Compliance Status

D. G. Black

This section summarizes the activities conducted to ensure that the Hanford Site is in compliance with federal environmental protection statutes and related Washington State and local environmental protection regulations and the status of Hanford's compliance with these requirements. Environmental permits required under the environmental protection regulations are discussed under the applicable statute.

Hanford Federal Facility Agreement and Consent Order

Originally signed in May 1989, the Tri-Party Agreement is an agreement among EPA, Ecology, and DOE to achieve environmental compliance for the Hanford Site with CERCLA remedial action provisions and with RCRA treatment, storage, and disposal unit regulations and corrective action provisions. At the end of 1994, a total of 378 enforceable milestones (including those from 1989 through 1994) had been completed on or ahead of schedule. The following are some of the more significant accomplishments for 1994:

Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA)

The CERCLA requires that specific procedures be implemented to assess inactive waste sites for presence of hazardous substances. The process is divided into three tiers of activity: 1) preliminary assessments, 2) remedial investigation/feasibility studies, and 3) remedial actions. The EPA has established procedures to conduct the three-tiered process.

Preliminary assessments conducted for the Hanford Site revealed that there are approximately 1,100 known individual waste sites where hazardous substances may have been disposed. These 1,100 sites have been grouped into 62 operable units, which have been further grouped into four aggregate areas using identifiable geographic boundaries. The four aggregate areas have been placed on the EPA's National Priorities List, which requires a schedule and actions for the remediation of each area.

DOE is actively pursuing remedial investigation/feasibility studies at some operable units on the Hanford Site. The operable units currently being studied were selected as a result of Tri-Party Agreement negotiations. The Tri-Party Agreement provides the framework for meeting CERCLA cleanup requirements. All milestones related to the CERCLA process established for 1994 were achieved, and the Hanford Site was in compliance with these CERCLA requirements.

Expedited Response Actions

Expedited response actions are a method of hastening cleanup at sites to prevent further spread of contamination. These actions were first proposed in 1990 and have been ongoing at various sites since 1991. Six accelerated cleanup actions at the Hanford Site were proposed by the Secretary of Energy in 1992. Two of these actions were completed in 1993, and final reports were issued. Two others, remediation of the North Slope and the Riverland Areas, were completed in 1994. A fifth action, mitigation of the flow of contaminated ground water to the Columbia River from the N Springs, was initiated. The sixth action, identification and characterization of hazards in the soil in the burial grounds north of the 300 Area, was deleted as a potential expedited response action because of complexities found at the site. The status of currently active actions is described below.

Carbon Tetrachloride Vapor Extraction

Vapor extraction from the contaminated vadose zone beneath the 200-West Area began in 1992 and continued through 1994. This Expedited Response Action uses three vapor extraction systems to draw carbon tetrachloride out of the soil column and absorb it into granulated activated-charcoal. The charcoal is shipped offsite for treatment. In 1994, about 41,000 kg (90,000 lb) of carbon tetrachloride were removed from the soil. The system is expected to operate for several more years in meeting the response action goals.

N Springs

The DOE, EPA, and Ecology agreed to initiate an expedited response action at the N Springs, which is located in the 100-N Area. The objectives of the expedited response action are to substantially reduce the transport of strontium-90 into the Columbia River through ground water and to obtain data sufficient to establish final remedial actions. An engineering study was conducted in April 1993 for the N Springs. Based on the results of this study, an expedited response action proposal was developed and submitted to the EPA Region 10 and Ecology for review in January 1994, followed by submittal for public review. An action memorandum was issued by the agencies in September 1994 that required the design, construction, and operation of a ground-water treatment system in combination with a barrier wall. Test installations of the barrier wall began in December 1994. Due to installation problems, the barrier has been delayed while alternative barrier installation methods are being evaluated. Design of the ground-water treatment system was initiated in October 1994, and operation is expected to begin in September 1995.

North Slope

In April 1992, the North Slope was selected for an expedited response action by Ecology and EPA. The area covers approximately 36,000 ha (89,000 acres) and is located north of the Columbia River. The area contained potential environmental hazards such as the remains of three missile sites, seven anti-aircraft artillery sites, several homestead sites, ten military landfills, several disposal sites, and three oil-contaminated sites.

In March 1993, an agreement was signed by the DOE, Ecology, and EPA Region 10 to identify additional measures to accelerate Hanford Site cleanup. As part of the newly renegotiated Tri-Party Agreement, a new milestone was established focusing on removal of physical hazards and asbestos from the North Slope. This milestone required that the remediation of the North Slope be completed by October 1994.

