Exhibit PWA 00009, Survey Of Costs Arising From Potential ... · For the data presented bel'm,v the...

7
PWA00009 Pilgrim LR Proceeding SO-293-LR,06-848-02-LR Survey of Costs Arising From Potential Radionuclide Scattering Events. Robert Luna. SNL. WM2008 Conference. February 24-28. 2008. Phoenix AZ- Lessons Learned SUI. .. -ey of Costs Arising from Po tl'ntiaI R.'1wonudid. 1' Scattl'ling Enn.15 - 8U? ABSTR.ACT Robert E. Luna, PhD, PE, Consultant Albuquerque, JI.L"M &7111 H. Richard Yoshimura and Mad S. Soo Hoo Sandia . a tionaI Laboratories' Albuquerque, JI.L"M &71 85 The potential effects from scattering radioocti, 'e m,1' t erials in public pl aces include he atth, social , and economic comequence.s" These. are consequences relative to po ential terror activities that include use of radioactive IlU erial dispersal de vi ces (RDDs) . Suc.h an event wid! radionuclides rel eased and deposited on Sl1Ii'aces outside. and inside people's resi de nces and pl aces of wod::, commerce, and recre .:ltion will require decisions on bow to recover from the ev ent. One aspect of those deci;ions " ,ill be die co.'" to clean up the re Jidnal radioactive cont amination to wake the area fuuctioml again v er sus abandollllleJl! andlor razing and rebtlildillg. Developme:oi of cleanup processes have bee Jl Ihe . subj eet of experiment from the beginning of !be nuclear age, but forwalized coot bre.akdowns are r elatively me and mostly applicable to long temJ. releases in uon- public sit es" Pre·ev ent cleanup coot estimation. of cost for cleanup of ra-dioactive IlU erials released to the publi.c. environmem is an issue that has seen s poradic activity over the las t 20 to 30 y ears. This paper will bri. efly several of the more important eff orts to e."1i.mate die costs ofremedia, tion or razing and reoonstmction of radioactively cont aminated <lreas. The cost estimate ,;; for such recoveries v.ill be, compared in terms of 2005 doll<lrs for the sake of consistency. Dependence of cost estimates on population density and needed degree of decont<llllination will be sboml to be q uite in the o verall presenlation of the data. UTIR\TV RE OYIR\1EW Teclmiques used for cases ofreleared raw. ooctive materials in Ihe event of an a. ccident during transport have been a principal source of cost estimating tec hniques . These <Ire contained in the RADIR.A!J'l iIansport risk codes that wer e fu:s t produced in 1974 for me in preparing NUREG-O 170 (NRC, 19 77) That versi. on, RADlRAJl'l I, had several revi si. ons in s ucceeding issues of the code to the present versio n contained in RADTRAN V I. Two non-RADIRAlI'l • sandia a 1001 program 1 _Cf)' 'opBa:ed by Sanlla CIllpOfa:lIll1. a OCUIeed Marun cccnpall)'. 1llr Ur1::ed S1a:E<& €j>aI1mEf1l or E h2'11l" Halronal ucl2ar Se<Utty All 1 ="" undEr COnlra. ct I'1\ge 11

Transcript of Exhibit PWA 00009, Survey Of Costs Arising From Potential ... · For the data presented bel'm,v the...

Page 1: Exhibit PWA 00009, Survey Of Costs Arising From Potential ... · For the data presented bel'm,v the original cleanup co&t ~~teg presented! ill the soume documems we.re extracted:mdl

PWA00009

Pilgrim LR Proceeding

SO-293-LR,06-848-02-LR

Survey of Costs Arising From Potential Radionuclide Scattering Events. Robert Luna.

SNL. WM2008 Conference. February 24-28. 2008. Phoenix AZ- Lessons Learned

SUI. .. -ey of Costs Arising from Potl'ntiaI R.'1wonudid.1' Scattl'ling Enn.15 - 8U?

