ML20122A111

Annual Environmental Operating Report

ML20122A111
Person / Time
Site:	Millstone
Issue date:	04/22/2020
From:	Armstrong L Dominion Energy Nuclear Connecticut
To:	Document Control Desk, Office of Nuclear Reactor Regulation
References
20-114
Download: ML20122A111 (11)

Text

Dominion Energy Nuclear Connecticut, Inc.

Rt 156, Rope Ferry Road, Waterford, CT 06385 Dominion Energy.com U.S. Nuclear Regulatory Commission Attention: Document Control Desk Washington, DC 20555-0001 APR 2 2 2020 DOMINION ENERGY NUCLEAR CONNECTICUT, INC.

MILLSTONE POWER STATION UNIT 3 2019 ANNUAL ENVIRONMENTAL OPERATING REPORT

~

Dominion

~

Energy Serial No.

MPS Lie/LO Docket No.

License No.20-114 RO 50-423 NPF-49 In accordance with Section 5.4.1 of the Environmental Protection Plan (EPP), Appendix B to the Millstone Power Station Unit 3 Operating License, Dominion Energy Nuclear Connecticut, Inc. hereby submits the Annual Environmental Operating Report (AEOR),

describing implementation of the EPP for the previous year. transmits information for the period of January 1, 2019 to December 31, 2019.

Should you have any questions regarding this

report, please contact Mr. Jeffry A. Langan at (860) 444-5544.

Sincerely,

'~~

L. J. Armstrong Director, Nuclear Station Safety and Licensing

Enclosures:

1 Commitments made in this letter: None.

cc:

U.S. Nuclear Regulatory Commission Region I 2100 Renaissance Blvd, Suite 100 King of Prussia, PA 19406-2713 R. V. Guzman NRG Project Manager Millstone Units 2 and 3 U.S. Nuclear Regulatory Commission One White Flint North, Mail Stop 08 C2 11555 Rockville Pike Rockville, MD 20852-2738 NRG Senior Resident Inspector Millstone Power Station Serial No.20-114 2019 Annual Environmental Operating Report Page 2 of 2 MILLSTONE POWER STATION UNIT 3 Serial No.20-114 Docket No.

50-423 License No. NPF-49 2019 ANNUAL ENVIRONMENTAL OPERATING REPORT JANUARY 1 - DECEMBER 31, 2019 MILLSTONE POWER STATION UNIT 3 DOMINION ENERGY NUCLEAR CONNECTICUT, INC. (DENC}

2019 Annual Environmental Operating Report {AEOR) 1.

Introduction:

This report covers the period January 1, 2019 through December 31, 2019. During 2019, Millstone Power Station Unit 3 (MPS3) concluded fuel cycle 19 in March 2019; MPS3 underwent a refueling outage from April 11, 2019 to May 14, 2019. Fuel cycle 20 began in May 2019 and is expected to continue until Fall 2020.

As required by the MPS3 Environmental Protection Plan (EPP), Appendix B to the MPS3 Operating License, this AEOR includes:

summaries and analyses of the results of environmental protection activities, a list of EPP non-compliances and the corrective actions taken to remedy them, a list of all changes in station design or operation, tests, and experiments which involved a potentially significant unreviewed environmental question, and a list of non-routine reports submitted in accordance with subsection 5.4.2.

2. Environmental Protection Activities:

2.1 Annual National Pollutant Discharge Elimination System (NPDES) Report of Ecological Monitoring (EPP Section 4.2).

Section 1 O(A) of Millstone Power Station's (MPS) NPDES permit (the Permit), as issued to Dominion Nuclear Connecticut, Inc. (DNC; now Dominion Energy Nuclear Connecticut, DENG) by the Connecticut Department of Environmental Protection (DEP; now the Department of Energy and Environmental Protection, or DEEP) on September 1, 2010, requires, among other things, continuation of biological studies of supplying and receiving waters.

These studies include analyses of intertidal and subtidal benthic communities, finfish communities, entrained plankton, lobster populations, and winter flounder populations. Section 1 O(A)(2) of the Permit requires an annual report of these studies to be sent to the DEEP Commissioner on or before July 31 of each year. The latest report that fulfills these requirements, "Annual Report 2018 - Monitoring the Marine Environment of Long Island Sound at Millstone Power Station, Waterford, Connecticut" (Annual Report), dated July 2019, presents results from studies performed during construction and operation of MPS, emphasizing those of the latest sampling year.