Remedial actions were completed in September 1994. Remediation consisted of cleaning up 39 waste sites and decommissioning 16 wells. A record of decision is expected from the regulators in mid-1995. Hazardous waste removed from the North Slope included the following: () of DDT-contaminated soil, () of petroleum-contaminated soil, several hundred containers of various petroleum-based lubricants and solvents, and lead-acid battery plates. The soils were disposed of at waste facilities in Arlington, Oregon and Pasco, Washington. The other wastes were taken to the 100-N storage pad. Additionally, several of the water wells had been broken into and used for the disposal of waste motor oil. These wells were cleaned to Ecology standards before being decommissioned.

Fitzner/Eberhardt Arid Lands Ecology Reserve

A new Tri-Party Agreement milestone was established in January 1994 to accelerate the remediation of the () ALE Reserve by October 1994. The ALE Reserve contains 25 abandoned gas wells that predate Hanford Site activities, several abandoned lysimeter plots, two concrete cisterns, 32 waste sites, and other potential physical hazards. The 1100-IU-1 Operable Unit is also located within the ALE Reserve and contains an old NIKE missile launch site and control center. Remedial actions at the ALE Reserve were completed in September 1994. Thirty-two waste sites were cleaned up, 14 wells were decommissioned, three lysimeter plots were remediated, and of DDT-contaminated soil were removed. Each waste stream was disposed of in accordance with Hanford Site procedures established under the Tri-Party Agreement.

Treatability Studies

Several treatability studies are identified in the Tri-Party Agreement. The purpose of the studies is to test cleanup technologies in the field to determine their effectiveness and provide better information on field conditions and probable costs. Three types of tests have been implemented, consisting of pump and treat systems, soil washing, and an excavation treatability study. More information on these studies is provided below.

Carbon Tetrachloride Ground-Water Plume

The carbon tetrachloride ground-water plume in the 200-West Area covers approximately (). It resulted from historical discharges from processes at the Plutonium Finishing Plant. In early 1994, construction of a pilot-scale pump and treat system was completed and a treatability test was initiated, meeting Milestone M-13-04A. The pump and treat system is testing the removal of carbon tetrachloride, chloroform, and trichloroethylene from ground water using activated carbon. Approximately 4.2 million L (1.1 million gal) of water were treated in 1994. A proposed plan outlining a preferred alternative of scaling up the existing system as an interim remedial measure was issued to the public in October 1994. Once regulator and public comments are addressed, a record of decision will be issued.

Uranium/Technetium Ground-Water Plume

Another ground-water plume in the 200-West Area contains uranium and technetium-99. The contamination resulted from historical uranium recovery operations. A pump and treat system was designed to test removal of these contaminants using ion exchange. The treatability test treated over 7 million L (1.8 million gal) of water in 1994.

200-East Area Ground-Water Plumes

The contaminants in the two 200-East Area ground-water plumes include cesium-137, cobalt-60, plutonium, strontium-90, and technetium-99. They result from historical fuel reprocessing operations in the 200-East Area, including operation of the PUREX Plant and B Plant. Two pump and treat systems, which began operations in 1994, are testing removal of these constituents from ground water using ion exchange and adsorbents. In 1994, approximately 200,000 L (53,000 gal) of water were treated.

Chromium Ground-Water Plume

Chromium-contaminated ground water that resulted from historical reactor operations underlies portions of the 100-D and 100-H Areas near the Columbia River. In 1994, a ground-water treatment system was designed, constructed, and began operation to test removal of the chromium using ion exchange. Through 1994, the system treated 1,930,000 L (511,000 gal) of ground water and removed 2,800 g (6.2 lb) of chromium. Essentially all of the chromium was hexavalent chromium, which has higher environmental and health risks. The system is continuing to operate in 1995.

Burial Ground Excavation Treatability Test

As part of historical operations, contaminated equipment and other solid wastes were buried in unlined excavations. The current condition of the buried wastes is uncertain. An excavation treatability test was undertaken at a large burial ground near the B and C Reactors to test the effectiveness of excavation techniques, analytical screening methods, and waste handling procedures. The objective was to excavate test pits to compare different excavation approaches, identify waste requiring special handling, and determine the feasibility of segregating different kinds of waste. The test was initiated in August 1994.

Emergency Planning and Community Right-To-Know Act and Pollution Prevention Act, Section 6607

The Emergency Planning and Community Right-To-Know Act of 1986 mandates that information about hazardous chemicals on the Site be provided to the public and establishes emergency planning and notification procedures to protect the public from a release. Subtitle A of the Act calls for creation of state emergency response commissions to guide planning for chemical release emergencies. State commissions have also created local emergency planning committees to ensure community participation and planning. Subtitle B contains requirements for periodic reporting on hazardous chemicals stored and/or used on the Site to provide the public with the basis for emergency planning.

