ML19260D361
| ML19260D361 | |
| Person / Time | |
|---|---|
| Site: | Sequoyah |
| Issue date: | 01/31/1980 |
| From: | TENNESSEE VALLEY AUTHORITY |
| To: | |
| Shared Package | |
| ML19260D360 | List: |
| References | |
| NUDOCS 8002080562 | |
| Download: ML19260D361 (11) | |
Text
5 TABLE OT CO:.7E'.75 Introduction i
1.
Caseous Ef fluents 11 1.1 Alarm / Trip Setpoints 1
1.1.1 P.elease Rate Linic Methodology - LCi/s 1
Step 1 1
A.
Noble Cases 2
B.
Iodines and Particulates 5
Step 2 11 1.2 Monthly Dose Calculations 12 1.2.1 Noble Cases 13 en Step 1 13 1
Step 2 15 s
1.2.2 Iodines and Particulates 16 Step 1 16 Step 2 18 1.3 Gaseous Radvaste Treat =ent System Operation 19 1.3.1
System Description
19 1.3.2 Dose Calculations 19 2.
Liquid Effluents 20 2.1 Concentration 20 2.1.1 RI!S Requirencnt 20 2.1.2 Prerclease.'calysis 20 2.1.3 MFC - Sus of the Ratios 20g 2.2 Instru=ent Setpoints 21 800e08o 54 n
.2 This ratio, R, represents how far above or below the guidelines the step 1 calculation was. Multiplying the original source term by R will give release rates that should correspond to the dose licits given above. Step 1 is redone using the adjusted source terms to ensure that this is the case.
Appropriate release rate limits in ACi/s for each nuclide and release point will be provided to plant personnel for use in establishing monitor setpoints.
The setpoint for each gaseous effluent monitor will be established using plant instructions. Release rate limit, principal gamma emitter, geometry, detector ef ficiency and a safety f actor are combined to give an equivaler.t setpoint in counts per minute (cpm). The safety f actor ranges from 0.2 for systems without automatic isolation features and 0.5 for systems with auto-matic isolation features. The physical and technical description, location and identification number for.,each gaseous radiation detector is contained in plant documentation.
1.2 Monthlv Dose Calculations Dose calculatiens will be perferred =onthly to determine co=pliance with specifications 3.11.2.2 and 3.11.2.3.
These specifications require that the dose rate in unrestricted areas due to gaseous ef fluents f rom
~
each reactor at the site shall be licited to the following values:
For noble gases, 1.
During any calendar quarter, 5 erad to air for gaena radiation and 10 nrad to air for beta radiation.
2.
During any calendar year, 10 crad to air for garna radis: ion and 20 crad to air for beta radiation.
For iodincs and particulates,,
1.
During any calendar quarter, 7.5 crem to any organ.
2.
During any calendar year, 15 cre: to any organ.
f.
12a This section of the ODCI describes the ccthodology that vill be used to perform these conthly calculations.
Doses vill first be calculated by a si plified conservative approach (step 1).
If these exceed the specification limits, a more realistic calculation vill be perforced (step 2).
m e
e t
8 4
e e
G e
4 me e
9 4 4
16 3
4 g = air concentration of radionuclide i in sector n Ci/m.
~
~
DFY = gan:ma-to-air dose f actor for radionuclide 1, mead /s per g
3 Ci/m (Table 1.5).
t,= time period considered (1 month, but number of s/mo is variable), s.
For determining the beta dose to air:
D6a " E ki DF6 (1.25) m g
where:
D
= beta dose to air for sector n, mrad.
6a 3
g g = air concentration of radionuclide i in sector n. Ci/m.
DFB = beta to air dose factor for radionuclide 1, mrad /s per f
3 Ci/m.
t, = time period considered (number of seconds in this cionth),
s.
The sector having the highest total dose is then used to check compliance with specification 3.11.2.2.
~ * 's.
1.2.2 Iodines and Particulates Step 1 Doses will be calculated using the methodology described in this step.
If any limits are exceeded, step 2 will be performed.
Equations and assumptions for calculating doses from releases of iodines and particulates are as follows:
Assumptions 1.
Dose is to be calculated for the critical organ, thyroid, and the critical age group, infant.
2.
Exposure pathway considered is milk ingestion.
20 2.
