<?xml version="1.0" encoding="ISO-8859-1"?><article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance">
<front>
<journal-meta>
<journal-id>0870-6352</journal-id>
<journal-title><![CDATA[Silva Lusitana]]></journal-title>
<abbrev-journal-title><![CDATA[Silva Lus.]]></abbrev-journal-title>
<issn>0870-6352</issn>
<publisher>
<publisher-name><![CDATA[Unidade de Silvicultura e Produtos Florestais]]></publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id>S0870-63522006000200005</article-id>
<title-group>
<article-title xml:lang="pt"><![CDATA[Optimização da Localização de Unidades de Remediação de Resíduos de Madeira Tratada]]></article-title>
<article-title xml:lang="en"><![CDATA[Optimisation Model for the Localization of Treated Wood Waste Remediation Units]]></article-title>
<article-title xml:lang="fr"><![CDATA[Optimisation de la Localisation des Unités de Remédiation des Résidus de Bois Traités]]></article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Gomes]]></surname>
<given-names><![CDATA[Helena]]></given-names>
</name>
<xref ref-type="aff" rid="A01"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Ribeiro]]></surname>
<given-names><![CDATA[Alexandra B.]]></given-names>
</name>
<xref ref-type="aff" rid="A01"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Lobo]]></surname>
<given-names><![CDATA[Vitor]]></given-names>
</name>
<xref ref-type="aff" rid="A02"/>
</contrib>
</contrib-group>
<aff id="A01">
<institution><![CDATA[,Universidade Nova de Lisboa Faculdade de Ciências e Tecnologia Departamento de Ciências e Engenharia do Ambiente]]></institution>
<addr-line><![CDATA[CAPARICA ]]></addr-line>
</aff>
<aff id="A02">
<institution><![CDATA[,Universidade Nova de Lisboa Instituto Superior de Estatística e Gestão de Informação ]]></institution>
<addr-line><![CDATA[LISBOA ]]></addr-line>
</aff>
<pub-date pub-type="pub">
<day>00</day>
<month>12</month>
<year>2006</year>
</pub-date>
<pub-date pub-type="epub">
<day>00</day>
<month>12</month>
<year>2006</year>
</pub-date>
<volume>14</volume>
<numero>2</numero>
<fpage>181</fpage>
<lpage>202</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http://scielo.pt/scielo.php?script=sci_arttext&amp;pid=S0870-63522006000200005&amp;lng=en&amp;nrm=iso"></self-uri><self-uri xlink:href="http://scielo.pt/scielo.php?script=sci_abstract&amp;pid=S0870-63522006000200005&amp;lng=en&amp;nrm=iso"></self-uri><self-uri xlink:href="http://scielo.pt/scielo.php?script=sci_pdf&amp;pid=S0870-63522006000200005&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="pt"><p><![CDATA[O principal objectivo deste trabalho consiste em optimizar a localização de unidades de remediação de resíduos de madeira preservada, de forma a assegurar-lhes uma gestão adequada e a minimizar os custos. Prevêem-se aumentos significativos neste fluxo de resíduos nas próximas décadas, sendo que dezenas de milhares de m³ gerados anualmente em Portugal terão de ter um destino adequado. A reciclagem destes resíduos apenas deverá ser realizada após a sua remediação, pelo que o planeamento e optimização da localização de unidades de tratamento assumem uma grande importância. O modelo de localização foi implementado com base em informação georreferenciada, utilizando Sistemas de Informação Geográfica (ArcGIS 8.2 © ESRI) e informação georreferenciada sobre o uso do solo e os resultados do inquérito enviado às indústrias de preservação de madeira. Foram testados dois métodos diferentes de análise de clusters (Self-Organizing Maps e K-means), em diferentes condições, para resolver este problema de localização. As soluções obtidas com os dois métodos fazem sentido e podem ser utilizadas para decidir a localização das unidades de remediação. Enquanto que o SOM obteve resultados mais robustos e reprodutíveis, em tempos computacionais mais longos, o K-means obteve melhores soluções, apesar da maior variância e dispersão geográfica.]]></p></abstract>
