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MtBE in Drinking Water
What is MtBE?
MtBE is the abbreviation for the compound methyl tertiary butyl ether.
This compound is a colorless liquid at room temperature and pressure. MtBE
is a manmade material and thus its presence in water would indicate that
manmade contamination exists in the recharge area of the well. MtBE degrades
very slowly, is highly soluble in water, has a very small molecular structure
and very low taste and odor thresholds.
Where Is MtBE Used?
MtBE increases the octane rating of gasoline and reduces air pollution
by also increasing the gasoline’s oxygen content. It was first introduced
into gasoline in the early 1980s as lead was removed. The 1990 Clean Air
Act Amendments required the reformulation of some gasoline. This requirement
prompted an increase in the percentage of MtBE used in gasoline in the
New England area currently to approximately 11 percent. There are few other
uses of MtBE in normal commerce or industry.
What are the Health Effects?
The U.S. Environmental Protection Agency (EPA) has not set a formal
health-based drinking water standard for MtBE in the federal Safe Drinking
Water Act (SDWA). The N.H. Department of Health and Human Services, Bureau
of Health Risk Assessment (BHRA) has recently developed a health-based
drinking water standard for MtBE of 13 micrograms per liter (ug/L) for
community public water systems. DES plans to adopt that value as a maximum
contaminant level (MCL) in New Hampshire’s Safe Drinking Water Act Program
during the spring of 2000.
Studies with animals suggest drinking water with high levels of MtBE
may cause stomach irritation, liver and kidney damage, and nervous system
effects. An increased amount of liver and kidney cancer was found in rats
and mice breathing high levels of MtBE. Because of the animal studies on
MtBE, the BHRA considers MtBE a possible human carcinogen. A health information
summary for MtBE can be obtained by calling BHRA at 271-4664. It can also
be viewed or downloaded from their
web
site .
The EPA’s public water supply program has recently made a nonhealth-based
recommendation to limit MtBE in drinking water to 20-40 ug/L. This recommendation
is based on preventing taste and odor complaints. MtBE has a very low odor
threshold at 20 ug/L, while the threshold for taste is 40 ug/L.
Assistance from DES
If you have MtBE in your water supply, DES may be able to provide assistance
to you in two areas.
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DES may assist in identifying the origin of the contamination. Please call
the DES Oil Remediation and Compliance Bureau at 271-3644 concerning this
assistance.
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New Hampshire has special funds which may be able to provide financial
assistance to abate pollution from hydrocarbon contaminants, such as from
heating oil fuel or gasoline that includes MtBE. Information regarding
these funds is contained in the Petroleum Reimbursement Funds information
packet. These funds are also administered by the DES Oil Remediation and
Compliance Bureau.
How Can MtBE be Removed from Drinking Water?
Unlike many other constituents associated with hydrocarbons, MtBE is
difficult to remove from water. There are generally three treatment methods
that have been shown to be effective in removing general hydrocarbon organics
from drinking water. They are aeration, adsorption using activated carbon,
and oxidation. These treatment methods are discussed below.
If the concentration of the contaminants is high, two treatment units
(typically using different methods) are often installed. The first device
is used to remove the “heavy” contaminant load while the second provides
a “polishing step” to assure full removal of the contaminant(s) and to
address “breakthrough.” Aeration is often the first method used while activated
carbon is often used as the polishing step.
See fact sheet WD-WSEB-2-5 for information
concerning purchasing and installation recommendations for water treatment
devices. A treatment system should not be purchased until sufficient water
quality testing has been done to identify all the following:
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The short term variability of the contaminant(s).
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Whether the contaminant concentrations are rising or falling over the long
term.
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What other contaminants are in your general area and how many are predicted
to affect your well in the future.
If contaminants are present in a pure product state in the well,
a recovery method is also necessary. This will reduce the size of the water
treatment equipment needed.
