ML20033F262

From kanterella
Jump to navigation Jump to search
Effluent Monitoring & Environ Surveillance Programs Annual Summary-1989,Vallecitos Nuclear Ctr
ML20033F262
Person / Time
Site: 07000754
Issue date: 12/31/1989
From: Cunningham G, Gest R
GENERAL ELECTRIC CO.
To:
References
NUDOCS 9003190129
Download: ML20033F262 (56)


Text

{{#Wiki_filter:_ 'l )0 - Wh -n - (' CLASS I JANUARY 1990 It g EFFLUENT MONITORING AND ENVIRONMENTAL-SURVEILLANCE PROGRAMS li ANNUAL

SUMMARY

- 1989

^ VALLECITOS NUCLEAR CENTER I ~ 1 Prepared by: Li ng R. E. Gest I G. E. Cunningham Nuclear Safety LI: 1I I GENERAL $ ELECTRIC I 7# ~ 7# ll w unsa rag s t L. d&k:b"l % oa MF%N

~ ] Nuclear SCfoty, M/C Vl8 0 ouailty Assurancs M/C vie ' RETURN T0: CSafsguards,M/C-V20 Licsnsing, M/C V18 .s _ ^'

GENERAL ELECTRIC COMPANY VALLECITOS NUCLEAR CENTER B

6 -Ploc3anton, CA 94566 NUCLEAR SAFETY . Attn: Nuclear Safety, M/C V18 TRANSMITTAL Effluent Monitoring and Tltle -rnvivnnmonen1 miry,411 nne., pengen. Date 3,M ~ f O Document No. & Rev. Annu.1 m.--nry k DISTRIBUTION LIST Mr.. Richard ningham, Acting Director Mr. Bruce Frnst Division of F 1- 'cle & Material Safety American Nuclear Insurers Office of Ni c ear terial Safety & Safeguards 230 Farmington Avenue U.S. Nuclear egulat y Commission Farmington. CT 06032 Washington._ .C. 20555 Mr. Steven R. Ritchie. Executive Officer Mr. C. A. Hooker Calif. Regional Water Quality Control Board U.S. Nuclear Regulatory Commission, Region V San Francisco Bay Region Oaks Office Park, Suite 210 1111 Jackson Street, Room 6040 1450. Maria.Lans Oakland. CA 94607 Walnut Creek. CA 94596 Mr. William Lew Radiation Health Unit Department of Environmental Health Division of Occupational Safety & Health Alameda County Health Care Agency. Dspartment of Industrial Relations 470 27th Street, Room 324 State of California Oakland. CA 94612 P.O. Box 603 San Francisco. CA 94101 Ceneral Electric Company Mr. Laurence'S. Gifford, Manager Corporate Environmental Programs R2gulatory Operations UnLt 3135 Easton Turnpike Gsneral Electric Company Fairfield. CT 06431 7910.Woodmont Avenue, Suite 203 Bethesda. MD 20014 Internal Distribution: John M. Sims, Ph.D, W. P. Springsteen, V18 SJ Library, Environmental Protection Department J. H. Cherb, V18 M/C 528 Lawrence Livermore National Laboratory C. E. Cunningham, V18 P.O. Box 808, L-255 B. J. Surma, M/C 402 lLivermore, CA 94550 O rirse issue. ror information oniv. O Revised oocument. oestrov previous issue. - For Review / Comment. O PCN. Attach to existing document. Refer-For Signature. ence or note change within document. . Controlled oistribution Acknowledgement Required. Sign Below and return trans-mittal as indicated above. For further information contact Receipt Acknowledgement Em N4 ADH. 150-A2 (10/82) kik / gg 6

I Class ! I I

s EFFIEENT MONITORING AND ENVIRONMENTAL SURVEILIANCE PROGRAMS ANNUAL

SUMMARY

- 1989 I

VALLEC3TOS NUCLEAR C UTER I I Prepared By: R. E. Gest, Specialist Facilities Protection Nuclear Safety Approved By: Cd b i ks J. M'. Cherb, Manager Nuclear Safety ,I I I I: vAmcmsnuctm e=Ta. Pms-N. cit==I*.au I einat O 5'5 cmc I

I I NOTICE AND DISCLAIMER This document was prepared by or for the General Electric Company. l-Neither the General Electric Company nor any of the contributors to this document: A. Makes any warranty or representation, express or implied, that the use of any information disclosed in this document may not infringe privately owned rights; or B. Assumes any responsibility for liability or damage of any kind which may result from the use of any infonnation disclosed in l_ this document. E I I I I I I I I I 11

I g 90NTENTS ZA&.t ABSTRACT-IV I 1. INTRODUCTION 1 A. Effluent Monitoring Program 1 1. -Waterborne Effluents 1 2. Airborne Effluents 2 I B. Environmental Surveillance Program 2 4 C. Compliance Summary 1. Nuclear Regulatory Commission and California State 4 Department of Health Services { 2. California Regional Water Quality Control Board 4 3. Listing of Laboratories and Analyses Performed 5 II. INFLUENT AND EFF1.UENT MONITORING DATA 7 A. Waterborne Releases 7 1. Influent and Effluent 7 2. Influent (Nonradioactive Parameters) 7 3. Influent and Effluent (Radioactive Parameters) 7 4 Nonradioactive Releases -12 B. Stack Monitoring 29 III. ENVIRONMENTAL SURVEILIANCE DATA 34 8: Vallecitos Nuclear Center - Plot Plan Indicating Sampling 35, 36 A. Surveillance for yaterborne Releases 34 1. Receiving Waters 34 2. Ground Waters 41 3. Stream Bottoa sediments 42 B. Surveillance for Airborne Releases 43 1. Environmental Air Samples 43 2. Cloud Gamma Monitors 43 46 f 3. Vegetation 48 ] IV. METEORO1DGY I 1 111

I I ABSTRACT ANNUAL, 1989 The data tables in this report include all results for the current calendar year 1989. All treated sanitary waste water has been disposed of on site by a sprinkler g irrigation system. No surface runoff was observed during the report period. 3 Ceneral Electric was in compliance with regulatory effluent limitations. I I' I I-t I I I I I iv

5 i EFFLUENT MONITORING AND ENVIRONMENTAL SURVE!LLANCE PROGRAMS ANNUAL SUtMARY - 1989 Lsa VALLECITOS NUCLEAR CENTER g R. E. Gest I l' ,.l~ 1. INTRODUCTION This report suninarizes activities and data for the Effluent Monitoring and Environmental Surveillance Programs for the calendar year of 1989-l at the Vallecitos Nuclear Center. p l Effluent monitoring includes measurements of airborne radioactivity releases L from facility stacks and the measurement of radioactive and nonradioactive constituents in water discharged through the site. sanitary and industrial h wastewater systems. Environmental surveillance encompasses the measurement of radioactivity in air near the site perimeter and the measurement of both radioactive and nonradioactive constituents in neighboring streams, wells, soils _and vegetation. A. EFFLUENT MONITORING PROGRAM The Effluent Monitoring Program has been developed to ensure that VNC site release limits for water are not exceeded and, additionally, to ensure that 'h; releases are maintained as low as reasonably achievable. Release limits for numerous nonradiological constituents have been established by the California Regional Water Quality Control Board (CRWQCB). Radiological release limits have been established by the Nuclear Regulatory Comission (NRC) and by the California State Department of Health Services (CSDHS). 1. Waterborne Effluents Waterborne effluents released from VNC site facilities can be classified { as industrial wastewater or clean water. r 1 1 L

I: Industrial wastewater in 1989 included cooling water and small amounts of process water which is first piped to a pH adjustment facility before discharge to one of three available 60,000 gallon retention basins. Tests for pH and radioactivity are performed on a water sample from each basin prior to discharge into Vallecitos Creek. In addition, samples from all basin discharges are accumulated and analyzed at specified intervals for a variety of constituents. Clean water discharges consist of storm runoff and small quantities of water g known to contain no contaminants. The latter includes condensate from building e air conditioning equipment. These waters flow directly to drainage ditches-which enter Vallecitos Creek. Sanitary wastes are collected and processed in a septic tank before undergoing sand filtration and chlorination (by addition of sodium hypochloride solution). Processed sanitary wastewater is discharged by land disposal (irrigation) onto - VNC property (Figure-1). 2. Airborne Effluents Airborne effluents consist of discharges from VNC facility stacks. Stack releases are monitored for radioactivity even though multistage filtering is accomplished prior to discharge. B. ENVIRONMENTAL SURVEILLANCE PROGRAM Vater samples are obtained within or beyond the site boundary to ascertain to what extent, if any, VNC discharges are detectable in the environment. Receiving waters, ground water, and stream bottom sediments are monitored for constituents which could have been dispersed by water. Air samples are utilized to detect the presence of radioactivity in air, and vegetation samples have been collected and analyzed in the past to assess the accumulation of constituents from both air and water pathways. The airborne release data are published only in this report. I I g 2

8 I I SANITARY / INDUSTRIAL / o I 2MHOTT TANK / ~~ TALLOUT BASIN j DRAINAGE I, \\ SAND TILTERS ADDITION SUMP i/ I l WASTE "PW Jg pH g gTME l SPRINKLERS l 8 2RRIGATION ISTRIBUTION PUMP VALVES 4 in. IRRIGATION N. 6 in. PIPE IRRIGATION 'RE ENTION : IPE 'I: BASINSQ { h, NOTE: -[ 0 ft I RASIN EACH SIDE l h SECTIONS TALLOUT y-- BASIN ( -(WE BOX) C ~8 LINE x DISCHARGE TO VALLECITOS ROAD

  • Added as Sodium Hypo Chlorite.