The Hanford Site 1994 Tier Two Emergency and Hazardous Chemical Inventory (DOE 1995a) was issued to the State Emergency Response Commission, local emergency planning committees, and local fire departments in February 1995. The report contained information on hazardous materials stored in quantities at or above mandated threshold levels throughout the Hanford Site in 1994. The Hanford Site 1993 Toxic Chemical Release Inventory (DOE 1994b) was issued to the EPA and the state in June 1994. Accordingly, the Hanford Site was in compliance with the reporting requirements contained in this Act.

EPA has issued two final rules expanding the list of toxic chemicals subject to reporting under Section 313 of the Emergency Planning and Community Right-To-Know Act and Section 6607 of the Pollution Prevention Act of 1990. The first expansion was effective for the 1994 reporting year and will be considered during preparation of the 1995 Toxic Chemical Release Inventory covering calendar year 1994. This expansion consists of 21 chemicals and two chemical categories that are listed wastes under RCRA, and 11 halogenated chlorofluorocarbons listed as ozone depleting substances under the Clean Air Act. An additional 286 chemicals, including six chemical categories, are added to the toxic chemical list, effective for the 1995 reporting year. These chemicals were added from lists of substances regulated under the Clean Water Act, Clean Air Act, RCRA, California's Proposition 65, and other sources.

Reporting and Pollution Prevention Program

As part of Section 313 of the Emergency Planning and Community Right-To-Know Act toxic chemical release inventory reporting program, a pollution prevention program has been established that requires an annual evaluation of the use and release of 17 specific priority chemicals. This program seeks to reduce releases of pollutants through avoidance or reduction in the generation of pollutants at their source.

The 17 priority chemicals targeted for reduction in this program are a subset of the chemicals listed in Section 313 of this Act. The thresholds listed in the Act are used to determine participation. DOE is committed to reducing the releases of these 17 priority chemicals by 50% (compared to the 1988 baseline) by 1995. Each DOE site annually evaluates its use and release of these 17 priority chemicals. The information is provided to DOE Headquarters, where it is aggregated for an annual progress report provided to the EPA.

Hanford did not exceed the reporting threshold for the use of any of the 17 priority chemicals during 1994.

The Hanford Site Pollution Prevention Program was designed to meet the requirements of DOE Orders 5400.1, and 5820.2A, the DOE Waste Minimization Cross Cut Plan (DOE 1994e) and EPA program guidance, and State of Washington Pollution Prevention Planning requirements. The major elements of the program were 1) establishment of management support, 2) identification and implementation of pollution prevention opportunities through an assessment process, 3) setting and measuring the progress of waste reduction goals, 4) development of waste generation baseline and tracking systems, 5) creation of employee awareness, training, and incentives programs, 6) championing sitewide pollution prevention initiatives, and 7) technology transfer, information exchange, and public outreach. The Pollution Prevention Opportunity Assessment is the cornerstone of the pollution prevention program and the primary mechanism used to identify and prioritize options to prevent pollution and reduce waste. These assessments are performed on waste-generating activities by a team of individuals selected for their process knowledge.

These assessments are a systematic approach to identify the materials entering, the pollutants and wastes exiting, and the activities that make up a waste-generating process. Potential pollution prevention opportunities are identified, evaluated, and prioritized according to environmental, health, safety, and economic criteria. Once pollution prevention opportunities are identified, schedules are developed, and the opportunities are implemented.

A methodology for pollution prevention opportunity assessments, specific to Hanford Site needs, was developed in 1992 and further refined in 1993. The baseline year established for waste generation was 1993. Significant waste streams for that year have been identified, prioritized, and scheduled for future assessment.

Resource Conservation and Recovery Act

Hanford Site Facility RCRA Permit

The Hanford Facility RCRA Permit was issued by Ecology and EPA in August 1994 and was in effect in late September 1994. The permit provides the foundation for all future RCRA permitting at Hanford in accordance with provisions of the Tri-Party Agreement.

RCRA/Dangerous Waste Permit Applications and Closure Plans

For purposes of RCRA and Ecology's Dangerous Waste Regulations, the Hanford Site is considered to be a single facility encompassing over 60 treatment, storage, and disposal units. The Tri-Party Agreement recognized that all of the treatment, storage, and disposal units cannot be permitted simultaneously and set up a schedule for submitting unit-specific Part B RCRA/dangerous waste permit applications and closure plans to Ecology and EPA. During 1994, 34 Part A Form 3's and three revised closure plans were submitted. A research, development, and demonstration permit for the Waste Water Pilot Plant was issued in May 1994 by Ecology and EPA and was effective in June 1994.

