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M".
EPA - LANSDOWNE PROJECT
CHARACTERIZATION REPORT
FOR
617, 619, 621, 623 PINE STREET
DarrellI. Turner
Performed by:
CHEM-NUCLEAR SYSTEMS, INC.140 Stoneridge DriveColumbia, SC 29210(803)779-0900
AR301526
_-*•".
TABLE OF CONTENTS
1.0 TITLE .............................................. 3
2.0 BACKGROUND ........................................ 32.1 Site History ....................................... 32.2 Preliminary Survey .................................. 32.3 CNSI Survey ...................................... 4
3.0 SURVEY METHODOLOGIES ............................... 43.1 Direct Exposure Rate Surveys ............................ 43.2 Fixed Contamination Surveys ............................ 43.3 Removable Contamination Surveys ......................... 43.4 Specific Activity Sampling .............................. 5
4.0 SAMPLE RESULTS ...................................... 54. 1 Direct Exposure Rate Survey ............................ 54.2 Fixed Contamination Survey ............................. 54.3 Removable Contamination Survey ......................... 54.4 Specific Activity Sampling .............................. 6
5.0 .,' CONCLUSIONS •. . . . . . • .: :. ."". ............... .". ........... 11
ATTACHMEi A7". r::i:".-:r:v.v > v-'VV- — • •' - •...: -•.......:.,• 14* " * •.•1'7*'V' ,;.•"• •*-• '<-"- • *-" ' _;. •' -. •• :"'-••*" .?>~'-~ft.
ATTAdHMENTB ..... ..... J ................................ 15
ATTACHMENT C ..........................•;............... 16
ATTACHMENT D .......................................... 17
LIST OF TABLESTABLE 4.1 ................................................ 7TABLE 4.2 ................................................ 8TABLE 4.3 ................................................. 9TABLE 4.4 ............................................... 10
AR30/527
1.0 TITLE
Characterization Report for 617, 619, 621, 623 Pine Street.
2.0 BACKGROUND
2.1 Site History
The property required radiological characterization of the structure, and wasperformed with the intent of determining what materials require removal torelease the structure for unrestricted use.
The contamination consists of natural radium an its parent and daughter products.The source of the contamination is a radium extraction process which operatedin Lansdowne between the years of 1915 and 1922. The sites were contaminatedduring the years 1915 to 1922, when tailings from the radium extraction processwere included in building masonry and plaster in place of sand. Sitecharacterization consisted of determining the levels of fixed and removableradioactive contamination in the structures. Surveys also included sample analysisto determine specific activity to satisfy safety, transportation, and disposalrequirements. :, ^ :-^, ; , • C
•2.2 Preliminary Surve '':'
The EPA has performed preliminary radiological surveys of the living areas ofthe property. The measurements were taken to assess exposure of the residentsto decide on the need for relocation, and were taken to access the need forrelocation, and were taken on beds and in locations where people spend themajority of their time. The measurements provided by the EPA includebackground levels of 10-15 /zR/hr.
These four houses (two semi-detached homes) are adjacent and were built aboutthe same time. Gamma levels on brick wall on the front porches are 180-280/iR/hr. Gamma levels on the brick veneer on the front wall appears to be themain area of contamination. Gamma levels in all four houses are similar, anddecrease toward the back of the houses. Gamma levels are 70 pR/hr in the livingroom centers, 40 pR/hr in the dining room centers, 30 /xR/hr on the bed in twobedrooms, 55 fiR/hr in a third bedroom, with a maximum of 80 pR/hr against afront wall.
Radon Level - < 4 pCi/liter
2.3 CNSI Survey ' • ;
The CWM survey team arrived at the property on April 13, 1992 atapproximately 9:25 AM, received a brief on the preliminary survey results,ventilated the property and commenced surveying in accordance with the Healthand Safety Plan and the Operations Plan. Surveys continued on April 14, 1992,and were completed on April 15, 1992 at 4:00 PM.
