Old industrial sites are generally contaminated with various pollutants, especially while groundwater are polluted by soluble organic contaminants such as chlorinated solvents or LNAPL (Light Non-Aqueous Phase Liquids) and may generate risks for human health and environment. The management of risks often requires the use of mid-and long-term monitoring methods to assess temporal and spatial changes in plume pollution.Depending on redox conditions and bacterial activity, natural biodegradation of chlorinated solvents may occur. Remediation strategies, such as biostimulation, may be conducted to enhance the degradation of chlorinated solvents. In general, monitoring of remediation is based on water samples analyses. However, this information is often limited in time and space for economical reasons. As a result, a spatiotemporal uncertainty remains on the evolution of the pollution plume. Complementary methods, such as geoelectrical methods, can be used to reduce this uncertainty.Resistivity and time-domain induced polarization (IP) experiment were carried out at different period time to monitor the evolution of pollution plume on the test site. This site is contaminated by chlorinated solvent (trichloroethylene (TCE), dichloroethyle (DCE) and vinyl chloride (VC)) where biodegradation remediation is performed. During the same periods, geochemist parameters, such as pH, redox, ion ferrous, sulphites, dissolved oxygen, conductivity, nitrates and temperature were measured to evaluate the evolution of biodegradation process. The result shows that it exist a link between geochemist parameters and IP response. The integration of results from IP experiment and geochemist parameters allow to point out the different areas of biodegradation process (methanogenesis, sulphate reduction, iron (III) reduction, denitrification and aerobic respiration). The combination of both techniques provides an efficiency tool to monitor pollution plume where biodegradation process is performed.