ML19064B345

Comment from Pine Dubois on the Pilgrim Nuclear Power Station; Consideration of Approval of Transfer of License and Conforming Amendment (NRC-2018-0279)

ML19064B345
Person / Time
Site:	Pilgrim
Issue date:	03/04/2019
From:	DuBois P Jones River Watershed Association
To:	NRC/SECY
SECY/RAS
References
NRC-2018-0279
Download: ML19064B345 (138)

Text

From: Pine duBois To: Docket, Hearing Cc: Lamb, John

Watson, Bruce

Klukan, Brett

David Johnston

Jack Priest

Sean Mullin

John Giarrusso

Subject:

[External_Sender] Revised PSDAR and Revised Site-Specific DCE for Pilgrim Nuclear Power Station Date: Monday, March 04, 2019 5:05:27 PM Attachments:

JRWA comment Holtec PSDAR.pdf For your consideration I am attaching comments to address some errors and omissions in the (revised) PSDAR which could reflect on the DCE submitted by Holtec International. My

concern is that the NPDES Permit and Fact Sheet referenced by Holtec is still in DRAFT form

under review by EPA, and that without addressing particular challenges the companies will

face over time due to rising sea levels, the potential to impact successful decommissioning and

site restoration can have significant cost consequences that must be addressed.

Thank you for your consideration Pine duBois pine@jonesriver.org Executive Director Jones River Watershed Association Jones River Landing

55 Landing Road

Kingston, MA 02364

781-585-2322 office

781-424-0353 (m)

Save the River, Save the World UNITED STATES OF AMERICA NUCLEAR REGULATORY COMMISSION BEFORE THE ATOMIC SAFETY AND LICENSING BOARD In the Matter of Docket No.

NRC 2018-0279 Entergy Corporation Pilgrim Nuclear Power Station License Transfer Agreement Application Via Email: hearingdocket@nrc.gov PILGRIM WATCH COMMENT DOCKET NO

. NRC 2018-0279 Mary Lampert Pilgrim Watch, director

148 Washington Street

Duxbury MA 02332 Dated, March 4, 2019

2 PILGRIM WATCH COMMENT DOCKET NO. NRC 2018-0279 Pilgrim Watch provides comment in the above captioned matter that includes the application (LTA); management purposes (LTA En closure 2); and -S pecific Cost Estimate (LTA Attach ment 2). Pilgrim Filed a Petition to Intervene and Hearing Request in Docket No. 50-293 & 72-1044 LT on February 20, 2019. This comment largely repeats the bases and facts of Petition to Intervene and Hearing Request. New information is included, also. We are commenting here in appreciation of the likelihood that the NRC staff that reviews will be part of the review of the Petition to Intervene and Request for Hearing.

Pilgrim Watch shows that:

a. Th e LTA documents do not provide reasonable assurance that there is sufficient financial assurance. A s a result , the funding shortfall will place public health, safety , the environment, and financial interests at risk. b. The documents also show that the Commission must conduct, at minimum, a compreh ensive environmental assessment at the beginning of the decommissioning process that is needed to determine actual cost estimates and to prevent the runoff of contaminants offsite. Previous site- specific environmental impact statements do not bound environmental impacts.

Therefore, the application should be denied

and a hearing provided to the Commonwealth and Pilgrim Watch.

3 FINANCIAL ASSURANCE

- SECTION 1 LTA does not provide the required financial assurance. It does not show that either HDI or Holtec Pilgrim is financially responsible, or that either has or has access to adequate funds for decommissioning. Neither does the LTA provide any reasonable assurance that Holtec Pilgrim and HDI have, or will have, the financial resources required to deal wi t h environmental impacts that would place the public health, safety, and the environment at risk

. BASES 1. As discussed in detail below the LTA and PSDAR that Entergy and Holtec have filed with the NRC are misleading and incomplete and are based on incorrect but important assumptions

. They do not present the evidence that would be required for the NRC properly to conclude that there is the level of financial assurance required to meet the regulatory requirements for the proposed license transfer and amendment. It is well established that Pilgrim Watch e a license amendment.

1 2. The Atomic Energy Act (AEA) requires the NRC to ensure protection of public health, safety, and the environment (AEA, Sec.2(d)

): The processing and utilization of source, byproduct, and special nuclear material must be regulated in the national interest and in order to provide for the common defense and security and to protect the health and safety of the public.

3. The NRC agrees that a shortfall in decommissioning funding would place public health, safety, and the environment at risk. Financial assurance is critical, and a licensee must ensure that sufficient funds are available throughout the decommissioning proce ss: The NRC has a statutory duty to protect the public health and safety and the environment. The requirements for financial assurance were issued because

1 In re Entergy Nuclear Vermont Yankee, LLC and Entergy Nuclear Operations, Inc., Docket No. 50

-271-LA-3, LBP-15-24, at 13 (Aug. 31, 2015), vacated, CLI-16-08.

4 inadequate or untimely consideration of decommissioning, specifically in the areas of planning and financial assurance, could result in significant adverse health, safety and environmental impacts.

The requirements are based on extensive studies of the technology, safety, and costs of decommissioning (53 FR 24018). The NRC determined that there are significant radiation hazards associated with non

-decommissioned nuclear reactors. The NRC also determined that the public health and safety can best be protected if its regulations require licensees to use methods which provide reasonable assurance that, at the time of termination of operations, adequate funds are available so that decommissioning can be carried out in a safe and timely manner and that lack of funds does not result in delays that may cause potential health and safety problems (53 FR 24018, 24033). The purpose of financial assurance is to provide a second line of defense, if the financial operations of the licensee are insufficient, by themselves, to ensure that sufficient funds are available to carry out decommissioning (63 FR 50465, 50473).

2 4. Holtec Pilgrim have not shown that they possess, or will be able to procure, the funds necessary to safely decommission the Pilgrim site. The lack of sufficient funds places Pilgrim Watch and its members, a nd neighboring citizens at risk that the se proposed new licensees will deplete the Decommissioning Trust Fund before they have met their decommissioning obligations. A ny shortfall in the Decommissioning Trust Fund would put Pilgrim Watch and its members, and indeed the entire Commonwealth of Massachusetts, at risk that the site will not be fully radiologically decontaminated.

3 5. As explained in detail below, the limited assets of the proposed new licensees, Holtec Pilgrim and HDI, are insufficient to pay even the decommissioning costs outlined in the PSDAR and LTA, much less to cover any significant or unconsidered shortfalls resulting from

2 NRC, Questions and Answers on Decommissioning Financial Assurance, at 1 (ADAMS Accession No. ML111950031).

3 Entergy, LBP-15-obligations is part of the bedrock on which NRC has built its judgment of reasonable assurance of adequate protection for the public health and

5 likely costs that Holtec incurs before the entire site (including the ISFSI) is decommissioned and released.

6. The PSDAR and LTA do not contain the information to demonstrate reasonable assurance that sufficient funds are available to properly complete the decommissioning process. Neither do they show the detailed cost estimate for decommissioning, or an adequate contingency factor any identification of and justification for using the key assumptions , required by 10 C.F.R §72.30(b)

7. Holtec PSDAR and Decommissioning Cost Estimate provide essentially no margin for error. They admit that only $3

.6 million (about one

-third of one percent of the supposed current value of the DTF) will remain after the decommissioning work set forth in the PSDAR and LTA have been completed; and

, say that they expect to spend the entire Contingency Allowance accomplishing the work outlined in the PSDAR.

8. do not include the adequate contingency factor required (PSDAR, Sec. 4.5)

9. 40 million legal claim.

(Common wion for Leave to Intervene, Feb 20, 2019, pg.,11) 10. its exemption request to use the DTF for spent fuel management costs and site restoration. If approved, it could lead to a shortfall in the amount of funding available to safely decommission and radiologically decontaminate the site and manage the spent fuel onsite endangering public health and safety.

Petition for Leave to Intervene, Feb 20, 2019, pg., 24)

6 11. The the only reason that the two LLCs, HDI and Holtec Pilgrim, are supposedly financially qualified is that decommissioning costs and spent fuel ., 18.) inclu., 17) because under the terms of the Decommissioning Operator Services Agreement costs of post

-shutd(Letter, pg. 3; LTA Enclosure 1, pg

., 1) g., 16) 10. Nothing in the LTA or PSDAR suggests that any Entergy entity, or any Holtec entity except the two named Holtec LLCs, will have any financial responsibility for any of what the  ; NRC does not have the authority to require a parent company to pay for the decommissioning expenses of its subsidiary

-licensee, except to the extent the parent may voluntarily provide a PCG(see Questions and Answers on Decommissioning Financial Assurance, ML111950031

).

7 11. At a meeting of the Nuclear Decommissioning Citizens Advisory Panel any such guarantee

. 12. At a NDCAP meeting, Holtec also said that it expects to sue the DOE for reimbursement of costs that Holtec will incur for spent fuel management , and indicated that it would not agree to put whatever monies a Holtec entity might recover from DOE into the Pilgrim Decommissioning Trust Fund, despite the fact that Holtec expects the NRC to allow Holtec to use almost half of the total funds in the DTF for the very same spent fuel management costs that DOE might reimburse.

13. Even if Holtec, Holtec Pilgrim, and HDI did agree to use any recovery from DOE to reimburse the DTF for Pilgrimlicensee attempts to use such potential future recoveries from DOE to show financial assurance

- for the simple reason that no recovery is guaranteed and the amount that might be recovered i s uncertain. See, 10 C.F.R. § 50.75(e)(iii)(A) (chosen method of financial assurance must 13. The proposed license transfer and amendment are explicitly intertwined with Holtec Post-Shutdown Decommissioning Activities Report (PSDAR), including cost estimates for decommissioning, spent fuel management, and site restoration, and also rely on outdated, incomplete and inaccurate 2000 GEIS and 2006 SEIS. 14. Neither the costs nor the economi2 GEIS , 2006 SEIS and other documents listed. A site assessment at the Pilgrim site would provide new and important showing that the 200 2 GEIS and 2006 SEIS are outdated and that additional decommission 8 15. NRC approval of the license transfer and amendment request would effectively approve the PSDAR and its financial and environmental analyses and assurance. The PSDAR is material to this proceeding -world consequences of approving the [license 4 16. The proposed license transfer and PSDAR will inexorably lead to a shortfall in the amount of funding available to fully and safely decommission and radiologically decontaminate Pilgrim and to manage its spent nuclear fuel as long as it remains on

-site. Any such shortfall could place public health, safety, and the environment at risk.

FACTS Fundamental fact s are that Holtec Pilgrim and HDI are not financially qualified, and that neither can provide the required financial assurance. The LTA makes clear that the only Trust Fund; nothing in the LTA indicates that either has, or has access to, any additional funds; and as shown below, there is not and will not be sufficient money in the Decommissioning Trust Fund to pay the costs that will be incurred during decommissioning.

THE LTA DOES NOT ENSURE SUFFICIENT FUNDS FOR DECOMMISSIONING As discussed in detail below, the LTA (and the PSDAR and DCE it includes) does not ensure that adequate funds for decommissioning will be available for at least the following reasons. Holtec makes incorrect assumptions and ignores significant facts each of which will result in additional costs

, above and beyond the funds available for decommissioning. Although 10 CFR.

4 Entergy, LBP-15-24, at 41.

9 §72.30 requires it to do so, Holtec has not justified key assumptions contained in the PSDAR and DCE. Even assumptions, only 0.03% of the DTF will remain after decommissioning. The DTF will not be sufficient if any assumptions are too low (as we show that they are) or if Holtec Pilgrim and HDI incur any of the multitudinous additional costs tha t are not considered in the PSDAR or DCE.

Examples the DTF is not sufficient, and that Holtec Pilgrim and HDI are not financially responsible and have not provided financial assurance include the following:

A. Allowance is sufficient B. assertion that there is s ufficient money in the DTF incorrectly assumes that decommissioning costs will not rise faster than inflation C. If the exemption request to use the DTF for spent fuel management and site restoration are approved, it could lead to a shortfall in the amount of funding available to safely decommission and radiologically decontaminate the site and manage the spent fuel on site endangering public health and safety.

D. E. unexplained assumption that DOE will remove all spent fuel by 2063.

F. G. Hbased on outdated documents.

H. decommissioning.

I. cost estimate assumptions ignore the cost of managing Low Level Radioactive Waste 10 J. LTA ignores potential costs from fires in structures, systems and components containing radioactive and hazardous material.

K. DCE fails to consider costs likely to result from climate change impacts on the site. L. Holtec cost estimates fail to consider that a significant shortfall in funds could occur if DOE requires repackaging of spent nuclear fuel into new containers approved by DO E for transportation.

M. Holtec fails adequately to consider delays in the work schedule leading to increased costs for overhead and project management.

N. cost estimates fail to consider pending state

-law requirements that will decrease funds available for radiological decontamination O. DCE fails to consider DTF funds that would not be available if NRC does not site remediation.

P. DCE fails to consider the economic consequences if the license exemption requests filed by Entergy may not be transferable to Holtec adding additional costs.

Q. pathway receptor populations and for that matter in the general public R. adiological accident(s)

S. Funds Necessary to Decommission the ISFSI.

Each of these is discussed in detail below.

A. Allowance is Sufficient n adequate contingency factor.

11 a Contingency Allowance of 17 percent was determined to be reasonable for the Pilgrim decommissioning project [and] is incorporated into the estimate of License Termination, Spent Fuel Mana(PSDAR, Sec. 4.5)

Site Restoration costs is $237 million. However, Holtec admits that (PSDAR, Sec. 4.5) that its inflation or escalation of the price of goods and services over the course of the project. contingency rate of inflation, spent fuel management costs incurred after 2062, site restoration costs resulting from the fact that the Pilgrim site is not cleaand PSDAR have essentially ignored.

-that [s] n adequate contingency facto rancial assurance.

B. hat there is Sufficient Money in the DTF Incorrectly Assumes that Decommissioning Costs Will No t Rise Faster Than Inflation In the PSDAR and LTA, Holtec Pilgrim and HDI assumed that the Decommissioning Trust Fund would grow at the rate of 2% more than inflation. Pilgrim Watch will not quarrel with this assumption.

However, they also assumed, incorrectly and with no apparent ba sis o r justification as required by 10 CFR §72.30(b)(3), that decommissioning costs will not rise faster than inflation:

12 The decommissioning costs presented in this report are reported in 2018 dollars. Escalation of future decommissioning costs over the remaining decommissioning project life

-; DCE, pp. 7, 18)

This assumption is simply wrong. Both the history of decommissioning cost s and the that decommissioning costs will increase more than inflation. This one fact alone demonstrates that the Decommissioning Trust Fund does not, and will not, provide that the existing decommissioning trust funds provide the appropriate basis for the The NRC Questions and Answers on Decommissioning Financial Assurance specifically state that decommissioning costs will increase at a rate higher than the rate of inflation , and that over a period of only 20 years (40 years less than the 60 year period allowed for decommissioning) there will be 2.5 to 5.6 times increase in costs, i.e., the annual increase in costs will be 5% to 9%

- much more than the average annual 3.7% rate of inflation: 5 NRC formulas represent the cost to decommission today, not in the future. Due to rising costs, the future value of decommissioning will be much larger than the NRC formula calculated today. For example, using the range of cost escalation rates based on NUREG - 1307, the increase in cost over a 20-year license renewal period would range from 2.5 to 5.6 times estimated cost, not counting costs that are not included in the formula, such as soil contamination.

The rates of increase in decommissioning cost are higher than general inflation 5 Over the past 60 years, the average annual US rate of inflation has been about 3.7 percent. Over the last 10 years it has been about 1.55%; in 2018 it was 2.44%.

13 Callan Associates produces an annual analysis and report of decommissioning funds and costs. Its 2015 Nuclear Decommissioning Funding Study 6 said that decommissioning cost estimates have risen 60% since 2008%, and 2014 decommissioning cost estimates rose approximately 11% from the previous year. 2015 Nuclear Decommissioning Funding Study, p. 3.

8 7 reported that decommissioning costs increased by about 80% (from $55 billion to $89 billion, an annual rate of about 5 percent) from 2008 and 201

7. Study, pp. 3, 9. During the same period, inflation was about 1.3% annually; in other words, decommissioning costs increased at a rate of 3.7% over inflation.8 In short, both the NRC statements are clear that there is no rinflation. The only rational and factually supportable assumption would be that decommissioning costs will increase at an annual rate that is at least about 4% higher than the rate of annual inflation.

9 The unavoidable conclusion is that einflationdecommissioning costs w ill wipe--. Any increase in

6 https://www.callan.com/library/

2015 7 https://www.callan.com/library/

2018 8 It is important to note that Callan reported that total estimated decommissioning costs decreased about 2.5% in 2017. The decrease was attributed to the fact that a number of reactors had decided to decommission rapidly after shut--year period (as https://www.powermag.com/data

-shows-nuclear-plant-decommissioning

-costs-falling/. - specific decommissioning costs.

9 Taverage of about 3.3% more than average inflation and is 3.3% to 7.3% more than inflation over the past 10 years

-year history reports an average increase in decommissioning costs of about 4.4% more than inflation.

14 decommissioning costs in the ranges that the NRC (5% to 9%) predicts , and Callan (5% to 6%)

re ports , would result in a hundreds of millions of dollars shortfall in the DTF

. For example, the HDI decommissioning cost estimate ( 10 CFR §72.30(b)(2) 2019-2024 at a total 2018

-dollar cost of about $577 million.

Holtec projects accomplishing most site restoration in 5 years - 2021-2025 at a cost, again in 2018 dollars, of about $39 million.

Based on calculations, if decommissioning costs were to increase at an annual rate of 4% more than inflation, a fair assumption based on NRC predictions and Callan Associates reports the 2018-dollar cost of decommissioning/license termination from 2019-2024 would increase to about $6 7 2 million, $95 million more than the DCE projectio n; and the 2018

-dollar cost of site restoration from 2021-2025 would be about 47 million, $

8 million more than the DCE allows.

10 million, about $221 million in 2019

-2021 and an average of about 6.7 million a year from then to 2063. If these costs were also to increase at an annual rate of 4% over inflation, calculations show that the cost of spent fuel management from 2019

-2063 would increase to over $950 million, $450 million more than the DCE allows.

In sum, if decommissioning costs increase as the NRC and Callan say they will, at an annual rate of 4%, the cost of decommissioning Pilgrim will be about a billion dollars more than

10 Because HDI plans to decommission at the front end rather than almost 60 years after Pilgrim shuts down, its actual 2018

-dollar costs of decommissioning are far less than 15 are considered

. llion, after all is said and done.

Pilgrim Watch does not doubt that others, based on different assumptions of periods of time or the annual increase in decommissioning costs, might make somewhat different assumptions. But the bottom line is clear decommissioning costs will (as the NRC has said) increase faster than inflation, neither Holtec Pilgrim nor HDI has or will have access to sufficient assets, and neither Holtec nor HDI is financially responsible or has provided the necessary financial assurance. Pilgrim Watch does not say that a decommissioning cost estimate must be precise. But for the NRC regulations and procedures to make any sense at all, a decommissioning cost estimate must be based on reasonable and justifiable assumptions. sumption that decommissioning costs would not rise faster than inflation was not reasonable or justified. See 10 CFR 72.30(b)(3) that requires Identification of and justification for using the key assumptions For this reason alone, absent enforceable agreements by Holtec, Holtec and Holtec Pilgrim to provide significant additional financial assurance, such as a large Parent Company Guarantee (PCG) and agreement to put all recovery from the DOE into the DTF, the LTA cannot properly be granted. C. If the exemption request to use the DTF for spent fuel management and site restoration is approved, it could lead to a shortfall in the amount of funding available to safely decommission

, radiologically decontaminate

, and manage the spent fuel on site endangering public health and safety

16 definition does not include: the removal or storage of spent fuel; demolition of decontaminated structures; or Site restoration activities after residual radioactivity has been removed. NRC Rules restrict use of the Decommissioning Trust Fund to reducing granting exemptions to allow DTF to be used for demolition and site restoration.

However , by allowing use of the fund for these other jobs, reduces what is left for removing radiological contamination.

D. $40 Million Legal Claim Motion to Intervene and Request for Hearing, February 20, 2019, at 11 explains that:

Entergy and Holtec also fail to inform the Commission that Boston Edison Company (doing business as Eversource) has an outstanding legal claim that is likely to decrease the amount of money that Holtec may recover from the U.S. Department of Energy (DOE) for spent fuel management by approximately $40 million. When Boston Edison Company sold Pilgrim to Entergy, Boston Edison claims that it provided Entergy with funds to cover post decommissioning spent fuel management costs. In re Boston Edison Co., 1999 WL 239703, 192 P.U.R. 4th 418, 3

-4 (Mass. D.T.E. 1999). breach of the Standard Contract, Boston Edison would not have incurred them.

After a lengthy trial, the United States Court of Claims Federal Circuit Court agreed million. Subsequently, the United States Court of Appeals for the Federal Circuit private parties should not set the amount of the government's liability for partial -transfer breach cannot be determined until the actual costs of [spent nuclear fuel] disposal is incurred at the time of 17 Edison Co. v. United States, 106 Fed. Cl. 330, 334 (Fed. Cl. 2012) (citing Boston claim of $40 million until after the commencement of decommissioning and spent fuel management costs are incurred. Entergy Nuclear Generation Co. v. United States, 130 Fed. Cl. 466, 472

-73 (Fed. Cl. 2017) (citations omitted). Throughout this litigation, DOE has consistently stated that if the Court orders DOE to pay Boston Edison damages for spent fuel management, DOE will reduce the amount that it pays Entergy by the same (i.e., DOE will not pay twice for the same spent fuel management damages).

Entergy and Holtec have not accounted for this potential reserved claim in the LTA and relbreach of the Standard Contract. See LTA, Encl. 1, at 18

-19. Instead, Holtec states that it intends to recover from DOE all of its spent fuel management costs caused by because it fails to acknowledge that any spent fuel management costs it recovers is likely to be reduced by at least the approximately $40 million potentially due to Boston Edison. This omission provides further reason to question the analysis that adequate financial assurance exists in this case.

E. estimated spent fuel management costs are b ased on the unlikely and unexplained assumptio n that DOE will remove all spent fuel by 2063. The spent fuel management at least three unexplained and unlikely assumption s: that DOE will remove all spent fuel from the Pilgrim site by 2062

. (Holtec PSDAR, pgs., 23 and 58), that Holtec will never have to repair or replace any failed casks or pads, and that Holtec will not to repackage spent nuclear fuel into new containers approved by DOE for transportation. All of these assumptions are unjustified.

18 Holtec assumes and, assuming a maximum rate of transfer described in the DOE Acceptance Priority Ranking & Annual Capacity Report (Reference 10), the spent fuel is projected to be fully removed the Pilgrim site in 206 2, consistent with the current DOE spent fuel management and acceptance strategy (References 9 and 10).. 23. Pilgrim Watch will assume arguendo removing spent fuel from Pilgrim will then take 32 years to accomplish.

