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Each indicator was evaluated using its margin of error and coefficient of variation.
Reversibility of the pH indicator was evaluated by monitoring the changes of the ratios in emission intensity of the two dyes (Figure 4).
The performance of fluorescein isothiocyanate (FITC) and tris 1, 10-phenanathroline) ruthenium ion (Ru phen 3 2+) co-doped silica particles as pH indicator was evaluated.
The resulting probability of functional connectivity (PFC) indicator was evaluated, alongside a patch-based connectivity measure, through the application to four model landscapes based on changes (2 negative and 2 positive) to a control landscape.
The expression of PARP, a well known apoptosis indicator, was evaluated by Western analysis.
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Spatial effects related to the choice of impact indicator were evaluated.
This indicator is evaluated differently for different species, where sheep favour short, fresh grass while cattle prefer taller, more mature forage.
The RNFL-I summary parameters (TSNIT, superior and inferior average, inter-eye symmetry, and nerve fibre indicator) are evaluated.
The performance of the plan with regard to selected indicators was evaluated through simulations.
Furthermore, the choice of indicators was evaluated iteratively to match the available data from the existing regional case studies.
The fate and transport of pathogens and fecal indicators was evaluated in waste stabilization ponds with direct reuse for irrigation, using two systems in Bolivia as case studies.
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