Big Chemical Encyclopedia

Chemical substances, components, reactions, process design ...

Articles Figures Tables About

Waste cycle

Various preferential interventions in the form of taxes, subsidies, and regulations also influence consumer prices, and hence consumer behavior. At the same time, however, the cost of important external effects, such as the stress on the global climatic system or lower national security, are also excluded from the prices that influence consumer trade-offs. And if the full cost of the mine-to-waste cycle needed to provide an energy-based service does not appear in the price of that service, then it will be consumed inefficiently. [Pg.34]

In some cases, alum precoating of the diatomaceous earth can improve performance. Typical alum doses range from 1% to 2% hy weight (1-2 kg/100 kg of diatomaceous earth applied). Typical precoats of diatomaceous earth of 0.49-0.98 kg/m (0.1 to 0.2 Ih/ft ) are applied to prepare the filter. These filters also require a continuous supplemental body feed of diatomite because the filter is subject to cracking. If the filter has no body feed, there will be rapid increases in headloss due to buildup on the surface of the filter cake. Body feed rates must be adjusted for effective turbidity removal. Diatomaceous earth filters do not need a filter-to-waste cycle, because of the precoating process. [Pg.168]

Suggest how such wasteful cycles are prevented or controlled. [Pg.274]

C denotes continuous agitation M" denotes continuous mechanical mixing "D denotes daily feeding and wasting cycles 0 denotes no nutrients added to feed slurry "MN" denotes mixed nutrient solution added to feed slurry "N" denotes ammonium chloride solution added to feed slurry pH maintained in indicated range by periodic NaOH additions. [Pg.235]

C" denotes continous agitation, "D" denotes daily feeding and wasting cycle. [Pg.247]

Demand-driven supply chains. Most aggressive partnership programs focus on cycle time reduction, building a just-in-time capability all along the supply chain. Partnerships will work to remove wasteful cycle time at all stages. [Pg.245]

An outline of the various stages of the waste cycle is shown in Figure 5.3. These will now he discussed. [Pg.54]

Once the life-cycle inventory has been quantified, we can attempt to characterize and assess the eflfects of the environmental emissions in a life-cycle impact analysis. While the life-cycle inventory can, in principle at least, be readily assessed, the resulting impact is far from straightforward to assess. Environmental impacts are usually not directly comparable. For example, how do we compare the production of a kilogram of heavy metal sludge waste with the production of a ton of contaminated aqueous waste A comparision of two life cycles is required to pick the preferred life cycle. [Pg.295]

Life-cycle analysis, in principle, allows an objective and complete view of the impact of processes and products on the environment. For a manufacturer, life-cycle analysis requires an acceptance of responsibility for the impact of manufacturing in total. This means not just the manufacturers operations and the disposal of waste created by those operations but also those of raw materials suppliers and product users. [Pg.296]

To the process designer, life-cycle analysis is useful because focusing exclusively on waste minimization at some point in the life cycle sometimes creates problems elsewhere in the cycle. The designer can often obtain useful insights by changing the boundaries of the system under consideration so that they are wider than those of the process being designed. [Pg.296]

In some appHcations, large quantities of waste or low cost heat are generated. The absorption cycle can be directly powered from such heat. It employs two intermediate heat sinks. Its theoretical coefficient of performance is described by... [Pg.352]

Another possibiUty is to enclose only the working, top part of the horizontal belt in a pressure vessel and pass the belt through the sides of the vessel. The operation must be intermittent because the belt cannot be dragged over the support surface with the pressure on, and the entrance and exit ports for the belt must be sealed during operation to prevent excessive losses of air. The movement of the belt is intermittent and is synchronized with decompression in the vessel therefore, the entire vessel volume must be depressurized in every cycle and this is wasteful. There is also an inevitable downtime. There are no problems with discharging the cake because this is done at atmospheric pressure. [Pg.407]

