The new immunochemical PETINIA method was associated with significantly higher MPA concentrations in routine therapeutic drug monitoring samples from heart transplant patients. The magnitude of the MPA overestimation was similar to that observed by use of the EMIT method.

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ab s t r ac tElectrodialysis reversal (EDR) treatment of inland brackish water reverse osmosis concentrate was examined. The resistance to CaSO 4 and CaCO 3 scaling in our single-pass and low residence time EDR is better than in the one that was originally developed by Ionics. Our approach is as follows. The RO concentrate of CaSO 4 and CaCO 3 content being close to the saturation level (or slightly supersaturated) is concentrated by EDR 4-5 times. This enables the concentrate volume to decrease and, probably, its disposal cost to the same extent. Assuming brackish water composition as follows (mg/L): Mg 2+ -95.4; Ca 2+ -208.4; Cl --1166; SO 4 2--868.8; HCO 3 --170.8; NO 3 --179.8 and 60% RO recovery, concentrate composition was calculated using Dow Chemical Co. RO system analysis (ROSA) software. Simulated RO concentrate containing (mg/L): Mg 2+ -237.7; Ca 2+ -519.2; Cl --2886; SO 4 2--2164; HCO 3 --414.4; NO 3 --424.3 was then treated in a laboratory EDR stand at 79.1% diluate recovery. The analysis of EDR stack voltage drop vs. EDR process time curves showed that scaling did not occur despite 358.9% calcium sulfate saturation level and 2.29 Langelier Index value. The overall RO-EDR water recovery was equal to 91.6% despite the high scaling potential of investigated water. The expected cost of EDR was found to be promising, especially as compared to evaporation. E.g. the RCC vapor compression evaporation (turned out to be useful for treatment of CaSO 4 containing brine) energy consumption was equal to ca. 20 kWh/m 3 while our EDR laboratory test showed the demand (in similar salinity range) of ca. 3 kWh/m 3 at the estimated unit EDR cost $0.30/m 3 . EDR has especially high potential in the case of waters containing calcium sulfate and calcium bicarbonate as dominant solutes. Thus, CaSO 4 and CaCO 3 may be crystallized in the EDR concentrate and disposed. This will allow zero-discharge technology to develop.

A water-floating photocatalyst composed of TiO 2 deposited on perlite granules was synthesized and characterized. TiO 2 was deposited by direct precipitation of titanium(IV) isopropoxide in the presence of perlite granules followed by calcination at three different temperatures. Temperature induced structural changes were monitored using UV-Vis, infrared and Raman spectroscopy, powder X-ray diffraction, BET surface adsorption, and scanning electron microscopy. The photocatalytic activity of the obtained materials was determined using a model reaction of the oxidative degradation of phenol. The ability of the obtained photocatalyst to float, combined with its ability to absorb solar light, makes it particularly well suited for the purification of shallow water reservoirs and industrial waste stabilization ponds.