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U.S. Spent Nuclear Fuel Policy: Road to Nowhere [Part V: Lessons]

By Robert Peltier -- July 13, 2010

Part 1 of this series explored the historical context of the U.S. nuclear waste storage policy. Part II and Part III looked at the failed Salt Vault and Yucca Mountain projects, respectively. Part IV reviewed the legal and political fallout from the Yucca Mountain failure.  In this final post, we review the past failed attempts to reprocess nuclear fuel in the U.S. and examine the global state-of-the-art reprocessing plants now operating or under construction.

Reprocessing and Recycling in the U.S.

The reprocessing of nuclear fuel first began in the U.S. in January 1943. The Bismuth Phosphate Precipitation Process was used for recovering macroscopic quantities of plutonium. The REDuction-OXidation (REDOX) process was the first successful solvent extraction process to recover both uranium and plutonium; it was further refined into the Plutonium and URanium EXtraction (PUREX) process, which has become the most common and fully commercialized liquid-liquid extraction process for the treatment of spent nuclear fuel (SNF).

In order to support a self-sufficient commercial nuclear power industry in the 1960s, the Atomic Energy Commission (AEC, circa 1946 to 1974)—the predecessor regulatory agency to the NRC (1974 to present) and the Department of Energy (circa 1977 to present)—encouraged the transfer of nuclear fuel reprocessing from the federal government to private industry. The three privately owned reprocessing plants constructed were the Western New York Nuclear Service Center (West Valley, N.Y.), Midwest Fuel Recovery Plant (Morris, Ill.), and the Barnwell Nuclear Fuel Plant (Barnwell, S.C.).

West Valley, N.Y.: The regulatory lesson. The West Valley facility started reprocessing SNF assemblies using the PUREX process in 1966, and by early 1972 it had reprocessed nearly 1,000 SNF assemblies. However, throughout 1973 and 1974, the AEC adopted increasingly rigorous safety criteria for nuclear facilities, mainly related to seismic issues. In September 1976, West Valley closed due to the economics of complying with heightened regulatory requirements applied retroactively.

Morris, Ill.: The technical lesson. The Midwest Fuel Recovery Plant (MFRP), completed in mid-1971, became a prototype for intermediate-size reprocessing plants to be built near existing nuclear power plants in an effort to reduce transportation costs and public acceptance obstacles. In addition, the designers attempted to minimize the generation of radioactive liquid effluents by avoiding, to the maximum extent practicable, the use of solvent extraction. The facility utilized an Aquafluor process that featured only one stage of solvent extraction and used remotely operated equipment. The waste was to be calcined, placed into containers, and stored in a pool awaiting shipment to a federal repository. During the design and construction phases, processes were demonstrated in the laboratory with bench-scale testing before being incorporated into the facility.

Unfortunately, equipment failures and technical problems prevented the plant from achieving full-scale operation. Its longest sustained run was 26 hours, and in March 1974 all operations were suspended. In July 1974, the MFRP was determined to be inoperable in its as-built configuration and to require a second decontamination solvent extraction cycle that would take a minimum of four years to complete. Finally, given the projected costs and the increasing regulatory scrutiny at West Valley, operations were terminated in August 1974. The MFRP closed without ever having reprocessed a single SNF assembly. It is currently used as an independent wet-pool storage installation.

Barnwell, S.C.: The political lesson. The Barnwell Nuclear Fuel Plant (BNFP) was the first large-scale commercial reprocessing facility in the U.S. consisting of:

· A fuel-receiving and storage station.

· A separations facility to chemically process SNF assemblies into liquid uranium, liquid plutonium, and liquid high-level waste (HLW) using advanced PUREX technology.

· A uranium hexafluoride facility to convert the liquid uranium into uranium hexafluoride.

· A plutonium conversion facility to convert the liquid plutonium to an oxide.

· A waste solidification facility to solidify the liquid HLW and store it prior to shipment to a federal repository.

The BNFP separations and uranium hexafluoride facilities were finished and undergoing preoperational testing when the NRC terminated all licensing actions on December 23, 1977, as part of U.S. policy to defer indefinitely the reprocessing of commercial SNF in response to proliferation concerns.