<abstract abstract-type="short" xml:lang="en"><p><![CDATA[The objective of this study is to optimise the location of remediation plants for treating CCA-treated wood waste for further recycling, minimizing costs and respecting environmental criteria. In the next decades, the amounts of treated wood that annually needs to be properly disposed of in Portugal will increase considerably. The recycling of this waste, containing chromium, copper and arsenic, should only be made after its remediation, so planning and optimising the units' locations is of major importance. The location model was implemented with geographic information using Geographic Information Systems (ArcGIS 8.2 © ESRI), soil occupation data and the results of a questionnaire sent to wood preservation industries. Two different clustering methods (Self-Organizing Maps and K-means) were tested in different conditions to solve the location problem. The solution obtained with either clustering methods are valid and could be used to decide the location of these plants. SOM provided more robust and reproducible results than K-means, with the disadvantage of longer computing times. The main advantage of K-means is the reduced computing time. Additionally it allows us to obtain the best solutions in the majority of cases, in spite of bigger variances and more geographical dispersion.]]></p></abstract>
<abstract abstract-type="short" xml:lang="fr"><p><![CDATA[Le principal objectif de cette étude est d'optimiser la localisation des usines de remédiation pour traiter les déchets de bois imprégné avec CCA, en minimisant les coûts et en respectant les critères environnementaux. Dans les prochaines décennies, au Portugal, les quantités de bois traité, devant être annuellement correctement entreposés, augmenteront considérablement. Le recyclage de ces déchets, contenant chrome, cuivre et arsenic, devrait seulement être fait après leur remédiation, donc la planification et l'optimisation des sites des usines sont très importantes. Le modèle de localisation a été implémenté grâce à l'information géographique en utilisant des systèmes d'information géographiques (ArcGIS 8.2 © ESRI), à l'occupation du sol et aux résultats d'un questionnaire envoyé aux industries d'imprégnation du bois. Deux méthodes de groupage différentes (Self-organizing Maps et K-means) ont été examinées dans différentes conditions. Les solutions obtenues avec les deux méthodes sont viables et pourraient être employées pour décider de l'endroit de l'emplacement de ces usines. SOM a fourni des résultats plus robustes et reproductibles que K-means, avec l'inconvénient de durées de calcul plus longues. Le principal avantage de K-means, comparé à SOM, est la durée de calcul plus réduite et l'obtention de meilleures solutions dans la plupart des tests, malgré de grandes variations et une dispersion géographique.]]></p></abstract>
<kwd-group>
<kwd lng="pt"><![CDATA[resíduos de madeira preservada com CCA]]></kwd>
<kwd lng="pt"><![CDATA[modelos de localização]]></kwd>
<kwd lng="pt"><![CDATA[Self-Organizing Maps]]></kwd>
<kwd lng="pt"><![CDATA[K-means]]></kwd>
<kwd lng="pt"><![CDATA[optimização]]></kwd>
<kwd lng="en"><![CDATA[CCA-treated wood waste]]></kwd>
<kwd lng="en"><![CDATA[location models]]></kwd>
<kwd lng="en"><![CDATA[Self-Organizing Maps]]></kwd>
<kwd lng="en"><![CDATA[K-means]]></kwd>
<kwd lng="en"><![CDATA[optimisation]]></kwd>
<kwd lng="fr"><![CDATA[déchets de bois traité avec CCA]]></kwd>
<kwd lng="fr"><![CDATA[modèles de localisation]]></kwd>
<kwd lng="fr"><![CDATA[Self-Organizing Maps]]></kwd>
<kwd lng="fr"><![CDATA[K-means]]></kwd>
<kwd lng="fr"><![CDATA[optimisation]]></kwd>
</kwd-group>
</article-meta>
</front><body><![CDATA[ <p align="center"><b>Optimização da Localização de Unidades de Remediação de Resíduos    de Madeira Tratada</b></p>      <p>&nbsp;</p>      <p align="center"><b>Helena Gomes*<sup><a href="#1">1</a><a name="top1"></a></sup>,    Alexandra B. Ribeiro** e Vitor Lobo***</b></p>     <p align="center">*Engenheira do Ambiente </p>     <p align="center">**Professora Auxiliar</p>     <p align="center">Departamento de Ciências e Engenharia do Ambiente. Faculdade    de Ciências e Tecnologia, Universidade Nova de Lisboa, Monte da Caparica, 2829-516    CAPARICA      <p align="center">***Professor Associado</p>     <p align="center">Instituto Superior de Estatística e Gestão de Informação. Universidade    Nova de Lisboa, Campus de Campolide, 1070-312 LISBOA</p>      <p>&nbsp;</p>      <p align="justify"><b>Sumário</b>. O principal objectivo deste trabalho consiste    em optimizar a localização de unidades de remediação de resíduos de madeira    preservada, de forma a assegurar-lhes uma gestão adequada e a minimizar os custos.    Prevêem-se aumentos significativos neste fluxo de resíduos nas próximas décadas,    sendo que dezenas de milhares de m<sup>3</sup> gerados anualmente em Portugal    terão de ter um destino adequado. A reciclagem destes resíduos apenas deverá    ser realizada após a sua remediação, pelo que o planeamento e optimização da    localização de unidades de tratamento assumem uma grande importância.</p>     ]]></body>
