The fate and effects of pharmaceutical products has recently become a matter of environmental concern although little is known about its entry into the environment. Therefore, the cholinergic and cholinesterasicpresent a major target of environmental research related to his entry into the environment and their physico-chemical and biological interactions. Tests using the protein compounds as probes are employed where the optical properties of the complex protein-signal in the presence of analyte or specific groups indicating the concentration of ligand present in the environment. The use of acetylcholinesterase (AChE) activity in biosensors for inhibitors determination is common but few studies explore the intrinsic fluorescence of enzymes in the development of methods to detect chemical species ligands. The objective of this study was to propose new forms of fluorescent probes and bioaffinity for the determination of neurotoxins in different samples. The proposal was to identify probes efficient, easily accessible and low cost for the development of simple, sensitive and selective. For this the detection was based on the variation of the intrinsic fluorescence of proteins (by its specific interaction with the analytes) and the specific combination of extrinsic fluorophores. For the results presented in this plan can be affirmed that the protein fraction obtained can be used as a fluorescent probe in the determination of analytes of this study.Based on the five determinations of analyte, the values of LD and LQ are satisfactory for applying the method in environmental samples (ground) and clinical (urine). Measurements of Gal showed satisfactory performance to suit different types of samples (LD = 1.3 x 10-9mol L-1eLQ = 2.1 x 10-8mol L-1) values and LD LQ to atropine (9.7 x 10-10 mol L -1 and 2.4 x 10-8 mol L-1, respectively) appear to be suitable as other sensors, such as eletroquimioluminescentes showed a value of 1 LQ × 10-7 mol L-1 in urine samples. The method for pesticide methomyl (LD = 9.5 x 10-10 mol L-1 and LQ = 2.2 x 10-8mol L-1), methamidophos (LD = 1.5 x 10-9 mol L-1 and LQ = 3.8 x 10-8 mol L-1) and methyl parathion (LD = 9.7 x 10-10 mol L-1 and LQ = 1.8 x 10-7 mol L-1) comparing presents betterperformance to the other methods described in literature. The method proposed in soil samples and urine (no pretreatment) had recovered from 88% (ground pesticides) and five of analytes in urine. The t test comparison of means, applied to sets of determinations by fluorescence probe method and HPLC indicated the statistical equality in both recoveries. The adaptation of the proposed method a system of the biosensor with the use of an extrinsic probe (thioflavin T) has positively evaluated allowing immobilization of the protein in microplates and the use of thioflavin T as a fluorescent probe-connecting AChE inhibitors.