8 VALLECITOS CREEK Rev. 4-30-89 FIGURE 1. WASTE TREATMENT FACILITY I I l

i C. COMPLIANCE

SUMMARY

1. Nuclear Rerulatory Commission and California State Denartment of Health Services All VNC liquid waste releases were well within the limits specified by these agencies. There were no items of noncompliance. Compliance limits g are listed in 10CFR20 Appendix B and California Code of Regulations Title E 17, Section 30355. Compliance with these limits for the release of individual basins is determined by gross alpha and beta analyses based on the most restrictive isotopes which could reasonably be introduced into the system. g Airborne effluents consist of discharges from VNC facility stacks. Stack releases are monitored for radioactivity even though multistage filtering = is accomplished prior to discharge. 2. California Rerional Water Ouality Control Board (CRVOCB) E Nonradioactive discharge parameters are established by CRWQCB Order 84-76 and NPDES Permit No. CA0006246. Unless noted in the Abstract to this report, all industrial wastewater discharged from the site met the limits set in those documents. The permit does not allow the discharge of sanitary waste. That material is processed and disposed of to the land via an irrigation system. I Although the discharge permit issued to VNC does not specify sampling criteria for this land discharge, the following sampling program is being practiced: a. Total coliform (two times a month) b. pH (per discharge) g c. Radioactivity (per discharge) W Records of these test parameters are being maintained at VNC. I I

.._8 3. Listint of Laboratories and Analyses Performed A listing of laboratories which perform analyses is shown in Figure 2. Two of 8 the external laboratories are approved by the California State Department of Health Services. In September,1979. GE.VNC established a new contract with an outside vendor for analysis of radiological samples. As a result, the method of reporting sample results changed in that the actual analytical results obtained from measurements are reported - this is to be contrasted with the previous method of reportin6 results as "less than the minimum sensitivities of measurement". This change does not necessarily mean that more sensitive analyses are performed on any given sample. Samples analyzed on site are reported as above or less than values, while contract service samples are -I reported as actual measured values, Values determined to be within the statistical background for the contract service samples may be listed in the I table as positive or negative numbers. I I 8 I I I i I I I I-

i L I L I LISTING OF CERTIFIED LABORATORY ANALYSES AT GENERAL ELECTRIC COMPANY, VALLECITOS NUCLEAR CENTER - l-1. pH 4. Total Alpha-Emitting Radioactivity 2. Dissolved Oxygen 5. Total Beta-Ganna-Emitting Radioactivity 3. Temperature 6. Total Suspended Matter l :: I g LISTING OF LABORATORIES AND ANALYSES PERFORMED FOR GENERAL ELECTRIC COMPANY, VALLECITOS NUCLEAR CENTER g FOR COMPLIANCE PURPOSES 5 1. Brown and Caldwell Performs fish bioassays, total Environmental Sciences Division coliform and analyses on water 1255 Powell Street as required. Emeryville, California 94608

  • 2..

United States Testing Co., Inc. Performs most radiological and 2800 George Washington Way nonradiological analyses on Richland, Washington 99352 water, soil, stream bottom, and vegetation samples. I The director of each laboratory listed above signs the analytical reports that the General Electric Company receives, and each such report is available for ' inspection. I

  • The U.S. Testing Co., Inc., is not certified by the State of California but does participate in the U.S. Environmental Protection Agency's cross-check program at the Environmental Monitoring and Support Laboratory, Las Vegas, Nevada; and the California Re ional Water Quality Control Board Staff has acknowledged our use of this aboratory.

Figure 2. Analytical Laboratories and Analyses I 6

I 3 f, W 'll. - INFLUENT AND EFFLUENT MONITORING DATA A.- WATERBORNE RELEASES 1. Influent and Effluent Daily industrial and sanitary wastewater discharge and monthly influent ' volumes are sumarized in Table 1.

2. ' Influent (Nonradioactive Parameters)

. A summary of data relating to nonradioactive influent parameters is given in Table 2. L8 0 3. Influent and Effluent (Radioactivety Parameters) Radioactivity measurements for influent and effluent waters are sumarized 4 inxTables 3 and 4 Table 3 indicates essentially no difference between measurements' of influent (from the San Francisco water supply system) and monthly composites of industrial effluent. l Aliquots of daily samples are combined to form the monthly composite. The monthly composite results will differ from a simple sumation of daily sample analyses because: (1) the monthly composite analysis is performed by a contractor laboratory with minimum sensitivities different from site counting equipment; (2) the monthly composite analysis'is performed on a much larger sample; and (3) most of the short half-life naturally occurring radioisotopes have decayed below detectability by the time the monthly I composite is analyzed. The data in Table 3 are derived by summing data obtained from measurements of short-interval (daily) water releases. Many of these sensurements w.re less than the' detection limits of the laboratory's measurement methods. The data listed as "less than" numbers necessarily include the sumation of these detection limits (i.e., a summation of "less than" nun 6ers) and represent maximum possible values for the sample analyses. I 7

f Ill .l' f i1 l W M j n y,h'yn' %s'$!d 7[7[j r 7 -y,hy4' j j['-j f 7%$!/ 7 /' j[/ ) j, 7 / M j[jry,hy j4' E%4-$ / ]7/f f / y,hg4' n, [j j gV2%%$ / 7 7 M y4' j y,h ]7[/7j[#j gI/%%$!/ T 7 T 7 N NE j /f['jry,hyg' E ,%%$b U h f / U L F~ L M F j['jry,h-gg<' F %%%$b E 7 FE L [jry, gg/' L w%%$!d A A T TO O 3)77' M g /%%$Y[ fjry,[ T T I %%gN%%$!/ ['jry,fgg' / 7,hyg<' M j 7 g /%%$b { n-2 7,hyg/' j yN% %7$b } ~ ..M =, - s e , - e .. M 2 7 8 3 4 0 7 1 5 1 3 5 "o 1 4 6 5 8 7 0 8 7 0 7 3 5 M s x 2 2 2 2 2 3 3 3 3 3 4 3 E. S t E B lm A T t. a 5 t i ,. 9 . O v. .y V t s 7 0 5 5 5 0 0 n t. o 0 7 0 0 0 0 d7 5 4 0 5 5 0 1 1 n9 . i 9 e 2 1 1 3 E u 1 a1 x 7 7 8 8 8 9 1 1 9 1 1 T t 1 l M r A r n1 W 1' o t T-v. y n 1 Jl N n - u E o 9 9 0 0 8 2 6 6 6 8 6 1 0

. J M

'o 7 4 6 9 4 6 3 8 9 3 3 mf ( U. /. 1 s t t x 1 2 2 1 1 1 1 1 1 3 1 1 so F a i v F o dn E t a ~ M s D i me N tt A ns

  • o 6

1 5 4 1 8 2 5 4 3 4 3 ey TN mi 7 0 9 4 9 2 7 9 9 6 0 us 5 .s;. W 1 l 1' E x 5 6 8 5 4 4 4 5 5 9 3 4 f n v f o U. ei t t F ea ' mM t g .y 1 7 4 4 2 7 5 2 3 0 0 7 si et4 ". = = =., or m,6SE =.., 4 3 3 3 2 0 1 8 0 2 8 6 e ir s vst"t 1 1 1 1 2 2 2 2 3 2 1 1 i em o,o F " .e y v rr s ae m e R tl Y E R R ik + Y R B R E E nn R A ? 8 E M R ai s 'o a U M 1 s U B M 4 s U m c 1 E Y u T 0 E D a, m. s a R T N L c P f V C l o M m h c R U U u E C 0 E l s a D Aa M a M J J m S O e ~ J s q m tIllilIl 1lllllfl ll) 1' f l J)l\\l 1 l<

I I I I INFLUENT NONRADI0 ACTIVE CONSTITUENTS (ag/t) I CHLORIDES CHROKIUM COPPER LEAD MERCURY

EINC, pH

. JANUARY 2.9 <0.005 0.0013 <0.005 <0.0001 <0.005 7.9 FEBRUARY 3.1 0.001 0.0009 <0.005 <0.0001 0.003 8.6 MARCH 3.1 <0.005 <0.001 <0.005 <0.0001 <0.005 8.51 APRIL 2.9 <0.005 0.005 <0.005 <0.0001 0.008 8.7 MAY 2.9 <0.005 0.0006 <0.005 <0.0001 <0.005 8.8 JUNE 2.8 <0.005 0.0003 0.006 < 0.0001 0.100 8.9 JULY 2.95 <0.005 0.0011 <0.005 <0.0001 <0.005 8.9 AUGUST 3.0 <0.005 0.0012 0.009 <0.0001 0.021 9.1 SEPTEMBER 2.9 <0.005 0.002 0.006 <0.0001 0.030 9.0 OC'!OBER 2.6 <0.005 0.001 <0.005 <0.0001 <0.005 9.0 NOVEMBER 2.9 <0.005 <0.005 <0.005 <0.0001 <0.005 9.2 I DECEMBER 3.0 <0.005 <0.005 <0.005 <0.0001 0.0086 8.9

  • "<" Indicates less than the detection limit for the measurement method.

