ML23103A448
| ML23103A448 | |
| Person / Time | |
|---|---|
| Site: | South Texas |
| Issue date: | 04/13/2023 |
| From: | Morgan J South Texas |
| To: | Office of Nuclear Reactor Regulation, Document Control Desk |
| References | |
| NOC-AE-23003952 | |
| Download: ML23103A448 (1) | |
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Nuclear Operating Company South Texas Project Electric Generating Station P.O Box 289 Wadsworth. Texas 77483 ------------VVV'v-ATTN: Document Control Desk U.S. Nuclear Regulatory Commission Washington, DC 20555-0001 South Texas Project Units 1 and 2 Docket Nos. 50-498; 50-499 South Texas Project Electric Generating Station 2022 Annual Environmental Operating Report April 13, 2023 NOC-AE-23003952 10 CFR 50.36b STI: 35454866 Pursuant to the South Texas Project Environmental Protection Plan (Non-radiological) and Technical Specification 6.9.1.3, the STP Nuclear Operating Company provides the attached South Texas Project Electric Generating Station 2022 Annual Environmental Operating Report.
There are no commitments in this letter.
If there are any questions about this report, please contact Zachary Dibbern at (361) 972-4336 or me at (361) 972-4045.
~
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Manager, Health Physics
Attachment:
South Texas Project Electric Generating Station 2022 Annual Environmental Operating Report cc:
Regional Administrator, Region IV U.S. Nuclear Regulatory Commission 1600 E. Lamar Boulevard Arlington, TX 76011-4511
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT SOUTH TEXAS PROJECT ELECTRIC GENERATING STATION 2022 ANNUAL ENVIRONMENTAL 2022 ANNUAL ENVIRONMENTAL OPERATING REPORT OPERATING REPORT
TABLE OF CONTENT S Figure 2-1: Plant Water Systems.... 2-4 Figure 4-1: 2022 Non-radioactive Waste Management......... 4-9 Figure 4-2: 2022 Non-radioactive Waste Generation......... 4-9 Figure 4-3: Hazardous Waste Shipped Historical Comparison..... 4-9 Figure 6-1: Radiological Environmental Monitoring Program Designated Sample Location Map........... 6-3 Figure 6-2: Radiological Environmental Monitoring Program Onsite Sample Location Map........... 6-4 Figure 6-3: Radiological Environmental Monitoring Program Zone Location Map. 6-5 Figure 6-4: Historical Comparison of Average Quarterly Beta Activity from Indicator and Control Air Samples.... 6-6 Figure 6-5: Environmental Dosimeter Comparisons....... 6-7 Figure 6-6: Historical Comparison of Cobalt-60 in Main Cooling Reservoir Sediment......... 6-7 Figure 6-7: Calculated Cumulative Curies of Cobalt-60 in the Main Cooling Reservoir. 6-7 Figure 6-8: Historical Comparison of Tritium Added to and Remaining in the Main Cooling Reservoir...... 6-9 Figure 6-9: Historical Comparison of Tritium Activity in Reservoir Relief Wells.. 6-9 Figure 6-10: Historical Comparison of Tritium Activity in Surface Water.... 6-11 Figure 6-11: Historical Comparison of Tritium Activity in Shallow Aquifer Ground Water. 6-11 Figure 6-12: Tritium Activity in Shallow Ground Water West of the Main Cooling Reservoir. 6-13 Figure 6-13: STP Protected Area Ground Water Monitoring Wells Results.... 6-15 Figure 6-14: STP Protected Area Ground Water Monitoring Wells.... 6-15 Figure 6-15: 2022 Radiological Laboratory Quality Assurance Program Performance. 6-17 Figure 6-16: Duplicate & Split Agreement of Environmental Samples in 2022... 6-17 FIGURES Table 1: Radiological Environmental Monitoring Program...... 6-19 to 6-21 Table 2: Sample Media and Location Descriptions..... 6-23 to 6-27 Table 3: 2022 Radiological Environmental Monitoring Program Analysis Summary...... 6-30 to 6-38 TABLES CHAPTER ONE EXECUTIVE
SUMMARY
............. 1-1 CHAPTER TWO SITE AND AREA DESCRIPTION........... 2-1 CHAPTER THREE NON-RADIOLOGICAL ENVIRONMENTAL INTRODUCTION AND
SUMMARY
............. 3-1 CHAPTER FIVE RADIOLOGICAL ENVIRONMENTAL INTRODUCTION AND
SUMMARY
............. 5-1 CHAPTER SIX RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT.............. 6-1 Program Description............. 6-2 Airborne Pathway.............. 6-6 Direct Exposure Pathway.......... 6-6 Sediment Samples.............. 6-8 Waterborne Pathway............ 6-10 NEI Groundwater Protection Initiative.. 6-15 Land Use Census............... 6-16 Quality Assurance.............. 6-18 Program Deviations............. 6-18 Radiological Environmental Monitoring Program Analysis Summary........ 6-29 CHAPTER FOUR NON-RADIOLOGICAL ENVIRONMENTAL INTRODUCTION AND
SUMMARY
............. 4-1 Environmental Conditions.......... 4-2 Aquatic and Ecological Monitoring..... 4-2 Water Quality Management......... 4-3 Air Quality Management........... 4-7 Non-radioactive Waste Management... 4-8 Chemical Control and Management... 4-10 Environmental Protection Plan Status.. 4-11 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT INTRO l OVERVIEW The 2022 Annual Environmental Operating Report for the South Texas Project Electric Generating Station combines in one report the requirements for the Annual Environmental Operating Report (Non-radiological) found in Appendix B to the renewed Facility Operating License No. NPF-76 and No. NPF-80 and the requirements for the Annual Radiological Environmental Operating Report found in Part A of the stations Offsite Dose Calculation Manual.
SOUTH TEXAS PROJECT ELECTRIC GENERATING STATION 2022 ANNUAL ENVIRONMENTAL OPERATING REPORT Completed in accordance with Technical Specifications for United States Nuclear Regulatory Commission l Renewed License No. NPF-76 and No. NPF-80 l April 2023 Authored by:
Laura Stoicescu, CHP Consulting Health Physicist, Health Physics Division Technical Review:
Edmond Hardcastle Jr.
Staff Environmental Radiological Services Specialist Health Physics Division Authored by:
Kenneth M. Cunningham Environmental Supervisor, Regulatory Affairs Approved by:
Jonah Morgan Manager, Health Physics Division Photo courtesy of Christie Dement
STP l ANNUAL ENVIRONMENTAL OPERATING REPORT
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT Photo courtesy of Christie Dement Photo courtesy of Christie Dement For over thirty years, STP has produced safe, carbon-free, clean-air energy at our site in beautiful Matagorda County with great respect and admiration for the land, water and air we all share.
Matagorda County prides itself on the beauty and variety of the ecosystems and wildlife that thrive here. It harbors a unique convergence of those ecosystems, including secluded, extensive forests, waterways, riparian wetlands, an expansive prairie and 40 miles of beautiful, wild coastline. Its uniqueness as prime habitat for wildlife is evidenced by it being consistently named as the county with the greatest variety of migratory birds than in any other county in the United States. STP is committed to caring for the natural resources with which we have been entrusted. We want Matagorda County residents to know that STPs dedication to protecting the environment will not diminish, and it is our great privilege to operate on this land that we all call home. Transparency in our environmental operations is a key element to maintaining our trust and good relationship with our community. This report exemplifies our dedication to maintaining this open communication.
Thank you for allowing us to continue to be your trusted neighbor. We look forward to serving this community and being a steward of our environment for many years to come.
Tim Powell President and CEO STP Nuclear Operating Company M E S S A G E F R O M T H E P R E S I D E N T A N D C E O MESSAGE l FROM THE PRESIDENT AND CEO
EXECUTIVE
SUMMARY
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT CHAPTER 0NE l EXECUTIVE
SUMMARY
1-2 The South Texas Project Electric Generating Station (South Texas Project) continues to operate with no adverse effect on the population or the environment. The dose equivalent for people living in the area remains at less than one millirem per year.
Environmental programs at the site monitor known and predictable relationships between the operation of the South Texas Project and the surrounding area. These monitoring programs verify that the operation of the South Texas Project has no impact offsite and is well below state and federal regulations and guidelines.
These programs are verified by the State of Texas through collection and analysis of samples and placement of the States monitoring dosimeters and other onsite and offsite inspections.
This report describes the environmental monitoring programs, non-radiological and radiological, conducted at the South Texas Project during 2022. Included in this report are the Environmental Protection Plan Status, the results of the Radiological Environmental Monitoring Program, and the Land Use Census.
Non-radiological environmental monitoring is performed each year as part of the stations overall Environmental Protection Plan which is intended to provide for protection of non-radiological environmental parameters during station operations.
Non-radiological monitoring encompasses, as a minimum, water quality, air quality, waste generation and minimization, and local aquatic and terrestrial ecological conditions. In 2022, non-radiological monitoring by the station confirmed that the South Texas Projects efforts to respect and protect local environmental conditions were successful. The operation of South Texas Project continued to provide high-quality habitat areas for a variety of flora and fauna and continued to have no indications of negative non-radiological impacts to local environmental conditions.
The environment within a 15-mile radius of the South Texas Project is routinely monitored for radiation and radioactivity. Sampling locations are selected using weather, land use, and water use information. Two types of sampling locations are used. The first type, Control Stations, are located in areas that are beyond the measurable influence of the South Texas Project CHAPTER ONE Photo courtesy of Gary Parkey Photo courtesy of Gary Parkey Photo courtesy of Gary Parkey
1-3 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT or any other nuclear facility. The sample results from these stations are used to explain radiation from sources other than the South Texas Project. Indicator Stations are the second type of station.
The samples from these stations measure any radiation contributed to the environment that could be caused by the South Texas Project. Indicator Stations are located in areas close to the South Texas Project where any plant releases would be detected.
Prior to initial operation of the South Texas Project, samples were collected and analyzed to determine the amount of radioactivity present in the area.
These results are used as a pre-operational baseline. Results from the Indicator Stations are compared to both current control sample results and the pre-operational baseline values to determine if changes in radioactivity levels are attributable to station operations or other causes such as previous nuclear weapons testing programs and natural variations.
Radioactivity levels in the South Texas Projects environment frequently fall below the minimum detection capabilities of state-of-the-art scientific instruments. Samples with radiation levels that cannot be detected are below the Lower Limits of Detection.
The United States Nuclear Regulatory Commission requires that equipment used for radiological monitoring must be able to detect specified minimum limits for certain types of samples. This ensures that radiation measurements are sufficiently sensitive to detect small changes in the environment.
The United States Nuclear Regulatory Commission also has a required reporting level. Licensed nuclear facilities must prepare a special report and increase their sampling if any measured radiation level is equal to or greater than this reporting level.
No sample from the South Texas Project has ever reached or exceeded this reporting level. Measurements performed are divided into four categories, or pathways, based upon how the results may affect the public.
Airborne, waterborne, ingestion, and direct radiation are the four pathways that are sampled. Each pathway is described on page 1-4.
The South Texas Project continues to operate with no adverse effect on the population or the environment.
The dose equivalent for people living in the area is maintained at less than one millirem per year. Environmental programs at the site monitor known and predictable relationships between the operation of the South Texas Project and the surrounding area.
