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A fluorometric technique, based on the combination of RNase and DNase incubation with the use of thiazole orange (RNase/DNase method), was investigated to determine DNA and RNA concentrations in marine plankton. Tests were performed to optimize both RNase and DNase assay conditions. The RNase assay should be conducted at 37° C for 20 min with 0.5 μg·mL−1 of DNase‐free RNase. An incubation at 25° C for 20 min with 10 units ·mL‐1 of RNase‐free DNase were the optimal conditions required for DNA digestion by DNase. The detection limits in terms of minimum biomass for reliable measurements of DNA and RNA were 7.5 and 10 μg of protein · (mL assay)−1, respectively. RNA and DNA concentration were estimated in oligotrophic water samples using the RNase/DNase and other available methods (e.g. a double fluorochrome method). The different techniques provided similar DNA estimations. However, the RNase/DNase method provided the highest sensitivity and a low variability for the estimation of RNA.
A fluorometric technique, based on the combination of RNase and DNase incubation with the use of thiazole orange (RNase/DNase method), was investigated to determine DNA and RNA concentrations in marine plankton. Tests were performed to optimize both RNase and DNase assay conditions. The RNase assay should be conducted at 37° C for 20 min with 0.5 μg·mL−1 of DNase‐free RNase. An incubation at 25° C for 20 min with 10 units ·mL‐1 of RNase‐free DNase were the optimal conditions required for DNA digestion by DNase. The detection limits in terms of minimum biomass for reliable measurements of DNA and RNA were 7.5 and 10 μg of protein · (mL assay)−1, respectively. RNA and DNA concentration were estimated in oligotrophic water samples using the RNase/DNase and other available methods (e.g. a double fluorochrome method). The different techniques provided similar DNA estimations. However, the RNase/DNase method provided the highest sensitivity and a low variability for the estimation of RNA.
As current techniques for the quantification of bacteria are laborious and often imprecise, instrumental approaches such as sedimentation field-flow fractionation (SdFFF) are attractive. In this technique, fluorogenic dyes specific for nucleic acids are used to identify bacterial cells. Bacterial biomass can be quantified directly with SdFFF if the specific fluorescence of bacterial cells is constant. The effect of different growth conditions on the specific fluorescence of one strain each of Escherichia coli, Pseudomonas aeruginosa, Proteus mirabilis and Staphylococcus epidermidis stained with 4',6-diamidino-2-phenylindole was examined. Specific fluorescence varied over a 500-fold range, from 0.22 to 103 arbitrary fluorescence units per cell. Specific fluorescence was highest when cells were in log phase, and lowest when cells were in stationary phase. Specific fluorescence decreased when cells harvested in log phase were starved for 7 d in a carbon-free minimal medium, and increased rapidly (within 2 h) after cells were relieved from carbon limitation. Such variations in specific fluorescence must be considered when using gross fluorescence as a direct indicator of bacterial numbers in the SdFFF technique for quantifying bacterial biomass. Moreover, they have serious implications for the application of fluorescence techniques in other instrumental approaches for bacterial enumeration in environmental samples.
SUMMARY: Assay protocols for RNA and DNA in crude plankton extracts using the fluorochrome SYBR Green II are developed here. The method is based on the fluorescence in 3 aliquots: the first measures RNA after DNA digestion; the second measures DNA after RNA digestion; and the third measures residual fluorescence after digestion of both DNA and RNA. This residual fluorescence measurement is critical for accurate calculations of the nucleic acids. Optimisation of the assay conditions are described: fluorochrome concentration, buffer composition, fluorescence stability, temperature and duration of nuclease incubation. In the optimised procedure, the assays are performed in 5 mM Tris buffer (containing 0.9 mM CaCl 2 ·2H 2 O and 0.9 mM MgCl 2 ·6H 2 O, pH 8.0); DNase and RNase incubations are conducted at 37ºC for 20 min; the fluorochrome is added to all assays at a final concentration of 3.5x10 -4 and readings are done within the 10-60 min period following the SYBR Green II addition. The study evidenced the importance of the residual fluorescence after nuclease digestion, which is especially taken into account in the calculation of the nucleic acid concentrations. Finally, the variability of the fluorescent response to different RNA and DNA standards is examined; from the performed tests, calculations are based on rRNA from calf liver and DNA from calf thymus standards. The accompanying paper (Berdalet et al., 2005) describes the development of the extraction protocol, as well as the application of both protocols in measuring RNA/DNA ratios in natural plankton samples, and a comparison with ethidium bromide based methods.Key words: SYBR Green II, DNase, RNase, RNA/DNA ratios, plankton. RESUMEN: CUANTIFICACIÓN DE ARN Y ADN EN ORGANISMOS PLANCTÓNICOS MARINOS MEDIANTE SYBR GREEN II Y NUCLE-ASES. PARTE A. OPTIMIZACIÓN DEL ENSAYO. -En este trabajo se desarrollan los protocolos para la cuantificación de ARN y ADN en extractos no purificados de plancton utilizando SYBR Green II. El método se basa en la fluorescencia de 3 alícuo-tas: la primera mide el ARN tras la digestión del ADN; la segunda mide el ADN tras la digestión del ARN y la tercera mide la fluorescencia residual tras la digestión tanto del ARN como del ADN. La medida de esta fluorescencia residual es críti-ca para obtener una buena estimación de los ácidos nucleicos. Se describen las condiciones de optimización del ensayo: concentración de fluorocromo, composición del tampón, estabilidad de la fluorescencia, temperatura y duración de la incubación con nucleasas. En el procedimiento optimizado los ensayos se realizan en tampón Tris 5 mM (0.9 mM CaCl 2 ·2H 2 O y 0.9 mM MgCl 2 ·6H 2 O, pH 8); las incubaciones con nucleasas se llevan a cabo a 37°C durante 20 min; el fluorocromo se añade a todos los ensayos a una concentración final de 3.5X10 -4 y las lecturas se realizan en los 10-60 min posteriores a la adición de SYBR Green II. Este estudio evidencia la importancia de la fluorescencia residual después de la digestión con nucleasas, la cual es especialmente incluída...
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