ML20154J581
| ML20154J581 | |
| Person / Time | |
|---|---|
| Site: | La Crosse File:Dairyland Power Cooperative icon.png |
| Issue date: | 11/17/1976 |
| From: | Madgett J DAIRYLAND POWER COOPERATIVE |
| To: | Reid R Office of Nuclear Reactor Regulation |
| Shared Package | |
| ML20154E750 | List: |
| References | |
| LAC-4339, NUDOCS 8805270058 | |
| Download: ML20154J581 (62) | |
Text
I n.sIIt YLsNn vn West ConPKItas TIVE '
\W Jih g Sg Bs Gmw, 0% min l $4601 d November 17, 1976
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t- k In reply please refer to LAC- 4339 y V DOCKET No. 50-409 Director of Nuclear Reactor Regulation ATTN: Mr. Robert W. Reid, Chief Operating Reactors Branch No. 4 Division of Reactor Licensing U.S. Nuclear Regulatory Commission Washington, D. C. 20555
SUBJECT:
DAIRYLAND POWER COOPERATIVE LA CROSSE BOILING WATER REACTOR (LACBWR)
PROVISIONAL OPERATING LICENSE NO. DPR-45 INFORMATION TO MEET REQUIREMENTS OF SEC. V.B.
j OF APPENDIX I TO 10 CFR 50. _
RE: Letter, Reid to Madgett, dated September 15, 1976 l
Dear Mr. Peid:
Enclosed is the additional information which you requested in your letter of Saptember 15, 1976 and as agreed upon with your staff. The information is being provided to meet the require-monts of Section V.B. of Appendix I to 10 CFR 50.
1 The information is complete with the exception of item 3 of Enclosure 1 concerning estimates of relative concentration (@Q), :
deposition (D/Q) , meteorology and dispersion todels. Since the !;
meteorology at the LACBWR site is affected by unusual topography as far as a nuclear plant site is concerned, Dairyland is review- !
ing available meteorology and developing a realistic dispersion i model to fit our case. This is being accomplished by outside '
consulta. tion as well as our own staff. We expect this review of item 3 of Enclosure 1 will be completed and submitted by December 15, 1976. 1 If there are any questions concerning the material submitted, please contact us.
Very truly yours, 70050 080516 m vmW r ND POWER COOPERATIVE s
kP AD0;K 050 g 9 q_ _
X '
Joh P. Madget ns"al Managet cc: J/ . Keppler, Reg. Dir. , NRC-DRO III 11976 1
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- 1. Your response to item 1 of Enclosuro 2 (NRC letter dated February 18, 1976, R. Reid to J. Madgntt) was not adeJuato since the informa~
tion provided lacked clarity, speci fi ci t y , and completeness. For example, the release point description for the ventilation and exhaust systems (sate and shape of flow orifice, height above grado, flow velocity, etc.) could not be located in the documents referenced in your letter dated June 3, 1976 (J . Madgett to R. Reid). provide a detailed response, as described above, to item 1 of Enclosure 2 of our February 18, 1976 letter.
- 1. General
- a. The maximum core hermal power (MWt) ovaluated for safety considerations in he SAR. (Notes all of the following responses should be adjusted to this power invel.)
The La Crosse Boiling Water Reactor (LACBWR) is rated at 165 MWt in the SAR.
- b. 1) The total mass (1hs) of uranium and plutonium in an equilibrium core (metal wcight).
The weight of Uranium in an equilibrium core is 8600 kg.
The weight of Plutonium in an equilibrium core is 24 kg.
- 2) The percent enrichmont of uranium in reload fuol.
The percent enrichment of Uranium in the reload fuel is 3.7t.
- 3) The percent a fisallo plutonian in reload fuel.
The percent of fissile Plutonium in reload fuel is zero.
- c. If methods and parameters used in astima ting the source terms in the primaty coolant are different from those given in Rejulatory Guide 1.CC, describe in detail the methods
.s n d parameters used. Include the following information Since LACBWR has been operating for 9 years we have no need for estimating source term information but would base our evaluation on actual release data.
- 1) Plant capacit; tactor.
The actual plant capacity factors over a ten year period are shown below. The average plant capacity factor at the 95%
confidence level for 1970-76 is 53.1 + 26.8%. Thus, the upper limit for the plant capacity factor is 79.9%.
1967 0 1970 42.6 3973 1968 46.1 0 1971 43.7 1974 79.2 1969 0 1972 54.6 1975 62.6 1976 4 3. 2 Est.
- 2) I s o t o;, i e tvl case rstes or noble gases to the reactor coolant at 30-minutos Jecay (uC1/sec).
( __ ______ _ _ . _ _ _ _ >
The actual measured release of noble gases is shown in the Radioactive Effluent Report and Environmental Monitoring Report for the years 1973 - July of 1976. Attached are copies of the pertinent pages for comparison.
- 3) Concentrations of fission, corrosion, and activation products in the reactor coolant (uC1/gn) . Provide the bases for the valucs used.
The actual measured concentration of fission, corrosion and acti-vation products at full power is shown in Table I.
d.
The quantity of tritium released in liquid and gaseous efflu-ents (Ci/yr/ reactor).
The average quantity of tritium released in liquid and gaseous effluents is 116.49 and 28.01 Ci/yr respectively. This average release is based on 4 years of data as shown in the Ef fluent and Environmental Monitoring Report 1972-75.
Ci/yr Gaseous Liquids 1972 26.47 1973 120.84 50.60 103.22 1974 18.26 1975 115.22 16.72 126.68 Averago 28.01 116.49
- 2. Nuclear Stean Supp1y S y s t u r;
- a. Tota 2 stean flow rate (1bs/ht).
The total steam flow rate is 611,500 lb/hr.
b.
Mass vessel of atreactor coolant (1bs) and secan (1bs) in the reactor full posar.
The mass of the reactor ecolant of water and 2,753 pounds of stean.in the reactor is 62,500 pounds
- 3. hen: tor Coolant Cleanup 9ystem
- a. Average flow rate (Ibs/hr).
The average flow rate is 20,000 lbs/hr.
7
( ..
lable f PRIMARY Pllitj flCAT ieri INTLUCHT r
Sample i San,p l e 2 Sample 3 Sarnple 4 Sample 5 Isotope 3-2 / /5 4-3 /s 7-2p?4 9 4-75 _
12-4 75 133 Xe 2.11x10') 3 28x10'1 9 76x10 1.60x10-3 9 15x10-4
$7to g ,3 73 ;o- 3 g , gg g g g o, ... g,ggxto 4 5.71x10-5 S9mic 4. 56 x 10' ) 3 38xio-2 ---
1.53x10-3 2.05xio-2 suKr 2.24x10** 2.05x10'4 --- ---
1 50x10'4 f 13988 8.54x10'3 1.62x10-2 3,95xio-3 9 32x10-3 1.01x10-2 20Ke 3 37x10'4 1.64x10-2 ..-
6.79410*4 3.24x10-4 i
! I33*Ae 3.83x10'2 5.08x10'3 ---
1.18x10-2 1.16x10-2
- 24Ra 7.10x10~3 1.12x10-2 ... .--
9 75x10-3 I3k Xc 6,31x10'3 1.24x10'3 3.15x10'3 1.65xto-3 1 98x10-3 i; 2 3 Np 2.64xic-? 4.72x10'2 2.83x10') 3.99x10-3 4.06x10'3
'I' Cr 8.21410') 8.97x10-3 1.39410') 4.84x10'3 3 06x10'3 i I3I I 1.67 10-2 8.40x10'3 1.34x10 2 g,34xto 4 9.55x10'3
- l 67 Kr 1, $ 5x l 0- 4 5.13s i g- 3 1,26,10-3 1.57x10-3 1.24x10'3 1255b 3.52x10*J 1.40x10'3 3.10x10'l 3.03x10*3 2.41x10*3 !
IO2Rh 4.10x10*" 7.35x10 ' 4.5i 10'4 ---
8.94x10'4 i
j I33 1 3.0610~2 1. 61 x 10 ' ' 2.25x10'2 5.39x10'1 1.11 x 10 - 2 I"
00 6,61x10 1.23 10-2 ---
2.63x10"3 1.79x10~3 4
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PR LMARY PUR I F I CAT I 0tt INFLUII)T - (cont'd],
Sample i Sample ? Seple 3 ,s ample 4_ $,,pi, g l j isotope 3-27-75 's - 3 + / ; 7-26-74 9 l-75 i 12-4-75 56Mn 1.27x10'2 4 3Bx106 2 32x10' 2 3.43x10'2 3.00x10-2 l
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2.5Gx10'I 7.09x10'2 24 tla 6.16x10'4 2.43s10 "' 3.96x10'4 ---
6.92x10"'
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RADIOACTIVE EFFLUENT REPORT and ENVIRONME!1TAL mot 11TORIt1C REPORT of T!!E LA CROSSE DOILING MATER REACTOR from January 1, 1973 to December 31, 1973 DAIRYLAND POWER COOPERATIVE Docket tio. 50-409 M
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.23 0.0540 0.0C27 C.0004 C.0303 7.;;79 0.6046 ac.CD39 0.0063 C.0253 0.0125 0.02:1
.;L *: C012 <0.0013 <0.C010 40.0c10 0. C'J4 C 0.0C36 0.1767
- . 0010 -0.05 0 C.0010 <G.CC1C C.C139 C.C047 <c.CC10 <C.C;10 Ce b s <0.0010 <C.0010 <0.0010 <0.0010 ac.043?
<0.0C10 40.f";0 <C.CC10 tr v <C.CC10 <C.r:20
/. .'!
. 14.6 23.3 C 0 C1 3:4.7 7;a.5 1207.4 0 0 D 0 0 7: ' C C 6.6 0 0; ;
. /,7. 2 s075.2 4Ps4.9 4.5 3 5.5 571.0 5: 4.0 66.1 r.'
- 5.9 1236.5 0 0 1!.2 1C9.9 f,51.1 1205.4 17;0.C C.4 4:If.+
19C3.2 C 0 7.3 130.6 6.6 13. :: .1 rr i .7 E 4 6. 5 1142.8 21'7.4 144.5 TE7.9 1452.5 2117.5 7,-;:3 J 0 0 7.9 24.7 1E3.9 9.C S:04.!
