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Radionuclides in Drinking Water

Radionuclides in Drinking Water: a Problem That Must Be Dealt With


Strategic Planning: Pathway to Small Water System Compliance

Process Factors Affecting Proper Aeration Basin Control

Radionuclides in Drinking Water: a Problem That Must Be Dealt With

After 150 Years Minnesota City Will See End of Major Flooding Problems

Part 1: Shakeout Predicted in Trenchless Technology Industry with Few Winners,
Many Losers

Over the Net with Ian Lisk: The Prince Didn’t Get it Right, and Neither
Did Marie Antoinette

6/2/2000 The potential for radioactive substances to present problems exists
throughout the United States as releases from medical facilities or nuclear
power plants may wind up in drinking water. Because of their potential health
effects and widespread occurrence, natural radionuclides—including radon,
radium, and uranium—cause much concern.

Contents Where do radionuclides occur, and what are the public health risks?
What water treatment process can remove radionuclides? Sources for more information

Radionuclide contamination of drinking water is a significant, emerging issue.
Until recently, decades manmade radioactivity in drinking water has not been
a major problem. Natural sources have been the primary cause of this type of
contamination. However, the potential for these radioactive substances to present
problems exists throughout the country as releases from medical facilities or
nuclear power plants may wind up in drinking water. Because of their potential
health effects and widespread occurrence, natural radionuclides—including
radon, radium, and uranium—cause much concern.

Where do radionuclides occur, and what are the public health risks? (top) Radionuclides
occur naturally as trace elements in rocks and soils as a consequence of the
"radioactive decay" of uranium-238 (U-238) and thorium-232 (Th-232).
This decay occurs because radioactive atoms have an excess of energy. When these
atoms release or transfer their extra energy, the phenomenon is known as decay.
The energy they release is called ionizing radiation, which may be in the form
of alpha particles, beta particles, or gamma rays. This energy is transmitted
through space or some other medium in waves (e.g., x-rays or gamma rays) or
particles (e.g., electrons or neutrons) and is capable of either directly or
indirectly removing electrons from atoms, thereby creating ions, which are electrically
charged atoms.

Radon-222, radium-226, radium-228, uranium-238, and uranium-234 are ions of
the U-238 and Th-232 decay series. They are the most common radionuclides found
in groundwater. Other naturally occurring radionuclides tend to be environmentally
immobile or have short half-lives, meaning they are far less likely to be found
in significant amounts in groundwater.

When ionizing radiation strikes a living organism’s cells, it may injure
these cells. If radiation affects a significant number of them, the organism
may eventually develop cancer. At extremely high doses it may even die.

Radon is a naturally occurring radioactive gas that emits ionizing radiation.
National and international scientific organizations have concluded that radon
causes lung cancer in humans. Ingesting drinking water that contains radon also
presents a risk of internal organ cancers, primarily stomach cancer. The U.S.
Environmental Protection Agency (EPA) and the U.S. Surgeon General recommend
testing indoor air for radon in all homes and apartments located below the third
floor. Persons who smoke and whose homes exhibit high indoor radon levels are
at especially high risk level and they could develop lung cancer.

Tap water only emits approximately 1% to 2% of the radon found in indoor air.
However, breathing radon from this source increases the risk of lung cancer
over the course of a lifetime.

Radium-226 and radium-228 are natural groundwater contaminants that usually
occur in trace quantities. At high exposure levels, radium-226 and radium-228
can cause bone cancer in humans and are believed to cause stomach, lung, and
other cancers as well.

Uranium is a naturally occurring radioactive contaminant found in both groundwater
and surface water. At high exposure levels, uranium is believed to cause bone
cancer and other cancers in humans. EPA also believes that uranium can be toxic
to the kidneys.

Gross Alpha emitters occur naturally as radioactive contaminants, but several
come from manmade sources. They may occur in either groundwater or surface water.
At high exposure levels, alpha emitters are believed to cause cancer in humans.

Beta and photon emitters are primarily manmade radioactive contaminants associated
with operating nuclear power plants, facilities that use radioactive material
for research or manufacturing, or facilities that dispose of radioactive material.
Some beta emitters occur naturally. Beta and photon emitters primarily occur
in surface water. At high exposure levels, beta and photon emitters are believed
to cause cancer in humans.

