Solidification/Stabilization Treatment Methods
John Poullain, P.E.
Course Outline
This two-hour
online course provides general guidelines for the treatment of hazardous and
toxic waste (HTW) at uncontrolled hazardous waste sites. The guidelines for
the selection of solidification and stabilization (S/S) treatment methods for
contaminated liquids, soils and sludge discussed in this course. Conducting
treatability studies prior to treatment, including the required testing, sampling
and optimization to establish mix ratios are also discussed. Remedial actions
performed at a contaminated site must comply with federal, state and local regulations.
This course includes a multiple-choice quiz at the end, which is designed to
enhance the understanding of the course materials.
Learning Objective
At the conclusion of this course, the student will:
Intended Audience
This course is intended for civil engineers and planners.
Benefit to Attendees
The student will
become familiar with solidification and stabilization (S/S) methods used for
treating contaminated liquids, soils and sludge at hazardous and toxic waste
sites. The basic guidelines for the S/S treatment methods, the advantages and
disadvantages and guidance in the selection of the most appropriate treatment
method are discussed. The differences in the methods and benefits of their combined
use and waste conditions not suitable for their use are explained. Understand
proper sampling techniques and tests required for mix designs and optimization
of mix ratios. Potential environmental risks caused by treatment, measures for
minimizing risks and beneficial uses for a treatments' final products are also
discussed.
Course
Introduction
This course provides
general technical guidelines and procedures for solidification and stabilization
(S/S) methods of treatment at uncontrolled HTW disposal sites. Remedial action
at an uncontrolled hazardous waste site consists of on site control, on site
treatment, on site storage or off site disposal or combinations of these. On
site and off site landfill disposal is a viable option when the volume of HTW
material is within the feasible or economic limits of available technology.
Landfills prohibit bulk or non-containerized liquid hazardous waste because
liquid wastes and free liquids will leach into the groundwater over time without
proper treatment and handling. To avoid groundwater contamination landfills
may accept only containerized liquids, which do not have free liquids or are
mixed with adsorbents or solidified to remove freestanding liquid. Lab packs
and very small containers, ampules, may also be placed in a landfill.
Remedial actions must comply with the regulatory guidelines of the Department
of Defense Environmental Restoration Program (DERP), the Formerly Used Defense
Sites (FUDS) Program, Resources Conservation and Recovery Act (RCRA), the US
Environmental Protection Agency (EPA) and the Comprehensive Environmental Response,
Compensation and Liability Act (CERCLA or commonly called "superfund").
Waste sites must be investigated for a wide range of conditions, including ground
water levels, surface drainage and subsurface ground conditions. Disposal methods
for radioactive waste are not discussed here since satisfactory disposal requires
special landfills that are regulated by the Nuclear Regulatory Commission (NRC).
S/S treatments are relatively quick and low cost processes. Because of great
variations in contaminants at waste sites, site specific design for the ratio
of waste and additives is required. Treatment is accomplished by first mixing
the waste with reagents using augers, excavators or backhoes and the pozzolonic
agents to harden the waste and is then allowed to cure. Reagents commonly used
are Portland cement, cement kiln dust (CKD), lime, lime kiln dust, fly ash,
slag, gypsum and phosphate mixtures. Fly ash has a pozzolonic effect if mixed
with Portland cement. CKD however does not have strong cementitious properties
but is economical. Lime will adjust the pH and drive off water. A benefit from
treating drilling fluids for instance is that after proper curing they may be
reused or else left safely in place. The treatment and cure times will depend
on the chemical types and amounts, extent of pollution and depth, subsurface
conditions and whether mixed in place or removed for mixing.
S/S are two different types of remediation methods which prevent or slow the
release of harmful chemicals from contaminated soil, sludge and liquids. These
methods targeted treating petroleum wastes such as oil field waste and wastewater,
drilling mud, cuttings and oil based drilling fluids. The chemicals are not
usually destroyed but are prevented from migrating into the environment. The
solidification process essentially binds the contaminated waste and cements
it into a solid form by mixing with reagents and then pozzolonic setting agents
to harden the waste material which may be safely left in place or removed. Rain
and ground water are prevented from dissolving or moving chemicals from the
treated waste material. Reagents added to metal contaminated soil changes the
metals to less soluble metal compounds and immobilizes them. Stabilization alters
the chemicals to become less harmful or less mobile. Both methods are often
used together as complementary treatments.
S/S techniques used to treat waste containing organic contaminants with traditional
cements and pozzolonic materials have not always been successful and are then
classified as hazardous. Organics have had adverse effects on cement hydration,
structure formation and stabilization of contaminants. Safe disposal would then
require a lined landfill with monitoring system or pretreated with thermal or
biological processes. As mentioned in the text, organophillic clay modified
with special additives holds some promise to chemically fix organic compounds.
Organophillic clay can tolerate excessive hydration with out losing stability
unlike the traditional cements and pozzolonic treatments. Br selective use of
these clays and other compounds it is believed the reactive properties of the
clay will chemically bind organic contaminants to a clay matrix. After mixing
with the clays the waste can then be solidified with other reagents. Organic
reagents such as asphalt, thermoplastics and urea-formaldehyde have also been
attempted but they are prohibitively expensive compared to inorganic reagents.
The advantages and limitations of S/S waste treatment methods are compared.
The treatment methods present certain environmental risks and other concerns
for consideration. Environmental risks include mismanagement of drainage, inadequate
treatment levels and air pollution control. Leachate, migration of contaminants,
runoff and wind erosion can contaminate the subsoil, groundwater and nearby
surface water. The treated waste must be tested for proper sealing, strength
and durability to provide a safe cleanup.
Course Content
This course is based primarily on the US Army Corps of Engineers
Technical Letter, "Treatability Studies for Solidification/Stabilization
of Contaminated Material", ETL 1110-1-158 (1995 Edition, 18 pages) PDF
file.
The course also uses Chapter 4, paragraph 4-21 of the US Army Corps of Engineers
Manual, "Technical Guidelines for Hazardous and Toxic Waste Treatment and
Cleanup Activities", EM 1110-1- 502, paragraph 4-21, (1994 Edition, 6 pages)
PDF file and the course paragraph, "Course Introduction".
The link to the Engineers Technical Letter is "Treatablility
Studies for S/S of Contaminated Material"
The link to the Engineers Manual is "Technical
Guidelines for Hazardous and Toxic Waste Treatments and Cleanup Activities",
Chapter 4, paragraph 4-21.
You need to open or download above documents to study this course.
You may need to download Acrobat Reader to view and print the document.
Course Summary
State and federal
regulations have to be complied with at hazardous and toxic waste sites in order
to remove any threat to human health, welfare or to the environment. Hazardous
and toxic waste includes materials defined as hazardous waste, hazardous substance
and pollutants. Among HTW substances are heavy metals, including lead, cadmium
and mercury and PCBs, dioxins, chlorine, sulfur, potassium and explosives. Solidification
and stabilization methods are discussed and can be used to remediate contaminated
soils and sludges prior to final disposal and to reduce the land needed for
disposal as for traditional landfills.
Related
Links
For additional technical information related to this subject, please refer to:
http://www.epa.gov/epaoswer/osw/hazwaste.htm
Comprehensive information about hazardous forms of waste, definitions, RCRA
requirements.
Quiz
Once you finish studying the above course content, you need to take a quiz to obtain the PDH credits.