3.0 SURVEY METHODOLOGIES
Surveys and sampling activities were conducted in accordance with EPA - LansdowneSite Health and Safety plan and the EPA -Lansdowne Operations Plan. A briefdescription of the methods utilized is included below:
3.1 Direct Exposure Rate Surveys
Direct exposure rate surveys were performed to determine what material in eachproperty requires removal in order for the property to be released for unrestricted
3.2
Direct surveys were performed to determine what material in each propertyrequires removal in order for the property to be released for unrestricted use.These surveys were performed only as needed to conclude that (for example) theplaster in wall or a section of foundation must be* removed. Once a section ofwall or foundation has been found to be contaminated, it was assumed that thewhole wall or a whole linear section of building foundation was consideredcontaminated unless the contamination was highly localized.
Direct contamination surveys were performed using a HP-210 detector with anappropriate instrument. Direct contamination surveys were also performedutilizing a 2"x2" Na-I detector with an appropriate instrument.
3.3 Removable Contamination Surveys•
Removable contamination surveys were performed to determine the levels ofloose surface contamination that existed in the property. Removablecontamination surveys will be performed by wiping a smear over an area of 100cm2. Smears were counted on a Tennelec LB5100 automated Alpha/Beta countingsystem in an oil-site laboratory.
PINE STREET - Revised Page (5/15/92)
3.4 Specific Activity Sampling
To the maximum extent possible, gamma spectroscopy was be used to determineradionuclide content and specific activity. Samples of hidden areas were takenas needed to assure that removal of an affected building component would besufficient. For example, once it was determined that the plaster is contaminated,it was necessary to remove a small sections of the wall to examine theradiological content of the underlying structure (studs, etc.). Samples of anymaterial (stucco, plaster, mortar, etc.) found to be contaminated were also takento assure necessary information for safe removal, transportation and disposal havebeen obtained.
4.0 SAMPLE RESULTS
4.1 Direct Exposure Rate Survey
Exposure rate surveys were obtained using a Eberline PRM-7 micro-R surveyinstrument. The exposure rates were obtained on contact with all of the wallsinside the structure. The results of this survey are shown on theContamination/Radiation report contained in Attachment A.
4.2 Fixed Contamination Survey
Fixed contamination surveys were performed using a Eberline ESP-2 with a HP-210L beta/gamma geiger-muller probe. Fixed contamination surveys were alsoperformed using a Ludlum Model 2221 with a 44-10 2"x2" Na-I detector. Thefixed contamination reading were obtained on contact with all accessible surfacesin the structure. The results of this survey are shown on theContamination/Radiation report contained in Attachment A.
4.3 Removable Contamination Survey
Removable contamination surveys were performed by wiping a smear over anaverage area of 100 cm2. Smears were counted on a Tennelec LB5100 automatedAlpha/Beta counting system in an on-site laboratory. The results of this surveyare shown on the Contamination/Radiation report contained in Attachment A.
AR30I530
4.4 Specific Activity Sampling
Various samples v. '.re obtained in areas with elevated count rates/exposure ratesand counted on a nigh purity germanium Qscector in an on-site laboratory. Dueto the difficulties involved with obtaining a constant sample geometry, the resultsare only accurate within the percent error listed on the report. The results ofthese samples are shown on the Contamination/Radiation report contained inAttachment A, a brief summary of these samples is also provided in Table 4.1 to4.4.
>; v v ^ M ^ ^ ^ * ' "
4R30I53I
TABLE 4.1SPECIFIC ACTIVITY SAMPLES
617 PINE STREET
04/13 Exterior B. Wall 8' r SX cornar 5' F ground 9 14.2 0 NO mortar
Bast Ext. Hall 4' T n cornar 6r F ground 7 12.3 109 22 nortar
Kitchen West Wall 30 IX.9 92 30 aortarNorth Wall of chimnn«y b«t 2 Layer* at brick 5 13.7 51 29 mortar
North Wall I edge of chlmmney Exterior S 10.7 30 30 mortarStairs to basement West Wall , - ; , : . '* " 77 15.fi 0 MO plaster.
