A simple methodological approach for counting and identifying culturable viruses adsorbed to cellulose nitrate membrane filters.

We identified conditions under which Buffalo green monkey cells grew on the surfaces of cellulose nitrate membrane filters in such a way that they covered the entire surface of each filter and penetrated through the pores. When such conditions were used, poliovirus that had previously been adsorbed on the membranes infected the cells and replicated. A plaque assay method and a quantal method (most probable number of cytopathic units) were used to detect and count the viruses adsorbed on the membrane filters. Polioviruses in aqueous suspensions were then concentrated by adsorption to cellulose membrane filters and were subsequently counted without elution, a step which is necessary when the commonly used methods are employed. The pore size of the membrane filter, the sample contents, and the sample volume were optimized for tap water, seawater, and a 0.25 M glycine buffer solution. The numbers of viruses recovered under the optimized conditions were more than 50% greater than the numbers counted by the standard plaque assay. When ceftazidime was added to the assay medium in addition to the antibiotics which are typically used, the method could be used to study natural samples with low and intermediate levels of microbial pollution without decontamination of the samples. This methodological approach also allowed plaque hybridization either directly on cellulose nitrate membranes or on Hybond N+ membranes after the preparations were transferred.

Surveillance and control of aflatoxins B1, B2, G1, G2, and M1 in foodstuffs in the Republic of Cyprus: 1992-1996.

Aflatoxins (AFs) B1, B2, G1, and G2 in locally produced and imported foodstuffs (nuts, cereals, oily seeds, pulses, etc.) were monitored and controlled systematically and effectively from 1992-1996. Samples (peanuts, pistachios, etc.) with total AFs above the Cyprus maximum level (ML) of 10 micrograms/kg fluctuated between 0.7 and 6.9%. The results indicate the effectiveness of monitoring, as well as the need for constant surveillance and control, especially at critical control points (sites of import, primary storage, etc.), to prevent unfit products from entering the Cyprus market. The control included sampling, retainment, analysis, and destruction of foodstuff lots with AF levels above MLs. The highest incidence of aflatoxin contamination was observed in peanut butter (56.7%) and the highest level of AF B1 was found in peanuts (700 micrograms/kg). Levels of AF M1 in raw and pasteurized milk analyzed in 1993, 1995, and 1996 were within both the Cyprus ML (0.5 microgram/L) and the lower ML (0.05 microgram/L) of some European countries. Only 12% of samples had detectable levels of AF M1. Analyses were performed by immunochemical methods. When recoveries were lower than 80%, the AF levels were corrected for recovery.

Nicotine levels in indoor athletic centres.

The levels of nicotine during athletic events were measured at six indoor athletic centres in Cyprus. Samples of air were pumped through a tube containing XAD-4 resin. Quantitation of nicotine was carried out by GC with a method detection limit of 0.03 microgram of nicotine, recovery ranged between 99.5 and 100.5%. Confirmation of the nicotine presence was carried out by GC/MS. The concentrations of nicotine measured were between 3.6 and 39.0 micrograms/Nm3 with a geometric mean range 6.5-28.3 micrograms/Nm3.

Investigating groundwater pollution from different sources with combined biological and chemical methods.

This paper reviews groundwater pollution caused by the disposal of untreated effluents of a dye factory located 20 km to the west of Nicosia (Cyprus). The task of the work was to investigate the nature of the pollution and differentiate it from other possible pollution sources in the area. It focused on toxicity testing and biofractionation in order to address the most toxic pollutants and, on the evaluation of GC/FID profiles for investigating the connection between groundwater pollution and the effluents. This connection was successful due to a multiple comparison amongst the GC/FID profiles resulting from the polluted groundwater, the water from the reference areas and the dye effluents.