ML20148M996

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Slide Presentation Re Compliance Determination Procedures for 40CFR190 Re Environ Radiation Protection Stds for U Recovery Facilities,Effective 801201.Related Documentation Encl
ML20148M996
Person / Time
Issue date: 11/30/1980
From:
NRC OFFICE OF NUCLEAR MATERIAL SAFETY & SAFEGUARDS (NMSS)
To:
Shared Package
ML20148M994 List:
References
FRN-45FR26072, RULE-PR-20 40CFR190, NUDOCS 8012290036
Download: ML20148M996 (30)
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Text

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DECEMBER 1, 1980 o 40 CFR 190 TAKES EFFECT o ORDERS ISSUED TO ALL NRC LICENSEES o NRC ISSUES REPORT o PROSPECTIVE ASSESSMENT OF EACH FACILITY o PREVIOUS COMMITMENTS CONTINUE O INTERIM PERFORMANCE OBJECTIVES o ENVIRONMENTAL MONITORING PROGRAMS o REVISE 10 CFR 20 TO INCORPORATE 40 CFR 190 1

i 8012290 1

0

l PilASED IMPLEMENTATION l

DEC. 1, '80 PilASE 1 VARIABLE PHASE 2 TIME NRC A PROSPECTWE INITIAL ONGOING ASSESSMENTS ASSESSMENTS - ASSESSMENTS 0 IDENTIFY LICENSES O COMPLETE POTENTIAL 0 INDICATOR POTENTIAL AMENDED BY INSTALLATION LICENSE CONCENTRATIONS PROBLEM ORDER - 0F EMP'S AMENDMENT WITil SPECIFIED AREAS 40 CFR 190 0 SORT Our OPERATING INSTITUTE TAKES EFFECT ONDITIONS EXTRANEOUS SIMPLIFIED 0 ESTABLISil DEN N IED AS SOURCE ASSESSMENT MNITORING TION LEVELS CONTRIBUTIONS PROCEDURE REQUIREMENTS 10 CFR 20 0 METEORLOGICA'L DATA INCORPORATES SET COMPLETED 10 CFR 190 0 Sil0RT TERM STUDIES AND IESTS 0 IDENTIFY NEEDED REMEDIAL CONTROL MEASURES, IF ANY-t

1 l

l QRDERS AMENDING LICENSES -

0 ENVIRONMENTAL MONITORING PROGRAM 0 ESTABLISH PROGRAM - WHERE NO APPROVED PROGRAM EXISTS

._ 0 MODIFY EXISTING PROGRAMi - MINOR CHANGES IN FEw CASES 0 SPECIFY SCHEDULE FOR INSTALLATION - WHERE NOT NOW INSTALLED .__ _,

O INVOKE QUALITY ASSURANCE REQUIREMENTS - R.G. 4.15 0 PERIODIC DOSE ASSESSMENTS 0 COMMIT OPERATOR TO PERIODIC ASSESSMENT PROCEDURE O REPORTING 4

0 SPECIAL INFORMATION NEEDS 0 SHORT IERM STUDIES 0 METER 0 LOGY - Futt YEAR'S DATA WHERE NOT CURRENTLY AVAILABLE O IDENTIFY AND CHARACTERIZE ALL SIGNIFICANT NEARBY

, EXTRANE0uS SOURCES 0 SUPPLEMENT EXISTING DUST CONTROL REQUIREMENTS

~ ~ ~ ~ ~ ~

0 WRITTEN OPERATING PROCEDURES 0 WEEKLY INSPECTIONS

NUCIFAR REGULATORY COMMISSION REPORT O PROSPECTIVE ASSESSMENT EACH MILL O SUPPORTING BASIS FOR ORDERS O CONCLUSIONS  :

O EXISTING REQUIREMENTS FOR EMISSION CONTROL..