South Wall of laundry Room mortar,,> door.,>.,.;.• ..-•*:•'-.' 32 14..0 65 31 mortarKitchenWorth.
' •' '''fl _' 2nd Brick wall S side I»t" ro"k"iiia«nfrt"door Jamb ""•',:'""'"-; tj "23.0 122 20 mortar _
. • • : .•.•.;,*.c: ..~ $ r : - :\ .&• -.;.-.*;- .-•"-•'.•.•'•.• i'- ?• - • •"'--- • • '• ' " 'r •1st Ft South sid*'Bxt. l B'of front door- " ' ' - • "11 31.3 477 10 mortar
' '" ;'' ''J ,. '.'-• ••
Baaenent Bast Wall 70 ur/hr , .. ... =88 32.0 0 HD red BricJe
04/14 Basement West Wall 100 ur/hr 86 35.8 59 II mortarWest Wall Stairway 80 ur/hr 40 81.0 46 22 mortarBasement South Wall ISO or/or 35 84.0 65 IS mortar
S Side Ext Brick Wall B side of frt door jamb 12 15.5 671 11 mortar
SD » <MDA typical I 15-20 pci/g
» Hot* lr Du« to inconsistent geometric considerations with the efficiency calibration and low samplevolumes the reported Ra226 activities must be considered approximate values 77UU.
AR30I532
TABLE 4.2SPECIFIC ACTIVITY SAMPLES
619 PINE STREET
03/26 lit PL South side Exterior mortar 2' W of frt door 14 20.4 490 10 mortarEast Wall 23 14 101 23 plaster
East"Wail mortar between bricks 23 20.3 192 19 mortar
Basement South Wall 50 16. 0 HO
South Side Ext. I W Side door jamb 13 13.2 664 10 mortarExterior West Wall SW corner 1 13.3 0 VD mortarExterior Morth Wall by door 4 14.8 72 10 mortar
Morth Wall window'' -: 4 :.:.-'.' 1« 11-3 S4 27 mortar..-• -,.'•• ;;*. .-, . '-I*'; >•• , ' . • •- . '.-V "''"; .-'2nd FL South Bedroom West Wall " . . • 42 16. S 462 13 mortar
' ' '13.1
* note It Due to' inconsistent geometric considerations vita the efficiency calibration and low sample. f .""*•• " *i •* "* . . . - . _ . _ • • ^ _~~— ~
volumes the reported Ra22S activities must be considered approximate values 77UJL
8
AR30I533
TABLE 4.3SPECIFIC ACTIVITY SAMPLES
621 PINE STREET
04/14 Exterior East Wall 4- deep (inside mortar) 4 16.3 0 HO mortar
Exterior Bast wall 4 11.2 28 24 mortarBasement TL South Room 70 10.5 0 SO concreteExterior South Wall 27 13.0 507 22 mortarBasement Southwest Corner 73 15.3 95 19 mortar
Kitchen E Wall HE corner behind plaster wall 23 14.1 0 HD mortar
Basement mortar South Wall 80 16.5 0 HO mortar
Living Rm Bast Wall 3 14.1 192 17 mortar' • i^ .-' ••-•'••:. • ; -
Exterior South. Wall 4" deep inside layer - 27 18.0 567 18 mortar
Hot* Ir'Due to 'inconsistent.'geometric: considerations with the efficiency- calibration and low sample' •••' .-'•'•>*-:--- ^ •'- "•-.:••• • ."••- • • ••«t?;volumes the reported Ra226 activities must be considered approximate values TTU t
" " ' "
TABLE 4.4SPECIFIC ACTIVITY SAMPLES
623 PINE STREET
04/13 Porch Horth Wall 27 20.2 90 18 mortar
Basement West Wall 62 12.4 7 53 mortar MDA I 3 pc/c
Basement South Wall 61 15.9 384 27 mortarBasement East. Wall Horth Corner 66 8.9 0 HO mortar
South Bedroom West Wall-behind plaster 37 13.9 109 17 mortar
Basement East Wall Center 58 12.2 0 HO mortar
Horth ndroom East Wall 28 12.3 68 58 mortar
Exter .r Horth Wall next to chimmney 1 12.0 18 40 mortar HDA. I • pc/<
Exterior Horth Wall Below 2nd FL window 14 13.5 38 23 mortar
Exterior West Wall I Bathroom window 2nd Story 12 10.5 107 26 mortar
South Bedroom Bast Wall behino. plaster , 7 35 16.5 406 10 mortar
South Bedroom West Wall .••'•-;: i ., ••- -.r^--:!\i ';•'•;;:, .->.:..'--v 37 7.4 ,'_, 0 HD plasterSouth
Basement Bast Wall South Corner; red.brick
.,..• ^ -. . , '•/ HD » <MDA typical I 15-20 pci/g