The EPA rules covering the various aspects of the radionuclide issue are shown
in the table. Acronyms used in the table are explained below in the section
reviewing treatment options for removal of radionuclides from drinking water.


PicoCuries per liter (pCi/L) is an activity measurement of radioactive decay
(1 pCi/L = 22 disintigrations per min); micrograms per liter (µg/L) is
a mass measurement; mrem is measurement of effective radiation dose to organs.
Except as noted, BAT for the purpose of issuing variances is the same as BAT
for compliance. 20 µg/L is based on kidney toxicity. 20 µg/L is
the equivalent of 30 pCi/L. Coagulation/Filtration and Lime Softening are not
BAT for small systems (those with fewer than 500 connections) for the purpose
of granting variances. Note: EPA recognizes that most radionuclides emit more
than one type of radiation as they decay. The lists of compounds labeled "alpha"
or "beta" emitters identify the predominant decay mode.

Note: In this document the unit mrem ede/yr refers to the dose ingested over
50 years at the rate of 2 liters of drinking water per day.

Source: U.S. Environmental Protection Agency


What water treatment process can remove radionuclides? (top) Whether or not
a particular treatment technology effectively removes radionuclides from drinking
water depends on the contaminant’s chemical and physical characteristics
as well as the water system’s characteristics (e.g., the source water
quality and the water system size). Other considerations include cost, service
life and co-treatment compatibility.

The following treatment process systems have been evaluated for their ability
to remove radionuclides from water:

ion exchange (IE) point-of-use IE point-of-entry IE reverse osmosis (RO) point-of-use
RO; point-of-entry RO lime softening (LS) greensand filtration co-precipitation
with barium sulfate selective sorbents electrodialysis/electrodialysis reversal
(ED/EDR) preformed hydrous manganese oxides (HMOs) Ion Exchange: Small systems
may readily use IE treatment, which removes approximately 90% of radionuclides.
The effluent must be regularly monitored and the IE resin must be frequently
regenerated to ensure that breakthrough does not occur. Ion exchange units may
be controlled automatically, requiring less of the operator’s time. However,
it is necessary to employ a skilled operator to determine when regeneration
is needed and to trouble-shoot. Also, disposal of concentrated radionuclides
can be expensive.

The ion exchange process generates wastes that include rinse and backwash water,
and the IE resin. The rinse and backwash liquid waste includes brine, radium,
and any other contaminants that the process removes.

Cation Exchange: A cation is a positively charged ion. Cation exchange resins
exchange like-charged ions equally with protons—sodium ions (Na+), or
in sodium-restriction cases, potassium ions (K+)—to remove undesirable
cations from water. Cation exchange is often used to remove calcium and magnesium
cations, and to treat hard water.

The quantity of waste in the rinse and backwash water that the cation exchange
process typically generates ranges between 2% and 10% of the treated water.

Lime Softening: This very common process used treat hard water also can be
applied to remove radium from drinking water with 80% to 95% efficiency. Also,
adding lime or lime-soda ash to water increases the pH of the water and induces
calcium carbonate and magnesium hydroxide precipitation.

Lime softening generates wastes that include lime sludge, filter backwash liquid
and sludge, and the supernatant liquid from the sludge.

Reverse Osmosis: This system can remove many inorganic contaminants very effectively,
including heavy metals and radionuclides such as radium and uranium. RO can
remove 87% to 98% of radium from drinking water. Similar elimination can be
achieved for alpha particle activity and total beta and photon emitter activity.

When an RO system is being used to remove radionuclides, its performance depends
on a number of factors. These include pH, turbidity, iron/manganese concentration
in the raw water, and the type of membrane employed. Pretreatment of the water
fed to an RO system is required and the process chosen to accomplish that depends
on the quality and quantity of the source water. Existing treatment plants may
already provide much of the required pretreatment—for example, coagulation/filtration
of highly turbid surface water or iron removal for a well water source. Reverse
osmosis can be a cost-effective solution for small systems.


