Chlorine (Sodium Hypochlorite)
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What is a Sodium hypochlorite?
Chlorine began to be widely used as a disinfectant in the early 1900’s. It revolutionized drinking water treatment and dramatically reduced the incidence of waterborne diseases. Chlorine remains the most widely used chemical for water disinfection in the United States.
Sodium hypochlorite is one form of chlorine used for water disinfection. It can be manufactured in most locations since it can be obtained through the electrolysis of salt water. Bottles can be purchased for household water treatment from many manufacturers in various sizes. Chlorine concentrations range from 0.5 to 10% and each product should have its own instructions for correct dosing of contaminated water. Liquid household bleach also contains sodium hypochlorite, and is widely available.
How Does It Remove Contamination?
Chlorine forms hydrochloric acid when added to water which reacts through oxidization with micro-organisms and kills them.
Three things can happen when chlorine is added to water:
- Some chlorine reacts through oxidization with organic matter and the pathogens in the water and kills them. This portion is called consumed chlorine.
- Some chlorine reacts with other organic matter and forms new chlorine compounds. This portion is called combined chlorine.
- Excess chlorine that is not consumed or combined remains in the water. This portion is called free residual chlorine (FRC). The FRC helps prevent recontamination of the treated water.
Operation
There are several different brands of chlorine products that have been manufactured specifically for household water treatment. Each product should have its own instructions for correct dosing and contact time.
Liquid household bleach products are also commonly used to disinfect drinking water. The strength of the product must be known to calculate how much bleach is needed to disinfect a given amount of water.
The effectiveness of chlorine is affected by turbidity, organic matter, temperature and pH.
For high turbidity levels, the water should first be strained through a cloth or sedimented before adding chlorine. These processes will remove some of the suspended particles and improve the reaction between the chlorine and pathogens.
Treatment efficiency
| Bacteria 1 | Viruses 2 | Protozoa3 | Helminths | |
|---|---|---|---|---|
| Resistance to Chlorine | low4 | moderate4 | high4 | not available |
Toxoplasma oocysts and cryptosporidium oocysts are highly resistant to chlorine disinfection 4). Chlorine alone should not be expected to inactivate these pathogens in drinking water.
Operating criteria
- Flow rate: Not applicable
- Batch volume: Unlimited
- Daily water supply: Unlimited
The manufacturer’s instructions for specific sodium hypochlorite products need to be followed. The required dose and contact time varies with water quality (e.g. turbidity, pH, temperature).
Use a 30 minute minimum contact time. If the pH is above 7.5, a higher FRC concentration of 0.6 mg/litre should be used and the contact time should be extended to 1 hour.
The contact time should be increased to 1 hour when the temperature is between 10˚ and 18˚C. It should be increased to two or more hours when the temperature falls below 10˚C.
Robustness
Free residual chlorine protects against recontamination. Most users cannot determine the dosing quantity themselves; proper use requires simple instructions from the manufacturer. Users often use less than the recommended dose to save money.
Chlorine requires a supply chain, market availability and regular purchase. It also requires quality control process to ensure product reliability. Sourcing suitable plastic containers to manufacture chlorine solutions can sometimes be a challenge.
Estimated lifespan
Chlorine deteriorates over time, especially in liquid form. Liquid chlorine products should be used within 3 months of being manufactured.
Manufacturing requirements
Worldwide producers
There are many producers of chlorine solutions all around the world.
Local production
Can be made locally using salt water solution and electrolysis equipment.
Materials and facilities
- Generator with electrolysis equipment
- Plastic bottles and labelling equipment
- Salt
- Water
Fabrication Facilities
Workshop space is required for chlorine production and bottling. Good ventilation required in the workshop space.
Labour
Trained workers needed to produce and test the sodium hypochlorite.
Hazards
Chlorine fumes and contact with skin are hazardous. Skin and eye protection should be used when handling chlorine solutions. Work should be conducted in a well ventilated area or in the open air.
Maintenance requirements
Chlorine should be stored in a cool, dark place in a closed container.
Cost
| Captial Cost | Operation Cost | Replacement Cost | Estimated 5 years Cost | Cost/liter treated |
|---|---|---|---|---|
| US$ 0 | US$ 3/year | US$ 0 | US$ 15 | US$ ~0.02 |
Note: Program, transportation and education costs are not included.
Other
Some users complain about the taste and odour that chlorine may cause in water. Chlorine reacts with organic matter naturally present in water to form by-products such as trihalomethanes (THMs), which are potentially cancer-causing. Lantagne et al. (2008)5 indicate that THM levels produced during household chlorination may fall below World Health Organization (WHO) guideline values.
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External links
Acknowledgements
This article is based on a factsheet from Centre for Affordable Water and Sanitation Technology (CAWST), which is gratefully acknowledged.
Footnotes
- ↑ Bacteria include Burkholderia pseudomallei, Campylobacter jejuni, Escherichia coli, Salmonella typhi, Shigella dysenteriae, Shigella sonnei, Vibrio cholerae, Yersinia enterocolitica.
- ↑ Viruses include enteroviruses, adenoviruses, noroviruses, rotavirus.
- ↑ Protozoa includeEntamoeba histolytica, Giardia lamblia, Toxoplasma gondii, Cryptosporidium parvum.
- ↑ 4.0 4.1 4.2 4.3 CDC (2007)
- ↑ Lantagne et al. (2008)
References
- Centers for Disease Control and Prevention (CDC 2007). Effect of Chlorination on Inactivating Selected Pathogens. Available at:www.cdc.gov/safewater/about_pages/chlorinationtable.htm
- Lantagne, D.S., Blount, B. C., Cardinali, F., and R. Quick (2008). Disinfection by-product formation and mitigation strategies in point-of-use chlorination of turbid and non-turbid waters in western Kenya. Journal of Water and Health, 06.1, 2008.
- Luby, S., Agboatwalla, M., Razz, A. and J. Sobel (2001). A Low-Cost Intervention for Cleaner Drinking Water in Karachi, Pakistan. International Journal of Infectious Diseases; 5(3): 144-150.