-------
FIELD CORE OBSERVATIONS AMD VELOCITY MEASUREMENTS
FILE HAMS: OU.OG8
CORK NO: (
STATUS (CUT/NOT CUT) : COT
SITE: QUEEN ELIZ. PARK OUTSIDE LOWER
POSmOH: H:.
CORE LENGTH - HATERrSEDIMENT:
CORE LBNGTTH - SEDIMENT:
WIGHT TOTAL CORE:
TARE WEIGHT: 1.2S LB
OFFSET HEIGHT: 0.125 LB
CORE TUBE HEIGHT: 0.01176
COMPUTED DSNSITT: 2.40 GM/OfJ ESTIMATED
VELOCnT/DIELSCTRIC
From Rec . Poซ . Xmic Poซ . RBC . Rec . Delay Dielect Commanti
Boccoo-cm cm cm Gain Arnpl . Microsec aic. farad
_ I _ I _ I _ I _ I _ I _ I _
HO CORE RETENTION ROCKS AND SAND ABSOLUTELY NO PENETRATION
A4-23
-------
FIELD CORE OBSERVATIONS AND VELOCITY MEASUREMENTS
FILE KAME: CXLOG9
COKE NO: ป
STATUS (CDT/NOT CDT) : CDT
SITE: QUEEN BLI2. PARK OUTSIDE LOHER
POSITION: >:
COU LENGTH - HATER+SEDIKENT:
COM LENGTH - SEDIMENT:
WBICBT TOTAL COM:
TAM VBIGHT: 1.2S LB
OFFSET HEIGHT: 0.125 LB
COM TUBE WEIGHT: 0.01176 CM/CM*3
COMPUTED DEKSmf: 2.40 (W/OTS ESTIMATED
VSLOCITT/DIBLECTRIC
Dilt From Rec. Poซ. Zmit Pos. Rec. Rec. Delay Dialect Comment*
Boccoa-cm cm cm Gain Anpl. Hicrocec ode.farad
I I I I I I I
NO CORE RETENTION ROCKS AND SAND ABSOLUTELY NO PENETRATION
A4-24
-------
FIELD COM OBSERVATIONS AND VELOCITY MEASUREMENTS
FILE NAME: CRLOG10
CORE 2(0: 10
STATUS (CUT/NOT CUT) NOT COT
SITE: O.OEEN ELIZ. PARK NORTH END LINE 1
POSITION: N:.
CORK LENGTH - MATERปSEDIMENT: 128 ca Saturated cloth in botcoa
COU LEHCTH - SEDIMENT: 37 em sediment ป 4 CO fluff
WEIGHT TOTAL CORE:
TARE WEIGHT:
OFFSET WEIGHT:
CORE TUBE WEIGHT:
COMPUTED DENSITY:
1C.25 lbป (include* cor* catcher and 142 core tube)
1.2S LB Core Catcher - 100 gmซ.
0.125 LB
0.01176 GM/CM~3
VELOCITY/DIELECTRIC
Dilt Pro* Rec. Pol. Xmit Pot. Rec. Rec. Delay Dielect C
Bottov-cn cm cm Gain Ampl. Microeec mic.farad
I I I I I I I
Water SO.O 50.0
52.2
48.1
93
101
104
190
Fluff
36.5
37.2
36.5
92
82
Sediment 30.1 29.4 1300 4
26.2
31.0
52
94
56
94
120
ISO
52
94
15.0 13.0
12.5
1300 2
52
70
lie
52
100
27.5
25.0
25.0
4B
96
ISO
42
98
Mote: Appears Co be at least a 14 microsec *ystem delay
- I I I I I I
A4-25
-------
FIELD CORE OBSERVATIONS AMD VELOCITY MEASUREMENTS
PILE NAME: CRLOG10A
COM MO: 10 CONT'
STATUS (CUT/HOT CUT) MOT CUT
SITE: QUEEN ELIZ. PARK EKD LIKE 1
POSITION: ฅ:_
COU LENGTH - HATER.SEDIMENT:
CORE LENGTH - SEDDtEHT:
MXIOHT TOTAL COU:
TARS WEIGHT: 1.25 L8
OFFSET WEIGHT: 0.125 LB
CORE TDBE WEIGHT: 0.01176 GM/CM*3
COMPtTTED DENSm: 1.S33 GM/CM*3 TO 1.56 COMPENSATE FOR CLOTH
VELOCITY/DIELECTRIC
Dilt Prom Rec. Pos. Xrair Pos. Rec. Rec. Dซlay Dielect Cocraents
Bottom-cm cm cm Gain Ampl. Microsec pCd
I I I I 1 I I
DIELECTRIC
ZERO LEADS SO. 2
wacer S7.0 107
SO.O 107
Foam 39.0 105
Core Sed 28.0 106
1S.O 107
EMPTY COR2 TUBE
28.0 101
16.0 100
A4-26
-------
FIELD CORE OBSERVATIONS AND VELOCITY MEASUREMENTS
FILE NAME: CRLOGll
CORE NO: 11
STATUS (COT/NOT CUT)
SITE: BLACZ LAGOON LOWER
POSITIOB: ฅ:.
CORE LSHCTH - MATER*SEDIMENT: NONE
CORE LENGTH - SEDIMENT:
WIGHT TOTAL CORE:
TARE WEIGHT:
OFFSET WEIGHT:
CORE TOTE WEIGHT:
COMPUTED DENSITY:
1.25 LB
0.12S LB
0.01176 GM/OT3
VELOCITY/DIELECTRIC
Dist Fro* Rec. Pol. Xmic Po<. Rec. Rec. Delay Dielecc Comments
Boccon-ca en cm Gain Ampl. Microsec mic.farad
.1 I I I 1 I I
BOTTOM - GRAVEL AND ROCK NO RECOVERY AT ALL
A4-27
-------
FIELD CORE OBSERVATIONS AND VELOCITY MEASUREMENTS
FILE NAME: CRLOG12
CORE NO: 12
STATUS (CUT/NOT COT) NOT O3T
SITE: BLACK LAGOON LINE 1C 94 METERS INTO LINE
POSITION: N:
CORE LENGTH - WATER+SEDIMBNT: 139.7 CM
CORE LENGTH - SEDIMENT: ซ . 04 CM
WEIGHT TOTAL CORE:
TARE WEIGHT:
OFFSET WEIGHT:
CORE TUBE HEIGHT:
COMPUTED DENSITY:_
n.s LB
1.00 LB ป TOP DEVICE AND CORE CATCHER 2 LB
0.000
0.01176 GM/CM*3
VELOCITT/DIELECTRIC
Diet Prom Rec. Poป. Xnit Po*. Rec. Rec. Delay Dialect
Bottom-on cm cm Gala Ampl. Microsec mic.farad
.1 I I I I I I.
Comment:*
NOTE: 3/1S' OF WHITE CHALK LIKE SUBSTANCE
WATER 60
62
61
59
57
SEDIMENT
42
42
40
39
20
22
.0 61.0 1100 5
.8 4
.8
.5
.8
.5 42.0 1700 3
.0
.5 2
.0 1
.5 22.0 0.1
.0 0.1
ON SEDIMENT SURFACE
93
96
94
92
104
96
120
100
120
120
120
A4-28
-------
FIELD CORE OBSERVATIONS AND VELOCITY MEASUREMENTS
FILE KAMB: OU.OG12A
CORE HO: 12
STATUS {COT/NOT COT) : CUT
SITE: BLACK LAGOON LOWES 94 METER ON LINE 1C
POSITION: ป:
CORB LEHGTH - WATER*SEDIMEST: 12ป.S CM TOTAL CORE US. 2
CORE LEMGTH - SEDIMENT: 52.7 CM
WIGHT TOTAL CORE: 15. S
TARS WEIGHT: 1.00
OFFSET WEIGHT: O.OO
CORE TDBE WEIGHT: 0.01176 GM/OT3
COMPDTED DENSITY: 1.23 GH/CM*3
VBLOCITT/DIBLECTRIC
Diซc Froa Rec. Poซ. Imic Poi. Rec. Rec. Delay Dielect Comment*
Boccon-co cm cm Gain Ampl. Microsec mic.farad
I I I I I I I
NOTE: BOTTOM CORE BLACK GRAKU1AR MATERXAL
A4-29
-------
FIELD COKE OBSERVATZOHS AMD VELOCITY MEASUREMENTS
PILE NAME: CRLOG13
CORE MO: 13
STATUS (OJT/HOT CUT) HO SAMPLE ROCK AND GRAVEL
SITE: BLACX LAGOON - LINE 1C 71.8 METERS FROM START
POSITION: M:
CORE LEHGTH - ซATEJUSEDrMBNT:
CORE LZBGTH - SEDIMENT:
WEIGHT TOTAL CORE:
TARE WEIGHT: 1.25 LB
OFFSET WEIGHT: 0.123 LB
CORE TUBE WEIGHT: 0.01176 GM/CM'3
COMPUTED DENSITY:
VELOCITY/DIELECTRIC
Diปt Proa Rec. Poป. Xmlt Pos. Rec. Rec. Delay Dialect Comment*
Bottom-cm ca cm Gain Ampl. Microaec mic.farad
1 ! I I I I I
NOTE: POtOR SAMPLE - ROCK AND GRAVEL NO RETENTION
A4-30
-------
FIELD CORE OBSERVATIONS AND VELOCITT MEASUREMENTS
FILE NAME: CRLOG14
CORฃ MO: 1ซ
STATUS (CUT/NOT CDT) HO RETENTION ซ SAND/GRAVEL
SITE: BLACI LAGOON LOWER LINE 1C ฃ2.4 METERS FROM START
POSITION: N: 721C3.5 K: 4091740.5
CORK LENGTH - HATER*SEDIMENT: NO RETENTION ( SAND/GRAVEL
CORE LENGTH - SEDIMENT:
HEIGHT TOTAL CORE:
TARE HEIGHT: 1.2S LB
OFFSET WEIGHT: 0 .12S LB
CORE TUBE HEIGHT: 0.0117S GM/CM"3
COMPUTED DENSITY: 2.10 (EST)
VELOCITY/DIELECTRIC
Dilt From Rec. Po(. Imic Poa. Rac. Rec. Delay Dialect Comments
Botcom-cm cm en Gain Ampl. Microcec mic.tarad
I I I I 1 I
NOTE: HARD BOTTOM SAND/PEA GRAVEL 6' CORE - NO RETENTION
A4-31
-------
FIELD CORฃ OBSERVATIONS AKD VELOCITY MEASUREMENTS
FILE KAMEi OU.OG15
CQU HO: 15
STATUS (CUT/NOT OJT) CUT
SITS: BLAOC LAGOON LOWER - 27 METEBS STJl. 6 METERS PORT
POSITION: N: 7212! E: 4098734.3
CORE LENGTH - WATER+SEDINEHT: St.S
COM LENGTH - SEDIMENT: 51.4
WEIGHT TOTAL CORE: 13. 8125
TAKE WEIGHT: 1.00 LBS
OFFSET WEIGHT: 0.00 LBS
CORE TDBB WEIGHT: 0.01176 GM/CM*3
COMPUTED DENSITY: 2.00 GM/CM*3
VBLOCTTY/DIELECTRIC
Ditc From Rec. Poป. Xmic Pos- Rec. Rec. Delay Dielact Comments
Boccom-cm cm cm Gain Ampl. Microsec mic.farad
I I I I I I I
NOTE: NO VELOCITY DATA TAKEN ON THIS CORE
CORE TO SHORT
NOT2: THIS WAS A DISTURBED CORE DENSITY ESTIMATE SLIGHTLY
HIGH
HOTS: UNCUT CORE DATA NOT GIVEN.
