ML20059E014
| ML20059E014 | |
| Person / Time | |
|---|---|
| Site: | Rancho Seco |
| Issue date: | 01/31/1990 |
| From: | SACRAMENTO MUNICIPAL UTILITY DISTRICT |
| To: | |
| Shared Package | |
| ML20059E008 | List: |
| References | |
| CAP-0002-APP-A, CAP-2-APP-A, NUDOCS 9009100004 | |
| Download: ML20059E014 (22) | |
Text
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I RSNGS SEMIANNUAL RADCACTNE EFFLUENT RELEASE REPOHT JANUARY. JUNE 1990 a
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I APPENDtX A - REMSION TO THE OFFSITE DOSE CALCULATION MANUAL CAPa)02 OFFSfTE DOSE CALCULATION MANUAL Revision 0 I
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JUSTIFICATION FOR CHANGES TO THE I
OFFSITE DOSE CALCULATION MANUAL Revision 7 General Comment:
The ODCM was changed from AP.310 to CAP-0002 to comply with new Rancho Seco procedures.
The contents were changed to e more orderly format, dose projection equations were added, I
an.1 the liquid ~ effluent monitor setpoint calculations were modified.
Therefore, although most of the calculations in the manusl-did not change, the numbering and location of cainulations did.
To provide an easy method of review, the step nacer from I
AP.310 will be referenced if a step number was changed.
ADDITIONS TO REVISION 7 S1EE The PURPOSE was reworded to coincide with the description 1.0 in Technical Specification 1.15.
This change is editorial and does not af fect the accuracy or reliability of dose calculations or setpoint determinations.
2.0 The SCOPE was also reworded to. coincide with the-3 description in Technical Specificatione.
This change is-.
editorial and does not af fact the accuracy or reliability g
of dose calculations or setpoint determinations.
3.0 The REFERENCES section was divided into a REFERENCE and COMMITMENT section.to conform to procedure guidelines.
Com;nitments and rsferences were added to ensure completeness.
This change is editorial and does not I
affect-the accuracy or reliability of dose calculations or setpoint determinations.
c F
4 '.1 The definition of REAL INDIVIDUAL was changed to MEMBER OF THE PUBLIC to coincide with-the definition in Technical Specification 1.19 and 40 CFR 190.
.The
=
definition was also expanded to clarify the difference between dose calculations for the MEMBER OF THE ~ PUBLIC and the MAXIMUM EXPOSED (HYPOTHETICAL) INDIVIDUAL.
The
- 7. '
MEMBER OF THE PUBLIC dose calculation will be based on actual food consumption, usage-and occupancy rates of a
' J!
real individual', whereas the MAXIMUM EXPOSED INDIVIDUAL i
will be based on maximum food consumption, usage, and occupancy rates identified for the site in the Land Use Census or RG 1.109.
This change is editorial and does not affect the accuracy or reliability of dose calculations or setpoint determinations.
4.2 The definition was expanded to include an explanation of e
an initial RB purge vs a continuing RB purge.
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.o
-. change is. editorial and-does not affect.the accuracy or
.i reliability of.
dose calculations or setpoint-
-determinations.
4.3 The definition of Continuous Release was clarified. -This change is editorial and does not affect the accuracy or
- I '
reliability of dose calculations or
.setpoint determinations.
I,'
~ 4.4 The definition of DEF/ ULT RADIONUCLIDE MIX. was edited when no- ' detectable activity is-deleting available."
The default mix tables ' may be used for determination of conversion factors-in addition to-when
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the release activity is negligible.
This change: -is editorial:nnd does not affect the accuracy or reliability-
,of dose calculations or setpoint determinations.
I, 4.6 The definition of MAXIMUM EXPOSED (HYPOTHETICAL)
INDIVIDUAL was reworded to coincide with the definition in. Technical Specification 1.21 and Regulatory Guide I
1.109.
In addition, the definition. was expanded to clarify.the difference between dose calculations for.the MEMBER OF THE. PUBLIC and the MAXIMUM EXPOSED : INDIVIDUAL..
,a,g This change is editorial and does not affect the accuracy or reliability of dose calculations or setpoint
' determinations.
L 4.8 The definition of UNRESTRICTED AREA was modified to stat'e that "For environmental ' protection / effluent control purposes; the Rancho.Seco Unrestricted Area is the area I
outside the Site Boundary as shown in Attachment 8.7."-
J
'This attachment is a map;of the Site Boundary used for
. liquid - and gaseous dose calculation purposes.
This change does not Laffect1the accuracy or reliability of 4
dose calculations or setpoint determinations.
t 4.9 The definition of EXCLUSION AREA was added.
This change-I is editorial and does not affect the accuracy or reliability of dose calculations or setpoint determinations.
4.10 The definition of NUISANCE PATHWAY was added to alleviate the 'needL.to track -activity. releases that do not contribute significantly(1 % for:1'iquids, 5 % for gases) i 7
to=the cumulative dcse totals.
These releases include a
l secondary steani releases and trace levels of activity in a
normally non-radioactive liquid effluents.