SHOULD ASSURE 40 CFR 190 IS MET AT EACH FACILITY l 0 NO SPECIFIC ADDITIONAL CONTROL MEASURES APPEAR REQUIRED 0 ADDITIONAL INFORMATION NEEDED AT SOME MILLS TO MAKE FIRM CONCLUSION O CURRENT DATA At:0MALOU6 OR INCOMPLETE O SCREEN OUT EXTRANEOUS SOURCES r 0 UNCERTAINTY AscuT EFFECTIVENESS OF CONTROLS l

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40 CFR 190 COVERAGE O 25 MILLIREMS TO WHOLE BODY AND ANY OTHER URGANS 0 REASONABLE ASSURANCE O INCLUDES -

0 ROUTINE RELEASES FROM NORMAL OPERATIONS 0 ANNUAL AVERAGE O CUMULATIVE MILL SOURCES 0 EXCLUDES -

O RADON AND DAUGHTERS 0 NATURAL BACKGROUND KADIATION O MINING OPERATIONS AND ASSOCIATED ACTIv! TIES 0 IRANSPORTATION O DECOMMISSIONING AND DECONTAMINATION O RELEASES PRIOR TO DEC. 1, 1980 AND ASSOCIATED GROUND CONTAMINATION l

e CONTROL OF SOURCES 0 INTERIM TAILINGS PERFORMANCE OBJECTIVES 0 CONTROL BLOWING OF IAILINGS 0 ALARA - 10 CFR 20 0 NEPA - 10 CFR 51 0 OCT. 3 - FINAL MILL REGULATIONS 0 CONTROL DUSTING FROM IAILINGS AND DIFFUSE SOURCES 0 FLEXIBILITY IN METHODS 0 WRITTEN OPERATING PROCEDURES .

O WEEKLY INSPECTIONS t

0 EM_Jfel0E CONTROL PRIMARY REQUIREMENT i

0 INSTITUTIONAL CONTROL SECONDARY 0 STRICT CONTROL OF DUSTING flEcESSARY, AS GEIS ILLUSTRATES b

a

l l

l COMPLIANCE ASSESSMENTS , _.

O PHASED IMPLEMENTATION .

0 OBJECTIVES 0 ESTABLISH SIMPLE AND STANDARDIZED ASSESSMENT PROCEDURES AND REPORTING REQUIREMENTS 0 ASSURE CONSISTENCY 0 BETWEEN MILLS 0 OVER TIME O ELIMINATE UNCERTAINTY 0 PUBLIC 0 MILL OPERATORS 0 REGULATORY AGENCIES 0 OTHER INTERESTED AGENCIES (E.G., EPA, STATE HEALTH SERVICE) 0 FACILITATE PROMPT IDENTIFICATION OF PROBLEMS WHERE THEY EXIST 0 MINIMIZE COSTS AND STAFF IIME FOR COMPLIANCE ASSESSMENTS l

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4

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l 40 CFR 190 COMPLIANCE DETERMINATION O BASED PRIMARILY ON ACTUAL MONITORING DATA -

i O EMPHASIS ON AIR SAMPLING AT NEAREST RESIDENCE

, o PREDICTIVE RAD ASSESSMENT MODELS WILL ROI BE BASIS 0 UNCERTAINTY IN SOURCE IERM AND ATMOSPHERIC IRANSPORT MODELS 0 NECESSARY AND VALUABLE TOOLS IN LICENSING OF PROSPECTIVE OPERATIONS 0 IDENTIFY NEEDED CONTROL MEASURES OR POTENTIAL PROBLEM AREAS 0 GUIDE DEVELOPMENT OF ENVIRONMENTAL, MONITORING REQUIREMENTS 0 CODES MAY AID IN ACTUAL MONITORING DATA INTERPRETATION 1

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COMPLIANCE DETERMINATION PROCEDURE O 2 ESTABLISH ENVIRONMENTAL MONITORING PROGRAM

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0 COLLECT DATA .

O COMPUTE DOSES AT NEAREST RESIDENCE 0 SUBTRACT DOSE CONTRIBUTION FROM EXTRANEOUS SOURCES AND BACKGROUND 0 COMPARE DOSE WITH STANDARD - DETERMINE COMPLIANCE .