IM6.C 1359.5 2103.9 241.6 447.3 649.4 51.3 1.3 r= ' ' 'n 2577.3 0 0 8.0 754.0 1973.1 3656.4 5751.2
& ;21 2057.8 3275.5 0 0 12.2 53C8.3 423.5 60.5 17.125.2 3153.9 2411.4 3838.4 201.1 1111.2 3352.9 4267.7 358.4 Er-127 0 0 14.3 11.6 1470.1 19.1 15.563.2 647.6 426.7 679.2 u 2721.4 3951.0 315.2 6.7 Crr.:rs as a;Srg riaa Is;<cify)Y.ellb C 207.6 171.3 O 2.5 377.1 522.9 9C8.0 1405.4 112.1 0 17,570.0 Jaa. .:.: 2o.cr. Avera;c.W 155 138 C C Q.6 1.4 0 0 C 5141.7 153 C 0 5 C 0 250.9 75 147 113 129 10 12 73
- 2as 4 cn ;.nrucu .ates wta > 8"dry En1f.11%s. aas rot on total paru viates as a nm in Wn 3.
Dar.rtrrer.tal Sa-des for Perico - War 56, Aar 172, stat 13, TID 80, Alk 42. Fim 25 4
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- m, RADIOACTIVE EPPLUENT REPORT and ENVIRONMENTAL MONITORING REPORT of
'tHE LA CROSSE BOII.ING WATER REACTOR frcm s.
January 1, 1974 - December 31, 1974
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DAIRYLAND POWER COOPERATIVE Docket No. 50-409 ed 1
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APPENDIX A RO) ORT L. RADIOACTIVE EFFLUENTS La Crosse Bolling Vafer Reactor Facility Dairyland Power Cooperative Docket __ SG-409 Year 1974 I. L10UID PELEASES
- 1. Units Jan. Feb. Mar. Apr.
Gross Radioactivity (p,,) May June a) Total celeasu Curies I.86 0.30 1.09 0.51 b) Averaae concentration released uC1/nl 1.43x10-' 1.75 0.9E
- 2. 3 0 x 10-
- 6.71x10-* 2.54x10-* 9.41x10-' 3.31x10-'
- 2. c) Maximum concentration released LCi/ml 9.62x10-' 6.64x10-7 3.4x10 ' 8.08x10-# 2.44x10-'
Tritium 1.92x10-'
a) Total releas? Curies 5.58 8.07 b) Average concentration relcat ed sci /n1 11.01 12.01 3.85 6.63x10 ' 5.07
- 3. D:ssolved noble gases 4.29x10 6.79x10 ' 5.98x10 ' 2.0?x10 ' l.75xlG '
a) Total release Curles 0.00? <0.002 (0.003 b) Average concentration released aci/ml <0.002 2.3x10 < l . 5 3 x10 - ' ' < l . 8 5 x 10' * * <1.0x10-*
<0.002 <0.002
- 4. Gross Alpha RTdloactivity < l . 0 8 x ] C-' ' < 6. 9 x10- ' '
al Total release Curles 2.5x10 ' 3.8x10 '
b) Average co.. centration released LCi/ml 1.92x10 3.29x10 ' 5.1x10 ' 2.02x10 ' 6.17x10 '
- 5. Volume of liquid waste to 2.91x10 2.03x10 2.54x10 1.09xlC ** 2.13x10 *'
1 dise$arge canal Liters 136,127 91,300 152,952 i
- 6. Volum3 of dilation water 117,500 166,800 Liters 2.302x10 1.307x10 l.624x10** 105,55p*
- 7. Isotopes Released Curles 2.0lx10** 1,859x10 2.9x10 Ba+La-140 0,002 0.002 Sr-89 0.003 0.002 0.010
<0.001 <0.001 0.002 0.001 1-131 0.003 0.004
<0.001 <0.001 <0.001 0.009 0.005 0.034 Xe _33 0.001 <0.001 0.018 xe-135 0.002 0.003 <0.001 0.001 <0.001 Cs-137 <0.001 <0.001 <0.001 <0.001 J.095 0.126 <0.001 Cs-134 0.492 0.247 0.186 0.055 0.070 0.112 Co-60 0.256 0.132 0.096 0.067 0.136 0.009 0.006 Co+58 1.457 0.057 0.013 0.056 0.038 Cr-51 0.187 0.042 1.261 0.014 <0.001 0.007 0.679 Mn-54 0.016 0.009 0.011 0.009 2n-65 0.001 0.004 0.001 0.016 0.002 0.006 0.009 0.C06 Sr-90
<0.001 0.004 0.010 0.010 Others (specify) ***I, a- Ce, Co,
<0.001 0.001 <0.001 <0.001 <0.001 0.061 0.024 8Np, "Tc, '*7r, Nb, Mo 0.113 0.051 0.000 0.016 B. Percent of Technical Specification 1 <1 limit for total activity released
- 1 <1 1 <1
- MPC of lx10LC1/ml used in calculating isotoped listed as "oth'ers", based on restrictive. 'I the most 4
. . c. ._. "
APPEN3IE A PIFORT T - RADIGICTItE ETFLCENTS La Crosse Poilirq Water Pe.ctor racility Dalryland Power Cooperative Docket 50-409 Year 1974 I. 1.10*;~3 FILEICES
- 1. Crcss Fadioactivity (3,3) a) Total relcase Curies 0.324 0.276 3.846 1.147 ~' 0.655 b; Iceerage ccccentration released aci/nl 1.19x1G
,, 0.334 13.052 9.49x10 1.50x10 ' 5.10x10 4.25x10 2.47x10 5.37x10
4.61x10"
~
c, .'uxirum concentra:1or. released LC1/cl 8.12x10
- 2. Tritiun 4.27x10 8.13x10 l.43x10 8.31x10 4.27x10
-) Tctal r,_ ;e a s e Curles 13.5 ,, 11.88 .. 8.03 6.07 13.83 15.70 115.22 t; ; eragr can c.tra11on re!cesed LCi/ml 4.96x10 4 ,, ,, , ,,
4.0ex10 3.13x10 2.7x10 6.97x10 1.16x10 4.74x10 '
- 3. 02 ssolved r eble gases a: Total release Curles < 0. 0 02 <0.002 ,,, so.C10 0.034 0.019 <0.002 b; Avera;c cor. centration released aci/.Tl < 7. 3 4 x10
<6.88x10 <3.9x10
. , , ,, ,, , , , 10.083 1.51x10 3.23x10 <1.48x10 3.42x10
- 4. C:c s Alpha r d- activity a: Tct ; reh ase Curles 4.36x10 <2.45x10 3 ,, 4 1.42x10 4.42x10 3.1x10 - <2.13x10 14.1x10 ,
) Average concentratloc released uCi/ml 1.60x10'*' 18.42x10 5.53x10 1.87x10 - ' '
2.01x10 <l.57x10 il.66x10
- 5. V: l u.Ta of 11guld waste to dir:harge car.al Liters 162,850 154,250 218,000 171,400 204,100 143,900
/, 5. vc 2 u_ . cf dilution water Liters 2.724x10,. 2.909x10,, 2.565x10,, 2.249x10,, 1.542x10,, 1.354x10,,1.826,729
<> 7 I.;:ctea .keleased Curies 2.43x10-'
i 2_+_a' 40 . <0.001 -0.001 0.035 0.013 0.008 2r.2) 0.004 r0.032
<0.001 <0.001 0.001 <0.001 <0.001 0.001 00.013 1 131 0.010 0.004 0.281 0.042 xe-;33 0.029 0.035 0.474
<0.001 <0.001 0.009 0.032 0.01E <0.001 <0.068 Et-135 0.001 <0.001 <0.001 0.002 0.003 C2-137 0.001 <0.016 0.064 0.094 0.764 0.268 0.188 0.082 2.718 C3-134 0.033 0.046 0.461 0.165 0.085 Co-60 0.038 1.506 0.019 0.016 0.138 0.038 0.036 0.023 0.528 Co-58 0.175 0.095 1.974 0.518 Cr-51 0.001 0.250 0.119 6.814 0.001 0.004 <0.001 <0.001 0.002 10.061 Mn-54 0.002 <0.001 0.025 0.007 0.005 0.002 10.079 tr-65 0.004 0.003 0.027 0.010 0.003 Sr 0.001 0.096
'7 0
8 !,
<0.001 <0.001 0.001 0.001 0.001 0.001 10.012 Others (specify) Ce, Co, 0.011 0.011 0.125 0.049 8Np, *Tc, Ir, Nb, Mo 0.029 0.024 0.585
- 8. Percent of Technical specification <1 <1 4.5 1 <1 1.1 <1.3 limit for total activity released *
-M.?C of lx10~'LCi/ml used in calc lating isotoped listed as *others', based on assI the most restrictive.
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RADIOACTIVE EFFLUENT REPORT and ENVIRONMENTAL MONITORING REPORT of Tile LA CROSSE BOILING WATER REACTOR I t n in January 1, 1975 - December 31, 1975 DAIRYLAt!D POWI:R COOPERATIVI:
Docket IJo . 50-409 i
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APPENDIX A .
REPORT OF RADIOACTIVE EFFLUENTS La Crosse Boiling Water Reactor Year 1975 Facility Dairyland Power Cooperative Docket 50-409 I. LIQUID RELEASES Mar. Apr. May June Units Jan. Feb.
- 1. Cross Radioactivity (8,Y) 2.445 0.550 1.241 1.634 0.598 a) Total release Curies 1.351 9.9x10-' 1.96x10-' 4.20x10-8 1.28x10-' l.26x10" 2.27x10~*
b) Average concentration released UCi/ml 7.95x10-' 3.7Bx10-* 4.50x10-' 3.51x10-8 1.12x10-' l.03x10*
c) Maximum concentration released UCi/ml
- 2. Tritium 15.60 18.07 15.92 11.27 3.82 a) Total release Curies 16.91 1.24x10-* 1.26x10-8 1.38x10-' 1.65x10-' 8 . 6 9 x10- ' l.45x10-'
b) Average concentration released uCi/ml
- 3. Dissolved noble gases 0.043 0.008 0.019 0.044 0.208 0.011 al Total release Curies 3.15x10-' 6.43x10-2' l.45x10-' 4.54x10-'- 1.6x10~* 4.lBx10 "
l b) Average concentration released uC1/ml Gross Alpha Radioactivity 2.07x10-' 9.37x10-8 7.55x10
- 6.1x10~'
4.