Characteristics of and changes to the biological communities noted in these studies are summarized in the Executive Summary section of the Annual Report, which is attached as part of this report.

2.2 Effluent Water Quality Monitoring:

Several sections of the Permit require monitoring and recording of various water quality parameters at MPS intakes and at multiple monitoring points within the plant, including outfalls of each unit to the effluent quarry, and outfall of the quarry to Long Island Sound. Section 8 of the Permit requires that a monthly report of this monitoring be submitted to the DEEP.

The report that fulfills these requirements, the "Monthly Discharge Monitoring Report" (DMR), includes discharge data from all MPS units.

Consistent with prior annual AEOR submissions, water flow, temperature, pH, and chlorine data pertaining to MPS3 are summarized in Table 1.

2019 AEOR Page 1 of 3

Each monthly DMR identifies NPDES permit exceedances (i.e., events where a parameter value was beyond permitted limits) or exceptions (i.e., events where Permit conditions were not met) for the month. However, during 2019, there were no exceedances or exceptions at a discharge associated with MPS3.

2.3 NPDES Permit Renewal By way of background, in 2014 MPS established a team, and scheduled milestones, to ensure that a completed permit renewal application was submitted to the DEEP, in accordance with general requirements, prior to the permit's expiration in August 2015. The permit renewal application was submitted on February 6, 2015, and the DEEP issued a Notice of Sufficiency on March 6, 2015; therefore, the permit is administratively continued and in effect until its reissuance.

3. Environmental Protection Plan (EPP) Non-compliances:

No EPP non-compliances were identified for MPS3 in 2019.

4. Environmentally Significant Changes to Station Design or Operation, Tests, and Experiments:

No MPS3 design change records or system operating procedure changes initiated during 2019 included a determination that a significant unreviewed environmental question existed.

5. Non-Routine Reports of Environmentally Significant Events:

No non-routine reports were submitted in accordance with subsection 5.4.2 of the EPP.

2019 AEOR Page 2 of 3

Table 1. MPS3 NPDES data summary, Jan 1-Dec 31, 2019. Selected water quality parameters for MPS3(1).

Discharge pH Discharge 2019 Maximum Temp. Range Average Maximum Range(SU)

Average 11 Maximum Maximum Discharge Flow (OF)

Discharge _

SWS FAC (106 gpd)

Temp. (°F)

Temp. (°F)

FAC (ppm)

TRC (ppm)

(ppm)

Min Max Min Max January 1360.9 7.8 8.1 54.2 68.0 61.3 19.3

<0.02

<0.02 0.19 February 1360.4 7.9 8.2 55.1 65.9 60.1 21.0 0.05 0.05 0.16 March 1351.1 7.8 8.2 56.2 _ 68.2 62.3 21.1 0.02 0.04 0.19 April 1209.4 6.5 8.1 44.6 74.3 57.3 9.7

<0.02 0.02 0.21 May 1360.4.

6.4 8.2 48.6 90.4 64.2 11.0 0.03 0.03 0.18 June 1360.8 7.6 8.1 72.8 85.2 77.9 16.1 0.05 0.05 0.15 July 1360.7 7.8 8.1 78.9 88.4 84.1 14.4 0.03 0.04 0.15 August 1360.8 7.9 8.2 84.5 89.2 86.3 14.9 0.02 0.04 0.18 September 1360.8 7.9 8.2 84.3 89.0 86.1 15.9 0.05 0.07 0.16 October 1360.8 8.0 8.2 77.7 87.5 81.1 17.0 0.04 0.02 0.19 November 1361.3 7.9 8.2 66.5 91.4 72.5 17.1 0.03 0.04 0.22 December 1360.9 8.0 8.2 41.9 73.2 61.1 14.5 0.06 0.02 0.20 (1)

Parameters are measured at MPS3 discharge (DSN 001(), except forTRC (total residual chlorine), which is measured at MPS discharge (quarry cuts; DSN 001-1), and SWS FAC (service water system free available chlorine; DSN 001C-5).

2019 AEOR Page 3 of 3

Attachment to the 2019 Annual Environmental Operating Report January 1 - December 31, 2019 Executive Summary Section of "Annual Report 2018 - Monitoring the Marine Environment of Long Island Sound at Millstone Power Station, Waterford, Connecticut" dated July 2019

Executive Summary This report summarizes results of ongoing environmental monitoring programs conducted in relation to the operation of Millstone Power Station (MPS). MPS can affect local marine biota in the following ways: large organisms may be impinged on the traveling screens that protect the condenser cooling and service water systems; smaller ones may be entrained through the condenser cooling-water system, which subjects them to various mechanical, thermal, and chemical effects; and marine communities in the discharge area may also be subjected to mechanical, thermaL and chemical effects resulting from the outflow of the cooling water.