But there is no reasonable basis for Hol treferences upon which it rests.

Reference 9 is concerned only with the rate of transfer to a site that has been constructed and is ready to accept spent nuclear fuel. The only Holtec reference that is concerned with when such a site might actually exist is Reference 10, January 2013 Strategy for The Management and Disposal of Used Nuclear Fuel and High

-Level Radioactive Waste). 11 Holtec ignores that the DOE strategy is a framework for moving toward a sustainable program to deploy an integrated system capable of transporting, storing, and disposing of used nuclear fuelegy, p. 1). It does even try to guess by when an interim or geologic repository might actually exist.

11 https://www.energy.gov/sites/prod/files/Strategy%20for%20the%20Management%20and%20Disposal%20of%20Used%20Nuclear%20Fuel%20and%20High%20Level%20Radioactive%20Waste.pdf

19 Holtec2 030 : With appropriate authorizations from Congressplans to implement a program over the next 10 years that: Sites, designs and licenses, constructs and begins operations of a pilot interim storage facility by 2021 with an initial focus on accepting used nuclear fuel from shut-down reactor sites; Advances toward the siting and licensing of a larger interim storage facility to be available by 2025 that will have sufficient capacity to provide flexibility in the waste management system and allows for acceptance of enough used nuclear fuel to reduce expected government liabilities; and Makes demonstrable progress on the siting and characterization of repository sites to facilitate the availability of a geologic repository by 2048.

The key s here are: W here have been no such authorizations in the 6 years since the DOE Strategy was announce d Six years have passed since the DOE Strategy was announced. Tknowledge, no such plans have been implemented. NLTA. Advances toward the siting and licensing of a larger interim storage facility to be available by 2025. sare that Holtecapplication

, to construct and operate a consolidated interim storage facility in New Mexico is pending before the NRC; and Interim Storage Partners (ISP) application for a site in Andrews County Texasthat either of the se facilit ies will be sited, licensed or available by 2025.

Makes demonstrable progress to facilitate the availability of a geologic repository by 2048.

20 knows is that a number of bills relating to the storage of spent nuclear fuel have been introduced in Congress.

In short, the legislation is needed -14) The fact that the Strateg y provides no rational Strategy: Full implementation of this program will require legislation to enable the timely deployment of the system elements noted above. DOE Strategy. p

. 2 This Strategy provides a basis for the Administration to work with Congress. DOE Strategy. p

. 4 characterized, and the repository designed and licensed by 2042; and the repository constructed, and its operations started by 2048. DOE Strategy. p

. 8 The unavoidable fact, that H avoids, is that no one knows when there will be an interim Congress has not passed enabling legislation. There is significant opposition to both lanned interim site in New Mexico

. Yucca has made no progress; there are hundreds of contentions opposing it

, 12 along with anticipated lawsuits along transportation routes

- from cities, states, environmental groups, such as NIR S 13 12 http://www.state.nv.us/nucwaste/licensing/Contentions_NV.pdf. 13 Civilian Nuclear Waste Disposal, Congressional Research Service, Sept 6 2018. ( https://fas.org/sgp/crs/misc/RL33461.pdf); www.NIRS.org

21 Nuclear waste may be stored at Pilgrim indefinitely, despite the unsupported assumption in the PSDAR (section 5.1) that it will leave the site beginning in 2030 and ending in 2062.

years;14 that would be until 3019 for Pilgrim, 57 years longer p. 60-61) estimated on-going spent fuel storage costs at $ 7.2 million per year in 2018 dollars. Even if one were to assume that there would be no greater

-than-inflation increase in those costs, those 57 additional years of spent fuel storage would add more than

$38 0 estimated cost

. Again, Holtereasonably expected spent fuel management expenses. LTA also makes the unexplained assumptions that Holtec will never have to repair or replace any failed casks or pads, and not will not have to repackage spent nuclear fuel into new containers approved by DOE for transportation. The PSDAR and DCE include no costs for repair or repackaging.

be repacked so that they can be transferred to either an interim or permanent repository. In addition, and both before and after 2062, Holtec will be responsible for repairing or replacing any dry casks that might fail; and will be required to replace both the casks and ISFSI storage pad if spent fuel remains on site every 100 years. The first casks will be 100 years old less than 100 years from now.

14 https://www.nrc.gov/waste/spent

-fuel-storage/wcd.html

22 Holtec will be required to continue paying ISFSI maintenance and security as long as spent fuel is on site, perhaps indefinitely.

Also, the canisters may corrode and leak and are vulnerable to acts of malice, adding considerable costs for mitigation. (See discussion regarding severe accidents at pp. 6 6-80) about the likely costs, and for this additional reason fails to provide assurance that Holtec Pilgrim and HDI are financially responsible and will have the funds required for decommissioning.

F Holtec and the NRC appear to agree that an accurate cost estimate is necessary for a safe and timely plant decommissioning (NUREG

-0586, Supplement 1, p. 68; DCE, p.55.)

But, at the time it filed its PSDAR and DCE, Holtec had not characterized the Pilgrim site, and had done essentially nothing to determine what contaminants are on the site or what it would cost to remove them.

Rather, Holtec admits that its cost estimates are based on nothing more than what appears records. sometime in the future:

In the time leading up to, and immediately following, the equity sale/closure and license transfer, the following activities will be performedSite Assessment (HSA) to support the identification, categorization, and quantification 23 of radiological, regulated, and hazardous wastes in support of waste management pp 8-9 (emphasis added) iod 1, planning and preparing for the prompt decontamination and site characterization activities so that radiological, regulated, and hazardous wastes are identified, categorized, and quantified to support decommissioning and waste -11 transfer, preparations for performance of characterization so that radiological, regulated, and hazardous wastes are identified, categorized and quantified to support decommissioning and waste management planning. DCE , p. 14 But the PSDAR and DCE make clear that Holtec prepared its cost estimates without having characterization activities so that radiological, regulated, and hazardous wastes are identified, categorized, and quantified to support decommissioning and waste management planni-11) Even Holtec admits that site characterization must be completed (PSDAR, pp 10

-11) and that site characterization o supplement plant quantification of radiological What this makes clear is at least four critical facts:

1. At the time it filed its PSDAR and DCE, Holtec simply did not know what 2. Pilgrim site.

24 3. curate decommissioning cost [that is] -0586, supra.)

4. Holtec quite properly does not attempt to justify its assumption that its PSDAR provided accurate cost estimates based on the Entergy HSA that Holtec had not reviewed when it filed its PSDAR and DCE. To the extent that Holtec might seek to justify its assumed PSDAR cost Holtec admits that the data and information both need to be supplemented by future site characterizations (PSDAR, p. 11) and confirmed (DCE, p. 22).

Holtec also could not properly assume that are old, incomplete, and inaccurate 15 The PSDAR and LTA provide no basis for concluding, as required by 10 CFR 50.82(a)(4) (i), that the environmental impacts associated with site

-specific decommissioning activities are bounded by these old impact statements.

6 SEIS. The GEIS (2002) is a generic document and is outdated by 17 years. A site

-specific environmental analysis is required since no two reactor sites and history are identical, but the SEIS (outdated by 12 years) 15 The SEIS NUREG

-1437, Supplement 29, Volume 1, Section 7.1, Decommissioning, concludimpacts related to these issues beyond those discussed in the GEIS. For all of these issues, the staff concluded in the GEIS that the impacts are SMALL, and additional plant

-specific mitigation measures are not likely to be sufficiently 25 was simply a review by NRC staff of documents provided by Entergy and involved no actual analysis by NRC of soil or liquid samples.

16 The GEIS, SEIS and Holtec incorrectly assume that the Pilgrim site is essentially clean. However, and as discussed in detail below, the GEIS, SEIS, PSDAR and LTA ignore both old and SEIS were published. and SEIS suggests that Holtec knows that that a new site assessment and environmental impact statement would show that the PSDAR and DCE do not include any rational or acceptable estimate of the costs of clean

-up. Whether by design, or because it does not know what contamination actually exists, conventional dismantling, demolition, and removal from the site of structures and systems after confirmation that radioactive contaminants have been removed. (p 19); an assumption again based absent information about the actual condition of the Pilgrim site.

As shown below, it is clear that the limited information on which Holtec based its PSDAR estimates did not include important relevant facts and overlooked significant contamination.

16 A-15), September 6, 2007

26 The actual cost of decontaminating and restoring the Pilgrim site will be more, probably far more than Holtec has estimated. At Connecticut Yankee, for instance, previously undiscovered strontium-90 contributed to the actual cost of decommissioning Connecticut Yankee being double what had been estimated.

During the decommissioning of Maine Yankee, the licensee encountered pockets of highly contaminated groundwater dammed up by existing structures, leading to cost increases. The Yankee Rowe site in Massachusetts incurred significant cost increases during decommissioning when PCBs were discovered in paint covering the steel from the vapor container that housed the nuclear reactor, as well as in sheathing on underground cables. Other plants have also ended up costing much more than what was estimated for decommissioning

- Diablo Canyon 1&2, San Onofre 2&3.

17 The NRC cannot properly conclude that the DTF provides financial assurance or that Holtec-Pilgrim or HDI are financially responsible. To do so, the NRC would have to ignore that conditions of the Pilgrim site , accept that there will be no complete or accurate radiological and hazardous materials site investigation and characterization, and accept that there would be certainty regarding what is required or what it will cost to clean

-up the site.

For Holtec to show that Holtec Pilgrim and HDI are financially responsible, and to provide the required financial assurance, it must conduct a new and complete site characterization, and submit a cost estimate based on the actual conditions at Pilgrim.

17 See, e.g., NRC, SECY 0105, at Summary Table, available at http://www.nrc.gov/reading

-rm/doc-collections/commission/secys/2013/2013

-0105scy.pdf ranging from $438 million, counting the River Bend Station as one unit, to over $1 billion).

27 Examples of Radiological/ Hazardous Contamination 18 radiological and hazardous contamination. What is not speculative, and would be confirmed by a new site assessment, is that there is significant contamination at PilgrDCE are inaccurate.

The LTA, PSDAR, DCE and GEIS and SEIS ignore that, over the years, Pilgrim has buried contaminated materials on site and has had many leaks and releases. Pilgrim opened with bad fuel and no off

-gas treatment system until 1987; later it blew its filters prompting Mass Dept. Public Health to do a case

-control study of adult leukemia testing the hypothesis that the closer you lived or worked at Pilgrim there would be an increase in leukemia. The hypothesis was confirmed.

19 Due to these leaks, many lethal radionuclides, including for example tritium, manganese54, cesium-137, Sr-90, I-131, cobalt

-60, and neptunium 20 were found in the surface water, Holtec nowhere recognizes the existence of these contaminated materials, the costs of removing them, or the costs of remediating portions of the site that they have contaminated. None of the documents Holtec relied upon bound environmental impact.

18 -vii, Exhibit 3; and , Pilgrim Watch Intervention Pilgrim License Renewal Application, Contention 1 filings, NRC Adams Electronic Hearing Docket.

19 The Southeastern Massachusetts Health Study

[published in the Archives of Environmental Health, Vol. 51, p.266, July

-August 1996 (Pilgrim Motion Request for Hearing and Motion to Intervene, May 2006, Exhibit F

-2, NRC Adams, EHD, Pilgrim LR, Pleadings 2006) 20 Neptunium releases into Cape Cod Bay reported by Stuart Shalat, who worked for the contractor doing the re

-fueling in the 1980s. Stuart Shalat, Sc.D. Associate Professor Robert Wood Johnson Medical School, Exposure Science Division, Environmental and Occupational Health Sciences Institute

28 Pilgrim is sited beside Cape Cod Bay. Due to the topography of the site, contaminants will leak into the Bay. Massachusetts and Cape Cod Bays are tidal. NUREG-1427, 2.2.5.1 Contaminants leaking into the bay during an incoming tide will be drawn into Plymouth, Duxbury and Kingston Bays

, up the rivers, such as the Jones, Eel, and Bluefish Rivers and into estuaries and marshes; in the outgoing tide they will flow into and circulate around Cape Cod Bay and beyond. Currents will move the contamination.

The figure below, provided by the Massachusetts Water Resources Authority, 21 show circulation in Massachusetts and Cape Cod Bays.

The dispersion of discharges also varies seasonally

. From information available, it is reasonable to predict that currents, winds and tides would spread contaminants around Cape Cod Bay, into Massachusetts Bay and eventually south down the outside arm of Cape Cod, impacting

21 Physical and Biological Oceanography of Massachusetts, Wendy Leo, Rocky Geyer, Mike Mickelson http://www.mwra.state.ma.us/harbor/enquad/pdf/ms

-085_04.pdf 29 also rivers, streams, and other waterways that are connected to the larger bodies of water. The impact, actual or perceived, would significantly affect public safety, the marine ecology and economy. -Carver Aquifer, the second largest aquifer in the state that provides drinking water to several towns and supports many natural resources.

Historic poor management, releases and contamination ignored As stated, Pilgrim opened in 1972 with bad fuel and no off

-gas treatment system

, a technology that attempts to reduce the radioactivity of gasses that are removed from the radioactive steam that turns the turbine in the condenser. It did not install the off-gas system until 1977.

This prompted Mass Dept. Public Health (MDPH) to do a case

-control study of adult leukemia testing the hypothesis that the closer you lived or worked at Pilgrim there would be an increase in leukemia. The hypothesis was confirmed.

22 hich began operations in 1972 ,

22 The Southeastern Massachusetts Health Study published in the Archives of Environmental Health, Vol. 51, p.266, July-August 1996

30 23 Due to the leaks

, many lethal and long

-lived radionuclides were identified. For example, neptunium (2.14 million years) was reported by Dr. Stuart Shalat who worked as a contractor at Pilgrim and now at Rutgers University.

24 Subsequently Pilgrim blew its filters in 1982, prompting authorities to send suited personnel into neighboring communities to take samples. The Annual Radiological Environmental Reports indicate considerable offsite contamination. If there was offsite contamination, the only reasonable assumption is that there was contamination onsite also.

For example, the Pilgrim Nuclear Power Station Environmental Radiation Monitoring Program Report No. 15 January 1 through December 31, 1982

- Issued April 1983 Boston Edison Co. (available ) shows the results from testing various media offsite for radionuclides. As an example, the milk sampling report on page 30. says that:

Milk samples were collected at two locations during 1982

- Kings Residence (Station 22-12 miles W), and Whitman (Station 21

- 21 miles NW)

Cs-137: Kings Residence in late June concentrations 1,000,000 times in excess of concentration expected (The contamination level of the June 11, 1982 spent resin incident was up to 100,000 dpm/100 cm2.)

Gamma isotopic analysis identified primarily long

-lived radionuclides including Cs 137 and the Whipple farm (1.5 mi

-SSW); lettuce 31.9 pCi/kg and Cs

-137 concentrations > 1,000,000 times what would be expected at both locations.

23 The Southeastern Massachusetts Health Study 1978

-1986 Martha Morris, Robert Knorr Principal Investigators Exec Summary, Background, pg.,1

31 pregnancy; Tufts University Veterinary School explained cows delivered calves not cesium.

Other media sampled show similarly high readings. NRC Inspection Reports from June-July 1982 document and confirm the releases of resin.

25 Due to these and subsequent releases discussed below, many lethal radionuclides were levels. These release s prompted additional health studies that were publishethru 2004 showing radiation linked diseases in communities near Pilgrim. (See Pilgrim Watch Motion to Intervene Pilgrim LRA, Contention 5, (5.3.3) and Exhibits F-2-F-4, Adams Library, Accession NO. ML061630125

.) All of this is GEIS and SEIS. The LTA cannot properly be approved until Holtec has conducted a new site radiological , regulacosts or removing all wastes and contamination on site and has provided assurance that it has the financial ability to do so.

25 NRC Inspection Reports June

-July 1982: June 11, 1982 Preliminary Notification of Event Or Unusual Occurrence

-PNO-1-82-42

Subject:

release of Resin; June 11, 1982: Licensee Event Report June 9, 1982;June 14, 1982: Preliminary Notification of Event or Unusual Occurrence

-PNO-1-82-42A

Subject:

release of spent resin update; July 7, 1982: Inspection Report by NRC of PNPS dated July 7, 1982;July 8, 1982: NRC Memo: Generic Implications of the Release of Spent Resin (Available NRC Adams, microfische).

32 Co n tamination onsite is exacerbated by Pilhistory of mismanagement 26 From 1986- 1989 , Pilgrim shut down due to a series of mechanical failures. (US nuclear plants in the 21 st century: The risk of a lifetime. Report by the Union of Concerned Scientists, David Lochbaum, May 2004.) In May 1986, The NRC identifie d Pilgrim as one of the most unsafe facilities in the U.S.

(Pilgrim on list of worst

-run nuclear plants, Boston Globe, A Pertman, May 23, 1986.) In January of 1988, a 5,000 cubic yard pile of dirt containing radioactive cesium

-134, cesium-137, and cobalt

-60 was found in a parking lot near the reactor.

(Radioactivity was detected in dirt pile near Pilgrim

, Boston Globe, L.

Tye, January 21, 1988

) In February 2014

, the NRC identifie d Pilgrim as one of the nine worst performing nuclear react ors in the U.S.

In September 2015

, (Category 4), joining 2 other Entergy reactors. (http://www.nrc.gov/info

-finder/reactors/pilg/special

-oversight.html

) December 2016, Special Inspection

27 NRC the November 28

- December 8 inspection. Written by Donald Jackson, the lead inspector, this report included a long list of flaws at the plant that were observed during the initial week of the inspection. In the email, Donald Jackson, said that , "The plant seems overwhelmed just trying to run the station." The list of Pilgrim failures mentioned in the email were: failure of plant workers to follow established industry procedures, 26 Pilgrim Chronology 1967

- 2015, https://jonesriver.org/legal/pilgrim

-chronology

-1967-2015/ Exhibit 4 27http://www.capecodtimes.com/news/20161206/nrc

-email-pilgrim-plant-overwhelmed

33 broken equipment that never gets properly fixed, lack of required expertise among plant experts, failure of some staff to understand their roles and responsibilities, and a team of employees who appear to be struggling with keeping the nuclear plant running. We are observing current indications of a safety culture problem that a bunch of talking probably won't fix." The report suggests that Pilgrim was just trying to run the station ,ing the probability of leaks that will require cleanup and more money than anticipated. Pilgrim remains in the lowest safety ranking in 2019. Contamination resulting from Buried Pipes and Tanks

- concrete, carbon steel, stainless steel, titanium and external coatings and wraps are susceptible to age

-related and environmental degradation.

28 The pipes and tanks are old and subject to age

-related degradation.

29 Some of the pipes and tanks contain industrial process, radionuclides in wastewater and embedded in the pipe/tank. Degradation of these components can lead to leaks of toxic materials into groundwater and soils.

28 Contention 1, The Aging Management Plan Does Not Adequately Inspect and Monitor for Leaks in All Systems And Components That May Contain Radioactively Contaminated Water. We refer the ASLB to the file, especially Pilgrim Watch Post Hearing Findings of Fact and Conclusion of Law, June 9.2008, Docket 50

-293 29 Pilgrim Watch Post

-Hearing Findings of Fact Conclusions of Law, June 9, 2008, 11 34 are within 10 feet of the surface, which is well within reach of groundwater and salt water flooding.30 31 There is every reason to assume that it is not the only one.

There has been no adequate program for inspecting buried pipes Piping/Underground Piping and Tanks Integrity Initiative, that began in 2009, is voluntary. The on inaccurate assumptions about corrosion and an insufficient inspection regime

. Rather than requiring a comprehensive approach to deal with leaks of radioactive materials from buried pipes and tanks, the NRC has allowed Pilgrim to take piecemeal approach by conducting physical inspections only in those rare instances when pipes are dug out for other purposes and by only fixing sections of failed pipe.

30 Ibid, 31 Pilgrim License Renewal Application Proceeding, Entergy submissions, PillR0045779

-Pill R00457

35 These voluntary processes have allowed leaks and spills to go unnoticed, 32 and are incapable of identifying failures in, or ensuring the integrity of, decades

-old piping systems.

33 Holes such as that shown above leak, and neither Holtec nor the N RC can properly assume that it is the only one. Holtec must be required to conduct a new site assessment to s wastes are identified, categorized and quantified to support decommissioning and waste management CDE, p. 14), and to include in its PSDAR and DCE the costs of removing contamination around buried pipes and tanks and a showing that the DTF has sufficient funds to do so. Tritium and Other Radionuclides in Groundwater 34 The Pilgrim Tritium in Groundwater Program has shown significant radioactive contamination (tritium, cesiu m-137, cobalt

-60, manganese

-contamina Prior to 2007, Pilgrim had no groundwater monitoring program. What had leaked into and contaminated the site is unknown; but what was found when wells were put into place in 2007 strongly suggests perhaps considerable prior leakage.

35 samples, have confirmed Pilgrim is leaking radionuclides and contaminating the soil and

32 Ibid, 55-59 33 Ibid, 37 34 https://www.mass.gov/lists/environmental

-monitoring

-data-for-tritium-in-groundwater

-at-pilgrim-nuclear-power-station; https://jonesriver.org/pilgrim

-contamination/

and see Attachment 2 for a full report.

35 Only four wells were installed in 2007.

36 wn levels ranging from non

-detect levels to as high as 70,000 piC/L.

36 is 400 piC/L. Every year since 2007 there has been at least one well with levels well above the upper limit of normal background levels. In all but 2 years, there was at least one well above drinking water standard of 20,000 piC/L.

By April 2012 an underground line leading to the discharge canal had separated. The leak was accidently discovered when tritiated water was found coming out of an electrical junction box inside the facility.

37 Five months later, groundwater tests results showed high tritium levels (4,882

-5,307 pCi/L), in one of the wells and this was suspected to be related to the separated underground line.

38 Soil sampling was done, and preliminary results showed tritium, cobalt

-60, and cesium

-137 at levels above normal (1,150 picocuries per kilogram (pCi/kg) of cobalt

-60 and 2,490 pCi/kg of cesium

-137). 39 By January 2014 nine months after the leak was originally discovered excessive levels of tritium (69,000

-near a basin that collects radiologically contaminated water and ultimately sends it to Cape Cod Bay. Entergy and Mass DPH continued their investigations, unsure of the sources of leakage, and performed no cleanup.

40 M Mass MDPH Pilgrim Nuclear Power Station (PNPS) tritium in groundwater monitoring wells, January 2014 37 Mass MDPH Pilgrim Nuclear Power Station (PNPS) tritium in groundwater monitoring wells, May 2013 38 Mass MDPH Pilgrim Nuclear Power Station (PNPS) tritium in groundwater monitoring wells, Sept 2013 39 Split sample testing at MDPH 40 Mass DPH. Pilgrim Nuclear Power Station (PNPS):

tritium in groundwater monitoring wells. Jan. 2014.

