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Fertilizers and Soil Amendments

Reducing nitrogen pollution while improving tomato production by controlled-release urea application

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Pages 632-641 | Received 11 Feb 2018, Accepted 15 Jun 2018, Published online: 04 Jul 2018

Figures & data

Figure 1. The accumulative release rate of N from controlled-release urea (CRU) in 25°C water.

Figure 1. The accumulative release rate of N from controlled-release urea (CRU) in 25°C water.

Figure 2. Irrigation events and the soil temperature at 15 cm depth in the first season (a) and the second season (b).

Figure 2. Irrigation events and the soil temperature at 15 cm depth in the first season (a) and the second season (b).

Figure 3. Nitrate N concentrations in soil water at a depth of 100 cm in the first season (a) and the second season (b). (The solid arrows represent N top-dressing only for CN treatment at 30, 61 and 83 DAT in the first season, and at 68, 90 and 104 DAT in the second season, respectively).

Figure 3. Nitrate N concentrations in soil water at a depth of 100 cm in the first season (a) and the second season (b). (The solid arrows represent N top-dressing only for CN treatment at 30, 61 and 83 DAT in the first season, and at 68, 90 and 104 DAT in the second season, respectively).

Table 1. Total N2O emissions in the seasons of 2012 and 2013.

Figure 4. N2O fluxes during the first season (a) and the second season (b) in a greenhouse tomato cropping system in Beijing, northern China.

Figure 4. N2O fluxes during the first season (a) and the second season (b) in a greenhouse tomato cropping system in Beijing, northern China.

Table 2. Tomato yields in the seasons of 2012 and 2013.

Table 3. Nitrogen fertilizer and labor costs as well as income from fruits for the two seasons.

Figure 5. Cumulative N release rate from CRUs under field conditions in the two seasons.

Figure 5. Cumulative N release rate from CRUs under field conditions in the two seasons.

Figure 6. Mineral N dynamics in the 0–20 cm soil layer from seedling to harvest in the first season (a) and the second season (b).

Figure 6. Mineral N dynamics in the 0–20 cm soil layer from seedling to harvest in the first season (a) and the second season (b).

Table 4. Calculated apparent N surplus in the greenhouse tomato system in 2012 and 2013 in Beijing, China.

Figure 7. Relationships between the N application rate and the average nitrate N concentration in the soil water (a), N2O emissions (b), and tomato yields (c) under the CK, CRN1, CRN2, and CRN3 treatments based on regression analysis.

Figure 7. Relationships between the N application rate and the average nitrate N concentration in the soil water (a), N2O emissions (b), and tomato yields (c) under the CK, CRN1, CRN2, and CRN3 treatments based on regression analysis.
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