I Justifications ' for secondary gas Nt*ISANCE pathways is in l
section 6.1.2.
Trace levels NUISANCE pathways are J i, evaluated in CCF 89-559 & 89-569.
This change does not affect the accuracy or reliability of dose calculations or setpoint determinations.
o 4.11' The definition of UNPLANNED RELEASES was added and is m
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. a-t m 3
l' quoted from Regulatory - Guide 1.21.-
Also, a statement that all' unplanned releases shall be reported in the SAER a
was added.
This change does not affect.the accuracy.or 4I rel iability
-of dose calculations
. or.-
setpoint de weiMtions.
4.12 7
- - t inition of MISCELIANEOUS releases was added to clo
- . y the requirements for release points such as the IOSF and Respirator Trailer. This change does net affect the accuracy or reliability of doso calculations or setpoint determinations.
4.13 Previously step 4.9.
No other changes.
4.14 The definition of LERTS was added to clarify that the sluiceable domineralizer skid is the system installed-to reduce the quantity of radioactive materials ~in liquid I
This change is editorial.and does not affect effluents.
the accuracy - or reliability of dose calculations or setpoint-determinations.
The definition of GRTS was added to clarify that.the WGS 4.15 and VETS are the systems installed to reduce the quantity.
of radioactive materials in gaseous effluents.
This I
change is editorial and does not affect the accuracy or reliability ~
of dose calculations or setpoint determinations.
5.0 The responsibilities section was added to comply with the formatting requirements of Rancho Seco Administrative I'
Procedures. This change is editorial and does not ' affect
- theo accuracy or reliability of dose calculations or-setpoint determinations.
Section 6 was formerly Section,5
=
g NOTE:
Section 5.01was' entirely rearranged.
Ifithe intent or method was changed, the change was g
referenced and justified as necessary.
' 6.1 (Formerly 5.1) 6.1.1 (Formerly 5.1.1-5.1.4)
These sections have been 1
reorganized.
Step 5.1.3 has been deleted and replaced 51 by a statement in step 6.12 & 6.1.5 concerning Fuel Cycle The statement that no dilution outside the-site Dose.
boundary is taken into account for 10 CFR 50 calculations I.
has been deleted.
This is implicit in the calculation of step 6.4.
This change is editorial and doe = not af fect the accuracy or reliability of dose calcult e.ons or setpoint determinations.
6.l.2
'(Formerly Step 5. 4.1, 5.6, 5.6.1, 5.9.2)
These steps have been restated and enhanced to include more detail i
- i 1
~.. -
1
- about NUISANCE, = UNPLANNED, and ' MISCELIANEOUS release
)
pathways and consolidate -the requirements for batch releases out of the Waste Gas Decay Tanks and Initial ~
,I in'former: step
-1 Reactor Building Purges.
-The statement 5.9.2 which stated that
- tritium, radioiodine, and-1 particulate activity dose _do not need to calculated for pre-release. purposes is implicitly implied-'by not f
1 requiring them and the rtatement is not included.
The R
general arrangement of the gaseous effluent release
.j pathways did not change.
Several potential release pathways other than those
/
idanufied in the schematic, Attachment 8.2, are 4
I
. unmonitored steam releases from secondary plant equipment discussed in this section.
These pathways are and ordinarily contribute-little to dose tdtals.
i An' analysis of the releases for the second half of 1988 K
showed that-needless time and effort-was spent on the trackingiof these releases because the doses' calculated
'l were insignificant.
To - alleviate this problem. Action'-
~
Le'rels will be established to trigger when the evaluation-o l'
of secondary plant vents / reliefs shall be evaluated. The Action ~ Levels will be based on conservative assumptions.
so that the cumulative doses due to-gaseous releases are l
not underestimated, For clarification, this section in the ODCM will not preclude -Rancho Seco personnel from the obligation to-1 control and limit unplanned ventings.
The correction of-
~
l
-equipment leakage is still a priority. Also, actual UNPLANNED : RELEASES as defined in Step 4.10 shall be 1
evaluated for the cause(s) of the release, the. action taken to prevent recurrence and the consequences of the release as required by Technical Specification 6.9.2.3.1.
3 However, most of the tracking of abnormal releases
.r.
3 1988 ' involved planned releases through plant equipmeat
- E which had little ef fect on cumulative dose totals.-
For.all of the reasons above, the use of Action Levels J
does not reduce the accuracy or reliability of dose
- calculations.
-1 I
BASIS FOR ACTION LEVELS In Attachment A, the abnormal gaseous celeases for-the~
second half of'1988 are listed. The curias released from the IOS and the Respirator Cleming Trailer have been I
segregated from the other releases because they are considered miscellaneous planned release pathways'in that i
they are routinely monitored.
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~ Attachment B areethe REIMS printouts showing the: organ and air doses due to these abnormal releases-M itiplied~
by two to simulate a year's worth of releases.
A summary I
1 of these cumulative doses are:
-)
' Miscellaneous Releases Dose Summary
)
Dose TS Limit
% of TS Organ: Dose 1.01E-2 mram 15 aren 6.73E-2%.
