On Tap Magazine - Fall 2003

From: Subject: On Tap Magazine - Fall 2003 Date: Thu, 28 Feb 2008 08:16:07 -0500 MIME-Version: 1.0 Content-Type: multipart/related; type="text/html"; boundary="----=_NextPart_000_003B_01C879E2.2B26C4F0" X-MimeOLE: Produced By Microsoft MimeOLE V6.00.2900.3198 This is a multi-part message in MIME format. ------=_NextPart_000_003B_01C879E2.2B26C4F0 Content-Type: text/html; charset="iso-8859-1" Content-Transfer-Encoding: quoted-printable Content-Location: http://www.nesc.wvu.edu/ndwc/articles/OT/FA03/well.html On Tap Magazine - Fall 2003 =

National Drinking Water Clearinghouse
West = Virginia=20 University
P.O. Box 6064
Morgantown, WV=20
26506-6064

How = well=20 is your well?

By=20 Larry Rader =95 NDWC Environmental=20 Consultant

When it comes to well water, most folks think their = water comes=20 from the ground pure and pristine. But those of us who have operated=20 groundwater treatment plants with any or all of the following=20 contaminants=97iron, manganese, carbon dioxide, arsenic, radon, iron = and sulphur=20 bacteria=97tell a different story.

Do I have carbon=20 dioxide?
Carbon dioxide (CO2) may = seem to be=20 an odd place to start an article on groundwater treatment, but, in my = area at=20 least, it contributes to more treatment problems than any other = contaminant.=20 CO2 reduces pH, which, in turn, contributes to a = wide=20 range of treatment difficulties.

Throughout the Lead and Copper = Rule,=20 we learned that decreased pH contributes to
corrosion problems and = the=20 leaching of lead and copper into customers=92 water. Also, the lower = the pH, the=20 more time it takes to oxidize metals, like iron, in the treatment=20 process.

Carbon dioxide tends to be most prevalent in areas = with large=20 underground deposits of carbon, such as coal, petroleum, or brine. = Companies,=20 including Hach and LaMotte, sell CO2 test kits that are quick and = accurate for=20 onsite testing, or an operator may choose to use an approved lab. = Using a pH=20 meter, you can detect carbon dioxide=92s presence, if not the = concentration. To=20 check for CO2, grab a sample of raw water and = quickly=20 check the pH. Then pour the sample back and forth between two beakers = several=20 times and check the pH again. If the pH has gone up, the chances are = that your=20 water is the proud owner of CO2.

The treatment = for=20 CO2?
Think a bit about pouring the raw water sample back and = forth=20 between the two beakers: what were you doing? Aerating.

CO2 vaporizes easily when aerated. This is a lesson that = those=20 working in West Virginia learned early on. A pH level in the fours is = not=20 uncommon here. Consequently, almost all groundwater treatment plants = in this=20 state come equipped with an aerator. It may be as simple as coke trays = or as=20 state of the art as vortex aerators, but they are there releasing the = CO2, hydrogen sulfide (H2S), = radon, and other=20 contaminants, making the water safer and easier to treat. =

There are=20 states that have decided aerating water turns it into surface water,=20 therefore, requiring full treatment. In my opinion this is foolish and = wrong-headed. These same states allow chemical treatment using soda = ash up to=20 300 milligrams per liter (mg/L). Using that much soda ash is = expensive, and=20 it=92s not even very effective.

Another design requirement = often used as=20 an argument against aeration is =93double pumping.=94 Aeration usually = requires a=20 basin or tank following the aerator to allow oxygen to release prior = to=20 filtration or pumping into the distribution system. A double-pumping = design=20 requires a second pump to move the aerated water through the filter = and into=20 the distribution system.

There are degassing units, which = allow=20 CO2=20 removal without the need for double pumping. However, the head loss = through=20 the unit makes single stage pumping practical in limited situations=20 only.