National Research Concil (NRC). "Safe Water form Every Tap: Improving
Water Service to Small Coummunities." National Academy Press. Washington,
DC. 1997. Limitations Footnotes a. The regeneration solution contains high concentrations
of the contaminant ions. Disposal options should be carefully considered before
choosing this technology. b. When POU devices are used for compliance, programs
for long-term operaion, maintenance, and monitoing must be provided by the water
utility to ensure proper performance. c. Reject water disposal options should
be carefully considered before choosing this technology. d. The combination
of variable source water quality and the complexity of the chemistry involved
in lime softening may make this technology too complex for small surface water
systems. e. Removal efficiencies can vary depending on water quality. f. This
technology may be very limited in application to small systems. Since the process
requires static mixing, detention basins, and filtration; it is most applicable
to systems with sufficiently high sulfate levels that already have a suitable
filtration treatment train in place. g. This technology is most applicable to
small systems that already have filtration in place.

Source: Environmental Protection Agency, 1998.


The following processes were not listed as best available technology (BAT)
systems for radionuclide removal by the EPA in the 1991 proposal.

Greensand Filtration for Radium Removal: A greensand filtration system utilizes
a conventional filter box with manganese greensand replacing traditional filtration
media. Studies have demonstrated that this process can remove up to 56% of radium.

The wastes generated by this method include sludge and supernatant liquid from
the filter backwash, and eventually the greensand medium must be disposed of.

Preformed Hydrous Manganese Oxide Filtration: The cost for HMO filtration can
be quite low if a filter system already is in place. The process is similar
to oxidation/filtration in its complexity and the operator skill it requires.
Proper dosages must be determined, and if water quality varies, the dosage must
be re-calibrated. Once the proper dose is determined, dosing is relatively easy.
HMO filtration requires simple equipment and is fairly inexpensive.

Filters must be backwashed, which may require intermediate operator skill.
Radium-containing wastes include HMO sludge, filter backwash, and sludge supernatant.

Co-precipitation of Radium with Barium Sulfate: Adding a soluble barium salt—such
as barium chloride—to radium- and sulfate-contaminated water causes co-precipitation
of a highly insoluble radium-containing barium sulfate sludge. This process
has primarily been used for wastewater treatment. Mine wastewater treatment
data indicates that this process removes up to 95%S of radium.

The process generates wastes that include the sludge containing the barium
sulfate precipitate, filter backwash, and sludge supernatant.

Other Technologies Available: Some other systems that may have the potential
to become useful processes for removing radionuclides from drinking water also
are available. However, these have not been adequately tested for that purpose,
or they have been used only in industrial or experimental situations. Examples
of processes that can remove radium include selective sorbents (e.g., acrylic
fibers or resins impregnated with manganese dioxide) and non-sodium cation exchangers
(e.g., hydrogen ions and calcium ions).

Sources for more information (top)

American Water Works Association & American Society of Civil Engineers.
1998. Water Treatment Plant Design; 3rd ed. The McGraw-Hill Companies, Inc.
U. S. Environmental Protection Agency. September 1998. Small System Compliance
Technology List for the Non-Microbial Contaminants Regulated Before 1996. EPA
815-R-98-002. U.S. Environmental Protection Agency. August 1998. Federal Register/Notices.
Vol. 63, No. 151. U. S. Environmental Protection Agency. October 1999. Office
of Groundwater and Drinking Water. Proposed Radon in Drinking Water Rule: Technical
Fact Sheet EPA 815-F-99-006. www.epa.gov/safewater/radon/fact.html U. S. Environmental
Protection Agency. June 1991. Office of Ground Water and Drinking Water. Radionuclides
in Drinking Water - Fact Sheet EPA 570/9-91-700. U. S. Environmental Protection
Agency. July 1991. "National Primary Drinking Water Regulations; Radionuclides;
Proposed Rule." Federal Register, Vol. 56, No. 138. U. S. Environmental
Protection Agency. March 1997. Federal Register, Vol. 62, No. 43.


Edited by Editor Emeritus, Ian Lisk, this article is based on a Tech Brief
prepared by the National Drinking Water Clearinghouse located on the campus
of West Virginia University at Morgantown, WV. For more information call 800-624-8301
or 304-293-4191. The NDWC Website address is http://www.ndwc.wvu.edu.

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