Curies 2.53x10-8 1.04x10-' 9.69x10-'8 5.82x10-** 2.32x10 -t a, a) Total release 1.85x10-18 8.38x10-38 1.58x10- 2 2 b) Average concentration released UCi/ml
- 5. Volume of liquid waste to 126.400 148,700 175,400 341,600 285,200 ~
Liters 142,300 2.633x10
i discharge canal Liters 1.365x1d ' l.245xid ' l.31xld ' 9.67xid 1.297xlC '
0' 6. Volume of dilution water Curies Y 7. Isotopes Released "
0.017 0.009 '0.001
< 0.003 <0.001 Ba+La-140 0.008 <0.001 0.003 <0.001 0.006 0.004 <0.001 Sr-89 0.011 0.285 0.362 0.016 0.194 0.048 0.205 0.010 l I-131 0.040 0.004 0.014 0.040 Xe-133 0.005 0.004 0.003 <0.001 i
Xe-135 0.003 0.004 0.107 -
0.148 0.192 0.130 0.179 0.274 t
Cs-137 0.109 0.061 0.095 0.165 0.059 l
0.078 0.040 0.063 Cs-134 0.044 0.085 0.018 0.035 Co-60 1.796 0.269 0.548 0.510 0.258 0.660 0.002 0.009 0.006 Co-58 0.010 <0.001 <0.001 Cr-51 0.015 0.004 <0.001 <0.001 0.004 0.004 0.001 0.009 Mn-54 0.002 0.025 0.002 <0.091 Zn-65 *<0,001 0.004 0.002 0.002 0.002 0.002 Sr-90 0.153 0.141 0.023 0.047 0.056 0.062 l 'Ce, Co, f
others (s 2Na,
gecifg Zr,88'I, Tc, **Nb l S. Percent of Technical Specification , 6.1 2.9 "J . 7 10.7 10.1 0.53 limit for total activity released
- e MPC of 1x10 2 ' pCi/ml used in calculating isotopes listed as "others", based on
- I the most.
restrictiva. .
s i APP NDIX A REPORT OF RADIOACTIVE EFFLUENTS La Crosse Boiling Water Reactor
- Tccility Dairyland Power Cooperative Docket 50-409 Year 1975 9
! I. LICUID RELT.ASES Aug. Sept. Oct. Nov. Dec Total Units July
- 1. Gross Radioactivity ( B ,6 a) Total release Curies 0.663 '2.195 0.386 0.233 0.481 2.862 - 14.144 7.28x10-8 1.25x10-* 2.46x10-* 1.95x10 7.95x10 4.22x10
b) Average concentration released pCi/ml 2.74x10-s 8. 2 6x10- -
c) Maximum concentration released uCi/cl 1.89x10-' 3.62x10-* 6.24x10-' 3.42x10- 8.26x10-' 4.22x10-
- 2. Tritium a) Total release Curies 1.65 4.32 7.1 7.993 13.756 126.676 -
b) Average concentration released WC1/ml 6.83x10-8 1.43x10-* 2.3x10-' 2.83x10-' 10.1875.2x10-' 9.37xlf 7.27x10 '
- 3. Dissolved noble gases Curies < 0. 002 0.003 <0.002 <0.003 <0.007 <0.057 -' <0.407 a) Total release 2.88x10 '
- b) Average concentration released ,,Ci/ml 8.3x10"* 9.95x10-**<6.48x10** 1.06x10~ 3.58x10 "' 3.88x10
- 4. Gross Alpha Radicactivity - -
Curies 1.17x10- 4: 5 4.85x10 ' 3.75x10-' 9x10-'
a) Total release b) Average concentration released uCi/ml 4.84x10 1.61x10-21 7.37x10"'
1.22x10-** 3.19x10-** 4.07x10 ' l.82x10" 9.58x10"
2.67x10-** 4.16x10 e 5. Volume of liquid waste to W Liters 196,100 211,800 140,500 95,730 134,000 189,500
' discharge canal 1.468x10',2,189,2302.359x10
- 6. Volu=e of dilution water Liters 2.416x10** 3.016x10 e 3.086x10*' 2.83x10** 1.958x10**
- 7. Isotopes Eeleased Curies Ba+ La-14 0 <0.001 <0.001 <0.001 0.003 <0.001 <0.001 0.047 Sr-89 <0.001 0.027 <0.001 <0.001 <0.001 <0.001 0.b48 4 I-131 0.002 0.002 0.003 0.006 0.012 0.054 0.995 Xe-133 <0.001 0.002 0.001 0.002 0.006 0.053 0.378
<0.001 <0.001 <0.001 <0.001 <0.001 0.004 0.029 Xe-135 0.023 0.035 1.407 Cs-137 0.113 0.142 0.034 0.030
, Cs-134 0.059 0.080 0.018 0.015 0.014 0.028 0.781 Co-60 0.064 0.152 0.019 0.011 0.019 0.099 0.649
- Co-58 0.378 1.548 0.267 0.147 0.372 2.368 9.121 l Cr-51 <O.001 <0.001 <0.001 <0.001 <0.001 <0.001 0.035 l Mn-54 0.003 0.020 (0.001 <0.001 0.001 0.014 0.069 2n-65 . <0.001 0.021 0.011 <0.001 <0 001
. 0.012 0.088 i
Sr-90 0.001 0.005 <0.001 <0.001 <0.001 <0.001 0.023
! Others (snecify) **8 I, 3 C% **Co, j ass Na, 'h Tc, Zr, Nb
- 0.037 0.193 0,027 0.013 0.028 0.191 0.911
- 8. Percent of Technical Specificatien
,~
linit for total activity released. 0.14 1.40 0.16 0.15 0.40 2.79 3.0 i *MPC of lx10~'pC1/ml used in calculating isotepes listed as "others" based on 8**I the most restrictive. ,
4 i
_.---_ _ - _ _ ---- - _ . . - - - - - - - - _ . - - - _ _ - _ . - - _ - - . _ _ . - _ _ - . - _ - - _ _ _ _ - - _ - . - _ _ , - - -v _
r _ ___ _ _ _ .
. }
s ZI. AIRBGRNE RELEASES Units Jan. Feb. Mar. Apr. May June
- 1. Total noble gases Curies 7751.02 6580.35 8136.96 5378.5 337.63 0
- 2. Total halocens Curies 0.011 0.016 0.0133 0.011 0.0469 0.0098
- 3. Total particulate gross radioactivity (S a)) Curies 11.64 8.57 12.80 7.00 0.44 <0.1
- 4. Total tritium Curies 3.3 1.62 2.67 1.16 0.77 0.63
- 5. Total particulate gross alpha radioactivity Curies <1.52x10-' =9.37x17 2.09x10 ' <1.1x10 J <l.52x10 ' 8. 4x10 '
- 6. Maximum noble gas release rate pCi/sec 5491 4906 5658 5141 4293 0 _
- 7. Percent of applicable limit fort
- a. noble gases % 26.4 24.8 27.7 18.1 1.1 0
- b. halogens (258I)
- 4.69 8.67 5.2 6.27 28.77 6.5
- c. particulates* t 0.43 0.45 0.49 0.23 0.23 0.23
- 8. Isotope released: Curies
- Particulates l Cs-137 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001- <0.0001 Ba a-140 <0.0001 0.0001 <0.on01 <0.0001 <0,0001 <0.0001 Sr-90 <0.0001 <0.0001 <G.000) <0.0001 <0.0001 <0.0001 '
Cs-134 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001
- Sr-89 0.0003 0.0007 0.0008 0.0004 0.0005 0.0004 ,
(( Halogens 1-131 0.0064 0.0107 0.0071 0.0083 0.0393 0.0086 I-133 0.0056 0.0043- 0.0052 0.0017 0.0066 <0.0002 l- I-135 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 Gases
( he-133m 17.83 15.13 16.75 34.42 2.16- 0 xe-133 273.61 232.29 287.24 316.26 19.85 0 Kr-28 539.47 457.99 566.35 460.94 28.93 0 Kr-87 684.42 581.04 718.51 557.21 34.98 0 Kr-85m 246.48 209.26 258.76 2C8.15 13.07 G xe-138 3203.50 2719.66 3363.10 1758.77 110.41 0 Xe-135m 1077.39 914.67 1131.10 772.89 48.52 0 Xe-135 1021.58 867.29 1072.50 885.84 55.61 0 Xe-137 475.14 403.38 498.81 250.10 15.70 0 Others as appropriate (specify) Kr-89 205.40 174.38 215.64 112.95 7.09 0 Kr-85 13.45 0.84 0 Xe-13 ba Reactor Power, Average MWT . 150 141 144 .
123 41 0
- Based on >S day half-life particulates. Not on total particulates as shown in Column 3.
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II. AIRBORhE RELEASES Nov. Dec. Total Units July Aug. Sept. Oct.
Curies 0 1739.99 5010.24 7090.68 (808.45 8298.73 5713255
.1. Total noble gases
- 2. Total halogens Curies <0.003 0.0052 0.0039 0.003i 0.0036 0.0054 0.1325
- 3. Total particulate gross radioactivity {6,y) Curies <0.1 4.01 6.52 8.52 *9.55 9.97 79.22 4 Total trititis Curies 0.02 0.6B 0.90 1.40 1.71 1.66 16.72
- 5. Total pa-ticulate gross alpha #
1x10 '
radioactivity Curies <9x10
- 1.2x10 7 2.13xlG-' 2.98x10-' 5.13x10-' 6.96x10
- 6. Maxamum r.oble gas release rato uci/sec 0 2032 3532 3420 3451 5671 5671 '
- 7. Percent of applicable limit for:
- a. noble gases t 0 6.4 19.0 22.0 22.6 26.7 16.3
- b. halogens (188I) . 4 <0.15 0.22 0.38 0.93 0.94 1.81 5.38
- c. particulatec* 4 0.22 0.29 0.22 0.49 0.49 0.51 0.36
- 8. Isotope released: Curles Particulates Cc-137 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 $0.0012 Ba-La-140 so.0001 0.0006 0.0001 0.0001 0.0001 0.0002 <0.0018 Sr-90 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <c.001.
de Cs-134 <0.0G01 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0012 j' Sr-89 Halogens 0.0007 0.0007 0.0007 0.0018 0.0017 0.0018 0.0110 I-131 <0.001 0.0003 0.0003 0.0013 0.0013 0.0025 0.0673 I-133 <0.001 0.0039 0.0024 0.0011 0.0013 0.0019 0.0332 1-135 <0.001 <0.001 <0.001 <0,001 <0.001 <0.001 <0.012 Cases Xe-133m 0 4.87 14.03 51.76 47.70 60.58 269.23 Xc-133 0 11.31 32.57 356.66 342.47 417.43 2289.69 Kr-88 0 41.24 118.74 307.74 295.49 360.16 3377.n5 Kr-87 0 101.09 291.09 528.26 507.23 613.26 4622.09 Kr-85m 0 16.51 47.60 164.50 157.96 192.53 1514.82 xe-138 0 724.53 2086.26 2405.R7 2310.11 2815.76 21497.97 xe-135m 0 221.67 638.30 1122.45 1077.78 1313.69 831A.46 Xe-135 0 58.64 168 85 474.37 455.49 555.19 5615.36 xe-137 0 398.98 1148.85 991.28 951.82 1160.16 6294.22 Others as appropriate (specify) Kr-89 0 147.03 423.37 451.68 '433.70 528.63 2699.87
- Kr-85 0 0 0 0 0 0 14.29 xe-131m 11.83 34.07 229.03 219.91 268.05 762.89 Reactor Power, Average MWT 0 62 152 158 158 137 '106
- Based on >8 day half-life particulates. Not on total pe ticulates as shown in Column 3.