Gamma Air 7.47E-6 mrad 10 mrad 7.47E-5 %
~
Beta Air 1.19E-5 mra' 20 mrad 5.95E-5 %
The Action Levels for noble
- xJases, iodines and-i particulates in the secondary. system will be based on I
1 the following assumptions:
The volume for determination -of Action ~ Levels 'for I
. particulate and iodine releases is 6.76E+08 ces.
The
-volume for determination of Action Levels for noble gas-releases 3.01E+10 ccs.
The volume for determination of 9
Action Levels for tritium releases is 3.29E10 ccs-Attachment C is the REIMS printouts showing the organ and air doses using the action levels to calculate the-doses..
I
'When all the nuclides having Action Levels are present at the concentrations specified in the Action Level,.then the dose-projected for one year would not exceed 5.0% of-the annual limit for organ dose, gamma air dose and beta I
air dose.
The following Action Levels--have been established based on Attachment C:-
ACTION LEVELS for MAIN STEAM and MAIN CONDENSER SAMPLES uCi/ml All Noble Gases 1.00E-03 I'
and Tritium Iodines 1.00E-06 (I-131,I-133\\
Particulates 1.00E-06 (Cs-137)
- I
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'._1__nn________.;
Miscellaneous P.eleases Nse Summary Dose TS Limit 4 of TS Organ Dose 4.56E-1 mram-15 mrem 3.04 %
Gamma Air 5.72E-2 mrad 10 mrad
.572 %
Beta Air 4.19E-2 mrad 20 mrad
.210 %
- - =
During start-up and shutdown, a factor of 10 may be applied.
When any one of the action levels above have been reached in secondary steam samples, then dose assessments 'of
'g secondary steam releases must be done.
The release g
points include but are not limited to the following:
j Auxiliary Boiler Vents / Reliefs Condenser Hogging Air Ejector Vents Auxiliary Feedwater Pump Exhaust
-l Atmospheric. Dump Valve / Main Steam Relief ~ Valves Vents I
-Miscellaneous Secondary System Steam Discharges-In addition, the Action - Levels must ~ be periodically evaluated to ensure tho assumptions used in this, basis l
are still valid. This change does not af fect the accuracy.
or reliability, of dose calculations-or setpoint j
determinations.
6.1.3 The meteorological data discussion-has not changed from.
Revision'6, however,. Attachment 8.4 has been updated ~to incorporate multi-year averaged atmospheric. dispersion and deposition factors.
Yearly updates of the ODCM for-
' incorporation of meteorological data will no longer be t
l l
required.
This change does not affect the accuracy or i
reliability of dose calculations or setpoint determinations.
6.1.4 (Formerly' Step S.4.3)
This step has-been generalize.d to:
include references to gaseous and liquid effluent boundaries. This change is editorial and does not affect I
the accuracy or re?.iability of dose calculations or 1
setpoint determinations.
6.1.5 This ste'p has been added to provide additional guidance I
and clarification for calculating FUEL CYCLE DOSE.
This change is editorial ~and does not affect the accuracy or reliability of dose calculations or setpoint J-
.. ~
v lg 4
us
---determinations.
1gl 6.1.6 A statement stating that if-the computerized methad of:
13 dose calculations is not available, _then the *aanual.
' calculation should calculate dose.
based en-the historically most restrictive receptor.. This chaugc does I
not affect the-accuracy or-reliability caf dose-calculations or setpoint determinations.
6.2 (Formerly-step 5.2.2)
This section has been-completely I.
reorganized and restated.
See separate : ht.adings for details of specific changes.
e (Formerly step 5.2.2.1)
Revision 6. required the~ setting of the liquid ef fluent monitor setpoint based on the
" DEFAULT HISTORICAL MIX" when no release =is occurring.-
This revision will require the setpoint. to - be set as I
close to background as possible without causing spurious alarms or as determined by Chemistry Supervision.
Thisi change does not af fect the accuracy or reliability ~ of ~
I dose calculations or setpoint determinations.
6.2.1 Because the conversion factor for the effluent monitors.
I plays a major role'in the detection capabilities;of the:
- monitors, a
section on the detarmination. of the.
conversion factor was added..8'was also-added listing the detection efficiencies fer-the liquid I
monitor.
This change will increar.e the reliability of setpoint calculations.
6.2.2
'(Formerly step 5. 2. 2.1.1 &
- 5. 2. 7. 1. 2 )
Since there is-only=one effluent monitor (R15017A), only one. equation-is applicable. Therefore, the previous'two calculations have been reduced to the one applicable calculationifor the liquid effluent monitor.
Also, since R15017A does not detect non-gamma emitting nuclides(H3),
the denominator of the equation has been modifed.to account-for this.
This change will increase the reliability of setpoV.t calculations.
I 6.3 (Formerly step 5.2.3 & 5.2.1.2)
Tnese steps have been-6.3.1 reorganized and restated to provide more clarification.
Previously, the pre-release and post-release equation E.
were separated into different steps.
Effectively, the 5-equation has stayed the same.
