The observed changes were used to build predictive models that were verified by the leave-one-out cross-validation.
For validation of the MCDM methods, the indices of percentage of changes and intensity of changes were used.
Changes in current density and impedance changes were used to monitor metal-tau interactions and tau-tau interactions.
Oxygen concentration changes were used as a proxy of microbial activity (consumption) and oxygen was measured at the beginning and at the end of each 96-hour test (FireSting Oxygen optical probe and temperature sensor, PyroScience®).
Paired t tests of mean percentage pressure changes were used to compare the study and control groups that received the continuous infusions.
Four components, namely, the future impervious area, future climate conditions, future water use, and recent land cover changes were used to evaluate the watershed vulnerability to artificial stressors.
Resulting relative fold changes were used to drive unsupervised hierarchical clustering for the purpose of classifying the cell lines based on proteomic profiles.
Cluster maps of positive (depositional) and negative (erosional) changes were used to derive statistically significant volumetric changes within discrete geomorphic units (beach, foredune, transgressive dune) over one year following vegetation removal.
Under optimal experimental conditions, differential pulse voltammetry (DPV) current changes were used to detect MCP-1 with a broad linear range of 0.09 360 pg mL−1 and a low detection limit of 0.03 pgmL−1 (S/N=3).
In a subsequent stage the scenarios of future climate and land use changes were used to analyse the future for the species selected as indicators of biodiversity in the studied area.
Electrochemical impedance spectroscopy (EIS), open circuit potential and pH changes were used to examine the corrosion of magnesium 4% yttrium alloy (Mg4Y) with and without a silane-epoxy-coating (SEC) in a stirred 0.154 M NaCl solution at 37 °C.
