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Tolerance set

The RAC and processed commodities to be collected for each crop are listed in OPPTS 860.1000. Close attention should be paid to the definition and description of many of the commodities listed in the footnotes to Table 1. Reviewing a summary of the actual commercial processing practices for the crop may be helpful. Once the processing procedures and the agronomic practices to be simulated in the field residue trial are understood, a field study can be designed that will truly represent commercial production and processing practices. This will ensure that the study will yield useful, reliable, and accurate data to be used in the tolerance setting process. [Pg.147]

Adequate sensitivity is required to measure an analyte accurately at the MRL (or tolerance) set by the regulatory agency. Tolerances and MRLs sometimes differ between agencies and may change as new scientific evidence indicates that the residue level... [Pg.688]

In order to find a reasonable configuration for our calculation, we take test calculation to optimize the bulk structure of pyrite with GGA and LDA exchange-correlation functional. In the calculation, the plane wave cutoff energy set is 280 eV and the key point set is 4 x 4 x 4, the convergence tolerances set is 10 eV/atom. The optimized cell parameter of the two methods is 0.5415 nm and 0.5425 nm respectively, which is in good agreement with the experiment data (0.5417 nm) reported. It indicates that this configuration is sufficient to satisfy the request of accuracy. [Pg.222]

The processes that the EPA applies to establish pesticide tolerances are confusing and are frequently misunderstood. Readers interested in EPA s tolerance-setting practices should consider reading a comprehensive paper on the subject (Winter, 1992), however the following text gives a brief summary. [Pg.259]

To use the information gained from these types of experiments to model the process. The model can then be optimized and the tolerances set with the only requirement being computer time and confirmation experiments. The large number of experiments that would be required to perform the tolerance design study can be eliminated by this procedure. [Pg.135]

It was assumed that the acute exposure limit was 10.0 and that 10 min samples were required. The tolerance set approach requires 21 samples (10th percentile at 95% confidence) whereas sets of 5, 10 and 20 samples are evaluated for the limiting distribution. [Pg.448]

Table VII shows that both the limiting distribution and the tolerance set generally lead to the correct decision concerning the safety of the environment. However, the limiting distribution produces a similar and often better performance than the tolerance set on the basis of h to % the sample size. For instance when... Table VII shows that both the limiting distribution and the tolerance set generally lead to the correct decision concerning the safety of the environment. However, the limiting distribution produces a similar and often better performance than the tolerance set on the basis of h to % the sample size. For instance when...
Performance of Schemes Based upon Tolerance Sets and Limiting Distributions for Evaluating Acute Exposures to Lethal Toxins. [Exposure Limit = 10.0]... [Pg.450]

In short the approach based upon the concept of a limiting distribution offers a viable alternative to that based upon tolerance sets. The stated objective of reducing the number of samples required for making correct decisions has been achieved. Additional refinements in the selection of parameters for the limiting distribution should further enhance its applicability in evaluating acute exposures. [Pg.451]

The use of a new statistical approach, the limiting distribution, which is based upon the assumption of lognormality, generally leads to correct conclusions on the basis of few samples relative to the number required by tolerance sets. Limiting distributions may also be indexed to the toxicological and environmental realities so that they can be made as conservative as desired. [Pg.452]

The graph at the bottom of Fig. 5 plots the error for each of the matched peptide masses and is useful for assessing whether the tolerance setting used for the search was appropriate. If desired, a more appropriate setting could be chosen and the data researched. [Pg.236]

Through its Pesticide Program, the USFDA samples individual lots of domestically produced and imported foods and analyzes them for pesticide residues to enforce the tolerances set by the USEPA (USFDA, 1989-2005). Domestic samples are collected as close as possible to the point of production in the distribution system ( farm gate ). Imported samples are collected at the point of entry into United States commerce. The emphasis is on the raw agricultural product, which is analyzed in an unwashed, whole (unpeeled), unprocessed state. Processed foods are also included. [Pg.419]

These are relative and absolute error tolerances set by the user. They can be either scalars or arrays, depending on the user s specification of Info(2) as described below. DDAPLUS uses these inputs to construct a vector of mixed local error tolerances... [Pg.193]

Sterilization specifications in the hold period are presented in terms of temperature and time with upper and lower tolerances set around them. The lower specification limits are critical to sterilization. [Pg.333]

Perhaps the greatest use of PAT at this time is to detect what are known as the priority pollutants. These originally included 128 industrial compounds that the Environmental Protection Agency considered as their first priority to monitor and regulate in our nations streams, lakes, and surface water. This list has since been expanded slightly. The tolerances set are very low, a safety factor of 1000 in most cases, and are usually not detectable by ordinary chemical means. However, the compounds can be concentrated by PAT and then are readily detectable. With computer assistance and a databank of standards for a mass spectrometer detector, the entire 128 compounds can be screened, detected, and quantitated at the ppb level and the report written in about 45 minutes. The technique is to choose a mass for each compound and set the mass spectrometer to monitor that mass. This eliminates most of the fragments and speeds up the identification and calculations. Table 33-2 is a list of the priority pollutants. Take a look at this list. If in later years you handle any of these compounds, be extra careful how you dispose of them. [Pg.390]

U.S. Food and Drug Administration (FDA) regulates polychlorinated biphenyls under the Food, Drug, and Cosmetic Act (FD CA) establishing tolerances for PCBs in several food and animal feed. The tolerance set for the milk and dairy products is... [Pg.860]


See other pages where Tolerance set is mentioned: [Pg.136]    [Pg.141]    [Pg.142]    [Pg.145]    [Pg.152]    [Pg.161]    [Pg.213]    [Pg.360]    [Pg.45]    [Pg.49]    [Pg.183]    [Pg.443]    [Pg.445]    [Pg.448]    [Pg.450]    [Pg.451]    [Pg.135]    [Pg.323]    [Pg.236]    [Pg.882]    [Pg.2303]    [Pg.3625]    [Pg.285]    [Pg.79]    [Pg.76]    [Pg.97]    [Pg.27]    [Pg.242]    [Pg.518]   
See also in sourсe #XX -- [ Pg.443 , Pg.444 , Pg.448 ]




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