A4-32
-------
PIBLD CORE OBSERVATIONS AND VELOCITY MEASUREMENTS
TILS KAMI: CRLOG1S
CORE NO: 1C
STATUS (COT/NOT OJT) : COT
SITE: BLACK LAGOON LINE IS
POSITION: H: 73917.> B: 4098731.9
CORE LENGTH - WATZJUSEDIMENT:
COU LENGTH - SEDIKBNT: IS. 5 CM
WIGHT TOTAL CORE: 3 LB
TARE WIGHT: 1.00 LB
OFFSET HEIGHT: 0.00 LB
CORE TOTE WEIGHT: 0.01176 GM/CM*3
COMPUTED DENSITY: 1.22 GM/CM3
VELOCITY/DIELECTRIC
Diปt Prom Ree. Pos. Xaic Poซ. Rec. Rec. Delay Dielect Comments
Bottom-cm cm cm Gain Ampl. Microsec mic.Carad
I I I I I I I
MOTE: ONLY A VERY SHORT CORE WAS OBTAINED.
DENSITY BASED ON CUT CORE ONLY
NOTE: BECAUSE OF TEZ SHORT CORE NO VELOCITY MEASUREMENTS TAKEN
I.
A4-33
-------
FIELD CORE OBSERVATIONS AND VELOCITY MEASUREMENTS
FILE NAME: CRLOG17
CORE NO: 17
STATUS (COT/NOT COT) HOT CUT
SITE: BLACT LAGOON LOVER OLD CORE 11 SS.O METERS SOL 2.7 M STB.
POSITION: H: 72*42.2 E: 4091117.2
CORE LENGTH - WATERปSEDIMENT: 142.2 CM
CORE LENGTH - SEDIMENT: f0.1 CM HITH S CM OF AIR
WEIGHT TOTAL CORE: 19.5 LBS
TARE HEIGHT: 1.00 BNLBS
OFFSET WEIGHT: 0.000 LB WITH TOP PLUNGER AND CORE CATCHER 2 LBS
CORE TUBE WEIGHT: 0 . 0117S GM/CM~3
COMPUTED DENSITY: 1.33 GM/CM'3
VELOCITT/DIELBCTRIC
Disc From Rec. Poป. Xmic Poa. Rec. Rec. Delay Dielecc Comment*
Bottom-cm cm cm Gain Aapl. Microsec mic.farad
I I I I I I I
NOTE: CORE HAD 4 CM OF FOCDLENT MATERIAL ON TOP
NOTE: BECAUSE OF AIR CORE REDONE AS 119 AND NO VELOCITY TAKEN
VELOCITY REPEATED IN LABORATORY COMPLETE ABSORPTION
CONFIRMED BY tJSACE.
.1 I.
A4-34
-------
FIELD CORE OBSERVATIONS AND VELOCITY MEASUREMENTS
TILE NAME: CRLOG18
CORE NO: IS
STATUS (COT/NOT CUT) : NOT CUT
SITE: BLACK LAGOON LOWER OLD CORE SITE II
REPEAT OF CORE 17 52.2 METERS SOL - 1 METER STB.
POSITION: B: 77941.4 E: 4098813.9
CORE LENGTH - WATERปSEDIKฃHT: 142.a CM.
CORE LENGTH - SEDIMENT: 92.0 CM. * S CM FOAM
HAVE 7.C CM SPACE ON IOTTOM CORE
WEIGHT TOTAL CORE: 20.125 LB
TARE WEIGHT: 1.00 LB
OFFSET WIGHT: 0.00 LB
CORE TUBE WEIGHT: 0.0117S
COMPUTED DENSITY:
VELOCITY/DIELECTRIC
Diic Proa Rec. Poซ. Zmic Poซ. Rec. Rec. Delay Dielect Commencs
Boczoo-cm cm cm Cain Ampl. Microtec nic.farad
-I I I.
WATER 82 .
83.
79.
81.
SEDIMENT
66
65
64
47
46
42
.0 81.3 1000 5
.0 1100 S
.0
.4
.2 66.6 1700 2
MAX
.2
.2
.ซ 4S.7 1700 1
.7 0.5
JT 0.2
104
100
100
130
130
96
88
90
94
96
94
96
100
2S.7 26.7 1700 0.4 9<
145
2S.O 95
175
23.0 100
A4-35
-------
FIELD CORE OBSERVATIONS MID VELOCITY MEASUREMENTS
PILE NAME: CRLOG1IA
COU NO: II
STATOS (OTT/NOT CUT) : COT
SITE: BLACX LAGOON LOWER OLD CORE SITE II
REPEAT OF CORE 117 52.2 METERS SOL. 1 METER STB.
POSITION: H: 72941.4 I: 40MI13.9
CORE LENffTH - WATERซSEDIMENT: 130.1 CM.
CORE LEBCTH - SEDIMENT: 75.2 CM.
WIGHT TOTAL CORE: 17.437 LB
TARE WIGHT: 1.00 LB
OFFSET WIGHT: 0.00 LB
CORE TUBE WEIGHT: 0.01176 CM/CM*3
COMPUTED DENSITY: 1.S3 GM/OT3
VELOCITY/DIELECTRIC
Dice From Rec. Pot. Xmic Pot. Rec. Rec. Delay Dielect Coonencs
Boccom-n cm cm Gain Ampl. Microtec mic.farad
NOTE: THIS DATA USED FOR DENSITY CALCULATIONS
A4-36
-------
FIELD COM OBSERVATIONS AND VELOCITY MEASORBfiDTTS
FILE MAKE: CRLOC19
CORE NO: 19
STATUS (CUT/NOT CUT) HOT COT
SITE: BLACX LAGOON LOWER LIME 22 OLD CORE I 7
14.C METERS FROM SOL 2.4 METERS PORT
POSITIOH: N: B:_
CORE LEBGTH - HATER* SEDIMENT: 142.2 CM. 3-4 CM OF FOAM OK TOP
CORE UMGTH - SEDIMEHT: ซ.2 CM CORE CATCHES. STILL OV
PEHXTRATIOH IT HSIGTH OF CORE
EIGHT TOTAL CORE: 17.SC LB
TARE WEIGHT r 1.12S LB
OFFSET WEIGHT: 0.00 LB
CORE TUBE HEIGHT: 0.01176 GM/OT3
COMPUTED DENSITY:
VSLOCrrT/DIELECTRIC
Diปt From Rec. Pos. Xmit Poซ. Rซc. Rec. Delay Dielecc Comanti
Boctoa-co en en Gain Ampl. Microsec nic.farad
I I I 1 I I I
NOTE: VELOCITY MEASUREMENTS ON CUT CORE
BATSR 53.1 53.0 1130 4 94
140
53.6 1300 4 98
140
54.1 1400 4 98
136
54.7 XOO
136
53.6 96
134
52.2 94
140
51.4 104
175
AIR TEST 245
50.6 1700 3 120
170
50.6 51.1 1500 5 108
49.8 108
48.8 49.6 92
48.4 120
179
I.
A4-37
-------
FIELD COHฃ OBSERVATIONS AND VELOCITY MEASUREMENTS
PILE NAME: CRLOG19A
CORE BO: 19
STATUS (COT/NOT COT) : COT
SITE: BLACK LAGOON LOWER LIME 22 OLD COKE |7
84.6 METERS FROM SOL 2.4 METERS PORT
POSITION: N: E:
CORE LENGTH - MATBRปSEDIMEHT: 121.9 CM CORE TUBE LENGTH 131.4
CORE LENGTH - SEDIMENT: 44.45 CM.
WEIGHT TOTAL CORE:
TARE WEIGHT:
OFFSET WEIGHT:
CORE TUBE WEIGHT:
COMPUTED DENSITY:
14.C2S
1.12S LB
0.000 LB
0.01176 GM/CM
1.11 GM/CM'3
VELOC ITT/DIELECTRIC
Diซt From
Boccom-cm
I.
Rec. Poซ.
Xmlc Poป. Rec.
cm Gain
I I
NOTE: CONTINUATION OP VELOCITY ON CUT CORE
Rec. Delay Dialect
Aopl. Microeec Die.farad
.1
Comment*
SEDIMENT
41.7
1/2 WAT. 39.0
37.0
37.0
36.2
35.1
33.4
30.8
32.0
28.2
38.5
1100
36.7
33.2
29.9
1700
UT CORE
5
5
3
1
5
1
92 ON CUT CORE 40.5 SED TOP
170 IN MEASUREMENT Of TAPE
92 MEASURE.
150
96
ISO
90
145
112
138
100
110
130
HO SIGNAL
27.6
26.2
20.6
20.6
12.5
13.5
26.7
20.5
19.5
18.5
13.5
1700 0.1
0.1
0.1
1
ISO
125
100
140
102
ISO
108
110
124
A4-38
-------
Tvrrov CHANNEL coNDucnvrrr MEASUREMENTS
PURPOSE: PROVIDE DATA FOR EVALOXTTOH OP RADAR IOTORMATIOH
APPARATUS: Dale consiicfrd of 2 1.5*3* plat** with a mean
eparacion of 9.S*. Tbซ lead* connected to a
high impedance obaaeter.
