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Water quality control, measures

DeVita and Crunkilton (1998) have examined QC associated with the use of SPMDs. The results of their study demonstrated that quality control measures applied to SPMD analysis met or surpassed conventional guidelines (EPA Method 610 for PAHs in water was used for this comparison) for precision and accuracy. This elevated level of data quality was achieved even though measurements of both overall precision and accuracy of SPMD data encompassed more steps (each with the potential for variability) than the conventional method. In summary, DeVita and Crunkilton (1998) found that QC measures could be used to validate data from the analysis of SPMDs used in the field. In view of the state of SPMD QC, it appears that the SPMD approach for monitoring hydrophobic organic contaminants is equivalent to some EPA-approved methods. [Pg.107]

Ion-exchange chromatography Has a wide range of uses in the food industry, medicine and life and health sciences. This technique has been extensively used in the food industry as a quality control measure and to detect contamination with metals and organic acids. Another important use of this method is in the purification of blood products such as human albumin, growth factors and enzymes. Perhaps the most common application of this technique is the deionization of water and water softening/purification. [Pg.154]

Near IR (NIR) is a quick and non-destructive method for the determination of water in effervescent products. In addition, it is suitable for in-process quality control. Measurement of pH of the solution is often performed. The conditions are important for congruent results. [Pg.1462]

Practical Problems. As we have seen, many different types of disturbances cause changes in ecosystems that are similar and in broad outline predictable. What has been called (8) the strategy of ecosystem development provides a most important basis to anticipate the ecological effects of pollution and to evaluate measures of water quality control. Table II lists some examples of measures and how they grossly affect water quality. This brief list illustrates that water pollution control... [Pg.33]

Table II. Some Measures of Water Quality Control... Table II. Some Measures of Water Quality Control...
General water quality control - the objective of this network is the control of the general quality and surveillance of the quality of the potentially contaminated sections. It measures 40 physical-chemical parameters, divided into four groups. Some of these parameters belong to the list of priority substances of Article 16 of the Water Framework Directive. Sampling frequency depends on the kind of station and the parameter to analyse. A total of almost 700 stations compose the general water quality control in Spain. [Pg.81]

This equation can also be used as a quality control measure for the analytical procedure in atmospheric water if the deviation of the quotient Z[anions]/Z[cations] is > 20% from unit (1), the analysis must be repeated or the samples should be rejected. [Pg.395]

The decision on the sampling method to use is constrained by the type of information needed to answer a specific hypothesis and by the available resources (both logistical and financial). Instantaneous or time-integrated, whole water, or dissolved (filtered), one sample or replicates, and how much and what types of quality control measures will be used are all options that need to be considered as part of the sample collection plan (Alvarez and Jones-Lepp, 2010). The development of a sound sampling plan will help eliminate problems in the field and ensure a representative sample will be collected to meet the needs of the study. [Pg.175]

In practice, inverse cloud point temperature is used more as a quality control measure rather than as a solubility requirement. Although methyl ester ethoxylates are less water soluble than their alcohol ethoxylate counterparts, they can achieve comparable formulatability characteristics at somewhat higher ethylene oxide levels. [Pg.477]

Plant maintenance. Quality of air filtration system maintenance, frequency of compressor blade washing (deposition leads to higher surface blade rou mess, which in turn leads to faster rate of degradation), prevention of potential bearing seal oil leaks into air inlet stream, periodic water quality control in closed-loop evaporative cooling systems, etc., are all measures that can positively influence compressor fouling and their rate of fouling. [Pg.771]

The water quality (air content) and the water flow influenced the measurements using one channel. Therefore the four channel system was first tested in the laboratory with a stationary tube. The best results were obtained using tap water and a well controlled flow in a water-filled chamber. A great difference in the concentration of air in the different grades of water was obvious, and the tap water was superior to soft water during these measurements. [Pg.900]

Statistical quality control is used to first measure and then continuously improve product quality. For example, The Dow Chemical Company s average 1989 performance compared to the typical sales specification were purity, = 99.65 wt % color, APHA = 4 acid (as HCl) = 7.3 ppm and water = 26 ppm. Averages of properties were based on rail car and tank tmck shipment samples during 1989. [Pg.35]

