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Maybell Mill Site
                                         

Maybell Mill Site
Moffat County, Colorado



Years of Operation Status of Mill
or Plant Site
Uranium Ore
Processed
(Million Short Tons)
Production
(Million Pounds U3O8)
1957-1964 Decommissioned 1.76 4.03
Remediated
Mill/Plant Area
(Acres)
Disposal Cell
Area
(Acres)
Disposal Cell
Radioactive
Waste
Volume
(Million Cubic Yards)
Disposal Cell
Total Radioactivity
(Ci, 226Ra)
Disposal Cell
Average Tailings
Radioactivity
(pCi/g, 226Ra)
UMTRA Project
Final Cost
(Million Dollars)
250 66 3.50 455 200 63.53
   Notes: Uranium Ore Processing and Production are estimated based on historical data. Production does not include uranium recovered from heap leaching of low-grade ore piles after the mill was closed. Radioactivity from radium-226 in the stabilized mill tailings is stated as total curies (Ci) and as average picocuries per gram (pCi/g) of tailings. A picocurie is 0.037 radioactive disintegrations per second. Radium-226 (1620 year half-life) is a decay product in the uranium-238 series. It undergoes radioactive decay to produce radon-222, which is a noble gas, an alpha emitter, and the longest-lived isotope of radon (half-life of 3.8 days).



Map of Colorado showing the location of the Maybell Heap Leach Facility. Having trouble? Call 202 586-8800 for help.

Location:   The Maybell uranium mill site is located 5 miles northeast of the town of Maybell in Moffat County, Colorado.

Background:   In November 1953, privately funded airborne radiometric surveying located anomalies over outcrops of fluvial sandstone strata of Miocene age near Maybell, Colorado. Only a few weeks earlier, radioactive outcrops had been located in similar strata near Baggs, Wyoming, during U.S. Geological Survey geological reconnaissance/radiometric surveying conducted for the U.S. Atomic Energy Commission (AEC). By March 1954, follow-up private airborne surveys, surface prospecting, and subsequent drilling had defined economic sandstone-type uranium deposits near Maybell. In August 1955, the AEC entered into a contract with the Trace Elements Corporation (TEC) for a uranium mill at Maybell, Colorado. TEC established a pilot-scale, ore-processing plant for test extractions and recovered 238 pounds of uranium concentrate, which the AEC purchased under the initial contract. In November 1956, the initial contract was superceded by a new AEC contract for a full-scale uranium mill near Maybell. Over the next year, TEC built the mill on an 84-acre tract near the uranium deposits. In late 1957, before the mill was placed in operation, TEC became a subsidiary of Union Carbide Corporation (UCC, later UMETCO), which assumed control of the operations. The first delivery of concentrate from the mill was received by the AEC in December 1957. In February 1962, TEC was fully merged into the Union Carbide Corporation, which assumed the TEC rights and obligations under the AEC contract. All uranium concentrate produced at the mill was sold to the AEC. Ore for the mill came from near-by open pit mines. In size, the ore deposits ranged up to 250,000 tons maximum. Output of ore from the open-pit mines varied from about 750 to 1,000 TPD of all grades. The average grade was about 0.20 percent U3O8, though the grade was highly variable, and economic ore was mined concurrently with large tonnages of low grade ore. The mine output was classified into four storage categories that ranged from mill-grade ore (at least 0.13 percent U3O8) down to waste rock (less than 0.02 percent U3O8). Over the years 1957-1964 under three AEC contracts, the mill processed nearly 1.8 million tons of ore that averaged 0.13 percent U3O8. The mill was operated at a throughput rate of about 700 tons per day (TPD), and its average uranium recovery rate was 88 percent. The mill was unique in that it used an upgrader circuit to treat low-grade ores before leaching. Low grade ore (containing less than 0.20 percent U3O8) was treated in the upgrader circuit that separated the uranium-bearing slimes from the sand fraction, which was rejected to the tailings pile. The slimes fraction was then acid leached. Higher grade ore was treated directly by acid leaching. The leached slurry passed through a classification/washing circuit that used parallel spiral classifiers and cyclones to separate the fine-grained slurry containing the uranium. This slime product was combined with the leached slimes from the upgrader circuit before entering ion exchange (IX) circuit. The resin-in-pulp ion exchange circuit consisted of six adsorption stages and ten elution stages. The continuous, countercurrent resin-in-pulp process was the first application of this technology in the domestic industry. Uranium was washed from loaded IX resin using ammonium nitrate solution and was precipitated directly with anhydrous ammonia. The coarse fraction from both circuits went to tailings storage. When the mill facility was closed down in October 1964, about 2.6 million tons of mill tailings remained at the site in a pond covering some 80 acres. In the late 1970s, UCC began heap leaching of the remaining low grade ore pile stockpiled at the site. A portable ion exchange plant was used at the site to collect the uranium from the heap-leach solution. The plant eluate product was trucked to the firm’s Gas Hills uranium mill for final processing. By 1982, the mill was dismantled, and the tailings pile was contoured and stabilized with a 6-inch covering of soil that was seeded with native grasses.

