Polymeric gel for surface decontamination of long-lived gamma and beta-emitting radionuclides.

Synthesis and characterization of strippable polymeric-gel solution based on a water-soluble polymer (PVA), plasticizing agent (glycerol), and chelating agent (8-Hydroxyquinoline) for the surface decontamination from 137Cs and 60Co was carried out. Decontamination of glass and PVC surfaces was investigated in the present study, as a function of various chelating agents, gel-layer thickness, and radioactivity level. The decontamination efficiency was up to 95% for both radionuclides after 24 h of contact time with the contaminated surface. The obtained results suggest that the decontamination process of 137Cs and 60Co by polymer gel is possible combined by two mechanisms: chemically and physically.

Preparation of polymer-coated, scintillating ion-exchange resins for monitoring of 99Tc in groundwater.

The present study was oriented to prepare new scintillating anion-exchange resins for measurement of (99)TcO(4)(-) in natural waters. The organic fluor 2-(1-naphthyl)-5-phenyloxazole was diffused into (chloromethyl)polystyrene resin. Thereafter, a thin layer of poly[[2-(methacryloyloxy)ethyl]trimethylammonium chloride] was grafted from the resin surface by surface-initiated atom transfer radical polymerization as an attempt to overcome potential problems related to the leaching of fluor molecules during usage. The residual chloromethyl groups of the polymer-coated resin were aminated by reaction with two different tertiary amines, triethylamine (TEA) and methyldioctylamine (MDOA). Off- and on-line quantification of (99)Tc was achieved with high detection efficiencies of 60.72 ± 1.93% and 72.83 ± 0.81% for resin with TEA and MDOA functional groups, respectively. The detection limit was determined to be less than the maximum contaminant level (33 Bq L(-1)) established under the Safe Drinking Water Act. The two functionalized resins were demonstrated to be selective for pertechnetate from synthetic groundwater containing up to 1000 ppm Cl(-), SO(4)(2-), and HCO(3)(-) and up to 1200 ppb Cr(2)O(7)(2-) in an acidic medium.

Utilization of natural chabazite and mordenite as a reactive barrier for immobilization of hazardous heavy metals.

INTRODUCTION: Understanding the sorption process in natural geomedia is necessary for effective utilization of these materials as low-cost adsorbents and consequently as controlled release hazardous elements. This research was oriented to investigate the affinity of two natural zeolite minerals towards cobalt, zinc, and nickel mixture as an important industrial and radioactive waste. METHOD: The uptake of metal ions as a function of different parameters has been studied using a batch equilibrium technique. RESULTS: The results revealed that the affinity and adsorption capacity of chabazite and mordenite follow the order: Zn(2+) > Co(2+) > Ni(2+), with good fits being obtained using Langmuir and Freundlich adsorption isotherms. The metal uptake was found to be concentration-dependent and independent of the pH over 3.0 to 8.0 range; this reveals that the adsorption mechanism is controlled mainly by a pure ion-exchange reaction at the experimental conditions used. Kinetic curves showed a rather fast exchange reaction for three cations, as equilibrium was mostly reached within 20 min. CONCLUSION: These materials especially chabazite are recommended to be used as a reactive barrier for hazardous heavy metals control.

Sequential separation of actinides by ion chromatography coupled with on-line scintillation detection.

The separation and measurement of actinides by ion chromatography (IC) coupled with on-line scintillation detection was investigated. Separation of (237)Np, (239)Pu, (241)Am, (244)Cm, (230)Th, and (233)U was accomplished using a Dionex CG5 guard column, CS5 separation column, and an elution program utilizing oxalic, diglycolic, and nitric acid eluents. Np(V) was eluted as a weak anionic oxalate complex or as free NpO(2)(+) cation, Am(III) and Cm(III) as anionic oxalate complexes, Pu(IV) and Th(IV) as nonionic diglycolate complexes, and U(VI) as a free uranyl cation. Response of the flow-cell detector was linear over the full range of activities tested (4-1500 Bq). The minimum detectable activities for the investigated analytes ranged from 3.6 Bq for (244)Cm to 5.4 Bq for (230)Th and (239)Pu. The corresponding minimum detectable concentrations based on a 1-L sample ranged from 3.6 to 5.4 KBq m(-3) (96 to 150 pCi L(-1)).