37 ls continued to show elevated levels of tritium and final soil testing results show levels of tritium, manganese

-54, cesium

-137, and cobalt

-60 at various depths near the separated underground line above typical background levels.41 According to Mass DPH in its August 2014, November 2014, and May 2015 Groundwater radionuclides (e.g., Cobalt

-60 and Cesium

-137) were still being found in soils on the site. The November report describes new samples showing high levels of tritium in air conditioning condensate at the facility (3,500

-4,000 piC/L).

In addition to the contaminating spills described above, at least five other historic spill events that have been reported on the Pilgrim site since 1976.

42 For instance, in 1988 there was a spill of low

-level radioactive waste water. The radioactively contaminated liquid waste was discovered inside a process building and had leaked outside the building. An estimated 2,300 gallons of contaminated water spilled, and 200 gallons leaked outside the building from under a door. About 2,500 square feet of asphalt and 600 cubic feet of sand and gravel were contaminated.

43 Soil samples obtained in 2014 as part of a larger tritium leak investigation showed high levels of manganese

-54, cesium

-137, and cobalt

-60 at various depths near a separated underground line above typical background level.

44 41 Mass DPH. Pilgrim Nuclear Power Station (PNPS): tritium in groundwater monitoring wells. May 2014.

42 Mass DPH. Pilgrim Nuclear Power Station (PNPS): tritium in groundwater monitoring wells. Aug 2014. 43 Mass DPH. 1988. Investigation of Radioactive Spill at Pilgrim on November 16, 1988. Prepared by Radiation Control Program.

44 Ibid. at 67 38 For the non

-drinking water reporting standards for cobalt

-60 (5.27 years half

-life), cesium-137 (30.17 years half

-life), and manganese

-54 (312 days half

-life), see Table4. For or these radionuclides is 4 mrem per year. For cesium

-137, the -60, the level nant level (MCL), non

-drinking water reporting standards, and the average concentration assumed to yield 4 mrem per year for select radionuclides Radionuclide Drinking Water Non-Drinking Water Reporting Standards (Entergy/NRC) 73 Average Concentration assumed to yield 4 mrem/year Tritium 4 mrem/year 30,000 piC/L 20,000 piC/L Manganese-54 4 mrem/year 1,000 piC/L 300 piC/L Cesium-137 4 mrem/year 50 piC/L 200 piC/L Cobalt-60 4 mrem/year 300 piC/L 100 piC/L Absent a new and complete site assessment, there is no certainty of the sources of crack in the Torus floor, materials and soil from subsequent construction left on site, and age-related degradation. Extreme temperatures and storms, salt water and air, corrosive chemicals, 39 and intense radiation most likely have caused components to thin and crack, compromising the structural integrity of the facility and underground/buried pipes.

45 During the past 12 years in which the licensee has known about the leaks, nothing has been done to clean up the soil. The cost of removing all on

-site radioactive tritium and other radioactive materials that have been released into the soil must be includPSDAR and CDE. They have not been.

Once again, Holtec must be required to conduct a new site assessment to determine the categorized and quantified to support decommissioning and waste management planning. (DCE , p. 14) Unless it does so, it will not be able to include in its PSDAR and DCE an accurate estimate of the costs of removing contamination around buried pipes and tanks, to show that the DTF has sufficient funds without which there can be no financial assurance, or to show that Holtec Pilgrim and HDI are financially responsible.

Stormwater Drains and Electrical Vaults 46 Pilgrim has twenty

-five electrical vaults on site. The vaults and other sources of untreated water are pumped out to four stormwater drains and directly into Cape Cod Bay. Over the past twenty

-pollutants, oil, grease, total suspended solids, as required by EPA. But Entergy failed to conduct

45 Pilgrim Watch, Contention 1, The Aging Management Plan Does Not Adequately Inspect and Monitor for Leaks in All Systems and Components That May Contain Radioactively Contaminated Water; Pilgrim Watch Post Hearing Findings of Fact and Conclusion of Law, June 9.2008, Docket 50

-293, NRC Adams, ML 081650345 46 https://jonesriver.org/getfile/ccbw/2012/10/RAD

-REPORT_2017.07.18_VS3.pdf (Attachment 3)

40 sampling over roughly the past 10 years, according to the EPA.

47 Sampling has only occurred three times since January 2009, and only three of the four storm drains were tested. There is inaccessible.

When storm drain sampling was done (from 1998

-2007), certain parameters were exceeded on many occasions.

48 Initial sampling by EPA from only seven vaults found total suspended solids, cyanide, phenols, phthalates, PCBs, antimony, iron, copper, zinc, lead, nickel, cadmium, hexavalent chromium. Lead, copper, and zinc exceeded marine water quality criteria.

Monitoring results from standing water in storm water manholes, junction boxes, and electrical duct banks show radioactive materials at tritium levels as high as 1,500 pCi/L in some storm water manholes and up to 4,500 pCi/L in some electrical duct bank manholes.

49 Even though these levels may be low in relation to the excessive levels in the groundwater, they still exceed the background level of 5

-25 piC/L for surface water and 6

-13 piC/L for groundwater.

Unless and until Holtec performs a new and complete site analysis, the actual extent of drain and vault radioactivity and the costs or removing it will not be known PNPS will continue to comply with the Offsite Dose Calculation Manual, Radiological Environmental Monitoring Program, and the Groundwater Protection Initiative Program during decommissioning (LTA, 1.4 Additional Considerations). The reports are not

47 Sheet) 48 page 31 of ESystem (Fact Sheet) 49 Ibid, at 22

41 reliablnegatively impacting public health.

The Tritium) at Nuclear Plants Task Force Final Report, September 1, 2006 50 that under the existing regulatory requirements the potential exists for unplanned and unmonitored releases of radioactive liquids to migrate offsite into the public domain undetectedLLTF Executive Summary ii)

Section 3.1.4 of the LL TF recommended that the following regarding the Radiological Environmental Monitoring Program.

The radiation detection capabilities specified in the Buried Tanks and Pipes Monitoring -of-the-art for routine environmental measurements in laboratories. More sensitive radiation detection capability exists today, but there is no regulatory requirement for the plants to have this equipment. The guidance primarily focuses on gamma isotopic analysis of environmental material and on tritium in water samples. There are minimal requirements for analyzing environmental samples for beta

- and alpha

-emitting radionuclides. P.18 licensees to reduce the scope of and frequency of the sampling program, without the NRC licensed radioactive material in several years, then the licensee typically reduces the scope and sample frequency of the associated environmental pathway. NRC inspections have 50 https://www.nrc.gov/docs/ML0626/ML062650312.pdf

42 The Task Force concluded (Conclusions 3.2.1.3)

(2) The radiological effluent and environmental monitoring program requirements and guidance largely reflect radioactive waste streams that were typically from nuclear plant giving the significant dose, while still important today, have been joined by new issues. Today, as a result of better fuel performance, and improved radioactive source terms reduction programs, a new radioactive waste stream has evolved. The new liquid radioactive source terms are made up of a lower fraction of gamma emitting radionuclides and a higher fraction of weak beta emitters. The NRC program has not evolved with the changes in technology and industry programs (3) The REMP has allowed licensees significant flexibility to make changes to their programs without NRC prior approval. The historical trend has been to reduce the scope of the program. There is no guidance on when the program need s to be expanded.

Its Recommendations

(1) The NRC should revise the radiological effluent and environmental monitoring program requirements and guidance consistent with current industry standards and commercially available radiation detection technology.

(2) Guidance for the REMP should be revised to limit the amount of flexibility in its conduct. Guidance is needed on when the program, based on data or environmental conditions, should be expanded.

(6) The NRC should require adequate assurance that spills and leaks will be detected before radionuclides migrate offsite via an unmonitored pathway.

43 The LLTF stated further in its Declaration Motion to Intervene and Request for Hearing Docket No. 50

-293 &72-1044 LT, February 20, 2019

- Excerpts Mr. Priest is the Director of the Radiation Control Department, Massachusetts Department of Publ ic Health. He worked at multiple nuclear power plants, including Pilgrim Nuclear Power Station. During that time, responsible for oversight of radiological plant surveys to support power plant operations, the radiological monitoring of the station staff and members of the public, and emergency planning activities with federal, state and local agencies. 3. I do not believe that Holtec has reasonably accounted for all site

-specific factors in its decommissioning cost estimate. I reached this conclusion for the following reasons.

SITE-SPECIFIC INVESTIGATION AND ENVIRONMENTAL ASSESSMENTS

4. Holtec has not done and has not indicated to DPH that it plans to do, a full site investigation (radiological and non

-radiological) before acquiring Pilgrim from Entergy.

A full site investigation is necessary to accurately determine the ultimate anticipated cost of decommissioning, spent fuel management, and site restoration. Instead, Holtec relied on a series of NRC Generic Environmental Impact Statements for nuclear power plant decommissioning and license termination and renewal:

5. The National Environmental Policy Act (NEPA) requires the NRC to prepare a detailed statement assessing the environmental impact of and alternatives to major federal actions, which includes decommissioning of nuclear power plants

6. The PSDAR does not discuss the potential future impact of changes to the coastline or water table due to climate change, including the ability to adequately survey below ground components or structures and the discovery of contaminants in previously unassessed areas.

44 8. In 2010, Entergy reported increased tritium measured at one well. In response to recommendations from DPH, Entergy has installed additional wells and continued to monitor for tritium and investigate possible sources. To date, the cause of the tritium contamination has not been definitively identified.

Entergy reported to DPH that it believed the contaminant was released from cracks in the basement of the condenser bay and into the adjacent seismic gaps between the buildings. To the extent tritium is discovered in groundwater in excess of the drinking water maximum contaminant levels (MCL) set by the U.S. Environmental Protection Agency (EPA), Holtec will have to ensure remediation. It is unknown whether the potential cost of having to 9. Based on my site knowledge, contamination has previously been identified by the utilities in the soil in the vicinity of the condensate water storage tank, the reactor truck lock and radioactive waste building. Further, there were other releases into the environment associated with a former condenser tube refurbishment building east of the radioactive waste truck lock. Historically, contaminated soil from previous site DPH does not know whether these sites and others were captured as part of decommissioning records required by 10 C.F.R. § 50.75(g), communicated to Holte c and evaluated by Holtec in its decommissioning cost estimate. Based on my knowledge of this site and experience at other nuclear power plants, it is reasonable to excavation and demolition begins.

12. Long-lived radionuclides are likely to be found in soils and groundwater far from the small excavation made to repair the leaks that likely allowed reactor condensate to enter into the site soils for many years. In addition, these same long

-lived radionuclides are likely to be found in many other structures, systems, and components, which may also have unknowingly leaked over the decades into soils and the groundwater at the Pilgrim property INDUSTRY EXPERIENCE

13. During radiological surveys that occurred prior to decommissioning of the Vermont Yankee Nuclear Power Plant, the Vermont Department of Health found cesium-137, strontium 90, and other long half

-life radioactive materials in soil samples. In addition to Vermont Yankee, other New England decommissioning projects at Maine Yankee and Connecticut Yankee uncovered long half

-life radioactive materials and hard

-to-detect radionuclides in soils. Similar contaminants can be expected at the Pilgrim property, including carbon

-14, nickel

-63, strontium 90, cesium-137 and transuranics, which include radioisotopes of plutonium, curium, neptunium, and americium.

45 12. Discussions with the New England Compact, Health Department staff in Vermont and Maine and Department of Energy and Environmental Protection staff in Connecticut indicate that decommissioning activities commonly reveal previously unidentified and unknown radiologically contaminated media that must be addressed and remediated during decommissioning and prior to license termination. For example, highly contaminated pockets of groundwater were discovered dammed up by existing subsurface structures at Maine Yankee and caused significant cost increases. In addition, the licensee at Connecticut Yankee had to excavate a large trench in soil around the reactor and its components that was not identified or 13.The Holtec PSDAR neither identifies nor reasonably accounts for the challenges of remediating contaminants encountered during decommissioning, including but not -lived radionuclides in the soil and in structures, systems, and components. These considerations should be factored into the planning and funding for the decommissioning of Pilgrim, but it is not apparent from the PSDAR that Holtec did so.

14. The discovery of additional contamination not accounted for in previous site investigations or previously filed Generic and Site

-Specific Environmental Impact Statements will result in additional costs to Holtec. A complete site characterization (i.e., an assessment of the vertical and horizontal extent of all radiological and non

-radiological contamination at the site) and a Supplemental Environmental Impact Statement that considers the information yielded by such a site

-specific characterization and considers climate change effects is necessary to provide a more accurate basis on which to estimate costs of decommissioning.

EXCAVATION / DEMOLITION

15. During discussions with DPH, Holtec has stated that previous remediation of Pilgrim eliminates the need to excavate deeper than three feet below grade. Consistent with th-ground structures will be removed to a nominal depth of three (3) feet below the surrounding grade level. Characterization surveys will then be performed in the remainder of the below ground structures and any areas with activity exceeding established [Derived Concentration -lived radionuclides at other nuclear decommissioning sites, as discussed above, creates doubt that Holtec will not need to excavate deeper than three feet below grade.

46 17. The Holtec PSDAR does not detail their plan to address soils outside the structures and components and how they would be characterized and remediated. As written, Holtec does not account for the costs or evaluate the health and safety effects of such a contamination. It is not clear from the Holtec PSDAR that Holtec addressed these issues in the contingency analysis in its cost estimate or, if it did so, whether it properly accounted from them. A detailed analysis of the likelihood of further excavation and associated costs is necessary to accurately estimate those contingencies.

ENVIRONMENTAL RADIATION MONITORING

18. The Holtec PSDAR does not describe the planned radiological environmental radiation exposure dosimetry and environmental land use analysis (monitoring power plant by

-product radionuclides in milk, vegetation, seafood, etc.). These activities should be conducted through the decommissioning timeframe, including spent fuel pool cleanout, dry fuel storage cask loading, reactor building and associated structure demolition, and finally site restoration. The values in table 3

-1 of the cost estimate included in the PSDAR represent a small fraction of costs needed to continue the current level of environmental monitoring. These considerations should be factored into the planning and funding for the decommissioning of the Pilgrim property.

19. The radiological environmental monitoring program should include a plan to submit all legacy and NRC

-filed site assessments and surveys to Massachusetts, conduct radiological and non

-radiological groundwater contamination sampling, report results to Massachusetts, and provide split samples as requested.

EMERGENCY PLANNING

20. The PSDAR does not adequately address preparedness in the event of a radiological emergency during decommissioning or the transfer of spent fuel to the spent fuel pool or from the spent fuel pool to dry casks or consider the cost of such an incident. An adequate radiological emergency preparedness plan would include state resource scenarios.

21. Holtec does not adequately address their capabilities to monitor and respond to the following: (a) Leaks of large quantities of radioactive materials in solid or liquid form into the environment; (b) Deficiencies in the structures, systems, and components containing stored radioactive materials; (c) Response plan for emergent scenarios including combustible fires containing either low level radioactive contaminants or 47 spent fuel, and hostile actions that destroy key structures that store radioactive materials; (d) Security measures surrounding the dry fuel pad, which should inc lude substantial physical barriers, especially once it is relocated closer to a nearby road; (e) Details on remote and onsite radiation monitoring of the facility and spent fuel storage; or (f) Adequate routine physical inspection of dry casks and detailed contingency for damaged/degraded dry fuel storage containers.

22. All of these items represent discrete, foreseeable risks that Holtec did not provide sufficient detail that they have considered and accounted for in the PSDAR.

RADIOACTIVE WASTE TRANSPORTATION

23. The Holtec PSDAR addresses the transportation approach for Class A, Low Specific Activity, or Surface Contaminated Object classes of waste. It states Holtec will use a combination of truck, rail and potentially barge to support bulk quantit y removal of waste. Since there is no active rail line at the site, Holtec states that a truck will be used to deliver the waste to a transload facility in Massachusetts. However, no such transload facility is licensed by the Massachusetts Radiation Control Program to perform such waste processing or repackaging for waste transfer. A more specific waste removal plan would be necessary to provide an accurate cost estimate.

24. Additionally, regarding the safety of transfer and storage of radioactive materials, the Holtec PSDAR does not include details describing state review for removal and transportation of all radioactive waste and does not describe provision of funding to agencies that will expend resources on plan review, approval and implementation, such as the Massachusetts State Police for route planning and escort of high

-level waste. RADIOLOGICAL STANDARDS

25. The Holtec PSDAR only references the NRC Final Status limit of 25 millirems per year for unrestricted release from all pathways. The Massachusetts standard for unrestricted release of residual radioactivity (cleanup) is no more than 10 millirems per year (105 C.M.R. § 120.245). In addition, EPA has established a drinking water MCL of no more than 4 millirems per year. The Holtec PSDAR does not include Massachusetts cleanup standard or the EPA drinking water MCL for all property transferred from Entergy to Holtec.

26. In order to apply a consistent clean up standard for all sites containing radioactive materials in Massachusetts, DPH issued a formal request that Holtec submit a 48 proposed compliance document detailing the methods and protocols for compliance with the Massachusetts clean

-up and EPA drinking water MCL prior to the unrestricted release of all or any part of the property transferred from Entergy to Holtec. DPH additionally requested these clean

-up standards be incorporated into eanup standard nor the EPA groundwater standard with the Commonwealth of Massachusetts related to the establishment of an oltec has expressed a willingness to sign an agreement with the Commonwealth on the radiological release standard.

Hazardous Waste Site specific analysis of hazardous waste onsite is absent from the application.

A site- specific analysis at the beginning of the decommissioning is required to document where it is, how to remove it, and costs.

Declaration of Paul Locke, the Assistant Commissioner of the Bureau of Waste Site Cleanup (BWSC) at the Massachusetts Department of Environmental Protection (MassDEP)

Excerpts from the declaration of Paul Locke

, the Assistant Commissioner of the Bureau of Waste Site Cleanup (BWSC) at the Massachusetts Department of Environmental Protection (MassDEP) in the February 20, 2019 Mass Attorney Generals Motion to Intervene provides highlights.

5. Pilgrim is located on Cape Cod Bay, adjacent to wetlands, and sits above a Potentially Productive Aquifer. A Potentially Productive Aquifer is an aquifer delineated by the U.S. Geological Survey (USGS) as a high or medium yield aquifer (310 C.M.R. § 40.0006) and such aquifers are protected for their potential future use as a public water supply source (310 C.M.R. § 40.0932). Any oil or hazardous material released to the environment at Pilgrim has the potential to affect both human and environmental receptors through direct contact with contaminated soil, use of the groundwater, and migration to adjacent surface waters and wetland resources. Based on my experience at MassDEP, large industrial facilities, including power plants like Pilgrim, use a variety of oil and hazardous material as part of their operations and facilities. These 49 include asbestos, transformer oils (including PCB

-containing oils), and cleaning and/or degreasing solvents (including chlorinated volatile organic compounds, or cVOCs). Methods for handling, storing and disposing of oil and hazardous materials have evolved over time, and it is not uncommon for older facilities like Pilgrim to have released oil and hazardous materials to the environment following common past practices. The potential impact of any such release is unknown until a comprehensive location where oil or hazardous material has come to be located. A comprehensive site assessment includes the identification of releases of oil or hazardous material on a property and delineation of the extent of those release including the investigation of off-property migration that may have occurred.

7. I have reviewed the November 16, 2018 Revised Pos t-Shutdown Decommissioning Activities Report and DECON Site

-Specific Decommissioning Cost Estimate prepared by Comprehensive Decommissioning International, LLC for Holtec Decommissioning International, LLC (HDI). The Revised Post

-Shutdown Decommissioning Report notes that Holtec will perform site characterization activities during the decommissioning process to supplement what is currently known about the nature and extent of radiological and nonradiological contamination at the site. Holtec will then use that information to establish contamination levels throughout the plant and adjust activities accordingly. On its face, the Report is, in my opinion, deficient because it (i) does not include an inventory of oil and hazardous materials that have been used at the facility and which may have been released to the surrounding environment and (ii) does not describe assessment activities that would occur outside the plant that would identify past releases of oil or hazardous materials and any contaminated media that Holtec legally needs to address.

8. I have also reviewed the release notifications and site cleanup activities that have occurred at Pilgrim pursuant to the MCP. As noted above, both Chapter 21E and the MCP require a site owner or operator to notify MassDEP when a release of hazardous mawork was conducted under fourteen (14) distinct Release Tracking Numbers (RTNs) for release notifications that occurred from November 16, 1994 through December 20, 2016. An RTN is the unique file number assigned by MassDEP to a release or threat of release reported in accordance with 310 C.M.R. § 40.0300. The following briefly summarizes those RTNs: (a) Nine (9) RTNs were assigned for releases of hydrogen gas, and no analysis of impacts to groundwater or soil was performed. (b) One (1) RTN addressed a release of hydraulic oil to pavement, and no analysis of impacts to groundwater or soil was performed. (c) One (1) RTN addressed a heating fuel release at a former residential property distant from the facility itself and was not related to plant operation. (d) One (1) RTN addressed an exothermic reaction of an 50 epoxy/hardener mixture that occurred within a 55

-gallon drum and liner, and no analysis of impacts to groundwater or soil was performed. (e) Two (2) RTNs addressed releases of transformer oil at the Main Transformer system, which included soil and groundwater characterization in the immediate vicinity of the releases.

As noted, eleven (11) of the releases required no investigation of underlying soil or groundwater. The remaining three (3) releases involved limited (localized) soil and groundwater sampling.

The results of these investigations provide little insight as to any potential environmental contamination that may be present throughout the site.

9. Based upon my review of this material and my experience at MassDEP, it is my opinion that Holtec has not adequately evaluated and included in its cost estimate the costs of environmental site assessment, remediation, and restoration and that it is likely perform that work. My opinion is also informed by the following facts: (a) Past environmental site assessments conducted for releases of oil and hazardous material at Pilgrim have been limited in nature and are not indicative of potential contamination present. (b) The Revised Post

-Shutdown Decommissioning Activities Report does not specifically address any environmental assessment of the site soil, groundwater, wetlands and surface water resources that would be implemented as part of the decommissioning. (c) The costs of environmental remediation and site restoration depend upon the nature and extent of contamination and, ultimately, the risk posed to potentially affected human and environmental receptors. These costs are best estimated following a comprehensive site assessment. The cost estimates for the work at the Pilgrim plant appear to be based on expectations rather than even a Preliminary (Phase 1) Site Assessment that is required under the MCP.

Declaration of David Howland, an environmental engineer and currently serving as Regional Engineer in the Western Regional Office of Mass Department of Environmental Protection Excerpts from the declaration of David Howland, an environmental engineer and currently serving as Regional Engineer in the Western Regional Office of Mass Department of Environmental ProtectioFebruary 20, 2019 Request for Hearing a nd helped manage MassDEP oversight of the non-radiological decommissioning of Yankee Rowe. His testimony further show s the actual and likely presence of hazardous materials

, not identified in the LTA

, that will increase costs and threaten public health and safety if not quickly identified and remediated.