Management of Listed-Waste-Contaminated Soil

Part of RCRA consists of a "contained-in" policy. This policy states that any waste mixture containing a listed hazardous waste is considered a hazardous waste, regardless of what percentage of the mixture is composed of listed hazardous wastes.

To facilitate implementation of this policy, sampling and analysis plans are being developed for the tank farms. These sampling and analysis plans will describe the protocol necessary to properly characterize tank farm soil for contaminants.

RCRA Ground-Water Monitoring Project Management

Table 2.2.1 lists all the RCRA facilities and waste management areas and their ground-water monitoring program status. During fiscal year 1994, samples were collected from 311 wells. There was one RCRA compliant ground-water well constructed in 1994. The well was constructed at the 216-U-12 Crib to provide characterization required by the RCRA interim-status assessment program.

The 183-H Solar Evaporation Basins were included as part of the Sitewide RCRA Permit. Ground-water monitoring will be conducted in accordance with the final status regulations and is planned to be implemented in FY 1995.









Three wells were constructed to support the ground-water monitoring network being established for the Environmental Restoration Disposal Facility. The facility is a CERCLA landfill but will follow RCRA monitoring requirements. This monitoring program will be conducted in accordance with 40 CFR 264 final status RCRA regulations.

Ground-Water Impact Assessments

As a part of the amended Tri-Party Agreement, DOE, Ecology, and EPA agreed that discharge of effluents from the processing of nuclear waste to the soil column will be stopped by June 1995 and that the impact to the subsurface will be determined by conducting ground-water impact assessments.

Two ground-water monitoring wells were installed to support ground-water impact assessments in fiscal year 1994. One well was drilled at each of the 216-T-1 and 216-T-4-2 Ditches. The wells were used to better define stratigraphy, ground-water flow direction and flow rates, and the nature and extent of any contamination. Three test pits were also excavated at each of the two ditches. These were used to determine the lateral extent of contamination within the vadose zone.

RCRA Waste Characterization Methods

Efforts continue to identify the scope of compliance with Test Methods for Evaluating Solid Waste: Physical/Chemical Methods (EPA 1986a) for highly radioactive laboratory analytical activities. To develop a methodology for choosing analytical procedures for highly radioactive wastes, documents such as the Hanford Analytical Services Quality Assurance Plan (DOE 1994f) have been prepared.

Underground Storage Tank Program

The Underground Storage Tank (UST) Program of RCRA regulates operation and closure of USTs. During 1994, the five remaining USTs were removed, finishing all fiscal year 1994 milestones.

Hanford Site Backlog Waste Program

In March 1993, Ecology issued Order Number 93NM-201 to the DOE Richland Operations Office and the Westinghouse Hanford Company for failure to properly designate as waste the contents of 2,276 containers. The Pollution Control Hearing Board modified the original Order (PCHB Number 93-64) such that designation of the backlog containers named in the Order was completed by September 1994.

In August 1994, the Richland Operations Office notified Ecology that waste designations for the contents of the 2,276 containers had been completed. The containers were processed according to the Waste Analysis Plan for Confirmation or Completion of Tank Farms Backlog Waste Designation. Copies of relevant portions of the Solid Waste Information and Tracking System database were provided to meet the requirement for a report detailing the final designation and selected waste management options for all containers identified in the Order. With the completion of these actions, all nine compliance actions of the Order have been completed.

RCRA Inspections

DOE and its Hanford contractors are working to resolve outstanding notices of violation and warning letters of noncompliance from Ecology that were received during 1994. Each of these notices lists specific violations. There were ten letters in total in 1994. Below is a brief summary of some of these noncompliance letters.

In June 1994, the DOE Richland Operations Office notified Ecology that 95% of the tank farms personnel had completed the required training, and all remaining personnel would be limited to work that did not directly affect dangerous waste management activities until their training was completed. Ecology found the corrective actions satisfactory and considers this action closed.

Clean Air Act

The DOH, Division of Radiation Protection, has promulgated regulatory controls for radioactive air emissions under Section 118 of the Clean Air Act. These controls are applicable to federal facilities such as the Hanford Site. Washington Administrative Code (WAC) 246-247 requires registration of all radioactive air emission point sources with the DOH. The Hanford Site received a state license for emissions based on this registration. The conditions specified in the license will be incorporated into the upcoming Hanford air operating permit, required by Title V of the Clean Air Act and 1990 amendments.

