poster - International Conference of Agricultural Engineering
poster - International Conference of Agricultural Engineering poster - International Conference of Agricultural Engineering
FIGURE 3: A – General view of the gypsum mine; B – area of the mine reject. The digital map of the land degradation levels for the municipalities of Barbalha and Crato in the State of Ceará, related to the years 1987, 2003 and 2008 (Fig. 4) clearly shows the risks to the process of desertification, with particular attention for the areas of the Araripe National Forest (FLONA) that even with low levels of degradation requires vigilance not to progress to more serious levels. In the municipality of Barbalha for the period of 1987/2008 the increase for the level serious of land degradation was 8.69%, and for the very serious corresponded to 9.55%. In the municipality of Crato for the same period, the level serious of land degradation represented 16.50% and for the very serious level of land degradation corresponded to 19.66%, representing a significant advance the process of land degradation in these municipalities. FIGURE 4: Digital maps of the levels of land degradation for the municipalities of: A) Barbalha B) Crato In the municipality of Barbalha, for example, the levels severe and moderately severe of land degradation are relating to clay extraction area. Fig. 5.A shows the appearance of these levels of land degradation along the highway CE-180. These levels also occur at the entrance to the Park Arajara in the municipality of Barbalha (Fig. 5. B and C), where is the largest source of fresh water in sandstone formation, with a flow rate of 240,000 l/h. The occurrence of the level serious of land degradation was observed at various places in the municipality of Crato, as near the urban area and the route to Arajara, in the village Ponta da Serra, where the slope of the mountain was cleared for pasture, and today has a high population density and presence of some quarries.
FIGURE 5. A – Area of exploitation of clay - level serious of land degradation. B and C – Partial view of slopes of the Araripe Mountain, showing areas of landslides. Municipality of Barbalha. In several places the exploitation of clay (Fig. 6 A and B), to supply the ceramic industries in the region, is present, as well as extensive areas explored in cattle raising that surpass the other agricultural activities, such as sugarcane. The mountain slopes are being cleared to supply as much the potteries of firewood as a cheaper source of energy and for use as pasture. The biomass burning was fairly observed during field work (Fig. 6 C). FIGURE 6: A – Area of exploitation of clay. B – Another view of area of exploitation of clay. C – Biomass burning Analyzing the land degradation in the municipality of Marcolândia, State of Piauí, and considering the years 1987, 2003 and 2008 (Fig. 7), the level very low of land degradation occurs only in 1987. FIGURE 7: Digital maps of the levels of land degradation. Municipality of,Marcolândia, State of Piauí.
- Page 41 and 42: Abstract Agriculture and water sour
- Page 43 and 44: In 1985 and 1986 hygienic protectio
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- Page 47 and 48: Biological Nitrogen Fixation In Gen
- Page 49 and 50: We used a completely randomized in
- Page 51 and 52: 5. References AYERS, R.S.; WESTCOT,
- Page 53 and 54: 2 However, the cultures are not alw
- Page 55 and 56: 4 TABEL 2: Mean values of radiation
- Page 57 and 58: accumulated ETo (mm dia -1 ) 6 900
- Page 59 and 60: only the expansion of agricultural
- Page 61 and 62: FIGURE 2: Content of chlorophyll a,
- Page 63 and 64: Evapotranspiration and Crop Coeffic
- Page 65 and 66: were respectively applied in the fi
- Page 67 and 68: TABLE 1: Irrigation depth and actua
- Page 69 and 70: NUTRIENT RETENTION IN WETLANDS USIN
- Page 71 and 72: Table 2. Daily affluent concentrati
- Page 73 and 74: IMPORTANCE OF DRY GEAR MASS CULTURE
- Page 75 and 76: mobilizing assimilated exerted by c
- Page 77 and 78: This method consists of covering th
- Page 79 and 80: uncovered ones, that mixed the wate
- Page 81 and 82: coliforms and E-coli that might hav
- Page 83 and 84: WATER TREATMENT BY COAGULATION WITH
- Page 85 and 86: in a grinder and passed through a 0
- Page 87 and 88: 3.2. Determination of the required
- Page 89 and 90: ANALYSIS OF LEVELS OF LAND DEGRADAT
- Page 91: This methodology consists of a sequ
- Page 95 and 96: Water technology improvements and t
- Page 97 and 98: The Multiattribute Utility Theory (
- Page 99 and 100: higher demand than those of scenari
- Page 101 and 102: YIELD AND BEAN SIZE OF COFFEA ARABI
- Page 103 and 104: uniformity of flowering. The irriga
- Page 105 and 106: Table 3 - Analysis of variance for
- Page 107 and 108: SUGARCANE FERTIRRIGATED WITH MINERA
- Page 109 and 110: 3. Results and Discussion The value
- Page 111 and 112: espectively, compared to that obser
- Page 113 and 114: Optimal Reservoir Operation Model w
- Page 115 and 116: all periods are computed using Eq.
