Humic Materials Offer Photoprotective Effect to Escherichia coli Exposed to Damaging Luminous Radiation.

The behavior of Escherichia coli immersed in aqueous systems amended with humic acids, under PAR, UV-A, UV-B, and simulated solar radiation was examined. Culturability, ability to elongate, functioning of the electron transport systems, and glucose uptake were assessed. Humic substances in the range from 1 to 50 mg L-1 protected cells from photoinactivation. Decrease in culturability and cellular activities was significantly (p <0.05) less in the presence of humic material. However, humic acids were not used as nutrients. Neither irradiated nor nonirradiated humic solutions (50 mg L-1) supported the growth of 105 cells ml-1. However, humic acids dissolved in 0.9% NaC1 efficiently absorbed light over wavelengths from 270 to 500 nm. Also, a photoprotective effect against simulated sunlight was observed when humic acids were not in contact with but rather enveloped the cellular suspensions in double-wall microcosms. The protection afforded by humic acids against luminous radiation likely derives from their ability to absorb these radiations and hence reduces the amount of energy reaching the cells.

Participation of oxygen and role of exogenous and endogenous sensitizers in the photoinactivation of Escherichia coli by photosynthetically active radiation, UV-A and UV-B.

We studied the mechanisms by which photosynthetically active radiation (PAR) and ultraviolet (UV-A and UV-B) radiation damage Escherichia coli suspended in water. The roles played by oxygen and exogenous and endogenous sensitizers were analyzed by monitoring changes in the physiological state of irradiated cells. Impairment of the cellular functions was more severe in the case of UV radiations. Radiation caused cellular damage in the absence of oxygen. PAR, UV-A, and UV-B radiation induced photobiological and photodynamic reactions mediated by endogenous sensitizers, which significantly shortened the T90 (time needed to reduce a cellular parameter by 90%) based on the growth ability of the cells. In addition, when exogenous sensitizers were present, the photodynamic reactions also had a negative effect on the operation of the electron transport chains. The presence of oxygen might enhance photoinactivation, affecting both the growth ability and the electron transport chains. Endogenous sensitizers were responsible for the noxious action of oxygen. The presence of dissolved organic material played a protective role against the oxygen by absorbing the incident radiation, thereby reducing the energy that reached the endogenous sensitizers.

Discharge of disinfected wastewater in recipient aquatic systems: fate of allochthonous bacterial and autochthonous protozoa populations.

The discharge of disinfected effluents affects the bacterivorous ability of protozoa and the effect depends on the disinfectant applied. Chlorine provokes a decrease in the number of protozoa and a delay in the bacterivorous ability. The discharge of ozonated and peracetic acid-treated wastewater provokes only an initial slight decrease in bacterivorous ability. No correlation was found between toxicity values detected using the Microtox assay and the effect of disinfected effluents on freshwater protozoa population. After the disinfection processes, recipient systems (fresh and marine water) have different effects on the survival of Escherichia coli populations discharged to them. The effect of the freshwater recipient system is less negative than the effect provoked by sea-water, and the differences detected depend on the disinfection treatment applied. The wastewater bacterial population as a whole is able to grow after discharge of disinfected wastewater to receiving waters. However, in the absence of predation or competition, the recipient systems exert selection, with rod-shaped bacteria predominating.