These monitoring programs verify that the operation of the South Texas Project has no impact offsite and is well within state and federal regulations and guidelines. These programs are verified by United States Nuclear Regulatory Commission inspections and the State of Texas through collection and analysis of samples and state radiation monitoring dosimeters.
Photos courtesy of 1. Greg McMullin, 2. & 3. Drew Richards
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT CHAPTER 0NE l EXECUTIVE
SUMMARY
1-4
- The airborne pathway is sampled in areas around the South Texas Project by measuring the levels
of radioactive iodine and particulate radioactivity on air filters. The 2022 airborne results were similar to pre-operational levels detecting only naturally occurring radioactive material unrelated to the operation of the South Texas Project.
- The waterborne pathway includes samples taken from surface water, groundwater, and drinking water. Also included in this pathway are sediment samples taken from the Main Cooling Reservoir and the Colorado River. Tritium was the only man-made nuclide consistently detected in water samples and was measured in the shallow aquifer, the Main Cooling Reservoir, ditches, and sloughs consistent with the South Texas Project Main Cooling Reservoir operating design. The levels of Tritium found were near or lower than the concentration of Tritium in the Main Cooling Reservoir. Additional onsite wells have been sampled to map Tritium migration. The average Tritium level in the Main Cooling Reservoir remained stable throughout 2022. Tritium levels remain well below United States Nuclear Regulatory Commission Each of the four pathways reporting limits and within United States Environmental Protection Agency drinking water standards.
Previously detected plant-related nuclides, such as cobalt-60 and cesium-137, were detected in the reservoir sediment at designated sample locations at very low concentrations. Additional samples had detectable cesium-137 which is normally present in the environment and is consistent with pre-operational concentrations.
Onsite sediment samples continue to occasionally indicate traces of plant-related nuclides such as cobalt-60. Offsite sediment samples continue to show no radioactivity from the South Texas Project. In summary, the station produced no detectable waterborne effects offsite.
- The ingestion pathway includes broadleaf vegetation, agricultural products, and food products. Naturally occurring nuclides were detected at average environmental levels in the samples. The data indicated there were no man-made nuclides detected in these types of samples.
- The direct exposure pathway measures environmental radiation doses using thermoluminescent dosimeters.
These results are consistent with the readings from previous years and pre-operational measurements indicating no effect from South Texas Project operations.
Photo courtesy of Christie Dement
SITE AND AREA DESCRIPTION 2-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT CHAPTER TWO l SITE AND AREA DESCRIPTION 2-2 The South Texas Project is located on 12,220 acres in Matagorda County, Texas, approximately 15 miles southwest of Bay City along the west bank of the Colorado River. The South Texas Project is owned by NRG South Texas LP, City of Austin, and City Public Service Board of San Antonio as tenants in common. Houston Lighting & Power Company was the original project manager of the South Texas Project and was responsible for the engineering, design, licensing, construction, startup, and initial commercial operation of the two-unit facility. In 1997, the STP Nuclear Operating Company assumed operational control of the South Texas Project and responsibility for implementation of associated environmental programs.
The South Texas Project has two Westinghouse pressurized water reactors. The rated core thermal power of each unit is 3,853 megawatts-thermal (MWt). Each unit was originally designed for a net electrical power output of 1,250 megawatts-electric (MWe). Unit 1 received a low-power testing license on August 21, 1987, achieved initial criticality on March 8, 1988, and was declared commercially operational on August 25, 1988. Unit 2 received a low-power testing license on December 16, 1988, achieved initial criticality on March 12, 1989, and was declared commercially operational on June 19, 1989. On September 28, 2017, the United States Nuclear Regulatory Commission approved the South Texas Projects request to extend the operating licenses an additional twenty years through 2047 and 2048.
The combined units currently produce enough electricity to serve more than two million homes and businesses throughout Texas. With approximately 1,000 baseline employees, the STP Nuclear Operating Company is the largest employer and source of revenue for Matagorda County. Nuclear energy continues to provide long-term cost stability and promote energy independence. It is our nations largest source of carbon-free energy. As we work collectively to secure our states long-term energy future, nuclear energy will continue to play an important role as a safe and reliable supply of clean baseload electricity.
Fossil-fueled and nuclear-powered steam generating plants operate on the same principle. Fuel is used to produce heat to convert water into high-pressure steam. The steam is directed through a turbine to turn a generator. In a fossil fuel plant, either coal, lignite, oil, or natural gas is burned in a boiler to produce the heat. In a nuclear plant, the reactor replaces the boiler and the fissioning or splitting of uranium atoms inside the reactor produces the heat.
The fuel for a nuclear reactor is uranium. It is formed into cylindrical ceramic pellets, each about the size of the end of your little finger. One pellet has the energy potential of about a ton of coal. Millions of these pellets are stacked in fuel rods that are arranged into assemblies that make up the core of the reactor. The use of uranium allows us to conserve natural gas, oil, and coal and to avoid the associated production of greenhouse gases.
The fission process and generation of usable heat begins in a nuclear reactor when control rods in the core are withdrawn. In pressurized water reactors, like those at the South Texas H O W T H E S O U T H T E X A S P R O J E C T W O R K S CHAPTER T WO Photo courtesy of Christie Dement Photos courtesy of Greg McMullin
2-3 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT Project, the fuel rods heat water circulating in sealed, stainless-steel piping that passes through large heat exchangers called steam generators.
The water in the reactor is under pressure to prevent boiling. This is why the South Texas Projects Units 1 and 2 reactors are called pressurized water reactors.
This hot, pressurized water heats a separate supply of water in the steam generators to produce steam that is directed through the blades of a turbine generator to produce electricity. The steam is then fed to a condenser where a separate supply of cooling water from the Main Cooling Reservoir condenses it back into water that is then pumped back to the steam generator for reuse.
A diagram of the plant water systems is shown in Figure 2-1.
In addition to its safety systems, the South Texas Project has many built-in physical barriers designed to prevent the release of radioactive materials in the unlikely event of an accident. The most visible ones are the 200-foot tall, domed containment buildings with steel reinforced concrete walls four feet thick. Inside each of these massive structures, two more concrete walls provide another 11 feet of radiation shielding. The reactor vessel itself has steel walls six inches thick, and the fuel pellets inside it are sheathed in hardened metal tubes.
Nuclear energy has one of the lowest impacts on the environment. It is the most eco-efficient energy source because it produces the most electricity in relation to its minimal environmental impact. 1Nuclear power plants generate approximately 50 percent of the carbon-free electricity generated in the United States. Additional information on nuclear energy and the environment can be found on the website maintained by the Nuclear Energy Institute at www.nei.org.
1Nuclear Energy Institute. Nuclear Energy Fast Facts; October 2022. As viewed at www.nei.org/resources/fact-sheets/
nuclear-fast-facts.
Sixty-five of the total 12,220 acres at the South Texas Project are occupied by the two current power plants.
Plant facilities include a 7,000-acre main cooling reservoir and a 47-acre essential cooling pond. Many smaller bodies of water onsite include wetlands, Kelly Lake, drainage ditches, sloughs, and depressions. Much of the land east of the cooling reservoir is leased for cattle grazing. Approximately 1,700 acres remain in a more natural state as a lowland habitat. A 110-acre wetland habitat area was established in 1996 on previously unused land located northeast of the power plants. The area surrounding the South Texas Project is characterized by coastal plain with farmland and pasture predominating.
Local relief of the area is characterized by flat land, approximately 23 feet above sea level.
T H E P L A N T S I T E Photos courtesy of 1. & 2. Greg McMullin, 3. Drew Richards
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT CHAPTER TWO l SITE AND AREA DESCRIPTION 2-4 PLANT WATER SYSTEMS Figure. 2-1 T H E A R E A Matagorda Countys economy is based primarily on ranching, farming, oil and natural gas production and refinement, petrochemical production, electricity generation, and commercial fishing and fisheries. The area within 10 miles of the site is generally rural and characterized as farmland, which is primarily pastureland used for livestock ranching. Although the surrounding area is heavily cultivated, significant amounts of woodlands, thicket, brush, fields, marsh, and open water exist to support wildlife. The area lies in the southern region of the central flyway and is host to an abundance of migratory birds. The local estuary environments provide the necessary habitat for a variety of fish types to complete their life cycles. The area also affords opportunity for recreational hunting and fishing.
The South Texas Project is home to many species of animals. Inhabitants include American alligators, a variety of birds, and several hundred deer. In winter, literally hundreds of thousands of waterfowl, principally migratory geese as well as white pelicans, have found that the plants 7,000-acre cooling reservoir provides a good resting place during their migrations.
The climate of the region is subtropical maritime, with continental influence. It is characterized by short, mild winters and long, hot, and humid summers.
Rainfall normally ranges from about two inches per month in February peaking to about four to five inches per month in May, June, September, and October. The prevailing wind direction is from the south-southeast, shifting to north-northeast for short intervals during the winter months.
NON-RADIOLOGICAL ENVIRONMENTAL INTRODUCTION AND
SUMMARY
3-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT CHAPTER THREE l NON-RADIOLOGICAL ENVIRONMENTAL INTRODUCTION AND
SUMMARY
3-2 Non-radiological environmental conditions and performance at the South Texas Project during 2022 remained satisfactory and demonstrated that the South Texas Project continued to operate in an environmentally responsible manner during the year. The South Texas Project achieved and maintained high standards of environmental performance and compliance throughout 2022.
The South Texas Project is committed to the production of electricity in a safe, reliable, and economical manner using nuclear energy. The stations programs, policies, and business plan objectives also incorporate a commitment to environmental protection and management. The stations commitment to sound environmental management in 2022 is illustrated below.
Everyone at the South Texas Project has a responsibility to protect the environment. Commitment to environmental safety is an integral component of the South Texas Project operating policy and core values. This responsibility reaches further than mere compliance with laws and regulations to encompass the integration of sound environmental practices into our daily operational and business decisions. The people at the South Texas Project understand the need to balance economic, operational, and environmental issues for the benefit of the station and the public.
We recognize our responsibility to hold ourselves to the highest principles of environmental stewardship.
CHAPTER TH REE Photo courtesy of Drew Richards Photos courtesy of 1. & 3. Greg McMullin, 2. Christie Dement 2Per Compliance History Report for CN601658669, RN102395654, Rating Year 2022; as prepared by the Texas Commission on Environmental Quality.
- Satisfactory performance classification2 by the Texas Commission on Environmental Quality based on the stations environmental compliance record in all areas considered, including water quality, waste management, and air quality compliance.
- Continued emphasis on waste minimization and source reduction allowing the station to maintain its classification as a small quantity generator of industrial waste.
- Continued support of community activities such as the annual Matagorda County Household Hazardous Waste Collection Day and hosting Science, Technology, Engineering and Mathematics (STEM) teachers for a summer workshop.
The stations commitment to sound environmental management in 2022
NON-RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT 4-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT CHAPTER FOUR l NON-RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT 4-2 CHAPTER FOUR E N V I R O N M E N TA L C O N D I T I O N S This section of the report describes the South Texas Projects non-radiological environmental program performance and environmental conditions for 2022. The STP Nuclear Operating Company employees closely monitor environmental conditions at the South Texas Project. NRG Energy, Inc. provides support and technical assistance to the South Texas Project.
The Texas Commission on Environmental Quality rated the South Texas Project as a satisfactory performer in 2022 based on the stations environmental compliance record. Facilities, such as the South Texas Project, can be classified by the state as a high performer, satisfactory performer, or unsatisfactory performer based on that facilitys compliance history. The states classification of the South Texas Project as a satisfactory performer was based on the stations environmental performance over the last five-year period.