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l RADIOACTIVE EFFLUENT REPORT and ENVIRONMENTAL MONITORING REPORT of T!!E LA CROSSE BOILING WATER REACTOR from January 1, 1976 - June 30, 1976 DAIRYLAND POWER COOPERAT2VE Docket No. 50-409 I
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able II II. AIRBORNE RELEASES 1976 Units Jan. Feb. Mar. Apr. May June
- 1. Total noble gases Curies 10,205.94 6945.35 0 0 0 0
- 2. Total halogens Curies 0.0072 0.0085 0.0031 <0.0012 <0.0014 <0.0012
- 3. Total particulate gross radicactivity (8,Y) 13.28 7.65 <0.1 <0.1 <0.1 <0.1
- 4. Total tritat:i Curies 3.404 1.694 0.042 0.081 0.081 0.150
- 5. Total particulate gross alpha radicactivity Curies 6.96x10_7 1.6x10 7 <1.7x10 , <1.0x10', 2.50x10 r 9.8x10 ,
- 6. Msximcm noble gas release rate UCi/sec 5896 5481 0 0 0 0
- 7. Percent of applicable limit for:
- a. noble gases g 32.9 25.3 0 0 0 0
- b. halogens ('88I) % 2.44 3.76 1.41 0.08 <0.07 <0.08
- c. particulates* % 0.61 0.58 <0.53 <0.02 <0.02 <0.02
- 8. Isotope released: Curies Particulates Cs-137 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 Ba-L4-140 0.0003 0.0002 <0.0001 <0.0001 <0.0001 <0.0001 Sr-90 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 Cs-134 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 Sr-89 0.0019 0.0017 0.0019 <0.0001 <0.0001 <0.0001 Ed Halogens j) I-131 0.0033 0.0048 0.0019 0.0001 <0.0001 <0.0001 1-133 0.0029 0.0027 0.0002 0.0001 <0.0003 40.0001 I-135 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 Gases Xe-133m 74.50 15.28 0 0 0 0 Xe-133 513.36 578.55 0 0 0 0 Kr-88 442.94 520.90 0 0 0 0 Kr-87 760.34 6L6.89 0 0 0 0 Kr-85m 236.78 243.09 0 0 0 0 Xe-138 3462.88 2053.74 0 0 0 0 Xe-135m 1615.60 1209.19 0 0 0 0 xe-135 682.78 914.70 0 0 0 0 Xe-137 1426.79 534.10 0 0 0 0 Others as appropriate (specify) Kr-89 650.12 232.67 0 0' O O Xe-131m 329.65 4.86 0 0 0 0 Xe-129m 0 0.69 0 0 0 0 Reactor Pow r, Average MWT 156 146 0 0 0 0
- Based on >8 day half-life particulates. Not on total particulates as shown in Column 3.
- b. Domineralizer type (deep bed or powdcred resin).
The resin used are of two types cation and anion. The cation resin tank uses Illinois Water Treatment company Type NR-1 and the-mixed (cation and anion) 1esin-uses Illinois Water Treatment Company Type NR-34.
- c. Regeneration frequency.
Demineralizers are not regenerated.
- d. Regnerant volume (gal / event) and activi ty.
There is no regenerant.
- 4. Condensate Demineralizars
- a. Average flow rate (1bs/hr).
The average flow rate is 306,000 lb/hr/ bed. Two resin beds are normally in service.
- b. Domineralizer type (deep bed or powdered resin).
Demineralizer are deep bed.
- c. Number and size (ft') of domineralizers.
The condensate demineralizer portion of the system consists of three ion exchangers in parallel, two of which are used during operation. Each bed consists of 30 cu ft. of cation resin and 15 cu ft, of anion resin.
- d. Rcgeneration Frequency Resin beds are not regenerated.
- e. Indicate whether ultrasonic resin cleaning is used and waste liquid volume associated with its use.
No ultrasonic resin cleaning,
- f. Regenerant volume (ga l / oven t ) and activity.
Resin beds are not regenerated.
. ~ - - . . - . -
. s S. Liquid Waste Processing SyntJm
- a. For each liquid waste processing syste.m provide in tabular form the following infctma tion
- 1) Sources, flow rates (gpd) and expacted activitias (frac-tion of primary coolant activity, PCA) for all inputs to each system.
The generation of liquid wastes at LACBWR can only be separated F into two groups, those that occur in the containment building and those that occur in the turbine building. There is no other separation of liquid wastes.
Based on two years of actual liquid releases for 1974-75, an aver-
- age of 666.8 gpd comes from the containment building and 787.0 gpd comes from the turbine building.
The activity of the combined releases for those years is shown in the enclosed Radioactive Effluent Report. ,
- 2) Holdup times associated with collection, processingi and >
discharge of all 11guld streams. l The curio releases that appear in the Radioactive Effluent Report are based upon samples taken immediately prior to release, there-fore, no credit should be given for holdup time prior to release. ;
- 3) Capacities of all tanks (gal) and processing equipment (gpd) considered in calculating hnidup times.
d I There are four collection tanks for liquid wastes, two six 1
thousand gallon tanks in the containment building and one three thousand and one forty-five hundred gallon tank in the turbine -
building. i l
- 4) Decontamination factors for cash processing step. ;
i
, There are no decontar' nation factors for processing liquid 4
releases.
- S) Fraction of each processing stream expectsd to be dis-l charged over the life of the plant, i
The fraction of each processing stream in LACBWR's 3)* stem is i 1 because of its single system.
- 6) For waste dominerali zer regenera tion provide s time between l
regenerations, regenerant volumes and activitirs o treatment y
of regenerants and tractions of regenerant dis.haryod. In-1 clude parameters used in making these determinations. ,
a i Haste demineralizer is not regenerated.
l 1
- 7) Liquid sou2ce term by radionuclide in Ci/yr for normal operation including anticipaled operational occurrences.
I The liquid source term should be the actual releases that occurred i during 1974-75 as shown in the enclosed Radioactive Effluent !
Reports.
- b. provide piping and instrumentation diagrams (p&ID's) and process flow diagrams for the liquid radwaste systems along wi th all othcr systems influencing the source term cricula- ;
tions. '
The piping and instrumentation diagrams for the liquid waste sys- {
tem ale enclosed. ;
- 6. Main Condenser and Turbine Gland Seal Air Pemoval Sustems
- a. The holdup time (hrs) for offgases from the main condenser l air ejector prior to processing by the offgas treatment '
system.
The holdup time for efcu uses from the main condenser air ejector is 0.17 hours1.967593e-4 days <br />0.00472 hours <br />2.810847e-5 weeks <br />6.4685e-6 months <br /> (10 ninutes) as described in SAR. Actual tests l show the holdup time to be an average of 11 minutes. i
- b. Description and expected performance of the gaseous waste treatment systems for the offgases from the condenser air
(
ejector and mechanical vacuum pump. The expected air in- \
, leakage per condenser shell, the number of condensar shc11s, and the iodine source tntm from the condonsr' The present routing of the gaseous waste from en" ait e;ector I l
is throi.gh a 10 minate holdup,then directly discharged to the stack. l The system is being redesigned to acquire additional holdup by routing through the Gas Storage Tanks in an unpressurized mode.
This modification will conservatively add 23 hours2.662037e-4 days <br />0.00639 hours <br />3.80291e-5 weeks <br />8.7515e-6 months <br /> to the present system for a total holdup of 23 hours2.662037e-4 days <br />0.00639 hours <br />3.80291e-5 weeks <br />8.7515e-6 months <br /> 10 minutes. The modifica-tion will go into service after the next refueling outage (March '
1977)
The expected air in leakage is 1 cfm. The number of condenser l shells is two-- one inner and one outer.
i I
- c. The mass of charcoal (cons) in the charcoal delay system used to creat the offgasos from the main condenser air ejector, the operating and dew point temperatures of the delay system, and the dynamic absorption coefficients for Xe and Kr.
There are no laassive amounts of charcoal in the delay system except those previously described in 7b.
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- d. Description of cryogenic distilla tion system s fraction of gases partitioned during distillation o holdup in system, stor-age following distillation, and expected system leakage rate.
There is no cryocenic distillation system at LACBWR.
- e. The steam flow (1bs/hr) to the turbine gland seal and the source of the steam tprimary or auxilia ry) .
The steam is condensate from the No. 2 feedwater heater.
- f. The design holdup time (hrs) for gas vented from the gland real condenser, the lodine partition factor for the condenser, and the fraction of radiciodine released through the system vent. Description of the treatment system used to reduce radiolodine and particulate releases from the gland seal system.
There is no holdup time for gas vented from the gland seal con-denser. There is no separate monitoring of gas vented from the gland seal condenser. All gas is monitored at stack gas monitor.
- g. Provide piping and instrumentation diagrams (P&ID's) and process flow diagrams for the gaseous waste treatment system along wi th all other systems influencing the source term cal-culations.
The piping and instrumentation diagrams are enclosed. The diagrams are titled as follows: L.a Crosse Reactor Plant Air Ejector Off Gas System Plow Diagram Condenser Vacuum System Reactor Plant Air Conditioning and Ventilation Systems
- 7. Ventilation and Exhaust Sustems For each plant building housing system that contains ra dioa c ti ve materials, the main condenser evacuation system and the turbine gland sealing system exhausts, provide the followings
- a. Provisions incorporated to reduce radioactivity releases through the ventilation or exhaust systems.
The only system that has provisions incorporated to reduce radio-active releases is the air ejector off aas system.