RKFXBXNCS: Normal clean near 10,000 ohM
Area
Location Obi -1
Oba-2
Obe-3
Obi-4
Obi -5
Haas Obe
Podr Surface
Ivadiace Mid Point
after Bottom
torrn Air-Wet
Q . E . Prk Surface
Bottom
Hid Point
Air-Wet
Blk. L.tJp Air-Dry
Surface
Bottom
BUc.L.Dpp
over aacd Air -Dry
Surface
Bottom
Center (mud
Surface
Bottom
2SC4
2487
1992
90000
1080
1077
1150
300000
1700000
2SOO
2650
3000000
2400
ฃ000
2800
2000
2Sซ4
2417
1992
90000
0
1010
1077
1150
300000
0
1700000
2600 2700 2(80 2ESO 2626
2630 2625 2616 2604 2625
0
0
3000000
2700 2600 2567
ฃ000 7000 6333
0
2900 3200 2000 2725
1500 2000 7000 312S
Dock
Next day Air 1700000
Surface 10000
Boctoa 10000
11000
9000
12000
10000
11000
10200
1700000
11000
9800
A4-39
-------
APPENDIX AS
SELECTED CALIBRATION ANALYSIS
SHEETS AND LOGS
AVAILABLE FOR REVIEW AT U.S.EPS/CBSSS,
GROSSE ILE, MI.
-------
APPENDIX A6
AMPLIFIER GAIN CURVES
A6-1
-------
V program name gaincomp.m
% version 1.00
% written by ddc 10/4/95
% compute gain and check with actual gain,
p(l) = 0.0017;
p(2) = -0.0600;
p(3) = 0.8815;
p(4)= -7.0764;
p(5) = 33.884;
p(6) = -99.2424;
p(7) = 175.9008;
p(8) = -181.6657;
p(9) = 105.5041;
p(10) = -8.1394;
pf(l) = 2.5057;
pf(2) = 2.2370;
%load p;
%load pf;
^ for W = 1:30;
ro
tor W = 1:JU;
gnset = input('Input gain setting value x.xx = ');
if gnset <= 1.40
gn = polyval(p,gnset);
end
if gnset > 1.40
x = gnset-1.40;
gn = polyval(pf,x) + 20.7433;
end
if gnset > 5.00
gn = gn - ((gnset-5)*0.22);
end
load gain;
load gainset;
Page 1
-------
axis( [0 10 -10 40]);
hold on;
plot(gainset,gain.gnset,gn,' x1 );
title(['Gain versus Gain Setting ']);
xlabel('Gain Setting1);
ylabeK 'Gain (db) ' ) ;
text(7,20,num2str(gn));
pause;
hold off;
elf;
if gnset == 11
break;
end
end
I
CO
Page 2
-------
50 r
Gain Setting Vs. Gain - Amp #3
Gain Setting
A6-4
-------
APPENDIX A7
STANDARD SEDIMENT PROPERTIES TABLE
A7-1
-------
STANDARD MARINE UNCONSOLIDATED
GEOTECHNICAL AND ACCOUSTIC PROPERTIES
SPECIFIC GRAVITY SOILS ASSUMED 2.70 GN/CH'3
ITEM
MATERIAL TYPE
BULK UET DRY
DENSITY DENSITY DENSITY
t*
i
ro
1
1
2
3
4
5
6
7
a
9
10
11
I
I
COARSE SAND
MEDIUM SAND
FINE SANDS
VERY FINE SANDS
SILTY SANDS
SANDY SILT
SAND-SILT-CLAY
CLAYEY SILT
SILTY cur
CLAtEY SILT
CLAY
I I
2.70
2.700
2.700
2.700
2.700
2.700
2.700
2.700
2.700
2.700
2.700
_i 1-
I
2.05
2.010
1.960
1.910
1.B30
1.600
1.560
1.A30
1.400
1.380
1.260
1.
I
1.658
1.628
1.515
1.420
1.274
0.856
0.891
0.675
0.621
0.578
0.383
1
POROSITY MEDIAN IMPED. REFLECT. BOTTOM
X GRAIN SZ. Z
1
38.60
39.700
43.900
47.400
52.800
68.300
67.000
75.000
77.000
78.600
85.800
i
1 1
0.520 3740
0.356
0.153
0.090
0.073
0.036
0.018
0.006
0.003
0.006
0.001
i
3510
3440
3265
3060
2500
2490
2200
2150
2110
1890
1.
R LOSS-DB
0.410
0.385
0.375
0.352
0.320
0.214
0.250
0.177
0.159
0.150
0.090
(__
7.8
8.3
8.6
9.1
9.9
13.5
12.1
15.2
16.1
16.7
20.6
WATER
CONT. X
i
1 1
23.284
24.384
28.983
33.376
41.431
79.799
75.196
111.111
123.994
136.033
223.787
I
WATER CNT
X CHECK
23.658
23.457
30.719
34.488
43.597
86.938
75.084
111.852
125.443
138.837
228.638
POROSITY WET OEN.
CHECK CHECK
1 *
38.600
39.700
43.900
47.400
52.800
68.300
67.000
75.000
77.000
78.600
85.800
2.044
2.025
1.954
1.894
1.802
1.539
1.561
1.425
1.391
1.364
1.241
G = SPECIFIC GRAVITY
n ป POROSITY
w ซ WATER CONTENT
DD ซ DRY DENSITY
WD ซ UET DENSITY
DRY DENSITY G*(N-1)
UET DENSITY(CHECK) <1-n)*G t n
U * (1/DD - 1/G)*100
W(CHECK) - (UO/DO -DMOO = (n/OD)ซ100
n(CHECK) " (1-DD/G)ซ100
STANDARD MARINE SEDIMENTS GEOTECHNICAL PROPERTIES
-------
FINAL REPORT
MICRO SURVEY - ACOUSTIC CORE AND
PHYSICAL CORE INTER - RELATIONS WITH
SPATIAL VARIATION,
TRENTON CHANNEL OF THE DETROIT RIVER
VOLUME II
CORE ANALYSIS AND SUMMARY FINDINGS
prepared
March 23, 1996
By
David Caulfield
Caulfield Engineering, Incorporated
Oroville, WA
And
John C. Filkins
U.S. Environmental Protection Agency, Office of Research and Development
National Health and Environmental Effects Research Laboratory
Mid-Continental Ecology Division-Duluth
Community Based Science Support Staff
9311 Groh Rd., Grosse He, MI 48138
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This report was prepared for the U.S. Army Engineers Waterways Experimental Station under
contract No. DACW39-95-C-0070. This report meets one of the deliverables for the Interagency
Agreement, DW96947730-01-0, between U.S. ACOE/Waterways Experimental Station and U.S.
EPA/Great Lakes National Program Office and U.S. EPA/National Health and Environmental
Effects Research Laboratory/Mid-Continental Ecology Division-Duluth/Community Based
Science Support Staff.
11
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CONTENTS
1.0 INTRODUCTION 1
2.0 PROJECT DESCRIPTION 2
2.1 Background 2
2.2 Site Overview 2
2.3 Project Objectives 3
2.4 Experiment Design 4
2.5 Project Schedule 5
2.6 Quality Assurance Procedures 5
3.0 TECHNICAL APPROACH AND ANALYSIS PROCEDURES 6
3.1 Field Procedures 7
3.2 Analysis Procedures 7
4.0 DISCUSSION OF RESULTS 17
4.1 Core Densities and Core Locations 17
4.2 Standard Marine Acoustic Properties 17
4.3 Processed Seismic Data Summary 22
4.3.1 Calibration Procedure Verification 25
4.3.2 Bottom Loss Analysis 25
4.3.3 Amplitude Decay Ratio 30
4.3.4 Plus Sign Percentage 30
4.3.5 Acoustic Parameters Summary 35
5.0 DETAILED CROSS-SECTIONS AT CORE SITES 36
6.0 DIRECT CORE VELOCITY/ABSORPTION 38
6.1 Core Velocity Measurement Review 38
6.2 Core Absorption Observations 45
iii
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7.0 PRELIMINARY AREA FINDINGS 52
7.1 Elizabeth Park Summary 52
7.2 Black Lagoon Summary 54
8.0 CONCLUSIONS AND RECOMMENDATIONS 56
9.0 BIBLIOGRAPHY 58
APPENDIX
Bl Addendum - Appendix B1 Detailed Examples of Analysis at Each
Core Site Bl-1
B2 Summary of Acoustic Properties at Each Core Site B2-1
B3 Core Sites Cross-Sections B3-1
B4 In Field Core Velocimeter Data B4-1
B5 In Field Core Absorption Data B5-1
IV
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1.0 INTRODUCTION
Significant deposits of contaminated sediment occur in many waterways near
urban centers, including those of the Great Lakes basin. Some of these deposits have
accumulated for decades and reflect historic loadings of pollution from cities, industry
and agricultural runoff. These deposits continue to contaminate benthic and pelagic
organisms through various transport and fate processes. The removal, treatment and
disposal of these contaminants may be extremely costly.
A cost effective and rapid means of mapping the distribution of sediments in
harbors and rivers is required to facilitate the remedial decisions facing environmental
managers. Models are being developed to predict the potential for sediment erosion in
harbors and rivers. An accurate prediction of sediment resuspension by these models
requires accurate mapping of sediments.
This final report has been prepared in three volumes. Each volume was originally
delivered as an interim project report. Upon completion of the final volume the interim
reports were edited and a final report consisting of a three volumes set and executive
summary was prepared. The three volumes include:
Volume I: Field Activities and Calibration Documentation (December 30,
1995). This volume summarizes field acquisition and calibration
procedures. Highlights of the field activities, associated field logs
and corrected file navigation, and the results of an extended
calibration program are provided.
Volume II: Core Analysis and Summary Findings (March 23, 1996). This
volume relates the acoustic properties of the sediments to the
physical properties of the cores at selected sites.
Volume III: Normal and Contaminated Sediment Distribution Maps (May,
1997). Volume III provides final outputs identifying
contaminated layer cross-sections as well as estimated dredging
volumes. Also presented are new spatial analysis techniques
developed to accommodate the spatial variations and
contaminants/gas content of the Trenton Channel sediments.
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2.0 PROJECT DESCRIPTION
2.1 Background
Both the Army Corps of Engineers/Water Ways Experimental Station (USACE-
WES) and the U.S. Environmental Protection Agency/Office of Research and
Development/Mid-Continent Ecology Division/Community Based Science Support Staff
(USEPA/MED/CBSSS) have research interest in mapping sediment in harbors and rivers
by acoustic profiling. In 1994, the Great Lakes National Program Office, The Michigan
Department of Natural Resources and USEPA/MED/CBSSS conducted a sediment
survey by contract with Caulfield Engineering using the Acoustic Core0 system. The
survey of the Detroit River's Trenton Channel demonstrated that the Acoustic Core0
system has the potential for mapping the sediment in harbors and rivers of the Great
Lakes. The 1994 survey results identified high spatial variance in sediment distribution
and possible gas content in these sediments. The acoustic method required optimization
for use in shallow water (2 ft. to 30 ft.) and areas which exhibit a high degree of sediment
spatial variability.