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O IDENTIFY ADDITIONAL CONTROLS; IF ANY NEEDED 0 IDENTIFY FURTHER MONITORING, IF APPROPRIATE -

0 REPORT TO NRC i

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i FIGURE 1 40 CFR 190

! COMPLIANCE DETERMINATION PROCEDURE ,

(BASED ON ACTUAL ENVIRONMENTAL MONITORING DATA) .

EMP REPORTS NRC ESTABLISH

/ -

40 CFR 190 COMPLIANCE

  • 40 CFR 190 COMPLIANGE -

EMP AS ESSMEU DETERMINATION l h PLAN DEVELOPED DATA NRC PROJECT BY APPLICANT / GATHERED BY MANAGER LICENSEE  : LICENSEE REVIEW APPROVAL! DOSES COMPLIANCE LICENSEE VARIANCES AND CALCULATED DETERMINED E

CORRECTIVE REVIEWED / +

ACTION LICENSE l l lDENTIFIED/ AMENDMENT

{ y LICENSE AMENDMENT ,

l EMP REPORT l OPERATIONAL SUBMITTED J i r lEtE DOCUMENTATION INSPECTION IN ANNUAL ,

- I REPORT i e S

ONGOING COMPLIANCE DETERMINATION - PHASE 2

~ ~ ~ -

o SIMPLE, STANDARDIZED PROCEDURE o POINT OF RECEPT 0R CONCENTRATION OR DOSE ACTION LEVELS ESTABLISHED

~ ~ ~ ~ ' ' ~ ~

o BASED ON PHASE 1 MONITORING AND ANALYSIS __ _._ _. _.

o MAY BE HIGHER IHAN 25 MILLIREM o COMBINED WITH PRESCRIBED CONTROL MEASURES o No SIGNIFICANT CHANGES IN LOCAL LAND USE

. OR NEARBY ACTIv! TIES

~~ ' ' '

o SIMPLIFIED PROGRAM IMPLEMENTED THROUGH LICENSE AMENDMENTS er

  • $*$d YO e - > gge, mm weg ,,w. ==== . us

1 MONITORING AND ASSESSMENTS - PHASE 1

~

0 COMPLETE INSTALLATION OF EMP'S 0 FINE TUNING O OUALITY ASSURANCE R.G. 4.15 O SORT GUT EXTRANEOUS SOURCE CONTRIBUTION O IDENTIFY MINING AREAS, ORE STORAGE PADS, IRANSPORTATION R0uTES, ETC.

O ESTABLISH SUPPLEMENTAL AIR PARTICULATE SAMPLING STATION O SHORT IERM SAMPLING 0 LIMITED ANALYSIS 0 CORRELATION OF METER 0 LOGICAL DATA 0 RE-EVALUATION OF DOSE ESTIMATES - ESTABLISH SIMPLIFIED CONCENTRATION OR DOSE ACTION LEVELS l

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REPORTING REQUIREMENTS PHASE 1 PHASE 2 l

ROUTINE REPORTING OUARTERLY SEMI ANNUALLY (60 DAYS AFTER (60 DAYS AFTER QUARTER END) 1 JULY AND 1 JAN) o IN REG Gu!DE 10 CFR 40.65 4.14 FORMAT o MEETING WMUR COMPLIANCE DETERMINATION PROCEDURE NON-COMPLIANCE REPORTING NONE 30 DAYS AFTER DETERMINATION o PURSUANT TO 10 CFR 20

l REGULATORY GUIDANCE ,

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o ENVIRONMENTAL MONITORING PROGRAM - R.G. 4.14 o QUALITY ASSURANCE - R.G. 4.15 o DOSE CALCULATIONS - R.G. 802-4 o MILDOS CODE USER'S MANUAL t

