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2 | Simulating the Risk of Sanitation to Drinking Water from Groundwater | |||||
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4 | Introduction: | |||||
5 | This simple model allows for looking at inter-relationship between various risk factors that contribute to | |||||
6 | contamination from on-site sanitation. | |||||
7 | The user can provide estimated values of controlling parameters such as depth to water table, depth of pit, distance to well | |||||
8 | The output is in the form of the time taken to travel from sanitation to well. Interpretation of this time as risk is provided. | |||||
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10 | In this example, parameters have been set to look at a 12 month cycle in which the depth to water table and groundwater gradient are varied. | |||||
11 | The situation is typical to a monsoonal type rainfall and a hard rock aquifer with very short distance to drinking water well. | |||||
12 | One can view the individual time taken to reach the water table, to reach the well and the total time taken. | |||||
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14 | The user has options of 3 interventions 1. Using drier latrines, 2. Raising the latrine pit and 3. Having the drinking water well farther. | |||||
15 | The travel time to the well can be seen by making variations on these interventions and see which of them has greater impact. | |||||
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17 | Assumptions: | |||||
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19 | The model is a simple one in which homogenous aquifer conditions are taken. Also, the unsaturated hydraulic conductivity is estimated | |||||
20 | by assuming it as a function of hydraulic loading from the sanitation structure. A 100mm/d loading is considered to lead to saturated conditions. | |||||
21 | From 500 mm/d to 100 mm/d the hysteresis factors is varied from 0.1 to 1 linearly. It is varied from 0 to 0.1 linearly with loading of 0 to 50 mm/d | |||||
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23 | Credit: | |||||
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25 | The first version has been prepared on June 8, 2011 by Sunderrajan Krishnan from INREM Foundation as inputs into a study support by the | |||||
26 | Bill and Melinda Gates Foundation look at sanitation-groundwater contamination linkages. | |||||
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