The USEPA requested that USAGE-WES optimize the Acoustic Corer. Two sites
on the Trenton Channel, Elizabeth Park and Black Lagoon, were selected for micro-
surveys to demonstrate the Acoustic Corer and to confirm the 1994 observations. The
request required survey grids of very closely spaced (5-10 meters) observation lines with
high ping repetition rates. In addition, ground truth piston cores were to be taken at
calibration sites and other sites of interest. The data were to be acquired and processed
with the Caulfield Engineering Acoustic Core suite of software. Final project outputs
were to include identification of the location and volume of depositional sediment, survey
line cross section plots of horizontal and vertical sediment distribution by density group,
and to specify the acoustic properties of the possible contaminated sediments.
2.2 Site Overview
The Detroit River has been identified by the International Joint Commission as an
Area of Concern due to a number of water quality problems, including contaminated
sediments and degraded benthic communities. In addition, the river is also listed under
the Michigan Environmental Response Act (P.A. 307, 1982 as amended) due to
contaminated sediments.
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Sediment studies conducted under the Upper Great Lakes Connecting Channels
Study (USEPA and EC, 1988) and other research activities, documented sediments
contaminated with metals, PCBs, and oil and grease (Farara and Burt, 1993) in multiple
locations in the Detroit River and Trenton Channel. Impaired uses relating to
contaminated sediments, as identified in the Detroit River Stage 1 Remedial Action Plan
(MDEQ, 1987), include restrictions on dredging activities, degraded benthic
communities, exceeding Michigan Water Quality Criteria for fish consumption
advisories, and increased incidence offish tumors.
The Trenton Channel is located in the lower Detroit River between Grosse He and
the Michigan mainland, Figure 2-1. It is approximately nine miles in length and carries
21 percent of the total river flow, with an average velocity of 1.08 to 1.9 ft/sec. The
Detroit River and Trenton Channel, a heavily industrialized area and a major navigation
route, has been identified as severely degraded in terms of water and sediment quality and
benthic communities (USEPA and EC, 1988). Numerous point sources in the area
include steel plants, waste water treatment plants and chemical and automotive
manufacturing industries. Concentration of arsenic, nickel, PCBs, and oil and grease in
Trenton Channel sediments have been found to exceed the recommended guidelines for
sediments (Long and Morgan, 1990; Persaud et al., 1993). Data from various sediment
Toxicity tests conducted showed sever impacts compared to other Detroit River locations
and reference stations for a number of biota tested (Giesy et al., 1988).
2.3 Project Objectives
The primary objective of the USEPA-USACE-Caulfield Engineering effort was
the acquisition of micro-survey data using the Acoustic Core0 system and the processing
and analysis of selected results and sites to determine what the sediment stratigraphy in
near shore areas of the Trenton Channel. Two specific sites were chosen to demonstrate
soft sediment mapping, allowing the calculation of volume estimates.
This project uses the Acoustic Core0 suite of software to identify and map the
gross distribution of these sediments as presented in this report. Piston core data is
required to calibrate the acoustic process. It is important to note that the exact
relationship engineering geo-acoustic properties of the marine sediments versus the
various types of pollutants is not known. It is only known that pollutants and or micro-
gas bubbles contained in sediment change the acoustic properties, and in some cases
radically, from standard marine sediments. Data shows (Volume II) that as the gross
contaminants (observed from the chemical analysis of the USEPA vibra-cores collected
in 1994) increase the deviation of the bottom loss for similar non-contaminated marine
sediments increases.
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The tasks listed in the interagency agreement between EPA and ACOE included:
> Optimize the Acoustic Corer for use mapping, in shallow water (2ft-30ft),
where sediments exhibit a high degree of heterogeneity .
> Demonstrate the accuracy of the Acoustic Corer to characterize sediment type
and map the distribution of sediment type at depth. The demonstration should
take place at three sites (shallow, medium and deeper water depths) in the Trenton
Channel, Detroit River.
> Collect and conduct the necessary geophysical characterization of sediment
cores needed for calibration and validation of the acoustic corer.
> At the demonstration sites provide mapping of the distribution of the soft
sediment.
> Provide a written report on the Acoustic Corer Optimization, describing the
rational, approach and results.
> Provide a survey report on the demonstration site surveys. This report is to
include:
1. A description of the Acoustic Corer and the fundamentals of operation
2. The survey design
3. Results of the survey
4. Graphical mapping of the sediment distribution for each site
5. A calculation of the volume of soft sediment at each site
Without the detailed quality assurance program carried out during the field
exercises this project would not have succeeded. The quality assurance program enabled
absolute calibrations of the sound sources, which in turn allowed for the quantitative
identification of the sediment types.
2.4 Experiment Design
The data acquisition procedures encompass standard shallow subbottom profiling
techniques in which a sound source emanates a sound signal (source) and the reflection
from the bottom and subbottom are received on an array or transducer (receiver). Various
sound sources and receivers are used with different amplifiers to format the data for
proper digitizing and data storage. The selection of source and receiver combinations are
a function of the soil types, the depths of penetration and vertical resolution required.
Based on the experience of the previous years survey, a number of different systems were
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made available. Volume I provides an extensive review of all the acquisition systems,
field procedures, sonar equation solutions, and calibration.
A new Caulfield Engineering program, Acoustic Core Reflection/Sign (ACRS1)
was utilized to automatically obtain water bottom depth and depths to each strong
subbottom layer, bottom reflection sign, and to compute bottom loss for the file being
analyzed. This program is in addition to the standard Acoustic Core routines discussed in
Volume I, the latter being also used in the preparation of this report.
2.5 Project Schedules
The project was scheduled to commence on July 24, 1995. The project was
started on time and Volume I provides a detailed description of all activities, equipment
and calibration procedures and results. The field acquisition was completed on schedule.
During the field operation, severe boat handling problems were encountered that severely
complicated the data processing. In many cases the boat was not anchored well, or not
anchored at all. This required trace by trace processing to obtain the proper
representation of the bottom. These problems and the solutions to them, are discussed in
detail in Volume I. Some of the same problems were encountered when relating the core
data to the seismic data in this report. The solutions outlined in Volume I were applied to
this core/seismic data with the same positive results.
2.6 Quality Assurance Procedures
The success of the entire program results from the implementation of a detailed
quality assurance procedure program. This QA program presented all system operating
specifications, tolerances, and calibration programs. These in field calibration programs
allowed verification of all results and, more importantly, allowed correction for boat
handling problems. Volume I provides complete descriptions of the QA procedure
program, along with the detailed individual system specifications and accuracy. The
same procedures established and documented in volume I were used to obtain the results
presented in this volume. Results are presented showing that, with the calibrated source
and receiver sensitivity values obtained, predicted non-polluted sediment bottom loss
values equaled, within 1.32 db, the theoretical bottom loss values for these sediments.
The Quality Assurance Procedure Section of Volume I also presented the main
mathematical equations used in data analysis. These are namely, the sonar equation,
reflection model, and transmission model. A complete discussion of the mathematical
procedures and equations used in the preparation of this volume can be found in Volume
I.
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3.0 TECHNICAL APPROACH AND ANALYSIS
PROCEDURES
The acquisition of seismic data and core data simultaneously was specifically
designed to accomplish the following:
Physical Verification of Spatial Variability - The 1994 seismic survey of the
Trenton Channel indicated high spatial variability in sediment type and
pollution variability. The physical cores, along with grab samplers, confirmed
this variability.
Confirmation of Seismic Predictions - The availability of multiple sediment
cores, characterized for material type and physical density, allowed for
verification of the acoustic core predictions. Bottom loss predictions were
within 1.32 db of theoretical bottom loss for non-polluted sediments.
Acoustic Properties of Polluted Sediments - The long term goal of the project
is to start to build a library of the relationship of the physical properties of
polluted sediments in relation to the observed acoustic properties of these
sediments. This program provided an initial step, and acoustic parameters can
be related to gross pollution measurements. Even more importantly, the
results provide a confirmed procedure for surveying and delineating these
highly variable depositional Trenton Channel sediments in an analytical
manner.
The 'R/V Mudpuddy' provided an excellent platform for performing this first
experiment in pollution classification with the Caulfield Engineering Acoustic Core
patented procedures. The transmitter and receivers were mounted in the front of the hull
on extended platforms, while a special Caulfield Engineering piston corer could be
dropped directly between the transducers. This ensured that when the boat was properly
anchored, the transducers were directly over the core location, allowing absolute
calibration of the bottom loss with physical samples. Unfortunately, the boat was not
always anchored properly or was not anchored at all. However, the statistical processing
to overcome these problems, developed in Volume I, was successfully used in this
core/seismic study.
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3.1 Field Procedures
Core location sites were at the same locations that previous detailed chemical
analysis cores were taken by the USEPA, and sites chosen from review of the seismic
records and a test grab sampler. The boat was then positioned over the desired spot and
sometimes anchored. While seismic acquisition with either the 3.5 KHz or 7.0 KHz
system running, the core was dropped. After retrieving the core, the core sample was
weighed, measured, and the general characteristics and sediment interfaces noted. If time
allowed, this core was then placed in the Caulfield Engineering Field Core
Velocity/Absorption System prototype unit. This unit measured the gross sound velocity
and absorption by placing a 330 KHz transmitter on one side of the core and a
corresponding receiver on the other side. Peaks travel time and amplitude were recorded
in the core logs. The latter being only rough estimates as this unit was a prototype and
was not part of the contract deliverables.
After the above measurements were properly recorded, the surface water was
removed, the cores cut, sealed, and the cores were again weighed and measured. The
empty weight of the core tube and its dimensions allowed in the field computation of the
average density. This information was useful for optimizing survey procedures. Rough
dielectric measurements were occasionally taken, however, the number of samples taken
was insufficient to make any conclusions. Some resistivity measurements were also
taken. The data suggest the bottom conductivity increased as the gross pollution
increased.
At the majority of core sites, data was acquired at both 3.5 KHz and 7.0 KHz with
additional calibration procedures performed. This allowed absolute checking of the
calibration procedures developed and discussed in Volume I.
At the completion of the survey effort, the packaged cut cores were shipped to
USACE-WES where precision absorption and density measurements were repeated.
Gross density measurements obtained agreed with the field measurements as presented in
Appendix B3. However, the precision velocity/absorption portion of the system could
not obtain data due to the extremely high sound absorption of the sediments. The
operating frequency of this precision system was approximately twice as high as the
Caulfield Engineering prototype unit. As frequency increases, so does the absorption in
marine sediments (Hamilton, E.L. 1972), explaining why the USACE-WES unit could
not get any data. These negative results confirm the high acoustic absorption in these
sediments.