Liquid Ef fluents 2.1 Concentration 2.1.1 RETS Rcquirement Specification 3.11.1.1 of the Radiological Effluent Technical Specifi-cations (RETS) requires that the concentration of radioactive material released at any time from the site to unrestricted areas shall be limited to the Maximum Permissible Concentration (MPC, attached as Appendix 1) specified in 10CFR20, Appendix B, Table 11, Column 2 for nuclides other than dissolved or entrained noble gases.
For dissolved or
~
entrained nobic gases, the concentration shall be limited to 2x10 " pCi/mi total activity. To ensure compliance, the following approach will be used for each release.
2.1.2 Prcrcicase Analysis Most tanks will be recirculated through two volume changes prior to sampling to ensure that a representative sample is obtained. Because of their size the high crud tanks, non-reclaimable vaste tank, and cask decontamination tank will not necessarily be recirculated through two volumes. An appropriate recirculation time for these tanks will be deter-mined by a one time test. The tank will be recirculated and periodically sampled for suspended particulates during the test. The appropriate recirculation time will be the time that the suspended particulate concentration reaches steady state. The condensate demineralizer waste evaporator blowdown tank cannot be recirculated. However the contents of the tank will be under administrative control and could be transferred to the distillate tanks prior to release.
- t
20a Prior to release a grab sampic will be analyzed for each release point for the concentration of each radionuclide.
n C) =
C (2.1) g where:
11 C) = total concentration in the liquid effluent at release point j, UCi/ml.
C = concentration of radionuclide 1, UCi/ml.
2.1.3 MI'C-Sum of ' the Ratios The sum of the ratios (R ) for cach release point will be calculated by the following relationship.
A 11 i
R (2.2)
+
n
= 5'C E+*+E
- + m' C A
B i
n e
g e~
1;.
22 The setpoint for each liquid effluent monitor will be established using plant instructions. Concentration, flow rate, dilution, principal gamma emitter, geometry and detector efficiency are combined to give an equivalent setpoint in counts per minute (cpm). The I hysical and technical description. location and identification number for each liquid effluent radiation detector is contained in plant documentation.
The respective alarm / trip setpoints at cach release point will be set such that the, sum of the ratios at cach point, as calculated by Equation 2.2, vill not be exceeded. The R is directly related to the total concentration calculated by Equation 2.1.
An increase in the concentra-tion would indicate an increase in the respcetive R, A large increase would cause the limits specified in Section 2.1.1 to be exceeded. The minimum alarm / trip setpoint value is equal to the relcase concentration, but for case of operation it may be desired that the setpo:nt(s) be set above the effluent concentration (C ).
That is,
= b) x C (2.4)
S or S
=1 b
J c
3 where:
S = desired alarm / trip setpoint at release point J.
b = scaling factor to prevent alarms / trips due to variations in the effluent concentrations at release point J.
C = total concentration in the liquid effluent at relcase j
point j specified by Equation 2.1, pCi/ml.
l-
22a The R used in Equation 2.3 must also be scaled by the corresponding scale factor.
Equation 2.3 and the corresponding alarm /t rip setpoints become f
(b x R )-1
+f (b x R )-1
+ [3 (b) x R )-1
+f (b xR) y 2
, 2 y
3 4
4 4
-1
<r (2.5) 5 1
b
= {1 (2.6) y S
b2" (2*7) 2 S
b) = J (2.8)
C3 S
b4ed (2.9) c4 9
e
/-
a
~
p Q p e-.
f
_ DOSE CO.TtITMENT AND FISH CONCENTRATION FACTORS Nkd@' O wa
+
rJUCL I OE HACICLO.
BICLOGICAI EFCECTlvE Hur' Ars IJO SE C0"MiT4ENT FaCrocs (REM /tsCI)
FISr HALF-LIFE HALF-LIFE MALr/ LIFE CONCEhTPATION FACT.
(CAYS)
(DAYS)
(DAYS)
BUNE CI IQaCT Infa LLO T01 At,_8MDY STWLE 4 AD_LQLC.
t- - 3 4.49E.03 1.00t+01 9.9dE+uh 9.7/E-ut___ l.9.5E-o*
._1_.__0._5.E_0 4 1.0tE-os l_ DOR 10 1._Q 0 E._0.0 0
C-14 2.0SE+06 1.00t+01 1.00E.01 e.d*E-03 5.6M-u*
5.enE-04 S. 6 r E - b.