EPA has retained authority in Washington State for regulating certain hazardous pollutants under the National Emission Standards for Hazardous Air Pollutants (NESHAP), in accordance with 40 CFR 61. These standards are designed to protect the public from hazardous air pollutants (for example, arsenic, asbestos, beryllium, mercury, radionuclides, and vinyl chloride).

Pursuant to this program within the Clean Air Act, the EPA has promulgated regulations specifically addressing asbestos emissions. These regulations apply at the Hanford Site in building demolition and/or disposal and waste disposal operations. Of the approximately 1,400 facilities on the Hanford Site, 456 facilities currently contain asbestos. During 1994, approximately () of asbestos were removed and disposed of in the Hanford Central Landfill in accordance with applicable regulations.

Revised Clean Air Act requirements for radioactive air emissions were issued in December 1989 under 40 CFR 61, Subpart H. Emissions from the Hanford Site are within the new EPA offsite emission standards of 10 mrem/yr (effective dose equivalent). The 1989 requirements for flow and emissions measurements, quality assurance, and sampling documentation are in the process of being implemented at all Hanford Site sources.

These specific reporting and monitoring requirements necessitate additional effort. The Richland Operations Office received a 2-year compliance extension for the Subpart H requirements until December 1991. During this extension period, evaluations were conducted to determine the need for any additional continuous sampling equipment and other actions to meet EPA criteria. Negotiations continued with the EPA in 1992 and 1993. In February 1993, the DOE Richland Operations Office received a Compliance Order and Information Request from EPA, Region 10. The Order required 1) evaluation of all radionuclide emission points on the Hanford Site to determine which are subject to continuous emission measurement requirements in 40 CFR Part 61, Subpart H, and 2) continuous measurement of radionuclide emissions in accordance with 40 CFR Part 61.93. DOE Richland Operations Office submitted a compliance plan to the EPA, Region 10, in April 1993. The compliance plan included, as one of its milestones, the requirement to develop a Federal Facility Compliance Agreement. In February 1994, the NESHAP Federal Facility Compliance Agreement for the Hanford Site was approved. This agreement was signed by the EPA, Region 10, and DOE Richland Operations Office. It provides a compliance plan and schedule to bring the Hanford Site into compliance with the Clean Air Act, as amended, and its implementing regulations in 40 CFR Part 61, NESHAP; Radionuclides.

Title VI of the Clean Air Act Amendments of 1990 requires regulation for the use and disposal of ozone-depleting substances through the requirements in 40 CFR Part 82. The Site operating and engineering contractor was assigned the lead by a DOE Richland Operations Office directive to coordinate the development of a sitewide plan to implement the Title VI requirements. Ozone-depleting substance management on the Hanford Site is administered through a sitewide implementation plan prepared and issued during 1994. This implementation plan will be updated periodically to reflect changing federal regulations.

The local air authority, Benton County Clean Air Authority, enforces Regulation 1, which pertains to detrimental effects, fugitive dust, incineration products, open burning, odor, opacity, asbestos disposal, and sulfur oxide emissions. They have been delegated the authority to enforce EPA asbestos regulations under NESHAP. In 1994, the Site was in compliance with the regulations.

During 1994, Hanford Site air emissions remained below all regulatory limits set for radioactive and other pollutants. Routine reports of air emissions were provided to each air quality agency in accordance with requirements.

Department of Health Enforcement Inspections

DOE and its Hanford contractors are working to resolve outstanding compliance findings from DOH inspections. Each of these notices lists specific violations. There were five DOH notices in 1994. A brief summary of these inspection findings follows.

Clean Water Act

The Clean Water Act applies to point discharges to waters of the United States. At the Hanford Site, the regulations are applied through National Pollutant Discharge Elimination System permits governing effluent discharges to the Columbia River.

The number of active outfalls operating within permit number WA-000374-3 has been reduced from eight to four over the past year. The active outfalls are located in the 100-K Area (outfall 004), the 100-N Area (N-Springs and outfall 009), and the 300 Area (outfall 003). A new permit, number WA-002591-7, was issued for the 300 Area Treated Effluent Disposal Facility, which became operational in December 1994. No instances of noncompliance occurred during 1994.