3.2 Analysis Procedures
The 'standard' Acoustic Core0 system measures the bottom reflection coefficients
7
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(Bottom Loss (BL)), estimates the absorption (for standard marine sediments) and
computes the impedance of the various layers. From historical tables embedded in the
software, the density is estimated from the impedance. In the case of polluted sediments,
this historical data base does not exist and a different approach must be undertaken.
The approach taken was to generate a new Windows based Acoustic Core
Reflection/Sign (ACRS1) program that performed all the normal computations of the
standard Caulfield Engineering's Acoustic Core software, but did not perform the density
predictions. In addition, a reflection sign output algorithm had to be added to detect and
measure the observed phase reversals caused by micro gas bubbles in the sediments.
Because of the large amount of data to be processed due to the high spatial variability of
the sediments, and ship handling problems, a gray-scale display was developed for use
with Laser printers, which increases the processing speed compared to conventional color
plotters. This ACRS1 program was combined with the new Calibration Program
discussed in Volume I to process the data. Appendix Bl, contained in an Addendum,
provides complete examples of processing for each core site. The following outline
summarizes step by step the process for relating the seismic data to the core information
at each location:
Step 1) Position Plots - At each core site location the precise position is
plotted from the navigational data. Figure 3-1 illustrates such a plot. This
plot demonstrates the movement of the boat when coring is attempted while
unanchored. The data nearest the core point were identified using the
navigational plots and chosen for analysis.
Step 2) CAL1 Processing - For several sub-files the CAL1 calibration
program is run to generate bottom and subbottom signal levels and to compute
the bottom loss and refection coefficients. This particular plot, Figure 3-2, is
from the 3.5 KHz Massa receiver data set. Data from the 7.0 KHz and the
crystal receivers were collected at the same position and analyzed, providing
four (4) independent observations at each core site. In addition to providing
the bottom loss calculations, the plots were used for sediment layer
identification. In this particular case, the surface layer is clearly identified and
is approximately 0.7 meters thick. The piston core obtained approximately
0.4 meters of sediment. Data output from this processing is provided in an
ASCII file and is included with this report on separate disks. The source and
receiver levels were those determined during the calibration program reported
in Volume I.
Step3) ACRS1 Processing - The ACRS1 processing provides layer depths, the
layer sign (a measure of the phase of the reflected signal, positive for non gas
containing sediments and negative for gas containing sediments), and plots of
the bottom loss for the entire subbottom file. Volume III, Appendix A3.6
provides a detailed discussion of the ACRS1 programs and descriptions of the
8
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SCRLE 1 =6.11 M
CRULF1ELD ENG]NEER]NG
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-------
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Typical ACRS1 Processing Output
Figure 3-3
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graphic symbols in the display. The left hand side of Figure 3-3 is the raw
seismic data. In this particular case the echo from the coring devise rising
from the sediment to the water surface is clearly shown. The ability to see the
corer on the acoustic records enabled certain identification of the seismic
records associated with the cored site. The right hand side of the same Figure
presents the layers and the bottom loss plots. Solid black thick lines indicate a
negative reflection coefficient, and dashed thick lines indicate positive
reflection coefficients. The average bottom loss (ABL) for all the traces
processed is presented in the data table on the right. The standard deviation is
also presented. Even though this was an extremely stable region (apparent
uniform bottom based on the seismic display), the standard deviation is still
quite large. This is representative of the spatial variation observed in Trenton
Channel. As above, the source and receiver levels were those determined
during the calibration program reported in Volume I. The detailed trace by
trace results of the processing is provided in ASCII files and is supplied on the
attached disks. In this example two major layers are detected. The third
possible layer was weak and below the ambient Signal-to-Noise and is only
partially detected.
Step 4) Site Data Summary - The principal observation from each file and
sub-file is summarized in Figure 3-4. This figure records the receiver levels,
source levels, transducer depths, directivity index, and the system gain. These
are all the parameters for solving the sonar equation to determine the bottom
loss, which is given on the right side of Figure 3-4. The type of processing
undertaken by the CAL1 program is also listed. The bottom loss is computed
by using the basic sonar equation, knowing the receiver and source strength
and solving the sonar equation for the bottom loss. This bottom loss
computation can also be confirmed using the multiple refection values. The
latter solution has higher variance due to bottom scattering. These calculations
are described in volume 1 and also in volume III, appendix A3. The top of
Figure 3-4 shows the outputs for the CAL1 processing and the bottom of
figure 3-4 shows the results of the ACRS1 processing. These data sets are
averaged and presented latter in the section on results.
Step 5) Amplitude Decay Ratio - The amplitude ratio is a gross estimate of the
absorption. Figure 3-5 illustrates the form used to record the amplitude decay
ratio (Ampl. Ratio). The amplitude decay ratio is the second prominent layer
amplitude divided by the bottom (surface sediment) amplitude. It has been
assumed that the region can be approximated as a one layer model.
Step 6) Reflection Sign Data Form - The reflection sign, when negative
indicates phase reversal, a phenomenon indicative of gas containing sediment.
Figure 3-6 presents the form used to record and generate the plus (+) sign
percentage seen over the entire file. The data is generated graphically by
12
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Figure 3-6
15
Caulfield Engineering
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measuring the gross amount of plus and minus data. The data is also provided
in ASCII format on the core analysis disks provided with this report. It is
important to note that in the ASCII file generation program there was an error,
and the plus and minus signs are interchanged.
The above processing steps provided literally thousands of observations for
statistically comparing the acoustic data to the core information. The next section will
review and summarize these findings. A quick review of Appendix A in the Addendum
will confirm that the spatial variations exist. The processing of such a large amount of
data was necessary to ensure that the ship handling and electrical problems were
removed.
16
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4.0 DISCUSSION OF RESULTS
The following subsections summarize the processed results from the Addendum -
Appendix Bl. Each major finding is broken out as a separate subsection. Only core sites
5 through 19 were processed as these were in the major areas of interest.
4.1 Core Densities and Core Locations
The core densities measured by the USACE-WES by weight and volume are
given in Figure 4-1 along with the field core densities obtained immediately on the
vessel. Volume I contains the complete raw core field log from which the field core
densities were derived. Note that Core 15 density obtained by USACE-WES is out of
range. This core was damaged during shipping from Detroit to Vicksburg. The table
given in Figure 4-1 shows how the average densities are computed from the core length
and volume.
Literature-derived densities were used for the cores that did not have good
retention. In particular, the sand material ran out the bottom of the core when the core
rube was raised out of the water. Sufficient material was recovered to classify the
material type. These cores were namely sand, or sand with gravel, or sand with rocks.
Refer to Volume I for complete reference material to standard densities for non-polluted
sediments and to the next sub-section for a summary of density and acoustic properties of
these standard marine sediments.
Figures 4-2 and 4-3 provide the locations of cores 5 through 19. Note that the
Northing (N) was mislabeled as an Easting (E) at core site 19 in Figure 4-3. Cores 5
through 10 were taken in the Elizabeth Park region, Figure 4-2, and Cores 11 through 19,
Figure 4-3, were taken in the Black Lagoon region. The core locations are given in the
Northing and Easting as observed by the USEPA staff.
4.2 Standard Marine Acoustic Properties
For purposes of comparison. Figure 4-4 is presented to summarize standard
marine sediments versus acoustic properties, developed by Hamilton. Refer to Volume I
for complete references. The graph at the bottom of the figure shows the analytical
function used to relate density to bottom loss (BL). The slight deviations from the curve
are negligible in comparison to the deviations for anomalous sediments which were
polluted and contained gas.
17
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Sheet2
Trenton Channel Core Densities
Second Laboratory Measurements
Core Tube = 8.683 gm/cm
I.D Core = 6.69 cm.
Core Number
Location
Material
Weight(lb)
gms.
Length-cm
Volume
cmA3
Weight -
Core Tube
Density
gm/cm^S
Field Density
gm/cm* 3
Pollution
Factor
Core 1
Core 2
Core3
Core 4
CoreS
Core 6
Core?
CoreS
Core 9
Core 10
Core 1 1
Core 12
Core 1 3
Core 14
Core 15
Core 16
Core 17
Core 18
Core 19
Celeron
Celeron
Crys. Bay
Crys. Bay
Q E. Inner
Q.E. Inner
Q.E. Inner
Q.E. Outer
Q.E. Outer
Q.E. Outer
Blk. Lagoon
Blk. Lagoon
Blk. Lagoon
rBlk. Lagoon
Blk. Lagoon
Blk. Lagoon
Blk. Lagoon
Blk. Lagoon
Blk. Lagoon
Clay/Silly
Silt/Clay
Gravel/Sand
Rock/Gr.
Silty-Sand
Gravel
Clay/Tr.Gr.
Rock/Gr.
Sand-SmGr
Silty-Clay
Clay
Sandy Silt
Sandy Silt
Clay-Silt
4.65
3
3
10.4
10.6
9
hard
hard
4.1
hard
6.4
hard
0.75
12
2
9.625
10.2
5.4
2109.800
1361.162
1361.162
4718.693
4809.437
4083.485
1860.254
2903.811
340.290
5444.646
907.441
4367.060
4627.949
2450.091
29.84
23.49
22.22
92.5
100.33
76.53
27.002
66.04
7.62
58.4
16.5
72.39
73.66
41.91
1048.719
0
825.5496
780.9158
3250.887
3526.071
2689.626
948.9779
2320.958
267.8028
2052.452
579.888
2544.127
2588.761
1472.916
1850.7
1157.198
1168.225
3915.516
3938.272
3418.975
1625.796
2330.386
274.1259
4937.559
764.1715
3738.498
3988.359
2086.186
1.7647
1.4017
1.4960
1.2044
1.1169
1.2712
2.1000
2.2000
1.7132
2.0000
1.0041
2,2000
1.0236
2.4057
1.3178
1.4695
1.5406
1.4164
1.249
1.18
1.39
2.10
2.20
1.533
2
1.23
2.20
2.10
1.45
1.22
1.33
1.53
1.18
10
10
10
0
0
5
0
7
0
0
3
7
9
9
10
oo
Note: Pollution Factor is arbitary scale based on in field/laboratory absorption measurements, site observations, and 1994 core analysis
Note: Core 15 weight seem to be in error. Penetration of core eliminates calculated density
Den s i ty Summa ry
caulfleld engineering
Figure 4-1
-------
Core 9
o
Core 10
O
Core 10 - N 7H89.0
E -(098540.0
Core 9 - N 71477.0 E 4098481.0
Cores 5/6
O
Core 7
O
Core 7 - N 71433.8 E 409839a8
Core 5 - N 71407.2 E 4098345,6
Core 6 - N 71408.0 E 4098346.1
Core 8
o
Core 8 - N 71376.0 E 4098447.0
CAULFIELD ENGINEERING
QUEEN ELIZ.PK.- CORE LDC.
