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Priority pollutant

Environmental Applications Although ion-selective electrodes find use in environmental analysis, their application is not as widespread as in clinical analysis. Standard methods have been developed for the analysis of CN , F , NH3, and in water and wastewater. Except for F , however, other analytical methods are considered superior. By incorporating the ion-selective electrode into a flow cell, the continuous monitoring of wastewater streams and other flow systems is possible. Such applications are limited, however, by the electrode s response to the analyte s activity, rather than its concentration. Considerable interest has been shown in the development of biosensors for the field screening and monitoring of environmental samples for a number of priority pollutants. [Pg.494]

Health nd Safety Factors. Isophorone is considered moderately toxic by ingestion and skin contact. Some rat tumor formation evidence has been found (264), but no demonstration as a human carcinogen has been proven. Isophorone is considered an Environmental Protection Agency (EPA) priority pollutant, and has a permissible acute toxicity concentration of 117, 000 ///L to protect freshwater aquatic life, 12, 900 ///L to protect saltwater aquatic life, and 5, 200 ///L to protect human life (265). Isophorone is mildly toxic by inhalation, but because of its low volatiUty it is not a serious vapor hazard. [Pg.496]

The high temperatures in the MHD combustion system mean that no complex organic compounds should be present in the combustion products. Gas chromatograph/mass spectrometer analysis of radiant furnace slag and ESP/baghouse composite, down to the part per biUion level, confirms this behef (53). With respect to inorganic priority pollutants, except for mercury, concentrations in MHD-derived fly-ash are expected to be lower than from conventional coal-fired plants. More complete discussion of this topic can be found in References 53 and 63. [Pg.424]

M. A. CaUahan and co-workers, Water-Related Environmental Fate of 129 Priority Pollutants, Vol. 1, EPA-440/4-79/029a, U.S. Environmental Protection Agency, Washington, D.C., 1980, pp. 17-1—17-11. [Pg.93]

New regulations for toxics and priority pollutants frequendy cannot be met by conventional technology. Other physical—chemical technologies must therefore be appHed. [Pg.192]

Chemical Oxidation. Chemical oxidation can be appHed ia iadustrial wastewater pretreatment for reduction of toxicity, to oxidize metal complexes to enhance heavy metals removal from wastewaters, or as a posttreatment for toxicity reduction or priority pollutant removal. [Pg.192]

Design data are available for the specific organics on the EPA s priority pollutant Hst. For mixed wastewaters, a laboratory study is necessary to determine adsorption characteristics. Wastewater is contacted with a range of concentrations of powdered carbon and adsorption occurs, as graphed ia the form of a Freundhch Isotherm, shown ia Figure 19. [Pg.192]

Antimony may enter the human body through the consumption of meats, vegetables, and seafood which all contain about 0.2—1.1 ppb antimony. Disposal of Antimony. Antimony and its compounds have been designated as priority pollutants by the EPA (35). As a result users, transporters, generators, and processors of antimony-containing material must comply with regulations of the Eederal Resource Conservative and Recovery Act (RCRA). [Pg.199]

T. M. Keinath, Technology Evaluation for Priority Pollutant Removalfrom Dyestuff Manufacture Wastewaters, USEPA report 600/S2-84-055, Washington, D.C., Apr. 1984. [Pg.392]

Tabak, et al., Biodegradability Studies with Organic Priority Pollutant Compounds," USEPA, MERL, Cincinnati, Ohio, April 1980. [Pg.2154]

Table 6 lists typical air emissions from petroleum refining operations. Where possible, typical quantities and concentrations of pollutants are reported. These should be considered very approximate figures since no two refinery operations are identical. However, they do provide a general idea of the quantities, flows, and levels of different types of priority pollutants handled by refinery operations. [Pg.102]

In addition to chemicals covered under TRI, many other chemicals are released. For example, the EPA Office of Air Quality Planning and Standards has compiled air pollutant emission factors for determining the total air emissions of priority pollutants (e.g., VOCs, SO, NO, CO, particulates, etc.) from many refinery sources. The EPA Office of Aerometric Information Retrieval System (AIRS) contains a wide range of information related to stationary sources of air pollution, including the emissions of a number of air pollutants which may be of concern within a particular industry. With the exception of volatile organic compounds (VOCs), there is little overlap with the TRI chemicals reported above. [Pg.106]

Biological Gross organic components (BOD,TOC) Dissolved oxygen Nutrients analysis (NH3, PO4, NO3) pH Priority pollutant analysis ORP... [Pg.121]

Due to the direct contact of water with various species, the aqueous streams are laden with various compounds including methanol, non-process elements NPEs, and organic and inorganic species. In this problem, we focus on methanol as the pimary species in water. Methanol is classified as a high priority pollutant for the pulping industry. In addition, it may provide a source of revenue if properly recovered. [Pg.100]

There are a variety of chemicals that are toxic and used in the drilling fluid makeup. Chromates and asbestos were once commonly used and are now off the market. A mud inventory should be kept for all drilling additives. Included in the inventory are the material safety data sheets (MSDS) that describe each material s pertinent characteristics. The chemicals found on the MSDS sheet should be compared with the priority pollutants and any material should be eliminated if a match is found. The chemicals should also be checked on arrival for breakage and returned to the vendor if defective packaging is found. All mud additives should be housed in a dry area and properly cared for to prevent waste. Chemicals should always be mixed in packaged proportions. Wasted chemicals, ejected to the reserve pit by untrained personnel, can present future liabilities to the operator. [Pg.1353]

Separation of a Series of Priority Pollutants with Programmed Fluorescence Detection... [Pg.182]

Another useful standard Is SRM 1647, priority pollutant polynuclear aromatic hydrocarbons (in acetonitrile). It can be used to calibrate liquid chromatographic Instruments (retention times. Instrument response), to determine percent recoveries, and to fortify aqueous samples with known PAH concentrations. Figure 8 Illustrates the HPLC separation and UV detection (fluorescence is also used extensively) for the 16 priority pollutants. [Pg.117]

Figure 8. Reversed-phase HPLC separation of SRM 1647, priority pollutant polynuclear aromatic hydrocarbons (In acetonitrile), using UV detection. Figure 8. Reversed-phase HPLC separation of SRM 1647, priority pollutant polynuclear aromatic hydrocarbons (In acetonitrile), using UV detection.
EPA. 1979. Water-related environmental fate of 129 priority pollutants. Vol. I Introduction and technical background, metals and inorganics, pesticides and PCB s. Washington, DC U.S. Environmental Protection Agency, Office of Water Planning and Standards. EPA-440/4-79-029a, 27.1-27.16. [Pg.285]


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