51 4. Until a comprehensive site characterization is performed, radiation specialists, environmental engineers and other consultants simply cannot estimate with any reasonable certainty how much it will cost to perform all necessary work.

5. The site characterization conducted at Yankee Rowe led to the discovery of previously unaccounted for contamination that caused costs to escalate significantly above and well beyond the original, pre

-characterization cost

-estimates. At Yankee Rowe, for example, the discovery of polychlorinated biphenyl (PCB) contaminated soils and structures and the discovery of a tritium release from the spent fuel pool dramatically increased actual cleanup costs. The PCB contamination by itself caused significant cost increases because it is extraordinarily expensive to recover and treat PCB contaminated soils and sediment. The discovery of PCB coated steel and concrete building components also proved costly, because the PCBs had to be removed prior to recycling, reusing, or local landfill disposal of non

-PCB contaminated materials. Remaining PCB contaminated waste had to be transported to a PCB licensed disposal facility. In addition, the discovery of the tritium release necessitated an extensive and costly hydrological assessment to accurately depict the plume. Without a thorough facility characterization of potentially impacted areas, these types of issues and the associated cost increases cannot be quantified and decommissioning, and site restoration costs cannot be quan tified and decommissioning, and site restoration costs cannot be estimated with any reasonable certainty.

6. The Yankee Rowe decommissioning process also reinforces the fact that one cannot isolate the costs associated with radiological decontamination work from the costs associated with the remediation of non

-radiological contamination. At Yankee Rowe, for example, the comprehensive site characterization discovered that facility structures at the site would contain both radiological and chemical contamination. Because of this discovery, Yankee Rowe had to work with both state and federal regulatory authorities to select appropriate abatement and disposal options for the debris. It was also difficult to isolate the radiological wastes from the non

-radiological wastes, which caused the incurrence of costs that could not be attributed solely to radiological or non-to conduct both radiological and non

-radiological work at the same time and over a short eight

-year period. Based on my experience, I do not believe radiological decontamination can be conducted independently from hazardous materials Decommissioning Trust Fund contains sufficient funds by looking only at radiological decontamination costs. any site-based empirical data to support the work plan or its cost projections. For this reason, MassDEP is unable 52 to determine if Holtec can perform the non

-radiological clean up and restoration work outlined generally in its PSDAR without significant cost overruns. For example, as outlined above, the presence of PCBs can result in significant cost increases due to the need to assess and remediate contaminated soil, groundwater, and dispose of structural components.

oils throughout the plant once it performs a comprehensive site assessment. As with PCBs, asbestos abatement of mastics, mortar mixes, caulk, flooring, wall board, ceiling tiles, roofing and insulation will be a significant and costly environmental clean-up obligation. Other materials such as lead and halogenated degreasers like trichloroethylene can require extensive work to remediate and are likely to be found at Pilgrim given its age and the activities conducted at the site.

Hazardous Waste Dumping 51 Numerous sources have reported that drums of hazardous waste were buried on the Pilgrim site in the 1980s and/or 1990s.

93 Barrels of chemical waste were reportedly shipped -planted with evergreen trees.

51 https://jonesriver.org/getfile/ccbw/2012/10/RAD

-REPORT_2017.07.18_VS3.pdf (Attachment 3)

53 This contamination was the subject of public comments to the NRC in 2007.

52 These comments The public, NRC officials and Entergy staff also are well aware of burials off the and of remediation.

In October 2015, community members filed a forma53 report to MassDEP about these hazardous materials. The Chapter 21E report triggers regulations that requires the agency to investigate and report its findings to the public. MassDEP followed up a year later saying that without more evidence, such as samples showing contamination, or pictures of stuff being buried, there is nothing more the agency could do.

There may be additional waste buried that requires investigation. Holtec must conduct the necessary investigations, and its decommissioning costs must include whatever is required to make the site clean.

G. based on outdated documents.

Holtec used the 2002 GEIS to base its decision on radiological impacts to the public and workers. (Holtec PSDAR 5.1.8) The outdated GEIS in turn used risk coefficients per unit dose

52 Bramhall W. October 2013 Pilgrim Coalition Newsletter.

<http://archive.constantcontact.com/fs159/1109945140723/archive/1115182751860.html> Accessed 11/24/2015 53 21E is a classification given to hazardous material disposal sites by MassDEP.

54 recommended by the International Commission on Radiological Protection (ICRP) issued in 1991- 28 years ago. BEIR VII report (2006), 54 the most recent report from the National Academies, found far greater health impacts than the 1991 ICRP. BEIR VII found mortality rates for women from exposure to radiation were 37.5 % higher than a BEIR 1990 report and that the impact of allowable radiation standards on workers was twice that estimated in 1991. Allowable dose during decommissioning must be reduced to reflect BEIR VII, new and significant information supported by the timated decommissioning costs. BEIR VII lifetime risk model predicts that approximately 1 person in 100 would be expected to develop cancer (solid cancer or leukemia) from a dose of 0.1 Sv [10,000 millirem] above background from a lifetime (70 year) exposure to various levels of radiation. Exposure to 25 millirem/year equates to a lifetime cancer risk of 175/100,000; whereas a 10 millirem/year equates to a lifetime cancer risk of 70/100,000

-a significant difference when considering that EPA permits only 1 in 100,000.

mixture of chemicals is a lifetime cancer incidence risk of 1 in one hundred thousand (1/100,000).

one chemical is lifetime cancer incidence risk o f 1 in a million (1/1,000,000)

Lifetime Cancer Risk estimates based on BEIR VII are much higher.

The Table below, based on 1 person in 100 would be expected to develop cancer (solid cancer or leukemia) from a dose of 0.1 Sv [10,000 millirem] above backgroundyear) exposure to various levels of radiation.

54 https://www.nap.edu/catalog/11340/health

-risks-from-exposure-to-low-levels-of-ionizing-radiation 55 a used to develop risk models, risk estimates are uncertain, and estimates that are a factor of two or three larger or smaller cannot be Exposure-millirem/year Lifetime Cancer Incidence Risk Cleanup Standards 10 millirem/year 70/100,000 (0.7/1,000)

Current Massachusetts Limit for Unrestricted Use for its licensees; requested limit to Holtec 25 millirem/year 175/100,000 (1.75/1,000)

NRC Limit for Unrestricted Use site 100 millirem/year 700/100,000 (7/1,000)

NRC & Mass. Limit for Restricted Use site 500 millirem/year 3,500/100,000 (35/1,000)

Cancer Incidence Risk resulting from whole body exposure is about 2 times mortality risk Reproductive disorders occur at lower levels of radiation exposure than cancer H. decommissioning.

result in negative socioeconomic impacts. But it relied on outdated 2002 GEIS findings. A 2015 University of Massachusetts

-Amherst study, commissioned by Plymouth and ignored by Holtec, found that the economic impact on Plymouth alone would be almost $500 million, and that there would be a more than $100 million impact on the rest of the region:

55 55 The Pilgrim Nuclear Power Station Study: A Socio

-Economic Analysis and Closure Transition Guide Book Jonathan G. Cooper, University of Massachusetts Amherst, April 2015 (https://scholarworks.umass.edu/cgi/viewcontent.cgi?article=1080&context=larp_ms_projects)

56 Pilgrim Station in 2014 Direct Impacts

$440 Million Wholesale value of electricity produced 586 - Pilgrim Station workforce

$77 Million Wages and benefits for plant workforce

$60 Million Spending for goods and services in southeastern Massachusetts

$17.4 Million State and local taxes and other payments

$300K Charitable giving by Entergy and Pilgrim Station Secondary Impacts

$105 Million Additional economic output attributable to Pilgrim Station 589 - Additional jobs created by Pilgrim Station

$30 Million Wages and benefits paid by additional jobs Town of Plymouth Impacts 190 - Pilgrim Station employees living in Plymouth

$24.9 Million Wages and benefits paid to plant employees

$58.5 Million Value of real estate owned by plant employees

$10.3 Million Municipal revenue from Pilgrim Station

$950K Municipal revenue from employee property tax payments

$23K - $61K Municipal revenue from biennial refueling outages Regional Impacts stimulates additional economic activity in Plymouth and Barnstable counties. The in-region spending by both Pilgrim Station vendors and plant employees creates an additional $105 million in regional economic output. Nuclear power plant employment is stable and well

-compensated, enabling employees to attain home ownership.

Additional socioeconomic impacts include that that Radiological Emergency Planning contributions from the licensee to towns and the state will drop despite the fact that the risk is not eliminated.

57 to licensees of operating reactors in the Commonwealth was $482,901.

56 emergency planning zone negotiate funding with Entergy. 2016 receipts ranged from $85,000/yr. to $295,000/yr. plus monies for training and equipment. If the towns do not continue to receive funds, training and equipment, they will be unable to provide the protection that their community needs, deserves and that they want to provide. Pending legislation in the state legislature would require that the licensee fund post shutdown emergency planning expenses.

Also, actual or perceived contamination in Cape Cod Bay and surrounding waterways will have regional impact on coastal economies. F or example , on c o mmerc i a l s e af ood, m ar i ne t r a nspo r t a ti on, c o a s t a l tou r i sm a nd r ec r ea t ion, m ar i ne s c i e n c e and t ec hno l og y , m ar i n e-re l a t e d c ons t r u c ti on a nd i n f r a st r u c t ure, and real estate

. I. cost estimate assumptions ignore the cost of managing Low Level Radioactive Waste In addition to spent nuclear fuel, Class A, B and C Radioactive Waste (LLRW) is also stored at includes the control rods, resins, sludge, filters, and will include the entire nuclear power reactor when it is eventually dismantled, 57 and is another potential source of contamination onsite and to Cape Cod Bay resulting in significant increased costs.

56 Massachusetts Emergency Management 2016 Nuclear Preparedness Budget $482,910 (2015 spending $ 447,176) costs assessed on operating reactor licensees in the Commonwealth http://www.mass.gov/bb/h1/fy16h1/brec_16/act_16/h88000100.htm 57 High-Level Dollars Low

-Level Sense, Arjun Makhijani, A Report of The Institute for Energy and Environmental Research, 1992

58 The figure below that Pilgrim has about 20

-30 white storage containers located approximately 30 feet away from the coastal bank. It will be susceptible to the impacts of climate change

-sea level rise, storm surges, flooding. According to the NRC, only one of these containers currently contains Greater

-than-Class- C waste, the most toxic type of LLRW, and the others are presently empty. We assume they will be filled during decommissioning.

In the photograph, the white containers are for Low Level Radioactive Waste. To the right of the storage area is the LLRW building that compress materials to store or for shipment.

The LLRW waste will remain on the Pilgrim site, like the high

-level radioactive waste, until will be filed with the Texas Compact Commission to gain approval for disposal of out of ance may well be more expensive than to compact members, and timely acceptance is not guaranteed to non

-compact members. Potential higher fees and prolonged onsite storage are not factored into 59 oactive waste will result during the decommissioning process, and likely more of these storage containers pictured will be used.

J. LTA ignores potential costs from fires in structures, systems and components containing radioactive and hazardous material. During decommissioning, there is a serious concern about fire protection for the structures, systems, and components containing radioactive and hazardous materials in storage. Capabilities to monitor for and respond to these kinds of toxic emergencies are not addressed by Holtec. Fire in a building would result in increase in mixed waste adding to cost and also impact worker and locating sites where potential masses of contaminated material susceptible to ignition might accumulate during decommissioning and the costs of forestalling a fire by removing or limiting heat, oxygen, and/or fuel. Also , costs for training and equipment for offsite fire personnel that are counted on in an emergency

. K. DCE fails to consider costs likely to result from climate change impacts on the site.

any estimates of increased costs resulting from climate change. The documents that Holtec relied upon do not even mention climate change.

60 New and significant information, ignored by Holtec, show that climate change impacts on the site are likely to decreaincreacing costs.

58 Based on current levels of greenhouse gas prediction, the UN Intergovernmental Panel on Climate Change (IPCC) 2018 Report 59 shows sea levels will rise more rapidly; severe storms will occur more frequently, coinciding with high tides and exceptional wave heights; rising groundwater tables, and floods more severe. The National Geographic (December 16, 2015) identified Pilgrim among the 13 nuclear reactors impacted by se a-60 As climate change impacts get worse and decommissioning commences in 2019 storm drains and stormwater testing (discussed above) will become even more critical, as these outlets could become further conduits for pollution into Cape Cod Bay. Increased flooding and storm intensity, sea level rise, and rising groundwater tables could increasingly flush contaminates present in groundwater and soil into Cape Cod Bay.

The numerous negative impacts resulting from climate change not considered by Holtec that would likely increase decommissioning costs include:

58 evaluation report (AREVA Report) by Florida-based Coastal Risk Consulting (CRC

), Analysis of AREVA Flood Hazard Re-Evaluation Report: Pilgrim Nuclear Power Station, Plymouth, MA https://jonesriver.org/ecology/climate/

59 https://research.un.org/en/climate

-change/reports 60 http://news.nationalgeographic.com/energy/2015/12/151215

-as-sea-levels-rise-are-coastal-nuclear-plants-ready/

61 Increased flooding and storm surge resulting from climate change is likely to cause corrosion of underground piping, tanks and structures and subsequent leakage. And corrosion and potential leakage of the Greater

-than-Class-C waste and low

-level waste containers located close to Cape Cod Bay.

Radiological and hazardous waste contamination, if not cleaned up quickly, will be washed out into Cape Cod Bay unable to be retrieved.

Severe storms and flooding can result in loss of offsite power and potential damage to the diesel generators located by the bay. The spent fuel pool requires electricity to operate its safety systems.

In Fukushima extreme weather conditions at the site prevented workers to perform necessary mitigating actions. Severe storms and flooding could present conditions at Pilgrim so that workers could not perform their jobs.

Once again, contaminants; and these costs are not L. Holtec cost estimates fail to consider that a significant shortfall in funds could occur if DOE requires repackaging of spent nuclear fuel into new containers approved by DOE for transportation.

The U.S. Government Accountability Office reported in 201of the standard contract, the agency does not consider spent nuclear fuel in canisters to be an acceptable form for waste it will receive. This may require utilities to remove the spent nuclear fuel already packaged in dry sto 62 Nuclear Fuel Management: Outreach Needed to Help Gain Public Acceptance for Federal Activities That Address Liability, GAO

-15.141, October 2014, P. 30.

61 Repackaging spent fuel so that it can be transported off

-site will be expensive, but that cost has been ignored by Holtec.

62 According to Task Order 12: Standardized Transportation, Aging, and Disposal Canister Feasibility Study, Option 3 (1 PWR/1 BWR/13.1/U) it will cost $34,311,000,000 to repackage 140,000 MT; the per ton cost is $245,078.00.

63 A BWR assembly has an average weight of 281 Kg, and thus, the per assembly cost is ~$68,887.00. At the Pilgrim station, repackaging could add $261,770,600 to the predisposal costs, not included in D&Nuclear Waste Policy Act requires reactor operators to pay for this additional expense from the NWPA fund.

This per-assembly cost above is based on one large centralized repackaging facility handling the entire projected SNF inventory. If reactor operators have to establish repackaging infrastructures at decommissioned or closed reactors, the lack repackaging becomes an even more expensive proposition.

M. Holtec fails adequately to consider delays in the work schedule leading to increased costs for overhead and project management

. Cleaning up previously unknown radiological or nonradiological contamination will delay the work schedule escalating costs. There inevitably will be other delays as there always are in large projects. HDI is new to decommissioning.

61 http://www.gao.gov/assets/670/666454.pdf

] 62 Robert Alvarez analysis for Pilgrim 2018, https://ips

-dc.org/ips

-authors/robert

-alvarez/ 63 https://curie.ornl.gov/system/files/documents/not%20yet%20assigned/STAD_Canister_Feasibility_Study_AREVA_Final_1.pdf (p-5-2) 63 N. cost estimates fail to consider pending state

-law requirements that will decrease funds available for radiological decontamination.

There are a number of now

-pending Massachusetts laws and regulations that, if passed or adopted, they would result in additional costs to Holtec and reduce the funds available for decommissioning.

Radiological Cleanup Standard: The Massachusetts of Public Health issued a MEMO requesting that the licensee agree to a <10/ml/rem/yr. and < 4 ml/rem/yr. for drinking the MEMO. If Holtec does not agree, Massachusetts is considering a regulation that, after decommissioning is complete and the NRC has released the site, would require the site to meet this lower standard. State Legislation filed 01/19 by Senator deMacedo (S. 183579) and Representative Muratore (HD 1752) includes a

< 10 ml/rem/yr. standard and less than 4ml/rem yr. for drinking water pathways.

Pending state

-law requirements for funding offsite emergency planning and H.181704, filed by Representatives Cutler and LaNatra require a licensee to fund offsite emergency planning post shutdown.

H183826 filed by Representatives Meschino and Cutler requiring an increase in funding for MDPH monitoring.

Pending state

- law requiring a $25 million annual fee to establish a Postclosure Trust Fund: SD 598 Sen 64 O. HDCE fails to consider DTF funds that would not be available if NRC does and site remediation.

HDI submitted a request to NRC to allow the DTF to be used for spent fuel management and site restoration costs; and asked NRC to approve the request by the time of the transfer. (Enclosure 2, LTA) If approved, it would divert hundreds of millions of dollars from the Decommissioning Fund for non

-decommissioning uses, and greatly increase the chances of a shortfall in the Decommissioning Fund that could leave the site radiologically contaminated.

Entergy has requested additional exemptions. Any licensee amendment request granted to submitted and would not apply to Holtec. Holtec likely will file similar license amendment request(s) and would be subject to a hearing because the request is directly related and intertwined with the LTA.

P. DCE fails to consider the economic consequences if the license exemption requests filed by Entergy may not be transferable to Holtec adding additional costs.

Entergy has requested additional exemptions. Any licensee amendment request granted to Entergy woulsubmitted and would not apply to Holtec. Again, Holtec must file its own license amendment request(s) and would be subject to a hearing because the request is directly related and intertwined with the LTA.

65 Q. pathway receptor populations and for that matter in the general public reports is the basis minority and low

-income populations would mostly consist of radiological effects. Based on the radiological environmental monitoring program data from PNPS, the SEIS determined that the radiation and radioactivity in the environmental media monitored around the plant have been well within applicable regulatory limits. As a result, the SEIS found that no disproportionately high and adverse human health impacts would be expected in special pathway receptor populations (i.e., minority and or low

-income populations) in the region as a result of subsistence consumption of As discussed in the foregoing at pp. 47-49, the at Nuclear Plants Task Force Final Report, September 1, 2006 64 that under the existing regulatory requirements the potential exists for unplanned and unmonitored releases of radioactive liquids to migrate offsite into the public domain undetectedLL TF Executive Summary ii)

64 https://www.nrc.gov/docs/ML0626/ML062650312.pdf

66 R. adiological accident(s)

Radiological accidents are neither remote

, speculative nor worst case scenarios; instead they are reasonably foreseeable. HDI (PSDAR, 5.19) concludes that the impacts of PNPS decommissioning on radiological accidents are small and are bounded by the previously issued GEIS. there are no impacts of severe accidents beyond (SEIS 5.1.2).

Both the GEIS and the SEIS concluded the risk from severe accidents is small. They improperly ignore vulnerability and the impact of a spent fuel pool accident or ISFI accident on decommissioning costs and public safety and environment.

However, as we show, the spent fuel pool and dry casks are vulnerable and the potential consequences huge. Therefore, the potential of a radiological incident must be properly analyzed and then Holtec set monies aside for potential mitigation.

The GEIS and SEIS, that Holtec relied upon, do not bound environmental impacts or radiological accidents, for at least the following reasons.

The GEIS was published in 2002 and is outdated

. 65 For example, the BEIR VII Report and the University of Massachusetts Socio-Economic Impact Report had not yet been published, and many of the examples of radiological/

hazardo us contamination had yet to occur.

The GEIS was also flawed. In assessing offsite related accidents, the GEIS only considered: seismic events, aircraft crashes (not small aircraft, that pose the more realistic and serious

65 Statement, Dr. Gordon Thompson, December 19, 2013

.

67 threat), tornadoes with high winds; and fuel related accidents

-fuel drops and loss of water, ignoring the greatest danger the partial loss water in the spent fuel pool

. The GEIS and SEIS both ignore the escalating terrorist threat with US infrastructure, including nuclear reactors as targets. Both predate awareness of an increased threat from cyber

-attacks, 66 drones, and electromagnetic attacks.

67 For example, while reactor safety systems are more or less isolated from an outside cyberattack, a hack knocking out the electrical grid system would shut down power to all reactor safety systems. On

-site emergency power generators are then vulnerable to insider and armed assault seeking to cause a meltdown. Loss of electric grid may disenable security cameras.

The GEIS and SEIS incorrectly assert that the environmental impact of accident

-induced or attack-induced pool fires is SMALL. That assertion is incorrect. The environmental impact is LARGE due to the large inventory of radionuclides in the pool.

totally ignore ISF S I radiological accidents. The casks are vulnerable to attack and releases from cracks caused by age, corrosion, manufacturing defects. Each cask contains a huge amount of radioactivity and each cask contains >1/2 the Cesium

-137 released at Chernobyl. The environmental impact is LARGE. Emergency plans are insufficient now during operations; and will be far less sufficient when funding is reduced and then completely cut to offsite departments

- MEMA, local EPZ towns

66 December 15, 2017, NRC issues license amendment to Pilgrim to change the implementation date for cyber security upgrades from December 15, 2017 to December 31, 2020 after Pilgrim is closed

. 67 Electromagnetic Defense Task Force (EDTF): 2018 Report. (Source: US Air Force's Air University; issued Nov 28, 2018). From 2022 August 2018, Air University Website, LeMay Papers http://www.defense

-aerospace.com/articles

-view/release/3/198020/report

-highlights

-gaps-in-us-electro_magnetic

-capabilities

,

68 and host communities. For example, the sirens are coming down and recent disasters have demonstrated cell and standard phones cannot be relied upon.

Also, the GEIS and SEIS use an inappropriate arithmetic definition of radiological risk, with respect to severe accidents, is a risk assessment

- the product of the probability and the consequences of an accident. This means that a high consequence low

-probability events, like a severe accident, will result in a small impact determination, because the probability is determined to be low so no matter how severe the consequences they will be trivialized.