During the period of this report, the station continued to promote green initiatives including the recycling of paper, plastics, and aluminum by site employees. The station also continued to support various bird counts and surveys in 2022 sponsored by federal and state agencies and volunteer organizations such as the annual National Audubon Society Christmas Bird Count and the United States Fish and Wildlife Services Colonial Waterbird Survey.
AQUATIC AND ECOLOGICAL MONITORING The location of the South Texas Project falls within the Texas Land Resource Area designation as coastal prairie and can be divided into two broad ecological areasbottomland and upland areasbased on topography, soils, and vegetation. The bottomland lowland habitat is a swampy, marshy area that provides an important habitat for birds and other wildlife and occupies approximately 1,700 acres of the site near the Colorado River. An upland spoil containment area, originally constructed in 1972 by the United States Army Corps of Engineers, is included in this area. In addition, a 110-acre wetland habitat area that attracts a variety of bird groups and other wildlife was established in 1996 on previously unused land located northeast of the power plants. The remaining area of the site offers diverse habitats for mammals and several types of birds. The South Texas Project regularly monitors the sites environs for changing conditions. Ecological conditions onsite in 2022 remained generally unchanged and stable.
The South Texas Project is located on the state-sponsored Great Texas Coastal Birding Trail that spans the entire Texas Gulf Coast from Brownsville to the Louisiana border.
Matagorda County, in which the South Texas Project is located, consistently Photo courtesy of Christie Dement Photos courtesy of 1. Gary Parkey, 2. & 3. Greg McMullin
4-3 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT ranks at or near the top of the National Audubon Societys Annual Christmas Bird Count for the number of species identified. Many bird species have been observed visiting the wetland habitat and elsewhere onsite. These include the bald eagle, white-faced ibis, and brown pelican. Additional migratory and resident bird species such as a variety of ducks, geese, turkey, and pelicans (both brown and white) have been observed during informal surveys of the sites diverse natural and man-made habitats. Intensive bird nesting continues throughout the lowland habitat, particularly in a heron rookery around the perimeter of Kelly Lake and on the internal dikes of the Main Cooling Reservoir at the South Texas Project. The South Texas Project continues to provide vital habitat for more than an estimated 125 species of wintering and resident birds.
The South Texas Project continues to monitor important wildlife species to detect population changes. Informal observations continue to indicate that the site provides high-quality habitat in which a wide range of animals thrive.
The site continues to attract extensive wildlife populations, offering a refuge for resident species as well as seasonal migrants. The lowland habitat located between the Colorado River and the east bank of the Main Cooling Reservoir offers a significant source of water year-round. These natural resource areas, in concert with numerous additional wetland and grassland areas, offer the key ingredients necessary to sustain the extensive wildlife population at the South Texas Project.
WATER QUALITY MANAGEMENT Water is an essential component in electricity production, and electric utilities must comply with extensive federal, state, and local water regulations. These regulations govern virtually every aspect of business operations at the South Texas Project.
Water usage, wastewater treatment onsite and certain maintenance and repair activities are regulated under the Safe Drinking Water Act, the Federal Clean Water Act, and the Texas Water Quality Act. Collectively, these Acts provide for the safeguarding of public drinking water supplies and maintaining the integrity of state and federal waters. Regulating agencies that administer these requirements include the United States Army Corps of Engineers, the United States Environmental Protection Agency, the Texas Commission on Environmental Quality, the Texas General Land Office the Lower Colorado River Authority, and the Coastal Plains Groundwater Conservation District.
The South Texas Project uses both surface water and groundwater for station purposes. Consistent with the stations environmental principles encouraging efficient water usage and conservation, surface and groundwater usage are carefully managed to conserve this important resource.
Groundwater is pumped from deep aquifer wells to provide onsite drinking water for station personnel, to replenish the Essential Cooling Pond, and for other industrial purposes onsite. Water from the Main Cooling Reservoir and the Essential Cooling Pond is used as cooling water for plant operations.
Water from the Colorado River replenishes the Main Cooling Reservoir via intermittent diversion periods.
Surface water diverted to the Main Cooling Reservoir from the Colorado River accounted for approximately 90% of the water used at the South Texas Project in 2022. Information regarding water use in Texas can be found on the website maintained by Photos courtesy of 1. & 3. Greg McMullin, 2. Kelly Callais
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT CHAPTER FOUR l NON-RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT 4-4 the Texas Water Development Board at www.twdb.texas.gov.
Most of the water used by the South Texas Project is needed to condense steam and provide cooling for plant generating systems. The majority of this water is drawn from and returned to the stations Main Cooling Reservoir.
The Main Cooling Reservoir is a 7,000-acre, above grade, off-channel reservoir capable of impounding 202,600 acre-feet of water at its maximum level. Water is diverted intermittently from the adjacent Colorado River to replenish the Main Cooling Reservoir.
In addition, the Essential Cooling Pond, a 47-acre, below grade, off-channel reservoir that supplies water to cool crucial plant components, is capable of impounding 388 acre-feet of water. Various water rights permits, contractual agreements, and compliance documents authorize the South Texas Project to maintain these reservoirs, impound water diverted from the Colorado River, and to circulate, divert, and use water from the reservoirs for industrial purposes to operate the plant. These authorizations also limit the amount and rate of diversion from the Colorado River to protect downstream environmental flow requirements for bays and estuaries. The South Texas Project diverted 9,555 acre-feet in 2022 from the Colorado River for Main Cooling Reservoir fill operations while preserving adequate freshwater flow conditions for downstream bay and estuarine ecosystems. Approximately 1,080 acre-feet of the water used by the station was withdrawn from onsite groundwater sources in 2022.
Existing federal and state water quality standards are implemented and enforced through the Texas Pollutant Discharge Elimination System (TPDES) permit program to restore and maintain the states waters. Under this permit program, the South Texas Project monitors, records, and reports the types and quantities of pollutants from wastewater discharges to ensure that the South Texas Project meets the stringent levels set in the permit. The TPDES permit was renewed in 2020. A monthly monitoring report is submitted to the Texas Commission on Environmental Quality for wastewater discharges. Reports identifying groundwater use, surface Photo courtesy of Christie Dement
4-5 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT water use, and water conservation are submitted annually to the Texas Water Development Board. Reports of surface water diversion and consumptive use are submitted to the Texas Commission on Environmental Quality and the Lower Colorado River Authority. An annual groundwater use report is also submitted to the Coastal Plains Groundwater Conservation District in accordance with groundwater district requirements.
Wastewater generated at the South Texas Project is processed and discharged to the onsite Main Cooling Reservoir to be re-used by the station as cooling water for plant systems. No water was discharged from the Main Cooling Reservoir in 2022 other than from the relief wells that are part of the reservoir embankment stabilization system. No aquatic monitoring was required to be conducted at the site in 2022 by the United States Environmental Protection Agency or the Texas Commission on Environmental Quality. Wastewater discharges met state and federal water quality standards during the year, while conserving and maximizing efficient water usage at the South Texas Project. In addition to the wastewater discharge permit program, the Federal Clean Water Act, as amended, requires permits for storm water discharges associated with industrial activity. The South Texas Projects Storm Water Pollution Prevention Plan ensures that potential pollution sources at the site are evaluated and that appropriate measures are selected and implemented to prevent or control the discharge of pollutants in storm water runoff. This plan is a document that is revised whenever there is a change in design, construction, operation, or maintenance that has a significant effect on the potential for the discharge of pollutants from the station. The stations Multi-Sector General Permit for storm water discharges was renewed in 2021.
Following a severe drought in 1996, the Texas Legislature recognized the need to address a wide range of state water resource management issues. In 1997, the Texas Senate drafted legislation known as Senate Bill 1 to address these issues and to develop a comprehensive state water policy. The legislation required the Texas Water Development Board to create a statewide water plan that emphasizes regional planning.
Sixteen planning regions were created, each tasked to prepare a plan for the orderly development, management, and conservation of water resources.
The South Texas Project was chosen to represent the interests of electric generating utilities for water-planning Region K, encompassing the lower Photo courtesy of Kelly Callais
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT CHAPTER FOUR l NON-RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT 4-6 Colorado River Basin. A state water plan is prepared by the Texas Water Development Board every five years based on the regional water plans.
The regional water plans are revised each planning cycle based on updated population and water demand projections, water supply analyses, and water management strategies for a water planning horizon out to the year 2070.
In November of 2020, the water plan adopted by the Region K water planning group was submitted to the Texas Water Development Board and was approved in 2021. The South Texas Project continues to actively participate in the Lower Colorado Regional Water Planning Group to identify strategies to meet future water supply demand projections for the region and to update the existing plan accordingly. Additional information regarding regional water planning in Texas can be found on the website maintained by the Texas Water Development Board at www.twdb.texas.gov.
Senate Bill 1 also required groundwater conservation districts to develop groundwater management plans with estimates on the availability of groundwater in the district, details of how the district would manage groundwater, and management goals for the district. The water planning and management provisions were further clarified in 2001 with the enactment of Senate Bill 2. Accordingly, the Coastal Plains Groundwater Conservation District, encompassing Matagorda County, was confirmed by local election in late 2001. The purpose of the district is to manage and protect the groundwater resources of the district.
The South Texas Project groundwater wells are registered with the Coastal Plains Groundwater Conservation District. Operating permits for the groundwater wells will be renewed in January 2023, as required every three years. Station personnel continue to monitor onsite groundwater usage according to the requirements of District rules. Additional information regarding the Coastal Plains Groundwater Conservation District can be found on its website at www.
coastalplainsgcd.com. In 2007, in further recognition of the importance of water conservation to meet future demands in the state, Senate Bill 3, enacted by the Texas Legislature, created a stakeholder-driven process for the development of environmental flows. Environmental flows are the amount of water necessary for a river, estuary, or other freshwater system to maintain its health and productivity. The law established a process to develop environmental flow regime recommendations for each major river basin in Texas. The process tasked a team of stakeholders from each area of the state, working with a science team, to develop a set of recommendations to the Texas Commission on Environmental Quality and to perform ongoing periodic reviews of the recommendations. The South Texas Project participated as a member of the stakeholder committee that included the Colorado River and Matagorda Bay. The environmental flow standards set flow levels at various points in rivers and streams to protect water in the rivers and estuaries along the coast. The existing South Texas Project right to divert surface water was not impacted by this legislation.
Additional information regarding environmental flows can be found at www.tceq.texas.gov/permitting/water_
rights/wr_technical-resources/eflows.
In February 2020, the Texas Commission on Environmental Quality approved a revised Lower Colorado River Authority Water Management Plan. The Lower Colorado River Photos courtesy of Greg McMullin
4-7 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT Authority Water Management Plan determines how water is allocated from the Highland Lakes (specifically Lakes Travis and Buchanan) to meet the needs of water users, including the South Texas Project, during water supply shortages. The process started in 2019 when the Lower Colorado River Authority submitted an updated Water Management Plan to the Texas Commission on Environmental Quality for approval. The South Texas Project participated in the development of the revision for presentation to and approval by the Texas Commission on Environmental Quality. Stakeholders included representatives from cities, industry, lake area businesses and residents, environmental interests, and agriculture. Additional information on the Lower Colorado River Authority Water Management Plan can be found at www.lcra.org.
