Bacterial Hazards
Most common bacteria: Camplyobacter
- size: minimum below .45 microns (can pass through)
- prevalence: extremely common, even in developed world
- effects: diarrhea for a week or longer, not usually lethal
- size: 1 micron (small dimension)
- prevalence: rare, but can cause epidemics
- effects: diarrhea, nausea, vomiting, shock, death, usually lethal if untreated
- size: .5 microns (small dimension)
- prevalence: extremely common, but pathogenic strains rare
- effects: haemolytic uraemic syndrome, death, deadly strains rare
- size: .5 micron (small dimension)
- prevalence: less common, mainly in children of developing countries
- effects: dysentery, death, not usually lethal
- death is rare for majority
- typically >2 microns
Chemical Hazards (removable by filtration)
Aldrin and dieldrin
- require coagulation
- chlorinated pesticides
- highly toxic
- generally requires coagulation
- can be deadly
- can be removed by bankside filtration and nanofiltration
- herbicide
- can cause reproductive and immune problems
Chlorpyrifos
- requires coagulation
- insecticide
- inhibition of cholinesterase activity
- requires coagulation
- carcinogen
DDT
- requires coagulation
- pesticide
- hazardous
Mercury
- coagulation
- from electronics, industrial waste
- highly toxic
Nickel
- coagulation
- potential allergic reaction
Polynuclear aromatic hydrocarbons
- coagulation
- industrial
- uranium
- coagulation
- radioactive
References
Rollins, David M. "Campylobacter Summary." Life.umd.edu. N.p., Aug. 2000. Web. 07 May 2013. <http://www.life.umd.edu/classroom/bsci424/pathogendescriptions/Campylobacter.htm>.
Formadi, Herman. "Vibrio Cholerae." Cv.vbi.vt.edu. N.p., 5 July 2007. Web. 07 May 2013. <http://ci.vbi.vt.edu/pathinfo/pathogens/V_cholerae_2.html>.
"Shigella." Cdc.gov. Centers for Disease Control and Prevention, 9 Feb. 2011. Web. 07 May 2013. <http://www.cdc.gov/pulsenet/pathogens_pages/shigella.htm>.
"Guidelines for Drinking-water Quality, Fourth Edition." WHO. N.p., n.d. Web. 07 May 2013. <http://www.who.int/water_sanitation_health/publications/2011/dwq_guidelines/en/index.html>.
Additional Research
Optimal Biofilm Growth Conditions
- higher temperature is better, as long as it is not too high to kill the microbes
- optimal hyduaulic loading ~3m/h
- *note, figures for sand filter
- **3 m/h is for testing, corresponds to ~900 ml/h flow rate
Filter Dimensions and the Use of Iron
According to one study, this group used 5kg iron nails to remove arsenic in a filter of 30'' diameter and 61 cm height. They put the iron nails in the top of the filter separated in a 'diffusion box'
Relative to our dimensions we would need ~7g scaled for radius and height. Scaled for only radius we need 6g - a study later showed the iron did not propagate very far through the filter, accounting for the full height may be unnecessary
References
Fengbing Tang, et al. "Effects of Bio-Sand Filter on Improving the Bio-Stability and Health Security of Drinking Water". Mechanic Automation and Control Engineering (MACE), 2010 International Conference on. 2010. 1878-1881. Print.
"Effects of Bio-Sand Filter on Improving the Bio-Stability and Health Security of Drinking Water". Mechanic Automation and Control Engineering (MACE), 2010 International Conference on. 2010. 1878-1881. Print.
Ngai, Tommy, and Sophie Walewijk. "THE ARSENIC BIOSAND FILTER (ABF) PROJECT: DESIGN OF AN APPROPRIATE HOUSEHOLD DRINKING WATER FILTER FOR RURAL NEPAL." N.p., 2003. Web. 8 May 2013. <http://web.mit.edu/watsan/Docs/Other%20Documents/KAF/NgaiWalewijk-%20ABF%20Report2003.pdf>.
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