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-MILD 05 COMPUTER CODE GENERATED 50-YEAR DOSE I COMMITMENTS (in mrem) FROM TYPICAL MILL ,

i I- WHOLE BODY BONE LUNG

- - _ . . . . . . . . 0.1.tt.ct lxpSsure Pathway ~ ~ ' - ' - ' ~ '"

o Inhalation 0.178 5.21 7.78 o External Gamma. 0.005 0.005 0.005 i

3 Ingestion Exposure Pathway

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o Vegetable Intake (1) 0.713 8.60 0.71 3 o Meat Intake (2) 1.40 17.50 . 1. 4 0 TOTAL 2.30 31.3 . 9.90 -

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4 (1) Vegetables are assumed t'o se grown in local gardens and the nearest resident' is assumed to consume only such

vegetables.

(2) Meat ingestion was assumed to be from locally grazed livestock.

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1 ACTUAL ENVIRONMENTAL MONITORING .-

PROGRAM OATA FOR A TYPICAL MILL LOCATION ANNUAL AVERAGE 50-YEAR DOSE COMMITMENT CONCENTRATION (in mrem)

. . . . . ...'. pCi/m3 Whole Body Bone Lung Off-Site U-nat.'= 0.0142 0.0656 1.13 2.40 Nearest Ra-226 = 0.0080 0.247 2.47 52.9 Residence - S Th-230 = 0.0085 1.41 50.6 27.4 Pb-210 = 0.0536 0.234 7.24 41.4 .

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TOTAL = 1.96 61.4 124 Off-Site Nearest .

Residence - N 0 -n a t . = 0.0084 0.0388 0.667 1.42 Ra-226 = 0.0052 0.1 61 1 .61 34.4 Th-230 = 0.0031 0.515 18.4 9.98 Pb-210 = 0.0460 0.201 6.21 35.5 TOTAL = 0.915 26.9 81 .3 0

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1 DOSE CONVERSION FACTORS FOR THE INHALATION OF AIRBORNE PARTICULATES (M1111 Rem per pCi/m3)*

Radionuclide Body, Bone Lung i

U-238 4.32 79.2 158 U-234 4.92 79.5 180 U-natural 4.62 79.4 ,169 Th-230' 166 5950 3220 Ra-226 30.9 309 6110 P b- 210 4.36 135 772 Po-210 0.47 1.92 420 7, l 4

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  • 1The 50 gear dose commitment for each year of exposure to pCi/m of each radionuclide for an adult breathing rate of 20 m3/ day. Particle size of 1.55 pm AMAD (i.e., mean diameter of 1 pm and density of 2.4 g/cm3) being representative of uranium ore. The Quality Factor for alpha radiations is 10.

The total dose per organ is the summation of doses due to each radionuclide. (Regulatory Guide RH#802-4).

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EXAMPLE EMP MODIFICATIONS

_ _ . _ . . . . . . . . . . . - '" '~ ~ " ~ ~ - -" ~~

o INVENTORY OF SOURCES .

o IDENTIFY MINING AREAS, ORE S'ToRAGE PADS, IRANSPoRTATIoN ROUTES, ETC.

o ESTABLISH SUPPLEMENTAL AIR PARTICULATE SAMPLING STATION o SHoRT IERM SAMPLING o LIMITED ANALYSIS -

o CoRRELATIoNOFMETEORLoGICLDkTA o REVIEW DATA o RE-EVALUATION OF DOSE ESTIMATES 4

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PRELIMINARY DATA COMPOSITE 50-YEAR DOSE COMMITMENTS TO THE INDIVIOUAL RECEIVING MAXIMUM EXPOSURE, FOR ONE YEAR, FOR EACH MILLING FACILITY

', Composite Dose Commitments. imrem '

Date and Whole Method of Facility Body Bone Lung Dose Prediction Reference _

1 2.4 74.8 34.6 January.1979 ' .