In 1999, the South Texas Project implemented a station Water Conservation Plan in accordance with state water use regulations. The purpose of the Water Conservation Plan is to identify and establish principles, practices, and standards to effectively conserve and efficiently use available ground and surface water supplies and meet historical and projected average industrial water demand. Annual implementation reports are submitted to the Texas Water Development Board and the plan is updated every five years. The station re-submitted a revised plan to the Texas Water Development Board in 2019. Managers and staff at the South Texas Project understand the water resources of the state are a critical natural resource requiring careful management and conservation to preserve water quality and availability. Accordingly, the station continues to support efforts focusing on the efficient use and conservation of water resources.
AIR QUALITY MANAGEMENT Air emission sources at the South Texas Project fall under the scope of air pollution regulations promulgated under the Texas Clean Air Act, the Federal Clean Air Act and numerous associated amendments. The purpose of these regulations is to protect air resources from pollution by controlling or abating air pollution and harmful emissions. Although nuclear generation of electricity is a form of zero-emission clean energy, the South Texas Project uses small amounts of fossil fuel for backup and emergency equipment.
Regulated emission sources at the South Texas Project include fossil-fueled emergency generators and fire pumps, fire-fighting training, and other minor maintenance equipment and activities.
The station is registered under Texas Commission on Environmental Quality Permit By Rule Registration No.
154767. This permit by rule registration grants the station the authority to operate identified emission sources in accordance with applicable permit and regulatory requirements.
In 2022, the South Texas Project had no reportable air emissions events and no violations.
Unlike conventional electrical generating stations, nuclear power plants do not burn fossil fuel to produce electricity. Therefore, the South Texas Project produces virtually no greenhouse gases or other air pollutants that are the typical by-products of industrial power production processes. The use of emissions-free nuclear power is a significant contributor to the preservation of our communitys clean air resources.
Photos courtesy of 1. & 2. Greg McMullin, 3. Drew Richards
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT CHAPTER FOUR l NON-RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT 4-8 NON-RADIOACTIVE WASTE MANAGEMENT Solid waste management procedures for hazardous and non-hazardous wastes generated at the South Texas Project ensure that wastes are properly dispositioned in accordance with applicable federal, state, and local environmental and health regulations.
By regulatory definition, solid waste includes solid, semi-solid, liquid, and gaseous waste material. The Texas Commission on Environmental Quality, which administers the Texas Solid Waste Disposal Act and the federal Resource Conservation and Recovery Act program, is the primary agency regulating non-radioactive wastes generated at the South Texas Project. The Texas Commission on Environmental Quality regulates the collection, handling, storage, and disposal of solid wastes, including hazardous wastes. The transportation of waste materials is regulated by the United States Department of Transportation.
The South Texas Project is classified as a small quantity generator of industrial solid wastes. Texas Commission on Environmental Quality regulations require industrial solid wastes generated at the South Texas Project to be identified to the Commission. These are listed in the Texas Commission on Environmental Quality Notice of Registration for the South Texas Project. The registration is revised whenever there is a change in waste management practices change at the site. Hazardous waste and Class I non-hazardous waste handling and disposal activities are summarized and documented in a waste summary report for the South Texas Project that is submitted annually to the Texas Commission on Environmental Quality. The South Texas Project five-year Source Reduction and Waste Minimization plan for hazardous waste was last updated and the associated executive summary was submitted to the Texas Commission on Environmental Quality in 2019.
Hazardous waste accumulation at the South Texas Project in 2022 was limited to a maximum holding period of 180 days.
The Resource Conservation and Recovery Act and Texas Solid Waste Disposal Act Photo courtesy of Paul Huff
4-9 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT Figure 4-1 Figure 4-2 Figure 4-3
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT CHAPTER FOUR l NON-RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT 4-10 also requires the use of proper storage and shipping containers, labels, manifests, reports, personnel training, a spill control plan, and an accident contingency plan. South Texas Project personnel routinely inspect areas throughout the site to ensure wastes are not stored or accumulated inappropriately.
South Texas Project policies and regulations encourage the recycling, recovery, or reuse of waste, when possible, to reduce the amount of waste generated or disposed of in landfills. Approximately 67 percent of the industrial non-radioactive waste generated in 2022 at the South Texas Project was recycled or processed for reuse (Reference Figure 4-1). Used oil, diesel fuels, electro-hydraulic fluid, and used oil filters were sent to a recycling vendor for reprocessing.
Empty polyethylene drums are returned, when possible, to the original manufacturer for reuse. In addition, the station supports recycling programs for cardboard, paper, aluminum, printer cartridges and plastic. Approximately 16 tons of scrap metal were removed from the station for recycle in 2022.
The South Texas Project continues to explore new areas where recycling may be expanded or initiated.
Non-radioactive solid waste that cannot be shipped for recycling is shipped for disposal.
Municipal type trash is transported to an offsite landfill. Hazardous waste accounts for only a small portion of the waste generated at the South Texas Project.
Minimization and reduction of hazardous waste generation where feasible remains an important goal. Changes in the amount of hazardous waste shipped each year generally reflect differences in operation and maintenance activities.
Successful waste minimization and source reduction efforts by employees have allowed the South Texas Project to remain classified as a small-quantity waste generator since 2004. (Reference Figures 4-2 and 4-3).
CHEMICAL CONTROL AND MANAGEMENT The stations Integrated Spill Contingency Plan for the South Texas Project, last updated and re-certified in 2019, consolidates multiple federal and state requirements into one plan. The plan is implemented through standard site operating procedures and guidelines.
The South Texas Project uses standard operating procedures, policies, and programs to minimize the generation of waste materials, control chemical use, and prevent spills. The South Texas Project also evaluates chemicals and products prior to their approval for use at the station. Site procedures that implement the stations Integrated Spill Contingency Plan and the stations Chemical Control Program address the evaluation, storage, use, labeling, spill control, and disposal requirements of chemicals. These guidelines also assist in reducing waste generation, ensuring proper packaging for disposal, and mitigating the consequences of inadvertent spillage.
The South Texas Project emphasizes awareness training for spill prevention and maintains readiness to respond should a spill occur. Spill response team members receive annual refresher training in hazardous material incident response. The South Texas Project did not have any reportable liquid spills in 2022.
Photos courtesy of 1. & 3. Gary Parkey, 2. Drew Richards
4-11 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT The South Texas Projects Environmental Protection Plan was issued in March of 1989 to protect non-radiological environmental monitoring parameters during operation of the nuclear plants. This report reviews Environmental Protection Plan non-compliances, if any, identified in 2022 and the associated corrective actions taken to prevent recurrence. Potential non-conformities are promptly addressed to maintain operations in compliance with plan requirements.
Plant personnel use a condition reporting process to document these conditions and track corrective actions to completion. Internal assessments, reviews and inspections are also used to ensure compliance.
Events that require notifications to federal, state, or local agencies are reported in accordance with the applicable reporting requirements.
The United States Nuclear Regulatory Commission is provided with a copy of any such reports at the time they are submitted to the cognizant agency. If a non-routine event occurs and a report is not required by another agency, then a 30-day report to the United States Nuclear Regulatory Commission is required by the Environmental Protection Plan. No such 30-day or other non-routine event report was required in 2022.
E N V I R O N M E N TA L P R O T E C T I O N P L A N S TAT U S Photo courtesy of Drew Richards Photos courtesy of 1. Drew Richards, 2. Gary Parkey
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT CHAPTER FOUR l NON-RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT 4-12 Photo courtesy of Greg McMullin
- A matter that may result in a significant increase in any adverse environmental impact previously evaluated in the Final Environmental Statement related to the Operation of South Texas Project, Units 1 and 2 (Docket Nos. 50-498 and 50- 499), environmental impact appraisals, or in any decisions of the Atomic Safety and Licensing Board.
- A significant change in effluents or power level.
Non-routine report reviews This annual report also reviews non-routine reports submitted by plant personnel and any activities that involved a potentially significant unreviewed environmental question. A proposed change, test or experiment is considered to present an unreviewed environmental question if it concerns:
No unreviewed environmental questions were identified in 2022.
- A matter not previously reviewed and evaluated in the documents specified in (1) above, that may have a significant adverse environmental impact.
RADIOLOGICAL ENVIRONMENTAL INTRODUCTION &
SUMMARY
5-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT CHAPTER FIVE l RADIOLOGICAL ENVIRONMENTAL INTRODUCTION &
SUMMARY
5-2 CHAPTER FIV E The Radiological Environmental Monitoring Program is designed to evaluate the radiological impact of the South Texas Project on the environment by collecting and analyzing samples for low levels of radioactivity. Measurements of samples from the different pathways indicate that there continues to be no adverse effect offsite from the operation of the South Texas Project.
Only Tritium and naturally occurring radioactive material were identified in the offsite environmental samples in 2022.
Samples of fish and meat collected and analyzed showed no South Texas Project related nuclides were present. Water samples from the onsite drinking water supply from the deep aquifer and from offsite sampling stations on the Colorado River show only natural background radioactivity. The station also monitors for radioactivity in onsite sediment from the Main Cooling Reservoir and ditches.
Measurements of direct radiation onsite and offsite indicated no federal dose limits were exceeded.
Tritium is a radioactive isotope of hydrogen that is produced in the reactor and cannot be removed from effluents released to the Main Cooling Reservoir because it is part of the water molecule.
Due to the design of the Main Cooling Reservoir, the presence of Tritium in various sloughs and ditches onsite and the shallow aquifer is expected. Tritium has been detected in these types of samples and the concentrations remain below the United States Environmental Protection Agency drinking water limits.
A sampling program was developed to monitor the Tritium in the immediate area around the plant for long term trending. Wells are sampled either semi-annually, annually, or once every five years, depending on location and the amount of Tritium present. The Tritium concentration remained below the United States Environmental Protection Agency drinking water limits in 2022 and within the design basis of the South Texas Project.
Analyses of the data collected from the implementation of the Radiological Environmental Monitoring Program indicates that the operation of the South Texas Project has no adverse radiological impact.
Photo courtesy of Kelly Callais Photos courtesy of 1. & 2. Gary Parkey, 3. Greg McMullin
6-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT CHAPTER SIX l RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT 6-2 The South Texas Project initiated a comprehensive pre-operational Radiological Environmental Monitoring Program in July 1985.
That program terminated on March 7, 1988, when the operational program was implemented. The data from the pre-operational monitoring program form the baseline against which operational changes are measured.
Analyses of the environmental pathways require that samples be taken from water, air, and land environments.
These samples are obtained to evaluate potential radiation exposure to people.
Sample types are based on established pathways and experience gained at other nuclear facilities. Sample locations were determined after considering site meteorology, site hydrology, local demography, and land use. Sampling locations are further evaluated and modified according to field and analysis experience. Table 1 at the end of this section lists the required sampling locations and frequency of collection.
Additional discretionary samples were also collected.
Sampling locations consist of Indicator Stations and Control Stations. Indicator Stations are locations on or off the site that may be influenced by plant discharges during plant operation.
Control Stations are located beyond the measurable influence of the South Texas Project. Although most samples analyzed are accompanied by a control sample, it should be noted that this practice is not always possible or meaningful with all sample types.
Fluctuations in the concentration of radionuclides and direct radiation exposure at Indicator Stations are evaluated in relation to historical data and against the Control Stations.