This report contains a separate section for each major biological monitoring program, some of which have been conducted without interruption since 1976. These long-term studies have provided the representative data and scientific bases necessary to assess potential biological impacts as a result of MPS construction and operation.

In addition to sections related to the biological monitoring program, this report includes a section providing a complete and thorough description of all National Pollutant Discharge Elimination System (NPDES) pennit compliance work undertaken for the implementation of flow reduction and/or entrainment mitigation technologies, operational methods or other measures undertaken in 2018, and a section which provides a comprehensive summary of activities and accomplishments of Dominion Energy Nuclear Connecticut (DENC) in the Niantic River Nitrogen Work Group effort.

Rocky Intertidal Studies Rocky intertidal habitats are extensive in the Millstone area, and support rich and diverse communities of attached algae and animals. Rocky intertidal studies at MPS are designed and implemented to characterize these communities. Analyses of rocky shore data to date indicate that changes attributed to MPS operation are minor, transient, and restricted to a small area along 150 meters of shoreline in the immediate vicinity of the discharge.

As in previous years, seasonal shifts in occurrence of annual algal species were noted at FI during 2018. These shifts included absence or abbreviated season for cold-water species (e.g.,

Monostroma grevillei, Protomonostroma undulatum, Spongomorpha arcta, and Dumontia contorta) and extended season for warm-water species ( e.g., Grinnellia americana, Antithamnion pectinatwn, and Grateloupia tun1turu). Similar shifts have been observed in most years included in this time-senes However, some species with cold-water affinity (e.g.,

Protomonospora, Dumontia) have recently occurred less regularly at MP and WP as well, reflecting regional temperature increases.

Thermal effects on dominant species' abundance and distribution patterns were also evident at FI in 2018, and most apparent in the low intertidal zone. Seasonally high abundance of Hypnea musciformis, a species observed for the first time in 2001, and expanded populations of Sargassum filipendula, Corallina officinalis, and Gelidium pusillum now characterize the lower shore community at FI.

Melanothamnus (previously Neosiphonia) han,eyi has maintained a perennial population at FI in 2018, but occurred mainly as a summer annual at sites unaffected by MPS.

Ascophyllum nodosum growth, represented as the most recent internodal length, was greatest at FI in 2018, significantly higher than both MP and WP. Although growth was slightly lower at WP, with all sites combined, growth in 2018 was lower than 2017, and continued a declining trend observed since 2011, but showing no correlation to annual mean water temperature.

This continues to demonstrate no clear relationships among monitoring sites, or correlation with station operating conditions, indicating that the thermal plume from MPS has had little effect on local populations.

Natural influences of other factors, such as ambient temperature conditions, stonns and wave action, nutrients and light, play the dominant role in determining Ascophyllum growing conditions in tl1e Millstone area.

The rocky intertidal monitoring program has also documented regional patterns and modifications to shore communities umelated to MPS operation. These include the introduction to the region of three exotic red algae (Antithamnion pectinatum in 1986, Grateloupia tun1tunt in 2004, and Dasysiphoniajaponica in 2010), decreases in barnacle abundance in recent years, and long-term increases in abundance of the common seaweeds Fucus vesiculosus and Chondnts crispus.

Eelgrass Eelgrass (Zostera marina L.) was monitored at three locations in the vicinity ofMPS. Data from 2018 surveys indicated that tl1e two study sites nearest to the MPS thermal plume (Jordan Cove (JC) and White Point(WP))

supported healthy and expansive eelgrass populations, consistent with results since the study began in 1985.

While there has been moderate variability in abundance and distribution over the entire study period at these two sites, this variability was not related to MPS operation.

Both predicted and measured thermal input to these sites from the cooling water discharge is at most minimal ( <

1 °C above ambient conditions) and well below levels considered stressful to eelgrass.

Executive Summary ii

By comparison, high eelgrass population variability has been observed in the Niantic River, where complete and often sudden eelgrass bed losses were documented on six separate occasions prior to 2018. Data from the 2018 survey show continued recovery of some eelgrass beds in the Niantic River, with some expansion into Smith Cove.