JDB'2060
DRN BY
DDC
DATE.
02/l5/%
SCALE
SHEET
REV.
DVG, ND, gQSO-CLDCl
Core Locations
Figure 4-2
-------
Core 19
O
E 72988.4 E 4098786.4
Core 11
O N 73008.0 E 4098765.0
Core 12
^ N 72993.7 e 4098757.9
Core 13
^ N 72917.2 E 4098747,8
OCore 14
N 72963.5 E 4098749.5
Core 15
0N
72928.5 E 4098735.6
O Core 16
N 72918.5 E 4098738.2
N 72943.2 E 4098816,7
Core 17
O
Core 18
N 72942.2 E 4098815.5
CAULFIELD ENGINEERING^
BLK. LAGnnN-mpF i nri
JDBigQ6D
DRN BY
DDC
DATE'
02/15/96
SHEET
SCALE
(REV.
DVG. NG. gQ60-CLDCg
Core Location
Figure 4-3
-------
Sheetl
Bottom Loss - Standard Marine Sediments
Material
Density Bottom Impedance
Loss
Sand-Coarse
Sand-Medium
Sand-Fine
Sand-Very Fine
Silty-Sand
Silt
Sand-Silt-Clay
Sandy-Silt
Clayey-Silt
Silty- Clay
Clay
Fluff
2.03
2.01
1.98
1.91
1.83
1.6
1.58
1.56
1.43
1.42
1.26
1.1
7.8
8.3
8.6
9.1
9.9
12
12.1
13.5
15.2
16.1
20.6
23
3734.7
3508.7
3443.3
3254.5
3063.3
2611.1
2493.9
2420.1
2198.9
2157.1
1891.1
1600
Bottom Loss vs. Density
Standard Marine Sediments
y = 0.0022X4 - 0.0454x3 + 0.4045X2 - 0.7418x + 8.2664
Density (gm/cmA3)
Figure 4-4
21
-------
4.3 Processed Seismic Data Summary
The processed seismic data at each core site, partially given in Addendum -
Appendix Bl, has been summarized in tabular format data sheets for each core site.
Figure 4-5 provides an example of such a data sheet. The top of the figure gives the
prominent physical properties such as density and core length. The standard marine
bottom loss for the specified density is given along with a 'Pollution Factor' term. This
term has arbitrary values from 0 to 10, where 10 represents severely polluted. This
pollution factor term is only a rough estimate, for Trenton Channel sediments, based on
the chemical analysis performed on the cores taken at 1994 core sites. Future research
should examine the acoustic effects of pollutants under laboratory conditions when
specific pollutants are added to clay sediments in known amounts. This 'Pollution
Factor' was assigned by reviewing the USEPA cores taken prior to the 1994 survey and
assigning a factor of 10 to the core sets which chemical analysis showed to chemically
contaminated. Lower numbers were assigned to cores which had lower levels of
contaminates relative to the selected highest contaminated ones. Cores that had no
contaminates were assigned a factor of zero. This factor has been derived based on this
site only and care should be employed in using this factor in other sites without having
detailed chemically analyzed cores to establish base line references.
Each frequency and receiver type is given on the left side of Figure 4-5 with the
observed bottom loss and standard deviation for each observation. The amplitude decay
ratio is only determined from the CAL1 calibration output data, and the plus sign
percentage is only available from the ACRS1 program. The ACRS1 program generates
symbols representing if the reflection sign is plus or minus. For reporting purposes, only
the positive sign percentage (the number of plus signs divided by the total number of
traces in a file) is used. Refer to Volume III, Appendix 3 for detailed description of the
operation and symbols used in the ACRS1 program.
The bottom of the chart in Figure 4-5, presents the overall means and standard
deviation for each type of observation. In some cases the Massa receiver data means and
standard deviations were broken out as separate items. The beam pattern for the Massa
receivers is more focused on the bottom than the omni-directional crystal phones. The
Massa receiver data were used for comparison of the amplitude decay and the signs.
Appendix B2 provides the complete set of acoustic property tables for each core
site.
Figure 4-6 provides an overall composite summary of the acoustic parameters
versus core number and density. The table in Figure 4-6 is derived from the tables in
Appendix B. It is important to note that cores 5 through 10 were taken without the boat
being anchored. Great care was taken during data processing to select only data near the
core site. The table in Figure 4-6 also presents the difference of observed bottom loss
22
-------
Sheets (14)
ACOUSTIC PROPERTIES AT CORE SITES
Core Site 19
Density =
Core Leng
1.20
69.2
cm.
Std. Marine B. L.
Pollution Factor =
21
10
System/
Process
CAL1
3.5 -ms
3.5-crys.
7.0 -ms
7.0-crys.
ACRS1
3.5 - ms
3.5 - crys.
7.0-ms
7.0 -crys
Bot.Loss
(db)
5.45
4.32
3.26
4.43
7.016
7.812
3.125
5.4687
Std. Dev.
2.64
5.956
1.184
2.074
0.796
Ampl.
Decay
(ratio)
0.221
0.26
0.142
0.205
Absorp.
per meter
(db)
Sign
+/- %
11.76
60.78
8.33
47.05
Comments
ro
CO
Means
Set Sldev.
5.110213
1.674478
2.53
2.047925
0.207
0.049105
31.98
25.97894
Massa Means
Massa Setdev.
0.1815
0.055861
10.045
2.425376
Typical Core Site Sheet
Figure 4-5
Caulfield Engineering
-------
Sheets
SUMMARY OF BOTTOM LOSS FINDINGS
VERSUS AMPL. RATIO & SIGN PERCENTAGE
ro
Core Site
Core5
Core 6
Core?
Core8
Core 9
Core 10
Core 11
Core 12
Core 13
Core 14
Core 15
Core 16
Core 17
Core 18
Core 19
Density
gm/cmA3
1.29
1.18
1.39
2.00
2.20
1.53
2.00
1.23
2.20
2.00
1.45
1.22
1.40
1.53
1.20
Mean
Observ.
B.L.(db)
11.377
11.377
6.646
8.882
9.63
12.045
8.323
7.121
10.4
9.138
12.8
12.607
6.578
6.578
5.11
Bottom Loss
Difference
St.Mar-Obs
8.62
10.62
10.85
-0.68
-2.13
1.96
-0.12
13.88
-2.90
-0.94
2.20
8.39
11.42
7.42
15.89
Massa
Ampl.
Ratio
0.141
0.141
0.171
0.874
0.507
0.763
0.542
0.409
0.494
0.594
0.789
0.716
0.149
0.149
0.185
Massa
+ Sign
Percent
27.43
27.43
13.23
50.62
46.21
22.80
82.95
67.08
87.61
82.93
32.47
66.14
31.37
31.37
10.045
Overall
Ampl.
Ratio
0.141
0.141
0.171
0.874
0.507
0.763
0.551
0.390
0.898
0.631
0.789
0.670
0.265
0.265
0.207
Overall
+ Sign
Percent
27.43
27.43
13.23
50.62
46.21
22.80
67.21
67.48
70.00
71.26
41.25
60.79
44.58
44.58
31.98
Pollution
Factor
10
10
10
0
0
5
0
7
0
0
3
7
9
9
10
Note: Cores 5-10 have only one sensor as input. Boat would not anchor.
Overall Acoustic Parameter Summary Chart
Figure 4-6
Caulfield Engineering
-------
from 'standard marine sediments' bottom loss. The data for the 'standard marine
sediments' is provided in Section 4.2. The data in Figure 4-6 is used as the basis for
establishing relationships between the various parameters and is discussed in the
following subsections.
4.3.1 Calibration Procedure Verification
All the computed acoustic parameters were based on the source and receiver
levels derived during the calibration program reported on in Volume I. See Figure 7-17
in Volume I. All levels checked out except for the crystal receiver. The receive level
should have been 108.35 rather than the 103.35 reported. The proper levels were used for
the data processed in this Volume II and Volume III.
Figure 4-7 compares the theoretical bottom loss for the non-polluted core
locations with the observed bottom loss. The mean deviation is only -1.354 db with a
standard deviation of 1.132 db. Considering all the problems that occurred, this result is
remarkable. It confirms the validity of the quality assurance procedures and the Acoustic
Core processing procedures. Further, it clearly establishes that the variation due to
pollution/gas that is observed are in fact very real.
4.3.2 Bottom Loss Analysis
The table given in Figure 4-8 shows the computation of the difference in the
observed bottom loss compared to 'standard marine sediment' bottom loss. The
difference in bottom loss between 'standard' and the observed are much greater than the
standard deviation of the data.
Figure 4-9 is a comparison of bottom loss to the core physical density. Series 1
represent the theoretical 'standard marine sediments' The point distributions about the
curve presented is what is normally seen in non polluted sediments. From region to
region in the country the curve sometimes has to be adjusted for specific gravity of the
material itself. However, this is normally well within 5 percent. Series 2 shows the data
for the Trenton Channel. It can be seen that the higher density material is very close to
standard marine case. As the density decreases, the deviation from normal increases and
is scattered. This deviation correlates with the gas and pollution content of the material.
This plot supports the hypothesis that contaminants are generally associated with the
"soft fine grained sediments which have lower densities.
Figure 4-10 is a comparison of the bottom loss difference between observed and
standard marine sediments to the qualitative pollution factor. It is important to note that
determining the exact causes of these deviations from normal as a function of the gas and
particular pollutants is beyond the scope of this work. However, the existence of this
25
-------
Sheet4
COMPARISON NON-POLLUTED SITES TO STD. MARINE SEDIMENT
BOTTOM LOSS
Core Number
CoreS
Core 9
Core 1 1
Core 13
Core 14
Density
2.00
2.20
2.00
2.20
2.00
Std. B.L.
8.2
7.5
8.2
7.5
8.2
Obs. B.L
8.8825
9.63
8.323
10.4
9.138
Difference
-0.6825
-2.13
-0.123
-2.9
-0.938
Mean Difference -1.3547
Standard Deviation Difference 1.132654
Note: Indicates the goodness of Calibration and Computation
Procedures.
Figure 4-7
26
Caulfield Engineering
-------
Sheets
SUMMARY OF BOTTOM LOSS FINDINGS
TRENTON CHANNEL 1995
Core Site No.
CoreS
Core6
Core?
