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Aluminium containers recycling

Aluminium can recycling. The bales seen here contain over one million cans. [Pg.152]

Many standard reactions that are widely applied in the production of fine chemicals employ. strong mineral or Lewis acids, such as sulphuric acid and aluminium chloride, often in stoichiometric quantities. This generates waste streams containing large amounts of spent acid, which cannot easily be recovered and recycled. Replacement of these soluble mineral and Lewis acids by recyclable. solid acids, such as zeolites, acid clays, and related materials, would represent a major breakthrough, especially if they functioned in truly catalytic quantities. Consequently, the application of solid acids in fine chemicals synthesis is currently the focus of much attention (Downing et al., 1997). [Pg.42]

Feeding device. 2 — Electrolytic cells, 3 — Catholyte receiver, i — Container for electrolyte which passed through the cathode spaces of the electrolyzer, 5 — anolyte receiver, 6 — Feeding device for ammonium persulphate solution (anolyte) to distillation equipment. 1, 7a— Distillation equipment, S, 9 — Separators, 10 — Container for returned electrolyte, 11 — Droplets separator, 12. 13, 14 — Stoneware fractionating columns, IS — Aluminium tube condenser, 19, 17, IS — Receivers for individual fractions of hydrogen peroxide, 19 — Receiver for manufactured product, 20 — Reservoir for recycled electrolyte, 21 — Tank for purification of the electrolyte. [Pg.407]

Scientific studies have found that the differences between microwave and conventional pyrolysis go beyond the obvious difference in the source of heat. Other differences arise from the very high rates of heat transfer from the microwave-absorbent to the waste, the amount heat received by the primary pyrolytic products once they leave the absorbent bed and the highly reducing environment. These three aspects have been shown to have an important effect in the final products since they modify the extent of secondary and tertiary reactions. Moreover, the scientific studies have shown that a nonthermal microwave effect in these processes is unlikely to exist. Tests have showed the potential of the microwave-induced pyrolysis process for the treatment of real plastic-containing wastes and it is believed that a commercial process could be developed, for example, to recover clean aluminium from plastic/aluminium laminates. Other materials, in particular tyres, coal and medical wastes are very good candidates to be treated/recycled using microwave pyrolysis and there have been a considerable number patents filed with this goal in mind. [Pg.587]

Recycling a yes score has been awarded because the CER contains a number of examples of the role played by recycling in reducing environmental impact. These include recycling aluminium oxide at Oulu, acidic sludge at Kvarntorp and aluminium hydrate at Police. The product stewardship report also includes a number of similar examples. [Pg.261]

Recycling the CER contains a number of references to recycling, particu larly in the Light Metals division, which currently recycles 300000 tonnes of aluminium, and has a target of 600000 tonnes by 2005. Reference is also made to recycling production waste from resins and of recycling PVC. [Pg.280]

After a sufficient length of time in operation, the electrolytic cell used to produce aluminium must be renewed and the waste materials it contains treated to produce solid phases that can either be safely dumped or recycled. A fluidized bed reactor is suitable for the combustion of the waste products of the cell, using humidified air. [Pg.175]

Strip off all the fibre shedding incoming packaging materials in the collation area and send the materials to the line in internally recycled (plastic) containers and an aluminium pallet. [Pg.387]

Volatile metal halides, usually chlorides and fluorides, also form the heart of several processes used to produce surface layers, rich in aluminium, chromium, or silicon, or combinations of these. In these processes, the workpiece to be coated is buried in a powder bed and heated to reaction temperature. The bed consists of a mixture of inert alumina filler, a master alloy powder that contains the aluminium, etc., and an activator such as ammonium chloride. Basically, at about 630°C, the activator volatilizes and the aluminium chloride vapour reacts with the master alloy to produce a volatile aluminium chloride, which then reacts with the workpiece surface to deposit aluminium. The deposited aluminium proceeds to diffuse into the surface layers of the workpiece to produce a diffusion coating. The process is driven basically by the difference in aluminium activity between the master alloy and the worlqtiece. These processes are well documented in principle, but their execution to provide reproducible and reliable results still involves considerable experience, or rule of thumb. These processes will be described in detail in Chapter 10. Finally, a chlorination treatment is used to remove tin from tin-plated steel. This uses a normally deleterious reaction to advantage and profit in the recovery of both tin and steel for recycling. Fluorination is used in the manufacture of polymers and fluorocarbon consequently, materials suitable for construction of these plants must be resistant to fluorine attack. [Pg.169]

The possibilities of recycling depend on the product and the generated wastes. Swarfs are mostly recovered for internal remelting while other scrap (containing too much other metal) will usually be sold to secondary aluminium production. [Pg.303]

PHA can be synthesised using proper catalysts (i.e., zinc- or aluminium-based catalyst) with water as the cocatalyst. This in vitro system has been shown to be possible using the PHA synthases purified from various sources [141, 179-181]. It is possible to produce homopolymers and copolymers containing 3HB, 3HV, 4-hydroxyvalerate and 3-hydroxydecanoate [90]. Multiple-enzyme systems have been developed that can utilise cheaper substrates as well as recycle expensive cofactors such as coenzyme A. Nevertheless, the in vitro systems are still expensive to use in order to produce PHA for applications as commodity plastics. Furthermore, hazardous organic solvents are generally required to achieve high enzymatic activity. Present studies focus on the replacement of these organic solvents with supercritical fluids [182] and ionic liquids [183]. [Pg.241]

Aluminium oxide is a very dense and extremely hard angular abrasive (specific gravity 4.0, 8.5 to 9 Mohr). It provides fast cutting and a good surface profile so that paint can anchor onto steel. This abrasive generates low amounts of dust and can be recycled, which is necessary because it is quite expensive. Aluminium oxide does not contain free silica. [Pg.72]

In order to consider effective strategies for the recovery and reuse of plastics recyclates, a quantitative method is described for the characterisation of polyester-based moulding compounds. Analytical procedures are described for the quantification of fibre, filler and fire retardant contents in polyester moulding compounds containing calcium carbonate filler, glass fibre reinforcement, and aluminium hydroxide flame retardant. 3 refs. [Pg.93]


See other pages where Aluminium containers recycling is mentioned: [Pg.11]    [Pg.437]    [Pg.226]    [Pg.93]    [Pg.194]    [Pg.232]    [Pg.456]    [Pg.431]    [Pg.816]    [Pg.49]    [Pg.38]    [Pg.273]    [Pg.152]    [Pg.60]    [Pg.294]    [Pg.93]    [Pg.78]    [Pg.387]    [Pg.68]   
See also in sourсe #XX -- [ Pg.442 ]




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