

Solving Environmental Waste Water, Soil, Sludge, Groundwater,
And Bio-
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Figure 4 shows the major components of the decision-

Figure 4. Flow chart of a patented procedure for managing biotreatment and bioremediation systems
measurements of the biomass degrading the waste. These measurements are translated via quantitative analysis into parameters that characterize the cell’s biodegradative ability.
This evaluation step also includes the evaluation of surfactants that might have
to be introduced to eliminate solubility problems and enhance biodegradation rates.
After biokinetic evaluation, the next step is design of the system. By using the
values of the biokinetic parameters and a process control model, it is possible to
generate a series of curves to predict process performance under a variety of treatment
conditions. For example, in activated sludge systems treating toxic or hazardous
wastes, generation of dilute-
After design, the next step in the procedure is process
operation. Figure 4 shows an additional biokinetic evaluation step and an operation
modification step. This is incorporated because treatment or remediation conditions
can change. Waste concentration or quality may vary, and given the biodegradation
characteristics of toxic or hazardous wastes, and the need to maintain process performance,
it is essential to be proactive in operation. By periodically evaluating the biokinetic
constants during remediation or waste treatment, one can detect changes in biological
parameters that reflect changes in the biodegradative capacity of the system. Such
updated values of the biokinetic constants are inserted into the process model for
additional analysis. This information is used in concert with any changes in treatment
conditions, such as contaminant concentrations in the waste stream, and inserted
into the model to determine if changes are required in the engineering controls to
maintain process performance and to continue to meet treatment or cleanup standards.
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