The risk and consequences are considered low because NRC had not in 2002, or now, conducted the comprehensive empirical and analytic inquiry needed to thoroughly understand probability and consequences; they inappropriately assume that the risk environment remains Spent Fuel Pool Accidents Ignored by the GEIS, SEIS and Holtec

- Examples Fuel Handling Accidents

Accidents can and do happen, even with single

-proof cranes. For example at Vermont Yankee (May 2008) 68 and it almost dropped a load of high

-level radioactive waste during the first removal of spent fuel assemblies from the spent fuel pool into a cask for dry cask storage outside of the plant. According to reports at the time, the brakes on the crane did not respond properly because its electrical relays it to stop four inches above the floor. Another mishap or nea r-miss failure with a single

-proof crane

68 https://www.reformer.com/stories/nrc

-reviews-vy-safety-system-after-crane-failure,65923

69 occurred at Palisades March 18, 2006 attirbutable to worker error

69. Human error, either in operations or manufacturing, is not considered, as it needs to be, in the GEIS, SEIS or by Holtec.

Canister Drop in the pool

If a cask is dropped in the pool and the pool floor is breached, there are many safety

-related components located on the floors below the spent fuel pool which could be disabled that could simultaneously initiate an accident and disable accident mitigation equipment. If a hole is punched in the pool floor or walls and water is lost simply to the top of the assemblies, a pool fire will likely follow.

A canister drop can lead to a crack in the canister

- especially a concern with HBU fuel. Each canister contains over 1/2 the Cesium

-137 released at Chernobyl.

Causes of Spent Fuel Pool Cooling Water Loss. significant draw

-Water could be lost from a spent-fuel pool throu g h leakage, boiling, s i ph oning, pu m p ing, displace ment by objects falling into the pool, or overturning of the pool. These m od es of water loss could arise from events, alone or in combination, that include: (i) acts of malice by persons within or outside the plant boundary; (ii) an aircr aft i mpact; (iii) an earthquake; (iv) dropping of a fuel cask; (v) accidental fir es or explosions

.70 Partial drain

-down: The GEIS did not recognize different consequences of both a full drain-down and a partial drain

-down. This is an important omission because total drainage of the pool is not the most severe case of water loss. In a partial drain

-down the presence of residual water would block air convection, e.g., by blocking air flow beneath the racks.

71 Previously, in

69 https://www.nirs.org/press/03 2006/ 70 Environmental Impacts of Storing Spent Fuel and High

-Nuclear Waste Confidence Decision and Environmental Impact Determination, Gordon Thompson, February 6, 2009; Comments on the US Nuclear Regulatory CommissionFuel Pool for a US Mark 1 Boiling Water Reactor, Gordon Thompson, August 1, 2013 71 http://www.environmental

-defense-institute.org/publications/Cover.Ltr.Thompson.NRC.SNF.Short.p df 70 filings made during a 2002 license

-amendment proceeding, NRC staff assumed that a fire would be inevitable if the water fell to the top of the racks.

Pool Fire Ignition Time: NRC Staff and industry today incorrectly claim that that it would take, a minimum of 10 hours1.157407e-4 days <br />0.00278 hours <br />1.653439e-5 weeks <br />3.805e-6 months <br /> for the fuel in a boiling water reactor aged 10 months or in a PWR for 16 months to heat to zirconium ignition temperature; and that the 10

- the licensee to take onsite mitigation measures or, if necessary, for offsite authorities to take appropriate response actions using an all

- NRC staff assumes that the minimum delay time for SNF ignition can be calculated by further assuming that an SNF assembly is perfectly insulated thermally. The NRC analysis provides no basis for assuming these assumptions are correct.

A 10-hour minimum delay time for BWR SNF aged 10 months is potentially plausible. But that is not the whole story. For example, an attack scenario could cause partial drain

-down and a local radiation field precluding access; and likewise, a fuel handling accident during transfer from pool to dry casks

- such as a cask drop.

Mitigation. enough time to put out a spent fuel fire. An attack scenario could rapidly cause partial drain

-down and result in a local radiation field that precludes access to the fire. There is no basis for assuming fficient. For example, Pilgrim supplemental water had little to no probability of working, especially in severe storm conditions.

72 72 Presentation to NRC: Status of Fukushima Lessons, Union of Concerned Scientists, David Lochbaum, July 31, 2014, https://www.nrc.gov/reading-rm/doc-collections/commission/slides/2014/20140731/lochbaum

-20140731.pdf

71 Evacuation. Ten hours is not enough time for offsite authorities to take appropriate response actions using an all

-hazards approach emergency management plan.

preparedness recommendation, option EP

-2, essentially eliminates offsite emergency preparedness at Level 2 (pool storage) and Level 3 (ISFI storage). In addition, the notification requirement to State and Local Governmental is changed from 15 minutes to 60 minutes; and public alert and notification systems and Evacuation Time Estimates (even with a significant population change) are not required. As early as Level 2, challenging drills and exercises involving hostile action said not to be warranted, and ORO participation in radiological drills and exercises would no longer be required. Even with offsite emergency plans in place during operations, a timely (less than 10 hour1.157407e-4 days <br />0.00278 hours <br />1.653439e-5 weeks <br />3.805e-6 months <br />) evacuation is not possible 73; therefore, absent offsite preparedness there is no way that 10

-hours would allow offsite authorities to evacuate the population.

ISF SI Accidents the GEIS, SEIS and Holtec Ignore

- Examples (PSDAR, pg.,25) They do not consider, as they should, something going wrong.

Causes of a Dry Cask Canister Rupture. Holtec ignores the potential of a dry cask canister rupture.

Casks, although safer than spent fuel pool storage, are vulnerable to attack ,

Pilgrim Watch Comment (11.16.2014) Waterways Application, No. W14

-414, Cape Cod Bay, Plymouth, Plymouth County, Ch 91 Application of Entergy Nuclear Operations, Inc. Pilgrim Nuclear Power Station; Pilgrim Watch Comment NRC, January 30, 2014 73 Station Until The NRC Can Assure Emergency Preparedness Plans Are In Place To Provide Reasonable Assurance Public Health Supplement To Its August 30, 2013 2.206 Petition To Modify, Suspend, Or Take Any Other Action To The Operating License Of Pilgrim Station Until The NRC Can Assure Emergency Preparedness Plans Are In Place To Provide Reasonable Assurance Public Health & Safety Are Protected In The Event Of A Radiological Emergency (09.03.2014) https://www.nrc.gov/docs/ML1433/ML14338A180.pdf

72 described below.

74 Vulnerability Pools and ISFSI to Acts of Malice Reactors make ideal targets for outside or inside attackers for the simple reasons that they in a military sense. The design of GE BWR Mark I reactors like Pilgrim makes those reactors highly vulnerable to attack because their spent fuel pools are in the top floor of the reactor, outside removed from inside the reactor is placed in thin

-walled dry casks. The casks are stacked vertically out in the open making them vulnerable to attack. Each cask contains about 1/2 the Cesium

-137 released during the Chernobyl accident.

The ISF SI is in the process of being moved to higher ground. But it will be very close to a public road, Rocky Hill Road. There is no plan to place the ISF SI in a reinforced building, surround it with earthen berms (a dirt cheap solution) or erect a blast shield. The ISF S I as it now sits with the canisters lined up vertically c The following table, prepared by Dr. Gordon Thompson for the Massachusetts Attorney General, 75 summarizes available means of attack. It shows that nuclear power plants are vulnerable.

74 Environmental Impacts of Storing Spent Fuel and High

-Level Waste from Commercial Nuclear Reactors: A Environmental Impact Determination, Gordon Thompson, February 6, 2009 (https://www.nrc.gov/docs/ML1001/ML100150145.pdf); Comments on the US Nuclear Regulatory l for a US Mark 1 Boiling Water Reactor, Gordon Thompson, August 1, 2013 (https://www.nrc.gov/docs/ML1401/ML14016A068.pdf) 75Entergy Nuclear Operand Petition for Backfit Order Requiring New Design features to Protect Against Spent Fuel Pool Accidents, Docket 73 Dr. Gordon Thompson also analyzed the impact of a shaped charge as one potential instrument of attack.[30] The analysis shows that the cylindrical wall of the canister is about 1/2 inch (1.3 m) thick, and could be readily penetrated by a vaila b le wea pons. The spent fuel

No. 50-293, May 26, 2006 includes a Report to The Massachusetts Spent Fuel Pool

- Risks and Risk-Reducing Options Associated with Pool Storage of Spent Nuclear Fuel at the Pilgrim and Vermont Yankee Nuclear Power Plants, Gordon Thompson, May 25, 2006 (Risks and Risk

-Reducing Options Associated with Pool Storage of Spent Nuclear Fuel at the Pilgrim and Vermont Yankee Nuclear Power Plants, Gordon Thompson, May 25, 2006. (https://www.nrc.gov/docs/ML1001/ML100150145.pdf

) [30] Gordon R. Tho mpson, Environmental Impacts of stor i ng Spent Nuclear Fuel and High- Level Wa s t e from Commerci a l Nucl e ar Reactor s: A Critique of NRC's Waste Confi dence Decision and Environmental Impact Determination (Ca mbridge, Massachusetts:

Institute for Resource and Security Studies, 6 February 2009). Tables also in Declaration of 1 August 2013 by Gordon R.

Tho mpson: Com ments on the US Nucle a r Regulatory C om m i Consequence Study of a Beyond-Design-Basis Earthquake Affecting the Spent Fuel Pool for a US Mark I Boiling Water Reactor 74 as semblies in s i de the canister are long, narrow tubes made of z irconium alloy, inside of which uranium oxide fuel pellets are stacked.

The walls of the tubes (the fuel cladding) are about 0.023 inch (0.6 m m) thick. Zirconium is a flam mable metal. Table 7-7: Performance of US Army Shaped Charges, M3 and M2A3 Target Material Indicator Type of Shaped Charge M3 M2A3 Reinforced concrete Maxi m u m wall t hickn e ss that can be perforated 60 in 36 in Depth of penetration in thick walls 60 in 30 in Dia meter of hole 5 in at entrance 2 in m i n imum 3.5 in at entrance 2 in m i n imum Depth of hole with second charge placed over first hole 84 in 45 in A r mor plate Perforation At least 20 in 12 in Average dia meter of hole 2.5 in 1.5 in Notes: (a) Data are fro m: A r my, 1967, pp 13

-15 and page 100. (b) The M2A3 charge has a mass of 12 lb, a ma xi m u m di a meter of 7 in, and a total length of 15 in including the standoff ring. (c) The M3 charge has a mass of 30 lb, a m ax i m um dia meter of 9 in, a charge length of 15.5 in, and a standoff pedestal 15 in long.

75 Table 7-8: Types of Atmospheric Release from a Spen t-Fuel-Storage Module at an ISFSI as a Result of a Potential Attack Type of Event Module Behavior Relevant Instruments and Modes of Attack Characteristics of Atmospheric Release Type I: Vaporiz a ti o n Entire module is vaporized Module is within the f ireb all o f a nuclear-weapon explosion Radioacti v e content of module is lo f ted into the at mosphere and a mpli fies fallout Type II: Rupture and Dispersal (Larg e) MPC and overpack are bro k en o pen Fuel is dislodged from MPC a nd broken apart Some ignition of zircaloy fuel cladding may occur, without sustained co mbustion Aerial bombing Artillery, rockets, etc. Effects of blast etc. outside the fireball of a nuclear weapon explosion Solid pieces of various sizes are scattered in vici n ity Gases and s mall particl e s form an aerial plu me that travels downwind Some release of volatile species (esp. cesiu m-137) if incendiary effects occur Type III: Rupture and Dispersal (S mall) MPC and overpack are ru p tured but retain ba s ic shape Fuel is da maged but most rods retain basic sha p e No combustion inside MPC Vehicle bomb I mpact by commercial air craft Perforation by shaped charge Scattering and plu me fo r mation as for Type II event, but involving s maller a mounts of m a t er i al Little r e le ase of volatile s p e c ies Type IV: Rupture and Co m bu stion MPC is ruptured, allowing air ingress and egress Zircaloy fuel cladding is ignited and co mbustion propagates within the MPC Missiles w ith tandem warheads Close-up use of shaped charges and incendiary devices The r m ic lance R emoval of overpack lid Scattering and plu me fo r mation as for Type III event Substantial rel ease of volatile species, exceeding amounts for Type II relea s e 76 One scenario for an at mospheric release fr o m a dry cask would involve mechanically creating a co mparatively s mall hole in the canister.

This could be the result, for example, of the air blast produced by a nearby explosion, or by the impact of an aircraft or m issile. If the force was sufficient to puncture the canister, it would also shake the spent fuel asse mblies and da mage their cladding. A hole with an equivalent dia meter of 2.3 m m would release radioactive gases and particles and result in an inhalation dose (CEDE) of 6.3 rem to a person 900 m downwind f r om the release.

Most of that dose would be attributable to release of two-millionths (1.9E

-06) of the MPC's invent ory of radioisotopes in the "fines" category.

Another scenario for an at m ospheric release would involve the creation of one or more holes in a canister, with a size and positi on that allows i ngress and e gress of air. In addition, this scenario would involve the ignition of incendiary material inside the canister, causing ignition and sustained burning of the zirconium alloy cladding of the spent fuel. Heat produced by burning of the cladding would release volatile radioactive material to the at mosphere. H eat from co mbustion of cladding w ould be a mple to raise the te mpera ture of adjacent fuel pellets to well above the boiling point of cesium.

Potential for Release from a Cask and Consequences: Dr. Thompson observed that a cask is not robust in ter ms of i ts ability to withstand penetration by weapons that are available to sub-national groups.

A typical cask would contain 1.3 MCi of cesiu m-137, about half the total a mount of ce s iu m-137 released during the Chernobyl reactor accident of 1986.

Most of the offsite radiation exposu re from the Chernobyl accident was due to cesiu m-137. Thus, a fire 77 inside an I SFSI module, as described in the preceding paragraph, could cause significant radiolog ical har m.76 Casks may corrode and leak especially over a long period of onsite storage Casks may remain onsite indefinitely subjected at Pilgrim, for example, to salt induced crack may crack within 30 years. No current technology exists to inspect, repair, or replace cracked canisters. With limited monitoring, we will only know after the fact that a cask has leaked radiation.

77 judge its depth in Holtec Casks

78. (October 6, 2015) Dr. Kris Singh said that it is not feasible to 79 Mitigation will be costly. The $3 million excess in the fund after decommissioning estimated by Holtec will be totally insufficient.

High Burnup Fuel (HBU)

Pilgrim has approximately 35% HBU; yet the NRC is just starting a test to see whether the casks can handle it, with results not in until 2027. Robert Alvarez (https://www.ips

-dc.org/ips-authors/robert

-alvarez/ ) explains the problems in doing so

Research shows that under high

-burnup conditions, fuel rod cladding may not be relied upon as a key barrier to prevent the escape of radioactivity, especially during prolonged storage in the "dry casks."

76 Ibid; and also see: Assessing risks of potential malicious actions at commercial nuclear facilities: the case of a proposed independent spent fuel storage installation at the diablo canyon site, Gordon Thompson, June 27, 2007 (https://www.nrc.gov/docs/ML1001/ML100150145.pdf

) 77 San Onofre Dry Cask Storage Issues analyses at: https://sanonofresafety.files.wordpress.com/2011/11/drycaskstorageissues2014 23.pdf 78 (https://www.youtube.com/watch?v=QtFs9u5Z2CA&t=17s) 79 (https://www.youtube.com/watch?v=QtFs9u5Z2CA&t=17s)

78 High-burnup waste reduces the fuel cladding thickness and a hydrogen

-based rust forms on the zirconium metal used for the cladding, which can cause the cladding to become brittle and fail

- a costly event. In addition, under high

-burnup conditions, increased pressure between the uranium fuel pellets in a fuel assembly and the inner wall of the cladding that encloses them causes the cladding to thin and elongate. And the same research has shown that high burnup fuel temperatures make the used fuel more vulnerable to damage from handling and transport; cladding can fail when used fuel assemblies are removed from cooling pools, when they are vacuum dried, and when they are placed in storage canisters.

High burnup spent nuclear fuel is proving to be an impediment to the safe storage and disposal of spent nuclear fuel. For more than a decade, evidence of the negative impacts on fuel cladding and pellets from high burnup has increased, while resolution of these problems remains elusive.

NRC Meeting Presentation Slides Dry Storage & Transportation of High Burnup, 9/6/18 meeting, slides 14 & 15: NRC said that storage and transportation of HBU is safe, providing no technical bases, for 60 years no guarantee for longer storage when fuel may still be onsite.

Consequences of a spent fuel pool fire or cask rupture.

The GEIS, SEIS and Holtec minimize the potential consequences of a spent fuel pool fire release limit, and the resulting off

-site damage to property and health would be unimaginable.

79 70 million curies.

80 Much of the damage from a pool fire or dry cask failure would be caused by the release of Cesium

-137. To make the risk meaningful, it is useful to compare the inventory of Cs

--137 released at Chernobyl.

81 Chernobyl

- 2,403,000 curies Cs

-- more than 44,000,000 curies Cs

-- 5,130,000 curies Cs

-137. Each cask contains more than half the total amount of Cs

-137 released at Chernobyl Studies of the consequences of a spent fuel pool fire show huge, potential consequences, ignored by Holtec and the documents Holtec relies on. 2016 Princeton Study: A major Spent Fuel Pool fire could contaminate as much as 100,000 square kilometers of land (38,610 square miles) and force the evacuation of millions.82 2013 NRC Study: A severe spent fuel pool accident would render an area larger than Massachusetts uninhabitable for decades and displace more than 4 million people.

83 2006 Massachusetts Attorney General Study: $488 Billion dollars, 24,000 cancers, hundreds of miles uninhabitable 84 80 Spent Nuclear Pools in the US: Reducing the Deadly Risks of Storage, Robert Alvarez, IPS, May 2011, pg., 14 81 See 2012 GAO Report: GAO 797, Spent Nuclear Fuel: Accumulating Quantities at Commercial Reactors Present Storage and Other Challenges, http://www.gao.gov/assets/600/593745.pdf

.. 82 F 24, no.3 (2016): 141

-173 http://scienceandglobalsecurity.org/archive/sgs24vonhippel.pdf; Science, May 24, 2016. (NRC variable at: http://www.sciencemag.org/news/2016/05/spent

-fuel-fire-us-soil-could-dwarf-impact-fukushima 83 Consequence Study of a Beyond Design

-Basis Earthquake Affecting the Spent Fuel Pool for A U.S. Mark I Boiling Water Reactor (October 2013) at 232 (Table 62) and 162 (table 33), Adams Accession NO ML13256A342) 84 r r Requiring New Design features to Protect Against Spent Fuel Pool Accidents, Docket No. 50

-293, May 26, 2006 includes a Report to The Massachusetts Attorney General On The Potential Consequences Of A Spent Fuel Pool Fire At The Pilgrim Or Vermont Yankee Nuclear Plant, Jan Beyea, PhD., May 25, 2006 (NRC RC Electronic Hearing Docket, Pilgrim 50

-293-LR, 26 pleadings, MAAGO 05/26 (ML061640065) & Beyea (ML061640329)

80 Dry Cask: A typical cask would contain 1.3 MCi of cesiu m-137, about half the total a mount of Ce s iu m-137 released during the Chernobyl reactor accident of 1986.

Most of the offsite radiation exposu re from the Chernobyl accident was due to Cesiu m-137. Thus, a fire inside an I SFSI module from a terrorist attack or significant rupture of the cask could cause significant radiolog ical har m 85 and huge expense. These facts cannot be ignored. The documents that Holtec relies upon, are outdated and factually incorrect. They do not bound environmental impact. Even today, NRC is ignoring both the vulnerability and severe consequences of spent fuel pools and cask storage. Site Specific analysis of spent fuel incidents are required before approval of the LTA. Funds for mitigation after a spent fuel accident must be included in cost estimates.

S. the Funds Necessary to Decommission the ISF S I. Holtec says that ongoing ISFSI operations will continue until 9/7/2063 (DCE 17) and the ISFSI will be decommissioned in 2063 (DCE 16ISFSI, in 2018 dollars will be about $4.2 million.86 DCE, pp 66, 70.

In making this estimate, Holtec again incorrectly assumes that decommissioning costs will not increase more than inflation. It also assumes, with no apparent basis particularly since ISFSI decommissioning will not happen until at least 54 years from now, that tDCE, pg. 25

.

85 Environmental Impacts of Storing Spent Fuel and High

-Level Waste from Commercial Nuclear ReactorNuclear Waste Confidence Decision and Environmental Impact Determination, Gordon Thompson, February 6, 2009; Comments nt Fuel Pool for a US Mark 1 Boiling Water Reactor, Gordon Thompson, August 1, 2013, pg., 30 86 81 the funds to pay ISFSI decommissioning costs will come from.

$1.134 billion estimated cost is the cost to decommission the site, safeguard the spent fuel until it can be transferred to the DOE and restore the impacted area of the site

. (PSDA R, p. 18; DCE, pg. 8)but not ISFSI decommissioning. (PSDAR, pg. 8)

Hoinclude the costs of decommissioning the ISFSIenough. This is particularly clear when the likely increase in decommissioning costs is taken into account. For example, if DOE fails to pick up the spent fuel by 2062, as H oltec assumes, then Pilgrim will began incurring significant additional costs; and that money has to be spent by the licensee before any possibility of refurbishment from D OE. In 2063 alone, spent fuel annual cost of approximatel y $7 million will exceed the $3.6 million left over.

Not picking up the fuel raises the possibility of far greater cost overruns to the tune of hundreds of millions of dollars.

ations show that the actual cost of decommissioning the ISFSI at the earliest point in time assumed by Holtec (2063), will be about $24 million if decommissioning costs between now and then increase at a rate 4% more than inflation, and would be about $6.5 million even if the decommissioning cost increase was only 1% more than inflation.

In the overall picture, a $6.5 to $24 million shortfall in the funds that must be available for ISFSI decommissioning is relatively small.

82 But this shortfall, together with the at least 1 6 other incorrect assumptions and ignored significant facts discussed above, each of which will result in additional costs above and beyond the funds available for decommissi oning. Cumulative impact must but was not considered.

The existing decommissioning trust funds do not provide a basis upon which the NRC could properly find the required financial assurance. Holtec Pilgrim and HDI are not financially responsible. The LTA should be denied and sent back to the drawing board. III. SITE ASSESSMENT

-NEPA (SECTION 2)

THE LICENSE TRANSFER AND AMENDMENT REQUEST DO ES NOT INCLUDE THE ENVIRONMENTAL REPORT REQUIRED BY 10 CFR 51.53(d), AND HA S NOT UNDERGONE THE ENVIRONMENTAL REVIEW REQUIRED BY THE NATIONAL ENVIRONMENTAL POLICY ACT BASES 1. The National Environmental Policy Act (NEPA) requires that a NEPA analysis be performed.

The NRC responsibilities under NEPA are triggered by the fact that Ross v. Fed. Highway Admin., 162 F.3d 1046, 1051 (10th ermitting [Holtec] to decommission the faciCitizens Awareness Network, Inc. v. Nuclear Regulatory Comm'n, 59 F.3d 284, 293 (1 st Cir. 1995). regulatory compliance, and then simply labelling its deciId.