ABSTR.ACT

Robert E. Luna, PhD, PE, Consultant Albuquerque, JI.L"M &7111

H. Richard Yoshimura and Mad S. Soo Hoo Sandia . ationaI Laboratories'

Albuquerque, JI.L"M &7185

The potential effects from scattering radioocti,'e m,1'terials in public places include heatth, social, and economic comequence.s" These. are sub~tantial consequences relative to po ential terror activities that include use of radioactive IlU erial dispersal devices (RDDs). Suc.h an event wid! radionuclides released and deposited on Sl1Ii'aces outside. and inside people's residences and places of wod::, commerce, and recre.:ltion will require decisions on bow to recover from the event. One aspect of those deci;ions ",ill be die co.'" to clean up the reJidnal radioactive contamination to wake the area fuuctioml again versus abandollllleJl! andlor razing and rebtlildillg.

Developme:oi of cleanup processes have beeJl Ihe. subj eet of experiment from the beginning of !be nuclear age, but forwalized coot bre.akdowns are relatively me and mostly applicable to long temJ. releases in uon-public sites" Pre·event cleanup coot estimation. of cost for cleanup of ra-dioactive IlU erials released to the publi.c. environmem is an issue that has seen sporadic activity over the last 20 to 30 years. This paper will bri.efly re\~ew several of the more important efforts to e."1i.mate die costs ofremedia,tion or razing and reoonstmction of radioactively contaminated <lreas. The cost estimate,;; for such recoveries v.ill be, compared in terms of 2005 doll<lrs for the sake of consistency. Dependence of cost estimates on population density and needed degree of decont<llllination will be sboml to be quite ~trong in the overall presenlation of the data.

UTIR\TVRE OYIR\1EW

Teclmiques used for cases ofreleared raw.ooctive materials in Ihe event of an a.ccident during transport have been a principal source of cost estimating techniques. These <Ire contained in the RADIR.A!J'l iIansport risk ~Jsment codes that were fu:st produced in 1974 for me in preparing NUREG-O 170 (NRC, 1977) That versi.on, RADlRAJl'l I, had several revisi.ons in succeeding issues of the code to the present version contained in RADTRAN VI. Two non-RADIRAlI'l

• sandia a 1001 program 1_Cf)' 'opBa:ed by Sanlla CIllpOfa:lIll1. a OCUIeed Marun cccnpall)'. 1llr ~ Ur1::ed S1a:E<& €j>aI1mEf1l or Eh2'11l" Halronal ucl2ar Se<Utty All 1="" undEr COnlra.ct m:·ACD~!!4AUISIlOJ _

I'1\ge 11

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methodologies are also notable. F'rnt, is an :mruy.;;is completed to estimate the cost of cleaning up pbrrtouiUill scattered as a reso]t of a nuclear weapons accident that was completed in ] 99,6 (Ohanin, 1996). Second is a compt!ller code developed m the UK. (:m appare:ntly onlymable for {)X goven:unent pllllPoses) called CONDO (Charnock, 2003). In adllitioll, some cle.anup co.. ... estimates have been put fon'ioard in a paper (R.eicluw.tb, 200'5) for the Department of Home]and Seaml), that gives cle<Dll1po co!>t e.stimates for high population demit}' areas based on RADTRAN IV cakulatious and ootua l costs for remediatioll of the World Trade Center ()!.'TC) site in New York City.

PROCESS LiSED

The metbodol.ogy for estimating demup C05ts uses two principaJ parameteIS" 1be fust md J:IJOO! basic is the acceptable residualleveJ of contamination detemJined for each mlc1ide released iliat \'iill avoid a girven level of radiological dose to per.sons, who "ill remain living/working m the cont:mJimted are.'!. The acoeptable dose and!, hence, the residual conta:mination level for each nuclide, is likely to be negotiated fo r each re1ease ell'ellt (DHS, - 007). The second parameter is the Decontamimltion Factor, DF, wbich can be rationalized in two ""aYs : • At my point at the s~te of the rndioo.ctive material. rele.'!se, it is the ratio of the local

contanJina'tion level for a released IDlcl!ide to the aroeptible Fesiduru contamination level, (OF.)

