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poster - International Conference of Agricultural Engineering

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2 Material end methods<br />

The wastewater (WW) was derived from the first environment <strong>of</strong> a system for wastewater<br />

treatment industry cassava and applied with a hydraulic gun with a fixed, maintaining a range<br />

<strong>of</strong> application <strong>of</strong> 30 meters for 10 weeks, 4 hours per week, totalling 40 hours <strong>of</strong> irrigation in<br />

the period from 20 November 2008 to January 23, 2009.<br />

It was used a point source with 6 treatments, 0, 100, 275, 296, 328 and 366 mm <strong>of</strong> WW<br />

applied during the production cycle, respectively L1, L2, L3, L4, L5 and L6, spaced bands at<br />

35, 5, 10, 15, 20, 25 and 30m away from the hydraulic gun. The samples analyzed for<br />

nutritional grass and soil fertility, were performed in the same rays according to Oliveira<br />

et al. (1991) and Embrapa (1997).<br />

The experimental area was set equal to a cut grading on November 20, 2008. Quantifying<br />

the production <strong>of</strong> dray matter (DM) was performed on /1/30/2009, using samples <strong>of</strong> the grass<br />

cut 1.0 cm from the soil in an area <strong>of</strong> 0.16 m 2 .<br />

The soil was characterized as Udult soil (Embrapa 1999) and during experiment were<br />

recorded by station City Gaucha, Paraná, Brazil, 431,8 mm <strong>of</strong> rainfall and the temperature<br />

were 30.0 and 21.0 o C respectively maximum and minimum .<br />

The fertility <strong>of</strong> the soil was measured by the difference between the control and each<br />

treatment <strong>of</strong> the bases sum (Sb) and the organic matter (OM) layers <strong>of</strong> soil from 0.20 and<br />

0.40 m .depth.<br />

To evaluate the extraction <strong>of</strong> soil nutrients by the grass was calculated efficiency <strong>of</strong><br />

absorption <strong>of</strong> nutrients which is the percentage <strong>of</strong> increase <strong>of</strong> nutrients in relation fo control<br />

according to equation 1.<br />

Ni Nt <br />

Ear .100 (1)<br />

Nt <br />

Were:<br />

Era: relative efficiency <strong>of</strong> nutrient absorption by the crops, %;<br />

Ni: content in the leaves <strong>of</strong> grass, after harvest, gKg -1 ;<br />

I, treatment, mm and<br />

Nt: content in the leaves <strong>of</strong> the grass after harvest the control treatment, gKg -1<br />

3 Results and discussion<br />

The chemical composition <strong>of</strong> major plant nutrients was found in RA used in this study<br />

collected the hydraulic gum at the time <strong>of</strong> application is presented in Table 1 which differs<br />

from those shown by Fioretto (2003) and Silva (2005) demonstrating the diversity<br />

<strong>of</strong> composition <strong>of</strong> this waste.<br />

Table 1 Analysis <strong>of</strong> WW collected the nozzle <strong>of</strong> the hydraulic gun<br />

N P K + Ca 2+ Mg 2+ C pH<br />

mgL -1<br />

168 13.3 91.8 21.35 13.23 3500 5.61<br />

In the Figure 1 is observed that the height <strong>of</strong> the grass (H) presents a quadratic<br />

relationship with the blades <strong>of</strong> WW, reaching a maximum height <strong>of</strong> 154 cm to 262 mm L,<br />

using a regression equation <strong>of</strong> the second order to fit the data. However the production <strong>of</strong> dry<br />

matter (DM) grass has been continued increasing in the range <strong>of</strong> L studied, 6.7<br />

to 26.0 Mg ha -1 . Both the linear and quadratic equation and its terms are significant at<br />

p≤ 0.01.

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