e-Resíduos: A influência da norma européia WEEE na estratégia da indústria de celulares no Brasil e no mundo e o impacto ambiental do descarte inadequado

This present Thesis, is explorer work and presents an analysis of e-wastes of the industry of cellular mobile telephony, evaluating the evolution of the telecommunications nets and as if it holds the global and Brazilian market of cellular telephony. It approaches the elements gifts in the cellular devices that can badly cause to the environment and the health, the discarding of the devices in end of life cycle is made. It analyzes the new European regulation of electric equipment residues and electronic, the WEEE, as it influenced the strategy of the companies manufacturers of mobile phone cellular and of that she forms is possible to create a Brazilian national industry for recycling of devices of cellular, with conditions to globally competition. For this some possible models of being implanted in Brazil are presented. The project of law 203/91 on solid residues is argued and as it would be interesting if to persist some proposals presented to the project, to create a Brazilian market of recycling with capacity of global competition for use to advantage of the European regulation if to get a competitive advantage

Efficiency and feasibility of product disassembly: A case-based study

The productivity associated with commonly available disassembly methods today seldomly makes disassembly the preferred end-of-life solution for massive take back product streams. Systematic reuse of parts or components, or recycling of pure material fractions are often not achievable in an economically sustainable way. In this paper a case-based review of current disassembly practices is used to analyse the factors influencing disassembly feasibility. Data mining techniques were used to identify major factors influencing the profitability of disassembly operations. Case characteristics such as involvement of the product manufacturer in the end-of-life treatment and continuous ownership are some of the important dimensions. Economic models demonstrate that the efficiency of disassembly operations should be increased an order of magnitude to assure the competitiveness of ecologically preferred, disassembly oriented end-of-life scenarios for large waste of electric and electronic equipment (WEEE) streams. Technological means available to increase the productivity of the disassembly operations are summarized. Automated disassembly techniques can contribute to the robustness of the process, but do not allow to overcome the efficiency gap if not combined with appropriate product design measures. Innovative, reversible joints, collectively activated by external trigger signals, form a promising approach to low cost, mass disassembly in this context. A short overview of the state-of-the-art in the development of such self-disassembling joints is included. (c) 2008 CIRP.

Oxidative Leaching of metals from electronic waste with solutions based on quaternary ammonium salts

The treatment of electric and electronic waste (WEEE) is a problem which receives ever more attention. An inadequate treatment results in harmful products ending up in the environment. This project intends to investigate the possibilities of an alternative route for recycling of metals from printed circuit boards (PCBs) obtained from rejected computers. The process is based on aqueous solutions composed of an etchant, either 0.2 M CuCl2.2H2O or 0.2 M FeCl3.6H2O, and a quaternary ammonium salt (quat) such as choline chloride or chlormequat. These solutions are reminiscent of deep eutectic solvents (DES) based on quats. DES are quite similar to ionic liquids (ILs) and are used as well as alternative solvents with a great diversity of physical properties, making them attractive for replacement of hazardous, volatile solvents (e.g. VOCs). A remarkable difference between genuine DES and ILs with the solutions used in this project is the addition of rather large quantities of water. It is shown the presence of water has a lot of advantages on the leaching of metals, while the properties typical for DES still remain. The oxidizing capacities of Cu(II) stem from the existence of a stable Cu(I) component in quat based DES and thus the leaching stems from the activity of the Cu(II)/Cu(I) redox couple. The advantage of Fe(III) in combination with DES is the fact that the Fe(III)/Fe(II) redox couple becomes reversible, which is not true in pure water. This opens perspectives for regeneration of the etching solution. In this project the leaching of copper was studied as a function of gradual increasing water content from 0 - 100w% with the same concentration of copper chloride or iron(III) chloride at room temperature and 80ºC. The solutions were also tested on real PCBs. At room temperature a maximum leaching effect for copper was obtained with 30w% choline chloride with 0.2 M CuCl2.2H2O. The leaching effect is still stronger at 80°C, b ut of course these solutions are more energy consuming. For aluminium, tin, zinc and lead, the leaching was faster at 80ºC. Iron and nickel dissolved easily at room temperature. The solutions were not able to dissolve gold, silver, rhodium and platinum.