Activated Carbon Treatment: Advantages and Disadvantages
Activated carbon has enormous surface area within each granule. One
pound of activated carbon has a surface area greater than the size of a
football field. Activated carbon is a material that attracts many types
of organic contaminants to its surface. Once the removal capacity of the
carbon is used up, then it may be returned to the manufacturer for rejuvenation
(for very large users) or can be disposed of appropriately for smaller
situations.
If activated carbon is used, the radon and mineral radioactivity concentrations
of the water should be determined. Activated carbon concentrates radioactivity,
potentially creating a low level radionuclide waste and possible source
of increased radiation within the home. Activated carbon can also foster
the growth of bacteria by concentrating other organics (such as food sources)
on its surface. A final concern with activated carbon is the possible release
of contaminants after they have been initially adsorbed. This action is
known as desorption or dumping. This could occur if other ambient water
quality characteristics change.
To address breakthrough and desorption, the overall amount of activated
carbon could be divided into two treatment tanks and the two devices installed
in “series.” In such an arrangement any breakthrough from the first unit
can be adsorbed by the newer carbon in the second unit. The advantage of
activated carbon treatment compared to other methods is that the water
does not need to be repressurized and is less likely to become contaminated
by dust and other airborne contaminants. The disadvantage is that carbon
attracts organic matter from the water and thus typically supports an elevated
level of bacteria on its surface.
Aeration Treatment: Advantages and Disadvantages
Aeration treatment consists of passing large amounts of air through
the contaminated water. The efficiency of the device is improved by breaking
up the bulk of the water into many small droplets. The goal is to allow
the contaminants to volatilize into the air. When aeration is used, two
operational problems are possible:
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If there are elevated levels of iron or manganese in the water, rusty precipitate
staining of fixtures and clothing is likely. Iron/manganese pretreatment
may be necessary.
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Bacterial slime may grow in aerators requiring continuous or periodic chlorination.
The advantage of aeration is that there is no disposal or regeneration
of the treatment media necessary.
Other Possible Treatments of MtBE
New methodologies still in the trial or experimental stage include:
Oxidation Treatment: Advantages and Disadvantages. Certain organic
contaminants will chemically react with oxygen and oxygen-like compounds.
After the oxidation treatment, the resultant compounds may be fully neutralized,
may have a lower level of hazard, or be more amenable to treatment by other
means. Further treatment may still be necessary, however. Oxidizing chemicals
could include potassium permanganate, (KMnO4), hydrogen peroxide (H2O2),
ozone (O3) and sodium hypochlorite (NaOCl).
UV Destruction. One newer treatment technique, which is now being
evaluated, is the use of ultraviolet radiation to break down MtBE. This
treatment would then be followed by either hydrogen peroxide or ozone to
oxidize the by-products of the UV breakdown. Presently, there are few instances
of this treatment and thus costs and operational effectiveness are still
being determined.
Monitoring Program After Installation of a Treatment System
Periodic laboratory testing should be done of both the raw and finished
water to determine treatment effectiveness. The frequency of this monitoring
would be determined based on variability and duration of the past sampling
record and other site specific conditions. Where activated carbon is used,
the carbon will lose its removal capacity and will need to be replaced
in time. A monitoring program will be needed to predict the expected longevity
of each new carbon recharge.
Laboratory Testing
The DES Laboratory and many commercial laboratories can test for MtBE.
The DES cost is $100 for each sample. This test provides information for
all of the volatile industrial solvents and hydrocarbons regulated under
the Safe Drinking Water Act. MtBE can vary in concentration, thus two or
more samples should be taken before judging the average MtBE concentration
in a well. The DES Laboratory can be contacted at 271-3445 or 3446.
For More Information
For more information please call DES’s Water Supply Engineering Bureau
at 271-3139. We would appreciate your comments concerning this fact sheet
and your experiences in treating for MtBE. Drinking water fact sheets are
available through the DES web site at: www.des.state.nh.us/wseb,
then select “wseb fact sheets.”
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