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Monitors/monitoring continuous emissions

Continuous Emissions Monitoring. A key aspect of the new CAAA is the requirement that plants prove their continued compHance to new emissions limits by installing continuous emissions monitoring systems (CEMs). The CAAA imposes new requirements for monitoring NO, SO2, and CO2 levels in a plant s exhaust gas stream. Affected plants typically must gather data from stack monitoring systems, gas analyzers, and the plant s data acquisition system and provide the data in a format approved by the EPA and state regulators. CEM systems must be in place by November 1993 for boilers affected by Phase I of the CAAA, and byjanuary 1995 for plants impacted by Phase II. [Pg.92]

A significant problem area for initial SCR systems has been the continuous emission monitoring (CEM) systems. In power plants, all sites equipped with CEM systems report the highest failure frequency. The CEM systems are the most labor intensive component, requiring as much as hill-time attention from one technician. At one power plant CEM systems were responsible for 100% of 73 reported SCR system shutdowns (38). As CEM systems improve, these concerns may disappear. [Pg.511]

The method used to develop the emission inventory does have some elements of error, but the other two alternatives are expensive and subject to their own errors. The first alternative would be to monitor continually every major source in the area. The second method would be to monitor continually the pollutants in the ambient air at many points and apply appropriate diffusion equations to calculate the emissions. In practice, the most informative system would be a combination of all three, knowledgeably applied. [Pg.92]

Discuss the availability and reliability of in-stack continuous emission monitors when they are required by U.S. New Source Performance Standards. [Pg.419]

Jahnke, I. A. (2000) Continuous Emission Monitoring, Wiley, Chichester. [Pg.555]

Air emissions at point of discharge should be monitored continuously for fluorides and particulates and aimually for ammonia and nitrogen oxides. Monitoring data should be analyzed and reviewed at regular intervals and compared with the operating standards so that any necessary corrective actions can be taken. Records of monitoring results should be kept in an acceptable format. The results should be reported to the responsible authorities and relevant parties, as required. [Pg.63]

They may require pH adjustment and settling. These effluents should preferably be recycled or reused. Spent catalysts are usually sent for regeneration or disposed of in a secure landfill. Air emissions should be monitored aimually, except for nitrate acid plants, where nitrogen oxides should be monitored continuously. [Pg.67]

Baghouses are preferred over venturi scrubbers for controlling particulate matter emissions from loading and pushing operations because of the higher removal efficiencies. ESPs are effective for final tar removal from coke oven gas. Stack air emissions should be monitored continuously for particulate matter. Alternatively, opacity measurements of stack gases can suffice. Fugitive emissions should be monitored annually for VOCs. [Pg.74]

Continuous Emission Monitor- Enviroplan, Inc. ing Data Acquisition System... [Pg.285]

Data acquisition system for continuous emission monitoring of ambient air or slack emissions. Also provides reports. [Pg.285]

Applications Transportable FTIR analyzers have been used in monitoring applications such as continuous emissions monitoring, process gas analysis, and car exhaust and industrial air hygiene. [Pg.1305]

Continuous monitoring of emission gases is necessary to ascertain that the emissions from a production unit remain within the limit values. - The limit value for SO2 in Finland is 4 kg or less per tonne of pulp produced. The authorities often require plants to continuously monitor the main emissions. Information on the environmental load generated hy a production unit is available to customers upon request. This information is also used for the environmental management of the plant. [Pg.1314]

The facility may also choose to use an advanced type of monitoring known as continuous emissions monitoring systems (CEMS). CEMS directly measure the pollutants that are exiting the combustion unit stack at all times. If a facility chooses to use a CEMS, they do not need to comply with the operating parameter that would otherwise apply. [Pg.463]

Trial bums, with appropriate stack sampling and analysis, and subsequent continuous emissions monitoring are conducted to demonstrate that the incinerator performs as specified. [Pg.960]

Continuous dyeing, 9 177, 201, 213, 231 Continuous emission monitoring (CEM) systems, 10 101... [Pg.213]

Evolved gases were monitored continuously for 02, C02, NOx, CO, and total hydrocarbons (THC) by a continuous emission monitoring system (CEMS). Batch samples of the offgases were also taken and analyzed for NH3, HCN, residual energetic materials, volatile organic compounds, and N2. The batch samples were collected over the entire duration of each run, and the single value reported represents the average concentration for the whole run. [Pg.46]

Continuous measurement of NOx emissions in vent gases —Continuous emissions measurements of total hydrocarbons —Chlorine emissions monitoring —Hold-test-release protocols... [Pg.86]

The reaction between olefins and ozone produces light that can be measured and related to the concentration of the reactants. One of the preferred methods for measuring ambient ozone concentrations utilizes the chemiluminescence generated in the ozone-ethylene reaction for detection. Recently, Hills and Zimmerman (16) described the use of this detection principle for determining hydrocarbon concentrations. They utilized the chemiluminescence created when ozone reacts with isoprene for development of a continuous, fast-response isoprene analyzer. This real-time isoprene system is reported to be linear over three orders of magnitude and to have a detection limit of about 1 ppbv. Because the system doesn t include a preseparation of hydrocarbons, interferences from other olefins (ethylene, propylene, and so forth) could occur. Thus far the chemiluminescent detector has been used to monitor isoprene emissions under conditions in which the concentrations of olefins that could interfere are negligible compared to those of the biogenic hydrocarbon. [Pg.296]

The Army should develop a process and schedule, including uncertainties in the permitting process, to determine the latest point in time when a decision can be made either to ship energetics off site or to dispose of them in a DFS and still meet the CWC treaty deadline. Tests should be undertaken to verity that stack emissions of heavy metals would be limited to acceptable levels by whatever technology is selected. The Army should also evaluate state-of-the-art tools for the continuous monitoring of emissions of metals, dioxins, and the products of incomplete combustion and, if practicable, install them at Pueblo. [Pg.22]

Recommendation 3-9. The Army should evaluate state-of-the-art analytical tools for continuous monitoring of emissions of metals, dioxins, and products of incomplete combustion. If they are effective, the Army could install them at chemical agent disposal facilities where applicable. If continuous monitors are not effective, the Army could conduct stack tests for dioxins/furans, mercury, and organics at suitable intervals to provide some additional assurance to the surrounding communities that the modified baseline process is working properly. [Pg.38]

Because of the extensive reuse of combustion air in the process at Calaveras facility, the fabric filter exhaust is the only point of emissions for the kiln, clinker cooler, and raw mill. Exhaust gases from the fabric filter are monitored continuously for carbon monoxide, nitrogen oxides, and hydrocarbons. Calaveras has tested toxic pollutants while burning 20 percent TDF. Table 4-5 summarizes these test results, giving emission factors for metals, hazardous air pollutants, polyaromatic hydrocarbons, dioxins and... [Pg.210]

Conrad s Centralia plant has no pollution control equipment except for the outside flare for the excess gas. No continuous emissions monitoring systems are used. No local regulations apply to the facility, although an annual inspection is conducted on site by regulatory agencies. [Pg.304]


See other pages where Monitors/monitoring continuous emissions is mentioned: [Pg.510]    [Pg.178]    [Pg.182]    [Pg.230]    [Pg.409]    [Pg.549]    [Pg.535]    [Pg.341]    [Pg.535]    [Pg.476]    [Pg.958]    [Pg.213]    [Pg.18]    [Pg.202]    [Pg.44]    [Pg.413]    [Pg.510]    [Pg.39]    [Pg.15]    [Pg.41]    [Pg.82]    [Pg.183]    [Pg.316]   
See also in sourсe #XX -- [ Pg.269 ]




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