Mass balance assessment

Heidler, J. and Halden, R.U. (2007) Mass balance assessment of triclosan removal during conventional sewage treatment. Chemosphere, 66, 362—369. 

Phase II Mass Balance. (/) Determine raw material iaputs. 2) Record water usage. 3) Assess present practice and procedures. (4) Quantify process outputs. (5) Account for emissions to atmosphere, to wastewater, and to off-site disposal. (6) Assemble iaput and output information. (7) Derive a preliminary mass balance. (8) Evaluate and refine the mass balance. 

Material Balances Whenever mass-transfer applications involve equipment of specific dimensions, flux equations alone are inadequate to assess results. A material balance or continuity equation must also be used. When the geometiy is simple, macroscopic balances suffice. The following equation is an overall mass balance for such a unit having bulk-flow ports and ports or interfaces through which diffusive flux can occur ... 

One of the key elements of the assessment phase of a pollution prevention program involves mass balance equations. These calculations are often referred to as material balances the calculations are performed via the consei vation law for mass. The details of this ofien-used law are described below. 

Methods. As discussed in the previous chapter, a number of approaches have been used to assess the presence of potentially toxic trace elements in water. The approaches used in this assessment include comparative media evaluation, a human health and aquatic life guidelines assessment, a mass balance evaluation, probability plots, and toxicity bioassays. Concentrations of trace elements were determined by atomic absorption spectrometry according to standard methods (21,22) by the Oregon State Department of Environmental Quality and the U.S. Geological Survey. 

The preparation of such mass balances can become very tedious. For this reason, the Environmental Assessment Tool for Organic Syntheses (EATOS ) was developed to provide... 

Inputs and outputs assessed in mass balancing are shown in Figure 5.3. The software EATOS was used to calculate all mass balances of processes. Outputs of EATOS are the mass index (equation (5.1), mass of raw material per mass of product output), and the environmental factor (equation (5.2), mass of waste output per mass of product output). EATOS also allows the calculation of cost indices (e.g., reference [15]) (equation (5.3), cost of raw material per mass of product output). 

The scope to increase resource efficiency during scale up was shown to be large in the case studies assessed here. Therefore, efforts to implement methods such as mass balancing or LCA would pay off soon, since this would help to fully tap optimization potentials concerning ecology and economy. 

Zhou et al. [55], The most effective method to assess the capacity is the flow simulation which includes volumetric formulas and more reservoir parameters rather than other methods [56], Mass balance and constitutive relations are accounted in mathematical models to capacity assessment and dimensional analysis consists of fractional flow formulation with dimensionless assessment and analytical approaches [33], From the formulations demonstrated by Okwen and Stewart for analytical investigation, it can be deduced that the C02 buoyancy and injection rate have affected the storage capacity [57], Zheng et al. have indicated the equations employed in Japanese and Chinese methodology and have noted that some parameters in Japanese relation can be compared to the CSLF and DOE techniques [58]. 

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