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Mets Technical Detail
The METS Process in Brief
The METS remediation process equipment is about the size of a large 4x4.
It is fully mobile and self-propelled. Previously excavated soil is deposited
in the hopper at the top of the apparatus by a conventional front-end
loader. Very large debris, such as rock, concrete or asphalt, is usually
screened off at the hopper opening. From the hopper, the soil is transferred
in a regulated flow to a custom designed processing mill. The mill impacts
and shreds the soil, while blending a treatment solution (chemical, biological,
or both), along with air and moisture, into the soil using a method that
is proprietary to MB Environmental. The contaminant molecules in the
soil are already being degraded or neutralized by the time the soil emerges
from the processing mill. The treated soil may be deposited directly to
the ground from the mill. However, the apparatus includes a conveyor system
at the back end, which may be used to deposit the soil in locations and
configurations as desired or to meet site space constraints.
Technical Principles Explaining METS Reliability
The METS process is designed to meet all of the critical requirements
for a successful soil remediation technology (i.e., one that produces
"non-detect" results from today's standard soil testing methods,
consistently and quickly), which are:
- Ability to apply a wide variety of proven chemical and biological
remediation treatment products that are available today, as well as
those yet to be invented.
Virtually any contaminant is susceptible to being degraded or neutralised
at the molecular level by a chemical reaction or digestion by microbes.
A great deal of research and development has gone on, and continues
to go on, with the objective of finding or creating specific treatment
products based on this principle. It is not as widely known that such
products have already been created and, in some cases, are already
in commercial use. For reasons that will be explained shortly, these
products have not been used reliably or extensively for remediation
of contaminated soil, prior to the commercialisation of METS.
An example of such a commercially available product (as described
in its patent: P/N 5,478,389) is a composition of a soluble silicate
(in this case, sodium silicate), an anionic surfactant (an ester of
organo-phosphoric acid), and a polyol (ethylene glycol), among other
ingredients. The product is used most commonly today to degrade hydrocarbons
as part of various cleaning and degreasing applications (for example,
in maintenance or emergency spill treatment activities at oil refineries).
The details of the chemical reactions involved are proprietary and
confidential, but the reactions are complex and, to a large extent,
occur simultaneously. The reactions begin immediately upon application,
quickly enough to inhibit the volatilization of any toxic components
into the atmosphere before the degradation process is completed We
have found that this product, when modified for our process, works
as effectively in degrading hydrocarbon contamination in soil as it
does in the cleaning or degreasing applications.
Another example of products based on a chemical reaction strategy
are practical implementations of a well-understood chemical principle
known as Fenton's Reagent Chemistry. FRC provides for direct oxidation
-- release of nascent oxygen -- via an exothermic reaction between
a peroxide and a catalyst. The exothermic reaction as well as oxygen
release, dependent upon catalyst, degrades the hydrocarbon molecule
to its carbon and hydrogen elements. The nascent oxygen reacts with
these elements to form benign compounds (for example, in the case
of gasoline, the byproducts are water and carbon dioxide). Chemical
reactions based on this chemistry are reliable and predictable, once
the proper environment has been created.
Researchers in a variety of organisations and enterprises have identified
and cultured microbes that are proven to degrade and/or neutralize
various types of contaminants. In all known cases, these are naturally
occurring biological organisms that have been found to thrive in environments
where these contaminants have been introduced by man-made events or
by natural causes. Not all of these discoveries have led to commercially
available products, but we have been cataloging them for compatibility
with our process, and are confident that we will have no problem obtaining
practical access to such "products" even if they are not
yet on the open commercial market.
In short, the means to degrade, destroy and/or permanently neutralise
contaminant compounds exists today. We do not believe that there is
any form of contamination that is forever immune to chemical and/or
biological treatment.
- Inconsistencies in soil conditions and content requires excavation
and proper processing to create a consistent and predictable soil matrix.
The primary reason that the products described above have not been
widely used to remediate contaminated soil, is the lack of an effective,
reliable and versatile method for introducing reagents into a stock
of soil. Soil conditions found in nature can vary significantly within
a matter of a few feet, or even a few inches (vertically and horizontally).
Soil naturally varies in its composition (e.g., clay, sand, hardpan,
gravel, etc.), compaction, acidity, moisture content, etc. Moreover,
a stock of soil can contain a variety of materials such as rock, wood,
metal debris, etc., which are capable of obstructing the free flow
of air and moisture.
Nevertheless, most of those who have been developing and promoting
soil remediation technologies, from vapor extraction, sparging, bio-injection,
thermal treatment, soil-washing, etc., have operated on the assumption
that this variability is not a significant constraint on the effectiveness
and efficiency of such technologies. Yet these technologies have not
been effective in removing or neutralizing contamination, except under
controlled conditions, or with incomplete results, or through intervention
with highly expensive and/or slow acting processes. In fact, in our
view, the only credible and meaningful success stories associated
with these technologies (especially bioremediation) is where they
have been applied to create barriers in front of contaminant plumes.
We have determined, after several years of research and practical
experience with a variety of these technologies, that this variability
of soil conditions and content is the principal, if not sole, barrier
to effective and efficient remediation of contamination-saturated
soil. We believe that for any remediation technology to be considered
viable it must, first and foremost, have a means of eliminating this
variability in the soil, in conjunction with introducing one or more
chemical/ biological reagent(s). Second, the method for rendering
the soil into a homogenous matrix must reduce the soil to a fine particle
state in order to maximise access to the contaminant molecules. Third,
the method must have a means of ensuring that the reagent(s) is evenly
distributed throughout this homogenous soil matrix, and allowed to
complete the degradation/neutralization process, before the soil loses
its homogenous and fine particulate composition.