Liquid Effluent Consent Order

Washington State Department of Ecology Liquid Effluent Consent Order regulating Hanford Site liquid effluent discharges to the ground contains compliance milestones for Hanford Site liquid effluent streams designated as Phase I, Phase II, and Miscellaneous Streams. State waste discharge permit applications have been submitted to Ecology for all liquid effluent streams identified within the Consent Order. A total of ten permit applications have been submitted to the State. Currently, Ecology is in the process of preparing and issuing final permits for the 200 Area Treated Effluent Disposal Facility, 200 Area Effluent Treatment Facility, and the 400 Area Secondary Cooling Water Streams.

The Miscellaneous Streams Plan and Schedule was submitted to Ecology for approval, as required by the Consent Order, in December 1994. This plan and schedule addresses how and when the remaining miscellaneous streams will become compliant with State regulations. The Plan and Schedule proposed that four categorical permits be submitted over the next 4 years to ensure the efficient use of both state and federal resources in the permit development.

Lawsuits Filed

Heart of America Northwest et al., filed a lawsuit against both the Site operating and engineering contractor and DOE in early 1992. The suit alleged violations of the Clean Water Act resulting from discharges of pollutants without a permit and for failure to notify the appropriate agencies of releases of hazardous substances from high-level waste tanks. In April 1993, U.S. District Court granted a Motion to Dismiss and dismissed all claims made by the plaintiffs. The plaintiffs appealed to the Ninth District Circuit Court of Appeals in October 1993. The United States Court of Appeals for the Ninth Circuit dismissed this case in January 1995.

In July 1993, a class-action lawsuit was filed against the current Site operating and engineering contractor and Westinghouse Electric Corporation in Yakima Superior Court in Yakima, Washington. The plaintiffs are seeking damages to provide medical monitoring and an injunction against further discharges to the environment. The federal court has dismissed all claims against the current operating and engineering contractor. DOE has consolidated the defenses for litigation purposes.

Safe Drinking Water Act

The National Primary Drinking Water Regulations of the Safe Drinking Water Act apply to the drinking water supplies at the Hanford Site. These regulations are enforced by the DOH. The Hanford Site water supplies are monitored for the contaminants listed in the rules and regulations of the DOE regarding public water systems. In 1994, all drinking water systems on the Site were in compliance with requirements and agreements. There are currently six Group A and six Group B water systems at Hanford. The Group A systems consist of five surface water systems and one ground water system; the Group B systems consist of two surface water systems and four ground water systems. A study is currently being performed that will validate the water's quality for the five Group A surface water systems onsite. The study will include measurements of chlorine concentration, temperature, and pH.

Toxic Substances Control Act

The application of Toxic Substances Control Act (TSCA) requirements to the Hanford Site essentially involves regulation of polychlorinated biphenyls (PCBs). Federal regulations for use, storage, and disposal of PCBs are found in 40 CFR 761. State of Washington dangerous waste regulations for managing PCB wastes are listed in WAC 173-303.

Various concentrations of PCBs are found in electrical equipment throughout the Hanford Site. The majority of transformers have been sampled and characterized. Nineteen PCB transformers (those with a PCB concentration greater than 500 ppm) remain in service. Schedules have been developed for removing these PCB transformers.

Defueled, decommissioned submarine reactor compartments shipped by the U.S. Navy to the Hanford Site for disposal contain small quantities of PCBs bound within the matrix of nonmetallic materials such as thermal insulation, electrical cables, and some synthetic rubber items. Because PCBs are present, the reactor compartments are regulated under this Act. A compliance agreement between EPA and DOE defines the process by which a chemical waste landfill approval under this Act will be issued for the disposal trench. The EPA Region 10 will grant a TSCA authorization for the disposal site after the State has issued a dangerous waste permit. The reactor compartments are currently stored in the trench without being covered by soil.

Nonradioactive PCB waste is stored and disposed of in accordance with the 40 CFR 761 requirements. Effective nationwide treatment and disposal capacity and technologies have not been developed for radioactive PCB waste. This waste remains in storage on the Site pending the development of adequate treatment and disposal technologies and capacities. A draft DOE-wide Federal Facilities Compliance Agreement allowing the storage of radioactive PCB wastes beyond the regulatory limit has been developed and is in the review cycle.

Federal Insecticide, Fungicide, and Rodenticide Act

The Washington State Department of Agriculture (WSDA) administers the Federal Insecticide, Fungicide, and Rodenticide Act of 1975 certification and storage requirements under authority granted by EPA. The Act and the Revised Code of Washington 17.21, Washington Pesticide Application Act, as implemented by WAC 16-228, "General Pesticides Regulations," apply to storage and use of pesticides. At the Hanford Site, pesticides are applied by personnel licensed by WSDA as commercial pesticide applicators. In 1994, the Hanford Site was in compliance with the Act's requirements and WAC 16-228 regulations pertaining to storage and application of pesticides.

