poster - International Conference of Agricultural Engineering
poster - International Conference of Agricultural Engineering poster - International Conference of Agricultural Engineering
In this way, the use of purified water, presents some problems: 1. Urban water derived to the water treatment plants suffers a quality loss since such treated volumes become partially saline in the wastewater treatment plant of Villajoyosa and mainly, in the Benidorm facility. 2. The treated water volumes are uniformly distributed along the year. However, agriculture water consumption does not follow such tendency. Mediterranean climate conditions set higher demand in summer months. 3. The treated water volumes have to be carried to the agricultural areas satisfying the flow and pressure irrigation conditions. 2.2. Improvements in the irrigation water management The previous issues have involved the search for a set of solutions that may or may not yet be implemented. As far as the issue of the water quality, the wastewater facility of Benidorm has improved the salinization problems with the installation of ultrafiltration equipment (Office of Water Programs, 2006). The reverse osmosis system reduces water salinity from 3800 ⁄ to 1000⁄ . The maximum daily treated volume is estimated in 21,000 m 3 when both the water rejection and the total capacity of the facility are taken into account. Thereby, the annual usable irrigation water can be determined straightforward resulting in a total volume of 7.5 hm 3 /year. It can be observed that such volume means around half of the total capacity installed at the Benidorm wastewater plant. Globally, the water treated in the three plants achieves a total volume of 11 hm 3 /year. If the annual consumption rate of the irrigation crops is 5,000 m 3 /hayear, it can be stated that the reuse of water is able to satisfy the irrigation needs of around 2,200 ha. With regard to the non-uniformity of the irrigation water demand, the previous irrigation area is estimated in 2,200 ha, but, it is not really true since it can be defined as the potential irrigation area. As the supply of treated water does not fit the irrigation demand, the real area will be lower. The maximum irrigation needs can be estimated in 35 m 3 /ha-day. Since the daily autonomy of the wastewater plants reaches 31,000 m 3 , the real irrigation area results in 900 ha. Then, farmers in the area are facing a critical situation during dry seasons that are very common in semi-arid regions. The problem can be solved by means of the design and construction of a reservoir, so water can be stored during low irrigation demand seasons. Later on, water will be available in times of high consumption. In brief, the following works and installations are needed in order to incorporate wastewater for irrigation: 1. Implementation of ultrafiltration and desalination technologies to be applied into the present purified wastewater. 2. Implementation of reservoirs with a storage capacity greater than 1 hectometre. Fig. 3 shows an overview of the Alfondons reservoir (Capacity = 300,000 m 3 ) storing the purified water from the Villajoyosa wastewater treatment plant. 3. Implementation and construction of water regulation tanks. 4. Implementation of pipelines driving wastewater from the treatment plants to the irrigation agricultural areas. Nowadays, public administration is performing the following works. 1. An ultrafiltration and desalination plant is being built with a daily capacity of 21,000 m 3 /day, so the annual maximum autonomy reaches 7.7 hm 3 /year. 2. The main water line conducts treated wastewater through a ductile cast iron pipe of 900 mm diameter and 25 kilometres length, Fig. 4.
Therefore, the remaining works are 1. Reservoirs with a storage capacity greater than 1 hectometre. 2. Water regulation tanks. 3. Some wastewater pipelines, from the main conduit up to peripheral irrigation areas. FIGURE 3: Alfondons Reservoir, Villajososa (Capacity = 300,000 m 3 ) FIGURE 4: Main wastewater conduit. a) Aerial passage b) Storage of conduits near Benidorm a) b) Furthermore, the irrigation management of the study area has to sort out an additional issue since: - Most of the irrigated area has changed from the antique surface irrigation technique into pressurized drip irrigation systems. - Water irrigation volumes coming from the reuse of urban water resources through the purification treatment do not individually resolve the whole problem. The higher agricultural water needs requires complementary water works. As a result, it is advisable to incorporate surface runoff either in dry season or in wet rainy seasons becoming the main water contribution to the irrigation management system. Its practical implementation into the pressure irrigation scheme needs some hydraulic works since to the present runoff volumes are exclusively used for flood irrigation. So, some pumping stations, regulating water tanks and both primary and secondary water conduits must be implemented to combine treated wastewater with runoff volumes.