Elektroniikka - ja sähköromun (SER) kierrätys

Tässä työssä pyrin tarkastelemaan sähkö- ja elektroniikkaromun kierrätystä erityisesti EU - direktiivin mukaisen tuottajavastuun näkökulmasta. Käytettyjen sähkö- ja elektroniikkalaitteiden vuori kasvaa koko ajan kaikkialla Euroopassa. Euroopan parlamentti hyväksyi joulukuussa 2002 kaksi uutta direktiiviä, joilla pyritään lieventämään sähköromuongelmaa. Parlamentin vaatimusten ansiosta unionin jäsenvaltioiden on taattava, että laitteiden valmistajat maksavat omista tuotteistaan syntyvän sähkö- ja elektroniikkalaitejätteen keräys-, käsittely- ja kierrätyskustannukset. Tämä merkitsee esimerkiksi sitä, että kuluttajat voivat viedä vanhat sähkölaitteensa asuinpaikkansa läheisyydessä sijaitseviin maksuttomiin keräyspisteisiin. Myös kuluttajien on otettava vastuu hankkimistaan tuotteista: sähkö- ja elektroniikkalaitejätteen hävittäminen tavallisen kotitalousjätteen seassa tullaan kieltämään.

Processamento de cartuchos de impressoras de jato de tinta: um exemplo de gestão de produto pós-consumo

This work presents a route for processing spent ink-jet cartridges in an experimental course. The disassembly of the cartridges requires several steps and the recognition of their different components is essential to define the best final destination (recycling, co-processing). The plastic strips were chemically processed so as to recover gold and copper. The students recognized the difficulty of processing multicomponent wastes and the importance of the chemical work under the best safety conditions; they also experienced many laboratory techniques and recognized the value of the selective collection and the reverse logistics to reach a viable commercial scale recycling.

Processamento de placas de circuito impresso de equipamentos eletroeletrônicos de pequeno porte

A hydrometallurgical process applicable to printed circuit boards of small electrical and electronic devices was developed. This involved three leaching steps (60 ºC, 2 h): 6 mol L-1 NaOH, 6 mol L-1 HCl and aqua regia. NaOH removed the resin and flame retardant that covered the circuit boards. HCl dissolved the most electropositive metals and a small amount of copper (~0.3 wt%). Aqua regia dissolved the noble metals. Silver precipitated as AgCl. Gold and platinum were quantitatively extracted with pure methyl-isobutylketone and Alamine 336 (10 % vol. in kerosene), respectively. Slow evaporation of the raffinate crystallized CuCl2.4H2O (89% yield).