• A measure of the Cllpllbilit}' of a given d e:mupo method (like water hosing) to reduce the contamination level for a given surfuoe 1lll\rena:l. 'Illm., .it is the ratio of contlnJinlltion I.e,vel before lreatmen! to contamination level after tre.artmeni, (DF.,J

Specillc cleanup teclmoJ!ogies applied to specillc smfaces and nucli<ks are ch:!rai: .erized by the maximum DFm achievable" IT the DF, is less thllll the effects of all the cleanup proce.;;ses lhat could be iippl!ied sequentially OF, <: :E OF""lhen clerump is succe.;;sful, but if the DE is greateI than the eft'eotli, of all the cleanup processes that are applied sequentially, DF. :> 1: DFm, then other alternative s, like razing and rdruilding 01' inte«liction IlllIh'1 be iipp]ied

The methodologies used in the all of the cited literatme recognized !be limitations of deamlp and employ razing or interdictioll in the event that !he required DF, for a giVell situatioll cmdd no be achieved by mmdard cleanup processes. For m.o!>t oflhe early cart ,estimation techniques, it was allS1!lllled that a DFm of 50lvas general.1)' attainable, but mOl'e Fecent data, nicely Sl1lJlDlaIized in the CONDO report, sugges lbat a DFmgrearterthm ]Oor so (v.ithsome irolatedexceptions) is ulllikdy to be attained This suggests iliat the e.arlier costest:imates would be expecJted to be somewhat low., s:ml)e cleanup costs are genendly lower Iihan rnze and rebuild or interdiction melbodS.

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For the data presented bel'm,v the original cleanup co&t ~~teg presented! ill the soume documems we.re extracted :mdl ecn .. 'eI1ed to 200S ecru using stanrl'rud COBt de:1ilators (Wil!liamsOll!, - GI06}. In generaJI, oosIs \VelTe &tratiified by the initial .level of contamiination all,

represented by DF, valDes, Light contamination corresponded! to, a DF. : meWlIIlll, So::: DF. < ]0; and hea\'}', DF. >10. Costs in theRADTP~ reports ''i'eIe fl.lrlher matified by a specmc-.ation relating to population density (rund, submban, omduroan) colFesponiting to mean popu]a1ion iJenloiJties: of aoout 10 750 and 3800 persons per knl respec,tively. In the Cha:nirn repok mban populaticm demity values \.YeJ7e, takien to be about 1350 pe;rsous/ J:m2 (oorresponiling to a. mean populaticm density in aFeas identiified as mOOnized! by the cemus bureau). Reichmuth. &tated that populaJtion dens.' ties (PO iin pernonsJkm~' 'ivere as follows:

Rm:aI 0 < PD < 50 Urilan 50 < PD < 3HOl) High Density Uwan 3000 0::: PD < 10,000 Hyper Density LiIban 10 000 0::: PD

As is ob\.-ioos fiom the ahO\'e 1hece is no strict translation of\"'ords descn1liingpoPl.llartion densiity terminology .in quantitati.\'e terul5 but 1!heFe is eno1lJgh specificity to. compare various ecsts e&t:imates all a fiurotiOil ofpopullation demit}'.

The SNL study (CbruJin, 1996) pro,,-ided a faITly detailed methodology in 'ivbich toestiimare oosts. For an urban area, the o,,-eran results, that came om of Iihe effort are mo\.ul in Table 1

'Fable 1 Urban Area (] 344 persomi'km") ReJDEJdiation Costs for Year 200S in $M.'km2 from Appendix G «(,'brurin, 199'6).

Ol,sts per sq. !km Aua W~fedl Costs

Ar'eli U!!lIIge' ligtI1 MOO!!'ae HeuJ .ma Light MOO!!'ae HenJ l)'P" (!<l)F.~l (5< [)F.<l O) (DF,>]O) Framna ('2<'m'.~ (5<DF,<l O) (DF.~[O)