.--. ;.'.,.,f.' -. ' -..»> ' * . • - _: _
* Hot* li Due to inconsistent geometric considerations with the 'efficiency calibration and low samplevolumes th* reported Ka22S activities must b* considered approximate values 77U«fc
10
flR30i535
5.0 CONCLUSIONS
The conclusions below have not taken into account the economic feasibility ofdecontamination and repair of each component. These conclusions are limited toidentification of which building components must be removed to allow for release of thestructure for unrestricted use.
5.1 617. 619 Pine Street
Based on Survey results the following building components (but not limited to)must be removed to allow for release of the structure for unrestricted use:
SOUTH EXTERIOR BRICK WALLS OF BOTH HOUSES
v o - The mortar between the bricks in die south wall from the ground level up to the roofline. Both the inner and outer brick layers are affected. Based on survey datacontamination appears uniform throughout the entire wall. Samples obtained from this. location are listed below:
Sample 13 = 664pCi/gram . >v( .Sample 12 = .,,671 pCi/gram . ;': 7
•---,.• • Af w- - ^ -' c f ^ v x: :-: ,:,.:,--••• rFIRE WALL BETWEEN HOUSES • .ffi£%&- : *..-;.
.-J, . ,. • , ...r,~-- o -*"- 'tr,' The mortar between the bricks m me both, sides of the fire waD. The facing plaster alsa
" '•,' • ' '.„••-,• - ' * .<**•/ *,•*«.• ' ' '-- , i 1*1 • ' "*--i •£• £ aV Jj.." " * l ••"" *:'. * f> ';-•V • • t °
~ "appears affected.. Based on survey data contamination appears uniform throughout the'•/'-"' " entire wall. "Samplesobtained;fiom thur focatioa are listed below:
Sample 23 = 192 /jCi/gram (mortar)Sample 23 - 101 pCi/gram plaster)
NORTH FACE OF BOTH HOUSES
o - The mortar between the bricks in the double brick wall on the norm face of both houses.The contamination b limited to a one foot band (approximately 5-6 bricks wide) atapproximately 6 feet from the ground. The band runs the entire length, of the north sideof both houses. Based on survey data contamination appears to be localized to the onefoot band of bricks. Samples obtained from this location are listed below:
Sample 6 = 168 pCi/gram (mortar)
11
4R30I536
WEST FACE OF DUPLEX
o - The mortar between the bricks in the double brick wall on the west face of the duplex.The contamination is limi* to a one foot band (approximately 5-6 bricks wide) atapproximately 6 feet from the ground. The band runs the entire length of the west sideof the duplex. Based on survey data contamination appears to be localized to the one footband of bricks. Samples obtained from this location are listed below:
Sample 6 « 168 pCi/gram (mortar)
EAST FACE OF DUPLEX
o - The mortar between the bricks in the double brick wall on the east face of the duplex.ontamination is limitH to a one foot band (approximately 5-6 bricks wide) at
s. ornately 6 fee Tom the ground. The band runs the entire length of the east sidet duplex. Basec a survey data contamtnati* - appears to be localized to the one footbaaa of bricks. Samples obtained from this locaaon are listed below:
Sample 7 - 109 pCi/gram (mortar)
5.2 621. 623 Pine Street T V ::. •> *.'•*& •-•- V'--. • ".-••.- • •• "f*%*. :"%-: • .• . •
Based on Survey results the following buflding components (but not limited to) must be removedto allow for release "of die strux ure Jfoj-u Mtrictod use: -~ ,.