Hydrometallurgical recovery of valuable metals from secondary raw materials

Wastes and side streams in the mining industry and different anthropogenic wastes often contain valuable metals in such concentrations their recovery may be economically viable. These raw materials are collectively called secondary raw materials. The recovery of metals from these materials is also environmentally favorable, since many of the metals, for example heavy metals, are hazardous to the environment. This has been noticed in legislative bodies, and strict regulations for handling both mining and anthropogenic wastes have been developed, mainly in the last decade. In the mining and metallurgy industry, important secondary raw materials include, for example, steelmaking dusts (recoverable metals e.g. Zn and Mo), zinc plant residues (Ag, Au, Ga, Ge, In) and waste slurry from Bayer process alumina production (Ga, REE, Ti, V). From anthropogenic wastes, waste electrical and electronic equipment (WEEE), among them LCD screens and fluorescent lamps, are clearly the most important from a metals recovery point of view. Metals that are commonly recovered from WEEE include, for example, Ag, Au, Cu, Pd and Pt. In LCD screens indium, and in fluorescent lamps, REEs, are possible target metals. Hydrometallurgical processing routes are highly suitable for the treatment of complex and/or low grade raw materials, as secondary raw materials often are. These solid or liquid raw materials often contain large amounts of base metals, for example. Thus, in order to recover valuable metals, with small concentrations, highly selective separation methods, such as hydrometallurgical routes, are needed. In addition, hydrometallurgical processes are also seen as more environmental friendly, and they have lower energy consumption, when compared to pyrometallurgical processes. In this thesis, solvent extraction and ion exchange are the most important hydrometallurgical separation methods studied. Solvent extraction is a mainstream unit operation in the metallurgical industry for all kinds of metals, but for ion exchange, practical applications are not as widespread. However, ion exchange is known to be particularly suitable for dilute feed solutions and complex separation tasks, which makes it a viable option, especially for processing secondary raw materials. Recovering valuable metals was studied with five different raw materials, which included liquid and solid side streams from metallurgical industries and WEEE. Recovery of high purity (99.7%) In, from LCD screens, was achieved by leaching with H2SO4, extracting In and Sn to D2EHPA, and selectively stripping In to HCl. In was also concentrated in the solvent extraction stage from 44 mg/L to 6.5 g/L. Ge was recovered as a side product from two different base metal process liquors with Nmethylglucamine functional chelating ion exchange resin (IRA-743). Based on equilibrium and dynamic modeling, a mechanism for this moderately complex adsorption process was suggested. Eu and Y were leached with high yields (91 and 83%) by 2 M H2SO4 from a fluorescent lamp precipitate of waste treatment plant. The waste also contained significant amounts of other REEs such as Gd and Tb, but these were not leached with common mineral acids in ambient conditions. Zn was selectively leached over Fe from steelmaking dusts with a controlled acidic leaching method, in which the pH did not go below, but was held close as possible to, 3. Mo was also present in the other studied dust, and was leached with pure water more effectively than with the acidic methods. Good yield and selectivity in the solvent extraction of Zn was achieved by D2EHPA. However, Fe needs to be eliminated in advance, either by the controlled leaching method or, for example, by precipitation. 100% Pure Mo/Cr product was achieved with quaternary ammonium salt (Aliquat 336) directly from the water leachate, without pH adjustment (pH 13.7). A Mo/Cr mixture was also obtained from H2SO4 leachates with hydroxyoxime LIX 84-I and trioctylamine (TOA), but the purities were 70% at most. However with Aliquat 336, again an over 99% pure mixture was obtained. High selectivity for Mo over Cr was not achieved with any of the studied reagents. Ag-NaCl solution was purified from divalent impurity metals by aminomethylphosphonium functional Lewatit TP-260 ion exchange resin. A novel preconditioning method, named controlled partial neutralization, with conjugate bases of weak organic acids, was used to control the pH in the column to avoid capacity losses or precipitations. Counter-current SMB was shown to be a better process configuration than either batch column operation or the cross-current operation conventionally used in the metallurgical industry. The raw materials used in this thesis were also evaluated from an economic point of view, and the precipitate from a waste fluorescent lamp treatment process was clearly shown to be the most promising.

Étude exploratoire de la phase d’usage des produits électroniques en vue de minimiser les impacts environnementaux : le cas du téléviseur

À cause de leur impact environnemental élevé, les déchets d’équipements électriques et électroniques (DEEE) sont un problème majeur pour les pays développés. La consommation importante de produits électroniques, dont la durée d’utilisation est de plus en plus courte, a entrainé une production croissante de DEEE. C’est dans ce contexte que l’Union européenne a instauré en 2003 la responsabilité élargie des producteurs (REP). Cet outil de politique environnementale a rendu légalement responsables les fabricants de la mise en oeuvre et du financement d’un programme d’intendance des DEEE. Alors que la REP vise principalement le traitement écologique des DEEE, cet instrument ne permet pas de réduire les quantités considérables qui sont produites par les consommateurs. Cette situation est d’autant plus inquiétante que les gains environnementaux obtenus, grâce à l’implantation de la REP, ont été annulés au regard de l’augmentation continue de la consommation de biens électroniques à l’échelle mondiale. En réponse à cette problématique, la présente thèse porte sur les pratiques de l’usager au cours de la phase de consommation des appareils électroniques (aussi appelée phase d’usage). Cette étape du cycle de vie regroupe l’achat, l’utilisation, la réparation et la mise au rebut des biens. Une approche qualitative de type exploratoire faisant appel à l’étude de cas a été utilisée. Le téléviseur, retenu comme cas d’étude, illustre des enjeux partagés par plusieurs équipements électroniques, tels que : la fréquente mise sur le marché de nouveaux modèles, le bas prix d’acquisition comparé au coût de la réparation et l’influence de la mode sur les choix effectués par le consommateur. Ces facteurs facilitent le remplacement des biens et, par conséquent, pourraient entrainer leur fin de vie prématurée qui se matérialise à travers différentes formes d’obsolescence. Dans le cadre de cette étude de cas, une trentaine d’entrevues semi-dirigées a été réalisée avec des usagers et réparateurs de produits électroniques en vue de documenter les différentes sous-étapes de la phase d’usage d’un téléviseur. Sur la base des informations recueillies, l’objectif de cette thèse est de formuler des recommandations, à destination des autorités politiques, qui pourront permettre une minimisation des impacts environnementaux liés à la phase d’usage des appareils électroniques. Les résultats ont permis de mettre en évidence, via le rôle et le statut singulier occupé par le téléviseur dans les foyers, les comportements de l’usager contribuant à augmenter l’empreinte écologique associée à la phase d’usage. L’acquisition de nombreux biens électroniques et non électroniques suite à l’achat du téléviseur, ses multiples fonctionnalités le rapprochant de celles de l’ordinateur et des tablettes, ainsi que la fin de vie prématurée de produits fonctionnels, mais obsolètes d’un point de vue technologique, font partie des résultats de cette recherche. En lien avec ces constats, cette étude propose des instruments de politique environnementale, dont l’affichage de la durée de vie des équipements électroniques, destinés à aider le consommateur à réaliser des choix plus éclairés au moment de l’achat. D’autres orientations, telles que la possibilité d’évoluer vers une réglementation horizontale, c’est-à-dire un cadre législatif qui ne se basera plus sur le produit individuel, mais sur l’ensemble des appareils ayant des fonctionnalités similaires, sont exposées. Par ailleurs, cette recherche explore certains leviers pouvant minimiser le phénomène de fin de vie prématurée des appareils électroniques, tels que l’envoi de biens obsolètes et fonctionnels des pays développés vers ceux en développement pour permettre leur réutilisation et la tendance du Do-It- Yourself dans la réparation des produits électroniques.