83 2. NRC requires environmental impact statements for major federal actions. Approval of proposal as a whole would constitute a major federal action. NEPA requires federal agencies to prepare an Environmental Impact Statement for every 42 U.S.C 4332(2)(c); accord 10 C.F.R. 51.20 (a)(1). As discussed above with respect to Contention 1, and the environment.

40 C.F.R. § 1508.18 defines major may be major and which are potentially subject to Federal control and responsibilitysubject to [NRC] The D.C. Circuit Court of Appeals has held that a federal action is involved, agency makes a decision which permits action by other parties which will affect the quality of the , 481 F.2d 1079, 1088 (D.C. Cir. 1973). Consistently, the 9 th Circuit has held that because the NRC has datory plans, would Ramsey v. Kantor, 96 F.3d 434, 445 (9th Cir. 1996).

3. A NEPA review is required if there is a potential environmental impact.

that this problem will occur, and what environmental consequences would ensue in those circumstances.

Id., U.S.C. § 4332(2)(C); see also, e.g., Blue Mountains, 161 F.3d at 1211.

84 Even if the proposed license transfer might not have any environmental impacts, the possibility of significant environmental impacts precludes a FONSI and triggers the need for an Environmental Impact Statement.

that may be major and which are potentially C.F.R. § 1508.18 San Luis Obisco Mothers for Peace, or will not result from the proposed action is a close call, an [environmental impact statement] National Audubon Soc. v. Hoffman, 132 F.3d 7, 13 (2d. Cir. 1997) (reversing a decision by the U.S. Forest Service not to prepare an environmental impact statement because the Forest Service failed to consider the possible effects of the challenged action). Id. at 18. I d. at will not that an environmental impact statement is not required.

Id. at 13. 4. NEPA requires a comprehensive environmental review.

The NRC is required to take a Baltimore Gas & Elec. Co. v. Natural Res. Def. Council, Inc., 462 U.S. 87, 97 (1983).

environmspeculativeSan Luis Obispo Mothers for Peace v. NRC, 449 F.3d 1016, 1030 (9th Cir. 2006).

85 Found. on Econ. Trends v. Heckler, 756 F.2d 143, 154 (D.C. Cir. 1985). The potential effects of Pilgrim decommissioning (including operation of the ISFSI during the many years before it might be decommissioned) are neither remote or highly speculative; and they cannot be ignored.

5. NRC regulations require an environmental impact statement.

Post Operating License appropriate, to reflect any new information or significant environmental change associated with the applicant's proposed activities is decommissioned, an environmental impact statement is also required by 10 C.F.R. §§ 51.20 license pursuant to part 72 of this chapterfor the storage of spent fuel in an independent spent fuel storage installation (ISFSI) at a site not occupied by a nuclear power reacto r 6. An Environmental Assessment helps an agency determine whether the proposed action is significant enough to require preparation of an Environmental Impact Statement.

Marsh v. Or. Natural Resources Council, 490 U.S. 360, 371 (1989).

86 does not require agencies to select particular options, it is intended to foster both informed decision-making and informed public participation, and thus to ensure that the agency does not act In re Duke Energy Corporation (McGuire Nuclear Station, Units 1 and 2; Catawba Nuclear Station, Units and 2), CLI-02-17, 56 N.R.C. 1, 10 (2002).

it to face those stubborn, difficult to answer objections without ignoring them or sweeping them National Audubon Soc.

, 132 F.3d at 12 (citing , 772 F.2d 1043, 1049 (2d. Cir. 1985)). The Lathan v. Brinegar, 506 F.2d 677, 693 (9th Cir.1974).

7. The NRC cannot issue a Finding of No Significant Impact (FONSI) without first evaluating all the evidence.

The N RC can issue a FONSI only if it reasonably determines, based on an evaluation of . (40 C.F.R. § 1508.1

3) A FONSI must include . Blue Mountains Biodiversity Project v. Blackwood, 161 F.3d 1208, 1212 (9th Cir. 1998). See also Citizens Against Toxic Sprays, Inc. v. Bergland, 428 F. Supp. more important than the potential effects of a federal [action] upon the health of human beings Maryland-87 Service , 487 F.2d 1029, 1039

-If the agency determines that a full environmental impact statement is not necessary, the agency must then id. § 1508.14; New York v. NRC I, 681 F.3d 471, 477 (D.C. Cir. 2012).

As shown Intervene and Requests for Hearing in this proceeding

, the proposed LTA will have a significant impact. 8. The generic determination of 10 CFR § 2.1315 does not apply

. Holtec seems to contend that no environmental assessment is required proposed conforming license As shown at pages 3

-4 above, this is simply not so. The proposed license amendment:

(Proposed Amended License, p. 1, subparagraphs c and d), a finding that would have to overlook that the only asset of Holtec Pilgrim and Holtec Decommissioning International Contention 1, below) and that as a Holte c representative (Ms. Joy Russell) said ay an NDCAP meeting . Holtec itself has never decommissioned a site

.

88 MS. J. RUSSELL (Holtec): Holtec International has not decommissioned any sites.

a. assurance of no less Particularly given the inadequacy of the Decommissioning Trust Fund, this is a significant change.

b. Deletes the requirement that the Decommissioning Trust agreement prohibit 5). Because of these requested changes, the generic determination of

§2.1315 does not apply. In addition, the clear import of § 2.1315 is that when, as here, the requested amendment does far affected", as required by NEPA.

Finally, the license to reflect the transfer action, the Commission should (as provided in § 2.1315(a), determine that its generic determination not apply here for all of the reasons set forth herein, including those set forth below:

a. The license transfer agreement raises significant questions with respect to safety hazards and whether the health and safety of the public will be affected. b. Pilgrim has a long history of bad fuel, blown filters, leaks, releases, buried hazardous materials, and mismanagement (see pp. 36

-51, above)

c. Neither Holtec nor the NRC knows what contamination exists at the PNPS site.

d. Holtec has not conducted a site analysis. hazard 89 e. to support the identification, categorization, and quantification of radiological, regulated, and hazardous wastes in support of waste pp 8-9 f. Holtec has made only an initial cursory required by 10 CFR 50.75(g) records.

g. Holtec admits that a new site assessment is necessary so that radiological, regulated, and hazardous wastes are identified, categorized and quantified to support decommissioning and waste management planning.. h. s Lessons Learned Task Force that under the existing regulatory requirements the potential exists for unplanned and unmonitored releases of radioactive liquids to migrate offsite into the public domain undetectedand recommended revising the regulations.

i. f areas will See pp. 5 3-54 above. Department of Environmental Protection list hazardous materials on site or likely to be onsite. 9. The categorical exclusion of 10 CFR § 51.22 does not apply

. In its LTA, Holtec also says (LTA, pg

. 10) that exempt from environmental review because it falls within the categorical exclusion contained in 10 CFR 51.22(c)(21) for which neither an Environmental Assessment nor an Holtec is again incorrect. 10 CFR § 51.22environmental iany 90 interested person Pilgrim Watch is , and itEnvironmental Assessment [and] an Environmental that exist at PNPS (See pp.

88-89, abov e), the Commission should determine that an environmental assessment or environmental impact statement is required

. environmental assessment or environmental impact statement Approvals of direct or indirect transfers of any license issued by NRC or any associated amendments of license required to reflect the approval of a direct or indirect transfer of an NRC license10 CFR § 51.22 (c)(21)) goes much too far. 10 CFR § 51.22 (a) says that some categories of licensing and regulatory actions are regulations directed to licensing or licensing transfers can have any environmental effect and are automatically excluded from any environmental review.

10. statements.

Holtec say s that it PNPS site specific decommissioning activities are less than and bounded by the previously issued 91 numerous environmental impacts associated with resulting from events that were not considered at all.

-35). But Holtec fails to show potential environmental impacts that would result from Holtec not performing a thorough and proper site assessment at the beginning of the decommissioning process. Such an up-front site assessment is required for Holtec to properly cleanup the site, to provide a valid cost estimate, and to assure the money will be there to do the job needed to protect public health and safety. As shown here and in Petition s , previously 11. The lack of sufficient decommissioning funds increases the need for an environmental impact statement.

Neither Holtec Pilgrim nor HDI is financially responsible, neither has or has access to any funds other than the DTF, and the DTF does not and will not have sufficient funds for decommissioning

. The NRC agrees that a shortfall in decommissioning funding would place public health, safety, and the environment at risk.

92 The requirements for financial assurance were issued because inadequate or untimely consideration of decommissioning, specifically in the areas of planning and financial assurance, could result in significant adverse health, safety and environmental impact s. The purpose of financial assurance is to provide a second line of defense, if the financial operations of the licensee are insufficient, by themselves, to ensure that sufficient funds are available to carry out decommissioning (63 FR 50465, 50473).

NR C Questions and Answers on Decommissioning Financial Assurance, at 1 (ADAMS Accession No. ML111950031, italics added

). Absent a complete and accurate environmental impact statement, neither the NRC nor anyone else will know what needs to be done to completely and safely decommission Pilgrim and protect the public health and safety, or what is needed to provide real financial assurance.

FACTS 87 Pilgrim Watch specifically incorporates, as if fully set forth here, the Bases of Finances in section 1, the Facts Supporting section 1, and the Bases of section 2. As shown above, NEPA and NRC Regulations require an environmental impact statement. The actual facts here make clear that prior environmental statements do not include, and that neither Holtec nor the NRC knows, the actual conditions at the Pilgrim site.

Other facts supporting at least one of section 1 and section 2 include the following

. Pilgrim is located on the shore of Cape Cod Bay; in a densely populated neighborhood; on top of the Plymouth

-

87 Many of the facts set forth below here also support Contention 1 and should be considered in connection with Contention 1.

93 tourist location. Its location puts a premium on an early site assessment and NEPA analysis . 1. Pilgrim is sited beside Cape Cod Bay. Due to the topography of the site, contaminants will leak into the Bay.

2. Massachusetts and Cape Cod Bays are tidal. NUREG

-1427, 2.2.5.1.

3. Contaminants leaking into the bay during an incoming tide will be drawn into Plymouth, Duxbury and Kingston Bays, up the rivers, such as the Jones, Eel, and Bluefish Rivers and into estuaries, marshes and wet lands; in the outgoing tide they will flow into and circulate around Cape Cod Bay and beyond.

4. Climate change is causing sea level rise

, increases in the number and severity of storms

, and flooding. This will result in contaminants left onsite washing out to Cape Cod Bay and adjacent waters; and hasten corrosion by exposure to salt and moisture of buried pipes, tanks and structures left in the ground that contain radiological or hazardous material. Low Level Radioactive Waste is stored about 30 feet from Cape Cod Bay, adequately consider and analyze this

. An early site assessment and NEPA must analyze the impact of climate change on the site.

5. tal impact statements do not adequately consider the possibility of s ite-neighborhoods (and potential airborne asbestos and lead contamination, as well as potential impacts from a radiological incident or radiological dispersion during demolition work and disruption of soils).

94 6. -Carver Aquifer, the second largest aquifer in Massachusetts, that provides drinking water to several towns and supports many natural resources. Neither Holtec nor the NRC knows what contamination exists at the Pilgrim site.

7. Holtec has not conducted a site analysis.

8. 9. Holtec admits a to support the identification, categorization, and quantification of radiological, regulated, and hazardous wastes in support of waste management pp 8-9. 10. Holtec has made only an initial cursory f PNPS decommissioning records required by 10 CFR 50.75(g) records.

11. Holtec admits that a new site assessment is necessary so that hazardous wastes are identified, categorized and quantified to support decommissioning and was te management (CDE, p. 14).

12. Previously issued environmental impact statements do not and cannot bound numerous incompletely and inaccurately discussed in the previously issued environmental impact statements or are not considered by them at all.

13. A site assessment at the Pilgrim site would provide new and important information that is not included in previously issued environmental impact statements, and that would show that previously issued environmental impact statements are outdated and incomplete.

95 14. NEPA explicitly requires an Environmental Impact Statement if an action such as a license transfer may be major and which are potentially subject to Federal control and Specific facts and impacts that Holtec and previous environmental impacts have not 15. Holtec says its estimates are based on nothing more than what appears to be an initial cursory sometime in the future (PSDAR, 8-9) 16. Pilgrim site. (DCE, p.2)

17. The GEIS, SEIS and Holtec incorrectly assume that the Pilgrim site is essentially clean. history, and new and significant information since the GEIS and SEIS were published. These documents do not bound environmental impacts. A new site assessment and NEPA are required. 18. An early site assessment and NEPA analysis will prevent the unexpected expenses experienced at other sites. 19. An updated site analysis or environmental impact statement would show that actual decommissioning costs, particularly removal of contamination and site restoration, may be far t other sites from happening here. This is illustrated by the facts that:

96 a. At Connecticut Yankee , previously undiscovered strontium

-90 contributed to the actual cost of decommissioning Connecticut Yankee being double what had been estimated.

b. During the decommissioning of Maine Yankee, the licensee encountered pockets of highly contaminated groundwater dammed up by existing structures, leading to cost increases.

c. The Yankee Rowe site in Massachusetts incurred significant cost increases during decommissioning when PCBs were discovered in paint covering the steel from the vapor container that housed the nuclear r eactor, as well as in sheathing on underground cables.

Other plants such as Diablo Canyon 1&2, and San Onofre 2&3 have ended up costing much more than what was estimated for decommissioning.

- Requires Site Assessment & NEPA 88 20. Pilgrim opened with bad fuel and no off

-gas treatment system

21. Later Pilgrim blew its filters in June 1982.

22. Operating with bad fuel and blowing its filters, prompt ed Mass Dept. Public Health to do a case-control study of adult leukemia testing the hypothesis that the closer you lived or worked at Pilgrim there would be an increase in leukemia. The hypothesis was confirmed.

89 88 Pilgrim Chronology 1967

- 2015, https://jonesriver.org/legal/pilgrim

-chronology-1967-2015/ 89 The Southeastern Massachusetts Health Study

[published in the Archives of Environmental Health, Vol. 51, p.266, July

-August 1996 (Pilgrim Motion Request for Hearing and Motion to Intervene, May 2006, Exhibit F

-2, NRC Adams, EHD, Pilgrim LR, Pleadings 2006)

97 23. Due to these leaks, many lethal radionuclides, including for example tritium, manganese54, cesium-137, Sr-90, I-131, cobalt

-60, and neptunium 90 were found in the surface water, groundwater, and soils at Pilgrim at levels e 24. The Annual Radiological Environmental Reports (see especially the 1983 report following the June 1982 releases) indicate considerable offsite contamination, some media having >1000 times Cs-137 of what would be expected.

25. Theshowing radiation linked diseases in communities near Pilgrim. (See Pilgrim Watch Motion to Intervene Pilgrim LRA, Contention 5, (5.3.3) and Exhibits F F-4, Adams Library, Accession NO. ML061630125.)

26. Knowing that there was offsite contamination, the only reasonable assumption is that there is contamination onsite also. This requires a site assessment and NEPA analysis, not yet done.

27. 91 28. Pilgrim was shut down from 1986

-1989 du e to a series of failures

29. January 21, 1988, a 5,000 cubic yard pile of dirt containing radioactive cesium

-134, cesium

-137, and cobalt

-60 was found in a parking lot near the reactor. (Radioactivity was detected in dirt pile near Pilgrim, Boston Globe, L. Tye, January 21, 1988).

30. February 2014: NRC identified Pilgrim as one of the nine worst performing nuclear reactors in the U.S.

90 Neptunium releases into Cape Cod Bay reported by Stuart Shalat, who worked for the contractor doing the re

-fueling in the 1980s. Stuart Shalat, Sc.D. Associate Professor Robert Wood Johnson Medical School, Exposure Science Division, Environmental and Occupational Health Sciences Institute 91 Pilgrim Chronology 1967

- 2015, https://jonesriver.org/legal/pilgrim

-chronology

-1967-2015/ Exhibit 4 98 31. In September 2015, two other Entergy reactors. (http://www.nrc.gov/info

-finder/reactors/pilg/special

-oversight.html) Pilgrim remains in the lowest safety ranking in 2019.

32. December 2016, Special Inspection 92: NRC report covering the November 28

- December 8 inspection. Written by Donald Jackson, the lead inspector, this report included a long list of flaws at the plant that were observed during "The plant seems overwhelmed just trying to run the station." 33. The list of Pilgrim failures mentioned in the leaked email were: failure of plant workers to follow established industry procedures; broken equipment that never gets properly fixed; lack of required expertise among plant experts; failure of some staff to understand their roles and responsibilities; a team of employees who appear to be struggling with keeping the nuclear plant running; and NRC inspectors are observing current indications of a safety cultur e problem that a bunch of talking probably won't fix." 34. leaks. 35. All of these facts, and those below, require a site assessment and NEPA analysis.

92http://www.capecodtimes.com/news/20161206/nrc

-email-pilgrim-plant-overwhelmed

99 Contamination resulting from Buried Pipes and Tanks

- concrete, carbon steel, stainless steel, titanium and external coatings and wraps are susceptible to age

-related and environmental degradation.93 36. The pipes and tanks are old and subject to age

-related degradation.

94 Most were put in place 37. Some of the pipes and tanks contain industrial process, radionuclides in wastewater and embedded in the pipe/tank.

38. Degradation of these components can lead to leaks of toxic materials into groundwater and soils. A site analysis and NEPA is required.

39. There has been no adequate program for inspecting buried pipes and tanks.

40. ive, that began in 2009, is voluntary and inadequate.

These voluntary processes have allowed leaks and spills to go unnoticed.

95 Tritium and Other Radionuclides in Groundwater 96 41. The Pilgrim Tritium in Groundwater Program has shown significant radioactive contamination (tritium, cesium

-137, cobalt

-60, manganese

-

93 See for Contention 1, The Aging Management Plan Does Not Adequately Inspect and Monitor for Leaks in All Systems And Components That May Contain Radioactively Contaminated Water. We refer the ASLB to the file, especially Pilgrim Watch Post Hearing Findings of Fact and Conclusion of Law, June 9.2008, Docket 50

-293 94 Pilgrim Watch Post

-Hearing Findings of Fact Conclusions of Law, June 9, 2008,11 95 Ibid 55-59 96 https://www.mass.gov/lists/environmental

-monitoring

-data-for-tritium-in-groundwater

-at-pilgrim-nuclear-power-station; https://jonesriver.org/pilgrim

-contamination/

and see Attachment 3 for a full report.

100 42. Prior to 2007, Pilgrim had no groundwater monitoring program. What had leaked into and contaminated the site is unknown; but what was found when wells were put into place in 2007 strongly suggests perhaps considerable prior leakage

. 43. have confirmed Pilgrim is leaking radionuclides and contaminating the soil and -detect levels to as high as 70,000 piC/L.

97 44. In all but 2 years, there was at least one well abopiC/L. 45. April 2012 an underground line leading to the discharge canal had separated. The leak was accidently discovered when tritiated water was found coming out of an electrical junction box inside the facility.

98 46. Five months later, groundwater tests results showed high tritium levels (4,882

-5,307 pCi/L), in one of the wells and this was suspected to be related to the separated underground line.

99 47. Soil sampling was done, and preliminary results showed tritium, cobalt

-60, and cesium

-137 at levels above normal (1,150 picocuries per kilogram (pCi/kg) of cobalt

-60 and 2,490 pCi/kg of cesium

-137). 100 48. By January 2014 nine months after the leak was originally discovered excessive levels of tritium (69,000

-

M Mass MDPH Pilgrim Nuclear Power Station (PNPS) tritium in groundwater monitoring wells, January 2014 98 Mass MDPH Pilgrim Nuclear Power Station (PNPS) tritium in groundwater monitoring wells, May 2013 99 Mass MDPH Pilgrim Nuclear Power Station (PNPS) tritium in groundwater monitoring wells, Sept 2013 100 Split sample testing at MDPH

101 near a basin that collects radiologically contaminated water and ultimately sends it to Cape Cod Bay. 49. Entergy and Mass DPH continued their investigations, unsure of the sources of leakage, and performed no cleanup.

101 50. of tritium and final soil testing results show levels of tritium, manganese

-54, cesium

-137, and cobalt-60 at various depths near the separated underground line above typical background levels.102 51. In addition to the contaminating spills described above, at least five other historic spill events that have been reported on the Pilgrim site since 1976.

103 52. Tritium moves quickly in the soil; other radionuclides more slowly. Therefore, if the monitoring wells show only tritium it does not prove that other radionuclides, perhaps with longer half

-lives, may be upstream.

53. In 1988 there was a spill of low

-level radioactive waste water. The radioactively contaminated liquid waste was discovered inside a process building and had leaked outside the building. An estimated 2,300 gallons of contaminated water spilled, and 200 gallons leaked outside the building from under a door. About 2,500 square feet of asphalt and 600 cubic feet of sand and gravel were contaminated.

104 54. leaks.

101 Mass DPH. Pilgrim Nuclear Power Station (PNPS): tritium in groundwater monitoring wells. Jan. 2014.

102 Mass DPH. Pilgrim Nuclear Power Station (PNPS): tritium in groundwater monitoring wells. May 2014.

103 Mass DPH. Pilgrim Nuclear Power Station (PNPS): tritium in groundwater monitoring wells. Aug 2014.

104 Mass DPH. 1988. Investigation of Radioactive Spill at Pilgrim on November 16, 1988. Prepared by Radiation Control Program.

102 55. Likely candidates include leaks from the Condenser Bay Area, seismic gaps, a crack in the Torus Floor, materials and soil from subsequent construction left on site, and age-related degradation.

56. Extreme temperatures and storms, salt water and air, corrosive chemicals, and intense radiation most likely have caused components to thin and crack, compromising the structural integrity of the facility and underground/buried pipes.

105 57. During the past 12 years in which the licensee has known about the leaks, nothing has been done to clean up the soil. A site and NEPA is needed.

Stormwater Drains and Electrical Vaults 106 58. When storm drain sampling was done (from 1998

-2007), certain parameters were exceeded on many occasions.

107 59. Initial sampling by EPA from only seven vaults found total suspended solids, cyanide, phenols, phthalates, PCBs, antimony, iron, copper, zinc, lead, nickel, cadmium, hexavalent chromium. Lead, copper, and zinc exceeded marine water quality criteria.

60. Monitoring results from standing water in storm water manholes, junction boxes, and electrical duct banks show radioactive materials at tritium levels as high as 1,500 pCi/L in some storm water manholes and up to 4,500 pCi/L in some electrical duct bank manholes.

105 Pilgrim Watch, Contention 1, The Aging Management Plan Does Not Adequately Inspect and Monitor for Leaks in All Systems and Components That May Contain Radioactively Contaminated Water; Pilgrim Watch Post Hearing Findings of Fact and Conclusion of Law, June 9.2008, Docket 50

-293, NRC Adams, ML 081650345 106 https://jonesriver.org/getfile/ccbw/2012/10/RAD

-REPORT_2017.07.18_VS3.pdf (Attachment 3) 107 nation System (Fact Sheet)

103 61. PNPS will continue to comply with the Offsite Dose Calculation Manual, Radiological Environmental Monitoring Program, and the Groundwater Protection Initiative Program during decommissioning (LTA, 1.4 Additional Considerations). The reports are not ic health.