Finally, to promote speed and efficiency, the soil matrix should include,
at least initially, a relatively high level of air entrainment and
a carefully calibrated level of moisture content. These are efficacious
conditions for promoting and sustaining the desired chemical reactions;
they are even more critical for a treatment regime based on biological
organisms. We have found for example, that bioremediation methods
that do not create these conditions (homogenous matrix, fine particulate,
effective distribution, air entrainment and proper moisture) can take
many months to show meaningful results, and may take years to achieve
remediation objectives (perhaps requiring periodic re-injections of
the biological reagents). However, with our process, meaningful results
using biological organisms can be seen within hours, and remediation
objectives achieved within a few weeks.
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Adaptation of existing soil processing technology to create
a homogenous, fine particle soil matrix.
Knowing that successful remediation technologies would depend upon
effective soil processing technologies -- i.e., technologies that
(1) create a homogenous soil matrix consisting of fine particle soil
elements; (2) ensure even distribution of chemical/biological reagents;
(3) promote air entrainment; and so forth -- we began researching
and evaluating possible candidates. We did not consider inventing
such a technology because we did not believe it would be necessary
to do so. In addition, we did not want our process design to be hampered
by uncertainties about the performance of such a critical element.
We did not find such candidates in the environmental remediation
industry. We did, however, find many attractive candidates, presenting
various combinations of strengths and weaknesses for our purposes,
in the mining, sand-and-gravel and agricultural equipment industries.
Processing and treatment of soils and soil content is, of course,
a vital element in mining and sand-and-gravel operations, and in agriculture.
In addition, we found similar technologies starting to become more
common in the demolition industry (for materials processing) and some
other industries far removed from, or at least outside the understanding
of, the environmental remediation industry.
It does not serve the purposes of this paper to detail this part
of our investigation. It should be sufficient to say that we not only
researched these technologies, but also in certain instances made
practical application of them to the purpose of remediating contaminated
soil or simulations thereof. As a result, we were able to identify
the best technology, its commercial embodiments and the basis for
modifying it to meet our objectives.
It should be noted, in the interest of proper disclosure, that we
are not the only company or inventor who has identified the need for
or usefulness of soil processing equipment, of one type or another,
to environmental remediation. We know of others who have attempted
to commercialise inventions based on this insight, and we are also
familiar with a variety of patents that have been issued, which contain
references to the use of such equipment for environmental remediation.
We do not, however, know of any other company or inventor who has
succeeded in developing a practical and commercially proven process
that meets all of the criteria for success that we identified, especially
the ability and knowledge base necessary to remediate a wide range
of contaminant types in a wide range of soil conditions, with efficiency
and reliability.
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Proper integration of chemical/biological treatment reagents
with the soil processing mechanism.
As noted above, it is a necessary but not sufficient condition for
success that the soil be processed into a homogenous matrix of fine
particle soil elements. In addition, there has to be a means for evenly
distributing the chemical/biological reagent(s) throughout the soil
while it is in this homogenous state. In order to meet this objective,
we again conducted research into commercially available technologies
that could be adapted to the purpose. We were able to identify a number
of promising candidates, primarily in the agricultural equipment industry.
In this industry, of course, it is desirable to obtain even distributions
of chemicals, nutrients, and organic materials, into soil. The modifications
required for our purposes were minor and involved minimal invention
on our part.
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Ability to treat multiple contaminant types at the same time.
Many remediation projects, particularly on industrial or military
property, are hampered, if not completely stymied, by the fact that
the soil is contaminated by more than one pollutant/hazardous material.
For example, a stock of soil might be contaminated with gasoline and
soluble lead. All of the problems and challenges, that make remediating
a single contaminant type so difficult and unreliable, are compounded
when multiple contaminants are present (in fact, most other remediation
technologies would be hard-pressed to efficiently remediate soil contaminated
with even two different hydrocarbon types, such as gasoline and motor
oil).
The ability to treat soil containing multiple contaminant types in
the same reliable, efficient, affordable process, was not a critical
objective of our research and development effort. However, we quickly
discovered that the technologies we identified, and the processes
we designed, were easily and readily adaptable to treating multiple
contaminant types during a single pass through the process equipment.
In fact, the modifications required to achieve this result are trivial.
Essentially, they involve installing a series of separate storage
and distribution systems acting in parallel, each of which applies
a different reagent to the soil (for example, one reagent to degrade
the diesel fuel, another reagent to neutralize the soluble lead) at
the same time. There is no practical limit to the number of reagent
delivery systems involved, and therefore number of contaminant types
that may be treated in this way, other than constraints on the desired
physical size of the processing equipment.
On the other hand, we recognize the possibility that, in certain circumstance,
activities by one reagent may hamper or block the actions by another
(for example, a chemical reagent might be harmful to, or inhibit a
biological organism until the chemical reactions are completed). Those
situations, which we think will be rare, would be identified in laboratory
testing prior to field application. In that event, the simple solution
would be the run the soil through the process equipment a second time.
Conclusion
METS is a commercial reality today. The explanation of the METS process
may seem surprisingly simple to those who have been frustrated by the
failure of other remediation technologies. The trend in recent years has
been to adopt remediation technologies that contain a high degree of engineering
complexity and expensive, custom-designed components. Nevertheless, the
simplicity of the technical concepts underlying the design of the METS
process, is part of the reason why it is so powerful. This is also why
METS is the only fully commercial technology, existing today, that can
treat such a wide range of contamination problems faster and at a lower
cost than any other active method of remediation, including landfilling
(i.e., "dig-and-dump").
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