Plan de empresa para TECO: modelo de impacto social, autosostenibilidad financiera y de minimización de la huella del e-waste en Bogotá

La red TECO es una iniciativa que integra elementos ya conocidos en el mundo de la publicidad y de la gestión RAEE, en un nuevo modelo de negocio. Esto le permite competir de manera efectiva en un segmento de mercado que si bien no está saturado, requiere de cambios estructurales para poder cumplir su objetivo. El éxito del modelo de TECO radicará en la capacidad de generar su propio flujo de dinero, lo que le garantiza su auto sostenimiento, mientras minimiza la barrera del pensamiento tradicional en la comunidad respecto al miedo de desechar el e-waste (a través de la educación). De igual manera ayudará a todos los participantes de la red a mejorar su reputación y posicionar sus marcas. En última instancia el gran ganador de esta iniciativa es el medio ambiente. Al juntar todos los segmentos de mercado, de entre los cuales TECO podrá participar en su mercado objetivo de mil empresas en Bogotá, estos suman alrededor de ochocientos treinta y ocho mil millones. De esta cifra global nada despreciable, TECO podrá aspirar a cerca de un 0.19% de participación. Más concretamente, en lo que respecta a la categoría de presupuestos destinados a programas posconsumo RAEE y Green Businesses orientados a la publicidad institucional, TECO espera obtener un 6.13% del share.

Diagnóstico da gestão e do gerenciamento dos resíduos eletroeletrônicos gerados no campus da Faculdade de Engenharia de Guaratinguetá/Unesp

Currently, in Brazil, the quantity and quality of new types of wastes, discarded without criteria in urban areas, has been responsible for considerable impacts on public health and the environment. According to a report prepared by the Institute of Applied Economic Research (IPEA), the country loses about U.S. $ 8 billion annually, due lack of waste recycling, which go directly into landfills or dumps. Among these solid wastes are waste electrical and electronic equipment (WEEE), whose characteristics are complex, by having in its composition substances of high value-added and other health hazards which require different treatment of household waste. Aiming to fill the gap in Brazilian environmental legislation, on 02/08/2010, was sanctioned the National Policy Solid Waste (Law No. 12,305), already regulated on 23/12/2010 (Decree No 7404), whose based on the following principles:reduction of waste generation and toxicity of shared responsibility, proper planning management, social inclusion of waste pickers and sustainable production and consumption. Given the above, this work presented here, aims generally present a diagnosis of the current situation of electronic waste generated in the Faculty of Engineering, Campus Guaratinguetá, FEG / UNESP, to provide data for management and management of these waste, based on sustainability, the economic losses and minimizing environmental impacts and public health related to the flow and the improper disposal of these wastes

Contribuições para a melhoria da gestão de resíduos de eletroeletrônicos no Brasil, no contexto da sustentabilidade ambiental

Pós-graduação em Engenharia de Produção - FEG

I rifiuti da apparecchiature elettriche ed elettroniche (RAEE) - Aspetti tecnico-gestionali e ambientali