, FES NUREG-0453 o . UDAD and HERMES Table 4.4 Codes -

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2 486 6.14 .782 July 1979, IEA Table 4 MILD 05 Code (REF H) 3 1.22 15.0 6.83 September 1980, Appendix 6 MILD 05 Code l 4 .799 17.5 22.3 September 1980 Appendix 2 i MILD 05 Code I

5 2.37 16.0 3.22 May 1979, UDAD FES NUREG-0556 Code Table 4.6

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, 6 .0081 .0831 .038 July 1979, MILOOS - Appendix 6 Code l

. 7 1.58 22.7 9.2 59ptember 1980, Appendix 1 t MILD 05 Code I 8 . 91 4 14.5 9.34 September 1980, Appendix 3 MILD 05 Code l ,

9 .709 10.4 5.35 September 1980, Appendix 4 i ,

MILD 05 Code 10 1.57 8.98 8.09 July 1979, UDAD FES NUREG-0583, l

Code Table 4.5 i

11 1.96 45.0* 61.1 *. September 1980*, Appendix 5 l' [ MILD 05 Code 12 0.97 1.81 12.4 July 1980, MILD 05 FES NUREG-0702 Table 4.6 l Code 13 .08 .34 .28 February 1979, UDAD FES NUREG-0532, and HERMES Codes Table 4.2 14 2.0 11.5 24.2 February 1980, UDAD FES NUREG-0639 and HERMES Codes Table 4.9 i

" Based on overestimate of source tenns in initi,11 co puter run. Being rerun; expect at least 50% reduction in estimated levels.

PRELIMINARY' DATA DIRECT EXPOSURE AND fNGESTION EXPOSURE PATHWAYS DOSE COMMITMENTS FOR EACH MILLING FACILITY Direct Exposure Ingestion Exposure Dose Commitment. mrem location Oose Commitment, mee?

Location of Individual Corresponding .. . *

. Receiving Maximum Whole Fict1ity, Of rect- Exposure Oose Body Bone Lung hg $"Nse y Bone Lung 1 8 km E 2.0 74.4 29.6 Grazing 2.7 km .4 .4 5.0

_. SE-Neat ._.

2 716 km NE .020 .373 .316 Veg.+ Grazing .466 5.77 .466

. 1.4 km NE-Meat -

i 3 4.3 km NE .107 3.26 5.72 Grazing, .5 km 1.11 11.7 1.11 W

4 .55 km WNW 421 12.8 21 .9 Grazing 1.24 km .378 4 . 71 .378 NE-Meat 5 .5 km NNE 1.03 1.99 1.88 4.5 km NNE-Veg + 1.34 14.0 1.34 1.9 km N-Meat .

6 35 km NE .0021 .0071 .032 Grazing 2.5 km .006 .076 .006 NE-Meat 7 3.1 ENE .179 5.22 7.79 Grazing 1.9 km 1.4 17.5 1.4 NE-Meat 8 4.8 km E .176 5.24 8.6 Grazing 1.81 km  ;

NNW-Meat .738 9.21 .738:

9 3.2 km S .0 91 2.77 4.73 Grazing 1.68 km .618 7.65 .61 8!

HE-Meat 10 5.6 km N .830 4.31 7.35 4.2 km .738 7.67 .738' SSW Meat + Veg 11 2.5 km NW 1.11 34.3* 60.2* Grazing .4 km SE .852 10.7+ .852<

12 8.7 km NE .03

.65 .87 Veg. + 1.4 km 0.94 11.7 0.94 ENE-Meat 13 10 km N .06 0,8 .26 Veg. + 13 km .02 .26 .02

/*

NW-Meat 14 2 km N Unavailable Veg. + grazbtg Unavailable 2.7 km ENE-Meat

" Based on overestimate of. source tenns En' initial ' computer run. Sei~ng rerun; expect at least 500 reduction. in estimated levels.

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. ]ASIE 2  ;

GPERAll001AL BA810toGICAL ltDelll0Niler. PheGaAll 108 tseAltitM hill 5 Iype of sample Sample Collection 5asele Analvols type ei 10 usher locatlea Method freeuency trsquency Analysis '

SIAy5 ,

Part iculates See for Yelleucake dryer Isokleotic Eluarterly Each sample Itatural israelsso;

. each stock and packaging stack (s) Th-2M, pa-226, and Ph-214 If met avall-  !