Implementation procedures determine how to apply the equation in different situations. This change is editorial / procedural and does I
not affect the accuracy or reliability of dose-calculations or setpoint determinations.
6.3.2 (Formerly step 5.2.1.3, 5.2.1.3.1, 5.2.1.3.2)
These steps -have been reorganized and restated but the
-methodology is still the same.
This enange is editorial and doeu not affect the accuracy or reliability of dose r
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eg y a.
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gt' calculations or setpoint determinations.
D6 6.4:
(Formerly step 5.3.1.2, 5. 3 '.1. 3 )
These sections have 6.4.1 been reorganized and restated to provide
'more clarification.
The liquid ef fluent dose calculation has not changed.
This change is editorial and does not I
affect the accuracy or reliability of dose calculations or setpoint determinations.
'B1 6.5 This section has been added to provide the methodology lBi to be used for dose projections due to liquid affluents.
This change is editorial and does not affect the accuracy or reliability of dose calculations or setpoint I
determinations.
6.6 (Formerly stop 5.7)
The section has been_ restated and
. I.
reorganized to provide more clarification.
This change (E'
is editorial and does not affect the accuracy-or reliability of
-dose calculations or setpoint determinations.
I 6.6.1 Because the conversion factor for the effluent monitors plays a major role in the detection capabilities of.the
- monitors, a
section on the determination of the I
conversion factor was added..12 was also added listing the detection efficiencies for-the gaseous monitors.- This change will inctsase the reliability of setpoint calculations.
6.6.2 (Forme.rly Table 5.4-1)
The tables contained extraneous 8
information not used in gaseous effluent dose calculations.
Therefore, this step reduced the tables to the needed information and provided some. -written clarifications.
This change is editorial and does.not I
affect the accuracy or reliability of dose calculations or setpoint determinations ~.
6.6.3 (Formerly part of step 5.7.1)
This' step separates out the partition factor calculation.
The calculation has not changed.
This change is editorial and does not I
affect the accuracy or reliability of dose calculations or setpoint determinations.
'E 6.6.4 (Formerly part of step 5.7.1)
This step contains the
=31 methodology for determining channel #4 (pci/sec) gaseous monitor setpoints.
The calculation methodology has not-changed from the previous revision.
This change is I
editorial and does not af fect the accuracy or reliability of dose calculations or setpoint determinations.
~
6.6.5 (Formerly part of step 5.7.1)
This step contains the methodology for determining channel #1 ( Ci/cc) gaseous monitor setpoints.
The calculation methodology has not changed from the previous revision.
This change is I w
LI I
editorial'and does not af fect the accuracy or reliability'
.of dose calculations or setpoint determinations.
The former revision did not contain the methodology for-
- 6. 7_-
determining gaseous MPC' values.
Even thougn Technical specifications do not have gaseous MPC limits, reporting I
compliance of 10 CFR 20.106 and 10_CFR 50.72 must still' be done.
Therefore, th'a MPC calculation methodology was added.
This change does not affect the accuracy ~ or reliability of dese calculations or setpoint I
determinations.
6.8 (Formerly 5.7.2 & 5.7.T The calculation methodology has; I
not changed sir.F
- last revision.
This change'is editorial and door not affect the accuracy or reliability of dose calculations or setpoint determinations.
6.9,10 (Fotaerly 5.8, 5.8.1, 5.9, 5.9.1)
The general methodology has not changed since the last revision. The-option to.use concurrent meteorology is included because I
the Semi-Annual Report uses concurrent values.
The:
acronym EMS -was changed to REIMS(They are synonomous).
This change does not affect the accuracy or reliability I
of dose calculations or setpoint determinations.
6.11 A section on gaseous dose projections was added.
Step 5.9.2 previously was called the Pre-Release Dose.
' [L Projection section but only addressed pre-release dose E
calculation requirements.
This section is implicitly L a~ ;
defined in step 6.1.2.
This change is editorial and does not affect the accuracy or reliability of dose
- g' calculations or senpoint determinations.
6,12 (Previously 5.10, 5.10.1,2,3)
The Fuel Cycle Dose B
section has been rewritten and modified to provide-clarificatic.a and -nimplification.
In the' previous g
revision, neparate equations were used to calculate Fuel.
g cycle Dose from noble gases. The separate equations'will~
not be used in this revision.
Equations from steps 6.4, 6.9, & ~6.10 will be referenced to provide the general methodology to perrorm. dose calculations.
Also, this
,I section will. not incorporate a standard residential-shielding factor.
Requiring that-certain-exact parameters be used would not be realistic because for an I
evaluation of a REAL INDIVIDUAL's doso, the parameters will change from one case to another.
Therefore, the g
general methodology only need:s to be provided and each I
instance' woc d be done on a case by case basis.
This change docs not af fect the accuracy or reliability of dose calculation::. or setpoint determinations.
6.13 This.is a new section addressing the new EPA requirements for 40 CFR Parts 302, Reportable Quantity Adjustment -
Radionuclides.
This change does not affect the accuracy a
+
.i
?
E o r -- reliability of dose calculations or setpoint determinations.