A perfect example of the effectiveness of aeration is the = water=20 treatment facility in Mt. Hope, West Virginia. The Mt. Hope plant was = built=20 just as the Lead and Copper Rule was getting into full swing. The raw = water=20 source was an artesian spring emanating from an abandoned coalmine. = The Mt.=20 Hope=92s water system operator decided the raw pH (6.3) needed to be = raised to=20 7.5 to make the water non-corrosive.
Because the plant was new and = there=20 was no money left in the budget for an aerator, the system=92s = management=20 decided to use soda ash to chemically adjust the pH. For more than ten = years=20 the operators fed 400 pounds of soda ash each day to adjust the pH of = 350,000=20 gallons of treated water.

Finally, using the ingenuity all = operators=20 gain from years of making poor designs work, the operators at Mt. Hope = constructed their own aerator. The pH increased to 7.5, and they were = able to=20 stop feeding soda ash altogether. The savings for the small town = amounted to=20 approximately $1,000 per month.

How to Shock Chlorinate a = Well

Chlorine=20 is highly toxic to bacteria at concentrations of 200 mg/L and = greater.=20 This procedure uses hypochlorite containing about 65 percent = calcium=20 hypochlorite or non-scented household bleach containing about = 5.25=20 percent sodium hypochlorite.

Mix a solution using five = gallons=20 of water in a clean, non-metallic container with the appropriate = amount=20 of either hypochlorite or bleach required for 10 feet of water = depth.=20

Iron Is = Common
Iron is the most common mineral in the Earth=92s = crust and,=20 therefore, the most common contaminant found in well water. Although = iron is a=20 secondary contaminant, its secondary maximum contaminant level is 0.3 = mg/L.=20 Together with manganese, they make up the terrible twins of = groundwater=20 treatment. Customers can drink water containing any number of harmful=20 contaminants without notice, but one washer load of white clothes = covered with=20 brown iron stains will cause most operators to lock the doors and take = the=20 phone off the hook.

Considering the problems iron can cause, = it is=20 actually very easy to control=97just oxidize, then filter. Iron is = fairly easy=20 to oxidize, changing ferrous (soluble) iron into the ferric state, = which are=20 particles of rust. If you have an aerator, it will introduce oxygen = and=20 possibly raise the pH that begins the process. Chlorine or potassium=20 permanganate can then be applied to finish turning soluble iron into=20 particles, which filtration easily removes.

When removing = oxidized iron=20 the filter must have several inches of anthracite capping the filter = sand or=20 greensand. Ferrous iron may be sequestered in concentrations of less = than 1.0=20 mg/L. Ferric or oxidized iron may not be sequestered in any = concentration.=20 Removal is always the best practice when = possible.

Iron=92s=20 Terrible Twin
Manganese is the terrible twin of = groundwater=20 treatment and usually is found keeping company with its sibling, iron. = The=20 secondary maximum contaminant level for manganese is 0.05 mg/L, six = times less=20 than iron. Several years ago a popular hair tonic for men advertised = =93A little=20 dab will do ya,=94 and so it is with manganese. Even in concentrations = less than=20 0.05, you can have a cumulative effect on the insides of pipes and = fittings=20 that will show up in customers=92 homes following line breaks, use of = fire=20 hydrants, or any other time the line flow has been drastically = altered. It=20 reaches the customers=92 homes either as black particles or black=20 staining.

Although more difficult than iron to oxidize, in my = opinion,=20 the best treatment is to bring the soluble manganese into a properly = operated=20 and maintained greensand filter or one of the many look-alike = manganese oxide=20 coated media. If iron is present, and it usually is, the filter should = be=20 capped with anthracite, chlorine applied to oxidize the iron that will = be=20 trapped in the anthracite, and then allow the greensand to remove the=20 manganese. Soluble manganese may be sequestered in small = concentrations;=20 insoluble manganese cannot be sequestered. (For more in-depth answers=20 concerning iron and manganese removal, see =93How to Operate and = Maintain=20 Manganese Greensand Treatment Units,=94 in the On Tap Winter=20 2003.)