The “Decision” to Defer

During the 1976 presidential election campaign, critics raised concerns over the acquisition of plutonium from civilian nuclear power programs, the proliferation of nuclear weapons, and controls over exporting nuclear technology. In response to these concerns, and just prior to the 1976 election, President Ford announced a major decision by the U.S. government calling for a temporary halt to reprocessing that was aimed at stopping the proliferation of nuclear weapons capability.

In 1977, the Carter Administration extended the moratorium into a long-term policy to defer indefinitely the commercial reprocessing and recycling of plutonium produced in U.S. nuclear power plants. As a result of this decision, approximately 97% of the recoverable uranium and plutonium from SNF became nonrecoverable waste products.

Although the goal in principle was desirable, it ultimately eliminated all U.S. commercial reprocessing. In spite of the U.S. position, reprocessing continued elsewhere in the world, causing the U.S. to lose much of its influence in international nonproliferation efforts.

In October 1981, President Reagan lifted the indefinite ban on U.S. commercial reprocessing activities. However, even overlooking the negative history of the West Valley, Morris, and Barnwell plants, the availability of low-cost uranium, numerous plant cancellations, and premature shutdowns eliminated any interest in and financial incentives to reprocess SNF. By 1993, President Clinton had reaffirmed the U.S. deferral policy that discouraged reprocessing and research.

Reprocessing Around the World

As in the U.S., reprocessing programs were started elsewhere in the world in order to support defense and nuclear energy programs. Currently, reprocessing and recycling is conducted in France, the United Kingdom, Japan, Russia, India, and China; Germany and Belgium have conducted pilot activities. Several facilities provide reprocessing and recycling services across national boundaries. Those facilities use an optimized PUREX process that separates uranium and plutonium and encapsulates the remaining transuranics (such as americium, neptunium, and curium) and fission products into a vitrified waste form.

For example, in France, the mission of the AREVA La Hague plant, which entered service in 1966, is to reprocess SNF. Reprocessing consists of separating and conditioning the various components of the SNF for recycling. Approximately 97% of the used fuel is recyclable when it leaves the reactor—96% as uranium and 1% as plutonium—while 3% is nonreusable waste materials and fission products. Therefore, natural uranium resources can be conserved, and the volume and toxicity of the final waste materials can be significantly reduced by treatment and conditioning specific to each type of waste.

The AREVA La Hague plant has a commercial reprocessing capacity of 1,700 metric tons of SNF per year, equivalent to annual SNF discharges from 90 to 100 light water reactors (Figure 1). For more than 20 years, AREVA La Hague reprocessing agreements have been in effect with the French nuclear program, Japanese power companies, and 29 European power companies, which are located in Germany, Belgium, Switzerland, and the Netherlands. From 1990 to 2007, the La Hague site has reprocessed approximately 23,600 metric tons of SNF for the recovery and recycling of uranium and plutonium for new fuel. The waste products consisting of transuranics and fission products are then vitrified for long-term storage. The volume of material requiring repository disposal is reduced by a factor of six compared with directly disposing of SNF.


1. AREVA operates a state-of-the-art used nuclear fuel reprocessing center in La Hague, France, that accepts fuel from nuclear plants across the European Union and Japan. Courtesy: AREVA

According to Dr. Alan Hanson, executive vice president, technology and used fuel management for AREVA (Bethesda, Md.), the economics of recycling can vary. “It is clearly economical to recycle aluminum because of the huge energy costs required to make aluminum, but it may be marginally economical to recycle paper. Nevertheless, it is the right thing to do. In the case of recycling used fuel, you can eliminate the need for 25% to 30% of new uranium. In addition, by reprocessing, we convert the waste form, primarily comprised fission products and transuranics, into highly stable vitrified glass that we believe is a better durable waste form than the fuel assembly itself.”

The COEX Process

Under GNEP, various reprocessing and recycling options have been proposed for separating SNF constituents into several product streams. Hanson stated that AREVA has proposed a recycling strategy based on a new integrated co-extraction (COEX) process (Figure 2).