. able free other seesrces.

pleasiere styk flew rate -

sealanomally.

Particislates ene for other stacks Represente- 5eala==aally Each sample statiaral israeless each stack Live grah Ih-2M, ta-226, and th-214. Measesre stock '

ilae.

AIR Particulates ihre~e tocations at er near Centleiseus I *I Weekly filter change, $serteri compeelte, llateral enraalism, the site hemsiderles and er more freapsently as bylocatfen of 84-226, th-2M, -

la different sectors roepstrrJ by dust tseeklysamples and th-210 that have the highest leadlag ,

predicted concentra-p Lleas of altbetae .

g e articulates (hs, .

Gee w At the nearest rest- Centlaucus Weekly filter change, $sarterly composite, Itatural israelim, more desce(s) er ecceptable er mere freepsently by locaties, of Ba-226, Ih-2 M. i structure (s) as resysired by dust tseekly seaples and Ph-218 leadfas See Centrol location (s)I'I Centlaucus Weekly filter change, 4lisarterly compeelte. Italieral uraalie.

er mere frecluently by location of Ba-226, th-2 M.

t as respaired by dust tseekly samp,es s and Ph-218 leading Raden Cas five er same locations as for Centlausens At least one sseek per thanibly Be-222 more air particulates or at least calender month repre-eine sseek ggy seating appreslaately

  • per aseth the same perled each meath WAllR Croised Water ihree or leydraleelcally deue Grab ihnathly (first year) Monthly (first year) Sissolved natural t more gradleal and rela- Ikearterly (af ter lluarterly (af ter first uraalum, P v226, tively close to the ggy first year) year) Th-2M, - IS, taillags impoundment and Pe-210,8 At least Hydrologically age Grab dluarterly lluvierly Bissolved natural one coa- gradleat (i.e., not israelism, Ra-226, trol sample lofluenced by eeepage Ih-2M, Pb-214 free taillegs) , and re-218 ,

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- OrtdA110064L BADI0t0GICAL Nilfl108llt, ts0 Git 48 tot LiaAH!tM Hitts Iw e of Saavle Sassale Collectlen Sassile Analysis Iype of thed.er tt.caLIon He t 4.ed f requesary Irequency Analysis one free Each well used for .Grah quarterly quarterly

  • Sisselved and each well drinking water er , suspeeded natural waterlag of Ilve- arenthe, ta-226, stock er crops within 11a-236. Ph-214, 2 to of the taillags and Pe-210 lepeunihnent Surf ace Water Two free surface waters passing Grah quarterly quarterly Sisselved and sects water througli ths all) site suspended satisral hedy or of fslie surface eranium, Ra-226, waters that are sufft- Th-230,Pl*-2l8, ciently clase to the and re-210(93 site to be seaject to surface dralmage from potentially contael-mated areas er that could he influenceal by l-seepage free flee Ings disposal area.( talh)

.* One sample cellected up-y streae of allt site and one sample collected at '

the slownstreas site bonsadary er at a loca-tion lamediately down- '

stream of leratten of -

potential influence -

One from large water lepoinul- Grah quarterly quarterly Bissolved and each water seats (i.e., lakeh, suspended natural body reservelrs) near the eranium, Ra-226, elll site that are ih-230. Pb-210, sufficiently close anal Pc-210 to the site to be sids-ject to dralnage free patentially contaeInated areas or that could be lafluesiced by seepage l

free the tallings disposal area.

WGflAlloff, fon0, AhD f1541 .

