Hexaammineruthenium (II)/(III) as alternative redox-probe to Hexacyanoferrat (II)/(III) for stable impedimetric biosensing with gold electrodes.

Gold electrodes have been used in a wide range of electrochemical biosensors because their functionalization process with thiols has been well described and, in general, they offer good chemical stability. However, one of the most commonly used redox-pairs in electrochemical impedance spectroscopy, Hexacyanoferrate (II)/(III), causes corrosion of the gold electrodes and consequently damages the surface modification. This leads to alterations of the sensing signals, and thus, renders the quantitative and sensitive detection of target molecules virtually impossible. To overcome this problem we introduced the in-situ generation of Hexaammineruthenium (II)/(III) as redox-pair during the impedimetric measurement by applying a DC-bias. This DC-bias was chosen in such a way that it supplied Hexaammineruthenium (II) in a suitable concentration at the electrode surface by reducing Hexaammineruthenium (III). We compared the stability of photolithographically fabricated thin-film and screen-printed gold electrodes in Hexacyanoferrate and Hexaammineruthenium solutions. Further, long-time characterization of the electrochemical properties with cyclic voltammetry and electrochemical impedance spectroscopy revealed that Hexaammineruthenium (II)/(III) was an excellent redox-pair for stable impedimetric measurements with gold electrodes. To demonstrate the suitability of Hexaammineruthenium for biosensing we applied it for the impedimetric detection of human-IgG. This biosensor exhibited a linear range from 11.3 ng/mL to 113 µg/mL, which is a suitable range for diagnostic applications.

On the volatilisation and decomposition of cyanide contaminations from gold mining.

Cyanide leaching is the predominant process of gold extraction in large scale mining. Current initiatives for reducing the use of mercury in small scale and artisanal mining tend towards the cyanide technology as the only feasible alternative. Thus, the deliberate handling in consideration of the hazardous nature of cyanide compounds is an issue of particular importance. The hydrogen cyanide volatilised during the leaching process and from the tailings solutions after the gold extraction is reported to be destroyed by oxidation and photolysis from the surrounding atmosphere of gold mines and the sunlight. Cyanide solutions, drained into the surrounding waterbodies are stated to volatilise at a high rate, thus detoxifying them and releasing hydrogen cyanide to the air. In this study laboratory experiments and field tests were conducted to deliver basic data for the volatilisation and destruction of cyanide in the environment. In our laboratory tests we observed neither oxidation by the oxygen of air nor photolysis by UV-irradiation of cyanides after volatilisation from water. The whole amount of volatilised cyanide was found in the exhaust gas after absorption in a strong basic solution. Field experiments in Segovia (Colombia) could confirm these findings. Cyanide concentrations in a range 17 to 30mg/L were measured in a local creek. Hydrogen cyanide amounts of 5ppm were found in the atmosphere surrounding cyanide leaching facilities. With the findings of this study we want to point out that the concentrations of cyanide in the surrounding of cyanide leaching facilities exceed uncritical limits and a destruction via oxidation and photolysis is not detectable. These conclusions should result in initiatives to protect workers and the surrounding population of gold mines from contaminations of cyanide treatments.

Characterization, quantification, and isolation of aluminum oxide particles on grit blasted titanium aluminum alloy hip implants.

BACKGROUND: This study was undertaken to verify whether or not the microstructure of aluminum alloy implants interferes with the characterization and quantification of aluminum inclusions on their surfaces, resulting from grit blasting. METHODS: Four factory-fresh prostheses were investigated by scanning electron microscopy and X-ray microanalysis. Specimens were cut out of the stems and the cross-sections analyzed. The specimens were etched in hot 25% hydrochloric acid. The hydrochloric acid was subsequently filtered with a 0.2-microm-pore filter. The filters were scanned using electron microscopy and X-ray microanalysis. RESULTS: Aluminum oxide particles were found on all investigated stems; the diameter of the particles ranged from 4 to 100 microm. One hundred fifty-four particles were counted per mm(2). No particles were seen on the cross-sections of the implants. Scanning electron microscopy of the Millipore filters revealed aluminum oxide particles. CONCLUSION: Remnants of grit blasting were found only on the surfaces; none were observed on cross-sections. We conclude that the microstructure of titanium aluminum alloy does not interfere with the identification and quantification of particles. Particles were identified on the filters by electron microscopy and X-ray microanalysis. Aluminum oxide on the surface of grit-blasted titanium aluminum alloy implants is, in fact, a residue of grit blasting.