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Environment

Nitrous oxide and carbon dioxide emissions from two types of soil amended with manure compost at different ammonium nitrogen rates

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Pages 473-490 | Received 04 Feb 2022, Accepted 04 Jun 2022, Published online: 15 Jun 2022

Figures & data

Table 1. Initial properties of two types of soil and compost.

Table 2. Cumulative N2O and CO2 emissions in the incubation experiment.

Table 3. Responses of cumulative N2O and CO2 emissions to compost type, soil type, and NH4+-N rates by three-way ANOVA.

Figure 1. N2O emissions in the incubation experiment.The left (a)–(c) show results for Kochi soil (K) and the right (d)–(f) do for Ushimado soil (U). The upper (a) and (d) show results for no compost-, the middle (b) and (e) for cattle manure compost (CC)-, and the lower (c) and (f) for mixed compost (MC)-amended soils. The numbers (160, 200, and 400) indicate NH4+-N application rates to soil (mg-N kg−1). Error bars indicate ± standard deviation (n=3).

Figure 1. N2O emissions in the incubation experiment.The left (a)–(c) show results for Kochi soil (K) and the right (d)–(f) do for Ushimado soil (U). The upper (a) and (d) show results for no compost-, the middle (b) and (e) for cattle manure compost (CC)-, and the lower (c) and (f) for mixed compost (MC)-amended soils. The numbers (160, 200, and 400) indicate NH4+-N application rates to soil (mg-N kg−1). Error bars indicate ± standard deviation (n=3).

Figure 2. CO2 emissions in the incubation experiment.The left (a)–(c) show results for Kochi soil (K) and the right (d)–(f) do for Ushimado soil (U). The upper (a) and (d) show results for no compost-, the middle (b) and (e) for cattle manure compost (CC)-, and the lower (c) and (f) for mixed compost (MC)-amended soils. The numbers (160, 200, and 400) indicate NH4+-N application rates to soil (mg-N kg−1). Error bars indicate ± standard deviation (n=3).

Figure 2. CO2 emissions in the incubation experiment.The left (a)–(c) show results for Kochi soil (K) and the right (d)–(f) do for Ushimado soil (U). The upper (a) and (d) show results for no compost-, the middle (b) and (e) for cattle manure compost (CC)-, and the lower (c) and (f) for mixed compost (MC)-amended soils. The numbers (160, 200, and 400) indicate NH4+-N application rates to soil (mg-N kg−1). Error bars indicate ± standard deviation (n=3).

Figure 3. NH4+-N contents in the incubation experiment.The left (a)–(c) show results for Kochi soil (K) and the right (d)–(f) do for Ushimado soil (U). The upper (a) and (d) show results for no compost-, the middle (b) and (e) for cattle manure compost (CC)-, and the lower (c) and (f) for mixed compost (MC)-amended soils. The numbers (160, 200, and 400) indicate NH4+-N application rates to soil (mg-N kg−1). Error bars indicate ± standard deviation (n=3).

Figure 3. NH4+-N contents in the incubation experiment.The left (a)–(c) show results for Kochi soil (K) and the right (d)–(f) do for Ushimado soil (U). The upper (a) and (d) show results for no compost-, the middle (b) and (e) for cattle manure compost (CC)-, and the lower (c) and (f) for mixed compost (MC)-amended soils. The numbers (160, 200, and 400) indicate NH4+-N application rates to soil (mg-N kg−1). Error bars indicate ± standard deviation (n=3).

Figure 4. NO3-N contents in the incubation experiment.The left (a)–(c) show results for Kochi soil (K) and the right (d)–(f) do for Ushimado soil (U). The upper (a) and (d) show results for no compost-, the middle (b) and (e) for cattle manure compost (CC)-, and the lower (c) and (f) for mixed compost (MC)-amended soils. The numbers (160, 200, and 400) indicate NH4+-N application rates to soil (mg-N kg−1). Error bars indicate ± standard deviation (n=3).