Endangered Species Act

A few rare species of native plants and animals are known to occur on the Hanford Site. Two of these are listed by the U.S. Fish and Wildlife Service as endangered or threatened. Others are listed by the Washington State Department of Fish and Wildlife as endangered, threatened, or sensitive species (see Appendix G). The Site wildlife monitoring program is discussed in Section 4.2, "Wildlife."

Bald eagles, a threatened species, are seasonal visitors to the Hanford Site. Over the past years, several bald eagles have begun nesting onsite. In compliance with the Bald Eagle Management Plan for the Hanford Site and Section 7 of the Endangered Species Act, access roads in the nesting areas are closed in the early spring to protect the nesting environment.

In 1993, the Richland Operations Office directed that an ecological review be conducted on all projects both on and off the Site that have the potential to affect the biological environment. The scope of the review includes evaluating whether any species protected by the Act occur in a proposed project area, quantifying any impacts that might result, and identifying mitigation to minimize or eliminate impacts. Reviews have been conducted on an ongoing basis. There were no additional compliance issues during 1994.

National Historic Preservation Act, Archaeological Resources Protection Act, Native American Graves Protection and Repatriation Act, and American Indian Religious Freedom Act

Cultural resources on the Hanford Site are subject to the provisions of these four Acts. Compliance with the applicable regulations is accomplished through an active management and monitoring program that includes a review of all proposed projects to assess potential impacts on cultural resources, periodic inspections of known archaeological and historical sites to determine their condition and eligibility for listing on the National Register of Historic Places, determination of the effects of land management policies on the sites, and management of a repository for federally owned archaeological collections. In 1994, 511 reviews and inspections were conducted on the Hanford Site.

The American Indian Religious Freedom Act requires federal agencies to help protect and preserve the rights of Native Americans to practice their traditional religions. The Richland Operations Office cooperates with Native Americans by providing Site access for organized religious activities.

There were no additional compliance issues during 1994.

National Environmental Policy Act

The National Environmental Policy Act (NEPA) requires preparation of an Environmental Impact Statement (EIS) to review the effects and alternatives for any major federal action that has the potential to significantly impact the quality of the human environment. Other NEPA documents include the environmental assessment, which is prepared to determine if a proposed action has a potential to significantly impact the environment and therefore requires preparation of an EIS. NEPA documents are prepared and reviewed in accordance with the Council on Environmental Quality regulations (40 CFR 1500 to 1508), 10 CFR 1021, and DOE Order 5440.1E (dated November 1992).

Recently Approved Environmental Impact Statements

The final EIS, Decommissioning of Eight Surplus Production Reactors at the Hanford Site, Richland, Washington (DOE 1992a) was recently approved. This EIS assessed potential environmental impacts of decommissioning eight water-cooled, graphite-moderated reactors on the Hanford Site. The EIS evaluated five alternatives including immediate one-piece removal, safe storage followed by deferred dismantlement, and in situ decommissioning. The scope of this EIS does not include decommissioning of the N Reactor.

The final EIS was issued as an addendum to the draft EIS in December 1992. The record of decision was published in the Federal Register in September 1993 (58 FR 48509). DOE has decided on safe storage followed by deferred one-piece removal of these eight surplus production reactors at the Hanford Site. DOE intends to complete this decommissioning action consistent with the proposed Hanford cleanup schedule for remedial actions included in the Tri-Party Agreement. Therefore, the safe storage period would be shorter than the 75 years outlined in the final EIS. Until decommissioning is initiated, DOE will continue to conduct routine maintenance, surveillance, and radiological monitoring activities to ensure continued protection of the public and the environment during the safe-storage period.

Environmental Impact Statements in Progress

Several related programmatic and site-specific EISs are in progress. One is the Programmatic Environmental Impact Statement, DOE Headquarters, Office of Environmental Restoration and Waste Management. The purpose of this EIS is to evaluate a broad range of alternatives for the configuration of new and expanded waste management facilities. It could include actions for remediations, compliance with RCRA and CERCLA, restoration, waste management, and repositories. The notice of intent was published in the Federal Register (55 FR 42633) in October 1990. DOE Headquarters issued an implementation plan for public comment in 1992 (DOE 1992a).