TABLE 2 E I I

aus as an es; as em am== me em> me en om as e m ens em as as:1 INFLUENT AND EFFLUENT RAD 00 ACTIVITY IN WATER (All detsin pCitt esecept as noessf) i timetract ser,tc, g,n,, vec o.t o. Avesnes T.es. Asees ty Presh Water GSo.tmey Effles.t w e

====.some e.a c s.ew S*"'88" su es ne. esse = sici ca. tract sereic, tentr.ct ser,tc. 8 Det s

  • Deto e l

a. n. a 6-y e 8-y m a B-y a 8-y ees. e JANUARY 0.593 2.37 0.493 1.44 15 <30 <30 <30 <50 <50 <50 0.388 1.548 0.016 0.073 FEBRUARY 0.299 1.24 0.493 1.81 15 <30 <30 <30 <50 <50 <50 0.417 1.627 0.017 0.074 MARCH 0.622 1.51 0.199 2.25 16 <30 <30 <30 <50 <50 <50 0.407 1.676 0.016 0.073 APRIL 0.338 0.492 0.513 0.592 17 <30 <30 <30 <50 <50 450 0.437 1.458 0.017 0.060 MAY 0.700 2.23 0.522 1.20 17 <30 <30 <30 <50 <50 <05 0.439 1.488 0.016 0.061 JUNE 1.070 0.80 0.728 1.10 18 <30 <30 <30 <30 <50 <50 0.467 1.385 0.017 0.055 JULY 0.965 1.35 0.281 0.122 24 <30 <30 <30 <30 <50 <50 0.453 1.217 0.017 0.049 AUGUST 0.539 0.958 0.986 1.12 24 <30 <30 <30 <50 <50 <50 0.487 1.239 0.020 0.050 SEPTEMBER 0.108 2.26 0.592 1.78 19 <30 <30 <30 <50 <50 -<50 0.512 1.258 0.021 0.050 OCTUBER 0.656 1.26 0.951 1.78 23 <30 <30 <30 <30 <50 <50 0.548 1.317 0.023 0.054 NOVEMBER 0.775 0.472 0.563 1.53 27 <30 <30 <30 <50 <50 <30 0.558 1.348 0.025 0.058 DECEMBER 0.613 1.40 0.627 0.634 22 <30 <30 <30 <50 <50 <50 0.579 1.284 0.026 0.058 f.,,,,, 0.607 1.36 0.579 1.28

  • See Section 1.C.3.

TABLE 3 I

8 TABLE 4 WATER EFFLUENT - THREE MONTH COMPOSITE Contratter Service Data PC1/8' m,0. $Af,K Cs437 00-60 1/1/89 - 3/31/89 0.0098 0.299 -0.110 4/1/89 - 6/30/89 -0.0054 0.105 0.553 7/1/89 - 9/30/89 -0.0041 0.147 -0.094 10/1/89 - 12/31/89 0.0023 0.299' -0.0342 e 8CP C *

  • 900 30,000 30,000
  • See Section I.C 3.
    • Mazia m permissible concentration.

3 Annual average release concentrations for the past 5 years are shown in g Table'5 below. These' data are from the Monthly Effluent Composite. -5 TABLE 5. Averare Concentrations In Industrial Effluent nCi/f* ,,gt_ h M8 x los 1985" 0.62 3.50 0.083 g 1986 0.72 5.12 0.033 W 1987 0.49 3.13 0.079 1988 0.35 1,56 0.024 1989 0.58 1.28 0.007 I

  • See Section I.C.3.

B. 11

~ t l' D. NONRAD10 ACTIVE RELEASES Sumaries of data relating to nonradioactive effluent parameters are given in Tables 6.through 24. A sumary of the nonradioactive effluent sample program is given in Table 6. The CRWQC8 compliance limits are sumarized on the Compliance Sumary. Table 7. Although Measurements are required, there are no I compliance limits for dissolved oxygen, turbidity, chromium, lead, silver, and EinC. Table 6. Sumery of Nonradioactive Effluent Tests I i

1. Daily - pH (Takenfromeachbasinpriortorelease.)

j !!. Weekly (Analyses perfomed on a grab semple once per week.) Total Colifonn Bacteria * (grab sample taken two times a month, sanitary only) 0er e e e e e e c e e t t t gE I $w# apo - m o o e o o o o o o o o o .a u.g a I m e e

  • e
  • e
  • g

$4* 06 D D o 8 D o D D o Arec em.tsen o D D o 11i tt

  • I la =5 ::
t e

e e e e & e c e e s.* en v ese, o o o e o o o o o o o I 2 h b N N h b N N N N N 3 3 3 3 3 3 3 h 3 3 3 3 E, I es. i. .M W m m 5 5 ep 4 4 th m 5 N U U C U E E U. U U U U U Ew g o,n y emps i o o o e o o o o o o o o go 1 I u 88 i e i I n

O II. I i l RETENTION BASIN 5AMPLES g-0 C) (Maximum limits: 6.5 to 8.5 pH end 32 Temperature P" Weber (# ) C shaber J I of of f Samples Samples Max Min Av Max Min Av e January 15 6.9 6.5 6.6 6 14 12 13 ) February 15 7.3 6.5 7.0 4 17 10 13 March 16 7.8 6.9 7.4 4 19 16 18 j April 17 8.3. 7.3 7.6 4 22 20 21 May 17 8.5 7.3 7.9 4 25 17 22 June 18 8.5 7.3 8.0 5 24 19 22 July 24 8.5 7.1 8.0 4 26 24 25 Ii August 24 8.5 7.0 7.7 4 26 21 24 september 19 8.5 6.8 7.4 4 26 16 22 g ll october 23 7.7 7.0 7.3 3 23 18 20 3l yovember 27 8.1 6.8 7.3 5 20 16 18 December 22 7.9 6.9 7.5 4 18 13 16 XXX XXX 8=no 'e 2" XX ,l XXX =a X 2e X XXX =.a XX io e> =9 e XXX 2 > XXX 2o Il 3; TmE. gl o

I I I I WEEKLY EFFLUENT GRAB SAMPLE m (Maximum daily limits: 10 mg./t TSM) _g 10TAL * 'roTAL e SUSPENDED SU5PECED I S W LING DATE a SAMPLEN3 DATE ff 1/5/89 <1.0 4/6/89 <1 1/12/89 <1.0 4/12/89 2.4 1/19/89 <1.0 4/19/89 <1.0 1/26/89 <1.0 4/26/89 1.1 MD!rnc.Y AVEM3E <1.0 MONTHLY AVEM3E <1.38 2/1/89 <1.0 5/3/89 1.6 8 2/8/89 <1.0 5/10/89 1.1 2/15/89 <1.0 5/17/89 <1.0 2/23/89 1.7 5/24/89 <1.0 I M0hWLY AVEM3E <1.18 MONTNLY AVEM3E <1.2 3/1/89 <1.0 6/1/89 <1 3/8/89 <1.0 6/8/89 1.5 3/15/89 <1.0 6/15/89 7.2 3/22/89

10. 5 *
  • 6/22/89 1.7 3/30/89

<1 6/28/89 <1.0 MONTHLY AVERGE <2.9 MONTHLY AVEMGE <2.48

  • "<" Indicates less than the detection limit for the measurement method.

