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The fluorescence properties of anticancer drugs (ACDs), including steady-state native fluorescence, time-resolved fluorescence, fluorescence polarization, excimer and exciplex emission, laser-induced fluorescence (LIF) with one- or two-photon excitation are reviewed, as well as the use of fluorogenic labels and fluorescent probes for the non-fluorescent ACDs. The interest of monitoring the fluorescence spectral changes to study the interactions of ACDs with biomolecules, such as DNA, proteins, vesicles, and the formation of complexes is discussed. The fluorescence methodologies used for ACDs studies, including fluorescence with two-photon excitation, liquid chromatography and capillary electrophoresis with fluorescence and laser-induced fluorescence (LIF) detection, and fluorescence microscopy, are also surveyed. Analytical and bioanalytical applications of fluorescence, indicating good selectivity and very low limits of detection at the nanomolar and picomolar level for most ACDs, are described. Biomedical and clinical applications of the fluorescence methods, mostly oriented towards the evaluation of the cytoxicity and anti-tumor potential of ACDs in single cells as well as in biological fluids, including blood, serum, plasma, cerebrospinal fluid, urine and feces, are also discussed in detail. This review is based on selected literature published in the last decade (1994-2003).

A detailed toxicological study on several pesticides, including chlorothalonil, cyprodynil, dichlobénil, pendimethaline, trifluraline, and alpha-endosulfan, present at trace levels in air and total atmospheric precipitations of Paris is presented. The pesticides contained in the atmospheric samples, collected during sampling campaigns in February-March 2007, are identified and quantified by a high-performance liquid chromatographic (HPLC)-UV detection method. The toxicity measurements are performed by means of the Microtox bioluminescence method, based on the evaluation of the bioluminescence inhibition of the Vibrio fischeri marine bacteria at two exposure times to the pesticide solutions. The specific toxicity, corresponding to the particular toxicity of the compound under study and represented by the EC(50) parameter, is determined for these pesticides. Also, the global toxicity, which is the toxicity of all micro-pollutants present in the sample under study, is estimated for the extracts of air and atmospheric precipitation (rainwater) samples. The specific toxicities strongly vary with the nature of the pesticide, the EC(50) parameter values being comprised between 0.17 and 0.83 mg/mL and 0.15 and 0.66 mg/mL, respectively, for exposure times of 5 and 15 min. The importance of the atmospheric samples' global toxicity and the respective contribution of the toxic potency of the various pesticides contained in these samples are discussed.