Difference between revisions of "Water treatment options"

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m (New page: ==Jargon== pH - a measure of the acidity of the water. Most fresh water sources have a pH of 6-8. The ocean's pH is ~8.3. A pH above 7 is considered preferable because enteric pathogens ...)
 
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== Jargon ==
==Jargon==
 
 
pH - a measure of the acidity of the water. Most fresh water sources have a pH of 6-8.  The ocean's pH is ~8.3. A pH above 7 is considered preferable because enteric pathogens prefer a pH below 7.
 
pH - a measure of the acidity of the water. Most fresh water sources have a pH of 6-8.  The ocean's pH is ~8.3. A pH above 7 is considered preferable because enteric pathogens prefer a pH below 7.
  
 
Enteric Pathogen - diseases which attack the digestive system such as Typhoid and Cholera
 
Enteric Pathogen - diseases which attack the digestive system such as Typhoid and Cholera
  
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Sedimentation - passing the water through a very calm, pond like structure so that the solids will settle out.
  
==Contaminants==
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Coagulation - using chemicals such as [[allum]] to accelerate sedimentation.
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== Contaminants ==
 
{| class="prettytable"
 
{| class="prettytable"
 
| Contamination types
 
| Contamination types
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The pH and salinity of different sources can vary, even though the sources may be in a close proximity. pH is an important factor where treatment involves the addition of coagulants (alum etc) as the quantity to be added is influenced by pH, as is the contact time for chlorine.  
 
The pH and salinity of different sources can vary, even though the sources may be in a close proximity. pH is an important factor where treatment involves the addition of coagulants (alum etc) as the quantity to be added is influenced by pH, as is the contact time for chlorine.  
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| Industrial effluents
 
| In a number of situations industrial or agrochemical pollution can be very marked. As the removal of such contamination requires high technology solutions, it is generally not possible to reliably achieve this during an emergency without use of more expensive and complex treatment plants. A check to ensure that insect larvae and fish life flourish in the water source can provide an indication of quality, e.g. by keeping fish in the header tank''. ''
 
  
Look for signs of agricultural activities, empty chemical sacks etc. to establish if there is a potential for chemical contamination. Rivers and streams are more likely to be “self cleansing” than ponds and lakes.  
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|}
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==Turbidity==
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Turbidity is measured in Nephlometric Turbidity Units (NTU).  A [[Turbidity Tube]] is required for this and can be [http://cartt.4j.lane.edu/ve/globe/globedata/Turbidity.pdf built from scratch]
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If it is found that your water has NTU greater than 5, a [[sedimentation test]] should be conducted.  The results of the sedimentation test will determine if sedimentation alone is adequate and if so, how large a sedimentation basin is required. Also, if sedimentation is ineffective at removing the suspended solids, [[coagulation]] may be necessary.
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Some information can be obtained visually.  If the water is greenish, organic material is present.  If large particles are present, sedimentation is likely to be effective. If the particles are microscopic, coagulation is more likely to be necessary.
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==pH==
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pH levels can be tested with a pool tester and should be between 6.5 and 8.5.  Chlorine reaction times are slowed above a pH of 8. Allum effectiveness is reduced for pH outside of
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==References==
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http://www.oxfam.org.uk/resources/downloads/emerg_manuals/water_treatment.pdf

Revision as of 02:06, 27 March 2009

Jargon

pH - a measure of the acidity of the water. Most fresh water sources have a pH of 6-8. The ocean's pH is ~8.3. A pH above 7 is considered preferable because enteric pathogens prefer a pH below 7.

Enteric Pathogen - diseases which attack the digestive system such as Typhoid and Cholera

Sedimentation - passing the water through a very calm, pond like structure so that the solids will settle out.

Coagulation - using chemicals such as allum to accelerate sedimentation.

Contaminants

Contamination types Contamination Agents Comments
Physical Particles and suspended solids It is common to experience large seasional variance in quantity of particles and suspended solids. When choosing intake location, consideration of the natural features such as flood terracing should be made to optimize the placement of the intake
Biological Faecal waste Faecal contamination is detected via the methods described in Water Quality Field Testing and approprate treatment methods determined based on those results. Common diseases spreat through Faecal contaminataion include cholera and typhoid fever.
Algae Algae can result in bad taste. It is difficult to remove with coagulants and can speed up deterioration of sand filters. Bankside filtration can help to avoid these problems
Chemical Minerals, soil type High salinity (due to the presense of Sodium ions) is treated with expensive procedures such as reverse osmosis and distillation. pH (due to the presence or lack of Hydrogen ions) must also be considered as its levels influence coagulant and chlorine dosages and contact times

The pH and salinity of different sources can vary, even though the sources may be in a close proximity. pH is an important factor where treatment involves the addition of coagulants (alum etc) as the quantity to be added is influenced by pH, as is the contact time for chlorine.

Turbidity

Turbidity is measured in Nephlometric Turbidity Units (NTU). A Turbidity Tube is required for this and can be built from scratch

If it is found that your water has NTU greater than 5, a sedimentation test should be conducted. The results of the sedimentation test will determine if sedimentation alone is adequate and if so, how large a sedimentation basin is required. Also, if sedimentation is ineffective at removing the suspended solids, coagulation may be necessary.

Some information can be obtained visually. If the water is greenish, organic material is present. If large particles are present, sedimentation is likely to be effective. If the particles are microscopic, coagulation is more likely to be necessary.

pH

pH levels can be tested with a pool tester and should be between 6.5 and 8.5. Chlorine reaction times are slowed above a pH of 8. Allum effectiveness is reduced for pH outside of


References

http://www.oxfam.org.uk/resources/downloads/emerg_manuals/water_treatment.pdf