Vegetatina 1hree er f ree anleal gra:Ing Grah ihree times during 'fach ,saeple sa-226 and Pb-21e er Ferage4 ,3 mere areas aear the allt graatag seassa .

site in the directlea of the highest predicted , , , .

alaberne radienuclide concentraliens h

-..___.-._..--s -._._.-___+-_+_mm.__,.. .--...__~..-....-~m..-w,,+-< .,e...... . - - + , , . , .w .. s . .--4..._ ..--. . - ..- .. v -, .-- - ,. -

IAtti 2 (CentlaueJI 8Pf 8Allel4AL SAalel0GICAL H0ellIDEllG PROGRAH FOR UNANitel Hill 5 lype of Sample Sample Collectlee Sample Analysis Type of Ilumber location Method frequency frequency Analysis feed ihree of . Crops, llwestock, etc. drah Ilme of harvest once Ba-226 and each type raised within 3 ta of er slaughter Pb-218 allt site Iish Each body Collectlee of fish Grah Sealanaually Tulce aa-226 of water (if any) from lanes, and Ph-218 rivers, and streams la the alte environs that say be subject to seepage er direct suriace runeff free potentially contaal- .

aaled areas or that could he affected by a tallings impound- .

eent failure -

Salt AIS StBIMMI

$ Soll five er Same as for Grab Annually Annually ,

f more air partic- -

Naturaluranium$le ta-226, and Pb-a ulate saeples(h) 5adiment one er Same as surface Grab Annually Annually .

Natural uranium, tuo free water samples (e) Th-238,34-226, each water and Pb-210 body ,

OlktCI RADIAlloll five or Same as for air Continuous quarterly chan0e quarterly Gamma espesure more particulate samples passive la- of passlwe desla- rate tagrating stars device e

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[s h tes for Tables I and 3:

(a) Centlaumus cellectlea means continuous sampler aperaties with filter change weetly er as resystred by dust leadlag, sditchever is men's freepsent.

(b) the term " nearest" as used here means the locallen with the highest predicted airborne radleauclide concentrattees sharing milling operatleas.

(c) Cars should be Laten la selectlen et the central sampling loca'tless se that it is representative of the site condillons. Im general, a loca-tien la the least prevalent wind directica free the site should provide a sultable location for a centrol sampling site.

' (d) Various methods are acceptable; for esamples (1) Continuous cellectlen of a gasestas air sample with samples being changed about every 48 hours5.555556e-4 days <br />0.0133 hours <br />7.936508e-5 weeks <br />1.8264e-5 months <br /> for a 1 week period er (2) coatlesuous sampling.

(e) If the sample contalas appreciable suspended material. It should be filtered as soon as possible felleutng callectica through a membrane filter and the filtrate acidilled to 11 hydrochloric acfd.

(f) the Iscation of the ground water sampling wells should be deteralmed by a hydrological analysis of the potential movement of seepage from the tallings disposal area. In general, the objective is te place maatter wells in all directimas around the taillags area with the engdsasis on the dawa gradient localleas.

(u) surf ace-water samples to be analyzed for dissolved and suspended fractless should be filtered *as sassi as possible fellowing cellectisse through a membrane filter and the filtrate acidilled le 11 bydrochteric acid.

(h) Natural dralmage systema (dry washes) that carry surface runoff free the alle fellowing a precipitatlea event should he sampled following the event but at a frequency not greater than sealkly. ,

(1) the allting area refers to the area that includes are storage pads, allt buildlags, and other processing areas.

(j) Ihessaliminescent desineters should contain two er aere chips er otherwise provide for two rqadings per espesiere period (see Regulatory .

6 Guide 4.11).

(k) Surf ace sell samples should be collected sesing a coasistent tachalque to a depth of 5 ca.

f** (1) subsurf ace sell profile samples should be cellected to a depth of one meter. Samples slieuld be div ded late three estual sectlens for 8

analysis. ~

(a) Several samples should be collected et each locatlea and composited for a representative sample.

(n) aadea enhalatten measurements slaauld not he laten during perleds wisen the ground is freren er covered with ice or saew or following perleds of rala. It is receananded that these measureassets be taken la the spring througli the fall during normal weather coadillons.