The other analytical methods necessary to control the typical specification given in Table 5 are, for the most part, common quality-control procedures. When a chemical analysis for purity is desired, acetylation or phthalation procedures are commonly employed. In these cases, the alcohol reacts with a measured volume of either acetic or phthalic anhydride in pyridine solution. The loss in titratable acidity in the anhydride solution is a direct measure of the hydroxyl groups reacting in the sample. These procedures are generally free from interference by other functional groups, but both are affected adversely by the presence of excessive water, as this depletes the anhydride reagent strength to a level below that necessary to ensure complete reaction with the alcohol. Both procedures can be adapted to a semimicro- or even microscale deterrnination. [Pg.413]

Valko et al. [37] developed a fast-gradient RP-HPLC method for the determination of a chromatographic hydrophobicity index (CHI). An octadecylsilane (ODS) column and 50 mM aqueous ammonium acetate (pH 7.4) mobile phase with acetonitrile as an organic modifier (0-100%) were used. The system calibration and quality control were performed periodically by measuring retention for 10 standards unionized at pH 7.4. The CHI could then be used as an independent measure of hydrophobicity. In addition, its correlation with linear free-energy parameters explained some molecular descriptors, including H-bond basicity/ acidity and dipolarity/polarizability. It is noted [27] that there are significant differences between CHI values and octanol-water log D values. [Pg.416]

The surface of concrete may be subjected to cycles of wetting and drying during normal service life. This process is a durability concern as harmful ions such as chlorides or sulfates can easily penetrate with the adsorbed water and there is the potential for saturation prior to freezing. Measuring the rate of water penetration into a dry concrete surface is thus important to the quality control of concrete mixes - hopefully yielding a durable product. [Pg.293]

The accuracy of the inductively-coupled plasma procedure was assessed by analysing waters of known sulfate composition, and by comparing measured sulfate values for a wide range of samples with those obtained for the same waters by an automated spectrophotometric procedure. Good agreement is obtained between the derived sulfate measurements and the normal values for International Standard Sea Water and an EPA Quality Control Standard. [Pg.106]

The WFD, so far, has identified 33 priority hazardous pollutants (PHS), for which Environmental Quality Standards (EQS) have been set. To some extent, these EQS can be met through the establishment of emission control measures. These PHS may originate from several different sources and activities. The main sources of toxic substances to water bodies in Europe may be categorised as agriculture, sewage treatment plants, urban runoff, industry, contaminated lake/ river sediment, soils and landfills. Input via atmospheric transport and deposition has also been identified as an important source both far from and close to source areas. Many of the PS are today banned in Europe, but due to their persistence they are still present in the environment [30]. [Pg.400]

Merika [3.51] emphasized from his 17 years of experience with the quality control of freeze dried transplants the importance of sterility and residual moisture control as the decisive characteristics. Furthermore, the leak tightness of the storage containers was constantly controlled. Merika did not measure the product temperature during drying, but controled the process by measuring water vapor pressure and temperatures of the shelves and the condenser. The residual moisture content after 2 years of storage must be below 5 %. All products were sterilized by gamma radiation. [Pg.228]

Effect-based critical limits for soils and ground water have been derived or are under development in various countries for multiple purposes (Radojevic and Bashkin, 1999). These criteria can be used to assess the environmental quality of a site or area, to set priorities in control measures and to derive emission reduction goals. Most of the values are derived from comparable starting points such as protecting terrestrial population, water supply, food quality, and finally, animal and human health. [Pg.62]

Franks, F. 1982. Water activity as a measure of biological viability and quality control. Cereal Foods World 27, 403 107. [Pg.92]

The widespread use of -hexanc as an extractant in the laboratory creates problems in interpreting concentration readings at low levels. Even with good quality control, it may often be impossible to determine whether to attribute a measured value to the actual levels in a sample or to contamination from M-hexanc in the laboratory environment (Otson et al. 1994). For the most part, -hexane is not a common target analyte from water or soil samples. While data based on ambient air samples or sampling in the air of various workplace or residential environments are more numerous, most EPA regulatory programs rely on bulk measurements of total hydrocarbons or total volatile compounds rather than on measurements of specific compounds such as -hexane (Bishop et al. 1994 DeLuchi 1993). [Pg.194]


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