UMTRA Surface Remediation:   The Maybell mill site was contaminated by residual radioactive materials. In the 1960s, routine tailings-effluent discharges during normal operations and inadvertent discharge of tailings materials (estimated at 200,000 to 400,000 pounds) into two natural stream courses had spread contamination from the site over a distance of three miles downstream from the mill site. Surface remediation was begun in May 1995 and was completed in September 1998. Contaminated materials from the site, including mill tailings, debris from demolished mill structures, and materials excavated from contaminated vicinity properties were relocated to the engineered disposal cell that was constructed on site. The mill site involves both federal and private lands. Administration of the larger part of the 250-acre site was transferred from the Bureau of Land Management to the U.S. Department of Energy on April 13, 1995. The smaller part was acquired by the State of Colorado, then transferred to the Federal Government in 1997.

Disposal Area:   The disposal cell covers 66 acres of the 250-acre site. The old mill tailings and radioactively contaminated debris and soil materials from the site were relocated to the new engineered cell. A total of about 3.5 million dry tons of contaminated material were placed in the cell. The cell is covered with a 7-foot thick multi-component cap constructed as follows. A 1.5-foot thick layer of compacted soil amended to 7 percent with bentonite that was placed directly on top of the contaminated materials and serves as the radon barrier and water infiltration barrier. To protect the radon barrier from adverse affects of freeze-thaw cycles, a 4-foot thick layer of compacted soil was placed on top of the barrier. Next, a 6-inch layer of coarse alluvial rocky material was placed to provide erosion protection for the underlying soil layer and to divert rainwater away from the radon/infiltration barrier. The top layer of the cap is composed of up to 12 inches of riprap to provide protection against wind and water erosion. The disturbed land surface surrounding the cell was graded to promote surface drainage away from the cell and an apron of riprap was placed at the toe of the cell’s downhill sides to direct runoff away from the side slopes. Disturbed areas surrounding the cell were backfilled with uncontaminated soils, graded for positive drainage, and seeded with a mixture of native grasses. The cell was closed in July 1998.

Responsibility for Remediation:   U.S. Government, 90 percent; State of Colorado, 10 percent.

Stewardship:   Long-term stewardship of the Maybell Mill Site is the responsibility of the Department of Energy’s Grand Junction Office and the site is being managed under the DOE’s Long-Term Surveillance and Monitoring (LTSM) Program in accordance with the approved site specific plan. DOE will be responsible in perpetuity for the safety and integrity of the Maybell site.

Groundwater Program:   Active remediation of the groundwater in the vicinity of the mill site is not required. The aquifers in the region contain naturally occurring uranium mineralization and the groundwater is not a potential source of drinking water. Groundwater beneath the site complies with Federal standards through the application of supplemental standards published in Title 40, CFR Part 192.22. Groundwater conditions downgradient from the Maybell Mill Disposal Cell site will be monitored for potential transient drainage from the cell and the dissipation of process-related contaminants from the site in the groundwater.



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