I

    • Due to algae growing in the water.

l TABLE 9 4 15A

I I I I WEEKLY ETTLUENT GRAB SAMPLE (Maximum daily limits: 10 mg./t TS!!) w:AL

  • to:AL
  • SUSPENDED SU5 PEN:tD fd SAMPLIN3 DA;t SAMPLING DATE 7/6/89 1.2 10/4/89

<1.0 7/12/89 <2.5 No Sample 7/19/89 1.2 1/18/89 <1 7/26/89 <1.0 1/26/89 1.4 Moh m Y AvtM3R <1.5 MONTHLY AVEMst <1.1 8/2/89 2.7 11/1/89 <1 8/9/89 1.4 11/9/89 9 No Sample 11/16/89 <1 g 8/23/89 2.6 11/22/89 1 3 8/30/89 15 11/30/89 1 M0mwLY Avtust 5.4 MONTHLY AVtust <2.6 9/6/89 <1.0 12/6/89 <5 9/13/89 1.4 12/14/89 <1 9/20/89 2.0 12/20/89 1.1 9/27/89 <1.0 12/27/89 <1 Mow:wtY Avtuct <1.35 MONTHLY Avtuct <2.03

  • "<" Indicates less than the detection limit for the measurement method.
    • Due to algae growing in the water.

g TABLE 9 I is,

~ 8 l' l g R R E E R R E E I. lE 8 8 8 8 8 8 9 R R R R 9 aP 8 8 8 8 8 8 8 R 8 8 8 R R a a 8 8 8 8 9 8 R R R E j O O O e e n n e R R o a o s s 4 s s s a s s s a 3 d d d e C C o C o o C O o b m m m e c e n n n ^ ^ ^ ^ 8 8 8 8 8 8 8 8 8 8 8 8 8 8 E' I i i i i i i i i Y Y Y I o 8 .a. <v a l.h{3 vW 8 8 8 8 h 8 8 a 8 8 k g m m m m m m m . le e i i i i e i e i e d ? ? g{ ,a - D-I h q 9 q q 9 N q o { I 1'H o o e o e o o o o o o 1 ? e .E w o S m o e o m e o o e o o b k b 5 b 0 0 5 A y cee g g N m m 5 m e=s e m M WM W 0" d d d E E E 5 N f.. h g he m m em M M M N y g 4 h5 i J 5 i E S -{ o, o k m 4 o e l g i i v e v d v 8 d v v v j!! ~ E o O o C e o o o o o e wW Y E w m e ~1 % 9 g - :n I i J o 4 J v d 4 O j; A ~ i wt 1 1 1 1 1 1 >8 1 l di,l-ni t a 45t m:. 16

~ I J f f f f f f f f. f f. f f f \\ s e e e e e e e o e o e e e g e# G G S & # # # # #.# # # t s. o-e O-o- c. o-o- s-s o-s- \\ t -l.ml.-l. -l. $. $. $. -l. $. -l-l ml.e# i 3 .s g z-g 4 4 9.p.p.p.p p.g.g p p t y y y x y y y y w x x x x I, s i !,! / / f l i t. e/ / / / y a g m-e e e e e e e = y e t r e e i s s 's g 'r e II r a s-s- s-s- a >- a s-a e-s- 5 9 9 f f f f f f f f f f f li e z-3 e-e- e-e- e-e- e-s- e-e- e-e- e-lI sj eg i v v v v v v v v v v v v v Bi ,* e/ / / / / / / / / / / / / a e e e e e e e e e e e e g3 @b N l / ?~ $ h ol l 5 r P e e e e o P k e e O -E$ 4 N 8 8 8 8 8 8 8

  • 8 8 8 8 8 8 "f

>= t a 0-o- 0 o* o-0 d-0 0-0 0-0- o-h. 3 E 9 9 8 9 9 9 m 9 9 3 w" m m m m m m m m E 5 e F Im m m m N0 -k- $ y& $ 0 4 0 0 4 8 8 4 $ 6 6 5 a y y y y y y s-y y y y y 3 7 9 G $ e lgl $j t 4 9 9 u< r = u-e v o-o- v o-a- 3 8

1. J a

9 9 4 4

  1. 8 9

8 9 gn1 m e s y e 3-m ~ ~ ~ m m e s e e s s s e s s . L e 4!g 3 r o 3 n t N 2 N v ig s,l' a m E D g, 8 E g 5 SA l li 9 te e e Il a e e e e e e e e z. e+-4;r s a, e e o ~ e e e e s o-x r R al e e e e e e e e e 4

  • e 2

0 2 2 m R R m A A e se ig _i 5, e o o e o e o o e o o o e 35 jg e o e e e o o e o o e o o E O O O O O O O O O O O O

  1. N Y

il 2 4 8 4 9 8 8 8 8 8 9 p ~ a C C O O O O O C O O O C O g y U C lI a i I .g 1 I A i i i }!j j M A u u u u g -I 8 1 g l 17

I I I ANNUAL WASTE CHARACTERISTIC AND LOADING SU!OiARY* (30 day average release limit 5.0 mg./O OIL AND GREASE A A LOADING (kg/ day) M CONCENTRATION (ag/1) g W NO. Or 5 AMPLE $ T Iwo.or SAMPLES ERuAxiwuu minimuu Avsn&os w Axswww winiwww avam&os VlOLAT IO N hh&LVIED E N Out sch &hATI$$ JANUARY 3.2 0.9 1.9 0 3 0.727 0 0.174 0 3 TIBRUARY a 0 0 0 mp,Cs a 0 APP.IL <0.3 <0.3 <0.3 0 3 (0.068 0 <0.032 0 3 MAY <0.3 <0.3 <0.3 0 3 <0.068 0 <0.031 0 3 .7UNE 2.6 <0.3 < 1.1 0 3 0.591 0 <0.125 0 3 JULY <0.3 <0.3 <0.3 0 3 <0.068 0 <0.044 0 3 AUGUST 1.4 0.3 0.73 0 3 0.318 0 0.103 0 3 SEPTEMBER 1,4 <0.3 < 0. 67 0 3 0.318 0 <0.077 0 3 OCTOBER 1.5 1.3 1.4 0 2* 0.681 0 0.197 0 2 NOVEMBER <0.3 <0.3 <0.3 0 3 0.136 0 <0.049 0 3 0 DECEMBER a 0 h[h.[hjl l N Qy 3.2 0.727 FM l

  1. ise ilB$i<o.3 1999 l~

IR$$$ o 7 I Fgg g$$ [? <0.089 <0.77 [ f[ f f,7 h 0 26 0 26 TOTAL

  • "<" Indicates less than the detection limit for the measurement method.

a Contractor lost samples during analysis. I TABLE 12 18

8 I I I ANNUAL WASTE CHARACTERISTIC AND LOADING SU!EARY (90 day everste release limit 250 mm./O 'A TOTAL DISSOLVED SOLIDS I AM CONCENTRATION (ag/1) 14ADING (kg/ day) E NO.0F SAMPLES NO. 0F S AMPLE S R ummuu ummeum avanAar uAsiwuu win:www AvgmASE I gp g MONTH A"u....T/b vietatiou a atvare 21.5 0 1 4.88 0 1.97 0 1 JANUARY 30.0 0 1 6.81 0 3.03 0 1 FEBRUARY 44.0 0 1 9.99 0 4.30 0 1 MARCH 22.0 0 1 5.00 0 2.36 0 1 APRIL 24.5 0 1 5.56 0 2.54 0 1 MAY 24.0 0 1 5.45 0 2.73 0 1 JUNE 24.0 0 1 5.45 0 3.52 0 1 JULY 27.0 0 1 6.13 0 3.79 0 1 AUGUST <1.0 0 1 <0.227 0 <0.115 0 1 SEPTEMBER 22.0 0 1 9.99 0 3.09 0 1 OCTOBER 24 0 1 10.9 0 3.93 0 1 NOVEMBER 5.0 0 1 1.14 0 0.672 0 1 DECEMBER [M ((,[M l l kk?(( l l 44,0 10.9 M I I $$ B_ E NBRB l =;= P/A o <>.0 y T m sg Y Y g,= gg33g <2.62 <22.4 I 333 333 3gg ggggpyg 0 12 0 12 mu I I =2 2 ' I 19

{ l I I ANNUAL WASTE CHARACTERISTIC AND LOADING SMNARY* (30 day averste release limit 5 as./O P TOTAL SUSPENDED MATTER A "AM CONCENTRATION (ag/1) LCC ING (kg/ day) g NO. 0F S AMPLES NO,0FSAMPLES E R=Axewow wiwowow AvenAes wAnimum weniwuw Avsmass viouvion 4% tyreo MONTH L,,...,. y:. sRNUARY <1.0 <1.0 <1.0 0 4 <0.227 0 <0.092 0 4 PESRUARY 1.7 <1.0 <1.18 0 4 0.386 0 <0.119 0 4 MARCH 10.Y (1.0 <2.9 1 5 2.38 0 <0.283 0 5 APRIL 2.4 <1.0 <1.38 0 4 0.545 0 <0.148 0 4 MAY 1.6 <1.0 <1.2 0 4 0.363 0 <0.124 0 4 7.d* <1.0 <2.48 1 5 1.635 0 <0.282 0 5 sunE JULY <2.5 <1.0 <1.5 0 4 <0.568 0 <0.220 0 4 AUGUST 15 1.4 5.4 1 4 3.407 0 0.758 0 4 SEPTEMBER 2.0 <1.0 <1.35 0 4 0.454 0 <0.156 0 4 OCTOBER 1.4 <1.0 <1.1 0 3 0.636 0 <0.154 0 3 NOVEMBER 9 <1.0 <2.6 0 5 4.088 0 <0.426 0 5 DECEMnER 5 <1.0 <2.03 0 4 1.136 0 <0.273 0 4 [kf[M l "(M%%[/] l 4.088 $Q 15 NBal g F#M MB L4 x=e F# o to f f f,[/ ((M <0.253 AY[cc / <2.01 3 50 L [ [ [ [ 0 50 TOTAL

  • "<" Indicates less than the detection limit for the measurement method.