'*'''o - The mortar between die bricks in the south wall from the ground level up to the roof
line. Bom the inner and outer brick layers are affected. Based on survey datacontamination appears uniform throughout the entire wall. Samples obtained from thislocation are listed below: •'.'_ .Jv sf '" '\
Sample 27 = 567 /jCi/gram".
WEST EXTERIOR WALL OF 623 PINE• - v ''.•'*•'?'.'.'' ~ ~
o - The mortar between the bricks in the west wall of 623 Pine. Based on survey datacontamination appears uniform throughout the entire wall. Samples obtained from thislocation are listed belowr ..' 5 .
Sample 12 =- 107 pCi/gram
EAST EXTERIOR WALL OF 621 PINE -
o - The mortar between the bricks in the east wall of the 621 Pine. Based on survey datacontamination appears uniform throughout the entire wall. Samples obtained from thislocation are listed below:
Sample 3 — 192 pCi/gram (sample taken through living room wall)
12
AR30I537
SOUTH BASEMENT WALLS OF 621, 623 PINE
o - The mortar from between the stones in the south basement walls of both houses. Basedon survey data contamination appears uniform throughout the entire walls. Samplesobtained from this location are listed below:
Sample 73 - 95 pCi/gramSample 61 » 384 pCi/gram
o - The mortar from between the stones in the south west comer of the basement wall of 623Pine. Based on survey data contamination appears localized and extends approximatelytwo feet down the west wall from the south wall. Samples obtained from this locationare listed below:
Sample 62 = 7 pCi/gram
Note: The contamination appears limited to where the south wall was tied in to thewest wall.
13
flR3QI538
ATTACHMENT A
CONTAMINATION/RADIATION REPORT
FOR
617, 619 PINE STREET
14
AR30I539
06/B/Z 'ABU f afiej
6UG-JU-SJ
06/B/2 'A3y f afiejximauv
AR30I5U2
flR3QI5U3
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617 PINE ST.SAMPLE DESCRIPTIONS
SAMPLE f DESCRIPTION
85 BASEMENT, MORTAR FROM SOUTH WALL ABOVE WINDOW
86 BASEMENT, MORTAR FROM WEST WALL IN SOUTHWEST CORNER
83 BASEMENT, MORTAR FROM EAST WALL IN SOUTHEAST CORNER
40 MORTAR FROM WEST WALL OF STAIRWAY
12 > EXTERIOR, MORTAR FROM EAST SIDE OF DOOR JAMB ON SOUTH WALL
11 EXTERIOR, MORTAR FROM SOUTH WALL 1' EAST OF DOOR JAMB
27 KITCHEN, PLASTER FROM EAST WALL
77 STAIRWAY TO BASEMENT, PLASTER FROM WEST WALL
32 MORTAR FROM SOUTH' WALL OF LAUNDRY ROOM
9 EXTERIOR/ MORTAR FROM EAST WALL, 3' FROM SOUTHEAST CORNER.• • • . . . " - • Vfr aM ftiSsSSE '-
30 ...... KITCHEN,. .'( MORTAR. BEHJTO 'PtASTBS t gV-WJiST, , WRLL CM ; .'- ..i... •