CoreS
Core9
Core 10
Core 1 1
Core 12
Core 13
Core 14
Core 15
Core 16
Core 17
Core 18
Core 19
Density
gmycmA3
1.29
1.18
1.39
2.00
2.20
1.53
2.00
1.23
2.20
2.00
1.45
1.22
1.40
1.53
1.20
Std. Mar.
B.L.(db)
20.00
22.00
17.50
8.20
7.50
14.00
8.20
21.00
7.50
8.20
15.00
21.00
18.00
14.00
21.00
Mean
Observ.
B.L.(db)
11.377
11.377
6.646
8.882
9.63
12.045
8.323
7.121
10.4
9.138
12.8
12.607
6.578
6.578
5.11
Mean
Observ.
Std.
2.0325
2.0325
1.444
2.444
2.13
2.38
1.399
2.108
1.299
3.424
2.68
3.331
2.197
2.19
2.53
Difference
St.Mar-Obs.
8.62
10.62
10.85
-0.68
-2.13
1.96
-0.12
13.88
-2.90
-0.94
2.20
8.39
11.42
7.42
15.89
Pollution
Factor
10
10
10
0
0
5
0
7
0
0
3
7
9
9
10
Diff. Bottom Loss Derivation Table
Figure 4-8
27
Caulfield Engineering
-------
Sheets
Density Vs. Bottom Loss (Std. & Obs)
?fi nn
3"
~o ie nn
in
in
5
o
em nn .
03
; nn
0 00
4ป
'-*-
i V
\
! \
A.
ป
\v
"\
1
Lj
0.00 0.50 1.00 1.50 2.00 2.
Density (gnWcmA3)
Seriesl
,.n BSeries2
Series 1 = Standard Marine Sediments
Series 2 = Trenton Channel Sediments
Figure 4-9
28
Caulfield Engineering
-------
Sheets
i
i
!
i
o
o
n
n
c
5
i =
o
i Q.
I
1
i
i
-5
Estimated Pollution Factor Vs. Delta Bottom Loss
1 "^
10
P
5
4
00 0.00 5.00 10.00 15.00 20
I
I
I
I
I
I
Series 1
.00
\ Std. Marine - Observed Bottom Loss (db)
Figure 4-10
29
Caulfield Engineering
-------
deviation allowed classification of potentially polluted sediments. This finding has only
been examined for the Trenton Channel study and must not be assumed valid for other
sites.
4.3.3 Amplitude Decay Ratio
The Amplitude Decay Ratio is a gross measure of absorption. When plotted
against difference in bottom loss, Figure 4-11, a linear approximation is indicated. The
straight line on the plot is a linear fit of the data points. It is important to recognize that
this result is only considered as a general trend. The large variance in boat position,
hence sediment type, explains some of the variance. In addition, examination of the ping
to ping variance could also be attributed to different amounts of gas. The higher
absorption (lower amplitude ratios) correspond to more polluted clay layers.
Figure 4-12 is a three dimensional plot of the amplitude ratio (vertical axis) versus
pollution factor by core number. The left portion is for normal non-polluted sediments
and the right, low values, are for the heavily polluted sediments. The middle bars are
slightly higher than expected. It is believed that this is due to the fact that the data were
not corrected for layer thickness. Time did not allow for this correction. The black
squares in the legend plot are an anomaly of the plotting routine and have no significance.
Spectral analysis tools, such as the Caulfield Engineering 'Digital Spectral Analysis
System (DSA10),' are available to refine these gross trends identified. However, the
amount of data processing is quite large and was beyond the scope of this contract.
4.3.4 Plus Sign Percentage
The plus sign percentage is lowest when the gas content is highest and there is a
phase reversal of the bottom reflection. Phase reversal occurs when the boundary is a
pressure release surface, where the reflecting layer is less dense than the incident layer.
The best example is the water-air surface where there is always a 180 degree phase shift.
Figure 4-13 compares the plus percentage to the difference in bottom loss (defined
above). This curve, like the amplitude ratio, shows that the largest deviation in bottom
loss, highest gas content, has the lowest plus sign percentage or the largest negative
reflection coefficients. The line plotted through the data is a linear fit of the data points.
Figure 4-14 is a three dimensional bar graph of the plus percentage (vertical axis)
versus the pollution factor by core numbers. The data on the left is the non-polluted
sediments and the data on the right is the highest polluted clay samples. Again, time did
not allow for correction for slight deviations in layer thickness, which would have
corrected the middle points. The black and white squares in the legend block are an
anomaly of the plotting routine and have no significance. The Plus Sign Axis is the
vertical axis in this Figure 4-14.
30
-------
1r
0.9
0.8
0.7
0.6
cc
S.5I
D.
^0.4
0.3
0.2
0.1
0
x
X
X
Ampl. Ratio vs. Delta Bottom Loss
x
x
-5
5 10
Delta Bottom Loss
15
20
Figure 4-11
31
-------
Sheetl
Amplitude Ratio vs Pollution Factor by Core Number
Core Number
D Series 1
Series2
DSeries3
DSeries4
SeriesS
DSeriesS
Series?
D SeriesS
SeriesS
SeneslO
DSeriesH
Pollution Factor
Series 1-11 represents Pollution Factor 0-10
Figure 4-12
32
Caulfield Engineering
-------
Plus Sign Percentage vs. Delta Bottom Loss
5 10
Delta Bottom Loss (db)
15
20
Figure 4-13
33
-------
Sheetl
Plus Sign Percentage vs Pollution Factor by Core
Number
Core Number
V90
Pollution Factor
|D Series 1
Series2
DSenesS
DSeries4
SeriesS
DSenes6
Series?
nSeriesS
Series9
Series 10
DSeries 11
Figure 4-14
Series 1-11 represents Pollution Factor 0-10
34
Caulfield Engineering
-------
4.3.5 Acoustic Parameters Summary
The data presented above should be considered only as general trends due to the
electrical and boat handling problems encountered during the survey. However, the
trends do suggest the potential for identifying polluted and/or gas containing sediments in
the Trenton Channel. In application, when the bottom loss is low, more sound is being
reflected back to the receiver, one normally would assume a very hard or rocky bottom.
In a normal marine case of a hard or rocky bottom the reflection sign would be positive
(plus percentage high). However, when the plus percentage is low, indicating negative
reflection coefficients (indicating gas), one can readily assume the that low bottom loss is
due to gas/polluted sediments. Cross referencing with the absorption can then provide a
rough classification of the sediment type and the potential for pollution/gas. The ability
to have some geotechnical data on the cores while in the field confirms the process.
The data processed to date has concentrated on the 3.5 KHz and 7.0 KHz data.
The boomer low frequency data, which was used to aid in layer identification, can also be
used for classification. Time did not allow for processing the boomer data in the same
detail as above.
ACOUSTIC PARAMETERS SUMMARY AS A FUNCTION
OF BOTTOM STATE
Sediment Type Density Bottom Loss Reflection Sign Absorption
(g/cmA3) (db) (db/m)
Clean Clay 1.3 -20 (High) + (High+%) Low
Polluted Clay 1.3 -8 (Low) - (Low+%) Very High
Clean 2.1 -8 (Low) + (High+%) Medium
Sand/Rock
It is also important to note that most pollutants lodge in clays and silty-sands and
do not lodge in sands.
35
-------
5.0 DETAILED CROSS-SECTIONS AT CORE
SITES
At each core site detailed cross-sections were generated providing material
identification by layer and depth. All core site cross-sections are provided in Appendix
B3. Note that Cores 5 and 6 were at the same seismic site. Likewise, Cores 17/18 were
at the same seismic site.
Figure 5-1 provides an example of the core site cross-section. For this site, two
cores were taken. The material legend is given in the upper-right hand comer of the
drawing. Potentially polluted materials have the hatching rotated 90 degrees with respect
to non-polluted sediments. The depth, in meters, below the water surface is provided.
The major layering is indicated with the hatching defining layer type. The actual core
stratigraphy is plotted on the left-hand side.
In this particular example, the predominant material is sandy/silt with fluff on the
bottom surface. The location, physical properties, and major acoustic parameters are
provided in the tables located at the top left of the drawing. A relative pollution factor
comment is provided to the right of the bottom cross-section. The amount of drift of the
boat is provided in meters. Even with a drift of only 0.405 meters, the bottom structure is
beginning to vary, confirming the spatial resolution required to fully understand these
complex structures.
36
-------
OBSERVATION
CDRE 17
CORE 18
NORTHING
EASTING
CDRE LENGTH
DENSITY
BDT. LOSS
AMPL. DECAY
PERCENT.
1.000 METERS
CDRE 17/18
Ul
(J
b
a
SEDIMENT
LEGEND
FOAM/FLUFF
POLLUTED
SEDIMENT
CLAY
SILTY CLAY TD
CLAYEY SILT
SILT
SILTY SAND TD
SANDY SILT
SAND
HARD/COMPACT
3.65 _,
4.38 _
5.11
5.B3
6.56 -
7.29 J
PDLLUTinN FACTHR HIGH
:,^7"v'iV,^S;-Sf.^^'^.r-V^V^'.-l-vS;i-
'rs..ป'^.:-^- ---i
-0.405 M
CAULFIELD ENGINEERING
CDRE 17/18 SUMMARY SHEET
JDBi ฃ060
DRN BY
DDC
DATE-
SHEET
SCALE
REV.
DVG. ND. gQ6Q-CR17/18
Typical Core Site Cross-Section
Figure 5-1
-------
6.0 DIRECT CORE VELOCITY/ABSORPTION
Caulfield Engineering provided, at no cost and not as part of the contract, a new
prototype Direct Core Velocity/Absorption System for use in confirming and aiding in
calibration of the polluted/gas containing sediments. This system allowed the direct
measurement of both velocity and absorption in the core as soon as it was brought on
board the boat. This allows verification of gas content, which normally would have
escaped by the time normal laboratory geotechnical analysis was carried out. Because of
the prototype nature of this system, data had to logged manually. Therefore, the data
should be reviewed for trends and not absolute values.
The system consisted of a steel frame that allowed the core to be firmly mounted
in the center. A transmitter and receiver crystal was mounted on sliding rods on each side
of the core. The position of the water-sediment interface with respect to the bottom of the
core was logged and the positions of the measuring transducer with respect to the bottom
were also logged. Data acquired at each position included the travel time (velocity), the
amplitude setting and the gain setting (absorption). At each core layer multiple readings
were taken so that statistical processing could be undertaken. The operating frequency of
the system was 330 KHz. A similar production system was used by USAGE-WES to
confirm the results. Unfortunately, this production system operated at 600 KHz and the
absorption at this frequency was so large that no data were acquired. This was actually a
positive result as it confirmed the high absorption parameters that were observed by the
Caulfield system and by the seismic data in polluted areas. These measurements were
only taken on seven (7) cores due to time limits and insufficient sample volume for some
of the cores.