NA-Step 5.11.1 has been deleted because the information is already. contained in the SCOPE. This change is editorial and does not affect the accuracy or reliability of dose calculations or setpoint determinations.
NA' Step'5.11.2 has been deleted because this information is included under the Chemistry Manager's Responsibilities.
I-
~ This change is editorial and does not affect the accuracy or ' reliability of dose calculations or-setpoint determinations.
I, NA Step 5.11.3 has been deleted since the RSAPs that provide guidance to procedure reviews already requiire a biannual review.
The biannual review will be sufficient for a I
proper review of the ODCM. The annual requirement is not in Technical Specifications or the USAR,. therefore, it has been changed to biannual.
This change is editorial q
'I and does not affect the accu.'acy or reliability.of dose calculations or setpoint determinations.
Attachments 8.1&8.2 (Formerly Figure 5.1 & 5.4)
The - Liquid Ef fluent. and Gaseous. Flowpaths have been modified to correct and L
clarity discharge pathways. This change is editorial and does not af fect the accuracy or reliability of dose calculations or setpoint determinations.
j I
8.3 (Formerly Table A-7)
This attachment has been expanded-
/
5 to include the variables associated with the calculation' of dose due to liquid and gaseous effluents-containing I
radioactive materials. This change is editorial and does not affect the. accuracy 'or reliability of dose calculations or setpoint-determinations.
7 8.4-
' Attachment 8.4 has incorporated the information contained y
in Revision-6, Tables A-4 AND A-5.
This attachment lists I
the highest X/Q or. D/Q associr.ted with each gaseous pathway based on 1989 Land Use Census data.
The highest X/Q for the Exclusion area boundary and the site boundary-are also listed for dose rate and air dose calculations.
I' The direction and distance-is also provided..
.'In' j
addition, meteorological-data for the interim Onsite.
ij' Storage Facility 1s provided.
Since the IOS' discharges I
at a different point than the normal release point, the distances to the boundaries and receptors are different.
Therefore, to ensure the most conservative meteorological
.E; data is used-to calculate doses frou an IOS discharge, W.
this data it included.
This chance increases the accuracy and reliability of-dose ' calculations and setpoint determinations.
1 4
m 3-8.5 (Formerly - Figure 4.8-1, No changes' to Exclusion ' Area Boundary Map)
- 8. 6.
_(Formerly Figure 4.8-2, No changes to Release-Point for Liquid Effluents for 10CFR 20 compliance)
(Formerly Figure 4.8-3, No changes to Site Boundary for 4.7 Gaseous and Liquid Effluents)
(Formerly Table A-1)
The historical liquid source terms 8.8
- have been updated using data collected in 1988.
This t
change is editorial'and does not affect the accuracy or I
reliability of doze calculations or setpoint-determinations.
L8.9 Liquid - monitor detector afficiencies are listed in-Attachment ; 8.9.
Efficiencies were not provided in Revision 6.
This_ change will increase the reliability of setpoint calculations and dose not affect the ' accuracy -
I or reliability of dose calculati.ons.
~The organ dose factor for liquid effluents are listed in' 8.10 I.10.
Dose factors were :not provided in Revision 6.. This change is editorial and does not af fect the accuracy or reliability of dose -calculations or-setpoint determinations.
8.11 (Formerly Table A-2) The historical gaseous source terms have been updated using data collected in 1988.
This change is editorial and does not affect the' accuracy or reliability of dose calculations or-setpoint determinations.
8.12-Gaseous monitor detector ef ficiencies - are listed' in-Attachment 8.9.
Efficiencies were not provided in Revision 6.
'This change will increase the reliability of setpoint calculations and dose not af fect the accuracy or reliability of dose calculations.
.8.13 (Formerly Table A-6)
(only format changes.)
-8.14 The organ dose factor for gaseous affluents are listed in Attachment 8.10.
Dose factors were not provided in-Revision ~6.
This change is editorial and does not affect the accuracy or reliability of dose calculations or setpoint determinations.
