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Priority Analytes

Work with those who submit samples to limit submissions to those likely to yield useful information. In a typical sample queue, some are outside of the parameters required for a standardized assay, having a concentration too low for the precision required or containing matrix components incompatible with the assay. Others may be low on the list of project priorities. Analytical morale gains if every sample run leads to results that are valued. [Pg.39]

The collection of a reference material for trace metals could complement collection of samples for other priority analytes including DOM and DOC. Seawater used for DOM analysis can also be collected in Teflon , for example. Although samples for DOM are not normally stored in plastic bottles (as the iron reference material would be), releases of plasticizers are minimal and are not expected to interfere with the detection of individual organic compounds such as amino acids and sugars. [Pg.52]

BLE 1 Priority Analytes for Studying the Ocean s Role in the Global Carbon Cycle... [Pg.26]

Sensors or analyzers exist for some of the priority analytes, such as 09, pH, and N03 . The challenge in these cases is to improve sensor stability, response rates, or lifetime. However, for most of the priority analytes, there is no existing sensor or analyzer system that will operate for long time periods without operator intervention. The development of sensors for most of these analytes, such as chlorofluorocarbons or dissolved iron, must circumvent the difficulties posed by low analyte concentrations or interference from other dissolved material. Development of specific sensing chemistry is the ultimate means of circumventing these problems. [Pg.30]

MIPS targeting single high-priority analytes may also find broad usage and the role of the template here is to create a site capable of accommodating only one compound thus, it can exhibit a closer structural resemblance to the target. For instance, the nitrosylated nicotine metabolite 4-(methylnitrosamino)-l-(3-pyridyl)-l-butanol (NNAL) (4), a biomarker for nicotine smoke exposure, could be selectively retained by an MIP prepared using the isosteric enamine (5) as template. " ... [Pg.2589]

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]

Improved targeting of pesticide monitoring will require the development of new analytical techniques and EQSs for priority pesticides to determine their environmental significance. To ensure confidence in the monitoring data, analytical techniques need to be able to detect the pesticide at 1/lOth of the EQS, which can be as low as 1 ngPk... [Pg.55]

The development of rapid, accurate, and noninvasive online measurement sensors and instraments is a high-priority goal in the commercialization of biotechnology (Figure 3.4). Some of these instraments will build on analytical methods now used in catalysis and other surface sciences, such as... [Pg.42]

Even if most examples and procedures presented apply to in-house validation, the procedure does not distinguish between validations conducted in a single laboratory and those carried out within inter-laboratory method performance studies. A preference for inter-laboratory studies can be concluded from the statement that laboratories should always give priority to methods which have been tested in method performance studies. Within the procedure a profound overview of different categories of analytical methods according to the available documentation and previous external validation is given. For example, if a method is externally validated in a method performance study, it should be tested for trueness and precision only. On the other hand, a full validation is recommended for those methods which are published in the scientific literature without complete presentation of essential performance characteristics (Table 9). [Pg.121]

Table 2 Summary of some representative current analytical methods for quantitative determination of selected priority and emerging organic contaminants in environmental samples. Adapted from [7]... [Pg.32]

No published data were available on effects and fate of famphur in aquatic ecosystems. This seems to be a high-priority research need in view of the increasing and illegal use of famphur to kill migratory waterfowl (White et al. 1989). In the absence of these data, it is recommended that concentrations of famphur and famoxon in water and in tissues of aquatic organisms not exceed current analytical detection limits of 0.005 mg/L in water or 0.01 mg/kg FW tissue. [Pg.1086]

In order to study simultaneously the behaviour of parent priority surfactants and their degradation products, it is essential to have accurate and sensitive analytical methods that enable the determination of the low concentrations generally occurring in the aquatic environment. As a result of an exhaustive review of the analytical methods used for the quantification within the framework of the three-year research project Priority surfactants and their toxic metabolites in wastewater effluents An integrated study (PRISTINE), it is concluded that the most appropriate procedure for this purpose is high-performance (HP) LC in reversed phase (RP), associated with preliminary techniques of concentration and purification by solid phase extraction (SPE). However, the complex mixtures of metabolites and a lack of reference standards currently limit the applicability of HPLC with UV- or fluorescence (FL-) detection methods. [Pg.25]

B94001 Guidance for the Determination of Appropriate Methods for the Detection of Section 313 Water Priority Chemicals 821F03009 Guidelines Establishing Test Procedures for the Analysis of Pollutants Analytical Methods for Biological Pollutants in Ambient Water Final Rule [Fact Sheet]... [Pg.218]

Detection and quantification of trace chemicals are a major thrust of analytical chemistry. In recent years, much effort has been put into developing detection systems for priority pollutants. Less mature are the detections of substances of interest to law enforcement and security personnel narcotics, chemical agents, and explosives. This volume will discuss the detection of the latter, emphasizing explosive detection both because of its public importance and because it has undergone remarkable developments in the last decade. [Pg.300]

Hall et al. (1985) reported that no 1,2-diphenylhydrazine (less than pg/L) was detected in the Nanticoke River near the Chesapeake Bay. The analytical method involved liquid-liquid extraction, concentration, and. analysis by GC/MS. The Contract Laboratory Program statistical database (queried April 13, 1987) reported that 1 2-diphenylhydrazine has been detected n water at i of 357 hazardous waste sites at a concentration of (96 ppb (CLPSDB 1987), and has been reported at 7 of 117, sites. n the national Priority List database (ATSDR 1990) The U.S. EPA Contract laboratory Program uses GC methods to analyze the contaminants of interest. Since 1,2-diphenylhydrazine oxidize, to azobenzene in the GC injector port and both 1,2-diphenylhydrazine and azobenzene, have the same GC retention time and mass spectra, reports of 1,2-diphenylhydrazine from the Contract Laboratory Program may actually represent detections of 1,2-diphenylhydrazine, azobenzene, or both (see Chapter 6 for more details). [Pg.53]


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