The equivalent of 25 kg of table salt
are discharged into the drainfield soils each year
from a household of 3-4 users. Within 4-10 years,
sodium discharge begins to effect the ability of
disposal soils to treat and absorb domestic waste
water. The amounts of sodium used, the precise
nature of local soils, and the volume of drainage
area in the system vary, of course. The high sodium content of household
products for laundry, kitchen, bath and cleaning
are a primary source of soil failures. Addition of
water softener wastes or sodium content in local
water supply also contribute to the problem.
New research pinpoints old
problem
A ten year study recently completed by Dr.
Robert Patterson contains the newest and most
thorough study ever undertaken on the contribution
of sodiums to septic system soil
failures.
Dr. Patterson's work sheds new light on the
influence of modern products on septic system
drainage soils. The detailed records and
scientific laboratory evaluations provided in this
outstanding scientific work by Dr. Patterson give
us clear insights into problems noted by leading
scientists over the years.
After ten years of thoroughly documented
research, Dr. Patterson concludes: "The inevitable
consequence of continual addition of sodium in
septic tank effluent is a decrease in the soil's
hydraulic conductivity leading, in many cases, to
drainfield failure."
Clay particles magnified by an electron
microscope.
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If a grain of sand were the size of a
basketball, then a piece of silt would be the
size of a marble, and a particle of clay would
be a pinpoint. Clay particles are tiny, less
than one 12,500th of an inch. When sodium is present in wastewater
passing through these tiny clay particles, the
particles tend to stick together forming hardpan
conditions in the
soil. | |
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Three causes of septic system soil
failure
Septic system soil failure may be physical,
biological or chemical. These three conditions
often occur in sequence. For instance, when
chemical (cationic) exchanges occur from sodium,
fines or clay particles may bond into a waterproof
barrier, which in turn causes the physical
flooding, blockage of soil passages and biological
death of air-dependent cleaning organisms in the
soil.
Agricultural soil and wastewater scientists
have long recognized that in time, sodium in
irrigation waters will cause finer soil particles
to bond together into impermeable layers. In
agriculture, this chemical change causes physical
or structural changes in the soil which ultimately
leads to loss of biological uptake of plant
nutrients.
In the septic system drainfield, problems
begin when a thin impermeable layer of bonded
fines develops directly under the leachlines or on
the trench floor or walls.
This layer grows in density over time and
soon a "waterproof" barrier prevents access to the
absorptive active soil surfaces needed for maximum
organism contact and cleanup of wastes.
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Historic recognition of sodium influence
on soils
In the late 1940s and early 1950s
researchers working at UC's Sanitary Engineering
Research Lab (SERL) in Richmond, California and at
the Federal Security Agency (FSA) facility in
Cincinnati made dozens of presentations to
environmental health professionals.
The role of sodium in waste water was
repeatedly mentioned as a contributing factor in
septic system leachfield failures. Publications of
SERL and Cincinnati findings published over the
next several years made note of sodium influences
on soils.
In a 1953 speech entitled Clogging
Characteristics of Domestic Effluent, T.W.
Bendixen outlined the role of sodium to a series
of audiences across the nation.
He observed, "It is generally considered
that waters containing 50 percent of total cations
(sodium, calcium, magnesium and potassium) as
sodium are potentially harmful to soil absorptive
characteristics. Even in sandy soils, waters of 85
percent or higher are likely to make soils
impermeable after prolonged use."
In 1973, Wastewater Treatment Systems for
Small Communities, published by the Commission on
Rural Water, stated that "High concentrations of
sodium ions exchange with calcium and magnesium
ions in the clay matrix. The exchanging ions alter
the forces that hold the clay together and cause
it to lose its structure ... the clay becomes
tighter and seals."
In 1984, University of Wisconsin scientists
assigned to study the effects of water softeners
on septic systems reported to the Water Quality
Research Council. The findings of these
researchers led them to recommend that, "Studies
be initiated to determine the effect of actual
salt concentrations in various zones of the septic
tank, with and without the addition of water
softener wastes."
Many field studies of septic system
chemistry and structure have historically noted
the high sodium levels where soils are used to
drain domestic waste water. In 1953, several
studies were performed by Universities,
consultants, wastewater and soil laboratories on
methods for correcting or reducing sodium impact
on septic system soils. None of these studies
compare to the decade of documentation found in
the 1994 work of Dr. Patterson.
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How soil failure contributes to health
concerns
When soils seal, aerobic organisms within
the drainfield "drown." Cleanup of wastewater
effluent slows or stops. As the soil area becomes
more and more limited, leach lines back up, the
tank surcharges, flow from the home is impeded and
eventually, building drains overflow exposing
residents to waste flow.
In many cases raw sewage rises to the
surface or ponds on the ground. Children are
attracted to puddles of standing waste water which
carries diseases such as dysentery, hepatitis A or
typhoid fever. Wastes may be also be tracked into
the home, where further exposure may take
place.
(Note: Dr. Kevin Sherman (University of
Florida) and Dr. Charles Gerba (University or
Arizona) have each studied the potential for
transmission of HIV or AIDS viruses via septage or
domestic wastewater and independently concluded,
due to the fragile nature of these viruses, no
danger could be found from domestic septic wastes.
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How to spot soil failures
Pumpers often observe water falling back
into the tank from the field as the level is
pumped down. This is an important sign of soil
failure. It is obvious that the problem does not
originate in the tank, but in the
drainfield.
It is possible to restore soil structure
and drainage by chemically treating the soil to
release the cationic bond which locks clays and
fines together. This is called "reflocculating"
the soils, and the process is commonly used in
agriculture to provide better absorption of plant
foods and water in field application.
It is not always easy to diagnose the cause
of backups. A recent issue of the EPA newsletter
Pipeline lists signs as "slowly draining sinks and
toilets, gurgling sounds in the plumbing, plumbing
backups, sewage odors in the house, or tests
showing the presence of bacteria in well
water."
***Written by Mary Gayman for an article in
Pumper magazine.*** |