ResidmtW' $72 .'1 $]63.9 $301.2 0.3 16 $22.9 IS1.8 $952

CQ~ $195.3 1295.5, $85 1.2 0.173 $33.8 $S1.1 $14:-13

Indu5t:!:iaI $61-'1.0 $7642 $1,245 .9 O.OM S43.1 S45.1 $1'9'.7

StIe£ils $15.9 $18.5 $247.7 0.17:5 $2.8 $1.2 $433

VammL:mi $81.1 $85.7 $95.2 0.2:72 ~"J'J 1 $233 $':25.9

OIIwall C.ost per sq. bn $1"14.,6 $174.:5 $391.'1

" ioo"nl&5 single and r::mL1iplffunail}' ,~ and i!piI!III:.eIW l!an;e;

'Fable I d'elmn&trates the methodology used aswel!l as resl!llJIs. Costs WeJ7e ,estiima ed for generic. ]:md use areas and 1be:nweighted bylbe fraction. OEthe overaIl are.ll .in. thlIt ]:md use class. Short of repeating the comidernhle ,elifort in developing the report reBuIls, \'iibat options exist for e&timarting the cleanup ecs! for higherpopulmion density are.as,'! If data :is available for kland me area irnctions in the higherpopulaticm area then 1111 estimate can be lDlIiIe b)T Plugging iin those vaJnes in the ) 111 rohmm of Table 1 In ad'dition, an adjlustmem for population density can

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be made by n()ting that higber poopubilion density irmpl!ies that there are more ch.,'elling uniils pel" knr and that 1he cools slIm.''ll m Table I areb<l.'Jled onindividruli dwelling;;_ lu a remh, multiplymg fue res:icJenjjal cost;;. by a ratio of population dem~ty sh()uld atfjust for IJigber popu]atiollS in the SlIlDe area_ In addition, inre commerc:ial ~ce is likely to expand! \,.ith popu]ation dem~ty, the connnercial \ralues would also be adjw;ted in a sim:ila:r manneT. These are appro:mnal:em.ethods and lIsefu] only for order ofmagnitllldle e,rtimates. The resul of mch adjlllrimenls is shm>;u in Tab e IL

Table II. Estimated R!emediation Costs fu:r i e"" York City Reflecting land Use Distnlm"tion and P'opulation Demity_

Al'e:II 'W~l!d

l:i:!'II:t MiId!r:lfe Hefi}" (WIi.~ (5<: DF,<lO) (I!IF, ~UI) FramDII.'

Res:idellful 0.287 $20.3 1 $45.99 $8'1.5] 6 .82" $B 8..55 $3B.64 $516,.3S

C~ 0.164 $32.00' $43.55 $139'.84 6.82" $218..M $331.1.2 $953.80

$4551 $47.55 $&1.12 LOO .$45.51 $47..505 $84. 12 U9"7 $4_62 $61.88 1.00 Sl.97 $'1.62 $61..88

$19'.29' $20.38 $22.64 Va.rnJl ~ 0.238 1.00 $1929' $2038 $22.64 1.00

o.."eruI ,(',;)st (SM'kut $121.2 $167.1 $}93·.0 $426 $717 S 1,@9

• dm1.ledfrom.New Yod;: City dam ( h.'1!p:lIu.1.\w..nyc.ga>.1,'htIllllfl¥ P{pdfilaJJdJEefxlsiladuse t?bles .!!df) • rntio Qfl'{~,yod; Cilypopul;;.lioIl dm;ity to ttmt m Table]" (916&1l4!4 = 6.82)

The proces.s med to produce Table II c.anbe ·w;edJ to derive remediation oos! ,estimartes for other popu]ation dem~ty areas as sho'''ll by I:b.e lrioogle points in Figure t Figure 1 abo contains. remediMion cost data n-0Dl I:b.e source docmnent;;. mscussed! above.