6 EXTERIOR, ' MORTAR FROM NORTH WALL AT NORTHEAST CORNER.' -• . .-,.%S-:;t ': < _,&Z-' & s.---i"'.- _ :fJ.&?i •• - . •• .- -
7 EXTERIOR, MORTAR 'FROM EAST WALL, 4' FROM NORTHEAST CORNER
5 EXTERIOR, MORTAR AT EDGE OF CHIMNEY ON NORT- WALL
5 EXTERIOR, MORTAR AT EDGE OF CHIMNEY, SECOND ..RICK LAYER
AR3015I45
7
619 PINE ST.SAMPLE DESCRIPTIONS
SAMPLE * DESCRIPTION
50 BASEMENT, MORTAR FROM SOUTH WALL AT WINDOW
23 PLASTER FROM EAST WALL OF STAIRWAY
23 MORTAR FROM BRICK WALL BEHIND EAST PLASTER WALL OF STAIRWAY
13 EXTERIOR, MORTAR FROM WEST SIDE OP DOOR JAMB ON SOUTH WALL
14 - EXTERIOR, MORTAR 2' WEST OF DOOR JAMB ON SOUTH WALL
1 EXTERIOR, MORTAR FROM WEST WALL AT SOUTHWEST CORNER
4 EXTERIOR, MORTAR FROM NORTH WALL BY DOOR
13 EXTERIOR, .MORTAR AT EDGE OF WINDOW ON NORTH WALL
42 MORTAR BEHIND PLASTER ON WEST WALL OF SOUTH BEDROOM
43 " _: MORTAR?BBH^ PIJ«£T bN BEDROOM
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WED APR 15, 19920RUUP A BACKGROUND
_S AMPLE_____TIME______ALPHA_____BETA______ALPHA______BETA TOD CLOCK. S N CODE (MIN.) COUNTS COUNTS______CPH______CPH HR:MN:SEC
OPERATION COMPLETE
WED APR 15, 1992GROUP F 617
SAMPLETOD CLOCKSN CODEHR:MN:SEC
17 1309:18:18
/- 1409:20:38
7 1509:22:58
V-167 175' 18
^Y- 19 'm> 20wn 21?r 22*'» 23a $ 24/Z-25If 26Z<-27#•28/V29/?30£/ 31/ 35
/$ 362/37,?/ 38
PINE SMEARSTIME
(MIN.)
2.00
2.00
2.00
2.002.002.002.002.002.002.002.002.002.002.002.002.002.002.002.002.002.002.002.00
00110000000001000100
ALPHA
COUNTS
0
2
0
43411313324242142532
BETA
COUNTS
-0.08-0.080.420.42
-0.08-0.08-0.08-0.08-0.08-0.08-0.08-0.08-0.080.42
-0.08-0.08-0.080.42
-0.08-0.08
2
2
2
0.800.300.80-0.70-0.700.30-0.700.300.30-0.200.80-0.200.80
-0.20-0.700.80
-0.201.300.30-0.20
ALPHA
CPM
-0.08
0.92
-0.08
-.24242424-.242424241.27272731.2727273-.24242424-.24242424-.24242424-.24242424-.24242424-.24242424-.24242424-.24242424-.242424241.2727273-.24242424-.24242424-.242424241.2727273-.24242424-.24242424
BETA
CPM
-0.20
-0.20
-0.20
2.50.9375
2.5-2.1875-2.18750.9375-2.18750.93750.9375
. -0.6252.5
-0.6252.5
-0.625-2.1875
2.5-0.6254.06250.9375-0.625
ALPHA
CORRECTED
-.24242424
2.7878788
-.24242424
09:25:1809:27:3809:29:5809:32:1809:34:3809:36:5809:39:1909:41:4009:44:0209:46:2309:48:4409:51:0609:53:2709:55:4809:58:0910:00:3010:02:5210:05:1210:07:3210:09:52
BETA. __ —
CORRECT
-0.62
-0.62
-0.62
OPERATION COMPLETE
AR30I579
24( ''' ° 8 ' -l26666667 .0.937!14:S1*07 ^ -
"'*<" ;
OPERATION M ' :.y' .-:- >M;fe?~:*M:?i •, , -. ... ._ :;. v
?-^'*" '"''•' ' " ", V*M /y.
