Hazardous Wastes.
Publié le 11/05/2013
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A Source Reduction
The best way to eliminate hazardous wastes is not to generate them in the first place.
For example, improvements have been made in the production of integratedcircuits: The toxic chlorinated hydrocarbons commonly used in the 1970s were replaced in the 1980s by less toxic glycol ethers and in the 1990s by low-toxicity estersand alcohols.
B Recycling
Recycling is the recovery or reuse of usable materials from waste.
About 5 percent of hazardous waste in the United States is recycled as solvents; a similar amount isrecovered as metals.
For example, approximately 15 percent of sulfuric acid is recycled in chemical manufacturing.
In the past, most sulfur used for sulfuric acid production was mined; nowthe amount of sulfur recovered from smelters (facilities that remove metals from ores), refineries (facilities that purify substances), and manufacturers is more thandouble that produced by mining.
In the United States, the practice of using industrial wastes, which often contain hazardous wastes, as ingredients in commercial fertilizers is encouraged as a means ofrecycling hazardous wastes.
The safety of this practice has recently been called into question, however, and some states are starting to regulate it.
C Treatment
Wastes may be made less hazardous by physical, chemical, or biological treatment.
Nearly 10 percent of hazardous waste in the United States is treated with water;another 11 percent undergoes other treatment.
For example, sodium hydroxide has been used to treat acid wastes at integrated-circuit plants.
Some newer plants nowtreat hydrofluoric acid wastes with lime, producing relatively harmless calcium fluoride, the mineral fluorite.
Sulfuric acid wastes, if not recycled, can be treated withammonia wastes from the same plant, forming ammonium sulfate, a fertilizer.
Incineration has been used since human beings learned to control fire.
It is the preferred method of handling infectious medical wastes.
However, it should not be usedfor wastes that contain toxic heavy metals or chlorinated hydrocarbons: When burned, old painted surfaces can release lead or arsenic into the air, whereas chlorinatedhydrocarbons produce hydrochloric acid and dioxins.
Solids left over from incineration may have to be disposed of as hazardous waste.
About 6 percent of hazardouswaste in the United States is incinerated, and another 11 percent is burned along with fuel.
Solidification of wastes involves melting them and mixing them with a binder, a substance that eventually hardens the mix into an impenetrable mass.
One suggestedtreatment of radioactive waste involves turning it into a glass through a process known as vitrification.
Approximately 8 percent of hazardous waste in the United States is stabilized—kept from moving through groundwater and air.
Sometimes waste can be stabilized on-site; simple remedies such as covering the waste may be sufficient.
Other stabilization methods involve building a barrier around the waste.
This barrier can be ofplastic, steel, concrete, clay, or even glass.
D Disposal
Surface impoundment (placing liquid or semiliquid wastes in unlined pits) keeps waste in long-term storage, but it is not considered a method of final disposal.
About 8 percent of hazardous waste is injected into deep wells; 21 percent enters landfills (large, unlined pits into which solid wastes are placed) as its ultimate resting place.
Abandoned and particularly serious waste sites may qualify as “Superfund” sites, eligible for cleanup with government funding under legislation passed in 1980.
In 1993,of about 38,000 hazardous-waste sites inventoried by the Environmental Protection Agency (EPA), 1407 sites were listed on or proposed for the National Priority List(NPL) for waste cleanup.
In 1995 the EPA estimated that 73 million people lived within 4 miles of a Superfund site in the United States.
Before 1995, 3300 emergencyremovals—urgent cleanups of hazardous wastes because of the immediate hazard they present—were conducted.
The serious problem of underground plumes of hazardous materials leaving the original disposal sites has only partial solutions at this time.
The typical method ofhandling this problem is the drilling of wells around a plume's perimeter.
Hazardous materials are then removed from some wells, and water may be injected into otherwells to produce a barrier to the plume's motion.
Drilling wells and monitoring holes near a toxic site carries risks; a plume originally confined between strata (horizontallayers of rock) may penetrate vertically through a drilled hole and escape confinement.
A recent method of treatment for shallow plumes of chlorinated solvents depends on their chemical reactivity.
A trench is dug around the leaking waste site and filledwith a mixture of soil and powdered iron.
The iron then reacts with the chlorinated solvents, turning them into simple hydrocarbons, which are less hazardous.
V LEGISLATIVE HISTORY
Hazardous waste has a broad definition in common use, but according to United States law, hazardous waste has a narrow, specific meaning.
In 1965, recognizing theneed to segregate hazardous materials from general solid wastes—unwanted solid or semisolid substances—to prevent soil and groundwater contamination, theCongress of the United States passed the Solid Waste Disposal Act (SWDA) to address problems of solid-waste disposal and landfills.
In 1976 the Toxic SubstancesControl Act (TSCA), regulating the use and management—including disposal—of PCBs and other toxic substances, was passed.
PCBs had been widely used in theinsulation of transformers and capacitors in electric power systems and had been discovered to cause cancer.
Also in 1976 the Resource Conservation and Recovery Act(RCRA) was passed, regulating the generation, transportation, and management of hazardous wastes.
In the 1984 reauthorization of RCRA, Congress added theHazardous and Solid Waste Amendments (HSWA).
In 1979 at Love Canal, near Niagara Falls, New York, and in 1983 at Times Beach, Missouri, neighborhoods were declared uninhabitable because they were discoveredto have been dump sites for hazardous wastes.
To control and clean up past hazardous-waste-disposal sites, Congress passed the Comprehensive EnvironmentalResponse, Compensation, and Liability Act (CERCLA) of 1980, which came to be known as the “Superfund,” and its 1986 reauthorization, the Superfund Amendmentsand Reauthorization Act (SARA).
Under RCRA, hazardous wastes are a type of solid waste.
Solid wastes are defined quite broadly and may include solids, sludge, liquids, or gases.
Wastes that are notconsidered solid waste include domestic sewage or wastes that pass through a publicly owned treatment works, industrial discharges subject to the Clean Water Act(1977, amended 1992 and 1995) or Clean Air Act (1970, amended 1977 and 1990), irrigation water, nuclear materials, mine wastes remaining in the ground, recycledsulfuric acid, and some other recycled materials.
Radioactive wastes are specifically controlled by the Atomic Energy Act (AEA) of 1954, and medical wastes by theMedical Waste Tracking Act of 1988..
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