<body><![CDATA[<p align="justify">O modelo de localização foi implementado com base em informação    georreferenciada, utilizando Sistemas de Informação Geográfica (ArcGIS 8.2 ©    ESRI) e informação georreferenciada sobre o uso do solo e os resultados do inquérito    enviado às indústrias de preservação de madeira. Foram testados dois métodos    diferentes de análise de clusters (<i>Self-Organizing Maps </i>e <i>K-means</i>),    em diferentes condições, para resolver este problema de localização. </p>     <p align="justify">As soluções obtidas com os dois métodos fazem sentido e podem    ser utilizadas para decidir a localização das unidades de remediação. Enquanto    que o <i>SOM</i> obteve resultados mais robustos e reprodutíveis, em tempos    computacionais mais longos, o <i>K-means </i>obteve melhores soluções, apesar    da maior variância e dispersão geográfica.</p>     <p align="justify"><b>Palavras-chave</b><b>:</b> resíduos de madeira preservada    com CCA; modelos de localização; <i>Self-Organizing Maps</i>; <i>K-means</i>;    optimização</p>      <p>&nbsp;</p>      <p><b>Optimisation Model for the Localization of Treated Wood Waste Remediation Units </b></p>      <p align="justify"><b>Abstract</b>. The objective of this study is to optimise    the location of remediation plants for treating CCA-treated wood waste for further    recycling, minimizing costs and respecting environmental criteria. In the next    decades, the amounts of treated wood that annually needs to be properly disposed    of in Portugal will increase considerably. The recycling of this waste, containing    chromium, copper and arsenic, should only be made after its remediation, so    planning and optimising the units' locations is of major importance.</p>     <p align="justify">The location model was implemented with geographic information    using Geographic Information Systems (ArcGIS 8.2 © ESRI), soil occupation data    and the results of a questionnaire sent to wood preservation industries.</p>     <p align="justify">Two different clustering methods (Self-Organizing Maps and    K-means) were tested in different conditions to solve the location problem.</p>     <p align="justify">The solution obtained with either clustering methods are valid    and could be used to decide the location of these plants. SOM provided more    robust and reproducible results than K-means, with the disadvantage of longer    computing times. The main advantage of K-means is the reduced computing time.    Additionally it allows us to obtain the best solutions in the majority of cases,    in spite of bigger variances and more geographical dispersion.</p>     <p align="justify"><b>Key words</b><b>:</b> CCA-treated wood waste; location models;    Self-Organizing Maps; K-means; optimisation</p>      ]]></body>
<body><![CDATA[<p>&nbsp;</p>      <p><b>Optimisation de la Localisation des Unités de Remédiation des Résidus de Bois Traités</b></p>      <p align="justify"><b>Résumé</b>. Le principal objectif de cette étude est d'optimiser    la localisation des usines de remédiation pour traiter les déchets de bois imprégné    avec CCA, en minimisant les coûts et en respectant les critères environnementaux.    Dans les prochaines décennies, au Portugal, les quantités de bois traité, devant    être annuellement correctement entreposés, augmenteront considérablement. Le    recyclage de ces déchets, contenant chrome, cuivre et arsenic, devrait seulement    être fait après leur remédiation, donc la planification et l'optimisation des    sites des usines sont très importantes. </p>     <p align="justify">Le modèle de localisation a été implémenté grâce à l'information    géographique en utilisant des systèmes d'information géographiques (ArcGIS 8.2    © ESRI), à l'occupation du sol et aux résultats d'un questionnaire envoyé aux    industries d'imprégnation du bois.