Drinking Water Treatment Systems
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UV Irradiation System
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UV Irradiation Disinfection Systems

THE POWER OF THE SUN
Ultraviolet (UV) rays are part of the light that comes from the sun. The UV spectrum is higher in frequency than visible light and lower than x-rays. As a water treatment technique, UV is known to be an effective disinfectant due to its strong germicidal (inactivating) ability. UV disinfects water containing bacteria and viruses and can be effective against protozoans like, Giardia lamblia cysts or Cryptosporidium oocysts.
UV has been used commercially for many years in the pharmaceutical, cosmetic, beverage, and electronics industries, especially in Europe. In the US, it was used for drinking water disinfection in the early 1900s but was abandoned due to high operating costs, unreliable equipment, and the expanding popularity of disinfection by chlorination.
Because of safety issues associated with the reliance of chlorination and improvement in the UV technology, UV has experienced increased acceptance in both municipal and household systems. There are few large-scale UV water treatment plants in the United States although there are more than 2,000 such plants in Europe.
Principles of UV Disinfection

Figure 1: Cross Section of UV Disinfection Unit
In recent years medium pressure UV lamps that operate at much higher pressures, temperatures and power levels and emit a broad spectrum of higher UV energy between 200 and 320 nm have become commercially available. However, for UV disinfection of drinking water at the household level, the low-pressure lamps and systems are entirely adequate and even preferred to medium pressure lamps and systems. This is because they operate at lower power, lower temperature, and lower cost while being highly effective in disinfecting more than enough water for daily household use. An essential requirement for UV disinfection with lamp systems is an available and reliable source of electricity. While the power requirements of low-pressure mercury UV lamp disinfection systems are modest, they are essential for lamp operation to disinfect water.
Since most microorganisms are affected by
radiation around 260 nm, UV radiation is in the appropriate range for germicidal activity. There are UV lamps that produce
radiation in the range of 185 nm that are effective on microorganisms and will also reduce the total organic carbon (TOC) content
of the water.
For typical UV system, approximately 95 percent of the radiation passes through a
quartz glass sleeve and into the
untreated water. The water is flowing as a thin film over the lamp. The glass sleeve
is designed to keep the lamp at an ideal temperature of approximately 104 °F.
UV Radiation (How it Works)
UV radiation affects microorganisms by altering the DNA in the cells and impeding reproduction. UV treatment does not remove organisms from the water, it merely inactivates them. The effectiveness of this process is related to exposure time and lamp intensity as well as general water quality parameters. The exposure time is reported as "microwatt-seconds per square centimeter" (uwatt-sec/cm^2), and the U.S. Department of Health and Human Services has established a minimum exposure of 16,000 µwatt-sec/cm^2 for UV disinfection systems. Most manufacturers provide a lamp intensity of 30,000-50,000µwatt-sec/cm^2. In general, coliform bacteria, for example, are destroyed at 7,000 µwatt-sec/cm^2.
Since lamp intensity decreases over time with use, lamp replacement and
proper pretreatment are key to the success of UV disinfection. In addition, UV systems should be
equipped with a warning device to alert the owner when lamp intensity falls below the germicidal range.
The following gives the irradiation time required to inactivate completely
various microorganisms under 30,000 ¦µwatt-sec/cm^2 dose of UV 254 nm
Used alone, UV radiation does not improve the taste, odor, or clarity of water. UV light is a very effective disinfectant, although
the disinfection can only occur inside the unit. There is no residual disinfection in the water to inactivate bacteria that may survive
or may be introduced after the water passes by the light source. The percentage of microorganisms destroyed depends on the
intensity of the UV light, the contact time, raw water quality, and proper
maintenance of the equipment. If material builds up on the glass sleeve or
the particle load is high, the light intensity and the effectiveness of treatment are
reduced.
At sufficiently high doses, all waterborne enteric pathogens are inactivated by UV radiation. The general order of microbial resistance (from least to most) and corresponding UV doses for extensive (>99.9%) inactivation are: vegetative bacteria and the protozoan parasites Cryptosporidium parvum and Giardia lamblia at low doses (1-10 mJ/cm2) and enteric viruses and bacterial spores at high doses (30-150 mJ/cm2). Most low-pressure mercury lamp UV disinfection systems can readily achieve UV radiation doses of 50-150 mJ/cm2 in high quality water, and therefore efficiently disinfect essentially all waterborne pathogens.
However, dissolved organic matter, such as natural organic matter, certain inorganic solutes, such as iron, sulfites and nitrites, and suspended matter (particulates or turbidity) will absorb UV radiation or shield microbes from UV radiation, resulting in lower delivered UV doses and reduced microbial disinfection. Another concern about disinfecting microbes with lower doses of UV radiation is the ability of bacteria and other cellular microbes to repair UV-induced damage and restore infectivity, a phenomenon known as reactivation.
