poster - International Conference of Agricultural Engineering

poster - International Conference of Agricultural Engineering poster - International Conference of Agricultural Engineering

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As the DM production was increased in the range of slides were evaluated, it is understood that not worked with the blade that maximizes the productivity of the grass, but the values are higher than those quoted by Mitidiere (1983) and Correa (1999), demonstrating that there is no restriction on the use of wastewater for irrigation and fertilization of grass. He also noted that there is a direct relationship between height and DM yield of grass. Figure 1 - Relationship between plant height (H), dry matter yield (DM) and the blades mean of WW applied in the area (L). Evaluating the results shown in Figure 2 it is observed that in the 0 to 0.20 m estimates of Sb according to AR applied blades reach a maximum of increase of 0.212 cmol c dm- 3 to the blade of 200 mm and the layer 0.20 to 0.40 m depth Sb maximum, .802 cmol c dm -3 was estimated with the blade of 270 mm. It is also observed that the addition of Sb was higher in the layer of 0.20 to 0.40 m in depth and that the reduction of Sb in the descending part of both curves results in leaching of the bases for the deeper regions of the soil. Figure 2 - Alteration in the sum of bases 0-20 and 20-40 cm soil depth

Queiroz et al. (2004) and (Fonseca et al. 2005) also obtained an increase in the sum of bases respectively applying swine wastewater and treated sewage effluent thus demonstrating that the bases are applied through the wastewater can supplement water demand of culture. However the balance of calcium magnesium and potassium may be compromised. The concentration of organic matter in soil extracts studied, differ from that of Malavolta et al. (2002) who observed a tendency of concentration of organic matter in swine wastewater decreases with the depth of the soil. This is due grained organic matter present in the AR is lower than that of swine wastewater. It should also be the efficiency of the system of treatment of these wastewaters. Figure 3 - Alteration in organic matter content in soil layers 0-20 and 20-40 cm depth In Figures 4.5 and 6 shows that the Ear were higher than the control which demonstrates the importance of WW for the purpose of fertirrigation of Brachiaria brizantha cv. MG-5. The values of the Ear nitrogen show that the presence of WW did not affect the transformation process of the nitrogen molecules in the soil a fact pointed out by Reis et. al. (2005). However, these do not coincides with the addition of MS accumulated by the plant during the experiment, which was linear and growing as shown in Figure 1, but correlated with the production factor H, maximized with 215 mm while the Ear nitrogen was maximized with the depth of 213 mm The Ear potassium, adjusted with a linear regression equation due to the applied layer of WW, showing that the potassium level of RA were not sufficient to limit the Ear this nutrient by the crops.. The Ear phosphorus showed lower values compared to the N and K, that fits as a second order equation with minimum point when it receives the estimated treatment of 238.3 mm and has Ear 9.3%.

Queiroz et al. (2004) and (Fonseca et al. 2005) also obtained an increase in the sum <strong>of</strong><br />

bases respectively applying swine wastewater and treated sewage effluent thus<br />

demonstrating that the bases are applied through the wastewater can supplement water<br />

demand <strong>of</strong> culture. However the balance <strong>of</strong> calcium magnesium and potassium may be<br />

compromised.<br />

The concentration <strong>of</strong> organic matter in soil extracts studied, differ from that <strong>of</strong> Malavolta<br />

et al. (2002) who observed a tendency <strong>of</strong> concentration <strong>of</strong> organic matter in swine<br />

wastewater decreases with the depth <strong>of</strong> the soil. This is due grained organic matter present<br />

in the AR is lower than that <strong>of</strong> swine wastewater. It should also be the efficiency <strong>of</strong> the<br />

system <strong>of</strong> treatment <strong>of</strong> these wastewaters.<br />

Figure 3 - Alteration in organic matter content in soil layers 0-20 and 20-40 cm depth<br />

In Figures 4.5 and 6 shows that the Ear were higher than the control which demonstrates<br />

the importance <strong>of</strong> WW for the purpose <strong>of</strong> fertirrigation <strong>of</strong> Brachiaria brizantha cv. MG-5. The<br />

values <strong>of</strong> the Ear nitrogen show that the presence <strong>of</strong> WW did not affect the transformation<br />

process <strong>of</strong> the nitrogen molecules in the soil a fact pointed out by Reis et. al. (2005).<br />

However, these do not coincides with the addition <strong>of</strong> MS accumulated by the plant during the<br />

experiment, which was linear and growing as shown in Figure 1, but correlated with the<br />

production factor H, maximized with 215 mm while the Ear nitrogen was maximized with the<br />

depth <strong>of</strong> 213 mm<br />

The Ear potassium, adjusted with a linear regression equation due to the applied layer <strong>of</strong><br />

WW, showing that the potassium level <strong>of</strong> RA were not sufficient to limit the Ear this nutrient<br />

by the crops..<br />

The Ear phosphorus showed lower values compared to the N and K, that fits as a second<br />

order equation with minimum point when it receives the estimated treatment <strong>of</strong> 238.3 mm<br />

and has Ear 9.3%.

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