4.SSF+03-4.55E+03 3
f.A-24 6.33E-01 1.10E+01 5._9 Ct-ul
.70E-93 1.yor-03 1.70E-n3
_1_._7 n E - o l 1._20E+02 1.00E+02 P-32 1.43t+01 2.57t+u2 1.35E+ul 1.93t-01 2.llE-02 7.47t-03
- 1. 4 + F -(> 3 1.00E+05 1.00E+0S n-*0 4.60E+11 S.60E.01
- 5. DOE +ol 3.456-Od 0.9 3._4_5 r' - L1 2 _ ___ 3 4 6 f - 1 E2
?_. h p E i O J _ __ 2. 1 0 E + 0 3 CR-bl 2.79E+01 6.16E+u2 2.6eE+01 3.21c-06 c.ME-04 1.59E-06 2.6eE-uo 2.00E+02 2.00E+02 Mr-54 3.03E+02 1.70E+01 1.$1E.01 r_*. e.3 E - u. _. _1. u u E _0 2 at. d d-114 P. 12E.04 4. 0.0 E.ifl2_
4. 0.0 Ef _0 2 MN-56 1.07E-01 1.70E+01 1.uoE-ul 2.06E-uS
- 3. 6 /E-0 3 c.06E-05 2.06E-65 4.00E+02 4.00E+02 FF-55 9.50E+02 d.00E+02 4.1*E+02
?.75t-u3 1.09F-0 8 2._7_4_t-04 4.43E-04 1.J10E 02 1.00E+0?
FE-59 4.56t+01 6.00t+u2 6.31E+ul 4.34E-u3 3.
uE-02 2.dlE-0J 3.91E-03 1.00E+02 1.00E+02 CO-58 7.13E+01 9.50E*00 9.3dE.00 1.e9E-u3 1.51F-02
_L.M E-0)
{. 6]f - 0 3 5._0_0E.p_1 2m0dE101 CG-n0 1.92E+03 9.50t+00 4.45E+00 4.73E-u3 4.0cE-02 4.73E-03 6.72t-u3 5.00E+01 4.75E+01 N I 6_5__
l.07E-01 6.67t+02 l_. 0 7 E - 01
- 5. 2 e t.- 0 4 1.74E_12.
3 2/F-05
- 1. LJf - 0 5 L. 0 0 E10 2. _1. 0.0 E +_02 CL-64 5.31E-01 P.
00E+01 5.27E-ul 3.91t-uS 7.10E-03 3.91r.-05 3.91E-05 S.00E 01 S.00E-01 ZA-65 2.45E+02 9.33E+02 1.c4E+02 4.84E-03 9.70E-O' 7.13E-n3 6.9AE-03 2.00r+03 1. '+ P E + 0 3 Zrs-69u o.75E-01 9.33E+02 5.75E-01 1.55E-Oe 2.ilE-03 3.e*E-02 3.64E-05 2.00E+03 1.14E+01 ZA-69 3.SeE-02 9.33E+02 3.9eE-u2
- 1. 0 E-u :
- 2. 9eE 16 l _t3 7_F,- 0,6
_1_. 3_7_E - o e 2.._0._UE+_Q_3 7._9 2E _01, 8F-H2 1.*8E*00 e.00t+00 1.25E+ue d.2ct-03 2.osE u2 2.2eE-0*
2.2eE-03 4.20E+02 6.20E+0?