62. The September 1, 2006 108 that under the existing regulatory requirements the potential exists for unplanned and unmonitored releases of radioactive liquids to migrate offsite into the 63. The LLFT recommended for example: (1) The NRC should revise the radiological effluent and environmental monitoring program requirements and guidance consistent with current industry standards and commercially available radiation detection technology. (2) Guidance for the REMP should be revised to limit the amount of flexibility in its conduct. Guidance is needed on when the program, based on data or environmental conditions, should be expanded.

(6) The NRC should require adequate assurance that spills and leaks will be detected before radionuclides migrate offsite via an unmonitored pathway.

64. The LLTF stated further in its Executive Summary ii that, 65. We cannot rely on a review of monitoring reports. An actual site assessment and NEPA analysis are required.

108 https://www.nrc.gov/docs/ML0626/ML062650312.pdf

104 Declaration John Priest, MassachusettRequest for Hearing Docket No. 50

-293 &72-1044 LT, February 20, 2019

- Excerpts Mr. Priest is the Director of the Radiation Control Department, Massachusetts Department of Public Health. He worked at multiple nuclear power plants, including Pilgrim Nuclear Power Station. During that time, responsible for oversight of radiological plant surveys to support power plant operations, the radiological monitoring of the station staff and members of the public, and emergency planning activities with federal, state and local agencies. 66. Based on my site knowledge, contamination has previously been identified by the utilities in the soil in the vicinity of the condensate water storage tank, the reactor truck lock and radioactive waste building.

67. Further, there were other releases into the environment associated with a former condenser tube refurbishment building east of the radioactive waste truck lock.

68. Ha small hill along the east protected area fence.

69. DPH does not know whether these sites and others were captured as part of decommissioning records required by 10 C.F.R. § 50.75(g), communicated to Holtec and evaluated by Holtec in its decommissioning cost estimate.

70. Based on my knowledge of this site and experience at other nuclear power plants, it is nants will be identified once excavation and demolition begins.

71. Long-lived radionuclides are likely to be found in soils and groundwater far from the small excavation made to repair the leaks that likely allowed reactor condensate to enter into the site soils for many years.

105 72. In addition, these same long

-lived radionuclides are likely to be found in many other structures, systems, and components, which may also have unknowingly leaked over the decades into soils and the groundwater at the Pilgrim property

73. The discovery of additional contamination not accounted for in previous site investigations or previously filed Generic and Site

-Specific Environmental Impact Statements will result in additional costs to Holtec.

74. A complete site characterization (i.e., an assessment of the vertical and horizontal extent of all radiological and non

-radiological contamination at the site) and a Supplemental Environmental Impact Statement that considers the information yielded by such a site

-specific characterization and considers climate change effects is necessary to provide a more accurate basis on which to estimate costs of decommissioning.

75. -lived radionuclides at other nuclear decommissioning sites creates doubt that Holtec will not need to excavate deeper than three feet below grade.

76. The Holtec PSDAR does not detail their plan to address soils outside the structures and components and how they would be characterized and remediated.

77. As written, Holtec does not account for the costs or evaluate the health and safety effects of such a contamination.

78. It is not clear from the Holtec PSDAR that Holtec addressed these issues in the contingency analysis in its cost estimate or, if it did so, whether it properly accounted from them. A detailed analysis of the likelihood of further excavation and associated costs is necessary to accurately estimate those contingencies.

106 79. Radiological Environmental Monitoring

The Holtec PSDAR does not describe the planned radiological environmental monitoring program, including both continuation of analysis (monitoring power plant by

-product radionuclides in milk, vegetation, seafood, etc.). These activities should be conducted through the decommissioning timeframe, including spent fuel pool cleanout, dry fuel storage cask loading, reactor building and associated structure demolition, and finally site restoration.

80. The values in table 3

-1 of the cost estimate included in the PSDAR represent a small fraction of costs needed to continue the current level of environmental monitoring. These considerations should be factored into the planning and funding for the decommissioning of the Pilgrim property.

81. The radiological environmental monitoring program should include a plan to submit all legacy and NRC

-filed site assessments and surveys to Massachusetts, conduct radiological and non

-radiological groundwater contamination sampling, report results to Massachusetts, and provide split samples as requested.

82. Emergency Planning

The PSDAR does not adequately address preparedness in the event of a radiological emergency during decommissioning or the transfer of spent fuel to the spent fuel pool or from the spent fuel pool to dry casks or consider the cost of such an incident.

83. An adequate radiological emergency preparedness plan would include specific resource scenarios.

107 84. Holtec does not adequately address their capabilities to monitor and respond to the following: (a) Leaks of large quantities of radioactive materials in solid or liquid form into the environment; (b) Deficiencies in the structures, systems, and components containing stored radioactive materials; (c) Response plan for emergent scenarios including combustible fires containing either low level radioactive contaminants or spent fuel, and hostile actions that destroy key structures that store radioactive materials; (d) Security measures surrounding the dry fuel pad, which should include substantial physical barriers, especially once it is relocated closer to a nearby road; (e) Details on remote and onsite radiation monitoring of the facility and spent fuel storage; or (f) Adequate routine physical inspection of dry casks and detailed contingency for damaged/degraded dry fuel storage containers.

85. All of these items represent discrete, foreseeable risks that Holtec did not provide sufficient detail that they have considered and accounted for in the PSDAR.

Hazardous Waste

86. representatives that provided testimony on the Motion to Intervene and Request for Hearing, Paul Locke and David Howland

, stated that until a comprehensive site assessment is performed it is not possible to know what is there and make a reasonable cost estimate.

87. Paul Locke (MassDEP) said that: (1) Based on my experience at MassDEP, large industrial facilities, including power plants like Pilgrim, use a variety of oil and hazardous material as part of their operations and facilities. These include asbestos, transformer oils (including PC B-containing oils), and cleaning and/or degreasing solvents (including chlorinated volatile organic compounds, or cVOCs).

108 88. Methods for handling, storing and disposing of oil and hazardous materials have evolved over time, and it is not uncommon for older facilities like Pilgrim to have released oil and hazardous materials to the environment following common past practices.

89. The potential impact of any such release is unknown until a comprehensive site assessment is conducted. 90. Paul Locke testified further that, A comprehensive site assessment includes the identification of releases of oil or hazardous material on a property and delineation of the extent of those release including the investigation of off

-property migration that may have occurred. 91. The Revised Post

-Shutdown Decommissioning Report notes that Holtec will perform si t e characterization activities during the decommissioning process to supplement what is currently known about the nature and extent of radiological and nonradiological contamination at the site. Holtec will then use that information to establish contamination levels throughout the plant and adjust activities accordingly.

92. On its face, the Report is, in my opinion, deficient because it (i) does not include an inventory of oil and hazardous materials that have been used at the facility and which may have been released to the surrounding environment and (ii) does not describe assessment activities that would occur outside the plant that would identify past releases of oil or hazardous materials and any contaminated media that Holtec legally needs to address. 93. Paul Locke said again that , estimate the costs of environmental site assessment, remediation, and restoration and that it is perform that work.

109 94. : (a) Past environmental site assessments conducted for releases of oil and hazardous material at Pilgrim have been limited in nature and are not indicative of potential contamination present. (b) The Revised Post

-Shutdown Decommissioning Activities Report does not specifically address any environmental assessment of the site soil, groundwater, wetlands and surface water resources that would be implemented as part of the decommissioning. (c) The costs of environmental remediation and site restoration depend upon the nature and extent of contamination and, ultimately, the risk posed to potentially affected human and environmental receptors. These costs are best estimated following a comprehensive site assessment. The cost estimates for the work at the Pilgrim plant appear to be based on expectations rather than even a Preliminary 95. David Howland (MassDEP) testified in agreement with Paul Locke that, also does not reference any site

-based empirical data to support the work plan or its cost projections. 96. coatings, caulk and oils throughout the plant once it performs a comprehensive site assessment. As with PCBs, asbestos abatement of mastics, mortar mixes, caulk, flooring, wall board, ceiling tiles, roofing and insulation will be a significant and costly environmental clean

-up obligation. Other materials such as lead and halogenated degreasers like trichloroethylene can require extensive work to remediate and are likely to be found at Pilgrim given its age and the activities conducted at the site 110 Hazardous Waste Dumping

97. Drums of hazardous waste were buried on the Pilgrim site in the 1980s and/or 1990sLTA does not adequately consider them.

98. identified , a site and NEPA assessment must. Climate Change Impacts on The Site. 99. Based on current levels of greenhouse gas prediction, the UN Intergovernmental Panel on Climate Change (IPCC) 2018 Report 109 shows sea levels will rise more rapidly; severe storms will occur more frequently, coinciding with high tides and exceptional wave heights; rising groundwater tables, and floods more severe. The National Geographic (December 16, 2015) identified Pilgrim among the 13 nuclear reactors impacted by sea

-level rise and predicted that, 110 100. As climate change impacts get worse and decommissioning commences in 2019 storm drains and stormwater testing (discussed above) will become even more critical, as these outlets could become further conduits for pollution into Cape Cod Bay. Increased flooding and storm intensity, sea level rise, and rising groundwater tables could increasingly flush contaminates present in groundwater and soil into Cape Cod Bay.

101. Numerous negative impacts resulting from climate change that need analysis

109 https://research.un.org/en/climate

-change/reports 110 http://news.nationalgeographic.com/energy/2015/12/151215

-as-sea-levels-rise-are-coastal-nuclear-plants-ready/

111 Increased flooding and storm surge resulting from climate change is likely to cause corrosion of underground piping, tanks and structures and subsequent leakage. And corrosion and potential leakage of the Greater

-than-Class-C waste and low

-level waste containers located close to Cape Cod Bay.

Radiological and hazardous waste contamination, if not cleaned up quickly, will be washed out into Cape Cod Bay unable to be retrieved.

Severe storms and flooding can result in loss of offsite power and potential damage to the diesel generators located by the bay. The spent fuel pool requires electricity to operate its safety systems.

In Fukushima extreme weather conditions at the site prevented workers to perform necessary mitigating actions. Severe storms and flooding could present conditions at Pilgrim so that workers could not perform their jobs.

Flooding 102. Flooding risk needs analysis because it can result in contaminants washing out into Cape Cod Bay; and contribute to corrosion of buried components and consequent release of hazardous material.

103. In 2012, the Nuclear Regulatory Commission (NRC) requested information from all U.S. nuclear reactors, including PNPS, to support its review of the Fukushima Daiichi nuclear accident (NRC, 2012). Part of this request addressed flood and seismic hazards at reactor sites. 104. In March 2015, Entergy provided the NRC with a Flood Hazard Re

-Evaluation Report prepared by AREVA, Inc. (AREVA, 2015). In September 2015, Jones River Watershed Association (JRWA) commissioned Coastal Risk Consulting, LLC (CRC) to provide an expert analysis of the methodologies and conclusions presented in the AREVA Flood 112 Hazard Re-Evaluation Report.

(https://jonesriver.org/ecology/climate/review

-pilgrims-flooding-re-evaluation/

) 105. Post shutdown, having a detailed and robust flood assessment for PNPS is important. It will provide the basis for good planning and management for the site leading up to and throughout decommissioning, which will help curb flooding risks and ultimately protect public safety, environmental health, and the economic well

-being of the area.

106. The following key points are presented and explained in this report:

Local Intense Precipitation is shown in the AREVA Report to be a primary hazard of concern that could inundate the site by as much as 2.5 feet of rainwater (AREVA p. 29). However, the AREVA analysis underestimates this risk by using outdated precipitation data and not considering future climatic conditions, which are projected to increase precipitation amounts during heavy rainfall events.

While the storm surge analysis was robust, sea level rise over the next 50 years was understated by relying primarily on historic rates of sea level rise. This approach produces only 0.46 feet of sea level rise by 2065. However, the National Oceanographic and Atmospheric Association (NOAA) estimates sea level rise of 3.05 feet by 2065.

Groundwater, subsidence, and erosion are not considered in the analysis, further underestimating the risks to PNPS, particularly when analyzing the combined effects of extreme storm events.

In addition to storm surge, other factors and mechanisms such as high tide and wave setup dramatically compound flooding. The main flaw in the Combined Flooding section combined event scenarios provided in the NRC guidance documen t, NUREG/CR-7046, 113 Appendix H, only one is deemed appropriate for PNPS. This conclusion disregards a wide range of possibilities for analysis with the available

. 107. low budget and it too needs to be updated. Climate change impacts are moving quickly. A site assessment and NEPA analysis are required to model flooding impacts based on the most current data.

Low-Level Radioactive Waste (LLRW) 108. ge, filters, and will include the entire nuclear power reactor when it is eventually dismantled, 111 and is another potential source of contamination onsite and to Cape Cod Bay resulting in significant increased costs.

109. The waste is stored about 30 feet from Cape Cod bay.

110. The shoreline location makes it susceptible to climate change impacts; hence, a site and NEPA analysis is required.

111. The LLRW waste will remain on the Pilgrim site, like the high

-level radioactive waste, until an offsite repository compacts. Radiological Occupational and Public Dose Based on Outdated Documents

- not protective public and worker health.

112. Holtec used the 2002 GEIS to base its decision on radiological impacts to the public and workers. (Holtec PSDAR 5.1.8) The outdated GEIS in turn used risk coefficients per unit dose

111 High-Level Dollars Low

-Level Sense, Arjun Makhijani, A Report of The Institute for Energy and Environmental Research, 1992

114 recommended by the International Commission on Radiological Protection (ICRP) issued in 1991- 28 years ago. 113. and significant information. The National Academies BEIR VII report (2006), 112 the most recent report from the National Academies, found far greater health impacts than the 1991 ICRP.

114. BEIR VII found mortality rates for women from exposure to radiation were 37.5 % higher than a BEIR 1990 report and that the impact of allowable radiation standards on workers was twice that estimated in 1991.

115. Allowable dose during decommissioning must be reduced to reflect BEIR VII, new and significant information supported by the Commonwealth, 116. BEIR VII lifetime risk model predicts that approximately 1 person in 100 would be expected to develop cancer (solid cancer or leukemia) from a dose of 0.1 Sv [10,000 millirem] above backgroundfetime (70 year) exposure to various levels of radiation. Exposure to 25 millirem/year equates to a lifetime cancer risk of 175/100,000; whereas a 10 millirem/year equates to a lifetime cancer risk of 70/100,000

-a significant difference when considering that EPA permits only 1 in 100,000.

117. Holtec does not describe, as it should, how it will assess dose. Will it use the Resident Model, supported by the Commonwealth? Will it use the Basement Inventory Model for structures left below ground, as agreed upon for example at Vermont Yankee?

Both models are most protective of public health and safety.

112 https://www.nap.edu/catalog/11340/health

-risks-from-exposure-to-low-levels-of-ionizing-radiation 115 Likely Adverse Health Impacts Expected in Special Pathway Receptor Populations and In the General Public 118. -income populations would mostly consist of radiological effects. Based on the radiological environmental monitoring program data from PNPS, the SEIS determined that the radiation and radioactivity in the environmental media monitored around the plant have been well within applicable regulatory limits. As a result, the SEIS found that no disproportionately high and adverse human health impacts would be expected in special pathway receptor populations (i.e., minority and or low

-income populations) in the region as a result of subsistence consumption of water, local food, 119. Discussed in the foregoing, the at Nuclear Plants Task Force Final Report, September 1, 2006 113 that under the existing regulatory requirements the potential exists for unplanned and unmonitored releases of radioactive liquids to migrate offsite into the public domain undetec ted ,Summary ii), showing the SEIS does not bound the environmental impacts and that a site assessment and NEPA analysis are required.

Spent Fuel Unlikely to Leave Site by 2062 120. Holtec assumes spent fuel in 2030 and, assuming a maximum rate of transfer described in the DOE Acceptance Priority Ranking &

113 on (tritium) at Nuclear Plants Task Force Final Report, September 1, 2006; https://www.nrc.gov/docs/ML0626/ML062650312.pdf

116 Annual Capacity Report (Reference 10), the spent fuel is projected to be fully removed the Pilgrim site in 206 2, consistent with the current DOE spent fuel management and acceptance strategy (References 9 and 10). 23.78. 121. January 2013 Strategy for The Management and Disposal of Used Nuclear Fuel and High -Level Radioactive Waste). 114 moving toward a sustainable program to deploy an integrated system capable of transporting, storing, an interim or geologic repository might actually exist.

122. DOE quappropriate authorizations from CongressHoltec does not, but should. There has been no enabling legislation in Congress.

123. ISPit, 115 along with anticipated lawsuits along transportation routes

- from cities, states, environmental groups, such as NIRS 116 124. Nuclear waste may be stored indefinitely. A site assessment and NEPA need to analyze this likelihood

. 125. 117 that would be until 3019 for Pilgrim, 57 years longer than Holtec presumed; or indefinitely.

114 https://www.energy.gov/sites/prod/files/Strategy%20for%20the%20Management%20and%20Disposal%20of%20Used%20Nuclear%20Fuel%20and%20High%20Level%20Radioactive%20Waste.pdf 115 http://www.state.nv.us/nucwaste/licensing/Contentions_NV.pdf. 116 Civilian Nuclear Waste Disposal, Congressional Research Service, Sept 6, 2018. https://fas.org/sgp/crs/misc/RL33461.pdf); www.NIRS.org 117 https://www.nrc.gov/waste/spent

-fuel-storage/wcd.html

117 Radiological Accidents 126. Radiological accidents are neither remote, speculative nor worst case scenarios; instead they are reasonably foreseeable.

127. HDI (PSDAR, 5.19) concludes that the impacts of PNPS decommissioning on radiological accidents are small and are bounded by the previously issued outdated GEIS. NRC staff there are no impacts of severe accidents beyond those discussed (SEIS 5.1.2). Showing the SEIS does not bound the environmental impact, discussed below.

128. The GEIS was published in 2002 and is outdated.

118 For example, the BEIR VII Report was not published 129. The GEIS was also flawed. In assessing offsite related accidents, the GEIS only considered: seismic events, aircraft crashes (not small aircraft, that pose the more realistic and serious threat), tornadoes with high winds; and fuel related accidents

-fuel drops and loss of water, ignoring the greatest danger the partial loss water in the spent fuel pool.

130. The GEIS and SEIS both ignore the escalating terrorist threat with US infrastructure, including nuclear reactors as targets. Both predate awareness of an increased threat from cyber

-attacks, 119 drones, and electromagnetic attacks.

120 For example, while reactor safety systems are more or less isolated from an outside cyberattack, a hack knocking out the electrical grid system would shut down power to all reactor safety systems. On

-site emergency power

118 Statement, Dr. Gordon Thompson, December 19, 2013

. 119 December 15, 2017, NRC issues license amendment to Pilgrim to change the implementation date for cyber security upgrades from December 15, 2017 to December 31, 2020 after Pilgrim is closed

. 120 Electromagnetic Defense Task Force (EDTF): 2018 Report. (Source: US Air Force's Air University; issued Nov 28, 2018). From 2022 August 2018, Air University Website, LeMay Papers http://www.defense

-aerospace.com/articles

-view/release/3/198020/report

-highlights

-gaps-in-us-electro_magnetic

-capabilities

,

118 generators are then vulnerable to insider and armed assault seeking to cause a meltdown. Loss of electric grid may disenable security cameras.

131. The GEIS and SEIS incorrectly assert that the environmental impact of accident

-induced or attack-induced pool fires is SMALL. That assertion is incorrect. The environmental impact is LARGE due to the large inventory of radionuclides in the pool.

132. radiological accidents. The casks are vulnerable to attack and releases from cracks caused by age, corrosion, manufacturing defects. Each cask contains a huge amount of radioactivity and each cask contains >1/2 the Cesium

-137 released at Chernobyl. The environmental impact is LARGE. 133. The GEIS and SEIS use an inappropriate arithmetic definition of radiological risk, probability times consequences.

with respect to severe accidents, is a risk assessment

- the product of the probability and the consequences of an accident. This means that a high consequence low

-probability events, like a severe accident, will result in a small impact determination, because the probability is determined to be low so no matter how severe the consequences they will be trivialized.

134. The incomplete and outdated GEIS and SEIS themselves make clear that a site assessment and NEPA analysis are required.

Spent Fuel Pool Accidents Ignored by the GEIS, SEIS and Holtec

- Examples 135. Fuel Handling Accidents

Accidents can and do happen, even with single

-proof cranes. For example at Vermont Yankee (May 2008) 121 . Another mishap or near

-miss failure with a

121 https://www.reformer.com/stories/nrc

-reviews-vy-safety-system-after-crane-failure,65923

119 single-proof crane occurred at Palisades March 18, 2006 attirbutable to worker error 122. Human error, either in operations or manufacturing, is not considered, as it needs to be, in the GEIS, SEIS or by Holtec 136. Canister Drop in Pool:

If a cask is dropped in the pool and the pool floor is breached, there are many safety

-related components located on the floors below the spent fuel pool which could be disabled that could simultaneously initiate an accident and disable accident mitigatio n equipment. If a hole is punched in the pool floor or walls and water is lost simply to the top of the assemblies, a pool fire will likely follow.

137. A canister drop can lead to a crack in the canister

- especially a concern with HBU fuel. Each canister contains over 1/2 the Cesium

-137 released at Chernobyl.

138. Partial drain

-down: The GEIS did not recognize different consequences of both a full drain-down and a partial drain

-down. This is an important omission because total drainage of the pool is not the most severe case of water loss. In a partial drain

-down the presence of residual water would block air convection, e.g., by blocking air flow beneath the racks.

123 Previously, in filings made during a 2002 license

-amendment proceeding, NRC staff assumed that a fire would be inevitable if the water fell to the top of the racks.

139. Pool Fire Ignition: A 10-hour minimum delay time for BWR SNF aged 10 months, as assumed by Holtec, is potentially plausible. But that is not the whole story. For example, an attack scenario could cause partial drain

-down and a local radiation field precluding access; and a fuel handling accident during transfer from pool to dry casks

- such as a cask drop.

140. d enough time to put out a spent fuel fire. An attack scenario could rapidly cause partial drain

-

122 https://www.nirs.org/press/03 2006/ 123 http://www.environmental

-defense-institute.org/publications/Cover.Ltr.Thompson.NRC.SNF.Short.pdf

120 down and result in a local radiation field that precludes access to the fire. There is no basis for water will be sufficient.

141. These must be considered in a new site assessment and NEPA analysis.

ISF SI Accidents the GEIS, SEIS and Holtec Ignore 142. such, only verification (PSDAR, pg.,25)

. Holtec does not consider, as a site assessment and NEPA analysis should, something going wrong

- acts of malice or leak from a crack

. A new site assessment and NEA analysis is required.