TUE APR 14, 1992GROUP F 619 PINE '
SAMPLE TIME ALPHA BETA ALPHA BETA ALPHA BETATOD CLOCK .... *.SN CODE (MIN.) ; <: COUNTS COUNTS CPM CPM CORRECTED CORRECTEHR:MN:SEC ..' /
2.00 ; .0 2 -0.08 -0.20 -.26666667 -0.62!,14:23:04 :;
2.00 .0 6 -0.08 1.80 -.26666667 5.62!14:25:2415 v 2*00 0 4 -0.08 0.80 -.26666667 2.!14:27:4416 2.00 . 3 6 1.42 1.80 4.7333333 5.62!14:30:05 . ;,
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ATTACHMENT B
CONTAMINATION/RADIATION SUMMARY
FOR
617, 619 PINE STREET
(1 Page)
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ATTACHMENT C
CONTAMINATION/RADIATION REPORT
FOR
621,623 PINE STREET
(36 Pages)
16
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621 PINE ST.SAMPLE DESCRIPTIONS
SAMPLE # DESCRIPTION
27 EXTERIOR SOUTH WALL MORTAR PROM INSIDE BRICK LAYER 4" DEEP
27 EXTERIOR SOUTH WALL MORTAR FROM FIRST BRICK LAYER
4 EXTERIOR EAST WALL MORTAR FROM FIRST BRICK LAYER
4 EXTERIOR EAST WALL MORTAR FROM INSIDE BRICK LAYER 4" DEEP
73 BASEMENT, MORTAR FROM SOUTH WEST CORNER
70 BASEMENT, CEMENT FROM FLOOR IN SOUTH ROOM
23 KITCHEN, MORTAR BEHIND PLASTER WALL IN NORTH EAST CORNER
80 BASEMENT, MORTAR FROM SOUTH WALL
3 LIVING ROOM, MORTAR BEHIND PLASTER ON EAST WALL
AR30I589
623 PINE ST.SAMPLE DESCRIPTIONS
SAMPLE f DESCRIPTION
35 SOUTH BEDROOM, PLASTER FROM EAST WALL
35 SOUTH BEDROOM, MORTAR BEHIND EAST PLASTER WALL
58 BASEMENT, PLASTER FROM EAST WALL IN CENTER
58 BASEMENT, MORTAR FROM CENTER OF EAST WALL
59 BASEMENT, BRICK FROM EAST WALL IN SOUTH CORNER
62 BASEMENT, MORTAR FROM WEST WALL
61 BASEMENT, MORTAR FROM SOUTH WALL
37 SOUTH BEDROOM, MORTAR BEHIND PLASTER IN WEST WALL
37 SOUTH BEDROOM, PLASTER FROM WEST WALL
27 PORCH, MORTAR FROM NORTH WALL
66 BASEMENT, PLASTER FROM NORTH CORNER OF EAST WALL
66 BASEMENT, MORTAR BENEATH PLASTER IN NORTH CORNER OF EAST WALL
1 EXTERIOR NORTH WALL, MORTAR NEXT TO CHIMNEY
12 EXTERIOR WEST WALL, MORTAR BENEATH BATHROOM WINDOW
28 NORTH BEDROOM, MORTAR BENEATH PLASTER IN EAST WALL
14 EXTERIOR NORTH WALL, MORTAR BELOW SECOND FLOOR WINDOW
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SAMPLE TIME ALPM " B E T A ALPHA' /' BETA TOD CLOCKSN CODE (MIN.) COURTS J^COUNTS CPM CPM HR:MH:SEC
/f
OPERATI
WED APR 15, 1992GROUP F 621 PINE SHEARS
SAMPLE TIME ALPHA BETA ALPHA BETA ALPHA BETA TOD CLOCKSN CODE (MIH.) COU8TS " COURTS CPM CPM CORRECTED CORRECTED HR:«H:SEC