- b. Decontamination facLuts assumed and the bases (include char =
coal absorbers, HEPA filters, mechanical devices). The air ejector off gas systaa is presently discharged through a 10 mhiute holdup tank imodification will give 23 leurs 10 minutes holdup) then a high C - - - - - _ - _ - - - _ _ _ _ _ _ _ . _ _ _ _ - - _ _ _ - - - - - - - - - - - - - - - - - - - - - _ - - - - - - - - - - - - - - _ - - _ - - - _ - - - - - - - - - - - - - - - - - - - _ - - - - - - - - - - - - - - - - - - - - - - - -
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67-6* DATE 717-72 CHKDt,h[ OWN. JSR APP. J<c4 REF. AC DA/G NO 414 00-238 : REV ICH4-60 REVISED NONL R-42 REV.O .
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. s efficiency particulate air filter, two 2-5/8 inch thick charcoal filters, and finally a second high efficiency particulate air filter. The removal efficiency for iodine by the charcoal filters is 98 percent and the removal efficiency for the HEPA filters is estimated to be >99 percent.
- c. Release rates for radiolodines, noble gases, and radioactive particulates (C1/yr) and the bases.
TP 3 release rates for radiciodines, noble gases and radioactive particulates are shown in the enclosed Radioactive Effluent Reports 1974-75.
- d. Release point description, including height above grade, height above and rela tive loca tion to adjacent structures, relative temperature difference between gaseous effluent and ambient, flow rate, velocity, and size and shape of the flow orifice.
Gases are released through a stack 350 feet above grade. The release point description is as follows: Stack Height 350 ft. 106.7 meters ' Vs 70 ft/sec 21.3 meters /sec Diameter of Stack 4.5 ft. 1.4 meters Exit Temperature 90* F 305'K Ambient Temperature 46*F 281*K Stack Blowers 20 35,000 cfm/each Adjacent Structures
- 1) Genoa #3 Turbine Building Height 204 ft., located 200 ft. SSW
- 2) LACBWR Containment Bldg. Height 117 ft., located 20 ft. WNW
- 3) LACBWR Turbine Bldg. Height 60 ft., located 100 ft. WNW (See enclosed drawing.)
- c. For the containment building indicate the expected purge and venting frequencies and duration, and continuous purge rate.
The containment building purge rate is continuous at 6000 cfm.
- 8. folid Waste Processing Systems l l
- a. Provide in tabular form the following information concerning all inputs to tha solid waste processing systent source, ;
volane (cu.ft./yr/ reactor), and activity (Cl ? y r/r e a c t or) of j principal radicnuclidos along with bases for values. The annual volume of solid waste is from two sourcas depleted i' resins and compacted solid waste. The depleted resins accumulate at the rate of 130 cu. ft. por year with an associated activity of 40 Ci as estimated from dose measurements. The dry solid waste volume is 900 cu. ft. per year (106 drums) with an asso- : ciated ac*.ivity of 3 millicurios per drum as estimated from doce meamarements.
( .. .
- b. Onsite storage provisions (location, capacity) and expected onsite storage times for all solid wastes prior to shipment.
There are two onsite storage locations for radioactive solid waste. In the Waste Disposal Building the dry storage pit has a capacity of nine 55-gallon drums. The Low Specific Activity Drum Storage, located west of the turbine b'.ilding, has_a capacity ; of 160 55-gallon drums. Shipment of drummed solid wastes is once , per year. '
- c. ' Provide piping and instrumentation diagrams (P&ID
- s) and process flow diagrams for the solid radwaste system. ;
There is no solid radwaste processing system. There is only a drumming station. 1 i i h J
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l I I I l 4 1 2 l { j
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a \ 2. In response to Question 2 of our forbt u.a t ut ida 1976 letter you should tabulate the centerlina Jastancas trca the nuclear plant to the foi-lowing current locatian for eash of the 22.5 degree radial sectors centered on 16 card 2nal comp.tsu directions.
- a. All milk cows out to a distanco at I miles and/or nearest to 5 miles.
The following Tablo I shows all milk cows and goats out to a distance of 5 miles in Sectors 1-10, and to a distance of 3 miles in Sectors 11-16. Table I Milk Cows and Goats in the LACBWR Vicinity Sector 1 (North) Sector 2 (North - Northeast) Distance No. of Distance No. of from Plant Subject Elevation from Plant Subject Elevation (meters) Individuals (feet MSL) (meters) Individuals (feet MSL) 6900 37 1100 2900 24 680 4000 25 1100 5200 31 660 7300 22 1140 7100 30 1160 Sector 3 (Northeast) Sector 4 (East - Northeast) 4900 40 1120 1000 45 1120 5000 41 1160 1800 41 1130 5300 50 1140 3800 36 1130 5600 42 1160 4300 36 1160 6600 11 1140 5000 53 1140 7500 39 1140 5900 29 1140 7500 29 1140 d600 12 740 7800 42 1140 7500 35 670 7900 1G 1160 7600 10 740 7900 21 670 Sector 5 (East) Sector 6 (East - Southeast 2700 64 1140 2600 66 1160 3700 43, 1G* 1160 2900 25 1140 5500 49 1160 3100 38 1140 5700 13 720 4700 30 1100 6700 25 000 5600 34 t 1160 8000 21 1080 6900 1 660 7700 12 700 7000 41 1000 Sector 7 (Southeast) Sector 8 (South - Southeast) 2200 24 1140 2900 25 1100 3200 28 1120 3600 24 1060 4700 9 700 5300 17 650 4900 30 1060 t000 1G* 6HO 6900 16 1060 7600 57 1060 7700 40 1100 i Sector 9 (South) nor4e Sector 10 (South - Southwest) nene Sector 11 (Southwest) nono Sector 12 (Fest Southutst) 4900 12 660 { Sector 13 (West) nona sector 14 (West Northwest) nens J Sector 15 (Northwest) rane Soetor 16 (North Northwest) none l
' Goat .
I l u____________._________________._____________________
? i
, 9 b. All esat animals out to a distance .> f 3 alles and/ar neasost to j
$ alles.
The following Table II shows the number of meat animals out to a distance of 5 miles in Sector 1-10 and out t, a distance of 3 miles in Sector 11-16. Table Il Meat Animals in the Viciteity of LACBWR Sector 1 (North) Sector 2 (North - Northeagt) Distance Distance from Plant No. of Elevation from Plant No. of Elevation (meters) Animals (feet MSL) (meters) Aninals (feet NSL) None 2900 6S 500 5200 30 660 5500 14 700 6500 12 740 6900 25 1100 7300 2 1140 Sector 3 (Northeast) Sector 2 (Fast - Nortneast) 5000 22 1160 1800 14, 1H* 1120 5600 9 1160 2700 50 1100 6400 26 ROO 4900 42 H* 1140 6600 25 1140 5200 3 1140 6700 21 1160 7600 47 1180 7600 9 1160 Sector 5 (East) Sector 6 (East - Southeast) 2700 22 1140 2600 12 1140 3700 4 1160 2700 2 1160 6600 3 720 4009 13 1100 6300 2 660 6300 4 650 8000 62 1000 Sector 7 ioutheast) Sector 8 (South - Southe.sst) 2200 7, 6 11
- 1140 2900 1 1120 4800 21, 2 H* 700 5000 14 650 7600 4 1060 5300 3 650 7800 12, 9 I:
- 1080 5500 15 650 5600 10 620 1200 31, 6 H* 1100 7703 40 8li' 740 Sector 9 (South) Nano Sector 10 (South Southwest) None Sector 11 (Couthwest) None Sector 12 (West - Southwest) 4800 50 11' 660 4300 25 H* 640 4900 50 700 Sector 13 (West) Sector 14 (West - Northwest) Ncne 4100 2$ 660 Sector 15 (Northwest) l'a no Sector 16 (North Northwest) None
- c. All asik gaats aue tu a :Istan:t s t
- miles and/or nearest to 5 miles.
The milk goats are Shawn 21. *able I of part 4, along with the milk caws. i ,
- d. All residences out to a distance of 3 miles and/or nea rest to
$ miles.
All residences out to a distance of 5 miles are shown in Table III. Table III Residences in the Vicinity of LACBWR Sector 1 (North) Sector 2 (North - Northeast) Distance . Distance from Plant No. of Elevation (rom Plant No. of Elevation (meters) Resid3nces (fect MSL) __ (meters) Residences (f eet MSL)
- 1. 1000 1 640 13. 1400 '30 660
- 2. 1100 1 640 14. 2000 15 680
- 3. 2300 3 660 15. 2700 3 700
- 4. 2400 2 660 16, 3100 1 1100
- 5. 3500 1 700 17. 4000 2 1100
- 6. 4000 4 680 18. 4900 1 700
- 7. 4700 1 660 19. 5400 1 700
- 8. 5500 3 660 20. 5900 2 680
- 9. 5900 1 700 21. 6400 1 740
- 10. 6700 1 680 22. 6800 1 1120
- 11. 7500 1 1120 23. 7300 1 820
- 12. 7600 5 680 24. 7500 2 1?.60 Sector 3 (Northeast) Sector 4 (East - Northeast)
- 25. 1900 1 1120 38. 1300 1 1120 26, 2800 1 740 39, 1900 1 1120
- 27. 4400 1 1160 40. 4100 1 1180 i
- 28. 4400 2 1120 41. 5000 3 1160
- 29. 5100 1 1180 42. 5200 2 1180
- 30. 5300 1 1140 43. 5500 31.
1 1160 5600 1 1180 44. 5900 2 1100
- 32. 5900 1 740 45. 6800 1 1200
- 33. 6500 2 1160 46. 7000 1 720
- 34. 6700 2 1160 47. 7200 1 680
- 35. 6000 1 860 48. 7600 1 680
- 36. 7500 2 1180 49. 7800 1 700
- 37. 7900 2 1180 Sector 5 (East) Sector 6 (East - Southeast)
- 50. 2700 1 1180 62. 800 1 700
- 51. 3300 2 1180 63. 1200 2 720 52, 3700 1200 2 64. 2400 1 1160 '
- 53. 3900 1 1180 65. 2600 2 1160
- 54. 4900 1 1160 66. 2900 2 1180
- 55. 5600 1 760 67. 4000 2 1140
- 56. 6600 4 680 68. 4100 1 1200
- 57. 6900 2 660 69. 5600 1 1060 sG. 7000 1 740 70. 6100 59.