Vulnerability Pools and ISFSI to Acts of Malice 143. Reactors make ideal targets for outside or inside attackers for the simple reasons that they contain large amounts of radioactivity that could create severe impacts, and their defense is 144. The threat against nuclear power plants is real. According to the 9/11 Commission report, the Sept. 11, 2001 terrorists initially considered attacking a nuclear power reactor.

124 - 125 prepared under a contract for the Pentagon by the Nuclear Proliferation Prevention Project (NPPP) at the University of Texas at reactors in the United States is protected against a maximum credible terrorist attack, such as

124http://www.resilience.org/stories/2004 25/911-report-reveals-al-qaeda-ringleader

-contemplated

-ny-area-nuclear-power-plant-p 125 http://sites.utexas.edu/nppp/files/2013/08/NPPP

-working-paper-1-2013-Aug-15.pdf 121 the one perpetrated on September 11, 2001, nor against airplane attacks, nor even against readily available weapons such as rocket propelled grenades and 50

-caliber sniper rifles. 145. The design of GE BWR Mark I reactors like Pilgrim makes those reactors highly vulnerable to attack because their spent fuel pools are in the top floor of the reactor, outside primary containment with a light roof structure overhead 146. t fuel when removed from inside the reactor is placed in thin

-walled dry casks. The casks are stacked vertically out in the open making them vulnerable to attack. Each cask contains about 1/2 the Cesium

-137 released during the Chernobyl accident.

147. spent fuel when removed from inside the reactor is placed in thin

-walled dry casks. The casks are stacked vertically out in the open making them vulnerable to attack. Each cask contains about 1/2 the Cesium

-137 released during the Chernobyl accident.

148. Dr. Gordon Thompson also analyzed the impact of a shaped charge as one potential instrument of attack.[30] The analysis shows that the cylindrical wall of the canister is about 1/2 inch (1.3 m) thick, and could be readily penetrated by a vaila b le wea pons. The spent fuel as semblies in s i de the canister are long, narrow tubes made of z irconium alloy, inside of which uranium oxide fuel pellets are stacked.

The walls of the tubes (the fuel cladding) are about 0.023 inch (0.6 m m) thick. Zirconium is a fla m mable metal.

[30] Gordon R. Tho mpson, Environmental Impacts of stor i ng Spent Nuclear Fuel and High- Level Wa s t e from Commerci a l Nucl e ar Reactor s: A Critique of NRC's Waste Confi dence Decision and Environmental Impact Determination (Ca mbridge, Massachusetts:

Institute for Resource and Security Studies, 6 February 2009). Tables also in Declaration of 1 August 2013 by Gordon R.

Tho mpson: Com ments on the US Nucle a r Regulatory C om m i Consequence Study of a Beyond-Design-Basis Earthquake Affecting the Spent Fuel Pool for a US Mark I Boiling Water Reactor 122 149. Table 7-7: Performance of US Army Shaped Charges, M3 and M2A3 Target Material Indicator Type of Shaped Charge M3 M2A3 Reinforced concrete Maxi m u m wall t hickn e ss that can be perforated 60 in 36 in Depth of penetration in thick walls 60 in 30 in Dia meter of hole 5 in at entrance 2 in m i n imum 3.5 in at entrance 2 in m i n imum Depth of hole with second charge placed over first hole 84 in 45 in A r mor plate Perforation At least 20 in 12 in Average dia meter of hole 2.5 in 1.5 in Notes: (a) Data are fro m: A r my, 1967, pp 13

-15 and page 100. (b) The M2A3 charge has a mass of 12 lb, a ma xi m u m di a meter of 7 in, and a total length of 15 in including the standoff ring. (c) The M3 charge has a mass of 30 lb, a m ax i m um dia meter of 9 in, a charge length of 15.5 in, and a standoff pedestal 15 in long.

150. Table 7-8: Types of Atmospheric Release from a Spen t-Fuel-Storage Module at an ISFSI as a Result of a Potential Attack Type of Event Module Behavior Relevant Instruments and Modes of Attack Characteristics of Atmospheric Release Type I: Vaporiz a ti o n Entire module is vaporized Module is within the f ireb all o f a nuclear-weapon explosion Radioacti v e content of module is lo f ted into the at mosphere and a mpli fies fallout Type II: Rupture and Dispersal (Larg e) MPC and overpack are bro k en o pen Fuel is dislodged from MPC a nd broken apart Some ignition of zircaloy fuel cladding may occur, without sustained co mbustion Aerial bombing Artillery, rockets, etc. Effects of blast etc. outside the fireball of a nuclear weapon explosion Solid pieces of various sizes are scattered in vici n ity Gases and s mall particl e s form an aerial plu me that travels downwind Some release of volatile species (esp. cesiu m-137) if incendiary effects occur 123 Type III: Rupture and Dispersal (S mall) MPC and overpack are ru p tured but retain ba s ic shape Fuel is da maged but most rods retain basic sha p e No combustion inside MPC Vehicle bomb I mpact by commercial air craft Perforation by shaped charge Scattering and plu me fo r mation as for Type II event, but involving s maller a mounts of m a t er i al Little r e le ase of volatile s p e c ies Type IV: Rupture and Co m bu stion MPC is ruptured, allowing air ingress and egress Zircaloy fuel cladding is ignited and co mbustion propagates within the MPC Missiles w ith tandem warheads Close-up use of shaped charges and incendiary devices The r m ic lance R emoval of overpack lid Scattering and plu me fo r mation as for Type III event Substantial rel ease of volatile species, exceeding amounts for Type II relea s e 151. Types of Atmospheric Release from a Spen t-Fuel-Storage Module at an ISFSI as a Result of a Potential Attack One scenario for an at mospheric release fr o m a dry cask would involve mechanically creating a co mparatively s mall hole in the canister.

This could be the result, for example, of the air blast produced by a nearby explosion, or by the impact of an aircraft or m issile. If the force was sufficient to puncture the canister, it would also shake the spent fuel asse mblies and da mage their cladding. A hole with an equivalent dia meter of 2.3 m m would release radioactive gases and particles and result in an inhalation dose (CEDE) of 6.3 rem to a person 900 m downwind f r om the release.

Most of that dose would be attributable to release of two-millionths (1.9E

-06) of the MPC's invent ory of radioisotopes in the "fines" category.

Another scenario for an at m ospheric release would involve the creation of one or more holes in a canister, with a size and positi on that allows i ngress and e gress of air. I n 124 addition, this scenario would involve the ignition of incendiary material inside the canister, causing ignition and sustained burning of the zirconium alloy cladding of the spent fuel. Heat produced by burning of the cladding would release volatile radioactive material to the at mosphere. H eat from co mbustion of cladding w ould be a mple to raise the te mpera ture of adjacent fuel pellets to well above the boiling point of cesium.

152. Road, a public thoroughfare. Most of the vegetation was removed to the street. A site and NEPA analysis should analyze its vulnerability.

Casks may corrode and leak especially over a long period of onsite storage 153. Casks may remain onsite indefinitely subjected at Pilgrim, for example, to salt induced canisters crack may crack within 30 years. No current technology exists to inspect, repair, or replace cracked canisters. With limited monitoring, we will only know after the fact that a cask has leaked radiation.

126 154. in Holtec Casks 127. (October 6, 2015) 155. 2014).128 156. understand a cask is guaranteed for manufacturing defects for 25 years and no warranty for corrosion.

126 San Onofre Dry Cask Storage Issues analyses at:

https://sanonofresafety.files.wordpress.com/2011/11/drycaskstorageissues2014 23.pdf 127 (https://www.youtube.com/watch?v=QtFs9u5Z2CA&t=17s) 128 (https://www.youtube.com/watch?v=QtFs9u5Z2CA&t=17s)

125 High Burnup Fuel (HBU) 157. Pilgrim has approximately 35% HBU; yet the NRC is just starting a test to see whether the casks can handle it, with results not in until 2027 158. NRC Meeting Presentation Slides Dry Storage & Transportation of High Burnup, 9/6/18 meeting, slides 14 & 15: NRC said that storage and transportation of HBU is safe, providing no technical bases, for 60 years no guarantee for longer storage when fuel may still be onsite.

Consequences of a spent fuel pool fire or cask rupture. 159. The GEIS, SEIS and Holtec minimize the potential consequences of a spent fuel pool fire rem release limit, 160. Studies of the consequences of a spent fuel pool fire show huge, potential consequences, ignored by Holtec and the documents Holtec relies on.

2016 Princeton Study: A major Spent Fuel Pool fire could contaminate as much as 100,000 square kilometers of land (38,610 square miles) and force the evacuation of millions.

129 2013 NRC Study: A severe spent fuel pool accident would render an area larger than Massachusetts uninhabitable for decades and displace more than 4 million people.130 2006 Massachusetts Attorney General Study: $488 Billion dollars, 24,000 cancers, hundreds of miles uninhabitable 131 129 Frank N. von Hippel, Michael Schoeppner, 24, no.3 (2016): 141

-173 http://scienceandglobalsecurity.org/archive/sgs24vonhippel.pdf; Science , May 24, 2016. (NRC variable at: http://www.sciencemag.org/news/2016/05/spent

-fuel-fire-us-soil-could-dwarf-impact-fukushima 130 Consequence Study of a Beyond Design

-Basis Earthquake Affecting the Spent Fuel Pool for A U.S. Mark I Boiling Water Reactor (October 2013) at 232 (Table 62) and 162 (table 33), Adams Accession NO ML13256A342) 131 tion for Leave to Intervene With respect to Entergy fit 126 161. Dry Cask: A typical cask would contain 1.3 MCi of cesiu m-137, about half the total a mount of Ce s iu m-137 released during the Chernobyl reactor accident of 1986.

Most of the offsite radiation exposu re from the Chernobyl accident was due to Cesiu m-137. Thus, a fire inside an I SFSI module from a terrorist attack or significant rupture of the cask could cause significant radiolog ical har m 132 and huge expense.

LTA and previous environmental impact statements ignore potential costs from fires in structures, systems and components containing radioactive and hazardous material.

162. There is a serious concern about fire protection for the structures, systems, and components containing radioactive and hazardous materials in storage. Capabilities to monitor for and respond to these kinds of toxic emergencies are not addressed by Holtec. Fire in a building would result in increase in mixed waste impacting worker and public health. 163. The documents that Holtec relies upon, are outdated and factually incorrect. They do not bound environmental impact.

Emergency Planning 164. The risk remains, described in foregoing.

The PSDAR does not adequately address preparedness in the event of a radiological emergency during decommissioning or the transfer of spent fuel to the spent fuel pool or from the spent fuel pool to dry casks or consider the cost of such an incident. An adequate radiological emergency preparedness Order Requiring New Design features to Protect Against Spent Fuel Pool Accidents, Docket No. 50

-293, May 26, 2006 includes a Report to The Massachusetts Attorney General On The Potential Consequences Of A Spent Fuel Pool Fire At The Pilgrim Or Vermont Yankee Nuclear Plant, Jan Beyea, PhD., May 25, 2006 (NRC RC Electronic Hearing Docket, Pilgrim 50

-293-LR, 26 pleadings, MAAGO 05/26 (ML061640065) & Beyea (ML061640329) 132 Environmental Impacts of Storing Spent Fuel and High

-Nuclear Waste Confidence Decision and Environmental Impact Determination, Gordon Thompson, February 6, 2009; Comments on the US Nuclear RFuel Pool for a US Mark 1 Boiling Water Reactor, Gordon Thompson, August 1, 2013, pg., 30

127 Petition) 165. Holtec does not adequately address their capabilities to monitor and respond to the following: (a) Leaks of large quantities of radioactive materials in solid or liquid form into the environment; (b) Deficiencies in the structures, systems, and components containing stored radioactive materials; (c) Response plan for emergent scenarios including combustible fires containing either low level radioactive contaminants or spent fuel, and hostile actions that destroy key structures that store radioactive materials; (d) Security measures surrounding the dry fuel pad, which should include substantial physical barriers, especially once it is relocated closer to a nearby road; (e) Details on remote and onsite radiation monitoring of the facility and spent fuel storage; or (f) Adequate routine physical inspection of dry casks and detailed contingency for damaged/degraded dry fuel storage containers

. (John Priest Testimony, 166. A timely evacuation would not be possible, absent funding for training and equipping emergency personnel and institutions

- such as nu rsing homes, hospitals, group homes, schools etc.

167. There is no reasonable assurance of mitigating an accident, especially after a successful terrorist attack resulting in a quick and large radiation field.

168. All of these items represent discrete, foreseeable risks that Holtec did not provide sufficient detail that they have considered and accounted for in the PSDAR.

128 Without a new Site assessment & NEPA analysis, we cannot determine what contamination needs remediation and measures must be taken to mitigate future contamination 169. he Pilgrim site is not 170. he generation and storage of non

-radiological contaminants both as currently existing and created during decommissioning of PPS and the continued operation and decommissioning of the ISFSI. 171. do not adequately consider t he existence of unidentified or inadequately identified, characterized or quantified, radiological and non-radiological contamination.

172. nown and unknown contamination at Pilgrim resulting from previously identified tritium and other leaks, buried hazardous waste, opening with bad fuel and no filtration and blowing its filters in 1982.

173. possibility of s ite-neighborhoods (and potential airborne asbestos and lead contamination, as well as potential impacts from a radiological incident) 174. Holtec has provided no identification, characterization and quantification of species that may become listed as endangered or threatened in the next 100 or more years; 175. Climate change is expected to cause sea level rise and increases in the number and severity of storms and flooding. previous environmental impact statements do not adequately consider this.

176. he u nique environmental and economic impacts related to the length of indefinite spent fuel storage.

129 177. Holtecs previous environmental impact statements do not adequately consider likely adverse health impacts expected in special pathway receptor populations and for that matter in the general public 178. LTA incorrectly assumed and concluded that the environmental impacts associated with planned PNPS site specific decommissioning activities are bounded by the 179. Holtec assum ed radiological occupational and public dose are based on outdated documents, and are inaccurate 180. LTA and previous environmental impact statements do not adequately consider potential radiological incidents at the site, including environmental impacts from the storage of spent nuclear fuel in both the pool and on the ISFSI that also includes impacts resulting from the possibility of terrorist attack.

181. quately consider potential environmental effects of continued storage of spent nuclear fuel, including the possibility of indefinite storage onsite and the possibility of a terrorist attack on stored spent nuclear fuel

. 182. and previous environmental impact statements do not adequately consider the possibility of accidents during transfers of spent nuclear fuel from the spent fuel pool to dry casks and from old dry casks to new dry casks or transfer have not been adequately considered 183. previous environmental impact statements ignore potential costs from fires in structures, systems and components containing radioactive and hazardous material.

130 184. The license transfer agreement raises significant questions with respect to safety hazards and whether the health and safety of the public will be affected.

185. The LTA has environmental effects that may be major and are subject to NRC control. A lack of sufficient funds to carry out decommissioning could result in significant adverse health, safety and environmental impacts, and would increase the need for an updated site assessment and environmental impact statement.

186. The NRC agrees that a shortfall in decommissioning funding would place public health, safety, and the environment at risk.

187. An updated site assessment and environmental impact statement is essential to reduce risks to the public health, safety and the environment.

188. An updated site assessment and environmental impact statement must consider both current and future conditions at Pilgrim, and whether Holtec Pilgrim and HDI are financially capable of dealing with potential adverse health, safety and environmental impact

. 189. An updated site assessment and environmental impact statemen t must also consider the category of operating reactors, Category 4.

190. An updated site assessment and environmental impact statement would show and confirm that Holtec has not adequately considered the potential environmental impacts of decommissioning, or the costs of mitigating the potential impacts that an updated site assessment and environmental impact would show.

191. An updated site assessment and environmental impact statement would show and confirm -

131 Pilgrim and HDI are not sufficient to mitigate the potential health, safety and environmental impacts of decommissioning.

192. An updated site assessment and environmental impact would show and confirm potential consider. 193. An updated site assessment and environmental impact would show and confirm that cost s An updated site analysis or environmental impact statement would show and confirm that decommissioning costs will rise faster than inflation

. 194. An updated LTA and site assessment and environmental impact statement would show and confirm that tassumes that decommissioning costs will not increase faster than inflation.

195. An updated LTA and site assessment and environmental impact statement would show and confirm that t he rates of increase in decommissioning cost are, and will be, higher than general inflation.

196. An updated LTA and site assessment and environmental impact statement would show and confirm that, as the NRC (NRC Questions and Answers on Decommissioning Financial Assurance) has found:

d. The NRC formulas represent the cost to decommission today, not in the future. Id. e. Due to rising costs, the future value of decommissioning will be much larger than the NRC formula calculated today.

132 f. U sing the range of cost escalation rates based on NUREG - 1307, the increase in cost over a 20-year license renewal period would range from 2.5 to 5.6 times estimated cost, not counting costs that are not included in the formula, such as soil contamination.

g. The rates of increase in decommissioning cost are higher than general inflation.

197. An updated LTA and site assessment and environmental impact statement would show and confirm that the NRC findings that increases in decommissioning costs are higher than inflation:

h. total decommissioning cost estimates rose 60%

between 2008 and 2014. Callan, 2015 Report; and rose approximately 11% from the previous year.

i. decommissioning costs increased at an annual rate of about 5.8 percent between 2008 and 2016, and total estimated decommissioning costs for all U.S. reactors has increased from $55.1 billion in 2008 to 88.1 billion in 2017 i.e., by about 60% over the ten

-year period.

An updated site analysis or environmental impact statement would show and confirm that Holtec Pilgrim and HDI do not have sufficient assets.

198. An updated LTA and site assessment and environmental impact statement would show and confirm that the only significant asset of Holtec Pilgrim and HDI is the Pilgrim Decommissioning Trust Fund

.

133 199. An updated site analysis or environmental impact statement would show and confirm that the assets of Holtec Pilgrim and HDI are insufficient to cover costs of dealing with the environmental impacts 200. An updated site analysis or environmental impact statement would show and confirm that the assets of Holtec Pilgrim and HDI are insufficient to pay the decommissioning costs outlined 201. An updated updated site analysis or environmental impact statement would show and confirm that the Pilgrim Decommissioning Trust Fund does not provide an appropriate basis to show that Holtec Pilgrim and HDI are financially qualified to accomplish the decommissioning or avoid placing the place public health, safety, and the environment at risk. For example: No Holtec entity except Holtec Pilgrim and HDI has any financial responsibility. There is no Parent Company Guarantee.

Neither Holtec Pilgrim nor HDI has agreed to put any monies recovered from DOE into the Decommissioning Trust Fund. Because -closure costs that Holtec Pilgrim and HDI have insufficient assets to pay

. 202. An updated site analysis or environmental impact statement would show and confirm that the neither Holtec Pilgrim nor HDI is financially responsible.

203. An updated site analysis or environmental impact statement would show and confirm that 134 An updated site analysis or environmental impact statement would show and confirm that Holtec has not considered potential significant costs 204. An updated site analysis or environmental impact statement would show and confirm that cost estimates ignore the cost of managing Low Level Radioactive Waste or its environmental impact. 205. An updated site analysis or environmental impact statement would show and confirm that consider costs likely to result from climate change impacts on the site, or the environmental impacts of climate change. 206. An updated site analysis or environmental impact statement would show and confirm that both the environmental impacts of radiological accidents and the costs of mitigating radiological accident

s. 207. An updated site analysis or environmental impact statement would show and confirm that consider ignore both potential costs from fires in structures, systems and components containing radioactive and hazardous material, and their related costs

. 208. An updated site analysis or environmental impact statement would show and confirm that adequately increased costs for overhead and project management.

resulting from consider delays in the work schedule. 209. An updated site analysis or environmental impact statement would show and confirm that environmental impacts.

210. An updated site analysis or environmental impact statement would show and confirm that the previously filed environmental impact statements.

135 211. An updated site analysis or environmental impact statement would show and confirm that it is unlikely that DOE will remove all spent fuel from the Pilgrim site by 2063. Holtec has not provided a sufficient or satisfactory basis for its assumption that DOE will do so.

212. An updated site analysis or environmental impact statement would show and confirm that nuclear waste may be stored at Pilgrim indefinitely.

213. An updated site analysis or environmental impact statement would show and confirm that cost estimates do not consider costs of spent fuel management after 2063.

214. An updated site analysis or environmental impact statement would show and confirm that costs of maintaining security at the site after 2063.

215. An updated site analysis or environmental impact statement would show and confirm that Holtec will be required to continue paying ISFSI maintenance and security as long as spent fuel is on site.

216. An updated site analysis or environmental impact statement would show and confirm that the lack of funding for the construction of a Dry Fuel Transfer Station to move spent fuel into new dry casks, or for the purchase of new casks and labor and material costs to transfer spent nuclear fuel into new cas ks. 217. An updated site analysis or environmental impact statement would show and confirm that 218. An updated site analysis or environmental impact statement would show and confirm that . 219. An updated LTA and site analysis or environmental impact statement would show and confirm that cost estimates do not consider pending state

-law requirements that will decrease funds available for radiological decontamination.

136 220. An updated LTA and site analysis or environmental impact statement would show and confirm that cost estimates do not consider DTF funds that would not be available if NRC costs and site remediation.

221. An updated LTA and site analysis or environmental impact statement would show and confirm that pending Massachusetts state

-law requirements would decrease funds available for radiological decontamination.

222. An updated LTA and site analysis or environmental impact statement would show and confirm that exemption requests filed by Entergy may not be transferable to Holtec.

223. An updated site analysis or environmental impact statement would show and confirm that the proposed license transfer and PSDAR will lead to a shortfall in the amount of funding available to fully and safely decommission and radiologically decontaminate Pilgrim and manage its spent nuclear fuel. Any such shortfall could place public health, safety, and the environment at risk.

224. An updated site analysis or environmental impact statement would show and confirm that lack of sufficient decommissioning funds increases the need for such an updated site analysis and environmental impact statement.

225. 226. The proposed license amendment rfinancially qualified

. 227. The proposed license amendment deletes the requirements that 137 fifty million dollars

. 228. The proposed license agreement deletes the requirement that the Decommissioning Trust . The License Transfer Application cannot be approved until:

1. Holtec has conducted a new and comprehensive site assessment

2. Holtec has submit ted the Supplement to Applicant's Environmental Report required by 10 CFR 51.53(d)

3. The updated and accurate environmental report and the environmental review required by NEPA and NRC regulations have been completed, 4. Holtec has revised and updated its application to reflect the actual conditions at Pilgrim, and revised its PSDAR and DCE decommissioning estimates to reflect these conditions and the required environmental reports.

CONCLUSION fer Application should be denied in order to Respectfully submitted on March 4 , 2019 , Mary Lampert Pilgrim Watch, Director 148 Washington Street, Duxbury MA 02332 Tel. 781.934.0389 Email: mary.lampert@comcast.net