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Concentration detection

In x-ray sedimentation, a collimated beam of x-rays permits particle concentration detection as a function of mass. The relationship between the fraction of x-rays transmitted and the mass concentration of particles of atomic weight >12 is expressed as in equation 13 ... [Pg.132]

Electrothermal vaporization can be used for 5-100 )iL sample solution volumes or for small amounts of some solids. A graphite furnace similar to those used for graphite-furnace atomic absorption spectrometry can be used to vaporize the sample. Other devices including boats, ribbons, rods, and filaments, also can be used. The chosen device is heated in a series of steps to temperatures as high as 3000 K to produce a dry vapor and an aerosol, which are transported into the center of the plasma. A transient signal is produced due to matrix and element-dependent volatilization, so the detection system must be capable of time resolution better than 0.25 s. Concentration detection limits are typically 1-2 orders of magnitude better than those obtained via nebulization. Mass detection limits are typically in the range of tens of pg to ng, with a precision of 10% to 15%. [Pg.638]

Minimum concentration causing slight symptoms after several hours Minimum concentration detectable by odour... [Pg.281]

LOD - below limit of detecion Max concentration detected Median... [Pg.215]

Another way in which to gain structural information concerning the N-terminal residue of glycophorins A" and A is to study the N-terminal, mono[ C]methyl derivatives these are produced by using limited amounts of [ C]formaldehyde. There are distinct differences between the N, N -di[ C]methylamino and N -mono[ C]methylamino species (i) a significant, chemical-shift difference exists between the N-terminal dimethyl and monomethyl species (43 and 34 p.p.m.) (li) all of the C resonances of the N-terminal dimethyl species move upheld as the pH is increased (if they move at all), whereas all of the C resonances of the N-terminal, monomethyl species move downfield as the pH is increased and (in) A for the N-terminal monomethyl species tends to be much larger than that for the N-terminal dimethyl species. Point (in) would tend to indicate that it may be more advantageous to study the N-terminal monomethyl species. However, because of allowable protein concentrations, detection limits on available instruments, and technical difficulties, it has thus far... [Pg.192]

Limits of detection for each of the three parent herbicides in surface and groundwater were determined using results obtained from control samples analyzed along with hundreds of surface and ground water sets during the years 1995-2001. In each of these years, the calculated LODs (minimum detectable true concentrations/detection) were below 0.03 pg for acetochlor and metolachlor and 0.05 pg for alachlor. A detection criterion is a measured concentration threshold that defines a likely upper bound for samples not containing the analyte. If the actual concentration of an analyte is at this detection limit or greater, there is at least a 95% chance of detection. [Pg.378]

The amount of analyte (in nanograms) detected in a sample injection was calculated by multiplying the concentration calculated above by the injection volume. Then the concentration detected (in ppm) was determined by dividing this result by the amount of sample injected ... [Pg.485]

Oxime carbamates are generally applied either directly to the tilled soil or sprayed on crops. One of the advantages of oxime carbamates is their short persistence on plants. They are readily degraded into their metabolites shortly after application. However, some of these metabolites have insecticidal properties even more potent than those of the parent compound. For example, the oxidative product of aldicarb is aldicarb sulfoxide, which is observed to be 10-20 times more active as a cholinesterase inhibitor than aldicarb. Other oxime carbamates (e.g., methomyl) have degradates which show no insecticidal activity, have low to negligible ecotoxicity and mammalian toxicity relative to the parent, and are normally nondetectable in crops. Therefore, the residue definition may include the parent oxime carbamate (e.g., methomyl) or parent and metabolites (e.g., aldicarb and its sulfoxide and sulfone metabolites). The tolerance or maximum residue limit (MRL) of pesticides on any food commodity is based on the highest residue concentration detected on mature crops at harvest or the LOQ of the method submitted for enforcement purposes if no detectable residues are found. For example, the tolerances of methomyl in US food commodities range from 0.1 to 6 mg kg for food items and up to 40 mg kg for feed items. ... [Pg.1153]

Table 15.4. Surface Concentrations Detected from the Two Catalyst Samples. Table 15.4. Surface Concentrations Detected from the Two Catalyst Samples.
Table 15.5. Surface Concentrations Detected on the Fresh and Used 5%Pd-0.3%Sn Catalyst Samples. Table 15.5. Surface Concentrations Detected on the Fresh and Used 5%Pd-0.3%Sn Catalyst Samples.
Plasma levels of diisopropyl methylphosphonate were measured in a single lactating Jersey cow after the sixth day of diisopropyl methylphosphonate oral administration (10 mg/kg/day) by gelatin capsule (Ivie 1980). For the first 5 days the cow was given unlabeled compound and fed hay ad libitum. The diisopropyl methylphosphonate administered on the 6th day was labeled with carbon 14. Based on measurements of label in the plasma, absorption in the cow paralleled that in rats and dogs, with the highest concentration detected in the plasma at 2 hours after administration. [Pg.67]

Analytes Matrix Extraction method Detection Range of concentrations detected in the environment REF... [Pg.34]

Ionic surfactants such as sodium dodecyl sulfate can also be detected by ESI. Figure 30 shows an overlay of sub ppm concentrations detected using ion pair chromatography with specific ion LC-MS detection (positive ESI at m/z 265). Gradient elution from 50.0% water containing 5 mM acetic acid triethylamine) to 50.0% 80/20 acetonitrile/water (5mM acetic acid triethylamine) was employed. [Pg.593]

Table 3 DEHP concentration detected in sewage sludge and soil of various countries... Table 3 DEHP concentration detected in sewage sludge and soil of various countries...
Sturgeon et al. [59] have described a hydride generation atomic absorption spectrometry method for the determination of antimony in seawater. The method uses formation of stibene using sodium borohydride. Stibine gas was trapped on the surface of a pyrolytic graphite coated tube at 250 °C and antimony determined by atomic absorption spectrometry. An absolute detection limit of 0.2 ng was obtained and a concentration detection limit of 0.04 pg/1 obtained for 5 ml sample volumes. [Pg.136]

Method3 Mass detection limit (moles) Concentration detection limit (molar)b Characteristics... [Pg.433]

To evaluate the potential risk of Ebro river sediments, the concentrations detected were compared to actual legislation. The WFD does not specifically address sediment management [95]. In contrast to this, the Canadian sediment quality guidelines for the protection of aquatic life [96] provide data for different types of sediments and include 33 compounds, PAHs and DDTs among them. All the PAHs included in the Canadian guidelines are present above the limit, ranging from 3% of the samples for naphthalene to 90% for dibenzo(a,h)anthracene. Special attention has to be paid to benzo(a)pyrene and dibenzo(a,h)anthracene, considered... [Pg.155]

Mass detection limit Concentration detection Advantages/disadvantages... [Pg.177]


See other pages where Concentration detection is mentioned: [Pg.131]    [Pg.315]    [Pg.106]    [Pg.205]    [Pg.293]    [Pg.285]    [Pg.203]    [Pg.448]    [Pg.30]    [Pg.216]    [Pg.489]    [Pg.133]    [Pg.174]    [Pg.464]    [Pg.162]    [Pg.32]    [Pg.241]    [Pg.50]    [Pg.519]    [Pg.272]    [Pg.150]    [Pg.225]    [Pg.101]    [Pg.50]    [Pg.351]    [Pg.470]    [Pg.422]    [Pg.705]   
See also in sourсe #XX -- [ Pg.236 ]




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