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Control industrial emission

Emissions control. See also Automotive emission control Industrial emission control... [Pg.312]

The seriousness of the smoke problems in England (as well as on the continent) led to numerous efforts by local governments to control smoke, such as the 1853 Smoke Nuisance Abatement Act in London and the 1857 Smoke Abatement Act in Scotland, which both defined smoke from furnaces as a nuisance. In 1863, the British Parliament passed the Alkali Act, which set up an Inspectorate to control industrial emissions of hydrogen chloride. Its... [Pg.121]

Control of NO emissions from nitric acid and nitration operations is usually achieved by NO2 reduction to N2 and water using natural gas in a catalytic decomposer (123—126) (see Exhaust control, industrial). NO from nitric acid/nitration operations is also controlled by absorption in water to regenerate nitric acid. Modeling of such absorbers and the complexities of the NO —HNO —H2O system have been discussed (127). Other novel control methods have also been investigated (128—129). Vehicular emission control is treated elsewhere (see Exhaust control, automotive). [Pg.391]

In the outdoor environment, the high concentrations of sulfur and nitrogen oxides from automotive and industrial emissions result in a corrosion having both soluble and insoluble corrosion products and no pacification. The results are clearly visible on outdoor bronze sculpture (see Airpollution Exhaust CONTROL, automotive Exhaust conthol, industrial). [Pg.425]

Gasoline composition may also be regulated in Europe. A tripartite initiative is being carried out among the European Commission, the oil industry, and the automotive industry. Based on an analysis of the required improvements in air quaUty, new regulations are to be written that control vehicle emissions and fuel composition into the twenty-first century. [Pg.191]

RCRA incinerator regulations include adrninistrative as weU as performance standards. Administrative standards include procedures for waste analysis, inspection of equipment, monitoring, and facihty security. Steps needed to meet adrninistrative standards are outlined ia the permit apphcation performance standards are demonstrated during a trial bum. Trial bum operating conditions are included in the permit to assure ongoing compliance with the performance standards. Performance standards include destmction and removal efficiency (DRE), particulate emissions limits, products of incomplete combustion emission limits, metal emission limits, and HCl and Cl emission limits (see Exhaust CONTROL, INDUSTRIAL). [Pg.44]

Emission Control. In 1993, for a net electric power generation of 3196 x 10 kWh, power industry emissions were as follows ... [Pg.9]

Sulfur Dioxide Emissions and Control. A substantial part of the sulfur dioxide in the atmosphere is the result of burning sulfur-containing fuel, notably coal, and smelting sulfide ores. Methods for controlling sulfur dioxide emissions have been reviewed (312—314) (see also Air POLLUTION CONTROL PffiTHODS COAL CONVERSION PROCESSES, CLEANING AND DESULFURIZATION EXHAUST CONTROL, INDUSTRIAL SULFURREMOVAL AND RECOVERY). [Pg.148]

Heavy metals on or in vegetation and water have been and continue to be toxic to animals and fish. Arsenic and lead from smelters, molybdenum from steel plants, and mercury from chlorine-caustic plants are major offenders. Poisoning of aquatic life by mercury is relatively new, whereas the toxic effects of the other metals have been largely eliminated by proper control of industrial emissions. Gaseous (and particulate) fluorides have caused injury and damage to a wide variety of animals—domestic and wild—as well as to fish. Accidental effects resulting from insecticides and nerve gas have been reported. [Pg.121]

Other industries of interest are (1) the manufacturing of spices and flavorings, which may use activated carbon filters to remove odors from their exhaust stream (2) the tanning industry, which uses afterburners or activated carbon for odor removal and wet scrubbers for dust removal and (3) glue and rendering plants, which utilize sodium hypochlorite scrubbers or afterburners to control odorous emissions. [Pg.513]

Venmri scrubbers have been applied to control PM emissions from utility, industrial, commercial, and institutional boilers fired with coal, oil, wood, and liquid waste. They have also been applied to control emission sources in the chemical, mineral products, wood, pulp and paper, rock products, and asphalt manufacrnring industries lead, aluminum, iron and steel, and gray iron production industries and to municipal solid waste incinerators. Typically, venturi scrubbers are applied where it is necessary to obtain high collection efficiencies for fine PM. Thus, they are applicable to controlling emission sources with high concentrations of submicron PM. [Pg.434]

Emissions monitoring is essential in controlling industrial environments and processes to ensure good air quality standards are maintained. It is also required in order that the various regulations and guidelines related to air quality are met. In addition to gaseous emissions, such as sulfur dioxide, carbon monoxide, nitrogen oxides, hydrocarbons, and many others, the emissions of particulate material and heavy metals must also be controlled. [Pg.1283]

The catalyst companies were encouraged to resume their research activities in automotive catalysis in the late 1960 s as further tightening of automotive emissions standards became imminent, and it appeared that mere engine modifications might be inadequate to meet the new standards. A systems approach was first used upon the formation of the Inter-Industry Emission Control Program by the Ford Motor Company and the Mobil Oil Corporation in 1967, which was joined by a number of oil companies in the U.S. and a number of automobile companies in Italy, Japan, and Western Germany. [Pg.62]

There are many types of emissions to atmosphere, and these can be characterized as particulate (solid or liquid), vapor and gaseous. Overall, the control of atmospheric emissions is difficult because the majority of emissions come from small sources that are difficult to regulate and control. Legislators therefore control emissions from sources that are large enough to justify monitoring and inspection. Industrial emissions of major concern are as follows. [Pg.551]

European Commission (2010) Directive 2010/75/EU of the European Parliament and of the Council of 24 November 2010 on industrial emissions (integrated pollution prevention and control)... [Pg.261]