Because the Niantic River is located well away from any influence of the MPS thermal plume, eelgrass population fluctuations there must be related to environmental factors such as increasing ambient seawater temperatures, disease, increased turbidity, and waterfowl grazing. Results from this monitoring therefore suggest that fluctuations in eelgrass populations observed at sites in the Niantic River are due to changes in local and regional environmental conditions and not to MPS operation.

Benthic Infauna Benthic infauna! monitoring documented long-term trends in sediment characteristics at all the subtidal sites in the vicinity of MPS. At the effluent sampling site (EF),

the sedimentary environment remains coarse, with low silt/clay which is related to discharge of cooling water into Long Island Sound (LIS) at the Quarry cuts.

Sediments at the intake site (IN) were consistent with sediment characteristics prior to dredging during MPS MPS3 construction.

Sediments at Jordan Cove (JC) continued to have the smallest mean grain size and highest silt/clay content of all four stations, attributed to the discharge area scouring and fine sediment deposition in the vicinity of the JC site. Sedimentary characteristics at the reference site at Giants Neck (GN) were similar to previous years' observations and continued to reflect natural variability umelated to MPS.

The 2018 infauna! communities at all sampling sites continued to respond to sedimentary environments.

Dominant taxa at all sites were reflective of climax communities that have undergone long-term successional development in response to increased stability of their sedimentary environments.

Multidimensional scaling showed distinct separation of communities affected by construction and initial operation of MPS3, but also illustrated regional temporal community shifts umelated to MPS operation. Changes in community structure and functional group dominance at subtidal benthic infauna!

stations during the period 1980-2018 reflect not only effects related to construction and initial operation of MPS3, but other regional and/or local biotic and abiotic factors. Community changes at the reference site (GN) during the period 1980-2018 were attributed solely to these latter factors, and not to operation of MPS.

Lobster Studies Impacts associated with recent MPS operations on the local lobster population were assessed by comparing results of the 2018 study year to data collected from 1978 through 2017. Emphasis has been placed on assessing long-term trends in the abundance and population characteristics of lobsters collected in the Millstone Point area.

Throughout LIS, the lobster population was stable or increasing from 1978 through 1999. Commercial lobster catches in LIS precipitously declined from 2000 to 2013 and have stabilized at record low levels through 2018. In th.is study, lobsters in the MPS area have shown a similar trend, with abundance indices (total catch and catch per unit effort (CPUE)) nearly 70% lower in research. pots and 98% lower in trawls during the past seven years (2012-2018), compared to highest levels in the 1990s. Declines in pot and in trawl catch.es were unrelated to MPS operations and attributed to an increase in mortality associated with ambient seawater temperature rise and temperature mediated stressors that include a shell disease affecting lobster populations from eastern LIS to the Gulf of Maine.

Egg-bearing females have been disproportionately and negatively impacted by shell disease in comparison to other lobsters.

In addition, predation by the high number of Tautog caught in traps contributed to record high lobster mortality during 2015 -

2018. Declines in the abundance of legal-size lobsters were attributed in part to the outbreak of shell disease and to a nearly 5 mm increase in the minimum legal-size since 1978. Recent reductions in landings oflegal-size lobsters harvested by commercial lo bstennen in eastern LIS coincided with declines observed in this study, and lobster catches remained severely depressed in other areas of LIS since the lobster die-off observed in 1999.

Long-term trends observed in lobster population characteristics during the past four decades (molting, female size at

maturity, abundance and size characteristics of egg-bearing females) appear related to warmer ambient seawater temperatures and/or the recent outbreak of shell disease, and not MPS operation.

Increased ambient water temperature may be responsible for the increased susceptibility and transmission of diseases affecting lobsters in LIS, which is at the southern boundary of their range of distribution in nearshore waters.

The number oflobster larvae entrained through the MPS cooling water systems was highly variable and low in recent years, due to low adult lobster abundance and low larval densities throughout LIS. Impacts associated with impingement oflobsters at MPS have been greatly reduced by the use of aquatic organism return systems at both units, which return impinged lobsters to Niantic Bay with documented very high survival rates.

Fish Ecology Studies Executive Summary 111

Results from the Fish Ecology monitoring studies during 2018 indicate that no long-term abundance trends for various life stages of seven selected species could be directly related to MPS operation. No significant long-tenn trends in abundance were identified for Anchovy, Cunner and Tautog eggs, American Sand Lance and Grubby larvae, or juvenile and adult Silversides. Atlantic Menhaden larvae showed a significantly increasing trend in abundance, as did juveniles collected in seines. A significant decreasing trend was exhibited for Grubby collected at the Intake, Jordan Cove, and Niantic River trawl sampling sites. Over the past 43 years, Cunner and Tautog larval abundances have significantly increased.

