisation of wood biomass residues from fruit tree branches, evergreen hardwood shrubs and Greek fir wood as raw materials for particleboard production. Part A. Mechanical properties. Wood Material Science & Engineering 9 [4]: 202-208. DOI: 10.1080/17480272.2013.875589
  • Moubarik A., Mansouri H.R., Pizzi A., Charrier F., Allal A., Charrier B. [2013]: Corn flour-mimosa tannin-based adhesives without formaldehyde for interior particleboard production. Wood Science and Technology 47: 675-683. DOI: 10.1007/s00226-012-0525-4
  • Nakano K., Ando K., Takigawa M., Hattori N. [2017]: Life cycle assessment of woodbased boards produced in Japan and impact of formaldehyde emissions during the use stage. International Journal of Life Cycle Assessment: 1-13. (in press) DOI: 10.1007/s11367-017-1343-6
  • Paiva N.T., Pereira J., Ferra J.M., Martins J., Carvalho L., Magalhaes F.D. [2014]: Development of phenol-formaldehyde resin with low formaldehyde emissions that respects LEED certification. International Wood Products Journal 5: 161-167. DOI: 10.1179/2042645314Y.0000000074
  • Rimar M., Fedak M., Korshunov A., Kulikov A., Mižakova J. [2016]: Determination of excess air ratio during combustion of wood chips respect to moisture content. Acta Facultatis Xylologiae 58 [2]: 133-140. DOI: 10.17423/afx.2016.58.2.14
  • Saravia-Cortez A.M., Herva M., Garcia-Dieguez C., Roca E. [2013]: Assessing environmental sustainability of particleboard production process by ecological footprint. Journal of Cleaner Production 52: 301-308. DOI: 10.1016/j.jclepro.2013.02.006
  • Silva D.A.L., Lahr F.A.R., Pavan A.L.R., Saavedra Y.M.B., Mendes N.C., Sousa S.R., Sanches R., Ometto A.R. [2014]: Do wood-based panels made with agro-industrial residues provide environmentally benign alternatives? An LCA case study of sugarcane bagasse addition to particle board manufacturing. International Journal of Life Cycle Assessment 19: 1767-1778. DOI: 10.1007/s11367-014-0776-4
  • Stubdrup K.R., Karlis P., Roudier S., Sancho L.D. [2016]: Best Available Techniques (BAT) Reference Document for the Production of Wood-based Panels; EUR 27732 EN; DOI: 10.2791/21807
  • Szostak A., Ratajczak E. [2009]: Results of the innovation activity of the wood sector. Drewno 52 [182]: 123-129
  • Wang L., Chen S.S., Tsang D.C.W., Poon C.S., Shih K. [2016]: Recycling contaminated wood into eco-friendly particleboard using green cement and carbon dioxide curing. Journal of Cleaner Production 137: 861-870. DOI: 10.1016/j.jclepro.2016.07.180
Uwagi
Opracowanie rekordu w ramach umowy 509/P-DUN/2018 ze środków MNiSW przeznaczonych na działalność upowszechniającą naukę (2019).
Typ dokumentu
Bibliografia
Identyfikator YADDA
bwmeta1.element.baztech-ca9529de-a86b-4fb4-a146-f6e0c072f6cf
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