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Residuals patterns

Species and variety of the crop and the cultivation method employed may have a significant impact on the residue pattern. Therefore, the selection, sowing, planting, treatment, and care of the crops should be described in detail and should reflect the methods typical of the region in question. [Pg.181]

A detailed overview of pesticide residue patterns in conventional, IPM grown and organic food has been published that draws on three datasets collected in the 1990s (Baker et al., 2002). Six years of data from the USDA s PDP... [Pg.267]

Kannan, K., J. Falandysz, N. Yamashita, S. Tanabe, and R. Tatasukawa. 1992. Temporal trends of organochlorine concentrations in cod-liver oil from the southern Baltic proper, 1971-1989. Mar. Pollut. Bull. 24 358-363. Kawano, M., T. Inoue, T. Wada, H. Hidaka, and R. Tatasukawa. 1988. Bioconcentration and residue patterns of chlordane compounds in marine animals invertebrates, fish, mammals, and seabirds. Environ. Sci. Technol. 22 792-797. [Pg.881]

In reality, neither residue levels nor food consumption estimates exist as single values. They can better be depicted as distributions because residue patterns vary greatly, as do food consumption practices. [Pg.268]

DCB, and 2,6-DCB] as the river flowed over contaminated upstream sediments. Thus, they hypothesized that the composition of the PCBs available for deposition in the downstream sediments had already undergone major changes. This theory led to the conclusion that the alterations in PCB residue patterns found in bottom sediments were not likely to be the result of in situ weathering processes. Instead they were seen as caused by the scavenging from the water column of previously altered mixtures of PCBs by suspended particles or water-filtering macrophytes growing in the sediments. [Pg.568]

Kannan, K., Tanabe, S., Tatsukawa, R., Sinha, R.K., 1994. Biodegration capacity and residue pattern of organochlorines in Ganges River dolphins from India. Toxicol. Environ. Chem. 42, 249-261. [Pg.479]

Figure 12.2. Organochlorine residue patterns in migratory migrant waders from the Philippines, Vietnam, and India (Kunisue et al., 2003). Figure 12.2. Organochlorine residue patterns in migratory migrant waders from the Philippines, Vietnam, and India (Kunisue et al., 2003).
In all cases, graphical or other methods should be used to access the adequacy of the fit obtained. These examinations often uncover residual patterns that may indicate the suitability of using a transformation, or some kind of weighting, or adding extra variables such as quadratic or interaction terms. Unfortunately, inference becomes almost impossible if the total subset of available predictors is augmented subjectively in this way. [Pg.139]

Figure 1. Residue pattern for single annual addition and first-order half... Figure 1. Residue pattern for single annual addition and first-order half...
The residue pattern for soil from the granule-treated pond is shown in Figure 3. Predictably, concentrations are highest within the first few... [Pg.285]

It may come to mind that the introduction of crops that impact pesticide use will inevitably lead to shifts in pesticide residue patterns in foods derived from these crops. In insect-resistant crops, for example, reductions in insecticide sprays against the target insects can be anticipated and concomitant reductions in crop residues. For herbicide toler-... [Pg.318]

The question about the fate of toxaphene in the environment cannot be answered in a simple way. In the environment, only some toxaphene components remain unmetabolized and are accumulated in biota. This leads to a simpler toxaphene residue pattern compared to the technical mixture. In 1979, Saleh et al. studied the metabolism of B7-515 (P-32) and technical toxaphene with seven test animals. Both were metabolized the least in chicken and the most in monkeys [175]. Furthermore, the major toxaphene congeners present in the technical mixture are not the same as those found in environmental samples due to selective bioaccumulation/metabolization and abiotic degradation mechanisms (see Table 6). [Pg.268]

Qiao, G.L. Chang, S.K. Riviere, J.E. Effects of anatomical site and occlusion on the percutaneous absorption and residue pattern of 2,6-[ring- C]parathion in vivo in pigs. Toxicol. Appl. Pharmacol. 1993, 121, 131-138. [Pg.3825]

Examine the daily disinfection log sheet for chlorine feed rates and chlorine residual patterns. Compare both contact time and chlorine residual with those required by the proper regulatory agency. As a general rule, residuals between 0.2 and 1.0 mg/L after 15-30 min contact times provide good disinfection. As shown in the example, the 27 min contact time and 1.0 mg/L chlorine residual should be generally sufficient. [Pg.408]

Bergman et al. 1994). All major -ortho-VCBs are transformed to 4-hydroxy-chlorobiphenyl metabolites, retained in plasma or blood. Changes in residue patterns, including actual increases over time, indicating possible dechlorination products were observed by Wolff et al. (1992). Brown (1994) further suggested that humans were capable of very slow PCB dechlorination. [Pg.354]

Tilmicosin, Figure 1, is a new semisynthetic antibiotic derived from the macrolide antibiotic tylosin. The synthesis and antibacterial activity of tilmicosin have been described by Debono, et al. and Kirst, et al. (/-4). Tilmicosin has in vitro activity against a variety of Gram positive and Gram negative bacteria, as well as mycoplasma species. It is effective for treatment of bovine respiratory disease caused by Pasteurella haemolytica when administered as a single subcutaneous injection (5, 6). This paper describes the excretion, tissue residue pattern, and metabolism of tilmicosin when injected into cattle, and also gives comparative metabolism data from rats which were dosed orally. [Pg.158]

Figure 10.4 Residue patterns in alfalfa and rye grass shoots and roots from the microcosm after chemical applied as a seed treatment. [Reproduced with permission from J. D. Gile and... Figure 10.4 Residue patterns in alfalfa and rye grass shoots and roots from the microcosm after chemical applied as a seed treatment. [Reproduced with permission from J. D. Gile and...
Figure 14.5 depicts the predicted vs. observed permeability constants (log Kp) for all 288 treatment combinations studied without taking into account the specific mixtures at which these chemicals were dosed. The residuals of this model showed no further correlation to penetrant properties. However, when vehicle/mixture component properties were analyzed, trends in residuals became evident. An excellent single parameter explaining some variability of this residual pattern (R of 0.44) was log (1 /Henry constant) (1/HC). Figure 14.6 depicts the modified LFER model including an MF = log (1/HC). [Pg.297]

Kawano M, Inoue T, Wada T, et al. 1988. Bioconcentration and residue patterns of chlordane compounds in marine animals Invertebrates, fish, mammals, and seabirds. Environmental Science... [Pg.223]

Figure 9. X-ray powder dififraction pattern of AS4M03O15 phase (1), M0O3 phase JCPDS No. 35-0609 and residual pattern of phase transformation (1)... Figure 9. X-ray powder dififraction pattern of AS4M03O15 phase (1), M0O3 phase JCPDS No. 35-0609 and residual pattern of phase transformation (1)...

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See also in sourсe #XX -- [ Pg.177 ]

See also in sourсe #XX -- [ Pg.149 ]

See also in sourсe #XX -- [ Pg.210 , Pg.213 , Pg.214 ]




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