2 680 7000 6 (60 71. 6600 1 640
- 60. 7500 1 660 72. 6900
- 61. 1 720 7900 1 760 73. 7700 1 680
Talile III (Cont'd) 1 Residences in the Vicinity of LACBWH Sector 7 (Southeast) Sector 8 (South - Southeast) ' i Distance Distance I from Plant No. of Elevation from Plant No. of Elevation ! (meters) Residences (foot MSL) (neters) Residences (feet MSL) i
- 74. 400 3 660 90. 900 22 660
- 75. 800 1 680 91. 1800 1 660 3 76, 2200 1 1120 92. 2100 1 700
- 77. 2700 2 1140 93. 3400 0 660
- 78. 3000 1 1120 94. 3600 28 660
- 79. 3400 1 1080 95. 4000 20 660
- 80. 4400 1 720 96. 5000 3 660
- 81. 4700 1 630 97. 5600 '3 680
- 82. 4900 1 640 93. 6400 2 700
- 83. 5300 1 640 99. 6900 2 680
- 84. 5500 1 720 100. 6900 1 1120
- 85. 5600 2 700 101. 7500 1 1140
- 86. 6100 2 660 102, 7900 1 700
- 87. 6600 1 680
- 88. 7600 2 1200
- 89. 7900 1 760 Sector 9 (South) Sector 10 (South - Snut6+est) 103. 2500 3 700 105,- 7900 2 640 l 104. 7700 3 680 Sector 11 (Southwest) Sector 12 (West - Southwest 106. 6000 1 700 112, 4300 1 640 107. 6400 1 740 113. 4800 3 660 !
108. 6900 1 700 114. 6100 2 1140 109. 7300 2 680 115, 7700 1 600 110, 7600 1 680 111. 8000 1 700 Sector 13 (West) Sector 14 (West - Northwest) 116, 4100 2 660 124. 4500 1 700 l 117 4800 1 1100 125. 5300 1 1040 118. 5200 1 1080 126. 5900 2 680 119. 6200 1 1140 127, 6200 2 680 120, 6600 1160 1 128. 6400 1 710 121. 7100 1 1140 129. 7300 1 1080 122. 7700 1 1140 130, 7600 123. 8000 1 1120 l 1 1140 131. 7600 1 1160 l Sector 15 (Northwest) Sector 16 (North - Northwest) 132. 5600 8 660 139. 7500 2 660 133. 5800 7 720 139. 7600 1 1120 134, 6500 1 700 135. 7500 2 700 136. 7900 1 650 l 137 0000 2 700
- e. All vegetable gardens *SCO sq. ft. oat to a distance of 3 miles and/or nearest to 5 mileu.
Since LACBWR is located in primarily a rural setting with no tosna within several miles, he havu assumed that all residences within 5 l riles of the plant as shown in part 2.d. could have ve7etablo g a r de r.s $500 sq. ft. during the months of June, July, August and September. 1 I l 1 I
- 3. Provide the information requested in items 3, 4, $b or 6b, 7 and 8 of Enclosure 1 or our February 18, 1976 letter.
- Based on considerations in Draft Regu otory Guide 1.DD, picvide es tima tes of rela tive concentration (X/Q) and deposition (D/Q) at locaticns specified in response to iten 2 above for each release point specified i. response to item 1 above, This question is still under revicw and is to be compleced by December 15, 1976.
- 4. Provide a detailea' description of the meteorological data, modele and parameters used to decernine the X/Q and D/O values. Include information coacerning the validity and accuracy of the models and assumptions for youc site and the representativencss of the meteorological data used.
This question is still under review and is to be completed by December M,1976. 6.b Describe the representativen'ess of the available data with respect to onsite and near site atmospheric transport and diffusion con ~ ditions, and wi th respect to expected long term conditions ,at and near tha site. This question is still under review and is to be completed by December 35,1976.
- 7. Describe altflow trajectory regimes of impor tanco in transtctcing effluents to the locations for which doac calculations are made.
This question is still under review and is to be,5cmpleted by December 15, 1976. N
- 8. Provido a map showing the detailed topographical featores (a s modified by the plant, on a large scale, witbin a 10-mi.e radius of the piant and a plot of the maximum topographic elevation vc 'rs us distance from the center of the plant in each of the sixteen 23 2/2 degree cardinal compass point sectors (centered on true north):
radiating from the center of the plant, to a dl3tarce of it m i l s .c . Three copies of a topographical map are enclosed. The distance to the maximuu topographical elevation in each sec~ tion is as follows: Sector Distance Elevation Sector Distance Fievation l N 24,000 ft. 1140 8 30,500f'. .1140 l l NNE 13,000 " 1112 SSW 27,000 " 1120 NE 32,000 " 1200 SW 34,000 4 '154 ENE 5,700 " 1136 WSW 21,000 - 1151 : E 10,300 " 1240 W 41,500 J 1179 ESE 9,600 " 1172 10n1 28.tu) " 1117 SE 10,500 " 1140 NW 35,.000
- 1149 SSE 9,000 " 1140 NNW 27 000 "
1140 1 Plant Grade 440
s
. i j
- 4. Please provida documentation of the history of the meccozological program at the site. This documentation should entall a summary of all meteorological dat a collected at the site (a s well as any j special studies) including a doscription of the measurements made during each data collection parlod, sensor locations with respect to the plant and prominent topography, and the accuracy and speci-fications of all the me teorological ins trumen ta tion.
The meteorological program at the LACDWR site began in 1962. Wind speed and directional data were collected during the months of October 1952-1963, and January, April and July 1963-1964. A Bendix-Priez Aerovano with strip charp recorder was used to collect this information. The aerovane was originally located on the roof of the old Genoa No. 1 steam plant and in 1968 was moved to the top of the 330-foot LACBWR off-gas stack. It was located on a boom about two stack diameters away from the stack and oriented toward the west. The strip chart recorder was moved to the LACBWR control room. The aerovane was removed from the stack in 1975. Data sum-maries were compiled for the above-mentioned months during 1962, 1963 and 1964 and for the years 1969, 1970 and 1971. These sum-maries are shown in tables 1 and 2. In addition to the annual summary contained in Table 2 for the period 1969-1972, this data was racomputed to represent the relative frequency distribution , expected at the 35pfoor level by assuming that wind speed increases exponentially with increasing height. Table 3 contains this data. Data for the periods 1965 through 1968 and 1972-1975 were collected but not summarized. The quality of the data for 1962-1964 is subject to some question as to interference trom the Genoa No. 1 plant building. The wind direction data for 1969-1971 with the aerovane at the stack-top location are probably rather good. The instrument would be sub-jected to stack intetterence only for east winds which occur infre-quently. However, yince the aerovane has a starting speed of 4-5 mph, the wind speec distr 3bution is probably shifted to lower speeds relattve to the actual distribution. 1bc LACDWR meteorological program has recently been modified by
- he addition of now instrumentation. Three new meteorological stations have been installed at varicus locations in the site vicinity to give a more accurate representation of atmotpheric !
ectivity in the hilly terrain around the site. The aerotane l
.has bee.n replaced ac stack-top with a Meteorology Research, '
Inc. thRI) Model 1074-22 anemometer and wind vane. This instru- l ment is equipped with a MRI sigma noter, providing a separate ! continuous output of the standard deviation of the fluctuation ! in horizontal wind direction which utves a ineasure of atmospheric ' s ta bil i.t y . Boom length has been increased to 2-1/2 stack dia-I meters to minimize stack aerodynamic interference. A second l MRI anemoneter/ wind vane / signa m 3ter has been installed on a 10- ! aeter pol.a on the LACBWR site in order to assess surface winds. A Roserount Model 442A dry bulb temperature system has been in-stalled to measure ambient temperature and differential temperature between the stack-top and 10-meter pole locations. A third MRI l anemometer / wind vane / sigma meter has been placed at the top of a j
. . \
100-foot radio tower located 2.0 miles east-sottheast of LACBWR ,. un the bluffs. Grade elevation at the tower is 1200 feet MSL. ! LACBWR site grade is 639 feet MSL. I~ The accuracy of this instrumentation surpasses the specifications of Regulatory Guide 1.23: Anemometer i starting threshold - 0.75 mph i accuracy - 1 0.25 mph ! Wind Vane ! starting threshold - 0.75 mph accuracy - 1 0.25* Temperature (dry bulb) accuracy - 1 0.18'F (t 0.10'C) Differential Temperature accuracy - 1 0.025'F (t 0.014*C) i Instrumentation was placed in service according to the following . schedule: Radio Tower anemometer / wind vane /cisma - July 1974 ! LACBWR Site ambient temperature - January 1976 surface anemometer / wind vane / sigma - June 1976 differential temperature - July 1976 stack cncoomater/ wind vane / sigma - August 1976 Monthly data summaries for the radio tower location e.re contained i in the enclosed computer printouts for August 1974 tSrough June l j 1976. An annaal summary is also included. Data for. the LACBWR ; site is insufficient as yet to prepare meaningful r,ummaries. ' l We are also enclosing a copy of the STAR data cummary compiled by I the NOAA National Climatic Center for the Ls Crosse, Wisconsin I j weather station located about 20 miles north of the LACBWR site in l the Mississippi Valley. l i 5 i j L - ]
I O 8 I.