E"-83 1.00E-01 P.00E*00 9.dFE-u2 3.S5E-u5 S.74F-49
- .55E-05 4.0;E-uS 4._R0E1Q2 e.10E_02 66-84 2.21E-02 5.00t+00
- 2. 2 :.E- 0 2 c.'s*t-ut 4.09E-10 e.04E-05 5.21E-05 4.20E.02 4.20E+02 E L.~ 5 2.0Pt-03 A.00E+00 W.0cd-93
'. 1 7 E - d '/
1.cor-21 5.17E-01 P.I.E-06 4.20c+02 4.20E+02 KF e39 7.75E-02 1. 0 0 c +.. o
- 7. I' E-u2 0.0 1.4c5-64 0.0 0.0 1 00E*00 1.00E+00 Ki-r*5F 1.d3E-01 1.00E.00 1.55E-01 0.0 4 30E-03 0.0 0.0
- 1. 0 0 E + 0 0___1..fl 0 E.+ 0.0 KF 3.93t+03 1 00E+uo 1.00E+uo 6.0 a.c2E-02 c.0 0.0 1 00E+00 1.00E 00 4 0 - % __
l.87E+01
- .50E+01 1.32E+vl s.e32-u3
- .leF-03
%. t* 3 - - 0 3 9.FlE-03 R._0_0.E + 0_3._ ___ 2. 0 0 E + 0 3 HE-93 1.24E-02 4.t0E+01 1.26t-u2 3.36t-05 e.stE-It
!.3-t-05 3.21E-uS 2.00E.03 2.00t+03 GE-69 1.07E-02 6.50E*01 1.072-02 2. e b t' - u S 2.33E-l'
- c. woe-es
?.92E-05 2.00F 03 2.00E+03 5A-H9 5.21E+01 1.30E+04 S.2SE 01 3.06t-J1 4.C*F-u2 9.22t-u3 8.94f-03 3.00E.01 1.04E+01 SF-oo 1.01E+04_
l.30E+u4 5.oeE.03 7.ScE+uo 2.lsc-cl 1.76E+00 1.eek.+00 3. 0 0 g._0.1. ___d 4 LEL+ A1.
SF-91 4.03E-01 1.30t+04 4.03E-01 S.e/E-u3 2.7CE-02 1.92t-0*
2.29E-04 3.00E+01 1.POE-01 Sle-42 1.13E-01 1.30E 04 1.13E-ul 2.15E-03 4. 2 t.f _0 2 6.6_t-OS 9 t22E-od 3._Q_qE. p.1 3_m.19 E _0 2.
SP-93 5.StE-03 1.30E+04 5.56E-u3 6.39E-uS 1.69E-03 H.90E-06 9.90E-06 3.00E+01
-1.67E-03 6
I TABLE 2.1 (Continu d)
_ _ DOSE CO.TIITMENT AND FISH CONCENTRATION FACTORS _
PJUCL I DE HACICLO.
B I CL O6 I C al.
EFFECilvE Hur1 ArJ UO5E C0'miT9ENT FACT 005 (AEtuoCII FISH HALF-LIFE HALF-LIFE HALr/ LIFE CONCENTPATION FACT.
(DAYS)
(OAYS)
(DAYSI BufiC GI IQACT TnvACIO T O TAL_3fLO Y S T 9LF;
_4AD1QLQ.
Y-00 2.67E+90 1.*0t>u*
?.t7E 00 4.c2E-oe 1.0cE-01 2.c 7E-0 7
- 7.5-E-07 P.50E+01 2.10F+P1 Y - 9 1r>
.3..7t-02 1.40t.96 3.-(L-u 4.09t-06 2.t7E-07 4.7?t-Os 3.52E-09 2.50E+01 2.50E+01 1-s1 5.59E 01
- 1. 4 0 r. + 0 4 5.nt-E+vl 1.*16.-u*
7.76E-02 3.eet-De 3.77E-vo R. iQ c +Ji l ____2,_5 0 Ez01 Y-42
- 1. - 7 t' - 01 1.~ot+0*
1.-IE-ol c.-tr-07 1.*eE-a2 c.47t-04 2.4/E-06 2.50E+01 2.50E+01 l'-45 6.55L ol 6.50F.+02,_
4.2sE-ol
- 2. m.-oe
,e.SOE_-02 5.flK 0a 7. 4 n F - O e ___ _. 2. 5 0 f t 0.l____2...c 0 E t.il l 1-73 4. c ^. r - 01 1.4uL+o4 c.3'E-0e 6. c) D E - O *-