2. In the AREVA COEX recycling process the used nuclear fuel is separated into three major streams: uranium-plutonium, uranium, and fission products and minor actinides. The COEX process does not separate out pure plutonium, which reduces the risk of its being used to build nuclear weapons. Source: AREVA

Whereas the PUREX process was originally designed to purify plutonium for weapons purposes, the COEX process does not separate pure plutonium at any point in the recycling plant. COEX consists of two colocated processes: the treatment process and the mixed oxide (MOX) fuel fabrication process. One additional attraction of MOX fuel is that it provides a way to dispose of surplus weapons-grade plutonium in the current U.S. fleet of conventional light-water reactors (LWRs).

In the COEX treatment process, SNF is separated into three major streams:

· Uranium-plutonium, extracted together and then turned into MOX fuel.

· Uranium, which is sent to external facilities for purification, conversion and reenrichment, and fabrication of additional recycled fuel.

· Fission products and minor actinides, which are vitrified into glass logs, stored on site as HLW, and eventually disposed of in a licensed repository.

In the COEX process, the uranium-plutonium mix is turned into MOX fuel for use in LWRs. Hanson commented that “The uranium-plutonium output stream is precipitated and co-precipitated and never, either as a product or in the piping in the facility, is pure plutonium. In that regard, COEX meets the nonproliferation requirements of GNEP by not producing pure separated plutonium, and the output product is one step further away from being usable for weapons purposes.”

The next generation of reprocessing and recycling plants in France that will ultimately replace the La Hague facility will use the COEX process.

Here in the U.S., AREVA announced in May 2008 that Shaw AREVA MOX Services LLC and the DOE had signed an agreement implementing construction of the Mixed Oxide (MOX) Fuel Fabrication Facility at the Savannah River Site in Aiken, South Carolina. The facility will remove impurities from surplus weapons-grade plutonium and mix it with uranium oxide to form MOX fuel pellets for reactor fuel assemblies. The assemblies then will be used in commercial nuclear power reactors. The facility’s design is based on AREVA’s La Hague and Melox fuel treatment facilities in France. From a physical protection perspective, the self-protecting, highly radioactive nature of the used MOX fuel will prevent direct handling of the assemblies, which will deter diversion of the residual plutonium.

U.S. Missed the SNF Boat

The closed fuel cycle option that involves reprocessing and recycling SNF has gradually gained recognition thanks to more than 40 years of demonstrated operational experience in France and a higher level of reliable economic data from actual operations. The Boston Consulting Group conducted an independent study funded by AREVA to review the economics associated with the closing stages of the once-through and recycling strategies. Proprietary data was obtained from AREVA, which reflected more than 20 years of nuclear materials reprocessing and recycling experience.

The study compared the long-term cost of recycling SNF against the possible cost of a repository handling the same SNF in a once-through strategy. In one scenario, the overall discounted cost of recycling SNF was on the order of $520/kg. This result was comparable to the cost of a once-through strategy, estimated at $500/kg, especially considering uncertainties, such as the price of uranium and repository costs.

Examining another possible scenario, the consulting group considered a new integrated recycling plant scheduled to open in 2020 that would use the COEX process, handle 2,500 metric tons per year of SNF, and be combined with a repository (such as Yucca Mountain) for storing HLW and legacy SNF. This scenario was projected to have a total net present cost of $48 billion to $53 billion. This result is equivalent to the net present cost of an exclusive once-through strategy with Yucca Mountain and an additional repository estimated at $47 billion to $50 billion.

Furthermore, the projected total undiscounted life-cycle cost for the recycling strategy would be approximately $113 billion, compared to approximately $124 billion to $130 billion for the once-through strategy. Given the intrinsic uncertainties used in the study, and the fact that almost 30 years have elapsed since President Reagan lifted the indefinite ban on U.S. commercial reprocessing activities, the economics of a recycling strategy are comparable to, if not better than, those of a once-through strategy.

International SNF Reprocessing

Through international agreements and contracts, and following International Atomic Energy Agency (IAEA) regulations, it is very common for European companies to ship their SNF by rail to La Hague for reprocessing and recycling. For example, 235 metric tons of SNF from Italy’s nuclear power plants will be sent to France for reprocessing.

However, French nuclear law does not allow AREVA or any other entity to take waste and keep it in France. Although the recovered uranium and plutonium can be recycled for new fuel, the vitrified waste products are returned to the country of origin or another third party, as long as it is not in France. Therefore, Italy has to take back its vitrified waste products at some point in the future, but no later than 2025 (Figure 3). Other countries that ship their SNF to France for reprocessing must adhere to the same requirements.