Indicator Stations are compared with characteristics identified during the pre-operational program to monitor for radiological effects from plant operation.
Two sample identification methods are used in the program. Figures 6-1 and 6-2 are maps that identify permanent sample stations. Descriptions of sample stations shown on Figures 6-1 and 6-2 are found in Table 2. Table 2 also includes supplemental sampling locations and media types that may be used for additional information. Figure 6-3 illustrates zones that may be used to complement permanent, numbered sample stations.
Environmental samples from areas surrounding the South Texas Project continue to indicate no radiological effects from plant operation. Measured values from offsite indicator sample stations continue to trend with the Control Stations. Measurements from onsite indicator samples continued to fluctuate within normal historical ranges.
CHAPTER SIX P R O G R A M D E S C R I P T I O N Photo courtesy of Gary Parkey Photos courtesy of: 1. Greg McMullin, 2. & 3. Drew Richards
6-3 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM D E S I G N AT E D S A M P L E L O C AT I O N M A P (Offsite locations are numbered)
Figure 6-1
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT CHAPTER SIX l RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT 6-4 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM O N S I T E S A M P L E L O C AT I O N M A P Figure 6-2
6-5 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT Figure 6-3 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Z O N E L O C AT I O N M A P The zone station is determined in the following manner:
- The first character of the station number Z to identify it as a zone station.
- The second character is the direction coordinate No. 1-8.
- The third character is the distance from the site No. 1-6.
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT CHAPTER SIX l RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT 6-6 Average quarterly air particulate sample beta radiation activity from three onsite Indicator Stations and a single control station have been compared historically from 2001 through 2022 (see Figure 6-4). The average of the onsite indicators trends closely with the offsite control values. The comparison illustrates that plant operations are not having an impact on air particulate activity even at the Sensitive Indicator Stations (#1, #15, and #16). These stations are located near the site boundary downwind from the plant, based on the prevailing wind direction. The beta activity measured in the air particulate samples is from naturally occurring radioactive material. Gamma radiation analyses are performed on quarterly composites of the weekly air particulate samples to determine if any activity is from the South Texas Project. The gamma analyses revealed no radioactivity from the South Texas Project.
A I R B O R N E P AT H W AY Figure 6-4 D I R E C T E X P O S U R E P AT H W AY Direct gamma exposure is monitored in the environment with thermoluminescent dosimeters (TLDs) located at 40 locations around the site. The natural direct gamma exposure varies according to location because of differences in the natural radioactive materials in the soil, soil moisture content, and other factors.
Figure 6-5 compares the amount of direct gamma exposure measured at the plant since the first quarter of 2001 from three different types of stations.
The South Texas Project started using a vendor for offsite processing of the thermoluminescent dosimeters for environmental measurement of direct radiation during the third and fourth quarter of 2014. The Control Stations, Stations #23 and #37, are greater than 10 miles from the site in the minimal wind direction. The prevailing wind direction was into the northwest sector.
The Sensitive Indicator Stations are one-mile NW, NNW, and N from the plants on FM 521 at Stations #15, #16 and
- 1 respectively. The Indicator Stations are the remainder of the required monitoring stations.
The values plotted are the averages for all the stations according to type. The average of the Control Stations is higher than the other stations because Station
- 23 is in an area that has slightly higher natural background radiation. The trends of Figure 6-5 show that South Texas Project is not contributing to the direct radiation in the offsite environment.
Photo courtesy of Gary Parkey
6-7 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT Figure 6-5 Figure 6-6 Figure 6-7
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT CHAPTER SIX l RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT 6-8 S E D I M E N T S A M P L E S The cobalt-60 inventory in the reservoir has decreased since 1992 because of radioactive decay and installed equipment to reduce radioactive effluents. Although the total activity of cobalt-60 has decreased over time, an inventory of cobalt-60 is still in the reservoir as seen occasionally at Stations #215 and #216. In 2022, cobalt-60 was identified in zero out of seven Main Cooling Reservoir sediment samples taken, all results were less than the reporting levels. Figure 6-7 demonstrates the calculated decline in the total amount of cobalt-60 in the reservoir. Bottom sediment samples are taken from the Main Cooling Reservoir each year. A study was performed in 2010 to locate the distribution and concentrations of cobalt-60 and cesium-137 in the Main Cooling Reservoir. Although no cobalt-60 was detected from 2007 through 2010 at Stations #215 and #216, the concentration of cobalt-60 is not uniformly distributed in the reservoir sediment and some cobalt-60 remains.
The highest cobalt-60 measurement was 43.5 pCi/kg at station #215, which is considerably less than the reportable levels. Figure 6-6 and Figure 6-7 show the results from the plant-produced cobalt-60 from the Main Cooling Reservoir. Cobalt-60 was not identified in any other sediment sample in 2022.
Cesium-137 was measured in three out of six bottom sediment samples from Stations #215 and #216 in the Main Cooling Reservoir in 2022. The highest measurement was 62.5 pCi/kg at Station
- 215. There was no cesium-137 detected at station 216. Cesium-137 is often found in environmental media including soil and sediment as residual radioactive material resulting from aboveground nuclear weapons testing conducted in the 1950s and 1960s. Soil and sediment samples taken in 1986 and 1987 prior to operation of the South Texas Project contained cesium-137 from weapons testing. The average pre-operational cesium-137 concentration was 118 pCi/
kg in soil and sediment samples, and the highest sample concentration was 383 pCi/kg. Cesium-137 activities measured at Station #215 in 2022 were slightly higher than previously detected due to sampling non-homogeneous media.
Results remained considerably less than reportable levels. The measured values at Station #215 and #216 are consistent with pre-operational concentrations reduced by 30 years of radioactive decay Photos courtesy of Greg McMullin Photo courtesy of Drew Richards
6-9 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT Figure 6-8 Figure 6-9
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT CHAPTER SIX l RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT 6-10 Tritium has been detected in the shallow aquifer on the south side of the Main Cooling Reservoir since 1999. Models used when licensing the site predicted Tritium in the shallow aquifer. These models were validated with additional studies in 2013. A site conceptual model, developed in 2008 and updated in 2014, validated the original predictions of the site hydrology study. A revision was completed in 2018 to include Independent Spent Fuel Storage Installation Project construction.
Tritium is a radioactive isotope of hydrogen and is produced in the reactors during plant operation.
Wastewater is treated to remove impurities before release, but Tritium cannot be removed because it is chemically part of the water molecule.
Some of the Tritium is released into the atmosphere and the remainder is released into the Main Cooling Reservoir. The Tritium escapes from the Main Cooling Reservoir by evaporation, movement into the shallow aquifer, and by percolation from the relief wells which are a part of the reservoir embankments stabilization system.
Figure 6-8 shows the amount of Tritium released to the Main Cooling Reservoir each year and the amount present during the last quarter of each year.
The concentration of Tritium in the Main Cooling Reservoir was relatively stable in 2022. The amount of Tritium measured in the Main Cooling Reservoir was consistent with the amount usually released to the reservoir. The amount of rainfall and reservoir makeup from the Colorado River influences the concentration of Tritium in the Main Cooling Reservoir and the shallow aquifer surrounding it. Tritium enters the sloughs and ditches of the site as runoff from the relief wells that surround the reservoir.
In 2022, Tritium levels remained consistent with historical values in the relief wells as shown in Figure 6-9.
Sampling of Main Cooling Reservoir relief well #701 has been discontinued due to no water flow at that location.
Another existing Main Cooling Reservoir relief well #707, is now used as a representative substitute for sampling the relief well water from the Main Cooling Reservoir. Station #707 is just west of the discontinued relief well #701 on the south side of the Main Cooling Reservoir. Due to different flow rates of water through the relief wells, the base concentration is slightly higher at relief well #707 compared to #701. The highest 2022 sample from relief well #707 indicated approximately 6,972 pCi/kg, which is less than required reporting levels.
The Tritium concentrations in eight surface water sample locations from 2001 through 2022 are shown in Figure 6-10. The specific sample point locations can be found in Table 2.
Tritium levels in the onsite sloughs and ditches vary with the concentration in the reservoir and the amount of rainfall received. The average Tritium concentration in the relief well, sloughs, and ditches are less than the reservoir because the water is diluted as it migrates through the reservoir relief well system. In 2022, seven out of twelve surface water sample locations tested positive for Tritium. All test results were below the United States Environmental Protection Agency drinking water limit of 20,000 pCi/kg. Rainwater was collected and analyzed during 2022 to determine if the Tritium from the reservoir precipitated in the local area.
Tritium was not measured in any of the rainwater samples offsite.
Tritium was identified in the shallow (i.e., ten to thirty feet deep) aquifer test W AT E R B O R N E P AT H W AY Photos courtesy of 1. Greg McMullin, 2. Gary Parkey,
- 3. Drew Richards
6-11 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT Figure 6-10 Figure 6-11
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT CHAPTER SIX l RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT 6-12 wells at Station #235 approximately seventy-five yards south of the reservoir embankment base during 1999. Starting in 2000, samples were collected from the shallow aquifer well at Station #251 south of the Main Cooling Reservoir.
The Tritium results from these two shallow aquifer wells are shown in Figure 6-11. In 2022, the concentration of Tritium at Station #235 was consistent with values over the past ten years.
Shallow aquifer Tritium concentrations have remained near the concentrations found in the relief wells. Wells at Stations
- 258 and #259 on the west side of the site boundary have been sampled since 2006. Wells at Stations #270 and #271 were installed during the last quarter of 2008. The sample results are shown in Figure 6-12. The well at Station #271, located adjacent to site property on a county road easement directly west of the Main Cooling Reservoir, indicated its highest concentration for 2022 at 920 pCi/kg. In 2022, a maximum value of 565 pCi/ kg was identified for onsite test wells. Tritium levels continued to remain below the United States Environmental Protection Agency drinking water limit (20,000 pCi/kg).
Tritium has not been detected in the deep aquifer that is the source of drinking water for the local communities and homes. These measurements follow the hydrological model described in the original license basis and the updated site conceptual model discussed earlier in this section.
A windmill-powered well, Station
- 267, was 310 pCi/kg, in 2022 which is just above detection. This onsite ground water sample station is the most distant location from the Main Cooling Reservoir that Tritium has been detected. This well is not used for human consumption.
The drinking water onsite is pumped Photo courtesy of Drew Richards Photos courtesy of 1. Greg McMullin, 2. Pedro Garcia
6-13 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT Figure 6-12 from deep aquifer wells and is collected monthly and composited quarterly to verify Tritium is not present. The South Texas Project does not use water from the reservoir, shallow aquifers, or other surface water for drinking. If the water with the highest Tritium concentration that leaves the site was used for drinking, the maximum dose to an individual would be less than one millirem in a year.
This dose is insignificant compared to the approximately 620 millirem the public receives a year from natural radioactivity in the environment and the radiation received from medical procedures.3 Other samples are collected and analyzed in addition to those required by our licensing documents or internal procedures. These samples are collected to give additional assurance that the public and the environment are protected from any adverse effects from the plant. These samples include pasture grass, sediment samples, rainwater, shallow aquifer well, water from various ditches and sloughs onsite, direct radiation, and air samples near communities or other areas of interest.
The results of these analyses indicate that plant operation has no health impact offsite and is well within state and federal regulations and guidelines.
3NCRP (2006). National Council on Radiation Protection and Measurements, Ionizing Radiation Exposure of the Population of the United States, (Bethesda, Maryland), NCRP Report No. 160.