Radon Can Be Aerated
Radon is a naturally = occurring=20 radioactive gas formed when uranium breaks down in the soil. Breathing = air=20 that contains radon can cause radioactive particles to become trapped = in your=20 lungs and lead to lung cancer. Radon is the second leading cause of = lung=20 cancer in the U.S. each year, second only to cigarette smoking. Most = radon=20 enters the home, and therefore your lungs, by seeping from the soil = under and=20 around your house. However, groundwater can also contain radon and = contribute=20 to the problem.

Although there are health issues from drinking = water=20 containing radon, most concerns center on radon in the air. Radon is = released=20 into the air in the customer=92s home from the shower and other = sources of=20 running water. What action is taking place when you turn on the shower = and=20 radon is released into the air? That=92s right, aeration! According to = the=20 Federal Register Vol. 64, No. 211, the best available technology for = the=20 removal of radon in groundwater is =93high-performance=94 aeration. = For individual=20 home wells, granular activated carbon (GAC) filters are effective = providing=20 all water used in the home passes through the GAC.

What = do iron=20 andsulphur bacteria do to a well?
Although neither iron = bacteria=20 nor sulphur bacteria pose a particular health hazard, they can, in = fact,=20 render a well field useless. Iron bacteria are generally the more = common of=20 the two simply because of the abundance of iron in groundwater. They = are=20 usually discovered when a well begins to lose efficiency. The well = pump=20 ispulled only to find the screen is covered with a foul smelling brown = slime.=20 By the time they are discovered, you are quite likely in big trouble.=20

Iron bacteria can grow extremely fast by combining iron in = groundwater=20 with oxygen. Iron bacteria cannot only reduce a good-producing well to = a=20 trickle, but the biofilm can also mask the presence of other more = harmful=20 bacteria, such as fecal coliforms. They are usually found in more = shallow=20 aquifers and the best protection is to make certain the well is = properly cased=20 and employs approved wellhead protection.

Sulphur bacteria are = divided=20 into two basic categories: 1) Sulfur-oxidizing bacteria converts = sulfide into=20 sulfate and produces a dark brown slime that plugs well screens, = plumbing, and=20 pumps, similar to iron bacteria; 2) Sulfur-reducing bacteria (SRBs) on = the=20 other hand, live in oxygen-deficient environments. SRBs produce = hydrogen=20 sulfide gas during the process of breaking down sulfur compounds. SRBs = are the=20 morecommon
of the two sulfur bacteria, and the hydrogen sulfide = gas they=20 produce is extremely
corrosive.

Do I have iron or = sulphur=20 bacteria?
A series of tests called BART (Biological = Activity=20 Reaction Tests) are available. BART kits are easy to use and simple to = understand. They consist of a plastic vial containing a ball coated = with=20 appropriate chemicals. A sample of raw water is poured into the vial, = which is=20 then tightly capped.

Color changes will begin to appear that = correspond=20 to a color chart provided with each test. Extremely or very aggressive = levels=20 of the appropriate bacteria will provide color changes within 12 to 24 = hours.=20 Moderately aggressive to background levels may take from two to 32 = days to=20 reach the correct color change. The charts provided with each test = also show=20 various other color changes along with the explanation. I have used = BARTS=20 almost from the time they became available. They can be found in most = any=20 water treatment supply catalog and cover a wide range of different = bacteria.=20

The method I used before BARTS was also simple. The test was = only for=20 iron-related bacteria and consisted of the following equipment: One = small jar=20 that can be tightly sealed (my preference was a baby food jar) and a = bright=20 new nail that would easily fit into the jar. The jar and cap I = sterilized with=20 boiling water, were placed upside down on a clean paper towel, and = allowed to=20 cool. The shiny nail is cleaned with alcohol to remove any traces of = oil. The=20 nail was placed in the baby food jar, which was then filled with raw = water and=20 tightly capped.

