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Emission standards limits

In the past, exhaust emission standards (limits) have been set in most industrialised countries for passenger cars, light-duty trucks and heavy-duty trucks (gasoline and diesel... [Pg.163]

Prevention of environmental harm/violation of emission standard limits... [Pg.1007]

It is shown in Fig. 23.23 that none of the emission components meets Euro 2 emission standard limits. This reveals somehow the current emission quality of the diesel engine in Vietnam. The emission components HC, CO, and PM were higher but NOjc was depleted within the test period. These results match with the deflection of engine... [Pg.727]

Emission Standards. In order to have a nationwide basis for air pollution emission controls and to set a minimum emission limit, the EPA developed New Source Performance Standards (NSPS). The NSPS set specific poUutant emission limits or describe the best available control technology (BACT) that should be appUed at that source. The EPA has issued NSPS, which apply to new constmction as weU as to large modifications, for many different sources. Sources in the chemical industry include the foUowing. [Pg.77]

A key parameter in the design of the fuel vapor control system is the volume of activated carbon required to meet the emission standards for the various regulatory tests. In the case of the three-day diurnal test sequence, the emission limits are 0.05 grams of HC per mile during the run loss portion of the test (maximum emission -0.85 grams), and a maximum release of 2.0 grams for the sum of the hot soak period and any one of the three 24-hour periods making up the diurnal test sequence. [Pg.259]

Another study found that trichloroethylene can be absorbed from the atmosphere by foods and concentrated over time, so that acceptable ambient air levels may still result in food levels which exceed acceptable limits (Grob et al. 1990). The authors estimated that in order to limit food concentrations of trichloroethylene to 50 pg/kg (the maximum tolerated limit for food halocarbons in Switzerland), the level in surrounding air should not exceed 38.5 pg/m (0.007 ppm). Since the accepted levels found near emission sources are often far above this limit, foods processed or sold near these sources may routinely exceed the tolerated trichloroethylene concentration, thus making the setting of air emission standards problematic. It is also noteworthy that the limits recommended by Grob et al. (1990) exceed acceptable ambient air concentrations for many regions of the United States (see Chapter 7). [Pg.220]

Hazardous waste burning incinerators, cement kilns, and LWAKs do not follow a tiered approach to regulate the release of toxic metals into the atmosphere. The MACT rule finalized numerical emission standards for three categories of metals mercury, low-volatile metals (arsenic, beryllium, and chromium), and semivolatile metals (lead and cadmium). Units must meet emission standards for the amount of metals emitted. For example, a new cement kiln must meet an emission limit of 120pg/m3 of mercury, 54pg/m3 of low-volatile metals, and 180 pg/m3 of semivolatile metals. [Pg.463]

The final emission standard under the BIF regulations limits the unit s output of HCI and chlorine gas (Cl j). These compounds combine with water in the air to form acid rain. They are also a known cause of human respiratory problems. The emission controls are implemented in the same way as the metal emissions, using the tiered approach. The owner/operator has a choice of three tiers with varying focal points. The Tier I and Tier II screening levels for waste feed and stack emission limits are located in Part 266, Appendices II and III.5... [Pg.973]

As shown in Figure 7.11, the difference between NO engine-out emissions and the NO standards limit value corresponds to the minimal quantity of NO to be treated. This characteristic constitutes the key factor for the design of the NO Trap volume. [Pg.223]

Regarding standards, they can be classified into two ambient standards, which fix a minimum desired level of air or water quality or a maximum level of emissions that must be maintained, and emission standards, which fix a maximum level of permitted emissions that can be performance based, setting emission limits that each firm is allowed, or technology based, specifying the best technology to be used.3... [Pg.29]

Boatbuilders who use composites have, at most, just one more year before they have to reduce emissions to meet National Emission Standards for Hazardous Air Pollutants (NESH AP), also known as Maximum Achievable Control Technology (MACT) standards. By 23rd Aug. 2004, most boat manufacturing facilities subject to NESHAP must comply with 40 Code of Federal Regulations (CFR) Part 63, Subpart VVW. The deadline applies to existing boat manufacturing facilities that are major sources of hazardous air pollutants (HAPs). Existing sources are those that commenced construction on or before July 14, 2000. ( New sources , those that commenced construction after this date, must comply with emission limits at startup.) Major sources are facilities that have the potential to... [Pg.39]

The US Environmental Protection Agency recently announced its intention to develop and implement new Clean Air Act Standards for industrial coatings operations within the next year. These emission standards will eventually require companies involved in fabric printing, coating and dyeing operations to comply with Maximum Achievable Control standards. The Hazardous Air Pollutants emission limits that will apply to facilities and the impact on fabric coating operations are discussed. USA... [Pg.60]

Eor fluidized catalytic cracking (FCC) units in the United States, the CAA created several regulatory requirements and emission standards including but not limited to the following ... [Pg.257]

Emission Standard A quantitative limit on the emission or discharge of a potentially toxic substance from a particular source. Tire simplest system is uniform emission standard where the same limit is placed on all emissions of a particular contaminant. [Pg.232]

Limit value (LV) The limit at or below which Member States of the European Community must set their environmental quality standards and emission standards. These limits are set by Community Directives. [Pg.245]

In the USA, for Tier 2 emission limits different bins have been defined. Passenger cars are certified in any of the available bins by choice of the vehicle manufacturer. With full implementation in 2009, the average NOx emission of the entire light-duty fleet sold by each manufacturer must meet 0.07 g/mile. For the individual bins, the full useful life emission limits are displayed in Table I. The very strict California low emission vehicle (LEV) II emission standards are covered in the lower number bins to make certification easier for vehicle manufacturers. [Pg.104]

More recent flame photometric methods rely on direct measurement of the phosphorus emission. If organophosphorus compounds are injected into a hydrogen flame, a continuous emission is obtained in the 490-650 nm region. A broad band system, with an intensity maximum at 526 nm, is superimposed on this background139 it is attributed to the HPO species formed in the flame. An early determination of phosphorus at 0.01-0.04 m concentrations was based on examination of the continuous emission standard and sample solutions were injected into the burner and the intensities were measured at 540 nm the calibration graph was linear down to the detection limit of 10 4 M phosphorus sodium or calcium, if present in the sample, interfered with the results140. [Pg.357]

The new specifications not only limit the concentration of sulfur to 0.05% but also specify that the fuel should have the combustion properties of a 10% or lower aromatics-containing fuel and have a minimum cetane number of 40. Fuels that have more than 10% aromatics are now able to meet these specifications through additives (22). However, as smoke emission standards become more restrictive, the aromatics content of diesel fuels may have to be lowered to a true value of 10% or less. A very thorough review of the consequences of this potential problem has recently been written by Stanislaus and Cooper, which covers in detail aromatic hydrocarbon hydroprocessing kinetics, thermodynamics, catalyst compositions, and mechanisms (109). There is little need to repeat the details of that report... [Pg.438]


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