I

    • Due to algae growing in the water.

I ~" 1 I 20

8 I I ANNUAL WASTE CHARACTERISTIC AND LOADING

SUMMARY

DISSOLVED OXYGEN (ag/1) M C - R* Concentration C-6** I ET NO,0rsAupLes NO.OFsAMPLss ER uuuuuu uinnavu avsnaos waxiuvu wineuvu avenass MONTH $5!!#4..Tyb UIIU8.,2vIto I Dry [*g [g 0 1 9.6 JANUARY l 1 7.7 9.2 1 rEsRUARY Dry 0 9.3 1 MARCH Dry 0 8.5 1 APRIL Dry 0 8.7 1 NAy Dry 0 8.3 1 .TcNE Dry 0 8.1 1 .TULy Dry 0 8.1 1 AUGUST l 1 7.2 7.9 1 SEPTEMBER l Dry 0 8.3 1 OC20sER O'9 I 8.1 1 ~ NOVEMBER 7.7 1 9.5 1 DECEMBER [g(([/] l [ f[% g 9.6 8.9 (( kh hp gIy's ,jr 7.9 7.2 I l V(( [ AQE f/ F 8.6 7.88 "[ [ [ [ 4 12

  • C - R = Reference Station (Retention Basin).
    • C - 6 = keceiving Water Station C-6 in Vallecitos Creek down stream of basin outfall.

,_ 1, l al

r 3 I ) ) AWUAL WASTE CHARACTERISTIC AND LOADING

SUMMARY

(90 day averste release limit 60 an'./O l' CHLORIDE 14ADING (kg/ day) M CONCENTRATION (ag/A) E NO. OF SAMPLES T Iwo.orsAupLas 3 g R uaxiwou wiwiuuu AvenAas wax www winimum Avtaaet MONTH A5ff,',....J'she viotation a atyrte 3.6 0 1 0.818 0 0.330 0 1 JANUARY 3.7 0 1 0.840 0 0.374 0 1 TEsRUARY 3.8 0 1 0.868 0 0.371 0 1 MARCH 3.06 0 1 0.695 0 0.328 0 1 APRIL 3.1 0 1 0.704 0 0.322 0 1 MAY 3.6' O 1 0.818 0 0.409 0 1 JUNE 3.5 0 1 0.795 0 0.513 0 1 JULY 3.4 0 1 0.772 0 0.477 0 1 AUGUST 3.3 0 1 0.750 0 0.381 0 1 SEPTEMBER 3.4 0 1 1.54 0 0.477 0 1 ocTosER 3.5 0 1 1.59 0 0.574 0 1 NOVEMBER 3.6 0 1 0.818 0 0.484 0 1 DECEMBER [MM/M l l ((((M l 1.59 g% 3.8 [h l l (h fM 0 .06 MIN V V g r V FRgragg 0.420 =as F## M 3.46 ridnF#A N9BR o 12

  1. RjWiBM 0

22

=

I I TABLE 16 I 22

'W 8 8 I I ANNUAL WASTE CHARACTERISTIC AND LOADING SinNARY* (30 day average release limit 0.02 mm./t) COPPER (dissolved) M CONCENTRATION (ag/1) 14ADING (kg/ day) I g No. or2 Auptas T wo.orsau, Lgs g R=Aximum win e AvenAes uAmiuvw minimuu Avtaast MONTH S*s!I,'*A..T#rb NIN = aNDYre -0.0020 0 1 0.00045 0 0.00018 0 1 JANUARY 0.0022 0 1 0.000$0 0 0.00022 0 1 TEBRUARY 0.002 0 1 0.00045 0 0.00020 0 1 MARCH < 0. 001 0 1 (0.00023 0 e0.00011 0 1 APRIL 0.0021 0 1 0.00048 0 0.00022 0 1 MAY 0.0026 0 1 0.00059 0 0.00030 0 1 JUNE 0.0040 0 1 0.00091 0 0.00059 0 1 JULY 0.0030 0 1 0.00068 0 0.00042 0 1 AUGUST 0.002 0 1 0.00045 0 0.00023 0 1 SEPTEMBER 0.009 0 1 0.00409 0 0.00127 0 1 october 0.006 0 1 0.00273 0 0.00098 0 1 NOVEMBER <0.005 0 1 0.00114 0

0.00067 0

1 DECEMBER ((j,#/M l kh [h lhh l l / 0.00409 N"M 0.009 [h l 1hhh } [ gNg$ kh 0 <0.00 f I, ((,%- ggg pgf 0.00045 < 0. 00' (([ E[h 0 12 f [// 0 12 TCffAL

  • "<" Indicates less than the detection limit for the measurement method.

I , m e 12 1 l 23

I I I ANNUAL WASTE CHARACTERISTIC AND LOADING SUle!ARY* (30 day average release limit 0.001 ag./O 'A MERCURY AM cowerNTRATION (ag/1) (X1P) LOADING (g/ day) ET - we.orsAMPLES NO. Or S AMPL.55 E RinAximuu uiseinsaa AvenAos wAximum wisetuum AvtaAar MONTH $5?I#A..T!A. MIU8u A=Yd'Ae <1 0 1 <0.0227 0 <0.0092 0 1 JANUARY <1 0 1 <0.0227 0 <0.0101 0 1 FEBRUARY <1 0 1 <0.0227 0 (0.0098 0 1 MARCH <2 0 1 <0.0454 0 <0.0214 0 1 APRIL <1 0 1 <0.0227 0 <0.0104 0 1 MAY <1 0 1 <0.0227 0 < 0. 0115 0 1 suME <1 0 1 <0.0227 0 <0.0145 0 1 scLY <1 0 1 <0.0227 0 <0.0140 0 1 AUGUST <1 0 1 <0.0227 0 <0.0115 0 1 SEPTEMBER <1 0 1 < 0. 0454 0 <0.0140 0 1 OCTOBER <1 0 1 < 0. 0454 0 <0.0164 0 1 NOVEMBER DECEMBER <1 0 1 <0.0227 0 <0.0134 0 1 [M h[fM [M([% l l E$ <2 <0.0454 [ l l MNM?M //$,<1 f 0 <0.0132 AYiig / <1 M M MA P7dMRM g, o 12 o 12 =

  • "<" Indicates less than the detection limit for the measurement method.

I TABLE 18 I h 24

~-____._ _ I I I ANNUAL WASTE CHARACTERISTIC AND LOADING

SUMMARY

TOTAL CHROMIUM l M, CONCENTRATION (ag/t) 14ADING (kg/ day) T*R no.or sAwetts No. or s Aupce s uAmimuu uimsea AvtaAes w Amimum utmouum Avsmaet MONTH 5,3'%'..'L% 8ioUE8 a=Ty?re 0.002 gh t 1 1 0.00045 0 0.00018 g JANUARY 0 00 T0 001j4 1 0o,, <0.005 1 TEBRUARY 01j4 0 0 00 1 1 00 l <0.005 04 MARCH 0 0,30 1 o'00174 <0.005 1 034 APRIL

  1. '0003, U'001j4 l

1 0 1 <0.005 MkY 0.009 1 0.00204 0 0.00102 1 l JUNE 0

00007, 0' 001j4 1

l JULY <0.005 1 TO Oogy 1 0 fjg 0 0 <0.005 1 AUGUST g l 1 0.006'4-0 0.0032 1 0.028 SEPTEMBER 0*0007g <0.005 1 TO. 00p 0 1 OCTOBER py l 1 0.001 1 0.00045 0 0.00016 NOVEMBER <0.001 1 c0.00023 0 <0.0001: I DECEMBER F((jMM l (($j <0.0064 gg 0.028 f 0 [ [ l gNN fh e0.001 t V WW a =E mrt o am4 o *6 WM FA t 12 RBRMM V !I 12 =

  • "<" Indicates less than the detect. ion limit for the measurement method.

i I l ,m, 19 g l 25

I I I ANNUAL h'ASTE CHARACTERISTIC AND LOADING

SUMMARY

LEAD A, M CONCENTRATION (ag/1) 14ADING (kg/dsy) g T wo.or sAuPLes NO. OF S AMPLE S ER uAximou uswimuu AvetAas uAximum wiwouvu Avsmass MONTH $,1*J,',.,,,,. m,. v,,ut iou an gyree <0.005 t 1 (0.00114 0 0000q g g 1 { JANUARY 0 00 y, l l 0 1 1 <0.00114 0 <0.005 FE3RUARY 1 <0.00114 0 0 00 1 l <0.005 0g MARCH 0 00034 1 <0.005 1 <0.00114 0 APRIL 0 00py, l 1 1 <0.00114 0 <0.005 MAY c0 0003, 1 <0.005 1 <0.00114 0 JUNE- <0.005 1 - <0.00114 0 0,00 1 i 07, JULY <0.005 1 <0.00114 0 0' 0 1 00fg AUGUST 0 00o3, 1 <0.005 1 <0.00114 0 SEPTEMBER <0.005 1 <0.00227 0 0 00 I 07a OCTOBER 0 00 ep 0 1 <0.005 1 (0.00227 0 NOVEMBER 1 <0.00114 0 0 00 I l l <0.005 06) DECEMBER kJj[M <0.00227 ((jkM l EN c0.005 (( [ (( 0 M hiMIM <0.005 f l f h[ [M ANAL ), / <0.005 <0.0006( 2 ((,,-h'[ TOTAL ,g' f f 12 12

  • "<" Indicates less than the detection limit for the measurement method.