Acrolein enters the environment as a result of normal metabolic processes incomplete combustion of coal, wood, plastics, tobacco, and oil fuels and industrial emissions. Acrolein has been detected in smog, foods, and water. It is used extensively in chemical manufacture, for control of fouling organisms, and as an herbicide to control submerged weeds in irrigation canals. [Pg.746]

FGD is used to control S02 emissions from coal and oil combustion from electric utilities and industrial sources. Impingement scrubbers are one wet scrubber configuration used to bring exhaust gases into contact with a sorbent designed to remove the S02. On occasion, wet scrubbers have been applied to S02 emissions from processes in the primary non-ferrous metals industries (e.g., copper, lead, and aluminum), but sulfuric acid or elemental sulfur plants are more popular control devices for controlling the high S02 concentrations associated with these processes. [Pg.232]

Fiber-bed scrubbers are used to control aerosol emissions from chemical, plastics, asphalt, sulfuric acid, and surface coating industries. They are also used to control lubricant mist emission from rotating machinery and mists from storage tanks. Fiber-bed scrubbers are also applied downstream of other control devices to eliminate a visible plume. Despite their potential for high collection efficiency, fiber-bed scrubbers have had only limited commercial acceptance for dust collection because of their tendency to become plugged. [Pg.237]

Industrial emission catalysts, 19 625-626 Industrial emission control, 10 67-112... [Pg.470]

French and European Union legislation relating to the control of emissions in the workplace is examined, with particular reference to the rubber processing industry. Air sampling and analytical procedures used in the detection of nitrosamines formed in vulcanisation reactions are reviewed. 2 refs. [Pg.102]

Figure 17-46 shows such a performance curve for the collection of coal fly ash by a pilot-plant venturi scrubber (Raben "Use of Scrubbers for Control of Emissions from Power Boilers, United States-U.S.S.R. Symposium on Control of Fine-Particulate Emissions from Industrial Sources, San Francisco, 1974). The scatter in the data reflects not merely experimental errors but actual variations in the particle-size characteristics of the dust. Because the characteristics of an industrial dust vary with time, the scrubber performance curve necessarily must represent an average material, and the scatter in the data is frequently greater than is shown in Fig. 17-46. For best definition, the curve should cover as wide a range of contacting power as possible. Obtaining the data thus requires pilot-plant equipment with the flexibility to operate over a wide range of conditions. Because scrubber performance is not greatly affected by the size of the unit, it is feasible to conduct the tests with a unit handling no more than 170 m3/h (100 ftVmin) of gas. Figure 17-46 shows such a performance curve for the collection of coal fly ash by a pilot-plant venturi scrubber (Raben "Use of Scrubbers for Control of Emissions from Power Boilers, United States-U.S.S.R. Symposium on Control of Fine-Particulate Emissions from Industrial Sources, San Francisco, 1974). The scatter in the data reflects not merely experimental errors but actual variations in the particle-size characteristics of the dust. Because the characteristics of an industrial dust vary with time, the scrubber performance curve necessarily must represent an average material, and the scatter in the data is frequently greater than is shown in Fig. 17-46. For best definition, the curve should cover as wide a range of contacting power as possible. Obtaining the data thus requires pilot-plant equipment with the flexibility to operate over a wide range of conditions. Because scrubber performance is not greatly affected by the size of the unit, it is feasible to conduct the tests with a unit handling no more than 170 m3/h (100 ftVmin) of gas.
After the pioneering studies of Haagen-Smit, an extensive scientific literature developed on the properties, measurement, and effects of photochemical smog. The attempt to control engine emission has had a profound effect on the automobile and petroleum industries. Estimated costs and associated benefits of automobile emission control each run into the billions per year. ... [Pg.1]

The United States has the most extensive environmental regulatory programs that aim to minimize the release of metals into the environment. These regulations seek to control the emission of pollutants from specific industries and to define the emission limits according to the type of industry, the age and size of the plant, and the nature of the processes involved. In addition, different limits are set according to the following criteria best... [Pg.646]

In response to recent federal and local environmental concerns (e.g., industrial emission controls and lead phase-out) and to the growing interest of refiners in cracking residual fuels, researchers have generated new families of cracking catalysts. There is now a need to review the merits of these newly developed materials. This volume contains contributions from researchers involved in the preparation and characterization of cracking catalysts. Other important aspects of fluid catalytic cracking, such as feedstocks and process hardware effects in refining, have been intentionally omitted because of time limitations and should be treated separately in future volumes. [Pg.360]

In 1970, new efforts were underway to solve Portland s suspended particulate problem. Early efforts relied on available emission factors and industrial source testing, as a basis for the emission Inventory. The inventory was then used, with a proportional rollback model, as a basis for the new strategy. New industrial controls were Installed which resulted in a 60,000 tons per year region-wide reduction in industrial emissions. Although progress toward cleaner air was made, air quality standard violations caused by then unknown sources continued and modeling efforts failed to account for over one-half of the particulate mass. [Pg.108]

Industrial emissions collectively accounted for only 5% of the particulate mass, a result that was not surprising given that these sources were well controlled before field sampling began. Some industrial source Impacts, however, may not have been identifiable because of emissions that chemically resembled geologic sources. [Pg.110]


See other pages where Control industrial emission is mentioned: [Pg.22]    [Pg.302]    [Pg.234]    [Pg.22]    [Pg.302]    [Pg.234]    [Pg.388]    [Pg.412]    [Pg.396]    [Pg.96]    [Pg.353]    [Pg.393]    [Pg.252]    [Pg.338]    [Pg.237]    [Pg.222]    [Pg.1592]    [Pg.82]    [Pg.5]    [Pg.144]    [Pg.55]    [Pg.80]    [Pg.128]    [Pg.194]    [Pg.113]    [Pg.76]    [Pg.29]   
See also in sourсe #XX -- [ Pg.31 ]




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