- Page 117 and 118: (a) Calibration (b) Verification Fi
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- Page 121 and 122: 2. Materials and Method 2.1. Study
- Page 123 and 124: TABLE 2: Devices for collecting of
- Page 125 and 126: Calibration of Hargreaves Equation
- Page 127 and 128: Relative error (RE): Index of agree
- Page 129 and 130: Stochastic modelling of Contaminant
- Page 131 and 132: widely used for various fields such
- Page 133 and 134: show that Extvalue and Logistic dis
- Page 135 and 136: Efficiency of water and energy use
- Page 137 and 138: Pressure: it was obtained by means
- Page 139 and 140: them cover similar percentages. Dur
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FIGURE 3: A – General view <strong>of</strong> the gypsum mine; B – area <strong>of</strong> the mine reject.<br />
The digital map <strong>of</strong> the land degradation levels for the municipalities <strong>of</strong> Barbalha and Crato in<br />
the State <strong>of</strong> Ceará, related to the years 1987, 2003 and 2008 (Fig. 4) clearly shows the risks<br />
to the process <strong>of</strong> desertification, with particular attention for the areas <strong>of</strong> the Araripe National<br />
Forest (FLONA) that even with low levels <strong>of</strong> degradation requires vigilance not to progress to<br />
more serious levels. In the municipality <strong>of</strong> Barbalha for the period <strong>of</strong> 1987/2008 the increase<br />
for the level serious <strong>of</strong> land degradation was 8.69%, and for the very serious corresponded to<br />
9.55%. In the municipality <strong>of</strong> Crato for the same period, the level serious <strong>of</strong> land degradation<br />
represented 16.50% and for the very serious level <strong>of</strong> land degradation corresponded to<br />
19.66%, representing a significant advance the process <strong>of</strong> land degradation in these<br />
municipalities.<br />
FIGURE 4: Digital maps <strong>of</strong> the levels <strong>of</strong> land degradation for the municipalities <strong>of</strong>: A)<br />
Barbalha B) Crato<br />
In the municipality <strong>of</strong> Barbalha, for example, the levels severe and moderately severe <strong>of</strong> land<br />
degradation are relating to clay extraction area. Fig. 5.A shows the appearance <strong>of</strong> these<br />
levels <strong>of</strong> land degradation along the highway CE-180. These levels also occur at the<br />
entrance to the Park Arajara in the municipality <strong>of</strong> Barbalha (Fig. 5. B and C), where is the<br />
largest source <strong>of</strong> fresh water in sandstone formation, with a flow rate <strong>of</strong> 240,000 l/h.<br />
The occurrence <strong>of</strong> the level serious <strong>of</strong> land degradation was observed at various places in<br />
the municipality <strong>of</strong> Crato, as near the urban area and the route to Arajara, in the village Ponta<br />
da Serra, where the slope <strong>of</strong> the mountain was cleared for pasture, and today has a high<br />
population density and presence <strong>of</strong> some quarries.