I RAEE (Rifiuti da Apparecchiature Elettriche ed Elettroniche) costituiscono un problema prioritario a livello europeo per quanto riguarda la loro raccolta, stoccaggio, trattamento, recupero e smaltimento, essenzialmente per i seguenti tre motivi: Il primo riguarda le sostanze pericolose contenute nei RAEE. Tali sostanze, nel caso non siano trattate in modo opportuno, possono provocare danni alla salute dell’uomo e all’ambiente. Il secondo è relativo alla vertiginosa crescita relativa al volume di RAEE prodotti annualmente. La crescita è dovuta alla continua e inesorabile commercializzazione di prodotti elettronici nuovi (è sufficiente pensare alle televisioni, ai cellulari, ai computer, …) e con caratteristiche performanti sempre migliori oltre all’accorciamento del ciclo di vita di queste apparecchiature elettriche ed elettroniche (che sempre più spesso vengono sostituiti non a causa del loro malfunzionamento, ma per il limitato livello di performance garantito). Il terzo (ed ultimo) motivo è legato all’ambito economico in quanto, un corretto trattamento dei RAEE, può portare al recupero di materie prime secondarie (alluminio, ferro, acciaio, plastiche, …) da utilizzare per la realizzazione di nuove apparecchiature. Queste materie prime secondarie possono anche essere vendute generando profitti considerevoli in ragione del valore di mercato di esse che risulta essere in costante crescita. Questo meccanismo ha portato a sviluppare un vasto quadro normativo che regolamenta tutto l’ambito dei RAEE dalla raccolta fino al recupero di materiali o al loro smaltimento in discarica. È importante inoltre sottolineare come lo smaltimento in discarica sia da considerarsi come una sorta di ‘ultima spiaggia’, in quanto è una pratica piuttosto inquinante. Per soddisfare le richieste della direttiva l’obiettivo dev’essere quello di commercializzare prodotti che garantiscano un minor impatto ambientale concentrandosi sul processo produttivo, sull’utilizzo di materiali ‘environmentally friendly’ e sulla gestione consona del fine vita. La Direttiva a livello europeo (emanata nel 2002) ha imposto ai Paesi la raccolta differenziata dei RAEE e ha definito anche un obiettivo di raccolta per tutti i suoi Stati Membri, ovvero 4 kg di RAEE raccolti annualmente da ogni abitante. Come riportato di seguito diversi paesi hanno raggiunto l’obiettivo sopra menzionato (l’Italia vi è riuscita nel 2010), ma esistono anche casi di paesi che devono necessariamente migliorare il proprio sistema di raccolta e gestione dei RAEE. Più precisamente in Italia la gestione dei RAEE è regolamentata dal Decreto Legislativo 151/2005 discusso approfonditamente in seguito ed entrato in funzione a partire dal 1° Gennaio 2008. Il sistema italiano è basato sulla ‘multi consortilità’, ovvero esistono diversi Sistemi Collettivi che sono responsabili della gestione dei RAEE per conto dei produttori che aderiscono ad essi. Un altro punto chiave è la responsabilità dei produttori, che si devono impegnare a realizzare prodotti durevoli e che possano essere recuperati o riciclati facilmente. I produttori sono coordinati dal Centro di Coordinamento RAEE (CDC RAEE) che applica e fa rispettare le regole in modo da rendere uniforme la gestione dei RAEE su tutto il territorio italiano. Il documento che segue sarà strutturato in quattro parti. La prima parte è relativa all’inquadramento normativo della tematica dei RAEE sia a livello europeo (con l’analisi della direttiva ROHS 2 sulle sostanze pericolose contenute nei RAEE e la Direttiva RAEE), sia a livello italiano (con un’ampia discussione sul Decreto Legislativo 151/2005 e Accordi di Programma realizzati fra i soggetti coinvolti). La seconda parte tratta invece il sistema di gestione dei RAEE descrivendo tutte le fasi principali come la raccolta, il trasporto e raggruppamento, il trattamento preliminare, lo smontaggio, il riciclaggio e il recupero, il ricondizionamento, il reimpiego e la riparazione. La terza definisce una panoramica delle principali metodologie di smaltimento dei 5 raggruppamenti di RAEE (R1, R2, R3, R4, R5). La quarta ed ultima parte riporta i risultati a livello italiano, europeo ed extra-europeo nella raccolta dei RAEE, avvalendosi dei report annuali redatti dai principali sistemi di gestione dei vari paesi considerati.