Photos courtesy of 1. Kelly Callais, 2. Greg McMullin Photo courtesy of Gary Parkey
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT CHAPTER SIX l RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT 6-14
6-15 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT In 2007, the Nuclear Energy Institute (NEI) established a standard for monitoring and reporting radioactive isotopes in groundwater entitled NEI Groundwater Protection Initiative, NEI 07-07. The station implemented the recommendations of this industry standard and has broadened the groundwater monitoring program to include additional samples collected near the plants. Some of the positive results of this broadened monitoring program reflect Tritium associated with the Main Cooling Reservoir.
Wells near the plants are sampled semi-annually, annually, or once every five years depending on the concentration of Tritium anticipated and the location of the wells. Wells with high concentrations are sampled more frequent over a five-year period which follow STP procedure requirements. Figure 6-13 contains the 2022 results for wells that were sampled along with the historical highs measured prior to 2022 for each station since sampling began in 2006. Their locations are shown in Figure 6-14.
Two wells sampled annually (Stations
- 807 and #808) are adjacent to where a pipe was damaged and repaired several years ago. The Tritium concentration at these two wells continued to decrease as expected in 2022. Station #809 Tritium concentrations were related to the previously referenced pipe and subsequent repair. All the wells sampled in 2022 that had detectable Tritium are influenced by groundwater originating in the Main Cooling Reservoir. Their concentrations remain in the range of groundwater Tritium concentrations associated with the Main Cooling Reservoir. All the 2022 measurements of Tritium in groundwater are a small fraction of the United States Environmental Protection Agency drinking water limit (20,000 pCi/kg).
During 2012, steam traps for the auxiliary steam system that could potentially contain trace amounts of N E I G R O U N D W AT E R P R O T E C T I O N I N I T I AT I V E Figure 6-14 STP Protected Area Ground Water Monitoring Wells Figure 6-13 Note: All measurements are reported in pCi/kg for increased accuracy and are equivalent to pCi/L for reporting purposes.
STP Protected Area Ground Water Monitoring Results
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT CHAPTER SIX l RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT 6-16 L A N D U S E C E N S U S The Annual Land Use Census is performed to determine if any changes have occurred in the location of residents and the use of the land within five miles of the South Texas Project.
The information is used to determine whether any changes are needed in the Radiological Environmental Monitoring Program. The census is performed by contacting local government agencies that provide the information.
In addition, a survey is performed to verify the nearest residents within five miles of the South Texas Project generating units in each of 16 sectors.
The results of the survey indicated no changes for 2022. The eleven sectors that have residents within five miles and the distance to the nearest residence in each sector are listed below.
Tritium were modified to re-direct the condensed steam or liquid water to the Main Cooling Reservoir. Information regarding the steam traps and subsequent response was documented in the stations condition reporting process.
This evaluation identified no new effluent release pathways and no impact to the drinking water or the health and safety of the public.
By the end of 2014, the majority of the protected area wells had undergone a modification to enhance the protection of the structural integrity of the water well casing used for sampling the upper aquifer. The modifications were completed in 2015 with continued improvements into 2016.
In 2022, there was one occurrence where condensed steam or water contacted the ground onsite. This occurrence did not result in impact to the public or the environment. No discharge occurred offsite or to groundwater that may be used as a source of drinking water.
Where applicable, the water was quickly recovered, recaptured, and clean up completed with no impact to groundwater.
Photos courtesy of 1. Gary Parkey, 2. Cheryl Bentley
- No commercial dairies operate within Matagorda County.
- There were no identified animals producing milk for human consumption located within five miles of STP.
- A commercial olive tree orchard is located approximately 4.9 miles WSW of the plant.
- One commercial fish farm continues to operate. It is located approximately four to five miles southwest of the
- Broadleaf vegetation sampling is performed at the site boundary in the three most leeward sectors and at a control location in lieu of a garden census. The broadleaf vegetation samples collected also satisfy the collection requirement when milk samples are not available.
plant located in the area north of Robbins Slough Road and east of South Citrus Grove Road. The water supply for the ponds is not affected by the operations of the South Texas Project.
- Colorado River water from below the Bay City Dam has not been used to irrigate crops.
- There were no identified commercial vegetable farms located within the five-mile zone.
Land Use Census items of interest
Figure 6-15 Figure 6-16 6-17 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT CHAPTER SIX l RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT 6-18 Quality assurance encompasses planned and systematic actions to ensure that an item or facility will perform satisfactorily. Reviews, surveillances, and audits have determined that the programs, procedures, and personnel are performing at a satisfactory level.
Quality audits and independent technical reviews help to determine areas that need attention. These areas are addressed in accordance with the stations Condition Reporting Process.
The measurement capabilities of the Radiological Laboratory are demonstrated by participating in an interlaboratory measurement assurance program as well as performing duplicate and split sample analyses. Approximately 21.4 percent of the analyses performed are quality control samples. These consist of interlaboratory measurement assurance program samples, duplicate samples, and split samples. All analyses include National Institute of Standards and Technology samples, blanks, intercomparison testing, duplicates and splits out of a total of 1369 samples analyzed for 2022.
The interlaboratory measurement assurance program provides samples that are similar in matrix and size to those measured by the Radiological Environmental Monitoring Program.
This program assures that equipment calibrations and sample preparation methods accurately measure radioactive material in samples. Figure 6-15 summarizes the results of the interlaboratory comparison programs.
Duplicate sampling of the environment allows the South Texas Project to estimate the repeatability of the sample collection, preparation, and analysis process. Splitting samples allows estimation of the precision and bias trends of the method of analysis without the added variables introduced by sampling. Generally, two samples split from the same original sample material should agree better than two separate samples collected in the same area and time. The 2022 variances for duplicates and splits are shown in Figure 6-16.
Q U A L I T Y A S S U R A N C E In addition to measurement accuracy, radiochemical measurements must meet sensitivity requirements at the Lower Level of Detection for environmental samples. Deviations from the sampling program or sensitivity requirements must be acknowledged and explained in this report. The loss of a small fraction of the total samples collected in 2022 did not impact the ability to demonstrate that the South Texas Project continues to operate with no negative effect on the population or the environment.
During 2022 samples not collected or unacceptable for analysis:
Eight out of 265 Offsite Dose Calculation Manual (ODCM) required air sample was not collected due to loss of power from Station #1, #15, #16, and #39.
Twenty-seven air samples not required by the ODCM were not continuously collected for the full-time interval because of power or equipment failures from station #35, and #6, and #6 duplicate.
One broadleaf vegetation sample was not collected in January due to weather conditions, since this sample is outside the growing season it was not required by the ODCM.
There were two instances where TLD results used for measuring direct radiation were questionable. One was hit by the mower and the second had questionable results when compared to the duplicate TLD used at the same location.
P R O G R A M D E V I AT I O N S Photos courtesy of 1. Kelly Callais, 2. Gary Parkey,
- 3. Drew Richards
TA B L E 1 R A D I O L O G I C A L E N V I R O N M E N TA L M O N I T O R I N G P R O G R A M MCR-STP Main Cooling Reservoir STP-South Texas Project 6-19 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT CHAPTER SIX l RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT 6-20 TA B L E 1 R A D I O L O G I C A L E N V I R O N M E N TA L M O N I T O R I N G P R O G R A M ( C O N T. )
MCR-STP Main Cooling Reservoir STP-South Texas Project Photo courtesy of Greg McMullin
6-21 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT TA B L E 1 R A D I O L O G I C A L E N V I R O N M E N TA L M O N I T O R I N G P R O G R A M ( C O N T. )
Photo courtesy of Gary Parkey Photo courtesy of Charles Townsend
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT CHAPTER SIX l RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT 6-22
TA B L E 2 S A M P L E M E D I A A N D L O C AT I O N D E S C R I P T I O N S 6-23 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT CHAPTER SIX l RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT 6-24 TA B L E 2 S A M P L E M E D I A A N D L O C AT I O N D E S C R I P T I O N S ( C O N T. )
This station may be used to obtain the required aquatic samples in the vicinity of STP that may be influenced by plant operations.
MCR-STP Main Cooling Reservoir STP-South Texas Project Media codes typed in bold satisfy collection requirement described in Table 1.
Station codes typed in bold identify offsite locations.
- Control Station
6-25 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT TA B L E 2 S A M P L E M E D I A A N D L O C AT I O N D E S C R I P T I O N S ( C O N T. )
This station may be used to obtain the required aquatic samples in the vicinity of STP that may be influenced by plant operations.
MCR-STP Main Cooling Reservoir STP-South Texas Project Media codes typed in bold satisfy collection requirement described in Table 1.
Station codes typed in bold identify offsite locations.
- Control Station
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT CHAPTER SIX l RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT 6-26 TA B L E 2 S A M P L E M E D I A A N D L O C AT I O N D E S C R I P T I O N S ( C O N T. )
This station may be used to obtain the required aquatic samples in the vicinity of STP that may be influenced by plant operations.
MCR-STP Main Cooling Reservoir STP-South Texas Project Media codes typed in bold satisfy collection requirement described in Table 1.
Station codes typed in bold identify offsite locations.
- Control Station
6-27 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT Station codes typed in bold identify offsite locations.
TA B L E 2 S A M P L E M E D I A A N D L O C AT I O N D E S C R I P T I O N S ( C O N T. )
Photo courtesy of Bethani Wittig Photo courtesy of Clarence Holley
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT CHAPTER SIX l RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT 6-28
6-29 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT A summary of all required samples is given in Table 3. The table has been formatted to resemble a United States Nuclear Regulatory Commission industry standard. Modifications have been made for the sole purpose of reading ease. Only positive values are given in this table.
Media type is printed at the top left of each table, and the units of measurement are printed at the top right. The first column lists the type of radioactivity or specific radionuclide for which each sample was analyzed.
The second column gives the total number of analyses performed and the total number of non-routine analyses for each indicated nuclide. A non-routine measurement is a sample whose measured activity is greater than the reporting levels for Radioactivity Concentrations in Environmental Samples. The LOWER LIMIT OF DETECTION column lists the normal measurement sensitivities achieved.
The sensitivities were better than required by the United States Nuclear Regulatory Commission.
A set of statistical parameters is listed for each radionuclide in the remaining columns. The parameters contain information from the indicator locations, the location having the highest annual mean, and information from the Control Stations. Some sample types do not have Control Stations. When this is the case, no samples is listed in the control location column.
For each of these groups of data, the following is calculated:
- The mean positive values
- The number of positive measurements/the total number of analyses
- The lowest and highest values for the analysis The data placed in Table 3 are from the samples required by the sites Offsite Dose Calculation Manual as described in Table 1.
Additional thermoluminescent dosimeters were utilized each quarter for quality control purposes. The minimum samples required by Table 1 were supplemented in 2022 by numerous direct radiation measurements, additional surface water samples, ground water samples, additional pasture grass, additional rainwater samples, additional relief well water samples, and additional sediment samples.
Fish and crustacean samples vary in number according to availability, but exceeded the minimum number required by Table 1, as well as other meat samples.
Also, numerous air station samples were collected from weekly air sample stations, in addition to the minimum number of samples required by Table 1 to strengthen the Radiological Environmental Monitoring Program.
The minimum required Radiological Environmental Monitoring Program is presented in Table 1. The table is organized by exposure pathway. Specific requirements such as location, sampling method, collection frequency, and analyses are given for each pathway.