The Legend .in Figure 1 is quite ]Mge, but .is ¥ 'or l1e} ed for oom.e addition clarity_ Red lill.e:s. md symbols are for (DF, > ]0) ornnge for (S <: DF. <: to}, anrlI green for (1 <: DF. <: S). Pwple symbols are for estimates. that are 1.UlSpeCmc abol!lt the DF. tlrey app]y to, bmlbe val'oe.s c01ll1d be as lanre 0lS 50_

Figur"e 1 sbo",;·~ . a fair imlOlmt oh.rn.abi1!ity in 1he co."1s estimated by the various medKKlS and! somces a)\'eI"ed in tl:W;. ovenriew. The Ihree straliight ]IDes. penciled in on lhe po ilFe intended! to sugges howlbe cools might \'aIJ' wiilipopulatiOIl density and degree of ContaminatiOD_ The lIines are a reasonable representation ofmuch of1he IDforn:JaJtion, but some data. points. de,,;;a e SlIDstantially :mdwill be mrousseci m e. The two red mscpoiints that areweH above the ourves aTe fromdte paper by Reiclmnlfu and are based on ,estima:tes of cos1 derived to clean -up and restore (n-ot retmiI.d) the 16 ac,re \VTC :site ill -a \' YOlk C~ty after 9f] 1. The cost 0 replace I:b.e facilities is es<tiima ed to be an order of magnirudle larger (not shown on the prot).

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$100,00;)

SlD,DOl

$1, 00

SlOO

+U •• LlI. H , ~ h ... ... ... ~~_ • ...., . ....... n·

.U~ML .. )oJly.tH~1 I

. ".dlillr ............. d .... L· .. iIi ,

. ...... hl.,OJ ... ·"".i1I

.AIr.IIL~I~ ld'lII uI •

• h!'ll.!.tta'~

. r~"'" lIk4.Jnhtr:t.r .....

100 1,000

Popu I<ltioll Density tperSOI'llS/sq. krill

Figure 1: Remediation Cost Estimate;:. Compared..

lO,OOO 100,000

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Since the esliwated 005! "\'35 based. Qn the ilfea of the WTC :site, oot the aotual expendimre covered aotiQns ma1ie O,ref the sumxmdmg areas and included. ations oomel ... ·bat beyoudwhat \"\'ould!be expected in response tOo aD. RDD f :1,'eIlt, the acllllal cm:t/krn? cOll.ddbe mterestimated by 5001., to 60%.

The pmpl'e SCJ1!IaFes belmv fue ctll'll'e represem the estima~es that "velie done using RAD'IRAN I in the mid ]970's \,oiJtb. an unsophisticated methodology_ Moreover the ,estimates me the aIdes and most sUb-ect tol.mCeltrinty associated with selecting the best dell.ator IaJtistic for updating CO&ts.

The R:AIJIR.."-L1f 6 estimates (pmple diamonds) also Me belQW the trend! .1in.es but IlOt as prooOlmced an efi'ec as , .. idt RADlI1R.,M-l" 6 (Osborn, 200"i)_ No e that the RADTRAN 6 values (square.;;:, willi center crosses) fit nnroh more closely'iViili the other ,estirmilltes and thetre,nd l:IDes" The trend! lines favor tbe cost values generateil by the Sand!i<a study (Chanin, ] 996) becomre of the detail in'lo'O]ved in llb.e initial e&timar es and the ability to project the co .. tslo ofuer populatiOIl densilie.s, and hod! use area m .otiQllS.

'CO~CLUSIO -

The l:i1reJ!ih.ood of a "Dirty Bomb atta-d: in ilie U or elsewhere is unknowlli. Moru somces suggest te, g. Karam, 20(5) that the radiOlogical consequences of :suCh an attack are milikeFy tOo be life thre.a aIing andlhatlhe gre.artesf llIDrtal d~mger is to peI"S"1lUS expo.sed tOo hlia&t from the device (assuming 1bat is its mode of operation). Howe\;eI the ,expernIihu-es, needed to recm .. 'ef

from a. sucre-,ssful attack using an ROD type de nce as depioted! in F'igtlre; 1, are J!ikcly to be

signiIicant from the standpoint of Je.i01!ll"ces available to loca] Qr state governm.ents_ E\ eJl ll. device that contamirnates an area of a fe,,¥ hlUldred. acre,;; (a SCJ1!Iare kilometer) to a Ib'e1 that requires !lIDd!estTeJD.eiliation is likcly to produce corus nmgirng fi-om ':,lOM to ·:3OOM or more depending Qn - em.i.ty of commercializa -OD., population density, and d.etai.Ils ofllm:l! use in the are.a_ As a result, it :is i.nljxIrtant to put appropriate emphru:is Olli theefforunow beinglakeJl by the Department of Energy, Nuclear R.egulawry C<J:mm:ission., andl!b.e Department of HomeL1!Il.d. Secw:iJty tOo prO\;ri.de aCCO\!IIltmcy for radioo.cfu.'e ma~erials used iin the public and. pri.""te seeton and! to detect as filII}' as, possible, traffic in poreruial dlrtybomb materi'lils wirlhin and! on the borders of the SA.