</p>     <p align="justify">Deux méthodes de groupage différentes (<i>Self-organizing Maps</i>    et <i>K-means</i>) ont été examinées dans différentes conditions. Les solutions    obtenues avec les deux méthodes sont viables et pourraient être employées pour    décider de l'endroit de l'emplacement de ces usines. <i>SOM</i> a fourni des    résultats plus robustes et reproductibles que <i>K-means</i>, avec l'inconvénient    de durées de calcul plus longues. Le principal avantage de <i>K-means</i>, comparé    à <i>SOM</i>, est la durée de calcul plus réduite et l'obtention de meilleures    solutions dans la plupart des tests, malgré de grandes variations et une dispersion    géographique.</p>     <p align="justify"><b>Mots clés:</b> déchets de bois traité avec CCA; modèles    de localisation; <i>Self-Organizing Maps</i>; <i>K-means</i>; optimisation</p>      <p>&nbsp;</p>      <p>Texto completo disponível apenas em PDF.</p>     <p>Full text only available in PDF format.</p>      <p>&nbsp;</p>      ]]></body>
<body><![CDATA[<p><b>Bibliografia</b></p>      <!-- ref --><p>Borrego, C.<i> et al.,</i> 2003. <i>Inventário de Resíduos Sólidos Industriais</i>. Departamento de Ambiente e Ordenamento, Universidade de Aveiro.&nbsp;&nbsp;&nbsp;&nbsp;&nbsp;&nbsp;&nbsp;&nbsp;[&#160;<a href="javascript:void(0);" onclick="javascript: window.open('/scielo.php?script=sci_nlinks&ref=000034&pid=S0870-6352200600020000500001&lng=','','width=640,height=500,resizable=yes,scrollbars=1,menubar=yes,');">Links</a>&#160;]<!-- end-ref --><p>Breslin, V.T., L. Adler-Ivanbrook, 1998. Release of copper, chromium  and arsenic from CCA-C treated lumber in estuaries. <i>Estuarine, Coastal  and Shelf Science</i> <b>46 </b>: 111–125.</p>      <p>Carvalho, A., 1997. <i>Madeiras Portuguesas: Estrutura Anatómica, Propriedades, Utilizações</i>. Direcção-Geral das Florestas, Lisboa.</p>      <p>Chirenjea, T., Maa, L.Q., Clarkb, C., Reevesa, M., 2003. Cu, Cr and As  distribution in soils adjacent to pressure-treated decks, fences and poles.  <i>Environmental Pollution</i> <b>124 </b>: 407–417.</p>      <p>Cooper, P.A., 2003.<i> </i>A review of issues and technical options  for managing spent CCA treated wood. <i>AWPA Annual Meeting</i>, AWPA.</p>      <p>Deroubaix, G., Cornillier, C., 2004.<i> </i>Treated wood waste in Europe.  Proposal for a management concept. <i>Final Conference COST Action E22 &quot;Environmental Optimisation of Wood Protection&quot;</i>, Lisboa, Portugal, 22<sup>nd</sup>-23<sup>rd</sup> March. </p>      <p>Drezner, Z.<i> </i><i>et al.</i> 2002. The Weber Problem. <i>Facility  Location: Applications and Theory</i>. Z. Dezner &amp; H.W. Hamacher (Eds), Springer-Verlag.<b> </b>pp.<b> </b>1-36.</p>      <p>FPL, 2000. <i>Environmental impact of preservative-treated wood in a wetland boardwalk</i>. FPL–RP–582, Forest Service, Forest Products Laboratory Forest Service, Forest Products Laboratory, United States Department of Agriculture, Madison, W.I., U.S.A..</p>      <p>Giannikos, I., 1998. A multiobjective programming model for locating  treatment sites and routing hazardous wastes. <i>European Journal of Operational Research</i> <b>104 </b>: 333-342.</p>      ]]></body>
<body><![CDATA[<p>INE, 2002. <i>Infra-estruturas Rodoviárias 2001</i>. Instituto Nacional  de Estatística, Lisboa.</p>      <p>INETI, 2001. <i>Plano Nacional de Prevenção de Resíduos Industriais</i>.  Volume II, Tomo I, Instituto Nacional de Engenharia e Tecnologia Industrial,  Lisboa.</p>      <p>INR, 2003. <i>Estudo de Inventariação de Resíduos Industriais</i>. Relatório Síntese. Instituto dos Resíduos, Lisboa, 28 pp.</p>      <p>Kohonen, T., 1990. The self-organizing map. <i>Proceedings of the IEEE</i> <b>78</b>(9) : 1464-1480.</p>      <p>Lahdelma, R.<i> et al.,</i> 2002. Locating a waste treatment facility by using stochastic multicriteria acceptability analysis with ordinal criteria. <i>European Journal of Operational Research</i> <b>142 </b>: 345–356.</p>      <p>Llurdés, J.C.