I TABLE 20 I I 2'

LI I I ANNUAL WASTE CHARACTERISTIC AND LOADING

SUMMARY

ZINC M CoHCENTRATION (ag/1) LOADING (kg/ day) .no.or SAuputs NO. OF s AMPLE s T,R mAximuu wiNeuvu Avsmaas wAmiuuw wtwswuu AvtaASE E MAAten AkND VtOLATION Ass ALY3 E D gh gh 1 0.0043 0 0.0017 0.019 JA!CARY l l 1 1 0.0057 0 0.0025 0.025 FEBRUARY I l l 1 1 0.0057 0 0.0024 0.025 MARCH 1 0.0048 0 0.0022 ~ 1 l 0.021 APRI:. l l 1 1 0.0025' O 0.0011 0.011 MAY l l 1 1 0.0109 0 0.0055 0.048 .7UNE l l 1 1 0.0043 0 0.0028 0.019 .7ULY l l 1 1 0.0045 0 0.0028 0.020 AUGUST l l 1 1 0.0045' 0 0.0023 0.020 SEPTEMBER l l 1 1 0.0195 0 0.0060 0.043 OCTOBER l 1 0.027 1 0.0123 0 0.0044 NOVEMBER g l 1 0.0052 0 0.0031 1 0.023 DECEMBER FWA BRM I E I ,rn o o'8 FMSS I I o m95 msg g tag I pr/A

== Eg o

0. On l

f E/[k(( [ l 0.0031 AYM 0.025 PMW#4 PARIT $$iFR2iRB t 12 12

== I

  • "<" Indicates less than the detection limit for the measurement method.

I TABLE 21 I g 22

I. Am:At WASTE C)L8MCTIIL3572C AND 10AMNC StMRM' 'n, TABLt 22 sILvt R (,,,,, s,,n. m 3 q 1 .a. .. w. .s.. l en. 1 neem t3c.t.i.Xu, lat*PL..??% - < 0. 001 %} 1 10.0002 0 <0.0001 $3 1 rtenur i - <0.001 1 <0.000{ 0 <0,0001 1 mr 3.023 1[0.0052' O 0.0032, 1 A m st -<0.001 l 1 <0.0005 0 <0.0002 1 weern g@i@ ).023 26f% l D.0052 (g@gi "?fsi EEi# K{$< 0.001 ?f$ $?{$b 0 WkA50 g i ~ ate % 0%{ id.j< 0. 007 fgTfd ffgf<0.0004 l g! MM INN Mflk 4 @Mid Md1l[N4N l 4 %a Taste ) AMON! A NM90 GEN CON 3NTRATION (ag/t) 3&hDINO fkg/4.y) 1. I. a. w.. 6.. I cer..re. ?;t:4.L?JW neem 40.06 h) 1 <0.014 0 <0.0061 dt l 1 muur 0.03 1 0.0068 0 [0.0031, l 1 mv 0.03 l 1 'O.0068 0 'O.0042 1 Amst 0.06 l 1 0.0273 0 3.0098 l 1 weath l d@i@ 0.06 RIjkT754 l 0.0273 biEdj 7/56 EEiM @ds 0.03[MIfh l $$2 0 ($4/5 ~ AE% @!$ idl<0.045 @$fd ff#!l<0.0058 @$jV$l % $ 4 88pf;j.MYjs.}&hM T 4 mu l N, m te := Nnnitt un=0GrN l M', CON 3NTRA?20N (ag/2) 8&hDING (kg/4.y) l._ l 4. .s.. i.erm e.e.v..ra, est:n.L?;m .co.10 @) 1 (0.023 0 <0.0101 dt l 1 meur <0.1 l 1 <0.023 0 <[0.0104, 1 mY < 0.1 l 1 <0.023 0 <0.014Q 1 A m *T <0.1 1 <0.045 0 <0.0164 l 1 weeta EM <0.1 If4*/{ ($fA <0.045 d:iN] MI@ l l UEi@ dd$ 0.10 /f$d j~ $Nj$ 0 Ri@@ AE% IR 9Js <o.1 E s es $tgi<0.0127 sh P#dMf4 T 4 fff!&G M921$Nsj T 4 = l ... i. m.. 2..... ii... m i m,,,,. e. I

I B. ETACK MONITORING Eight stacks at WC required either regular or intermittent sampling during 1989. Data for each stack are given in Table 25A. The operating components serviced are given in Table 25B. Each of these stacks is equipped with a sampling line that contains a particulate filter for sampling particulate radioactivity. Selected sample lines are also equipped with charcoal cartridges for radiciodine I monitoring. Other stacks are equipped with noble gas monitoring systems. Filters and cartridges are changed weekly and analyzed for gross alpha, gross beta gamma, and 1 131. The noble gases are counted continuously, and a recording system provides a readout of the quantity released from each monitored stack. Results of the WC stack sampling program are presented in Figures 3 I through 6. Figures 3 and 4 present the emissions from the two major WC stacks, Building 102 (Stack 4) and the Nuclear Test Reactor (Stack 16). Figure 5 is a composite of the remaining minor stacks. Figure 6 is a composite of all WC stack discharges. I I I I I I I I 29 I

I ! 1I! TABLE 25A. Stack Meicht. Site and Flow Rate Design Stack Height (ft. Stack Size Flow Rate j gg;hg,g 12eation above roof) (inchen) (efa) b 4" Building 102A 75 66 diam. 40,000* D 12 Building 103 48 60 dian. 27,000* 16" Building 105 3 13.5 x 13.5 3,000 26" GETR 95 38 diam. 7,000 30 Waste Evaporator 19.5 13 x 17.75 2,400 34 Waste Storage 13 13 x 17,75 1,000 45d Building 300 15.8 15.75 x 22.25 2,800 mg, 48 Building 300 14.5 16 x 22.25 4,300 " Major stack 3Feet above ground level " Average flow 1 Stack #45 taken out of service 10-25-89. I i I l TABLE 258. Ocerating comconents Serviced Stack No. I l Remote Handling Operation, Isotope Production Facility, 4 gRadiochemistry, Remote Handling Operations Radioactive Storage Room 12 Metallurgy and Ceramics Laboratories, Chemistry Laboratories 16 Nuclear Test Reactor 26 Ceneral Electric Test Reactor 30 Liquid Waste Evaporator 3 34 Waste Storage Facility 5 45 Metallurgy Test Laboratory, West Area 48 Chemistry Training Laboratory I I~ I.

I I I Seta-Gessna (pC1) Noble ces (C1) 1-131 (UC1) 10!. Alpha (WC1) i to'I 10! 101 I f l l i l l 5 I 'l ,i..! 1 1 ( 4 e i.. i ~ \\ j' ' l' l lli J ~ I n 4

  1. 1 N Yk I l f 'Til ll

\\ ) f 3gi goe

C 3

10, 10!. r s i ? .i i ql .i '{l, = i i in . l llll1I I 15'. 15 i,, 10'.,........,,,,,, 10" 77. c. 77. 77. I FIGURE 3. BUILDING 102 (STACK 4), I 101. 1-131 (WC1) Alpha (pC1) Beta-Camma(WC1) Noble Gas (C1) I 10!. 15' 10: 1 e e N i. I / 76 m ) 3 / / ll l (j y l l. { l rl )\\ l%f 1 100 16l 16} 10 i i I I M Y ll [ u a i i i 1 1 n g l i n a 1 2 i [ e g I 1 ~ 0'si.<i..<,l, 16 3.~i. 1.~..~.~i>.'. ii i6<,i, .I El<>ll..