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANALYSIS
SUMMARY
Photos courtesy of 1. & 2. Gary Parkey, 3. Kelly Callais,
- 4. Drew Richards
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT Photo courtesy of Greg McMullin CHAPTER SIX l RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT 6-30
6-31 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT TABLE 3 2022 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANALYSIS
SUMMARY
Medium: Surface Water Units: PicoCuries per Kilogram ANALYSIS TOTAL ANALYSES LOWER INDICATOR LOCATIONS LOCATION WTI11 HIGHEST ANNUAL MEAN CONTROL LOCATIONS TYPE
/NONROUTINE UMITOF MEAN t LOCATION MEAN t MEAN t MEASUREMENTS DETECTION RANGE INFORMATION RANGE RANGE Hydrogen-3 12/ 0 2.5E+02 I.I E+04 ( 4 / 8) 3 miles SSE I.I E+04 ( 4 / 4)
--- ( 0 / 4)
( 9.3E+03 - l.4E+04 )
(#216)
( 9.3E+03 - l.4E+04)
Iodine-131 48/ 0 4.2E+OO
--- ( 0 I 32)
--- ( 0 I 16)
Cesium-134 48/ 0 2.0E+OO
--- ( 0 I 32)
--- ( 0 / 16)
Cesium-137 48/ 0
- 2. IE+OO
--- ( 0 I 32)
--- ( 0 I 16)
Manganese-54 48/ 0 2.IE+OO
--- ( 0 I 32)
--- ( 0 I 16)
Iron-59 48/ 0 4.9E+OO
--- ( 0 I 32)
--- ( 0 I 16)
Cobalt-58 48/ 0 2.2E+OO
--- ( 0 I 32)
--- ( 0 I 16)
Cobalt-60 48/ 0 2.3E+OO
--- ( 0 I 32)
--- ( 0 I 16)
Zinc-65 48/ 0 5.0E+OO
--- ( 0 I 32)
--- ( 0 I 16)
Zirconium-95 48/ 0 3.9E+OO
--- ( 0 I 32)
--- ( 0 I 16)
Niobium-95 48/ 0 2.2E+OO
--- ( 0 I 32)
--- ( 0 I 16)
Lanthanum-1 40 48/ 0 4.7E+OO
--- ( 0 I 32)
--- ( 0 I 16)
Barium-140 t Number of positive measurements I total measurements at specified locations.
TABLE 3 2022 RADIOLOGICAL ENVIRONMENT AL MONITORING PROGRAM ANALYSIS
SUMMARY
Medium: Ground Water (On site test well)
Units: PicoCuries per Kilogram ANALYSIS TOTAL ANALYSES LOWER INDICATOR LOCATIONS LOCATION WTI11 HIGHEST ANNUAL MEAN CONTROL LOCATIONS TYPE
/NONROUTINE UM ITOF MEAN t LOCATION MEAN t MEAN t MEASUREMENTS DETECTION RANGE INFORMATION RANGE RANGE Hydrogen-3 27/ 0 2.8E+02 4.2E+03 ( 16 / 27) 4.0 miles SSE 5.3E+03 ( 7 / 7) no samples
( 2.0E+03 - 5.6E+03 )
(#25 1)
( 5. IE+03 - 5.6E+03)
Iodine-131 27/ 0 2.7E+OO
--- ( 0 I 27) no samples Cesium-134 27/ 0 2.8E+OO
--- ( 0 I 27) no samples Cesium-137 27/ 0 2.8E+OO
--- ( 0 I 27) no samples Manganese-54 27/ 0 2.6E+OO
--- ( 0 I 27) no samples Iron-59 27/ 0 5.SE+OO
--- ( 0 I 27) no samples Cobalt-58 27/ 0 2.6E+OO
--- ( 0 I 27) no samples Cobalt-60 27/ 0 3.0E+OO
--- ( 0 I 27) no samples Zinc-65 27/ 0 8.SE+OO
--- ( 0 I 27) no samples Zirconium-95 27/ 0 4.SE+OO
--- ( 0 I 27) no samples Niobium-95 27/ 0
- 3. IE+OO
--- ( 0 I 27) no samples Lanthanum-1 40 27/ 0 3.8E+OO
--- ( 0 I 27) no samples Barium-140 t Number ol pos111ve measurements / total measurements at spec1 fied locat10ns.
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT CHAPTER SIX l RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT 6-32 TABLE 3 2022 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANALYSIS
SUMMARY
Medium: Drinking Water Units: PicoCuries per Kilogram ANALYSIS TOTAL ANALYSES LOWER INDICATOR LOCATIONS LOCATION wrrn I-IIGI-IEST ANNUAL MEAN CONTROL LOCATIONS TYPE
/NONROUTINE LIMJTOF MEAN t LOCATION MEAN t MEAN t MEASUREMENTS DETECTION RANGE INFORMATION RANGE RANGE Gross Beta 24J 0 1.4E+00 2.2E+00 ( 10 J 12) 14 milesNNE 3.7E+00( 12 J 12) 3.7E+00( 12 J 12)
( L7E+00 - 2.8E+00)
(#228)
( 3 0E+o0 - 4.8E+00)
( 3 0E+00 - 4.8E+00 )
Hydrogen-3 8J 0 2.SE+02
--- ( 0 J 4 )
--- ( 0 J 4) lodine-13 1 24JO 3.3E+00
--- ( 0 J 12)
--- ( OJ 12)
Cesium-1 34 24J 0 3.I E+00
--- ( 0 J 12)
--- ( OJ 12)
Cesium-137 24JO 3.l E+00
--- ( 0 J 12)
--- ( 0 J 12)
Manganese-54 24J 0 3 0E+00
--- ( 0 J 12)
--- ( OJ 12)
Iron-59 24J 0 6.4E+00
--- ( 0 J 12)
--- ( OJ 12)
Cobalt-58 24JO 3.0E+00
--- ( 0 J 12)
--- ( 0 J 12)
Cobalt-60 24J 0 3.4E+00
--- ( 0 J 12)
--- ( OJ 12)
Zinc-65 24J 0 9.3E+00
--- ( 0 J 12)
--- ( OJ 12)
Zirconium-95 24JO S.2E+00
--- ( 0 J 12)
--- ( OJ 12)
Niobium-95 24J 0 3.SE+00
--- ( 0 J 12)
--- ( OJ 12)
Lanthannm-140 24J 0 4.SE+00
--- ( 0 J 12)
--- ( 0 J 12)
Barium-140 t Number of positive measurements J total measurements at specified locations.
TABLE 3 2022 RADIOLOGICAL ENVIRONMENT AL MONITORING PROGRAM ANALYSTS
SUMMARY
Medium: Rain Water Units: PicoCuries per Kilogram ANALYSIS TOTAL ANALYSES LOWER INDICATOR LOCATIONS LOCATION WITH HIGHEST ANNUAL MEAN CONTROL LOCATIONS TYPE
/NONROUTINE LIMIT OF MEAN t LOCATION MEAN t MEAN t MEASUREMENTS DETECTION RANGE INFORMATION RANGE RANGE Hydrogen-3 4JO 2.SE+02
--- ( OJ 4) no samples lodine-131 4J 0 2.8E+00
--- ( OJ 4) no samples Cesium-1 34 4J 0 2.8E+00
--- ( OJ 4) no samples Cesium-1 37 4JO 3.IE+00
--- ( OJ 4) no samples Manganese-54 4J 0 2.7E+00
--- ( OJ 4) no samples lron-59 4J 0
- 6. IE+00
--- ( OJ 4) no samples Cobalt-58 4JO 2.8E+00
--- ( OJ 4) no samples Cobalt-60 4J 0 3.2E+00
--- ( OJ 4) no samples Zinc-65 4JO 7.3E+00
--- ( OJ 4) no samples Zirconium-95 4J 0 4.8E+00
--- ( OJ 4) no samples Niobium-95 4J 0 2.7E+00
--- ( OJ 4) no samples Lanthanum-140 4JO 3.8E+00
--- ( OJ 4) no samples Barium-1 40 t Number of pos1t1ve measurements J total measurements at specified locat10ns.
6-33 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT CHAPTER SIX l RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT 6-34 Photo courtesy of Robert Nies TABLE 3 2022 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANALYSIS
SUMMARY
Medium: Sediment-Shoreline Units: PicoCuries per Kilogram dry weight ANALYSIS TOTAL ANALYSES LOWER INDICATOR LOCATIONS LOCATION WIII-I I-IIGI-IESI ANNUAL MEAN CONTROL LOCA IIONS
'IYPE
/NONROUT!NE LIMITOF MEAN t LOCATION MEAN t MEAN t MEASUREMENTS DETECTION RANGE lNFORMA TION RANGE RANGE Cesium-134 4/ 0 2-3E+OI
--- ( Of 2)
--- ( Of 2)
Cesium-137 4/ 0 2-3E+OI
--- ( 0 / 2)
--- ( 0 / 2)
Mangancsc-54 4/ 0 2-3E+Ol
--- ( 0 / 2)
--- ( 0 / 2)
Iron-59 4/ 0 5-3E+OI
--- ( Of 2)
--- ( Of 2)
Cobalt-58 4/ 0 2.2E+OI
--- ( 0 / 2)
--- ( 0 / 2)
Cobalt-60 4/ 0 24E+OI
--- ( Of 2)
--- ( Of 2)
Zinc-65 4/ 0 7-2E+O l
--- ( 0 / 2)
--- ( 0 / 2)
Zirconium-95 4/ 0 4.IE+Ol
--- ( 0 / 2)
--- ( 0 / 2)
Niobium-95 4/ 0 2.6E+OI
--- ( Of 2)
--- ( Of 2)
Lanthanum-140 4/ 0 4.0E+OI
--- ( 0 / 2)
--- ( 0 / 2)
Barium-140 t Number of positive measurements I total measurements at specified locations_
TABLE 3 2022 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANALYSIS
SUMMARY
Medium: Sediment-Bottom Units: PicoCuries per Kilogram dry weight ANALYSIS TOT AL ANALYSES LOWER lNDJCA TOR LOCATIONS LOCA TJON WITI-1 I-IIGI-IEST ANNUAL MEAN CONrROL LOCATIONS TYPE
/NONROUTINE LIMIT OF MEAN t LOCATION MEAN t MEAN t MEASUREMENTS DETECTION RANGE INFORMATION RANGE RANGE Cesium-134 6/ 0 2.6E+OI
--- ( 0 I 6) no samples Cesium-1 37 6/ 0
- 2. IE+OI 44E+OI ( 3 / 6)
I mile SW 44E+OI ( 3 / 3) no samples
( 2.8E+Ol 3E+Ol )
(#215)
( 2.8E+O I - 6.3£+01 )
Manganese-54 6/ 0 24E+O l
--- ( 0 I 6) no samples lron-59 6/ 0 6,2£+01
--- ( 0 / 6) no samples Cobalt-58 6/ 0 2-3E+OI
--- ( Of 6) no samples Cobalt-60 6/ 0 2.6E+Ol 4.2E+O l ( 2 / 6)
I mile SW 4_2E+Ol ( 2 / 3) no samples
( 4.0E+Ol - 44E+Ol )
(#215)
( 4.0E+OI - 44E+Ol )
Zinc-65 6/ 0 7,9£+01
--- ( 0 I 6) no samples Zirconium-95 610 4.6E+OI
--- ( Of 6) no samples Niobium-95 6/ 0 2.9E+OI
--- ( 0 / 6) no samples Lanthanum-140 6/ 0 6.8E+Ol
--- ( 0 / 6) no samples Barium-140 t Number of postl:Jve measurements / total measurements at specified locattons_
6-35 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT TABLE 3 2022 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANALYSIS
SUMMARY
Medium: B anana Leaves U n its : PicoCuries p er Kilogram wet w eigh t ANALYSIS TOTAL ANALYSES LOWER INDICATOR LOCATIONS LOCATION WTI1-I I-IIGI-IEST ANNUAL MEAN CONTROL LOCATIONS TYPE
/NONROUTINE LIMITOF MEAN t LOCATION MEAN t MEAN t MEASUREMENTS DETECTION RANGE INFORMATION RANGE RANGE Iodine-131 11/ 0 I.4E+01
--- ( 0 / 7)
--- ( 0 / 4)
Cesium-1 34 l l/ 0 l.6E+Ol
--- ( 0 / 7)
--- ( 0 / 4 )
Cesium-1 37 11/0 l.5E+Ol
--- ( 0 / 7)
--- ( 0 / 4)
Manganese-54 11/ 0 1.5E+Ol
--- ( 0 / 7)
--- ( 0 / 4) lron-59 Il l 0 3.4E+Ol
--- ( 0 / 7)
--- ( 0 / 4)
Cobalt-58 11 / 0 l.5E+OI
--- ( Of 7)
--- ( Of 4)
Cobalt-60 Il l 0 l.SE+O l
--- ( 0 / 7)
--- ( 0 / 4)
Zinc-65 11/0 4.7E+Ol
--- ( 0 / 7)
--- ( 0 / 4)
Zirconium-95 11 / 0 2.5E+OI
--- ( 0 / 7)
--- ( 0 / 4)
Niobium-95 Il l 0 l.6E+O l
--- ( 0 / 7)
--- ( 0 / 4)
Lanthanum-140 11/0 2.IE+Ol
--- ( 0 / 7)
--- ( 0 / 4)
Barium-1 40 t Number of positive measurements / total measurements at specified locations.