3.33E.00 3.33E.00 5.(2E.ul 3.04r.-05 3.05F-OF 2'-47 7.98E-01
%. cot +o2
/.o?E-ul 1.6df-Je 1.utE-01
- 1. L5f - a l_
_1_.fif
'8 7 3 d3 c. 0 0 3.33F+00
'r-75*
.s. / ct.40 7.eul+02 3.73t+00
- 5. net-u7 3. :: 5 E - 0 2 c.e*E-07
- 7. Set-u7 3.00E+04 3.00E 04 tw-4S 3.54E.01 7.60E*02 3.35t+u) e.22t-06 2.10E-02 l_._f31 _0 e
_J _. 4 E - M 3.00Elo_4 3.00E*_04 M -97 5.00t-0 7. e G r.+ 0 c 5.00E-uc 4.90t-u8 2.10E-03 9.e')t-Os
- 4. oat -u 7 3.00t+04 3.00E+04 vo-99 2. 7 6 E. 0 0_
<.oeE+on 1.7sE+00 e. 4 7 t; - 0
- 9. %J - 0 3 c. 7 E _Q2 9.P_0E-u*
1.0_0E10.1 1..QQE +.01 TC-99*
2.52E-01 1.00E+0C 2.01E-ul 2.47E-67 4.13E-04 4.37E-06 e.95E-06 1.50E+01 1.50E+01 iC-44 7.7-E.07 1.00E+00 1.uoE+ue
- 1. 2 7F -04 1.f4F-02
- .6ef-05 9.04E-OS 1.c0F+01 1.50F 01 TC-101 s.93t-03 1.00E+00 9.93E-u3 2.5% -07 1.iUE-la 3.60t-0e 3.59E-06 1.50E+01 1.5uE+01 40-103 3.96E+01 7.30E+00
'a.lcE*00 1.btr-u4 2.loE-02 7.GeF-OS 7.HE-v5 l_.10_f _0_1 l_.3_0 E + 01 CL-106 3. t t*t + 0 2 7.30L+00 1.16E u0 2.73E-03 1.7eE-01 3.SOE-04 3.46E-04 1.00E+01 1.00E*01 FF103" 3.96t-02 7.30L+u0 3.74E-02 1.e7E-07
- 1. P l f,_- o 4 4. 9 4 E - o ra 4,CCE -08 1..r_0E19_1 l.00E101 at110" 2.:3E+02 5.00E+oO 4.soE+uu
- 1. cat-u-e.t..E-02 c.7eE-05 H.79E-o5 2.00E+00 2.00E+00
. S :- - 1 2 4 c.02E.01
?.90E+ul 2.33E+0 e.. sui-u3 7.35F-0?
- .72E-a6 1_. I I E - 0 3 1.30F+00 1.00F+00 Si - 125 5.9eE.a2
?.eot.nl 3.deE+ul 1./cE-u3 1.97E-02 1.e2F-Oc 4.2.E-us 1 00F+00 1.00E.00 TE125*
- 5. dot.01 1.SOE+ol 1.15E+ul
- 2. cot-03 1. 0 7 c - n 2 _, _ e. 0 e t __0
- 3.. iG E - 0 4 4.
0 0 E 1.0 2
- 4.. 0 0E2.02.
I t 12 7 t' l.0%+02 1.50t+bt 1.ht+vl
- 6. 7 /E -o 3 2.<7.'-02 1.73F-0; e.45E-u4 4.uuE+02 4.00E+02 IF-127 3.s2E-01 1.buE+ol 3. ia ? E - u l 1.10t -0 e. c e E d L3_ ____c.. l A t -Jn.5
- 2. 3 *E_ _95 4.
0 0 E10 2__.___'e m0Il O_0 2.
Ti1/9*
3.etE.ol 1.50t+ul 1.0*E+ul 1.ldt-02 m.74E-02
..4ct-03
- 1. dst-03 4.00F+02 4.00E+02 TF-129
- .77t-02 l'.50t+01 4. 7 t r. - 0 2 s.let-05 2.3/E-05 2.41E-05 7.ett-do 4.00E+02 4.00E+02 TFl'lv 1.2SE.00 1.50t*01 1.15d 00 1.7Jt-vJ e.40E-02 1.1-E-03 7.0SE-u*
- .00E+02 4.00E+02
.It-131 1.12E-02 j.. _t e t y.u l.
