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Czech Republic selection

Table 3.2 shows the 5 Cu and 5 Cc values of herbivores, omnivores, carnivores and humans. The (climate-corrected) trophic level effect between herbivores and carnivores is 0.90%o. Human values are closer to carnivore and omnivore values than to herbivore 5 Cc values. The human 5 Cc values are on average 0.66%o more positive than the herbivore 5 Cc values, a good estimate for a carnivore effect in humans (see section on trophic level effects, below). The average human 5 Cc value is -19.92 1.28%o,which would indicate that Holocene humans in Europe had a diet that consisted of C3 terrestrial foods, whieh is as might be expected. By looking at the humans separate from the total bone data set, we notice potential human food selection (Fig. 3.3) we can see a non-climatic pattern, which is much less uniform than in the total bone data set (Fig. 3.2b). Italy (6 Cc = -21.3%o) has a much more negative 8 Cc value than the Czech Republic (8 Cc =-18.7%o), Spain (8 Cc = -19.3%o) and Greece (-18.9%o but the 8 N of 9.0%odoes not indicate marine food), while the northern European coimtries are closer to a 5 Cc value of-20%o. What the actual causes are for this pattern in the human samples is not clear to better understand these variations it is best to consider, where possible, the 8 N values with the 8 Cc values. [Pg.54]

Michulec, M. and W. Wardencki. 2005. Selected aspects of chromatographic solvents residues determination using HS, SPME an SDE techniques for isolation and preconcentration of analytes. Book of abstracts of 11th International Symposium on Separation Sciences, September 12-14, 2005, Pardubice, Czech Republic. [Pg.367]

Table 4.2 summarises some of these product data for selected countries. Only in Austria and the Czech Republic did vegetables not feature largely. Growth rates for the vegetables market vary considerably from 1% in the Netherlands to 58-100% in Greece, Belgium and Switzerland. [Pg.66]

Smirous, P. (2005). The influence of recurrent phenotypic selection to the chosen yield characters of caraway (Carum carvi, L.). Ph.D. Thesis, Mendel University of Agriculture and Forestry in Brno, Czech Republic, 79 p. [Pg.23]

Cerna M, Spevackova V, Cejchanova M, et al. 1997. Population-based biomonitoring in the Czech Republic-the system and selected results. Sci Total Environ 204 263-270. [Pg.325]

Pribylova P, Klanova J, Holoubek I (2006) Screening of short- and medium-chain chlorinated paraffins in selected riverine sediments and sludge from the Czech Republic. Environ Pollut 144 248-254... [Pg.104]

The results of the project of National Institute of Public Health, Prague, The Health Risk Assessment of Dietary Exposures to the Selected Chemical Substances (Total Diet Study), Czech Republic, 1994 are presented in Table 14 (National Institute of Public Health in Prague, 1995b). In this study 552 composite food samples were analyzed representing 1920 individual commodities from 12 sites of the Czech Republic. No statistically significant difference was found between individual sites with a different environmental pollution level. The estimated exposure dose for the Czech Republic ranges between 28 and 41% of the PTWI. [Pg.99]

Cema, M., Spevackova, V., Cejchanova, M., Benes, B., Rosser, P., Bavorova, H., Ocadlikova, D., Smid, J., Kubinova, R., 1997. Population-based biomonitoring in the Czech Republic - the system and selected results. Sci. Total. Environ. 204, 263-270. [Pg.106]

National Institute of Publie Health in Prague, 1995b. The Health Risk Assessment of Dietary Exposures to the Selected Chemical Substances in the Czech Republic. Prague. [Pg.106]

Sigmundova, V., Skripenova, A., Borosova, B., Benasova, A., 1997. Content of toxic metals in biological materials in inhabitants from selected regions of the Slovak Republic. In Proceedings of the Conference Health and the Environment, Milovy, Czech Republic, pp. 242-247 (in Slovak). [Pg.107]

Figure 6.4 Histogram of age by gender (F, female M, male) in general (a) and hospital (b) populations. Results of a population study conducted in the Czech Republic during the period 1995-2002 concerning iodine intake in the country. Three thousand nine hundred and two individuals participated in this study from a general, randomly selected population (a) and 4642 individuals from a hospital population, which consisted of patients from the Institute of Endocrinology in Prague, The Czech Republic. Figure 6.4 Histogram of age by gender (F, female M, male) in general (a) and hospital (b) populations. Results of a population study conducted in the Czech Republic during the period 1995-2002 concerning iodine intake in the country. Three thousand nine hundred and two individuals participated in this study from a general, randomly selected population (a) and 4642 individuals from a hospital population, which consisted of patients from the Institute of Endocrinology in Prague, The Czech Republic.
Figure 86.1 loduria in selected regions of Czech Republic (1991-2006) for adults (N = 4205). [Pg.837]