3. The vitrified waste is kept in storage cells located below the floor at the La Hague facility. Courtesy: AREVA

Overseas shipments of another country’s SNF and shipments returning the vitrified waste for disposal must use specifically modified ships that adhere to the International Code for the Safe Carriage of Packaged Irradiated Nuclear Fuel, Plutonium and High-Level Radioactive Wastes on Board Ships (INF Code).

Hanson indicated that because processes are in place for a country to export its SNF and re-import its vitrified waste for disposal, this option could help the U.S. alleviate its SNF storage problem. However, international agreements would need to be developed between the NRC and France’s equivalent regulatory agency, the Nuclear Safety Authority (ASN).

“Furthermore, there is a well-utilized international program through the IAEA for transporting nuclear materials,” Hanson noted. “However, every nation that adopts these regulations tends to modify them in practice to meet their own needs. Because of that, there is a difference between the NRC’s and France’s regulations to certify nuclear transport casks. In practical purposes, there is no existing transport cask that has been licensed by both the NRC and the ASN. So there is no existing fleet of casks to move the fuel today between the United States and France. Possibly some of the existing fleet of transport casks could be adopted for this purpose, but there would need to be some up-front engineering and licensing considerations that must be worked out. Still, the biggest challenge in making this option economically justifiable is the cost of the marine transport of the used fuel and vitrified waste.”

Hard Lessons Learned

It remains unclear if a logical and politically acceptable path toward developing a national, long-term storage facility for SNF and HLW  or construction of a fuel reprocessing facility is possible in the U.S.. It is our opinion that there is not. The DOE and its predecessor agency has tried and failed multiple times, over several decades. State veto power over siting a storage facility makes approval of a facility essentially a national referendum on nuclear power, given that a veto must be overridden by the Senate and the House. Also, the extremely long period of time required to develop any storage facility would certainly span presidential administrations of both political parties, making any project like Yucca Mountain susceptible to closure when the political winds change. Why would we expect a different result at a new site a decade hence?

History can be a stern teacher, and we should learn this important lesson. There is no long-term, politically expedient road to a Yucca Mountain–type facility anywhere in the U.S. We expect the blue ribbon commission to spend the next two years or more studying the problem only to come to the same conclusion. Nuclear fuel reprocessing has only received political lip service for decades. If there isn’t the political will to complete Yucca Mountain, building a reprocessing plant in the U.S. is beyond comprehension.

As a nation, we would be better served if Congress would amend the NWPA and NWPAA to delete the statutory responsibility of the DOE to store SNF, refund the NWF contributions, and quickly settle the 60-plus lawsuits pending to cover all current and future nuclear plant SNF storage costs. The elegant solution is to prime the nuclear fuel reprocessing pump by reprogramming NWF money into building such a facility without using public money. This approach also will minimize the size of a Yucca Mountain-like repository and thus improve the chances of actually siting and building a waste fuel repository.

Portions of this post were first published in POWER magazine and co-authored with Contributing Editor James Hylko.


  1. Jon Boone  

    A sober but honest conclusion to a good survey of this soggy history–in this land of Lilliput. The real nuclear waste problem is the scientific illiteracy animating our politics, beginning with our politicians, extending out to our regulatory agencies, media at virtually every level, our schools, the sunk costs involved with our existing energy usage, our entrepreneurial culture (so knee deep in nonknowledge, nontalent, and rent seeking), and, not least, our friends and neighbors.

    This is a time for genuine leadership to emerge. But without real knowledge, this would prove to be empty posturing. However, Richard Peltier’s account here is a positive step in the acquisition of such knowledge. Once again, thanks to Master Resource.


  2. Ruta Wagner  

    While there are strengths to this useful series, it ignores the unresolved scientific and technical issues that made Yucca Mountain the wrong choice for the disposal of high-level radwaste. Uncertainty Underground: Yucca Mountain and the Nation’s High-Level Nuclear Waste by Allison M. Macfarlane and Rodney C. Ewing lay out the science in this 2006 book published by MIT Press.


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