Effects of N02-, C103-, and C102-on the induction of nitrate transport and nitrate reductase activity (NRA) as well as their effects on N03-influx into roots of intact barley (Hordeum vulgare cv Klondike) seedlings were investigated. A 24-h pretreatment with 0.1 mol m-3 N02-fully induced N03-transport but failed to induce NRA. Similar pretreatments with C103-and C102-induced neither N03-transport nor NRA. Net C103-uptake was induced by N03-but not by C103-itself, indicating that N03-and C103-transport occur via the N03-carrier. At the uptake step, N02-and C102-strongly inhibited N03-influx; the former exhibited classical competitive kinetics, whereas the latter exhibited complex mixed-type kinetics. C103-proved to be a weak inhibitor of N03-influx (Ki = 16 mol m-3) in a noncompetitive manner. The implications of these findings are discussed in the context of the suitability of these N03-analogs as screening agents for the isolation of mutants defective in N03-transport.Most high-affinity solute transport systems in plants appear to be derepressible; when their solutes are withheld, transport rates increase severalfold (14,22). Ion transport systems involved in the absorption of Cl-, S04, H2PO4-, K+, Na+ (see ref. 14 for review), and NH4' (34) conform to this this pattern.The HATS2 for N03-absorption is, therefore, exceptional in being substrate inducible as well as subject to negative feedback (6,24,31). Enzymes involved in nitrate assimilation, NR and NiR, are also substrate inducible.The absence of a readily available radiotracer for N03-has led to the widespread use of C103-as a N03-analog in studies of N03-uptake and assimilation in both plants and microorganisms (10). 36C03-, which can be generated by electrolysis of 36Cl-, has provided a useful tracer for N03-. However, at high concentrations (0.5 mol m-3 and above) and during prolonged exposures, C103-has proven to be toxic to most plants. Indeed, C103-was previously used extensively as a herbicide (16 In Vivo NRA In vivo NRA in roots was assayed by measuring NO2-production under anaerobic conditions (12). Briefly, excised roots were incubated in potassium phosphate buffer (pH 7.7) containing 100 mol m-3 NO3-, maintained at 250C for 20 min. Before the transfer of roots to anaerobic conditions, the buffer was purged with He for 5 min. At the end of the incubation period, the tubes were transferred to a boiling water bath for 10 min to extract NO2-from the roots. NO2 content was measured spectrophotometrically: the color re-