Our findings are the result of a study that was carried out on a population sample selected randomly from the register of a Czech Health Insurance Company (VZP) over a 5-year interval after the realization of the need for a sophisticated program of iodine prophylaxis in the Czech Republic. The examinations were conducted by the same individuals... [Pg.842]

Petrov, V.A. Abstracts of 15th European Symposium on Fluorine Chemistry, Prague, Czech Republic, July 15-20, 2007, p 161. (a) Petrov, V.A. Marshall, W.J. Reactions of Polyfiuorinated Thietanes. Selective Synthesis of Polyfluorinated Thietanes S-Oxides and 2-Substituted 5-fiuoro-4-(trifiuoromethyl)-2,3-dihydrothiophenes, J. Fluorine Chem. 2009, doi 10.1016/j.jfiuchem.2009.06.011. [Pg.88]

Using the comparative methodology discussed above, we will in the following present some results based on data which were collected with the help of national experts in each of the EU member States as well as in Norway, Switzerland and the Czech Republic. The financial performance of the farms is assessed using the indicators profits per ha and profits per family work unit in combination with important factors which determine profitability, e.g. yield levels and prices realised and support payments received. Most of the studies analysed are based on approach 3. In some cases, the selection of an adequate reference group was, in our opinion, not completely successfixl. Since the selection of the reference system has a large influence on results, the findings of the respective studies have to be interpreted with due care. [Pg.143]

Kapicka a., Petrovsky E., Ustjak S. and Machackov a K. (1999) Proxy mapping of fly-ash pollution of soils around a coal-burning power plant a case study in the Czech Republic. In Geochemical Exploration 1997 Selected Papers from the 18th International Geochemical Exploration Symposium, (eds. R. BoGOCH and M. Shirav), VoL 66, pp. 291-297, Elsevier, Amsterdam. [Pg.186]

ABSTRACT The article deals with the landfills and risk identification within waste disposal in a selected region of the Czech Republic. As a case study the systematic risk identification, its evaluation and selection of critical risks during waste disposal at the selected landfills was made. Within the risk management process the methodology of safety audit and checldist analysis were apphed. This methodology is based on semi-quantitative evaluation of received data which are the base for the risk comparison at the selected landfills. [Pg.894]

None of the above mentioned approaches, methodical instructions or suggestions for risk management of waste disposal at rim landfills is apphed in the Czech Republic. The mentioned resume has become the reason for the risk management execution and evaluation at the selected landfills, as well for the evaluation of their safety and elaboration of general principals of risk management for landfills operations. [Pg.895]

In the region of South Moravia in the Czech Republic there are 2 landfills of inert waste, 10 landfills of non-hazardous waste and 4 landfiUs of hazardous waste. In 2007 66,77% of municipal waste was placed to these landfills. The article represents the results of the risk identification at two selected landfUls of non-hazardous waste (S-003) in the region of South Moravia. Furthermore, within the specific research the risk identification at 2 landfiUs of hazardous waste was conducted (Bumbova, A. 2009). [Pg.895]

For the determination of the vertical temperature difference component, several models are given in EN 1991-1-5 (2003). Two alternative procedures based on the linear or non-linear difference components are allowed for the national choice as one of 23 National Determined Parameters (NDPs) included in EN 1991-1-5 (2003). The comparative analyses made in the Czech Republic in some prestressed bridges and in one composite bridge resulted in the selection of the nonlinear approach for the vertical temperature difference component in the National Annex. Presently, the longterm experimental measurements of temperatures in some bridges in the Bohemia and their statistical analyses will facilitate to refine the thermal models recommended in Eurocodes for national conditions. The decision of giving preference to the non-Unear approach than to linear approach in the CzechNational Atmex of EN 1991-1-5 (2003) will be verified. [Pg.1353]

The information given in the Background document (1999) and the recent results of experimental monitoring on selected bridges in the Czech Republic are considered for the analyses of temperature components and assessment of partial factors for thermal actions. [Pg.1353]

To illustrate the implementation of remote-controlled systems within electrical distribution networks and their contribution to improvement in reli-abftity of electric energy supply to customers, we conducted an analysis of effects produced by the remote-controlled devices (Distribution substations within municipal underground system. Section switch-disconnectors and circuit-breakers in over-head hnes) to operation parameters of a selected section of the electrical distribution network in the Northern Moravia (Czech Republic). [Pg.1845]

Argon, helium, hydrogen and nitrogen (99.9 % purity, Technoplyn Linde, Czech Republic) were selected for transport measurements. Because of their inertness the surface transport was absent. [Pg.218]


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