- 1. _7 k E - 0 2___ 1. vj t - u : _ _. 2. 7 s_E - n_. _i. e 2 t _0.:
6_. 2 LF - 0A_ ___6. 0 0.E 92 4.3uE+02 It-137 3.ist.qc 1.50E*01
.ceE.uu 2.52E-u3 7.71E-02 a.e0E-03 1.53t-03 4.00E+02 4.00E+02 it-134 2.42E-02
- 1. d GA +.91
_.2.S I E - 9 2___.. c.10 E - 0 5. _
ed. s 3 E.- 0 S_ _ _2. 0 0 t - 0 3.. _1. 52E _do 4.00E102 A.00Es0P_
l-12C e.21E.0G 1.3et+02 1.3rE+02 3.20E-u3 0.0 s.61t+00 1.24f-02 S.00E*01 S.00E.01 1-130 5.17F-01
%.17t-ol 2.5%-ul 7.Sec-us l_.ic E - 0 1..f,,_iE-n1
(._60v-04 5.00c.01 1 10F.01 1-131
- 6. 0St. 0 0 1.36t+u2
/.olt+uO 6
let-03 1.5/E-03 1.*5E+0u 3.41E-03 5.00E+Cl 4.4SE+01
- t. 2 0 D _0_Q.
1-132 v.42E-02 1.37t+o2 9.41E-ud
- 2. 0JE -u4
_1.0cf.-o4_
_].. Sot-0.2
_1.S_0E-04 5_,.QOF+01 4
1-133 6. 4 *- t - 0 1
- 1. 3 rit+o2 9.*lE-ul 1.42t-03 c.c2E-03 3.6 sE-01 7.53E-04 5.00E+01 2.29E.01 1-134 3.clE-02
- 1. 3 t'E + 0 2 3.61E-02 l_._u o E - 0 4 2.All-Q7 4._4 9E - 0 3 1.03c-us S._aQF+01 1..L E.00 1-135 2T7eE-01 1.38E+02 2.77E-ul 4.*3E-04 1.31E-03 7.6SE-02 4.2aE-04 5.00E+01 1.09E.01 J
Gu
.=2
TABLE 2.1 (Continued)
DOSE C01DtIT'fENT AND FISH CONCENTRATION FACTORS rauCL I DE RACICLO.
BICLOh! Cat EFFECilvE HurprJ UO5E t' 0 " M I T ** E N T F3CTOos ( A (g n J C,,I l F I s r.
HALF-LIFE HALF-LIFE nAlr/ LIFE CONCEN TP A T IOF. FACT.
(Cars)
(OAFS)
(DAYS)
BOtJE GI IQACT T r* v r70,LQ T C._T_e L__ 9 0 0 Y _ _ _ S l 3 E L F Q alLQLC.
x F 17 3 Pe 2.2%.00 1.UOt+00 6.UE-ol re. 0 2 a9E ;.,n 9.S 1.atlE.+_0_0 1-laE-06 2
XE-133 5.27E+0c 1.0ut+00 t.-lE-ul 0.0 2.5cE-c2 e.0 0.0 1.00E 00 1.60E+00 a E 125t>
l.CFE-02 1.00E+00 1.utt-ud u.0 3.24_E-0.,4.__
u.0 0._0
_L._0AEf_00_____1..0_QE2.0a XE-135 3.53E-01 1.00E*00 2.77E-ul 0.0 1.00E-Oc a.0 n.0 1.00E+00 1.00E+60 CS-134 7.47E+02 7.00E+ul 6. -1E,.2_u_1 e. 22. - 0_L2 2._5.9E.-03 1.2pt-01 1_. 21 E _11 2a 0.0F + 0 3 2.00E203 CS-135 1.10E+u9 1.15E+02 1.1:E+ur 1.96E-02 0.0 e.06E-03 9.06E-u3 2.00E+03 2.00E.03 C5-ll6 1.37E+0},
7.00E+ul 1 15E.ul e.11,E-03
[._w d _p }
.c,.AR -02
- 1. ;4 S F - 0 2
- 2. 0_0 E 0 3 1.%F+03 C5-137 1.10E+p4
,00t+01 c.scE+01 7.97E-02 2.llE-03 7.2dE-02 7.14E-02 2.00E+03 2.00E+03 C5-13H 2 2*E-02 7.00E+01 2.24E-o2 5.o2E-ud
- . *- Sf - 1 0
- 5. 7 2E -o S
% 4 0E-u5 2.,_0.1Ef_iO_
4.JaE+01 ac-134 5.76t-02 6.S0t+01 5.75E-02 i.70E-ut 1.7cE-C4 3.07E-oe 2.84E-06 4.00E+00 4.00E+00
'e-160 1.2AF-01 6.SOE+ul 1.07E+01 2. 0 3_d _u e 4. l c E - Oi_
- 1. 2.3.E _u j 1.JJi _it3 4_._0.0 E +3LO
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