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Decomposition in acidic medium (Fig. 7b) at low concentration of [H3O+] (≤0.07 mol L−1 of HCl ≈ pH = 1.13 for T = 30 and 50 °C) results in an incomplete solid dissolution using steady state conditions for calculation of the conversion.
These, however, are used frequently in neurodegenerative disease and it is therefore necessary to be aware of the methodological boundary conditions for calculation of effect sizes for additive scales.
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The model is applied to a steady-state simulation of Sandia Flame D. The model is useful for simulations where kinetic mechanisms are not available, and also to provide good initial conditions for calculations with full chemical kinetics.
The experimental conditions for calculations using our method were as follows: Water levels were H1 = 40 cm, H2 = 5 cm.
We present an effective boundary condition, for calculation of Local Density Of electromagnetic States (LDOS) via Finite Difference Time Domain Method (FDTD) for applications to nano-scale geometries.
The effect of using "the same" and "different" boundary conditions for the calculation of initial stress and for the subsequent vibration analysis is studied.
The correlation distance of the heterogeneities and fractional fluctuation of elastic parameters control the heterogeneous conditions for the calculation.
The soil parameters that have been used for different soil conditions for the calculation of impedance functions are as given in Table 2.
The deterministic method required calculation to determine the limit-equilibrium of the slope stability given the strength parameters of mass, failure depth, and groundwater conditions for every calculation point in the study area.
Conditions for the calculation were as follows: sample size 353, conventional border for type I error (0.05), exposure variable present in 15% (biomarker level above 85% percentile), endpoint (successful weaning within 28 days) present in 55% patients in the high-level biomarker group, variance inflation factor of 0.2 and detection limit of hazard ratio in a Cox proportional hazards model of 0.60.
The initial conditions for each calculation are the same as those applied for the nominal model.
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