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Nitrous Oxide Emission from an Agricultural Soil Fertilized with Liquid Swine Waste or Constituents

S.C. Whalen

Dep. of Environmental Science and Engineering, C.B. #7400, Univ. of North Carolina, Chapel Hill, NC 27599-7400 USA



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Fig. 1 Location of North Carolina's "Hog Belt" and the study site

 


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Fig. 2 Treatment effects on N2O emission from fertilized plots (n = 3, each treatment) in Exp. 1. Treatment codes are as follow: CT, control; H2O, deionized water; C, glucose-C; NH4, NH4–N; NC, NH4–N plus glucose-C; W, liquid swine waste. The CT treatment received no nutrient addition, while all other treatments consisted of a liquid phase application of 2.5 cm. Error bars represent ±1 SD. Fluxes followed by the same letter on each sampling date do not differ significantly by Tukey's HSD

 


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Fig. 3 Time course for change in NO3–N and NH4–N concentrations in the 0- to 20-cm soil zone in Exp. 1 for (a) control plots (CT) with no nutrient addition; and (b) plots amended with liquid swine waste (W) or NH4 plus glucose (NC). Each data point represents the mean (±1 SD) for triplicate plots for each treatment. Error bars fall within the symbols in (a). Ordinal scales are similar in (a) and (b) to facilitate comparison

 


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Fig. 4 Time course for change in (a) percentage water-filled pore space (% WFPS) in control (CT; no addition) and liquid swine waste-amended plots (W); and (b) average soil temperature at a central reference station. All data are for the 0- to 20-cm soil zone in Exp. 1. Each data point in (a) is the mean (±1 SD) for triplicate plots for each treatment

 


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Fig. 5 Treatment effects on N2O emission from fertilized plots (n = 3, each treatment) in Exp. 2. Treatment codes are; CT, control; NH4H, high NH4; NH4L, low NH4; NO3H, high NO3; NO3L, low NO3. CT plots received no nutrient addition to Day 11, while all other treatments consisted of a liquid phase application of 2.5 cm. High and low fertilization levels are 150 and 75 kg N ha-1, respectively. Following N2O flux determinations on Day 11, all plots (including CT) were amended with 2.5 cm of deionized water and N2O emission was assessed at Day 11.12. Error bars represent ±1 SD. Fluxes followed by the same letter on each sampling date do not differ significantly by Tukey's HSD

 


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Fig. 6 Time course for change in NO3 and NH4 concentrations in the 0- to 20-cm soil zone for plots fertilized with: (a) NH4–N; and (b) NO3–N. Treatment codes are as follow: NH4H, high NH4; NH4L, low NH4; NO3H, high NO3; NO3L, low NO3. Each data point represents the mean (±1 SD) for triplicate plots amended with high (150 kg N ha-1) or low (75 kg N ha-1) concentrations of nutrient

 


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Fig. 7 Time course for change in (a) percentage water-filled pore space (% WFPS) in control (CT) plots (no addition) and plots amended with liquid NH4–N fertilizer at 150 kg N ha-1 (NH4H); and (b) average soil temperature at a central reference station. All data are for the 0- to 20-cm soil zone in Exp. 2. Each data point in (a) is the mean (±1 SD) for triplicate plots for each treatment

 





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