Guide to COST-BENEFIT ANALYSIS of investment projects - Ramiri
Guide to COST-BENEFIT ANALYSIS of investment projects - Ramiri
Guide to COST-BENEFIT ANALYSIS of investment projects - Ramiri
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An alternative option considered <strong>to</strong> be technically feasible, taking in<strong>to</strong> account the hydrological and geomorphologicalconditions <strong>of</strong> the project area, is the construction <strong>of</strong> a dam and a long aqueduct (more than100 km long), that supplies water <strong>to</strong> the irrigation and industrial networks. This option has been rejectedfor economic reasons. No other alternative was considered feasible from a technical point <strong>of</strong> view.Figure 4.9 Diagram <strong>of</strong> the overall scheme for the project infrastructuresCity’s sewerage networkEffluent mainWaste water treatment plantT ti t t t l tIndustrial areaWater body <strong>of</strong> thewater final dischargePumpingstationsIrrigatedagricultural landFOCUS: THE WATER DEMANDThe volume <strong>of</strong> water <strong>to</strong> be treated has been estimated on the basis <strong>of</strong> an average daily water actual supply <strong>of</strong> 190 litres per inhabitant, taking in<strong>to</strong>account a reduction fac<strong>to</strong>r <strong>of</strong> 0,8 for the wastewater collected by the urban sewerage system.The size <strong>of</strong> the daily water supply was determined on the basis <strong>of</strong> a study <strong>of</strong> the needs <strong>of</strong> the civil population <strong>of</strong> areas similar <strong>to</strong> those <strong>of</strong> theproject (similar social cus<strong>to</strong>ms, similar consumption levels, same geographic area, etc.) and corrected in the light <strong>of</strong> data on his<strong>to</strong>ric consumptionavailable from the Municipality 81 .For the industrial area the water demand was estimated on the basis <strong>of</strong> the specific consumption <strong>of</strong> industrial plants, taking in<strong>to</strong> account aperiod <strong>of</strong> activity <strong>of</strong> about 11 months per year.The water demand for irrigation, has been calculated on the basis <strong>of</strong> the expected water consumption <strong>of</strong> various specific kind <strong>of</strong> agriculturalcultures, taking in<strong>to</strong> account a period <strong>of</strong> activity <strong>of</strong> about 6 months per year (the dry season). For the cultivation in greenhouses the full year <strong>of</strong>activity is assumed.The <strong>to</strong>tal supply is considered gross <strong>of</strong> leakages in the water network. The real consumption is calculated as follow:real consumption = <strong>to</strong>tal supply – leakagesThe water demand quantification- Drinking water supplied <strong>to</strong> the urban users: 725,000 inhabitants x 190 l/inh.d. x 365 / 1,000 = 50.3 Mm 3 /y- Wastewater <strong>to</strong> be treated in the plant: 50.3 Mm 3 /y x 0.80 = 40.3 Mm 3 /y- Water supplied <strong>to</strong> the urban users: 12.1 Mm 3 /y- Agricultural water demand for irrigation: 3,500 he x 4,500 m 3 /ha y = 15.75 Mm 3 /yThe overall recycled water is 27,9 Mm 3 /y, that is about 70% <strong>of</strong> the <strong>to</strong>tal amount <strong>of</strong> the treated wastewater.The dynamics <strong>of</strong> demandThe dynamics <strong>of</strong> Household demand were determined by the forecast <strong>of</strong> the population resident in the city, which has two components:- a demographic rate <strong>of</strong> growth (the average for the region) <strong>of</strong> 0.06% per year;- a migra<strong>to</strong>ry flow with a positive balance, that gives an average rate <strong>of</strong> growth <strong>of</strong> 0.09%;- as result, an average yearly rate <strong>of</strong> growth <strong>of</strong> 0.15% has been set in the CBA model.The industrial demand is assumed <strong>to</strong> decrease (average yearly rate = -0.3%), because <strong>of</strong> the reduction <strong>of</strong> the network leakage and because <strong>of</strong> therecovery <strong>of</strong> efficiency for the water usage inside the fac<strong>to</strong>ries.For similar reasons the irrigation water demand is assumed <strong>to</strong> decrease as well, with an average yearly rate = -0,5%For simplicity, no other dynamic <strong>of</strong> demand is considered in the present case study.81As it has been mentioned, the volumes <strong>of</strong> wastewater take in<strong>to</strong> account a reduction coefficient <strong>of</strong> 0.80. The contamination level (BODBiochemical Oxygen Demand, COD, Chemical Oxygen Demand) was estimated using standard environmental engineering methods.169