Fig. 5. Equipment foi surface treating plastic components. Parts ate loaded into one of the two lower chambers which is then evacuated to remove most of the air. This chamber is then flooded with a dilute mixture of fluorine and nitrogen which is made and stored in the upper chamber. After the treatment is completed, the fluorine mixture is pumped back up to the upper chamber for storage and the lower chamber repeatedly flooded with air and evacuated to remove any traces of fluorine gas. Two treatment chambers are cycled between the loading/unloading operation and the treatment step to increase equipment output. The fluorine—nitrogen blend may be used several times before by-products from the treatment process begin to interfere. AH waste... Fig. 5. Equipment foi surface treating plastic components. Parts ate loaded into one of the two lower chambers which is then evacuated to remove most of the air. This chamber is then flooded with a dilute mixture of fluorine and nitrogen which is made and stored in the upper chamber. After the treatment is completed, the fluorine mixture is pumped back up to the upper chamber for storage and the lower chamber repeatedly flooded with air and evacuated to remove any traces of fluorine gas. Two treatment chambers are cycled between the loading/unloading operation and the treatment step to increase equipment output. The fluorine—nitrogen blend may be used several times before by-products from the treatment process begin to interfere. AH waste...
Fig. 6. In a binary electricity generation plant, the hydrothermal water from the weU, A, is passed through a heat exchanger, B, where its thermal energy is transferred to a second, more volatile working fluid. The second fluid is vaporized and deflvered to a turbine, D. After exiting the turbine the spent working fluid is cooled and recondensed in another heat exchanger, E, using water or air as the coolant, F. It is then fed back to the primary heat exchanger to repeat the cycle. Waste hydrothermal fluid, C, can be reinjected into the producing field. Fig. 6. In a binary electricity generation plant, the hydrothermal water from the weU, A, is passed through a heat exchanger, B, where its thermal energy is transferred to a second, more volatile working fluid. The second fluid is vaporized and deflvered to a turbine, D. After exiting the turbine the spent working fluid is cooled and recondensed in another heat exchanger, E, using water or air as the coolant, F. It is then fed back to the primary heat exchanger to repeat the cycle. Waste hydrothermal fluid, C, can be reinjected into the producing field.
Owing to the cycHc nature of the TBRC operation, waste heat recovery from the off-gases is not practical and the SO2 content of the gas varies with the converter cycle. In order to supply a relatively uniform flow and strength SO2 gas to a sulfuric acid plant, a system has been installed at RonnskAr whereby the SO2 from fluctuating smelter gases is partially absorbed in water. During smelter gas intermption, SO2 is stripped with air and the concentrated gas deflvered to the acid plant. [Pg.40]


See other pages where Waste cycle is mentioned: [Pg.963]    [Pg.319]    [Pg.289]    [Pg.16]    [Pg.134]    [Pg.255]    [Pg.274]    [Pg.245]    [Pg.286]    [Pg.73]    [Pg.297]    [Pg.97]    [Pg.273]    [Pg.317]    [Pg.963]    [Pg.319]    [Pg.289]    [Pg.16]    [Pg.134]    [Pg.255]    [Pg.274]    [Pg.245]    [Pg.286]    [Pg.73]    [Pg.297]    [Pg.97]    [Pg.273]    [Pg.317]    [Pg.295]    [Pg.18]    [Pg.282]    [Pg.361]    [Pg.388]    [Pg.180]    [Pg.293]    [Pg.1]    [Pg.12]    [Pg.45]    [Pg.176]    [Pg.509]    [Pg.497]    [Pg.383]    [Pg.384]    [Pg.526]    [Pg.172]    [Pg.424]    [Pg.424]    [Pg.436]   


SEARCH



Classification of Fuel-Cycle Wastes

Commercial nuclear fuel cycle, radioactive wastes from

Dual Regulation of Other Fuel-Cycle Wastes

Effectiveness of closed cycle small reactor initial loadings as a waste sequestration strategy

Life cycle analysis solid waste

Life cycle analysis, industrial waste

Waste incineration, life cycle assessment

Waste management life cycle assessment

Waste minimization cycle

Waste minimization life cycle analysis

Waste nitrogen urea cycle

© 2024 chempedia.info