UV inactivates microbes primarily by chemically altering nucleic acids. However, the UV-induced chemical lesions can be repaired by cellular enzymatic mechanisms, some of which are independent of light (dark repair) and others of which require visible light (photorepair or photoreactivation). Therefore, achieving optimum UV disinfection of water requires delivering a sufficient UV dose to induce greater levels of nucleic acid damage and thereby overcome or overwhelm DNA repair mechanisms.
Table
1. Estimated
Irradiation Time to
Inactivate Microorganisms at a
Dosage of 30,000 µwatt-sec/cm^2 of UV 254 nm
| Name |
100%
lethal Dosage
(Second) |
Name
|
100%
lethal Dosage
(Second) |
| Bacteria | |||
| Dysentery bacilli |
0.15
|
Micrococcus
Candidus
|
0.4
¨C 1.53
|
| Leptospira SPP |
0.2
|
Salmonella
Paratyphi
|
0.41
|
| Legionella Pneumophila |
0.2
|
Mycobacterium
Tuberculosis
|
0.41
|
| Corynebacterium Diphtheriae |
0.25
|
Streptococcus
Haemolyticus
|
0.45
|
| Shigella Dysenteriae |
0.28
|
Salmonella
Enteritidis
|
0.51
|
| Bacillus Anthracis |
0.3
|
Salmonella
Typhimurium
|
0.53
|
| Clostridium Tetani |
0.33
|
Vibrio
Cholerae
|
0.64
|
| Escherichia coli |
0.36
|
Clostridium
Tetani
|
0.8
|
| Pseudomonas Aeruginosa |
0.37
|
Staphylococcus
Albus
|
1.23
|
| Virus | |||
| Coxsackie Virus A9 |
0.08
|
Echovirus
1
|
0.73
|
| Adenovirus 3 |
0.1
|
Hepatitis
B Virus
|
0.73
|
| Bacteiophage |
0.2
|
Echovirus
11
|
0.75
|
| Influenza |
0.23
|
Poliovirus
1
|
0.8
|
| Rotavirus SA 11 |
0.52
|
Tobacco
Mosaic
|
16
|
| Mould Spores | |||
| Mucor Mucedo |
0.23
¨C 4.67
|
Penicillium
Roqueforti
|
0.87
- 2.93
|
| Oospara Lactis |
0.33
|
Penicillium
Chrysogenum
|
2.0
¨C 3.33
|
| Aspergillus Amstelodami |
0.73
¨C 8.80
|
Aspergillus
Niger
|
6.67
|
| Penicillium Digitatum |
0.87
|
Manure
Fungi
|
8
|
| Algae | |||
| Chlorella Vulgaris |
0.93
|
Protozoa
|
4 -
6.70
|
| Green Algae |
1.22
|
Paramecium
|
7.3
|
| Nematode Eggs |
3.4
|
Blue-Green
Algae
|
10
¨C 40
|
Inactivation Doses for Giardia and
Cryptosporidium
UV dose is a product of UV light intensity and exposure time in seconds (IT), stated in units; mWs/cm2 or mJ/cm2. IT is analogous to the chemical dose or CT (concentration x time). Microbes show a range of sensitivities to UV as shown by the UV data. Cryptosporidium and Giardia are more sensitive to UV than bacteria and viruses are more resistant than bacteria. Similar results have been obtained using low-pressure, medium-pressure and pulsed UV irradiation- Look for a Class A UV disinfection system. UV dose required for a 4log inactivation of selected waterborne pathogens.
Table 2 .
UV Dose 4 log Inactivation
|
Pathogen |
UV dose mJcm/2 |
|
Cryptosporidium parvum oocysts |
<10 |
|
Giardia lamblia cysts |
<10 |
|
Vibrio cholerae |
2.9 |
|
Salmonella typhi |
8.2 |
|
Shigella sonnei |
8.2 |
|
Hepatitis A virus |
30 |
|
Poliovirus Type 1 |
30 |
|
Rotavirus SA11 |
36 |
Source: http://www.trojanuvmax.com
UV Irradiation Pretreatment
|
Turbidity |
5 FTU or 5 NTU |
|
Suspended solids |
< 10 mg/L |
|
Color |
None |
|
Iron |
< 0.3 mg/L |
|
Manganese |
< 0.05 mg/L |
|
pH |
6.5-9.5 |
UV is often the last device in a treatment train (a series of treatment devices), following reverse osmosis, water softening, or
filtration. The UV unit should be located as close as possible to the point-of-use since any part of the plumbing system could be
contaminated with bacteria. It is recommended that the entire plumbing system be disinfected with chlorine prior to initial use of
a UV system.
1. Obtain information about your water source.
2. Get your water tested - At least
Annually
3. Determine which problems are associated with infrastructure deficiencies,
i.e., cracked casing, no cap, improper seal, poor surface drainage, etc.
Make the necessary repairs and improvements to the system.
4. Install the necessary water
treatment systems. I have provided some
online links for water treatment systems, but I always recommend a preliminary water test.
Resources
http://www.uvdisinfections.com/tech/
For more information on common water treatment problems, please visit the
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