TABLE 3 2022 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANALYSIS
SUMMARY
Medium: Cana Leaves Un its : PicoCuries p er Kilogram wet weight ANALYSIS TOTAL ANALYSES LOWER INDICATOR LOCATIONS LOCATION Willi IIIGI-IEST ANNUAL MEAN CONTROL LOCATIONS TYPE
/NONROlJTINE LIM ITOF MEAN t LOCATION MEAN t MEAN t MEASUREMENTS DETECTION RANGE INFORMATION RANGE RANGE Iodine-131 21/ 0 l.3E+01
--- ( 0 I 15)
--- ( 0 / 6)
Cesium-1 34 2 1/ 0 l.5E+O l
--- ( 0 I 15)
--- ( 0 / 6)
Ccsium-1 37 21/ 0 l.5E+Ol
--- ( 0 I 15)
--- ( 0 / 6)
Manganese-54 21/ 0 l.5E+Ol
--- ( 0 I 15)
--- ( 0 / 6)
Iron-59 21/ 0 3.4E+Ol
--- ( 0 I 15)
--- ( 0 / 6)
Cobalt-58 21/ 0 l.5E+Ol
--- ( 0 I 15)
--- ( 0 / 6)
Cobalt-60 21/ 0 1.SE+Ol
--- ( 0 I 15)
--- ( 0 / 6)
Zinc-65 2 1/ 0 4.6E+OI
--- ( 0 I 15)
--- ( 0 / 6)
Zirconium-95 21/ 0 2.5E+O l
--- ( 0 I 15)
--- ( 0 / 6)
Niobium-95 2 1/ 0 l.6E+O l
--- ( 0 I 15)
--- ( 0 / 6)
Lanthanum-140 21/ 0 2.0E+Ol
--- ( 0 I 15)
--- ( 0 / 6)
Barium-1 40 t Number of positive measurements / total measurements at specified locations.
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT CHAPTER SIX l RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT 6-36 TABLE 3 2022 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANALYSIS
SUMMARY
Mediwn: Collard G reens U nits : PicoCuries p er K ilogram wet weight ANALYSIS TOTAL ANALYSES LOWER INDICATOR LOCATIONS LOCATION wrrn HIGHEST ANNUAL MEAN CONTROL LOCATIONS TYPE
/NONROUTINE LIMIT OF MEAN t LOCATION MEAN t MEAN t MEASUREMENTS DETECTION RANGE
!NFORMA TION RANGE RANGE Iodine-131 4/ 0 1.2E+O\\
--- ( 0 / 4) no samples Cesium-1 34 4/ 0 1.3E+O I
--- ( 0 / 4 )
no samples Ccsium-1 37 4/ 0 l.4E+Ol
--- ( 0 / 4) no samples Manganese-54 4/ 0 l.3E+O\\
--- ( 0 / 4) no samples lron-59 4/ 0 3.0E+Ol
--- ( 0 / 4) no samples Cobalt-58 4/ 0 l.3E+O I
--- ( 0 1 4) no samples Cobalt-60 4/ 0 l.6E+Ol
--- ( 0 / 4) 110 samples Zinc-65 4/ 0
- 4. l E+Ol
--- ( 0 / 4) no samples Zirconium-95 4/ 0 2.2E+O I
--- ( 0 1 4) no samples Niobium-95 4/ 0 1.5E+O l
--- ( 0 / 4 )
110 samples Lanthanum-140 4/ 0 l.8E+Ol
--- ( 0 / 4) no samples Barium-1 40 t Number of positive measurements I total measurements at specified locations.
TABLE 3 2022 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANALYSIS
SUMMARY
Mediwn: F ish - Piscivorous U nits: PicoCuries per Kilogram wet weight ANALYSIS TOTAL ANALYSES LOWER INDICATOR LOCATIONS LOCATION WJTH HIGHEST ANNUAL MEAN CONTROL LOCATIONS TYPE
/NONROUTINE LIMIT OF MEAN t LOCATION MEAN t MEAN t MEASUREMENTS DETECTION RANGE INFORMATION RANGE RANGE Cesium-1 34 5/ 0 3.2E+Ol
--- ( 0 / 4 )
--- ( 0 / I )
Cesium-1 37 5/ 0 3.2E+Ol
--- ( 0 / 4)
--- ( 0 / I )
Manganese-54 5/ 0 3.3E+OI
--- ( 0 / 4)
--- ( 0 / 1)
Iron-59 5/ 0 7.3E+Ol
--- ( 0 / 4 )
--- ( 0 / I )
Cobalt-58 5/ 0 3.2E+Ol
--- ( 0 / 4)
--- ( 0 / I )
Cobalt-60 5/ 0 4.lE+Ol
--- ( 0 / 4)
--- ( 0 / 1 )
Zinc-65 5/ 0 8.IE+OI
--- ( 0 / 4)
--- ( 0 / I )
Zirconium-95 5/ 0 5.9E+Ol
--- ( 0 / 4)
--- ( 0 / 1 )
Niobium-95 5/ 0 3.3E+Ol
--- ( 0 / 4)
--- ( 0 / 1 )
Lanthanum-140 5/ 0 5.9E+Ol
--- ( 0 / 4)
--- ( 0 / I )
Barium-140 t Number of pos1llve measurements / total measurements at specified locat10ns.
6-37 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT TABLE 3 2022 RADIOLOGICAL ENVIRONMENT AL MONITORING PROGRAM ANALYSIS
SUMMARY
Medium: Fish - Crustacean & Insect Feeders Units: PicoCuries per Kilogram wet weight ANALYS IS TOTAL ANALYSES LOWER INDICATOR LOCATIONS LOCATION WITH HIGHEST ANNUAL MEAN CONTROL LOCATIONS TYPE
/NONROUTINE LIMIT OF MEAN t LOCATION MEAN t MEAN j" MEASUREMENTS DETECTION RANGE INFORMATION RANGE RANGE Cesium-134 3/ 0 3.3E+()l
--- ( 0 / 2)
--- ( 0 / I )
Cesium-1 37 3/ 0 3.4E+()l
--- ( Of 2)
--- ( Of I )
Manganese-54 3/ 0 3.3E+()I
--- ( 0 / 2)
--- ( 0 / I )
Iron-59 3/ 0 7.2E+()l
--- ( 0 / 2)
--- ( 0 / I )
Cobalt-58 3/ 0 3.2E+()J
--- ( 0 / 2)
--- ( 0 / I )
Cobalt-60 3/ 0 4.0E-t-()1
--- ( 0 / 2)
--- ( 0 / I )
Zinc-65 3/ 0 8.0E-t-()1
--- ( Of 2)
--- ( Of I )
Zirconium-95 3/ 0 5.7E+()J
--- ( Of 2)
--- ( Of I )
Niobium-95 3/ 0 3.3E+()l
--- ( Of 2)
--- ( Of I )
Lanthanum-140 3f 0 5.3E+()l
--- ( Of 2)
--- ( Of I )
Barium-140 t Number or positive measurements f total measurements at specified locations.
TABLE 3 2022 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANALYSIS
SUMMARY
Medium: Crustacean Shrimp Units: PicoCuries per Kilogram wet weight ANALYSIS TOTAL ANALYSES LOWER INDICATOR LOCATIONS LOCATION WITI-I HIGHEST ANNUAL MEAN CONTROL LOCATIONS TYPE
/NONROUTINE LIMIT OF MEAN t LOCATION MEAN t MEAN t MEASUREMENTS DETECTION RANGE INFORMATION RANGE RANGE Cesium-1 34 3f 0 3.9E+() I
--- ( 0 I 3) no samples Cesium-137 3f 0 3.7E+()J
--- ( 0 / 3) no samples Manganese-54 3/ 0 3.7E+()l
--- ( 0 / 3) no samples Iron-59 3/ 0
- 8. IE-t-()1
--- ( 0 / 3) no samples Cobalt-58 3/ 0 3.7E+()l
--- ( 0 / 3) no samples Cobalt-60 3/ 0 4.4E+()l
--- ( 0 / 3) no samples Zinc-65 3/ 0 9.5E+()l
--- ( 0 / 3) no samples Zirconium-95 3/ 0 6.6E+Ol
--- ( 0 / 3) no samples Niobium-95 3/ 0 3.8E+Ol
--- ( 0 / 3) no samples Lanthanum-140 3f 0 5.5E+Ol
--- ( 0 / 3) no samples Barium-140 t Number of pos11Ive measurements / total measurements at specified locations.
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT CHAPTER SIX l RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT 6-38 Photo courtesy of Dana Buckley Photo courtesy of Pedro Garcia
STP l ANNUAL ENVIRONMENTAL OPERATING REPORT
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT Photo courtesy of Gary Parkey
1-1 STP l ANNUAL ENVIRONMENTAL OPERATING REPORT Maps provided by Janice Hopes Cover photo by Gary Parkey Other photos courtesy of: Charles Townsend, Cheryl Bentley, Christie Dement, Clarence Holley, Dana Buckley, Drew Richards, Gary Parkey, Greg McMullin, Kelly Callais, Paul Huff, Pedro Garcia, Robert Nies and Bethani Wittig Graphics by Diane Davis Design Coordination and support by Corporate Communications