(e) Vegetation er fora 0e saepling need lie carried out only it dese calculations indicate that the lagestien pathway free grating antaals is a potesillally significant esposure pallesay (an espesure pathway should be considered leportant if the predicted dose to se Individual would esceed 51 el the applicable radiation protectlen standard). -

t

f .

TA8tE 3I *I 1AMPtE l0MH41108 REP 08tiltra IIDilll0EING DAIA -

1. Siussuetu ,

for each sample analysed, report the fellowleg Ir.lermallea

a. Sate sample was cellected b.
c. Location Stack flewof rate samp(le cellectJoe m*/sec)
  • Concentration Error Estimats II Belease EeLe Error Estimate lleI 'I sa llosusclida (pCl/el l f El/el) (Cl/er) ICI/or) fitt/al) 3 frCI *I u mat 11-234 s

Ra-226 Pfa-2IS .

2. AIR SMel(5 for each sample analysed, report the fellowleg 14formellen:

.a- a. Sale sample was cellected *

b. locatlea et sample cellectlen
  • Concentration Error Estimate its
  • aadIasuscI1 ele (nacl/sI) ' (atI/al) (pc1/ml) X HPC U nat lla-230 ,

Ra-216 Pla-2 tB -

En-222 Ihis taisle Illustrates format saly. It is met a complete list of data to be reported. (See text of golde and Tables 1 and 2.)

I"I frier estimate should be calculated at 951 eencertainty level, based on all sources of randon error, met merely countingfrror.

Stanificant systematic errer should be reported separately. See Sectimas 6.1, 7.1.4, and 7.3.

I'I All calculations of lower limits of detecklen (118) and percentages of maalaus paraissible concentratisa (WC) should be inclesded as sagvlemental laformatlea.

6 6

  • TAatf 3 (Continued) 1AHrtE [0AMAT (DE Rfr0AlllIG HDettleelleG BAIA
3. I 1 48:30 SAMPt E 5 for each saeple emelyzed, report the following Informaties:

e *

a. Bate sample toes cellected
h. Location of sample cellectlen -
c. Type of sample (for examples sierface, ground, drinklag, stock. er irrleatten)

Concentrollee Error Estlaste llB Ba.IlenucIIde (i.C l/el

  • fa.CI/sI) (pC1/al) 48 nat (dissolved)

U nat (suspended)I I Ih-230 (dissolved)

Th-230 (suspended)

Ba-226 (dissolved)84-226 (suspended)I I

$ rb-218 (disselved)

I Pb-210 (suspended)bI '

re-218 (dissolved) re-210 (suspended)I I .

4. VECEI AI10tl. IC00. AHR f1564 5AMPtE5 f or each sample analysed, report the felleules laternation:
a. Date sample was cellected
h. locatloa of sample callectlen
c. Iype of sample and partion analysed Concentratten Error Estimate lit aa.Ilonuclide j pCl/La met L (s.Cl/te) (sil/tts)

U nat -

Ik-238 84-226 Pb-218 .

re-210 .

tant all samples must be analyzed for suspended radiensactides. See Sectieas 1.2 and 2.2 of this guide.

s 2

JA8tf 3 (Coatinued) 5AMPtf f0AH45 (OR SEP0Elli4G N0tillotilar. BAIA

5. Soll Atal SIDlitfMI 5AMPtI5 far each saacle analysed report the followlas infersallear.
a. Date semple was cellected I.. Locallen of sample cellection
c. Iype of sample and partion analyzed Concentratlea Error Estimate 118 sadio.u cIl4 heCl/ul_ L'I/al indI/al u nat Ih-230 Es-226 Pb-210 re-21e ,
6. DIEICI RA01AT1001 NEA5NSIMNIS s

L ior each measuressat. report the dates covered by the measurement and the followlag informatten:

f' .

5 Empesure Eate Error Estimate location (mR/or) f eR/c.r)'

~

7. RA11084 FIDE Mf A5ptfMMIS for each meestarement, report the dates covered by the measuroesset end the following fr. formation:

F line Error Estimate locatlog {pCl/e8 sec} j ott/m -sec) 8 O

e 4

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