2.00 0 4 -0.08 0.80 -.24242424 2.5 13:29:28''?14 2.00 0 4 -0.08 0.80 -.24242424 2.5 13:31:48/«?15 2.00 0 3 -0.08 0.30 -.24242424 0.9375 13:34:08?M6 2.00 0 6 -0.08 1.80 -.24242424 5.625 13:36:28; 17 2.00 1 2 0.42 -0.20 1.2727273 -0.625 13:38:48W 18 2.00 0 4 -0.08 0.80 -.24242424 2.5 13:41:087? 19 2.00 0 1 -0.08 -0.70 -.24242424 -2.1875 13:43:285<~20 2.00 0 2 -0.08 -0.20 -.24242424 -0.625 13:45:48-V21 2.00 0 3 -0.08 0.30 -.24242424 0.9375 13:48:08f, 22 2.00 0 4 -0.08 0.80 -.24242424 2.5 13:50:294^23 2.00 0 0 -0.08 -1.20 -.24242424 -3.75 13:52:49%C 24 2.00 0 2 -0.08 -0.20 -.24242424 -0.625 13:55:09<T-?25 2.00 0 2 -0.08 -0.20 -.24242424 -0.625 13:57:297 26 2.00 0 4 -0.08 0.80 -.24242424 2.5 13:59:49? 27 2.00 0 6 -0.08 1.80 -.24242424 5.625 14:02:08
OPERATION COMPLETE
BR30I6I8
3C,
»n> APR 15, 1992"P"'T F 623 PINE SMEARS
FAmtE TIME ALPHA BETA ALPHA BETA ALPHA BETA TOD Ct,nCKm CODE (BIB.) COUNTS COURTS CPH CPH CORRECTED CORRECTED HR:MN:SEC
/'/ I 2.00 0 5 -0.08 1.30 -.24242424 4.0625 16:29:2610 7 2.00 0 3 -0.08 0.30 -.24242424 0.9375 16:31:16// 1 2.00 1 3 0.42 0.30 1.2727273 0.9375 16:34:0620 1 2.00 0 2 -0.08 -0.20 -.24242424 -0.625 16:36)2627 s 2.00 0 3 -0.08 0.30 -.24242424 0.9375 16:38:17/Z.6 2.00 0 2 -0.08 -0.20 -.24242124 -0.625 16:41:072? 7 2.00 0 3 -0.08 0.30 -.24242424 0.9375 16:11:27/$ B 2.00 0 0 -0.08 -1.20 -.24242424 -3.75 16:45:47.75"? 2.00 0 3 -0.09 0.30 -.24242424 0.9375 16;48:07# 1" 2.00 0 5 -0.08 1.30 -.24242424 4.0625 16!50!2fl(f M 2.00 0 1 -0.08 -0.70 -.24242424 -2.1875 16:52:48/ P 2.00 0 t -0.08 -0.70 -.24242424 -2.1875 16:55:085.7 M 2.00 0 2 -0.08 -0.20 -.24242424 -0..625 16:57:28
I 2.00 1 3 0.42 0.30 1.2727273 0.9375 16:59:49i 2.00 0 3 -0.08 0.30 -.24242424 0.9375 17:02:09i 2.00 0 1 -0.09 -0.70 -.24242424 -2.1875 17:04:29' 2.00 0 0 -0.08 -1.20 -.24242424 -3.75 17:06:19
31 IB 2.00 0 0 -0.08 -1.20 -.24242424 -3.75 17:09:09£/ H 2.00 0 2 -0.08 -0.20 -.24242424 -0.625 17tll:30i,2?.n 2.00 0 4 -0.08 0.80 -.24242424 2.5 17:13:50(,{,71 2.00 0 1 -0.08 -0.70 -.24242424 -2.1875 17tl6:ll$<jn 2.00 0 3 -0.08 0.30 -.24242424 0.9375 17818:31£_}2.1 2.00 1 2 0.42 -0.20 1.2727273 -0.625 17:20:51
'TF.PAT10B COMPLETE
flR30!6!9
ATTACHMENT D
CONTAMINATION/RADIATION SUMMARY
FOR
621, 623 PINE STREET
(1 Page)
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