Relative Phytotoxicity of Dicyandiamide and Availability of its Nitrogen to Cotton, Corn, and Grain Sorghum 1
1986
The nitrification inhibitor, dicyandiamide (cyanoguanidine) (DCD), can improve fertilizer N efficiency; however, yield reductions and phytotoxicity from the use of DCD have been reported. A green house experiment was designed to determine the effect of DCD on growth, chlorophyll concentration and nutrient concentration of corn ( Zea mays L.), cotton ( Gossypium hirsutum L.), and grain sorghum [ Sorghum bicolor (L.) Moench.]. Dicyandiamide-N/urea-N combi nations of 0:60, 5:55, 10:50, 20:40, 30:30, 40:20, 50:10, and 60:0 mg kg soil were applied to pots containing a Norfolk sandy loam (fine loamy, siliceous, thermic, Typic Paleudults) cropped to each of the three species. Increasing the proportion of N as DCD decreased plant dry weight and leaf chlorophyll concentration and increased stem-leaf N concentrations. Nitrogen recovery decreased curvilin early from 103% to 4%. from 64% to -6%. and from 72% to 4% for corn, cotton, and sorghum, respectively. with increasing propor tion of N as DCD-N. The effects of DCD-N on stem-leaf tissue concentrations of P, K, Ca, Mg, Fe, Mn, Zn, and Cu varied with DCD-N concentration, plant species, and nutrient element. At lower DCD-N concentrations, most nutrient element concentrations were affected by uptake of NH; -N derived from urea; while higher con centrations of DCD-N resulted in increased nutrient element con centrations as a result of reduced plant growth. Additional Index Words: Zea mays, Gossypium hirsutum, Sorghum bicolor, nitrifiication inhibitor, DCD, nutrient composition, chloro phyll. Reeves, D.W., and J.T. Touchton. 1986. Relative phytotoxicity of dicyandiamide and availability of its nitrogen to cotton, corn. and gram sorghum. Soil Sci. Soc. Am. J. 50:1353-1357. D (cyanoguanidine) (DCD), C2H4N4, is a dimer of cyanamide, and is an effective ni trification inhibitor (Hauck, 1980; Nommik, 1958; Reddy, 1964a; Rodgers and Ashworth, 1982). In ad dition to its nitrification inhibiting properties, DCD contains 67% N. In soil, DCD undergoes decompo sition to ammonium and nitrate (Reider and Mi chaud, 1980; Amberger and Vilsmeier, 1979), and the nitrogen in DCD is thus eventually plant-available. The decomposition rate increases with organic carbon (Reddy, 1964a), Fe hydroxides (Amberger and Vils meier, 1979), and temperature (Vilsmeier, 1980). Data from Reddy (1964a) indicated that in the presence of an organic carbon source (sucrose), substantial min eralization of 67 mg kg DCD-N took place in a Cecil sandy loam after only 15 d. Reider and Michaud (1980) reported that rapid mineralization, in three soils (DCD N, to NH; -N and NO3-N) began after 28 d and was complete after approximately 70 d. Contribution of USDA-ARS, Soil-Plant Interaction Research Unit, in cooperation with Dep. of Agronomy and Soils, Alabama Agric. Exp. Stn., Auburn Univ., AL 36849. Received 30 Jan. 1986. Research Agronomist, USDA-ARS, and Associate Professor, re spectively, Auburn Univ., AL 36849. Although DCD is an effective nitrification inhibitor and can improve fertilizer N efficiency, yield reduc tions and phytotoxicity from the use of DCD have been reported. Cowie (1918) reported toxicity symp toms in pot trials with barley ( Hordeum vulgare L.) from concentrations of nitrogen as DCD (DCD-N) ex ceeding 18 mg kg soil. In field trials, however, no injurious effects were noted from 30 kg ha of DCD N. Nommik (I 958) noted leaf injury symptoms in oats ( Avena sativa L.) when rates of DCD-N exceeded 28 kg ha. Reddy (1964b) reported that 16.7 mg kg DCD-N decreased dry matter yields of wheat ( Triti cum aestivum L.), oats ( Avena sativa L.), maize ( Zea mays L.), cotton ( Gossypium hirsutum L.), and to mato ( Lycopersicon esculentum Mill.), but Increased yields of Coastal bermuda grass [ Cynodon dactylon (L.) Pers.]. The decreases in dry weights were, in part, de pendent on the interaction between plant species and N source. In a field experiment with wheat (Sommer and Rossig, 1978), DCD in combination with urea increased N uptake, but reduced grain yields by 10%. Maftoun and Sheibany (1979) reported that DCD de creased green and dry tissue weights of pot-grown soy beans [ Glycine max (L.) Merr.]. The soil concentra tion of DCD-N needed to reduce fresh and dry weights by 50% was 72 and 58 mg kg, respectively. Visual symptoms of DCD phytotoxicity, other than reduced growth, on wheat (Allison et al., 1925; Reddy, 1964b), barley (Cowie, 1918), oats (Nommik, 1958; Reddy, 1964b), and corn, tomato, and cotton (Reddy, 1964b) include leaf tip and margin chlorosis and necrosis. These symptoms suggest that one effect of DCD phy totoxicity may be reduced synthesis or increased deg radation of chlorophyll. The only report of DCD phytotoxicity to corn and cotton limited DCD-N rates to 3.3, 6.7, and 16.7 mg kg (Reddy, 1964b). No efforts have been made to quantify DCD’s phytotoxicity at rates that could result from banded application of N formulated with DCD. In addition, the relative phytotoxicity of DCD to grain sorghum [ Sorghum bicolor (L.) Moench.] has not been
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