Content of total phenols in not treated plants of Chenopodium album biotype susceptible to atrazine was 40% higher compared to resistant one. Atrazine applied at 1 kg per hectare increased the amount of these compounds in both biotypes, especially as regards on the level of monophenols in susceptible biotype, which was 3 times higher than in untreated plants. Amount of monophenols in atrazine-resistant biotype increased slightly due to atrazine application. After application of atrazine the polyphenols/monophenols ratio decreased from 4.2 to 1.1 in susceptible biotype, while it was not much changed in resistant biotype. Atrazine increased the content of flavanols in S biotype eight-times compared with untreated plants, while in resistant one this phenomenon was not observed. IAA-oxidase activity measured in vitro was modified by leaf extracts from C. album and Echinochloa crus-galli. Than the extracts from triazine-treated resistant biotype were more capable of protecting the indoloacetic acid (IAA) against enzyme activity. It may suggest that the mechanism susceptibility or resistance to herbicide is not only involved with PS II complex, but consists also in formation in plant the systems which favour or protect the auxin degradation, respectively.

Some active ingredient of herbicides, after application, can create a risk for ground and surface water. The aim of investigations was monitoring of herbicidal pollution in ground and surface water on arable areas. The investigations were conducted in the years 2000-2002. The samples were collected (from stationary points located in the south-west Poland) twice a year (in spring and autumn about 3-6 weeks after nominal term of herbicide application). Surface water was sampled in 27 points and ground water in 18 wells. The residues of herbicide active ingredients (triazine and phenoxy acids) were determined using HPLC methods with UV detection and GLC method with ECD detection. The residues of active compounds in surface water (in spring and autumn) were detected. Residues at concentrations exceeding the EU safety standards were detected most frequently in springtime. The contamination levels in excess admissible limits were found in ca. 15% of surface water samples. In ground water (from wells) residues were detected sporadically and its level was very low (ca. 0.01- 0.1 mg=dm").