Figure 4. NO3−-N contents in the incubation experiment.The left (a)–(c) show results for Kochi soil (K) and the right (d)–(f) do for Ushimado soil (U). The upper (a) and (d) show results for no compost-, the middle (b) and (e) for cattle manure compost (CC)-, and the lower (c) and (f) for mixed compost (MC)-amended soils. The numbers (160, 200, and 400) indicate NH4+-N application rates to soil (mg-N kg−1). Error bars indicate ± standard deviation (n=3).

Figure 5. pH (H2O) values in the incubation experiment.The left (a)–(c) show results for Kochi soil (K) and the right (d)–(f) do for Ushimado soil (U). The upper (a) and (d) show results for no compost-, the middle (b) and (e) for cattle manure compost (CC)-, and the lower (c) and (f) for mixed compost (MC)-amended soils. The numbers (160, 200, and 400) indicate NH4+-N application rates to soil (mg-N kg−1). Error bars indicate ± standard deviation (n=3).

Figure 5. pH (H2O) values in the incubation experiment.The left (a)–(c) show results for Kochi soil (K) and the right (d)–(f) do for Ushimado soil (U). The upper (a) and (d) show results for no compost-, the middle (b) and (e) for cattle manure compost (CC)-, and the lower (c) and (f) for mixed compost (MC)-amended soils. The numbers (160, 200, and 400) indicate NH4+-N application rates to soil (mg-N kg−1). Error bars indicate ± standard deviation (n=3).

Figure 6. Electrical conductivity values in the incubation experiment.The left (a)–(c) show results for Kochi soil (K) and the right (d)–(f) do for Ushimado soil (U). The upper (a) and (d) show results for no compost-, the middle (b) and (e) for cattle manure compost (CC)-, and the lower (c) and (f) for mixed compost (MC)-amended soils. The numbers (160, 200, and 400) indicate NH4+-N application rates to soil (mg-N kg−1). Error bars indicate ± standard deviation (n=3).

Figure 6. Electrical conductivity values in the incubation experiment.The left (a)–(c) show results for Kochi soil (K) and the right (d)–(f) do for Ushimado soil (U). The upper (a) and (d) show results for no compost-, the middle (b) and (e) for cattle manure compost (CC)-, and the lower (c) and (f) for mixed compost (MC)-amended soils. The numbers (160, 200, and 400) indicate NH4+-N application rates to soil (mg-N kg−1). Error bars indicate ± standard deviation (n=3).

Figure 7. Cumulative N2O emissions until day 7 or 21, narG, and nosZ gene copy numbers in the incubation experiment.The left (a)–(c) show results for Kochi soil (K) and the right (d)–(f) do for Ushimado soil (U). The upper (a) and (d) show results for no compost-, the middle (b) and (e) for cattle manure compost (CC)-, and the lower (c) and (f) for mixed compost (MC)-amended soils. The numbers (160, 200, and 400) indicate NH4+-N application rates to soil (mg-N kg−1). Error bars indicate ± standard deviation (n=3).

Means of N2O emissions or each gene type with the same letters are not significantly different within the same treatment across NH4+-N rates (p >0.05). In the original Kochi soil, narG and nosZ gene copy numbers were 0.13×1014 and 0.22×1014 copies g−1 dry soil, respectively. In the original Ushimado soil, narG and nosZgene copy numbers were 0.91×1014 and 0.19×1014 copies g−1 dry soil, respectively.
Figure 7. Cumulative N2O emissions until day 7 or 21, narG, and nosZ gene copy numbers in the incubation experiment.The left (a)–(c) show results for Kochi soil (K) and the right (d)–(f) do for Ushimado soil (U). The upper (a) and (d) show results for no compost-, the middle (b) and (e) for cattle manure compost (CC)-, and the lower (c) and (f) for mixed compost (MC)-amended soils. The numbers (160, 200, and 400) indicate NH4+-N application rates to soil (mg-N kg−1). Error bars indicate ± standard deviation (n=3).

Figure 8. Relationship between cumulative N2O emissions until day 7 and copy numbers of the narG gene in Kochi soil treatments.

Figure 8. Relationship between cumulative N2O emissions until day 7 and copy numbers of the narG gene in Kochi soil treatments.

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