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{Clmnin, 1996): Chanin, 1).1.00 I. and Mw:fiin Walte£ R ""Site, Restornlion: Estimation of Attributilile Com From PImonimn .llispersaJi Acoidents", Sandia ationru Laboratories, R!eport SAl'll) g6-0957, May 1996_ (Clml'llock, 1003): Ohamook, 'I.e al, "CONDO: Sofu,,'me for Esfunal:ing the Consequenres of' Deconlruninarion Options'\ Nationa] Radiological ProtecnonBoru:d, Repon NRPB-\V43, !May

(03).

,(DRS,.! O : DepMtment of Ho:mel.md Security, PFeplU'edne:ss lliTecwllIre; "Protective Ac,tion Guides fOT Railiologi.ca] Dispersal De\ice (ROD) and Improvised! Nuclear I)e"i e (IND)', Federa] Register, VoL 71, 0 '_ 1 Jamary 3, 2006. pH4-196. (Kanipe,1992):_ Kanipe F' and aihauser, K So, "RADTRAN 4: Volume 41Jorognmnner:s Mannail , Sandia National Laboratories, Repon SAND89-1370 Jllly] 992_ '(Karam, 100::-): KacmJ, AndIew "Radiologrc.'ll TerrariBilll," Human and Eoologica] Risk &~s.slllfm, Vol. 11 1005 pp. 501-523. ,_ iJeubllU5el', 1991): -euhauser, K. S. andKanipe E RA.DTRAN 4: Voll!lme 3 UsaGWde Sandia ationaJ Laoornl:ori.es Report SANDS9-1370, Jimnmy 1992_ 'INeubllU5el·. 1993): Neuhauser., K. S_ and Kanipe F. ''R.A.DTRAN 4: Voll/lllle 2 Techni.cal MannaiI , Sandia._ atiorull Laooratories, RepoJt. SAND89-1370, Au:mst 1993_ (OsOOl'll!, 200 : Pri"ate CoJllllll!.lllicartion 'lith. DDuglias O:sbom, SNL reblive to· estio:Jared c erump cost ,estimared by RADTRAN VI, October 2007. (feuistfR, 100 : Pemsten, 1. P_ and Weiner R "An &.onomic Model of a Ra.dioac,ti"e Materi.als. Transportation Aocident for the RIillTRAN Risk J\s~meut Code ' Proceedings of' Waste }-llanagement 1005, February 27 -March 3 1005 Tucson, .A2 (SANDlooS-3801C). (NRC, 19 : "Final En"ironm.emaJ. Statement on the Tranq>OrtatioJ:] of Radiooctii'l;'e Mlteriah by.Ali and Olli.er !Mode:S" NLlREG-0l.7O, US Nucle.ar Regul!awJ)' Collllllission, W~Dil:on,

DC Deoemlba 1977. (Rfio]]ml]th,~OO:5) : Reichmuth, B.., et aI, ''Economic Consequences of a R.ADJlNUC Attack: Clemnw, Standards S:ignifiamtly Aff'ec C<Jsf', .Proceeding:;: of WoOOng Togelhe£ R&D Partnerships in Hom.e]aIOd Security Boston, Ml\., April 1003 (Pacmc No:rth\\'est National Laboratory, PiNNL-SA-45256). (·\\'illiaIMOD, . OO6,): Wi.lIliamscm, Sannrel H 'Fi¥e Ways to Compute the Rclam.'e Value ofa

.s. Dollar Amount, 1 90 - 2005," M.eamringWorthCom, 2006 (Wql':llwWl. ... ·.meamriingworfu.comlcalcnliatorsitlSOOrtyJareke:ml1_pbl" .