1. i > I n,b a

i 4 i <,15 . d i il 11 a I P FIGURE 4. NUCLEAR TEST REACTOR (STACK 16). I 1 31 I

.P I I I' Alpha (uci) Beta-Gasma(pCi) 1-131 (pC1) IQ 10l 10; 'I 5 ^ ? i e ti1iI l lill l ll I JP ) / [h 10$ 10I 15} ?. lio t us e i m I, 4 ~

  1. 1 1i

./IV-l lll1 ~ ~ ~ 11llll 1 1 7 g' ~ - 15# 15 '......... ~, o..,, 10'.:.::.::.::. ~ .,.......v,,,,,, FIGURE 5. COMPOSITE ALL STACKS EXCEPT NUMBERS 4 and 16. Alpha (pCi) Bata-Camma(pCi) Noble Gas (C1) 1-131 (pci) I l 10' 10I. 10[ 10!. 3 6 I i i i { ,7 >1 t .4 i i i e iI i ,i, i y a I 3 8 10 10'. 10 10I. n e r s.it ~ .A' t i i f ,f '\\ / i ' '1 r li ); 7l lb1dl IP l f f hH f f IHs + ,i 1DI.ino... 10' r(n m n.. m o n ', o lY 10 .romo..onoun 108.7o.~. 7. II. 1 .onon FIGURE 6. COMPOSITE - ALL STACKS. I g. 32 I ~

~ I I Total airborne releases (stack emissions) for 1989 are as follows: I Alpha Particulate: < 3.09 pCi (predominantly redon thoron daughter products) Seta.Camma Particulate: < 18.1 pC1 Iodine.131: < 0.18 oCi I 2 Noble Cases:

7. 39 x 10 C1 I

Noble gas activities recorded from Stack 16 integrate background readings with the actual releases, which, in some cases, account for 40 to 50% of the activity released. Stack 4 data have been corrected for background. I As with the water effluent data, these data above are derived by summing data obtained from seasurement of short interval releases. Many of the sensure. I sents on these releases were found to be less than the detection limits of standard laboratory instrumentation. The data listed include the multiple summation of these detection limits and therefore represent the maximum releases possible from the VNC during the calendar year. I I I I I I I 4 g 1

.-- ~----. ..~. -- -...- - - - .. - -. ~. _. ~ -..,. e u-I !P%.. Muefe~ j i g ll 0 lg f i i A;? ,\\ 8 g . I n - _i ~ I q ~ y _y l!! y,_!\\'! l 3 <m I 1 f Sg e s

A f a 'O ]!

E g N* I l] g Er g& lI i g f,*, /jh lp/ll ~ / ,M N I %' :g ia T T = l 't \\ rs N se c g x. p, -- p.. _. l g N. ib( I N.Ngo v 33 l i

_m._ u ~ -. _ ~. s {' I m*b n'Q' : .I ~ ' e g- .,s [, V s y.,4A x w\\ ,a x s n J 'N l Iy .hg' I' ' k., f' //f[ s- .a a '\\/(. y' i,. 3 \\ Wt, h} j(l r ") \\ i ./ n l =:r L x:.....-......g.n- , Gfr v 9 V l > v..g.w.... w . a l +. i, a? gMf , ! ;f ' $ E"W ' .Y :1hj,. l I 'p..:.5...'D3W,.T....:.: 4o g,l.s# 4

7,e n

2.. 7 '. 4.. -c. j. g. 5 ?' .) l l . p r, v.... .,+ I ~ q;;; g

.d%

-'"=tt',", !.r.:'.it'N".**" s, 1.....e i- ._;it=&- g n co n s. 5 36

N i I COMPLIANCE

SUMMARY

RECEIVING WATERS j (Tests failed wrsus tests performed) I D lv* hsperstmo pH gn I I I I !- j I E Y If II: I b.r an: pi 1 s a

g ae ou,,mi s-I Dry January February 0/1 0/1 0/1 Dry March Dry April Dry May I_

1 Dry June July Dry Dry August ( september 0/1 0/1 0/1 g Dry october November 0/1 0/1 0/1 pecember 0/1 0/1 0/1 l I TABLE 26 I 37

I RECEIVING WATERS ANALYSES DATE: 1/4/89 4/5/89 STATIONS C-4 C-6 C-4 C6 i TIME SAMF12D: Dry Dry Dry Dry Tesiperetute 'C g ( L e s olv.6 0, -.g/1 l tit'Eli!!n*"r""-' "oh'Is!"lo?"Ta'nM* - ' g [oIlbs 'NN tubidity - m PH l Copper - og/1 Chloride - 99/1 DATE: 2/1/89 5/3/89 { STAT 20NS: C-4 C-6 C-4 C-6 TIME SAMF12Dv Dry 0800 Dry Dry f. Tempereture - 'C 8 l Diosc1ved 02

  • 89/1 77 k!!No$!n 9

65 l hh*NsEhobIESh 64 $$I$1s 18Q 128 l l tabidity - m 7.6 pH 7.4 g; f Copper - 3g/1 0.0016 5 l l Chacride - 99/1 27.7 + p ignigeo g nia 0.06 Basin #2 <0.02 DATE: 3/1/89 6/7/89 STATIONS C-4 C-6 C-4 C-6 TIME SAMP1ED: Dry Dry Dry Dry Temperature 'C Dissolved 02 - ag/t Diseolvee Cuygen as - 6 Saturstion h Non or I"oltis*!'nM" Tubiolty = M pH Copper - og/1 Chlor 16e - og/1

  • "<" Indiestes less then the detettien limit for the measurement method.

3

    • Not scheduled or required.

3

I RECE!VING WATERS ANALYS15 uni 7/5/s9 10/4/s9 I STATION $i C-4 D-6 C-4 C6 ts e s wer3J:D Dry Dry Dry Dry I tempereture 'C ei. son,ee 0, - men I iltult!!n'"Y""-' $N*Mo?"mW' - ' I airisi'u r a M idity - #T0 g ,s Copper - og/t Chloride - eg/t uni 8/2/89 11/1/89 STAT 20NS: C-4 C-6 C-4 C-6 I Tzm SAwLte: Dry Dry Dry 0930

  • C 9

Tarperature - I-Dissolve $ 02 - 29/1 8.9 Dissolve 6 Owygen - 6 77 laturation I Ik'$$ hen $$h 86 I$ltis*!'M)Te6 52 9.0 Midity - #W 7.1 pg <0.005 Copper - et/g Chloride - 99/1 7+1 I Jgtgnisee g onia Basin #4 <0.02 <0.02 DAni 9/6/89 12/6/89 STAT 20NS: C-4 C-6 C4 C-6 I T!n SAMPLtD Dry 0845 Dry 0815 Temperature 'C 16 10 Dissolved 02

  • e9/A 7.2 7.7

(({sog{go erygenas-6 72 6B n Ib" Nan"foNIE** *

  • 75 72 I$$ths l'M}}'

67 62 M ialty - #TU 14.4 5.3 PH 7.0 7.0 Copper - og/l <0.001 <0.005 4 Chlor 16e - og/1 10 9.2

  • "<" Indfeates less than the detettien limit for the seasurement method.
  1. eNot scheduled er required.

son

? t I I I RECEIVING WATERS ANALYSES SM9LE STATIONS c-4 C-6 Radionetivity Radioactivity (oci/t)* (oci/t)

  • u>

3 3 o By M 3 a Sy n3 McNTH (alo ) (x10 ) Dry Dry JANUARY. 0.0270 1.55 -0.151 Dry FEBRUARY Dry Dry MARCH-Dry a Dry. APRIL Dry Dry MAY Dry JUNE Dry Dry Dry .7ULY Dry Dry AUGUST 0.694 1.32 0.063 Dry SEPTDOLER Dry Dry OCTOBER -0.133 1,49 0,091 Dry NOVEMBER -0.248 1.60 0.255 Dry DECEMBER gN$ 0.085 1.49 0.0645

  • See Section 1.C.3.

I TABLE 28. i 39

I I A2. GROUND WATERS Ground water is monitored by obtaining quarter 1/ samples from five wells on or near the site. Sample point designations and 1 scations are listed below and shown in Figures 7 and 8 I

  • G-2N1 Well southeast of Building 105. California State Well No.

45/1E--2N1 Fennerly 6-1). 6-10A1 Well south-southwest of Building 102. California State Well No. 45/1E-10A1. l G-10H1 Well on private property south of site entrance. California State Well No. 45/1E-10H1 (Fonnerly G-4). I 6-10J1-Well on private property 0.4 miles southwest of site entrance. California State Well No. 45/1E-10J1. 6-10P3 Well on private property 0.6 miles southwest of site entrance. I California State Well No. 45/1E-10P3. I ~g Sample data are summarized in Table 29. I I l *Not required. I I. i a I

