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Screening, water

It has been suggested that this spherical layer of charges effectively screens water from the external electric field, leading to an apparent dielectric constant much lower than that of bulk water [35,91,95,96]. [Pg.482]

From Figure 9 it can be concluded that the sensitivity of the assay is adequate to screen water samples for the presence of atrazine at a MAC value of 0.1 ppb. In a preliminary experiment 10 river water samples were screened for the presence of atrazine. In eight out of 10 an immunological response corresponding to atrazine levels greater than 0.1 ppb could be confirmed by GC-MS analysis. The other two samples contained atrazine at levels below 0.1 ppb (both with the enzyme immunoassay as with the GC-MS analysis). [Pg.542]

Membrane test to screen water for bacterial contamination developed in Germany -1944... [Pg.278]

Classification screen Water filter tank Water pump Pneumatic feed... [Pg.195]

Jefferies, C., C. L. Alfinson, and 1. McKeown (1997). Performance of a novel combined sewer overflow with perforated coiucal screen. Water Science Technol. Proc. 1997 2nd lAWQ... [Pg.306]

Farre M., Brix R. and Barcelo D., 2005. Screening water for pollutants using biological techniques under European Union funding during the last 10 years, Trends Anal. Chem. 24, 532-45. [Pg.302]

Figure 1.13 Schematic representation of the water/oil interfacial tension = 0.50, the interfacial tension (Xat, decreases from 50 mN m 1 to values as low as 1 0-4 mN m 1. After having crossed the monomeric solubility 70 of the surfactant in the water- and oil-rich phase, 70, where the microemulsion phase (c) exist in form of a lens (right). (From Ref. [26], reprinted with permission of Elsevier.)... Figure 1.13 Schematic representation of the water/oil interfacial tension <jat, (drawn line) as function of the non-ionic surfactant mass fraction 7 at the mean temperature T of the three-phase body. Starting from equal volumes of water (A) and oil (B), i.e. <[> = 0.50, the interfacial tension (Xat, decreases from 50 mN m 1 to values as low as 1 0-4 mN m 1. After having crossed the monomeric solubility 70 of the surfactant in the water- and oil-rich phase, <rab remains constant. The test tubes illustrate the situation without surfactant (left), with only partially screened water/oil contact (centre) and at 7 > 70, where the microemulsion phase (c) exist in form of a lens (right). (From Ref. [26], reprinted with permission of Elsevier.)...
Microtox is used in the field to screen water samples rapidly, even in areas where intermittent electricity supplies may preclude the use of more conventional techniques. The use of Microtox is one of screening to monitor signs of toxicity [35]. Chemical analysis would need to be undertaken if long-term use of a water source were required. Alternative bioassay (fathead minnows, trout, Daphnia magna, etc.), arc unsuitable for field use and requires 48 — 72 h to produce results. [Pg.216]

High performance thin-layer chromatography (HPTLC) has also been used for the determination of carbamate pesticides.Thus, TLC methods provide increased selectivity through silica derivatization, as well as higher analytical precision and sensitivity with high-performance plates. Butz and Stan reported an HPTLC system with automated multiple development (AMD-HPTLC) to screen water samples for pesticides. The method was applied to the determination of 265 pesticides in drinking water spiked with 100 ng/1 of each analyte. [Pg.920]

The slurry of fibers is drawn up through the shaped screen. Water passes through and a layer of fibers builds up on the screen. [Pg.156]

Heat input in the cooling screen water (temperature difference)... [Pg.186]

A total of 15 work days would be needed to analyze the 1115 water sanples by ELISA based on the 80 singular sample on each 96-well plate. Whereas for LC/MS/MS, a total of 115 work days would be required to analyze the same amount of san les based on the 10-12 san les per assay set. In addition, ELISA uses and generates minimum chemicals and waste(solvents and reagents) and is sinq)ler and time-and cost-effective conq>ared to the conventional chemical meftiod. The ELISA kit for sulfentrazone and SCA is, therefore, a reliable and effective analytical tool for screening water sanq>les. It is particularly useful in the beginning and at the end of each groundwater study, when detectable residues are not expected. [Pg.303]


See other pages where Screening, water is mentioned: [Pg.47]    [Pg.404]    [Pg.472]    [Pg.472]    [Pg.276]    [Pg.470]    [Pg.377]    [Pg.89]    [Pg.129]    [Pg.39]    [Pg.2951]    [Pg.24]    [Pg.287]    [Pg.241]    [Pg.42]    [Pg.450]    [Pg.148]    [Pg.57]    [Pg.184]    [Pg.95]   
See also in sourсe #XX -- [ Pg.307 ]




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Screening methods water-reactive materials

Screening, of water

Stationary water screens

Surface waters screen-printed electrodes

Water-Sensitive Virtual Screening Approaches and Applications

Water-sensitive virtual screening

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