. ac.le .e Pericd .'363 - 1971 350-F.. E .' e v a s t or. Stabilst*/ Class A '.1 A!.NAI. F:<EQUESOY 3: 3 TPIBC T! 3N - LACBWE W a r.d Wird 5'esd, mFh Direct;;r C-12 >14 13-2._4 S .;3'25 N Ni,
.'3230 . 00575
.",6330 .02560 . 00460
.E .012i1 *
.stl'8 . 00212 EME .30626 .';C230 . S0041 E .01446 '
.,0538 . 00097 E3E .S0679 .00230
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.;2164 .00794 . 0~143 S .11650 .35013 . 00902 S 3*d .03772 .G3564 . 00644 3W .05313 .321 i "L39; WIW .0113'
)
00435 . 0007E ' h .31231 y"* y*
.012'.3 . 00216
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.. 336 . )6276 l
l 's a . : e l :. t t / e T r e p e r.:-. cf ;uir.s Listributed A:,ove - .147 1 1 Tabla 2 - Period 1969 - 1971 350-Ft. Elevation Stability Class A ANNUAL PREQUENCY DISTRIBUTION - LACBWR i Wind Wind Speed, mph Direction 0 12 13-24 >24 N .00035 .00013 .00002 - NNE .00027 .00010 .00002 NE .00013 .00005 .00001 ENE .00003 .00001 ,000001 E .00005 .00002 .000003 ESE .00003 .00001 .000001 SE .00006 .00002 .000004 SSE .00009 .00003 .0n0006 S .00055 .00020 .00004 SSW .00039 .00014 .00002 SW .00024 .00008 .00001 WSW .00005 .00002 .000003 W .00013 .00005 .000008 t.'NW .00007 .00002 .000006 NW .00018 .00007 .00001 NNW .00017 .00006 .00001 l i 1-
\
1 e 1
~
E , Table 2 Period 1969 - 1971 350-Ft. Elevation Stability Class B ANNUAL FREQUENCY DISTRIBUTION - LACBWR Wind Wind Speed, mph Direction 0-12 13-2,4 >24 N .00419 .00154 . 00028 3 14hE .00335 .00123 . 00022 NE .00154 .00056 . 00010 1 ENE .00030 .00011 . 00002
- r. .00070 .00026 . 00005 ESE .00030 .00011 . 00001 3 SE .00080 .00029 . 00005 SSE .00010 .00038 . 00007 S .00657 .00241 . 00043 ,
SSW .00469 .00172 . 00031 SW .00285 .00104 . 00019 , WSW .00057 .00021 . 00004 W .00157 .00058 . 00010 WNW .00080 .00029 . 00008 NW .00221 .00081 . 00015
- NNW .00201 .00073 . 00013 t
l 5 e i i J, t j
.- .. I l
i Table 2 I l Period 1969 - 1971 l l l 350-Ft. Elevation Stability Class C l ANNUAL FREQUENCY DISTRIBUTION - LACBWR ' Wind Wind Speed, mph Direction 0-12 13-24 >24 N .00864 .00317 .00057 l NNE .00691 .00253 .00046 i NE .00318 .00116 .00021 ENE .00062 .00022 .00004 ; E .00145 .00053 .00009 ESE .00062 .00023 .00004 : SE .00166 .00061 .00011 SSE .00214 .00079 .00014 i S .01354 .00497 .00089 l SSW .00967 .00355 .00064 SW .00587 .00215 .00039 WSW .00117 .00043 .00008 W .00325 .00119 .00021 ) WNW .00166 .00060 .00016 I NW .00456 .00167 .00030 NNW .00415 .00152 .00027 i l l l I, 1 i i
Table 2 Pericd 1969 - 1971 350-Ft. Elevation Stability Class D ANNUAL FREQUENCY DISTRIBUTION - LACBWR Wind Wind Speed, mph Direction 0-12 13-24 >21 N 0.04920 .01804 .00324 NNE 0.03937 .01444 .00259 NE 0.01811 .00664 .00119 ENE 0.00354 .00130 .00023 E 0.00827 .00303 .00055 ESE 0.00357 .00130 .00023 SE 0.00945 .00346 .00062 SSE 0.01220 .00448 .00080 S 0.07716 .02830 .00509 SSW 0.03511 .02021 .00363 SW 0.03346 .01227 .00220 WSW 0.00669 .00245 .00044 W 0.01850 .00678 .00122 WNW 0.00945 .00346 .00090 NW 0.02598 .00953 .00171 NNW 0.02362 .00866 .00156 I I i L._
1 t '. Table 2 Period 1969 - 1971 i 350-Ft. Elevation Stability Class E ANNUAL FREQUENCY DISTRIBTUION - LACBWR Wind *- Wind Speed, mph ' Direction 0-12 13-24 >24 N .00977 .00358 .00064 NNE .00782 .00287 .00051 NE .00360 .00132 .00024 ENE .00070 .00026 .00004 E .00164 .00060 .00010 ESE .00070 .00026 .00005 SE .00188 .00069 .00012 SSE .00242 .00089 .00016 S .01532 .00562 .00101 SSW .01094 .00401 .00072 SW .00664 .00244 .00044 WSW 0.00133 .00049 .00009 W .00367 .00134 .00024 WNW 0.00187 .00069 .00018 NW 0.00516 .00189 .00034 NNW 0.00469 .00172 .00031 L_
e e 1 Table 2 Period 1969 - 1971 350-Ft. Elevation Stability Class F ANNUAL FREQUENCY DISTRIBUTION - LACBWR Wind Wind Speed, mph Direction 0-12 13-24 >24 N .01509 .00554 .00099 NNE .01207 .00443 .00080 NE .00555 .00204 .00037 ENE .00108 .00040 .00007 E .00254 .00093 .00017 ESE .00109 .00040 .00007 SE .00290 .00106 .00019 SSE .00374 .00137 .00025 S .02366 .00868 .00156 SSW .01690 .00620 .00111 SW .01026 .00376 .0006E WSW .00205 .00075 .00013 W .00568 .00208 .00037 WNW .00290 .00106 .00028 NW .00797 .00292 .00053 NNW .00725 .00266 .00047 o 6
I Te.ble 3 Period 1969 - 1971 Stability Class F 35-Ft. Elevation ANNUAL FREQUENCY DISTRIBUTION - LACBWR Wind Wind Speed, mph Direction 0-3.8 3.8-7.7 >7 . 7 N .01509 .00554 .00099 NNE .01207 00443 .00080 NE .00555 00204 .00037 ENE .00108 .00040 .00007 , E .00254 .00093 .00017 ESE .00109 00040 .00007 SE 00290 .00106 .00019 SSE .00374 00137 .00025 S .02366 .00868 .00156 SSW .01690 .00620 .00111 SW .0i026 .00376 .00068 ; WSW .00205 ,00075 .00013 ' W .00568 .00208 .00037 WNW .00290 .00106 .00028 ! NW .00797 00292 .00053 NNW .00725 .00266 .00047 e 1 V
~~'
[1 , , f Table 3 l t Period 1969 - 1971 i 35-Ft. Elevation . Stability Class E ANNUAL FREOUENCY DISTRIBTUION - I.ACBWR Wind Wind Speed, mph : Direction 0-3.8 4.2-7.7 > 7. 7 N .00977 .00358 .00064 : NNE .00782 .00287 .00051 NE .00360 .00132 .00024 ; ENE .00070 .00026 .00004 E .00164 .00060 .00010 ESE .00070 .00026 .00005 . SE .00188 .00069 .00012 l SSE .00242 .00089 .00016 S .01532 .00562 .00101 : SSW .01094 '
.00401 .00072 SW .00664 .00244 .00044 WSW 0.00133 .00049 .00009 W .00367 .00134 .00024 WNW 0.00187 .00069 .00018 ,
NW 0.00516 .00189 .00034 NNW 0.00469 .00172 .00031 4 f' " Table 3 Period 1969 - 1971 35-Ft. Elevation) Stability Class D ANNUAL FREQUENCY DISTRIBUTION - LACBWR Wind Wind Speed, mph Direction 0-6.7 7.2-13.4 >13.4 M 0.04920 .01804 .00324 NNE 0.03937 .01444 .00259 NE 0.01811 .00664 .00119 ENE 0.00354 .00130 .00023 E 0.00827 .00303 .00055
- ESE 0.00357 .00130 .00023 SE 0.00945 .00346 .00062 SSE 0.01220 .00448 .00080 S 0.07716 .02830 .00509 SSW '
O.05511 .02021 .00363 SW 0,03346 .01227 .00220 WSW 0.00669 .00245 .00044 W 0.01850 .00678 .00122 WNW 0.00945 .00346 .00090 NW 0.02598 .00953 .00171 NNW 0.02362 .00866 .00156 1 i I L___ _ _ _ _ ________________--____ _ _
i Table 3 ; Period 1969 - 1971 ! 35-Ft. Elevation Stability Class C i ANNUAL FREOUENCY DTST13IBUTION - LACBWR Wind Wind Speed, mph Direction 0-6.7 772-13.4 >13 . 4 N .00864 .00317 .00057 NNE .00691 .00253 .00046 NE .00318 .00116 .00021 ! ENE .00062 .00022 .00004 E .00145 .00053 .00009 ESE .00062 .00023 .00004 ' SE .00166 .00061 .00011 -i SSE .00214 .00079 .00014 S .01354 .00497 .00089 SSW .00967 .00355 .00064 > SW .00587 .00215 .00039 ! WSW .00117 .00043 .00008 ' W .00325 .00119 .00021 WNW .00166 .00060 .00016 l tIW .00456 .00167 .00030 NNW .00415 .00152 .00027 l i l i I t
- f. , . .
Table 3 Period 1969 - 1971 35-Ft. Elevation Stability Class B ANNUAL PRE 00ENCY DISTRIBUTION - LACBWR Wind Wind Sooed, mph Direction 0-6.7 7.2-13.4_
>13.4 N .00419 .00154 .00026 NNE .00335 .00123 .00022 NE .00154 .00056 .00010 ENE .00030 .00011 .00002 E .00070 .00026 .00005 ESE .00030 .00011 .00001 SE .00080 .00029 .00005 SSE .00010 .00038 .00007 S .00657 .00241 .00043 SSW .00469 .00172 .00031 SW .00285 .00104 .00019 WSW .00057 .00021 .00004 .
W .00157 .00058 .00010 WNW .00080 .00029 .00008 NW .00221 .00081 .00015 NNW .00201 .00073 .00013 f t _m
( a i 1 Table 3 ; Period 1969 - 1971 : 35-Ft. Elevation Stability Class A 1 ANNUAL FREQUENCY' DISTRIBUTION - LACDWR f Wind Wind Speed, mph ; Direction 0-6.7 /.z-1J.g >13.4 N .00035 .00013 .00002 ! NNE .00027 .00010 .00002 NE .00013 .00005 .00001 ! ENE -
.00003 .00001 .000001 E .00005 .00002 .000003 i ESE .00003 .00001 .000001 !