M M 8 0 3 6 0 7 M H 2 1 8 0 0 6 0 0 0 0 0 5 8 9 3 p 8 8 7 8 8 y 0 t, 0 0 0 0 s t, 3 e3 8 3 i tg 6 9 9 P s 4 2 1 0 3 2 3 tf 0 6 5 0 y 1 M 3 2 e3 1 l C 2 4 9 0 0 0 s c, 1 1 1 1 a 1 0 e C n lg A d 1 2 9 1 1 e 6 S 6 3 7 4 0 m 6 4 7 2 D 8 3 9 8 0 2 M 0 T 4 5 4 4 5 0 0 0 0 5 7 5 5 4 9 8 9 7 8 H 2 4 3 2 2 0 1 0 0 1 m 7 7 7 7 7 f* 1 p 0 0 0 0 M t* i 0 s I 1 t' 0 7 1 6 1 i t J s t 2 4 0 4 0 t/ 4 8 5 6 0 y 1 1 t C 6 4 5 6 3 et 1 1 1 4 1 2 mc 1 0 1 0 1 o ee C n tt M A se 0 3 3 5 1 D 9 0 2 2 1 7 3 1 6 0 S 5 4 5 2 2 t 2 0 T 4 5 9 5 6 1 0 0 M 1 8 6 4 3 1 2 2 1 H 3 6 7 5 h. r 1 1 0 0 S p r N e 7 7 7 7 y* e 0 0 0 0 O s d t* d t r I 1 r e3 t t t O 9 6 8 4 M T H s O 0 5 7 4 t/ A 0 y 1 9 6 1 6 TS l C f 6 6 6 6 et f 1 a o 1 1 1 1 ec o 1 0 1 1 e ) R E. C n sg t 1 T f A. t d 8 9 / E t 4 8 S u 9 9 8 2 o u 9 m O 7 1 5 3 g M A O O 7 8 7 8 A f = 2 0 0 W S T 4 4 4 4 0 0 ( D E s L M e B ft d 0 H A M y "s R p i C t* r T i s t* o 1 i el l 4 s tt y y y y h y y y y t/ 9 y 1 c r r r C 1 l C r r r r et D D D s a D D D D mc I M = ee C n lS A d 1 e C S m D T ) M 1 7 8 1 7 9 / 0 3 8 0 g 5 2 2 H 6 5 4 3 4 5 0 1 1 2 m p ( 7 7 7 7 7 y i 0 0 0 0 0 t ** d M s t + i eI i 1 0 7 1 1 5 s i t l N 5 3 0 3 0 t/ 1 9 6 1 9 o y 1 l C 1 3 4 3 3 ct 2 S 2 2 2 2 2 ec 2 2 1 1 1 a C ee n ll d M A d e e 8 2 1 9 0 v 5 4 1 6 1 8 0 2 1 0 9 0 5 4 5 6 3 m l o 1 7 7 7 6 7 2 0 0 1 1 ss 3 t s, i M t a0 Dd e c. err $ t 1 1 1 1 4 1 I 1 1 4 l r1 soe p e ai n s t u o u s oqi r n r n T et M M e t e c e t e r e n s n n s n = s e e w u e n e e s s a s e t a e u i e s s v 5 o e s s p v m e a a e a o u 0Ns r s i

  • a r

g 1 M m C

I-

A 3.

STREAM BOTTOM SEDIMENTS Stream bottom sediment sample locations are listed in Table 30A. The sample locations are the same as for receiving water shown in Figures 7 and 8. Quarterly data are shown in Table 30B. ( TABLE 30A STREAM BOTTOM SEDIMENTS - DESCRIPTION AND SCHEDULE OF SAMPLES Sample Gross Number Location Frequency Rad. Co 60 Cs-137 S-4 Outfall of retention Annually X X X basins at south boundary of site S-6 Vallecitos Creek, Annually X X X 0.6 miles west-of site B. TABLE 30B BOTTOM SEDIMENTS Contract Service Data * (All Results in pCi/g) Sample Gross Gross Station Alpha Beta-Gamma Cs-137 Co-60 S-4 2.50 8.48 1.66 1.04 ~ S-6 6.29 10.4 4.10 0.367 7/24/89

  • See Section I.C.3.

I I 42 I

I 3,- BURVEILIANCE FOR AI)LBORNE RELEASES 1. Environmental Air Samnles I Environmental air monitoring stations are positioned approximately I 90' apart around the operating facilities of the site (see Figure 9). Each station is equipped with a membrane filter. Filters are analyzed for gross alpha and gross beta gamma. Results are graphed in Figure 11. I 2. Cloud. Cam a Monitors There are 31 stations on site for measuring cloud. gamma radiation, These are located in sixteen 22.5' sectors surrounding the facilities. Each station consists of a thermoluminescent dosimeter (LiF or CaSo :Dy) sealed in a plastic-coated aluminum foil package 4 which is placed in a protective brown paper covering. These dosimeters are changed once annually (Station 4, quarterly). Station locations are shown in Figure 9. South boundary stations are numbers 1, 2, 3, 8, 9, 31 East boundary stations are numbers 10, 11, 12, 13, 14, 15; North boundary stations are numbers 16, 17, I 18, 19, 23, 24; and West boundary stations are numbers 25, 26, 27, 28, 29 and 30. TABLE 31. Cloud Cam a Monitors * (aRem/yr) South East North West Roundarv Boundary Roundary Roundary 0.83 0.83 13 1.67

  • Boundary cloud gamma monitor data are reported as mean values.

321g: Background radiation in this area is due to naturally occurring radioactive elements.. The TLD process background used was 72 miem. I g

I I I I . A... S. A. S 0 AIR SAMPLER STATIONS v, I I l ,,. 3,.. ,,.... ~...... 9 /

  • .'~s s

.. * *gg 't 's. 4 l l (.j ,') I.. o'! a-l..,. g l /.m ,/ 4,, N.,V g g ,3........ g / / / A' t! ,/ l e ./ ,,'a$ < *', _{ ""I O

  • ~4*. (,,,

,... /< ' 5 40

  • a

\\

  • ,*2 -

.q f, s, m..... ~ .--*L-, l .S ",,**"g**= g i,... .Rg 'et.' ll-; \\' B ,/,, .?% g.. / ,/.,' s, 'l ',,,',*/ '*?.I.' a ,/ / j ao... = s a 87* "'.. 4.........L..~......&.. / f g ~# VALLECITOS ACAD I ENVIRONMENTAL AIR STATIONS AND CLOUD-GAMMA MONITORS FIGURE 9. I g

I I I No. A-1 No. A-2 Beta-Gama Alpha Beta-Camma Alpha 152l 15 1

158, 15,:

,c t. ..'i; i i i. i,i,,,. i i ii iii ti i i i 1 I i il li lil + I } ll ll l 153i 15 ' 152} 158j i t i ..i., i

,i, o,, i,.

I it l' iA i i f iii' r i + . i\\ l i \\ Ji u; p l ( lH- . )*' l Illl lp l J / l \\ln I

  • / i

5" ' l ~ v V <r 15:=........-,.,, 1536.,.q.44. 1525.,,......oo.m 152'....f.o.4 I No. A-3 No. A-4 Alpha Beta 4amma Alpha Be ta-Gama I ,3 161' 1312 131 10{ I 4 i I i lll I a g e 161; 331r 151' 13 6 I 6, t + n 1 l' if / M g )55g S [ J N M n o v 3 f f y Mi l )f l f [ 15i. 15>- 15 >. ~...... - 15 >...,.<c, - ....._.m.. I FIGURE 10 ANALYTICAL RESULTS FOR ENVIRONMENTAL AIR STAfl0NS 'f FOR PARTICLES (pCi/cc). 45 I

I l: 3, Vegetation The description and schedule of vegetation samples are summarized in Table 34. See Figure 11 for map locations. Samples collected annually are analyzed for gross alpha and gross beta gamma. All sample points are sampled annually. These results are shown in ag Table 34 TABLE 34A. Descriotion of Vegetation Samoles Samole Number Location V2 Easternmost stream crossing south boundary of site VAL 1V West of site boundary, 500 ft, down road (Both sampled once/ year, 4 12 89) I I TABLE 34B. Annual Veretation Samole Analvtical Results (oCi/eram) Sample Gross Number Gross a h Cs-137 Co 60 V-2 0.00* 26.9 0.0227 -0.00535 VAL-1V -0.862 23.4 -0.0070 0.0166 I

  • See Section I.C.3.

I, Ii I 46 5

I I I l WALLECtT06 NWCLSAR CENTtm & V8 SET ate 9N Saesekt begatiews I I I I I o I I ara = g } Ta .,a..ew I ww eTU: I Jr.., 9Ba8t8 m.w g c I il g: 47

y I IV. METEOROLOGY I Rainfall to date and for the past five (6) years is as follows: DATE TIME PERIOD M 1984 1985 July to July 12.50 1985 1986 July to July 16.90 1986 1987 July to July 9.20 g 1987-1988' July to July 6.51 5 1988 1989 July to July 7.95 1989 1990 July to Jan. 3.00. I I I I I I I I I I I 48 I

I I INTERNAL DISTRIBUTION I M/.G l J. H. Cherb V18 C. E..Cunningham V18 R. E. Cost (10) V20 W. P. Springsteen V18 B. J. Suraa 402 C. W. Titus V18 Library-San Jose (2) 528 I I I I I lI; I I

I I

I I

I I EXTERNAL DISTRIBUTION a l Conies Alameda County Health Care Agency 1 American Nuclear insurers 1 California Department of Industrial Relations 1 California Regional Water Quality Control Board 1 CE-EP0/RECO (Fairfield, CT) 1-CE Regulatory Operations Unit (Rockville, MD) 1 Lawrence Livermore National Laboratory 1 Nuclear Regulatory Commission; Washington, D.C. 4 Nuclear Regulatory Commission, Region V 1 I I I g I I I I I I I _ _ _ _ _}}