<i> et al.,</i> 2003. Ten years wasted: the failure of siting waste facilities in central Catalonia, Spain. <i>Land Use Policy</i> <b>20</b>: 335-342.</p>      <p>Maas, R.P., Patch, S.C., Stork, A.M., Berkowitz, J.F., Stork, G.A., 2002.  <i>Release of total chromium, chromium VI and total arsenic from new and aged pressure treated lumber</i>. Report 02-093, Environmental Quality Institute, University of North Carolina-Asheville, Asheville, U.S.A..</p>      <p>McQueen, J.<i> et al.,</i> 1998.<i> </i>Recycling of CCA Treated Wood in the US. <i>4th International Symposium on Wood Preservation</i>, Cannes - Mandelieu, France, 2-3 February 1998.</p>      <p>Megiddo, N., Supowit, K., 1984. On the complexity of some common geometric location problems. <i>SIAM Journal on Computing</i> <b>18</b>: 182-196.</p>      <p>Nema, A. K., Gupta S.K., 1999. Optimization of regional hazardous waste management systems: an improved formulation. <i>Waste Management</i> <b>19</b>: 441-451.</p>      ]]></body>
<body><![CDATA[<p>OECD, 2000. <i>Report of the OECD Workshop on Environmental Exposure Assessment to Wood Preservatives</i>. OECD. Belgirate, Italy: pp 74.</p>      <p>Reimão, D., Cockcroft, R., 1985. <i>Wood Preservation in Portugal</i>. Swedish National Board for Technical Development.</p>      <p>Ribeiro, A.B., 1998. <i>Use of Electrodialytic Remediation Technique for Removal of Selected Heavy Metals and Metalloids from Soils</i>. Department of Geology and Geotechnical Engineering, Technical University of Denmark. Denmark: pp 314.</p>      <p>Ribeiro, A.B.<i> </i><i>et al.,</i> 2000. Electrodialytic removal of Cu, Cr and As from chromated copper arsenate-treated timber waste.  <i>Environmental Science &amp; Technology</i> <b>34</b>(5) : 784-788.</p>      <p>Sanches, R., 2004. <i>Comunicação pessoal</i>.</p>      <p>Solo-Gabriele, H.<i> et al.,</i> 1998. <i>Generation, Use, Disposal, and Management Options for </i><i>CCA</i><i>-Treated Wood</i>. Report #98-1, Florida Center for Solid and Hazardous Waste Management. Gainesville: pp. 54.</p>      <p>Solo-Gabriele, H., Kormienko, M., Gary, K., Townsend, T., Stook, K., Tolaymat, T., 2000. <i>Alternative chemicals and improved disposal-end management practices for </i><i>CCA</i><i>-treated wood</i>. Report #00-03, Florida Center for Solid and Hazardous Waste Management, Gainesville, U.S.A.. Humar, M. &amp; F. Pohleven (2001).<i> </i>Recycling of CCA or CCB treated waste wood. <i>Commodity science in global quality perspective: products – technology, quality and environment: proceedings of the 13th IGWT Symposium</i>, Maribor, Slovenia, 2<sup>th</sup> - 8<sup>th</sup> September 2001.</p>      <p>Tãhkãlã, T., 2002.<i> </i>Waste and recycling. <i>Workshop 4 - COST E22</i>, Tuusula, Finland, 03 June 2002.</p>      <p>Townsend, T., Stook, K., Ward, M., Solo-Gabriele, H., 2003. <i>Leaching and toxicity of CCA-treated and alternative-treated wood products</i>. Report #02-4, Florida Center for Solid and Hazardous Waste Management, Gainesville, U.S.A..</p>      <p>Veríssimo, P., 2004. <i>Comunicação pessoal</i>.</p>      ]]></body>
<body><![CDATA[<p>Villumsen, A., 2003. <i>Elektrodialytisk Rensning af </i><i>CCA</i><i> Impraegneret Affaldstrae</i>. LIFE Project Number LIFE ENV/000/369. Lyngby, Denmark.</p>      <p>Weis, J.S., Weis, P., 2002. Contamination of saltmarsh sediments and biota by CCA treated wood walkways.<i> </i><i>Marine Pollution Bulletin</i> <b>44 </b>: 504–510.</p>      <p>&nbsp;</p>      <p><i>Entregue para publicação em Março de 2005</i></p>      <p><i>Aceite para publicação em Abril de 2005</i></p>      <p>&nbsp;</p>      <p><sup><a href="#top1">1</a><a name="1"></a></sup> 1º Autor E-mail: <a href="mailto:helenaig@netcabo.pt">helenaig@netcabo.pt</a></p>       ]]></body><back>
<ref-list>
<ref id="B1">
<nlm-citation citation-type="book">
<person-group person-group-type="author">
<name>
<surname><![CDATA[Borrego]]></surname>
<given-names><![CDATA[C.]]></given-names>
</name>
</person-group>
<source><![CDATA[Inventário de Resíduos Sólidos Industriais]]></source>
<year>2003</year>
<publisher-name><![CDATA[Departamento de Ambiente e OrdenamentoUniversidade de Aveiro]]></publisher-name>
</nlm-citation>
</ref>
</ref-list>
</back>
</article>