S F. .00006 .00002 .000004 ; SSE .00009 .00003 .000006 i S .00055 .00020 .00004 SSW .00039 .00014 .00002 ; SW .00024 .00008 .00001 ! WSW .00005 .00002 .000003 l W .00013 .00005 .000008 . WNW .00007 .00002 .000006 i NW .00018 .00007 .00001 l NNW .00017 .00006 .00001 ! i i h l l l 1 l u
m l l - l Table 1 WitJD DIRECTICF4AL FREQUEt4CY AND SPEED AT LACBWR SITE * (E,ompte- During Octc6er the wind is from the North 10.64 percent of the time. its eeed is - 12 mph 90.25 percent of the time, 12-24 mph 9.79 percent of the time,ond its overage geed is 6.20 mph.) Period 1962-1964 cerect;onoi frequency, % of :We 0 - 12 reph, '% of tim 12 - 24 ryph,S.d time , ' 24 mph, % of time
. overage weed. @
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,;4 8 5 A O R N A C 8 % A 6 -R & Q O A & Q f N 4.31 6.83 7.71 10.64 95.08 92.63 95.50 90.21 4.72 5.26 4.50 9.79 0.00 2.11 0.00 0.00 3.41 5.21 5.07 6.20 NNE 0.42 0.86 0.76 1.64 100.00 100.00 100.00 100.00 0.0C 0.00 0.00 C.00 0.00 0.00 0.00 0.00 I.83 1.08 1,73 1.95 1 8 NE 0.14 0.5a 0.35 0.22 100.00 i00.00 100.00 100.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 1.00 2.00 0.60 0.00 0.14 0.36 0.76 0.15 100.00 100.00 100.00 100.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 C.00 1.00 0.t9 0.00 l
1 fENE E 0.14 0.79 0.69 0.37 100.00 100.00 100.00 100.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.50 3.73 2.30 0.60 ESE 0.42 0.72 1.67 0.60 100.00 100.00 luo.00 100.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.67 2.80 2.54 0.63 l S E' 5.93 5.04 7.71 5.58 94.05 75.71 96.39 93.34 5.95 24.29 2.70 6.67 0.00 0.00 0.90 0.00 4. 6 7.69 5.45 6.44 I SSE 28.04 19.71 29.38 23.20 80.61 68.98 91.25 82.59 19.14 29.93 8.75 17.41 0.25 1.09 0.00 0.00 7.36 9.44 5.60 8.16 5 11.65 15.54 13.26 14.36 93.33 74.08 96.33 88.60 6.67 25.46 3.66 11.40 0.00 0.46 0.00 0.00 4.98 8.50 4.81 6.42 55W 3.39 7.34 4.51 4.91 100.00 89.21 98.47 95.45 0.C'> 10.78 1.54 4.55 0.00 0.00 0.00 0.00 3.06 5.33 2.75 3.86 SW 2.9C 3.38 2.85 2.90 97.56 68.09 100.00 94.87 2.44 31.91 0.00 5.13 0.00 0.00 0.00 0.00 3.4I 5.57 2.49 2.51 l ! WSW 2.97 3.38 3.19 1.79 103.00 95.75 100.00 100.00 0.00 A.26 0.00 0.00 0.00 C.00 0.00 0.00 3.07 3.55 1.57 3.*7 i WNW 5.23 3.45 3.26 2.68 97.30 95.83 100.00 94.44 2.70 4.17 0.00 5.56 0.00 0.00 0.00 0.00 5.01 3.83 1.74 5.14 l NW 9.11 8.85 5.00 6.03 83.72 90.24 100.00 87.65 16.28 9.76 0.00 12.35 0.00 0.00 0.00 0.00 7.67 6.36 2.96 5.37 l W 4.31 3.17 2.15 1.49 100.00 97.73 100.t% 93.00 0.00 2.27 0.00 5.00 0.00 0.00 0.00 0.00 3.89 2.82 1.13 3.05 pqNw 20.90 20.00 16.74 18.45 69.93 73.74 S3.40 78.23 30.07 21.22 15.77 21.77 0.00 5.04 0.83 0.00 8.87 9.38 7.12 7.50 l l *Doto was taken .lonuary, Ap<il, and July 1963 - 1964, and October 1962 - 1963 . Instrument used was Bendix-Friez Aerovane l located on Genoa No. I plant roof. I l
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- U.S. DEPAP.fMENT Oi
- COINAERCE , .
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NATIONAi. OCEANIC AND ATMOSPHERIC ADMINISTRATION
^
l ENVIRONMENTAL D.ATA SERVICE - f y - JOB NO. 01.'72 4 l SEASOLM,AND ANNUAL , q , WIND DISTRIBUTION BY PASQUILL STABILITY CLASSES (6) 'l (STK1 PROC!AM) gj ! Station: #14920, Lacrosse Wisconsin l 1l6 4
, Period: Jan. 1949-Dec. 1953 i y a
j. j 5aurce: TDF 1440 (24 Obs/ Day) l ' l i DATE July 12,1972 i! i :. NATIONAL CLIMAllC CENTER ll I.l
! FEDERAL BUILDING, A31iEV!LLE, N.C. 3, 1 n ! v.:.c .r.r.m-ma:ut i
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8 JC3 180. 01772 SF).50"AI AND A'IUAL tJIND DISTRIBUTION BY PASQUILL STABILITY CIASSES (STAR PROCRAM) (6 Classee) Page 1 of 3 * (24 Obs/ Day) STATION: #14920. Lacrosse. Vis. W pggyop; Jan. 1949-Dec. 1953 .
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Data are presented by stability classes and also combined for the period indicated; first, as a b1 variate frequency distributicn of wind direction vs. wind speed, and secono, as normalized values (i.e.. relative f requency). Stability classes used are based on Pasquill's class structure (see Journal of Applied Meteorology February 1964), as follows: P squill Stability Class Ventified in lower Definition
.left correr in this tabulation as 1 A Extremely Unstable 2 8 Unstable 3 C Slightly Unstable 4 D Neutral 5 E Slightly Stable 6-7 F Stable to Extremely Stable s
l Average wind speed in knots, to tenths, for each direction and each speed class. Overall average wind speed is computed by Sum of wire $ speed Number of occurrences 3tHBER OF OCCUsEENCES: Number of DIR/SPD observations, plus number of calas (winds are tabulated to 16 points 1 speeds are in knots.) REIATIVE PRiiQUENCY OF OTIRRENCES: Number of occurrences / stability class Total number of observations l 1DTAL NUPSER OF OBSERVATIONS: Number of observations in each, month, season, annual or period. , TOTAL REIATIVE FREQUENCY OF OBSERVATIONS: Total number of observations = 1.0M Total number of observations j This normalized (relative frequency) table is self explanatory, except that the cala values have been distributed in the 0-3 speed ! critegory based on the number of observations in speed categories 0-3 and 4-6 Number of cales in "C" class ( 7) = .0005554 0005554 = .0000185 F.xseple: Total Obs (N) = 3601 (DJF) N (3601) (30) Number obs. in classes 1-3 and 4-6 ! From the South direction there are seven observations in the first two speed categories, hence 7(.0000185) = .0001295 observations. 2/3601=.0005554 h n added togettwr 0005554 + 0001295=.0006849 the resultant ( "T,0485) In the first category there are 2 i figure is placed in the South 0-3 category and 00389 in the South 4-6 category. This method is used to distribute the calms into the 0-3 l cpead category, by directions. i I
i Page 2 of 3 . 01772 : A STAB 11.1TY CLASSIFICATION BASED ON HOURLY AIRPORT OBSERVATIOt6 The following explanation of the Pasquill Stability classification has been extracted from an article by De Bruce Turner in the February 196a. Icurnal of Appliad Meteorolos;y. This system of classifying stability on an hourly basis for research in air pollution is based upon work accomplished by Dr. F. Pasquilt of 2.s British Meteorological Of fice (1961). Stability near the ground is dependent. primarily upon net radiation and wind speed. Without the influence of clouds, insolation (incoming radiation) during the day is dependent upon solar altitude, which is a function of time cf day and
-ine of year. When clouds exist their cover and thickness decrease incoming and cu tgoing radiation. In this system insolation is estimated i sy solar altitude and modified for existing conditions of total cloud cover and cloud ceiling height. At night estimates of outgoing radiation
( ars nada by considering cloud cover. This stability classification system has been made completely objective so that an electronic computer l :en be used to compute stability classes. The stability classes are as follows: 1) Extremely unstable, 2) tinstable, .3) Slightly unstable. l a) Neutral, 5) Slightly stable, 6) Stable, 7) Extremely stable. Table A-1 gives the stability class as a function of wind speed and net radiation. The net radiation index ranges from fa, highest positive net radiation (directed toward the groucd), to -2, highest negative net radiation (directed away f rom the earth). Instability cecurs with high positive net radiation tow wind speed, stability with high negative ist radiation and light winds, and neutral conditions with cloudy skies or high wind speeds. The net radiation inden used with wind speed to obtaia stability class is determined by the following procedure
- 1) If the total cloud cover is 10/10 and the ceiling is less than 7000 feet, use net radiation index equal to O (whether day or night).
- 2) For night-time (night is defined as the period from one hour before sunset to one hour af ter sunrise):
a) If tot.sl cloud covers /10, use net radiation inder equal to -2. b) If total cloud covery4/10, use net radiation index aqual to -1.
- 3) For daytime r a) Determine the insolation class number as a function of solar altitude from Table A-2.
b) If total cloud cover $5/10 use the net radiation inder in Table A-1 corresponding to the insolation class number. c) 12 cloud cover >5/10, modify the insolation class number by following these six steps:
- 1) Ceiling 47000 f t, subtract 2.
- 2) Ceiling 2:7000 f t but4.16,000 f t, subtract 1.
- 3) Total cloud cover equal 10/10 subtract 1. (This will only apply to ceilingsE7000 f t since cases with 10/10 coverage be low 7000 f t are considered in item 1 above.)
- 4) If insolation class number has not been modified by steps (1), (2), or (3) abovs, as9ume modified class number equal to insolation class number.
- 3) If modified insolation class number is less than 1. :et it equal 1
- 6) Use the net radiation inden in Table A-1 corresponding to the modified insolation class numbe .
ince urban areas do not became as stable in the louer layers as non-urban areas, stability etesses 5, 6 and 7 computed using the STAR ' fogram may be combined inte a single class (5), or classes 6 and 7 any be combined and identified as class 6 e -_ _ . - _ _ _ _ _ _ __ _ _ _ . - _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ . - - _ _ _ _ _ _ _ -____m -__-m--oegmm-y= -- e e w n- mm e,e- assem.,e---i__wi .m,m-eia m% e.w+-es_- eaus w. n m__ __--__,y,-o.-so- a,rw-=.mwm--em8esm amt., e m es e
w Prge 3 of 3 A STABILITY CIASSIHCATION BASED ON HOURLY AIRPORT OBSERVATIONS (CONT
- 0) (STAR PROGRAM) .
t TARLE A-1. STABILITY CIASS AS A FUNCTION OF NET RADIATION AND WIND SPEED WIND SPEED NET RADIATION INDEK (KNOTS) 4 3 2 1 0 -1 -2 0, 1 1 1 2 3 4 6 7 2, 3 1 2 2 3 4 6 7 4, 5 1 2 3 4 4 5 6 6 2 2 3 4 4 5 6 7 2 2 3 4 4 4 5 8, 9 2 3 3
- 4 4 5 10 3 3 4 4 4 4 5 11 3 3 4 4 4 4 4 3 4 4 4 4 4 4 2 12 TABLE A-2. INSOIATION AS A TLEON OF SOLAR ALTITUDE SCIAA ALTITUDE INSO1ATION (c0 INSOLATION CIASS f.LHBER .
Strong 4 60* t 4 Moderate 3 35 % ( 660* 15 *ug35' Slight 2 Weak 1 Q. 6 15*
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