Juvenile and adult trawl catches of Cunner increased at the Niantic River (NR) station and decreased at the Jordan Cove (JC) trawl stations.

Trawl catches of juvenile and adult Tautog have significantly increased at the NR station. No trends in the abundance of juvenile and adult Cunner and Tautog were observed at 1N following the removal of the MPS3 intake cofferdam in 1983.

The magnitude of entrainment is dependent upon egg and larval densities and condenser cooling water flows during their periods of occurrence.

Reductions in cooling-water flows have been implemented at MPS with the use of VFDs during the peak period of Winter Flounder annual spawning. In addition to the Unit 3 fish return, which was in operation at unit start-up in 1986, impingement impacts were further reduced at MPS with the installation of a fish return at Unit 2 in early 2000.

The implementation of these mitigation measures serve to minimize entrainment and impingement impacts at MPS.

Annual variations in ichthyoplankton entrainment likely reflected differences in spawning and transport of eggs and larvae within LIS.

Other factors, such as extremes in seasonal water temperature, may also affect larval growth and development. A number of temporal and spatial changes were identified in the community of fishes and macroinvertebrates collected in the MPS trawl monitoring program. These changes were unrelated to the operations of MPS, but rather were associated with shifts in the dmninance of individual taxa from changes in habitat, range extensions or contractions related to a warming trend in ambient seawater temperature, and changes in fishing rates and fishing regulations.

Winter Flounder Studies Various life history stages of Winter Flounder have been monitored since 1976 to determine what effect, if any, MPS may have on the local Niantic River population, particularly through the entrainment of larvae. Over the past two decades, low Winter Flounder abundance levels have been found throughout LIS by the Connecticut Department of Energy and Environmental Protection (CTDEEP). During the same time pe1iod, adult Winter Flounder abundance in the Niantic River has remained low. Reflecting the continued trend of low abundance, The.6.-mean Catch Per Unit Effort (CPUE) for adult fish(> 15cm) captured in the year-round Trawl Monitoring Program (TMP) in 2018 was tied with 2016 as the lowest (0.6) value since 1976.

In 2018, overall combined larval abundances in Niantic Bay (sampling sites EN and NB) and Niantic River (sites A, B, and C) were below average for their respective time-series. Stages 1 and 2 larval abundances in the River stations were below time-series means, while Stages 3 and 4 larval abundances were above time-series means. All stages of larval abundances in the Niantic Bay Stations were below time-series means. Relative to the Niantic River, larval abundance in Niantic Bay has increased in recent years, suggesting higher production in LIS rather than in estuaries such as the Niantic River.

Summer juvenile abundance from the 2018 Niantic River beam trawl survey was low for the time-series and reflected low larval abundance.

The number oflarvae entrained at MPS is a measure of potential impact to Winter Flounder. Annual estimates of entrainment are related to both larval densities in Niantic Bay and MPS cooling-water volume. The 2018 entrainment estimate of 51 million reflected slightly lower than average Niantic Bay larval densities. An entrainment reduction of 33.12% (based on maximum permitted flow) in 2018 can be attributed to the use of the variable frequency drives (VFDs) during the "Interval" from April 4 to May 23 (defined in the MPS NPDES permit as the period "from April 4 to May 14 or the first day after May 14 when the intake water temperature reaches 52 °F, whichever is later, but no later than June 5").

Processes that are unrelated to MPS operation and which occur after juvenile Winter Flounder leave shallow nursery waters during the fall of their first year of life seem to be operating to account for fewer adults. A bottleneck in recruitment may occur during the late juvenile life stage (ages-1 and 2), probably from predation. Environmental effects, including changes to the Niantic River habitat ( e.g., widely fluctuating eelgrass abundance), a warming trend in regional seawater temperature, and interactions witl1 other species (e.g., predation), especially during early life history, are also important processes affecting Winter Flounder population dynamics.

Results from Winter Flounder studies through 2018 suggest that MPS operations have had minimal effects on Winter Flounder biomass in the Niantic River. Declines in stock size have been greatly evident on a regional basis, including LIS, Rhode Island and all other Southern New England waters. Entrainment during the larval life stages of Winter Flounder occurs, however there has been large variation in the amount oflarval mortality and Executive Surnmary iv

recruitment in recent years, both occuning independently of MPS operations.

Executive Summary v