cp p
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ATTACHMENT A TO.OOCM REVISION 7 ABNORMAL RELEASES 3RD & 4TH OUARTER,1988 RADIONUCUDES RELEASED in CURIES Release #
Descr4mion Vol(cc)
H-3 1131 1-133 Cs-137 Xe-133 - Xe-133m Xe 135 Xe-135m Kr45m Kr47 Kr48 Mn-54 Rt>48 Sr45 3
Aux Bir 1.13E+ 07 1.61E44 4
Aux Bir 1.43E+07 998E45 5
Aux Bir 1.43E+07 9 42E45 6
MSRV 8 82E+07 6.17E-04 1.69E46 1.50E46 6.16E44 1.91E45.1.65E44 1.36E44 1.59E45 4.98E-06
~ 2.18E46 1/AE44 1.58E46 7
Aux Bir 4.48E+08 1.94E43 8
ADV 7.70E + 06 5 30E45 1.47E47 1.31E47 5.38E45 1.86E-06 f.44E45 1.19E45 1.39E46 4.35E47 1.90E47 1.64E45 138E47
'9 Hoggers 1.51E+ 08 1.06E-0312.88E.06 2.57E-06 1.05E43 326E45 2.82E44 2.33E-04 2.72E45 8.53E46 3 73E46 3.22E44 2.70E46 ;
. j
- i 10 Resp.Trtr See'#17 11 Ho90ere 920E+06 8.79E45 -
8 68E45 2.22E45 126E45 3.13E-06 2.82E46 4.85E-06 12 AuxFeedPump 1.51E+07 1.12E44 4.50E46 1.26E46 3.19E-07 13 Aux Bir 1.40E + 07 1.06E-04 5.35E-08 14 MSRV<ADV
..uuE+07 5 28E45 5.19E47 2.22E-07 15 Hoggers 3.39E+ 05 1.16E-06 8.37E-09 2.75E46 1.04E-08 16 Aux Bir 8.43E+08 3.54E 17 Resp.Trtr 1.67E + 11 9 91E46 1796 18 Feed Hester 1.17E+10 861E-02 1.43E43 1.84E-04 C-19 Resp.Trtr 4.40E + 10 6.80E47 20 Resp.Trtr 1.31E + 10 1.41E45 21 IOS 3.88E + 12 4.98E47 22 MSRV. Hoggers 9.06E+07 7.58E-04 2.84E46 6.22E.06 6 93E44 8.07E45 9 97E-06 23 M6scetteneous 3 00E+09 2 01E42 1.26E43 396E44 24 Resp.Trtr 2.98E + 10 232E48 TOTAt.
1.15E41 1.87E45 1.31 E-03 1.05E-05 5.19E43 534E-05 1.14E43 3 98E-04 5.76E45 1.88E45 4.85E46 6.10E46 528E44 4.42E46 TOTAL excluding Resp Trtr & IOS 1.64E+10 1.15E41 7.58E46 0.00E+00 '1.05E45 5.19E43 i 5.34E-05 1.14E43 3.94E-04 5.76E45 1.88E45 4.85E46 f,10E46 528E-04 4.42E4s
~
3.44E47 3.54E49 1. cot-06 2 61E-06 3 82E49 1.1tE-09 tME-10 2.19E48 1.8eE-06 1.58E48 >
uCi/ cc excluding Resp Tcir & IOS 7.02E-05 224E45 0.00E+00 3.78E-06 Semi-AncualTotal ' AnnualTotal Volume from Tritium Reseases (cc) 1.64E + 09 '
327E + 09 Volumo from lodme Releases (cc) 3.30E + 08
- 6.,5E+08 Volume from Part. Releases (cc)
- 2.79E + 08 5 57E+ 08 Volume from N. Gas Reteeses (cc) 1.51 E + 10 '
3.01E + 10
.4 x
m
,g,.,.y g,-w.m.g w,w%+
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3,r*'<*P
"'f+--'
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RANCHO;SECO 9
Sacrosant'o Municipol--[ Utility Diotrict-24-aug-1989l12:42:19 4ASEOUS EVALUATION REPORT
'PART I:' DATA Pormit#
O ABNORMAL RELEASE ODCM EVALUATION (NOBLE GASES)-
sSource of Release -20 MISCELLANEOUS-GASEOUS RELEASE Diocharge Point
-15 ATMOSPHERE Rolocse: Flow rate 1.00E+03 CFM Volume 3.01E+1( cc-
-Moximum Flow Rate Allowed Due to Dose Rates 1.00E+03 CFM I', Sample _Date/TimeRoloase Start / Time 01-jul-1988 00:00:00
.Rolcase Stop/ Time 01-jul-1988101:00:00 Technician ML lPartII:l CALCULATIONAL RESULTS Maximum MPC Fraction 9 Exclusion Area Boundary 3.0096E-05 DOSE RATE CALCULATIONS (10CFR20)
T-Body Skin Organ IRolsase#
Dose Rate Dose Rate Dose Rate mram/yr mrem /yr mram/yr'
'This Release-3.50E-03 7.22E-03 0.00E+00 ( ADLT/ BONE) -
ALL RELEASES 3.50E-03<( 400.0) 7.22E-03<(2400.0) 0.00E+00<(1200.0)
DOSE CALCULATIONS (10CFR50 APP I)
Cumulative-
-This' Release GAMMA AIR DOSE (mrad) 7.47E-06 (31D) 7.'47E-06 1
7.472-06'<
4.0 (Q) Y 5.35E-03 <
8.0 (Y)'Y BETA AIR DOSE (mrad) 1.19E-05 (31D) 1~.19E-05 1.19E-051<. 8.0 (Q)-Y 1.59E-02 < 16.0 (Y) Y MAXIMUM ORGAN DOSE
.(mrem)
'ADUT/ BONE / SITE'O.00E+00 CHLD/GTRC/ HYPO 0.00E+00 (31D)
INFT/ THYR / HYPO 0.00E+00 <
6.0 (Q) Y INFT/ THYR / HYPO 3.01E-03 < 12.0 (Y) Y i
ISOTOPIC IDENTIFICATION
___..........__--_______~______..__...... __..._......... _.........._... _.___
~ Isotope.
