956 resultados para DECISIÓN 792


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Declara infundado el recurso de anulación

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Solicitar al Tribunal de Justicia de la Comunidad Andina la interpretación prejudicial respecto del presente asunto en cuanto corresponde a los artículos 2, 3 y 32 de la Decisión 462 de la Comisión de la Comunidad Andina; 1, 3. 32 y 35 de la Resolución 432 de la Secretaría General de la Comunidad Andina, así COITIO de todas aquellas disposiciones comunitarias que el referido Tribunal de Justicia Internacional considere que deben interpretarse para este caso.

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Se declaró infundado el recurso de anulación interpuesto contra el laudo arbitral proferido el 26 de agosto de 2010 por el Tribunal de Arbitramento constituido para dirimir las controversias surgidas en relación con el contrato de consultoría No. 104 de 2007, celebrado entre el señor Juan Bernardo Botero y la Empresa de Obras Sanitarias de Caldas S.A., E.S.P. - EMPOCALDAS S.A., E.S.P.

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El a quo incurrió en una vía de hecho, por lo tanto revoca dicha sentencia.

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La Cámara de Comercio se abstuvo de registrar el acta de asamblea general de accionistas de la sociedad GOLDEN MEDICAL GROUP COLOMBIA SAS, por medio de la cual se nombraba el revisor fiscal y se aceptaba la renuncia del suplente del gerente. Esta decisión se fundamentó en 2 motivos: (1) No se indicó de manera clara el número de acciones representadas en la reunión. (con fundamento en los artículos 22 de la Ley 1258/08 y la ley 222/95) y (2) A título de recomendación: que por prohibición expresa del código, no es viable dejar un cargo de representación legal vacante, en consecuencia, debe o eliminarse el cargo, lo que acarrea una reforma estatutaria, o nombrar a alguien en dicho cargo.

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Relationships between surface sediment diatom assemblages and lake trophic status were studied in 50 Canadian Precambrian Shield lakes in the Muskoka-Haliburton and southern Ontario regions. The purpose of this study was to develop mathematical regression models to infer lake trophic status from diatom assemblage data. To achieve this goal, however, additional investigations dealing with the evaluation of lake trophic status and the autecological features of key diatom species were carried out. Because a unifying index and classification for lake trophic status was not available, a new multiple index was developed in this study, by the computation of the physical, chemical and biological data from 85 south Ontario lakes. By using the new trophic parameter, the lake trophic level (TL) was determined: TL = 1.37 In[1 +(TP x Chl-a / SD)], where, TP=total phosphorus, Chl-a=chlorophyll-a and SD=Secchi depth. The boundaries between 7 lake trophic categories (Ultra-oligotrophic lakes: 0-0.24; Oligotrophic lakes: 0.241-1.8; Oligomesotrophic lakes: 1.813.0; Mesotrophic lakes: 3.01-4.20; Mesoeutrophic lakes: 4.21-5.4; Eutrophic lakes: 5.41-10 and Hyper-eutrophic lakes: above 10) were established. The new trophic parameter was more convenient for management of water quality, communication to the public and comparison with other lake trophic status indices than many of the previously published indices because the TL index attempts to Increase understanding of the characteristics of lakes and their comprehensive trophic states. It is more reasonable and clear for a unifying determination of true trophic states of lakes. Diatom specIes autecology analysis was central to this thesis. However, the autecological relationship of diatom species and lake trophic status had not previously been well documented. Based on the investigation of the diatom composition and variety of species abundance in 30 study lakes, the distribution optima of diatom species were determined. These determinations were based on a quantitative method called "weighted average" (Charles 1985). On this basis, the diatom species were classified into five trophic categories (oligotrophic, oligomesotrophic, mesotrophic, mesoeutrophic and eutrophic species groups). The resulting diatom trophic status autecological features were used in the regressIon analysis between diatom assemblages and lake trophic status. When the TL trophic level values of the 30 lakes were regressed against their fi ve corresponding diatom trophic groups, the two mathematical equations for expressing the assumed linear relationship between the diatom assemblages composition were determined by (1) uSIng a single regression technique: Trophic level of lake (TL) = 2.643 - 7.575 log (Index D) (r = 0.88 r2 = 0.77 P = 0.0001; n = 30) Where, Index D = (0% + OM% + M%)/(E% + ME% + M%); 4 (2) uSIng a' multiple regressIon technique: TL=4.285-0.076 0%- 0.055 OM% - 0.026 M% + 0.033 ME% + 0.065 E% (r=0.89, r2=0.792, P=O.OOOl, n=30) There was a significant correlation between measured and diatom inferred trophic levels both by single and multiple regressIon methods (P < 0.0001, n=20), when both models were applied to another 20 test lakes. Their correlation coefficients (r2 ) were also statistically significant (r2 >0.68, n=20). As such, the two transfer function models between diatoms and lake trophic status were validated. The two models obtained as noted above were developed using one group of lakes and then tested using an entirely different group of lakes. This study indicated that diatom assemblages are sensitive to lake trophic status. As indicators of lake trophic status, diatoms are especially useful in situations where no local trophic information is available and in studies of the paleotrophic history of lakes. Diatom autecological information was used to develop a theory assessing water quality and lake trophic status.

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Tesis (Maestría en Ciencias de la Administración con Especialidad en Relaciones Industriales) UANL

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Tesis (Maestría en Ciencias de la Administración con Especialidad en Relaciones Industriales) UANL

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Tesis (Maestro en Ciencias de la Administración con Especialidad en Relaciones Industriales) UANL, 1997

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