13.07.2015 Views

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

SHOW MORE
SHOW LESS

Create successful ePaper yourself

Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.

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

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!