- 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
- Page 119 and 120: Characteristics of Heavy Metal Cont
- 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
- Page 141 and 142: Relationship among compaction, mois
- Page 143 and 144: Cylindrical containers (191mm diame
- Page 145 and 146: Figure 9 High compaction. Bulk dens
- Page 147 and 148: Simulation of water flow with root
- Page 149 and 150: water contents were almost greater
- Page 151 and 152: Operation and Energy Optimization M
- Page 153 and 154: Urmia Salt Lake Urmia FIGURE 1: Gha
- Page 155 and 156: changes have been done in system. F
- Page 157 and 158: Application of Surface Cover and So
- Page 159 and 160: significantly lower than those from
- Page 161 and 162: Choi, J. D., (1997). Effect of Rura
- Page 163: 1.1. Scope and aim The growth of th
- Page 167 and 168: network makes such volumes unaccept
- Page 169 and 170: Reclaimed wastewater reuse has been
- Page 171 and 172: Fig. 2 shows the monitoring results
- Page 173 and 174: 3. Conclusions Reclaimed wastewater
- Page 175 and 176: Q P Ia 2 P Ia S for P≥Ia Q 0
- Page 177 and 178: data P (mm), gauged in 130 pluviogr
- Page 179 and 180: TABLE 2: CN emp values obtained for
- Page 181 and 182: References Chapman, T. G. & Maxwell
- Page 183 and 184: This work, after applying Kennessey
- Page 185 and 186: TABLE 2 - Partial runoff coefficien
- Page 187 and 188: Figure 3 also reports a comparison
- Page 189 and 190: 2. Material and Methods The experim
- Page 191 and 192: TABLE 2: Summary of variance analys
- Page 193 and 194: BEZERRA, I. L.; GHEYI, H. R.; FERNA
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- Page 197 and 198: Figure 3. Hourly values of ET estim
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- Page 201 and 202: 2 Material end methods The wastewat
- Page 203 and 204: Queiroz et al. (2004) and (Fonseca
- Page 205 and 206: Reference list CEREDA, M.P. (2001)
- Page 207 and 208: 2. Data and Methods 2.1. Methods Ir
- Page 209 and 210: 3. Results The water balance model
- Page 211 and 212: Acknowledgments This work was carri
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In this way, the use <strong>of</strong> purified water, presents some problems:<br />
1. Urban water derived to the water treatment plants suffers a quality loss since such<br />
treated volumes become partially saline in the wastewater treatment plant <strong>of</strong><br />
Villajoyosa and mainly, in the Benidorm facility.<br />
2. The treated water volumes are uniformly distributed along the year. However,<br />
agriculture water consumption does not follow such tendency. Mediterranean climate<br />
conditions set higher demand in summer months.<br />
3. The treated water volumes have to be carried to the agricultural areas satisfying the<br />
flow and pressure irrigation conditions.<br />
2.2. Improvements in the irrigation water management<br />
The previous issues have involved the search for a set <strong>of</strong> solutions that may or may not yet<br />
be implemented.<br />
As far as the issue <strong>of</strong> the water quality, the wastewater facility <strong>of</strong> Benidorm has improved the<br />
salinization problems with the installation <strong>of</strong> ultrafiltration equipment (Office <strong>of</strong> Water<br />
Programs, 2006). The reverse osmosis system reduces water salinity from 3800 ⁄ to<br />
1000⁄ .<br />
The maximum daily treated volume is estimated in 21,000 m 3 when both the water rejection<br />
and the total capacity <strong>of</strong> the facility are taken into account. Thereby, the annual usable<br />
irrigation water can be determined straightforward resulting in a total volume <strong>of</strong> 7.5 hm 3 /year.<br />
It can be observed that such volume means around half <strong>of</strong> the total capacity installed at the<br />
Benidorm wastewater plant. Globally, the water treated in the three plants achieves a total<br />
volume <strong>of</strong> 11 hm 3 /year. If the annual consumption rate <strong>of</strong> the irrigation crops is 5,000 m 3 /hayear,<br />
it can be stated that the reuse <strong>of</strong> water is able to satisfy the irrigation needs <strong>of</strong> around<br />
2,200 ha.<br />
With regard to the non-uniformity <strong>of</strong> the irrigation water demand, the previous irrigation area<br />
is estimated in 2,200 ha, but, it is not really true since it can be defined as the potential<br />
irrigation area. As the supply <strong>of</strong> treated water does not fit the irrigation demand, the real area<br />
will be lower. The maximum irrigation needs can be estimated in 35 m 3 /ha-day. Since the<br />
daily autonomy <strong>of</strong> the wastewater plants reaches 31,000 m 3 , the real irrigation area results in<br />
900 ha.<br />
Then, farmers in the area are facing a critical situation during dry seasons that are very<br />
common in semi-arid regions. The problem can be solved by means <strong>of</strong> the design and<br />
construction <strong>of</strong> a reservoir, so water can be stored during low irrigation demand seasons.<br />
Later on, water will be available in times <strong>of</strong> high consumption.<br />
In brief, the following works and installations are needed in order to incorporate wastewater<br />
for irrigation:<br />
1. Implementation <strong>of</strong> ultrafiltration and desalination technologies to be applied into the<br />
present purified wastewater.<br />
2. Implementation <strong>of</strong> reservoirs with a storage capacity greater than 1 hectometre. Fig. 3<br />
shows an overview <strong>of</strong> the Alfondons reservoir (Capacity = 300,000 m 3 ) storing the<br />
purified water from the Villajoyosa wastewater treatment plant.<br />
3. Implementation and construction <strong>of</strong> water regulation tanks.<br />
4. Implementation <strong>of</strong> pipelines driving wastewater from the treatment plants to the<br />
irrigation agricultural areas.<br />
Nowadays, public administration is performing the following works.<br />
1. An ultrafiltration and desalination plant is being built with a daily capacity <strong>of</strong> 21,000<br />
m 3 /day, so the annual maximum autonomy reaches 7.7 hm 3 /year.<br />
2. The main water line conducts treated wastewater through a ductile cast iron pipe <strong>of</strong><br />
900 mm diameter and 25 kilometres length, Fig. 4.