Another EIS in progress is the Weapons Complex Reconfiguration Modernization Programmatic Environmental Impact Statement, DOE Headquarters, Office of Defense Programs. The purpose of this programmatic EIS is to evaluate alternative approaches for reconfiguring the DOE defense program and its facilities, on both a programmatic and site-specific level. With the end of the Cold War, the U.S. is reducing its stockpile of nuclear weapons. This reduction requires DOE to reevaluate its earlier alternatives for reconfiguring the nuclear weapons complex. A revised notice of intent was published in the Federal Register in July 1993 (58 FR 39528). Significant changes include the addition of consolidated long-term storage facilities for plutonium and uranium, and consolidation of all weapons-complex functions at one site. The Nevada Test Site has been proposed as a new candidate site, and the Hanford Site was dropped from further consideration. The scope is continuing to be reviewed.

Another EIS is the DOE Programmatic Spent Nuclear Fuel Management and Idaho National Engineering Laboratory Environmental Restoration and Waste Management Programs EIS. The purpose of the programmatic part of this EIS is to evaluate alternatives for the management of spent nuclear fuel within the DOE complex. The EIS will evaluate the use of several sites, including Hanford, as potential sites for spent nuclear fuel storage. This EIS is on an accelerated schedule. The EIS will also evaluate environmental and waste management issues at the Idaho National Engineering Laboratory. In August 1993, Hanford was requested to support the preparation of this EIS. DOE issued the draft EIS in June 1994, and the final EIS in April 1995.

Site-Specific Environmental Impact Statements In Progress

The National Parks Service released a final EIS in June 1994 that covers options for the future management of the Hanford Reach of the Columbia River. The agency's proposed action is to make Hanford's North Slope a National Wildlife Refuge and to designate the Hanford Reach as a recreational river under the Wild and Scenic River system. This would transfer responsibility for the river, a 0.4 km (0.25 mi)-wide strip of land on both shores, and the North Slope, to the U.S. Fish and Wildlife Service. The Richland Operations Office would retain responsibility for remediation and Hanford Site security. A record of decision has not yet been issued.

The Tank Waste Remediation System EIS has its origin in two DOE decisions. The first was an October 1990 commitment by the Secretary of Energy to prepare a supplemental EIS to the Hanford Defense Waste EIS (DOE 1987a) to address tank management and safety issues. The second was a December 1991 decision by the Secretary of Energy to revise the entire tank safety/tank waste treatment and disposal program and to accelerate retrieval of single-shell tank wastes. This EIS combines the scope of the originally planned supplemental EIS and the tank safety mitigation/remediation issues EIS. The notice of intent (59 FR 4052) was published in the Federal Register in January 1994. Public scoping was conducted during February and March of 1994.

An EIS is also underway for a proposed Multi-function Waste Tank Facility. The EIS will review potential environmental impacts associated with the construction and operation of six new 3.8 million L (1 million gal) double-shell waste tanks. The notice of intent in January 1994 for the Tank Waste Remediation System EIS also included the new tanks. The new tanks will be addressed under NEPA by an interim action EIS. In July 1994, the implementation plan and the draft EIS for the Safe Interim Storage of Hanford Tank Wastes were released for public review and comment.

Potential environmental impacts of CERCLA and RCRA past-practices remediation activities at the Hanford Site, particularly cumulative impacts, will be assessed in the Hanford Remedial Action EIS. This EIS will cover environmental restoration of past-practices liquid effluent disposal sites, buried solid low-level wastes, pre-1970 transuranic wastes, high-activity wastes associated with storage tanks and their piping, and miscellaneous dangerous and nondangerous waste sites. Additional NEPA documentation could be prepared, as needed, for specific remediation of individual operable units or construction of waste management facilities. The Hanford Remedial Action EIS will not make site-specific level-of-cleanup decisions. Instead, the final decision on this EIS may establish future site use objectives that in turn support the regulatory framework for establishing individual waste site cleanup levels. The scope of this EIS will be clear once the implementation plan is issued. The notice of intent was published in the Federal Register during August 1992. The final decision on this EIS is targeted for 1995.

Planned Environmental Impact Statements

Several EIS are currently being planned. An EIS addressing the proposed operation of the Plutonium Finishing Plant to stabilize reactive materials is being prepared. An environmental assessment was originally prepared regarding the proposed scope. However, the scope of the project was changed in 1993, resulting in an announcement of the preparation of an EIS for terminal cleanout. A notice of intent has been published. An interim action environmental assessment was published in 1994 for the Plutonium Reclamation Facility stabilization.

Another EIS is anticipated for spent nuclear fuel at the Hanford Site. The EIS would support implementation of the final decision that is expected to be made in the record of decision in June 1995 for the DOE programmatic spent nuclear fuel EIS.

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