Concentration (uci/ml)
Curies "i
H e
$ (p i
lllko
/
$
- 4*
l
+
IMAGE EVALUATION
[/'gf\\
Og, k'k gqjfey;:W
- %f[<t'#
TEST TARGET (MT-3)
M 4
I.0
- m m jfljLE I.I [" Ehl I.25 1.4 1.6 4
150mm -
y 4%
+<$
4 4
+R;f*zzzzz)t,Azzzz
[ s g+;,+
,I frCs
_. =
m
_- r;7 T s a men 7.-; u :
4 g
8sto 7. o[ f--
Bh
- XE 133" 7.60E-08'
.2.29E L XE-135M - 2.61E-08-.
7.86E-04 IifE-133 L 3. ' '. E - 0 7 '
1.04E-02 s
~XE-133ML 3.54E-09 1.07E-04 KR-88 3.22E-10.
9.69E-06 I
KR-87i_
~1.11E-09 3.34E-05 LKRe85M-3.82E-09 1.15E-04 TOTALS 4.55E 1.37E-02 E:..... _ _ _ _ _ _ _ _ _ _. _ _...... _ _ _ _................ _ _......
I I
is I
I 8
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-s:crcd nt'o Municipal Utility Dictrict~
RANCHO SECO i
24-aug-I989 14:08:55 GASEOUS EVALUATION' REPORT q
- PART I: ~ DATA-i POrnitiL 0
ABNORMAL RELEASE ODCM EVALUATION (PARTICULATES/ IODINES)-
1 Source of-Release 20 MISCELLANEOUS GASEOUS RELEASE Diccharge Point.
15 ATMOSPHERE'
.R31 Case Flow rate 1.00E+03 CFM Volume 6.75E+08 cc Maximum Flow Rate Allowed >Due to Dose Rates 1.00E+03'CFM Snaple Date/ Time R31 Case Start / Time 01-jul-1988 00:00:00 R31 Case Stop/ Time.
01-jul-1988 01:00:00 l
TCchitician ML lI!!!!!!!E:!EEEiiiiEEEii!!!i::::::::::::::::::::::::::::::::::::::::::::::::
l t>
Maximum MPC Fraction @ Exclusion Area Boundary 2.0860E-02 DOSE RATE CALCULATIONS (10CFR20)
T-Body
~ Skin Organ IRsloasef Dose Rate Dose Rate Dose Rate mrem /yr mrem /yr mram/yr 0.00E+00 7.88E+00 (TEEN / THYR) l Thio Release-0.00E+00 O.00E+00<(2400.0) 7.88E+00<(1200.0)
ALL RELEASES 0.00E+00<( 400.0)
DOSE CALCULATIONS (10CFR50 APP I)
Cumulative l 3 This Release Lg GAMMA AIR DOSE-(mrad) 0.00E+00 (31D)
'O.00E+00 0.00E+00 <
4.0 -(Q) Y-5.34E-03 <
8.0 (Y) Y l
BETA AIR DOSE (mrad)
~0.00E+00-
- ( 31D)
I.0,00E+00 0.00E+00 <
8.0 (Q). Y 1.59E-02 < 16.0 (Y) Y MAXIMUM ORGAN DOSE (mrem) c INFT/ THYR / HYPO 1.01E-02 (31D)-
INFT/ THYR / HYPO 1.01E-02
-INFT/ THYR / HYPO 1.01E-02 <
6.0 (Q) Y INFT/ THYR / HYPO 1.30E-02 < 12.0 (Y) Y r
ja:
ISOTOPIC IDENTIFICATION
['
l I
i Il
.. ~
mTrs enent v g'
l oft. 3ef [
' g
,.Icatopa Conc 3ntration(uCi/ml)'
Curios I-131' 2.24E-08:
'1.51E-05 i
!l:'.RB-88 1=.89E 1.28E-03 sMN-54.
~2.19E-08.
1.48E-05 Li
'H-3 3.40E-04 2.29E-01 1
- I-TOTALS" 3.42E-04 2.31E-01 a
'I
[
l s
y I
I I
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P I
3 43
~
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s
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i
m r tmvo r - v hye. {c f Y RANCHO-SECO-SscrCm3nto fluniciphl Utility District NASEOUS_ EVALUATION REPORT 24-aug-1989 12:51:14-
\\...............................................................................
I PART DATA-B....f I:J Parmit$-
0-ABNORMAL RELEASE ODCM EVALUATION (NOBLE GASES)
- Source of Release 20 MISCELLANEOUS GASEOUS RELEASE Di 15 ATMOSPHERE I
ocharge; Point R31 case' Flow rate 1.00E+03 CFM Volume 3.01E+10 cc Maximum Flow Rate Allowed Due to Dose Rates 1.00E+03 CFM IRolcaseStart/ Time Scaple Date/ Time 01-jul-1988 00:00:00
.R310ase:Stop/ Time 01-jul-1988 01:00:00 Technician ML I.....
