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Primary batteries collection

The Directive batteries constitute less than 10% of the general purpose batteries marketed in Europe today. As these are typically rechargeable systems, they remain with the consumer far longer than the primary types. In those countries collecting all batteries, studies undertaken by the battery industry, in collaboration with the collection authorities, have shown that more than 95% of the batteries collected fall outside of the European Battery Directive. [Pg.180]

The Canadian report concluded that dry-cell batteries do not represent a concentrated source of heavy metals in municipal solid waste and their disposal by landfill or incineration poses insignificant risk to human health. Furthermore they concluded that separate collection, storage and disposal of most household batteries produced more significant health related problems and that recycling of primary batteries was neither necessary nor needed. [Pg.182]

This report in itself is not conclusive. However it does stimulate debate on the separate collection of wastes in general. Further work is necessary in order to determine alternative solutions to reduce the differential between the negative impact of collection and the positive impact of recycling. One possible approach is to integrate the collection of primary batteries together with other suitable waste streams. Clearly such an approach will depend on the end use of the waste batteries, but the advantages in terms of minimising collection and transport impacts are obvious. [Pg.190]

Today DK Recycling und Roheisen GmbH recycle mercury free manufacturing scrap from primary battery manufacturing facilities and are undergoing further trials to extend this service to collected post consumer batteries. [Pg.218]

The typical life cycles of consumer batteries depend to some extent on their applications. Primary batteries employed in portable devices are most often discarded casually with domestic trash and end up in landfills. Exceptions exist in communities where deliberate efforts are made to collect spent batteries for recycling or proper disposal and in communities where battery vendors participate in incentive programs to return spent batteries to the manufacturers or collect them for recycling or proper disposal. The magnitude of such programs is still... [Pg.134]

The subject of the study of passivation processes by impedance analysis has been extensively reviewed by Epelboin et al [19]. Other areas where the impedance method has been developed include solid electrolytes and superionic conductors [20], electrocrystallisation [21] and state-of-charge testing of primary batteries [22]. Numerous other examples of the use of a.c. techniques have been collected together by Gabrielli [23],... [Pg.278]

Secondary lead is primarily sourced from scrap lead-acid batteries but also processed scrap metallics such as sheet and pipe. Secondary operations are characterised by relatively small plants in comparison with primary smelters, and are sized to handle scrap availability within a local area. This is determined by the economics of scrap battery collection and transport to the secondary operation, and it follows that the largest secondary plants are located in the high vehicle density areas of the USA. [Pg.14]

Sulfuric acid may be reclaimed for reuse in batteries by filtration of discard from the primary paste collection settler, or it may be neutralised with lime and the resulting gypsum filtered off and discarded. [Pg.171]

Secondary Lead. The emphasis in technological development for the lead industry in the 1990s is on secondary or recycled lead. Recovery from scrap is an important source for the lead demands of the United States and the test of the world. In the United States, over 70% of the lead requirements are satisfied by recycled lead products. The ratio of secondary to primary lead increases with increasing lead consumption for batteries. WeU-organized collecting channels are requited for a stable future for lead (see BATTERIES, SECONDARY CELLS Recycling NONFERROUS METALS). [Pg.48]

The produced oil or gas is connected to surface flowlines from the wellhead pumping unit or surface regulating valve assembly typically referred to as a Christmas tree but to its arrangement. The flowlines collect the oil or gas to local tank batteries or central production facilities for primary oil, water, and gas separation. The reliability of electrical submersible pumps (ESPs) has increased to the point where the submersible electrical pump is commonly used for the production of liquid hydrocarbons where artificial lift is required for production. [Pg.11]

A battery of six different FFF systems was used to provide a comparison of results obtained not only from different systems of the same type but from systems of entirely different types (i.e., with different primary force fields). The characteristics of the six systems are summarized in Table I. Included in the collection are two sedimentation FFF systems, three flow FFF systems, and one thermal FFF system. The characteristics and operation of these different categories of instruments are described in more detail in this section. [Pg.309]

During the nineties, three collection systems were under development for portable reehargeable batteries a dedicated collection scheme, a general collection scheme for all types of portable batteries (primary and rechargeable) and the collection of portable electrical and electronic equipment associated with the de-manufacturing in order to reeover valuable components as batteries. [Pg.71]

General collection schemes for all types of portable batteries (primary and rechargeable) from which rechargeable batteries like Ni-Cd batteries are sorted out in a specific stream has been initiated in several european coimtries. The impact of the startup of such a program as a follow-up of a dedicated scheme is illustrated in Figure 26 for the case of Germany. [Pg.73]

By contrast, relatively uncontaminated single polymer types can be collected from retail outlets by segregation on site [e.g. discarded polypropylene crates, battery cases and supermarket shrink-wrap). These can be recycled with the addition of new antioxidants and UV stabilisers into the primary application, generally as a blend with virgin polymer, without significant loss of mechanical properties. [Pg.70]


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See also in sourсe #XX -- [ Pg.177 ]




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