I put the jar was on a shelf and checked for = brown=20 hair every few days, which indicates the presence of iron bacteria. If = the raw=20 water did contain iron bacteria, it immediately began looking for a = food=20 source and discovered the nail. In a few weeks, if the sample = contained iron=20 bacteria, strings of brown hair (slimy by-product) could be detected = rising=20 from the nail. You won=92t find this in the American Water Works = Association=92s=20 =93Standard Methods,=94 but it was all I had = available.

If I have=20 iron or sulphur bacteria, what can I do?
Because these = bacteria=20 are extremely difficult to completely destroy, the best defense is a = proactive=20 offense. Wells should be monitored frequently, in my opinion every six = months,=20 using something like the BART tests.

The other part of that = offense is=20 also extremely important. Anything=97and I do mean anything=97that = goes into the=20 well must be disinfected with a 250 mg/L solution of chlorine. This = includes=20 pumps, electric cables, pipe or hose, portable water level indicators, = or=20 anything else that enters the well. If you discover bacteria early, = shock=20 chlorination may work. (See the water well disinfection = table.)

If the=20 bacteria are advanced, ask your well driller about other options. But=20 remember, it is best to catch the problem early, or better yet, = prevent it=20 from happening at all.
Hydrogen Sulfide Is an SRB Byproduct = Hydrogen=20 sulfide (H2S) is not only a byproduct of = SRB; it can=20 also exist naturally in the ground. A rotten egg odor that becomes = stronger as=20 the levels increase announces its presence. Although H2S = can be toxic,=20 the odor at those levels should prevent anyone from drinking the = water. The=20 major concern with H2S is its corrosiveness to metals such as copper, = iron,=20 brass, and steel. There are kits available to check H2S = concentrations; however, testing must be preformed onsite because it = vaporizes=20 very quickly. If samples are sent to a laboratory, ask for directions = to=20 stabilize the sample.

What=92s the treatment for=20 H2S?
Because it readily = vaporizes,=20 aeration can remove high levels of H2S. Other methods of oxidation such as chlorination, = ozonation, and=20 potassium permanganate treatment also are effective if there is at = least=20 twenty minutes of contact time. Manganese greensand filters can remove = H2S up to 6 = mg/L, and=20 activated carbon filters work well through the process of adsorption. = If your=20 system contains H2S, it may = be necessary=20 to retrofit hot water heaters by replacing the magnesium corrosion = control=20 rods with rods made of aluminum.

Although I am a believer in = aeration=20 for most, if not all, groundwater systems, there are cautions. H2S, = for=20 instance, can be flammable when = vaporized.

It can also be = toxic when high=20 levels of the vaporized gas are breathed. Other volatiles such as = radon would=20 be hazardous if contained inside a building, for instance, following = aeration.=20 Make certain the vaporized gasses are vented to the outside air, and = you have=20 checked with the agency that regulates air quality in your=20 state.

About the Author: Larry Rader has more = than 25=20 years in the water industry. If you have a question for Rader, = he can be=20 reached by e-mail at lrader@meer.net.=20

References:
Nebraska = Health and Human=20 Services System. 2003. =93Iron and Sulfur Bacteria in Water = Supplies.=94 Water=20 Well Disinfection. http://www.hhs.state.ne.us/.

U.S.=20 Geological Survey. 2003. =93Bacteria and Their Effects on Groundwater = Quality.=94=20 http://www.usgs.gov/.

Ameri= can=20 Groundwater Trust. 2003. =93Bacteria and Water Wells.=94 www.agwt.org/gwinfo.htm.=

Well=20 Owner.Org. 2003. =93Iron Biofouling/Iron Bacteria.=94 Hydrogen = Sulfide, What=20 You Need to Know. WellOwner.org.

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