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We report a quantitative, two-antibody sandwich immunoassay for phosphinothricin acetyltransferase (PAT), the selectable marker protein. The method yielded a standard curve with a working range of 0 to 5 ng PAT per mL extract. Replicate absorbance values for standards within a single assay showed a coefficient of variation typically less than 5 percent. Over three separate assays, the coefficient of variation for the slope and y-intercept of the standard curve was 3.8 and 3.7 percent, respectively. TransgenicBrassica napus L. seed was used to demonstrate the utility of the assay. Non-transgenic seed extracts did not show a positive immunoassay signal. Determinations of the PAT enzyme conducted on spiked non-transgenic seed extracts repeated in three separate assays fell in the acceptable range of 80 to 120 percent recovery. Transgenic canola seed, analyzed in three separate assays, showed a mean PAT enzyme content of 403 ng/g with a standard error of 19 ng/g and a coefficient of variation of 8.1 percent. The method has also been applied to several other tissues and processed products of canola, maize, and tobacco.

Greenhouse and field studies were conducted to determine the effect of the isooctyl ester of MCPA on the activity of the ethyl ester of fenoxaprop in four grass species. In the greenhouse, wheat tolerated fenoxaprop better than barley, oat, and wild oat. Among wild oat populations, SH 430 was the most tolerant to fenoxaprop followed by MON 73, CS 40, the natural population, and AN 51. MCPA reduced fenoxaprop activity in wheat and barley, protecting the crops from herbicide injury. However, MCPA did not reduce the activity of fenoxaprop in most wild oat lines. In field studies, wheat and barley treated with fenoxaprop at 150 g/ha plus MCPA at 300 g/ha were not appreciably different from weed-free controls while fenoxaprop applied alone at 150 g/ha damaged the crops. Fenoxaprop applied at 150 g/ha in combination with 300 g/ha MCPA resulted in at least 78% wild oat control.

Concentrations of 2,4-D could be quantitated with an indirect enzyme-linked immunosorbent assay (ELISA) and a radioimmunoassay (RIA) in river water and urine. Concentrations of picloram could be quantitated in river water and urine by RIA