Part II:. CALCULATIONAL RESULTS Maximum MPC Fraction 9' Exclusion Area Boundary 1.6614E-01 DOSE RATE CALCULATIONS (10CFR20)
T-Body Skin Organ IR310ase#-
Dose Rate Dose Rate Dose Rate mrem /yr mrem /yr arem/yr-This Release 2.83E+01 5.07E+01 0.00E+00-(ADLT/ BONE)
.ALL RELEASES 2.83E+01<( 400.0) 5.07E+01<(2400.0) O.00E+00<(1200.0)
DOSE CALCULATIONS (10CFR50 APP I)
Cumulative BThisRelease GAMMA AIR DOSE (mrad) 5.72E-02'.
(31D) 5.72E-02 5.72E-02 <
4.0 (Q);Y 6.26E-02 <
8.0 (Y) Y BETA AIR DOSE.(mrad) 4.19E-02 (31D)
B4.19E-02 4.19E- 02 <
8.0 (Q) Y 5.78E-02'< 16.0 (Y) Y MAXIMUM ORGAN DOSE (arem)
-ADLT/ BONE / SITE 0.00E+00 CHLD/GTRC/ HYPO 0.00E+00 (31D)
~INFT/ THYR / HYPO
-0.00E+00 <
6.0 (Q) Y INFT/ THYR / HYPO 3.01E-03 < 12.0 (Y)
Y-E............................................................-...................
ISOTOPIC IDENTIFICATION
-I otope Concentration (uCi/ml Curi s I
8
g
" '~ ' " ''.
l 'f..
Aye 2.cf f
'XE-1350 1.00E-04 3.01E+00 XE-135M' 1.00E-04 3.01E+00-I 'XE-133' 1.00E-04' 3.01E+00 XE-133M-1.00E-04 3.01E+00 KR-88E 1.00E-04
- 3.01E+00 I;LER-85M' KR.1.00E 3.015t00 1.00E-04'
-3.01E+00 h
' TOTALS
- 7.00E-04 2.11E+01 t
'I.
1 ij 8
I' 1
l l _.
I I
II:
i I
eg!
-46.-
m m.
.~_ - _
nel ~.t.n..n u
I cr=Onto Municipsi-Utility District RANCHO'SECO LS
- l 24-aug-1989 14108:55 IGASEOUS' EVALUATION l REPORT PART I:
DATA
- POrnitt 0
ABNORMAL D'tLEASE ODCM EVALUATION (PARTICULAT :S/ IODINES)
Source of-Release 20 MISCELLANEOUS GASEOUS RELEASE Diccharge Point 15 ATMOSPHERE-I case Flow rate-1.00E+03 CFM
.I
~
R31 Volume 6.75E+66 cc
-M2ximum Flow Rate Allowed Due to Dose Rates 1.00E+03 CFM
.g Sample Date/ Time 5 Rolcase_ Start / Time
')1-jul-1988 00:00:00 iR31 case-Stop/ Time J1-jul-1988 01:00:00 Tcchnician ML Part II:
CALCULATIONAL RESULTS
'1
- Maximum MPC Fraction 9 Exclusion Area Boundary 3.8663E-01 l
DOSE RATE CALCULATIONS (10CFR20)
[
T-Body Skin Organ
_Rslease #~
Dose Rate Dose Rate Dose Rate-l mrem /yr _
mrem /yr mrem /yr L
- This Release 0.00E+00 0.00E+00 2.26E+02 - (CHLD/ THYR)
ALL RELEASES-0.00E+00<(-400.0) 0.00E+00<(2400.0) 2.26E+02<(1200.0)
DOSE CALCULATIONS (10CFR50 APP I)
Cumulative-l -
1This Release-GAMMA AIR DOSE (mrad)
'l L
0.00E+00 0.00E+00 (31D) 1
'O.00E+00 <
4.0 (Q) Y
)
45043-03 <
8.0 (Y) Y
]
BETA. AIR DOSE (mrad)
O'.00E+00 0.00E+00 (31D) 0.00E+00 <
8.0
-(Q) Y 1.59E-02 < 16.0 (Y) Y j
4 MAXIMUM ORGAN DOSE (mrem)
INFT/ THYR / HYPO 4.56E-01 INFT/ THYR / HYPO 4.56E-01 (31D)
.INFT/ THYR / HYPO 4.56E-01 <
6.0 (Q) Y INFT/ THYR / HYPO 4.59E-01 < 12.0 (Y) Y z
" ________________________ ISOTOPIC IDENTIFICATION
-Isotope Concentration (uCi/ml)
Curies h
- -. ~
w
....--.;~.---..
~.
nt:..
nen' ig fog 4e/ 7
~i 3 C8-1371
.1.00E-06 6. 7 '. E- 0 4
~
m I-131--
1.00E-06 6.75E-04
- )
1.00E-06 6.75E-04
,gRB-88 6'.75E-04
.q MN-54' 1.00E-06, 4.84E-03; 3.27E+00
^H-3,,
ITOTALS'.4.84E-03 3.27E+00 i
L.;'.................. ------................................----..--..........
r l.
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I 3
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I 9
LI I
r i
4 i
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1