The original field log for this data was reported in Volume I. The analysis sheets
for the velocity and absorption observations for all processed cores are provided in
Appendices B3 and B4, respectively. The following sub-sections will review the
observations obtained in detail for cores 5, 6, 7, 10, 12, 18, and 19.
6.1 Core Velocity Measurement Review
Figure 6-1 shows the form developed to estimate the velocity across the core at
the various location along the core. Note that all position point measurements were
referenced to the bottom of the core in the field. For reporting purposes the position
(depth) down the core from the water sediment interface is also presented in Column 2 of
Figure 6-1. The actual field positions of the transmitter and receiver, referenced to the
38
-------
Sheet"!
ESTIMATED IN FIELD CORE VELOCITY ANALYSIS
CORE NO:
Core Dens ity:
Core Material:
Est.
Material Depth
Below Bot
cm.
Page 1 POLLUTION FACTOR:
Sample Diameter:
1.29
Clay/Silt
Frequency - 330 KHz
10
0.073
From Core Bot.
Xmit
Position
cm.
Receiver
Position
cm.
Distance IstArr. 2nd Arr. 3rd Arr.
Xmt-Rec. Delta T Delta T Delta!
cm. micro-sec, micro-sec micro-sec
System
Offset
micro-sec
IstArr.
Velocity
m/sec
2nd Arr.
Velocity
m/sec
3rd Arr.
Velocity
m/sec
Water
Sediment
-10
5
103.5
103.5
103.5
103.5
103.5
103.5
103.5
103.5
89
89
89
89
87.5
103.5
101.5
102
102.5
104
105
106
107
89
90
91
89
90
7.3
7.569016
7.452516
7.368175
7.317103
7.452516
7.716217
8.095678
7.3
7.368175
7.569016
7.3
7.716217
100
110
60
80
mov->
90
mov->
mov->
36
60
36
36
36
100
140
160
145
144
96
100
100
108
96
10
10
10
10
10
10
10
10
Mean velocity
160
176
179
160
10
10
10
10
10
Mean Velocity
811.1111
756.9016
1490.503
1052.596
931.5645
2807.692
1473.635
2911.16
2807.692
2967.776
2484.172
1688.562
1490.503
1714.715
1812.465
1423.309
2546.512
2456.058
2523.005
2234.694
2691.703
2481.806
2433.333
221933
2239.354
2433.333
Fi gure 6-1
corvel - core 05-1
-------
bottom of the core, are also given. Knowing the diameter of the core, and after correction
for wall thickness, the actual transmission path was computed (Distance Xmt-Rec.,
Column 5, Figure 6-1).
Because of the high frequency and short time intervals involved, the standard
Acoustic Core digitizer could not be used for this prototype. The data was displayed on
an oscilloscope and the travel time to the various peaks was read along with the
amplitude of the peak signal and the gain setting. These latter items are discussed in the
following absorption sub-section. The multiple peaks existed because of multiple echoes
inside of the tube. These multiples are called the 1st arrival (direct), the 2nd arrival and so
forth. The various reading, in microseconds, were placed in the appropriate columns on
the chart shown in Figure 6-1. It is important to note that because of the weak signal
levels and the prototype nature of the system, these placement may not always be correct.
However, by taking many observation, the approximate estimate can be determined
through averaging all of the possible velocities computed from the data. These computed
velocity estimates are shown in the leftmost three columns. For example, in the example
in Figure 6-1, the mean velocity of water came out to be 1423.3 meter/second. Slightly
low from the normal velocity of water, which is 1459.2 meter/second. The lower value is
expected due to migrating gas from the core into the water column. The tests at the
multiple compensated for any arrivals coming from the plastic tube. The velocity of the
plastic is much higher than water and would raise observed velocities if the plastic had
any effect on the readings.
To ensure an independent calibration of the velocity system, the core tube was
removed and the velocity of the air gap was measured. Figure 6-2 presents the table for
the air calibration. The air velocity was 317.39 meters/second. The ideal velocity for air
is 330 meters/second at ideal temperature and humidity. This measurement showed that
the system was working properly.
Figure 6-3 provides a summary table for the velocity reading taken from seven (7)
cores. The second column is the water velocity observed. As was noted, this velocity is
slightly low. Part of this can be explained by the gas escaping into the water from the
core and part is the prototype nature of the device. The third column provides the mean
velocities observed and the fourth column the ideal velocity of standard marine sediments
for the density measured. The next columns present the difference from ideal and the
absolute difference from ideal. Also shown is the observed bottom loss and the
difference in bottom loss from ideal. The ideal bottom loss data was obtained by using
the core data density and using Hamilton's 1970 data for average bottom loss for standard
marine sediments. The plus percentage and amplitude decay ratio are also presented.
These latter numbers are taken from the tables presented in Section 4.0.
Figure 6-3B shows the ideal sediment plot of velocity versus density, while
Figure 6-4 shows the observed velocity versus density measured with the core
velocimeter system. The general trend of both plots shows that velocity increases as
40
-------
Sheets
ESTIMATED IN FIELD CORE VELOCITY ANALYSIS
AIR CALIBRATION
Frequency - 330 KHz
Est.
Material Depth Xmit Receiver Distance
Below Bot Position Position Xmt-Rec.
cm. cm. cm. cm.
IstArr. 2ndArr. 3rd Arr. System IstArr.
Delta T Delta! Delta T Offset Velocity
micro-sec, micro-sec micro-sec micro-sec m/sec
2nd Arr. 3rd Arr.
Velocity Velocity
m/sec m/sec
Air
0
50
50
7.3
240
10
Published Air Velocity = 330 m/sec.
317.3913
Core Velocimeter Calibration - Air
Figure 6-2
corvel - Air Calibration
-------
Sheetl
CORE VELOCITY ANALYSIS SUMMARY SHEET
ro
Seismic
Mean Ideal Diff. Std. Abs. Diff Observed Diff. Std. Plus
Core No Water Density Sediment Sediment Velocity Velocity Bot. Loss Bot. Loss Percent Ampl.
Vel.m/sec g/cmA3 Vel.m/sec Vel.m/sec m/sec m/sec db db Sign Ratio
5
6
7
10
12
18
19
1423.3
893.7
1351.9
1303.6
1342.1
1280.2
1.29
1.18
1.39
1.53
1.23
1.53
1.20
1531.3
1623.4
1842.9
2130.9
1940.6
1487.9
1252.2
1510
1500
1540
1677
1505
1600
1505
21.3
123.4
302.9
453.9
435.6
-112.1
-252.8
21.3
123.4
302.9
453.9
435.6
112.1
252.8
11.37
11.41
6.64
9.64
7.12
6.57
5.11
8.62
10.62
10.85
1.96
13.88
7.42
15.89
27.43
27.51
13.23
22.8
67.08
31.37
10.04
0.141
0.144
0.171
0.763
0.409
0.149
0.185
Means 1265.8
Stdev. 188.7516
Theorectical 1450.0
Figure 6-3
corvelsum
-------
Chart4
Standard Velocity Vs. Density
f.f. * -' *
: .? " "
' *
;-:_ .= =y-_j;
^'^fj;;=i vri
v^i4;
J>'v -":._Ir
1 1.2 1.3 1-4 1.5 1.6 1.7 1.8 1.9 2
Density
Figure 6-3g
corvelsum - std. vel vs. density
-------
Charts
Core Velocity vs Density
2200
2100
2000
1900
o
OJ
w
* 8
2
o
o
1500
1400
1300
1.1 1.2 1.3 1.4
1.5
Density (g/cm*3)
1.6 1.7 1.8 1.9
corvelsum - core vel.vs density
Figure 6-4
-------
density increases. The high variance of cores exhibiting anomalous standard marine
sediments is in part due to the prototype system and in part due to variations in other
geophysical properties or chemical contamination. The curves presented in this section
must be reviewed for gross trends only. This variance in observed velocity explains in
part the high spatial variance seen in the Trenton Channel sediments and is possibly due
to different concentrations of gas and or pollutants.
Figure 6-5 shows the difference between observed and standard marine sediment
velocities plotted against the difference between observed and standard marine sediment
bottom loss. The general trend is for delta velocity to increase as delta bottom loss
increases. This plot further confirms the hypothesis that increased pollution/gas may
cause increased deviation of the Trenton Channel sediment acoustic properties from those
of standard marine sediments.
6.2 Core Absorption Observations
The relative amplitude and gain levels of the traverse signal through the core were
recorded while taking the velocity data. Figure 6-6 shows the compilation of this data on
an analysis sheet. The gain settings were logged along with the signal levels in volts.
The corrected levels referenced to 1 volt were computed and this data was normalized to
0 db absorption for water. The last column converted these values into decibels (db) per
meter. It is important to note that these db/meter values are extremely high. The absolute
values should not be considered final because of the prototype nature of the system. Only
the general trends should be reviewed. Appendix B4 provides the analysis sheets for the
seven (7) cores examined.
Figure 6-7 provides a summary of the absorption values observed along with the
acoustic properties for each core site processed. Figure 6-8 presents the observed relative
absorption versus the observed difference in bottom loss from 'standard marine
sediments.' The linear fit curve demonstrates the direct relationship between absorption
and deviation in bottom loss. An increase in absorption is associated with an increase in
delta bottom loss, which corresponds to increased pollution and or gas in the sediment.
Again, the deviation from the line are due in part to the prototype nature of the measuring
device and possibly the variations in gas and pollution.
Figure 6-9 displays the relationship between absorption and plus sign percentage.
The plot of these data demonstrates that almost all the cores contained gas. Low plus
sign percentages correspond to negative reflection coefficients, which indicates the
presence of gas in the sediment.
Figure 6-10 shows the plot of absorption versus amplitude decay ratio. This data
set confirms that those areas of high absorption observed in the seismic data also have
high absorption as observed with the independent core absorption monitoring system.
45
-------
Chartl
ABS(Velocity Diff.) Vs. Delta B.L. from Standard B.L.
20
18
en
cd 12
o
re
S 10
(0
- 8
J
00
!t
Q 6
50
100
150
200 250 300
ABS(Velocity Diff.) (m/sec)
350
400
450
500
corvelwum - vel.diff vs. BL diff
Figure 6-5
-------
Sheetl
CORE RELATIVE ABSORPTION ANALYSIS
CORE NO:
POLLUTION FACTOR
Sample Diamter:
10
0.073 meters
Core Density: 1.29
Core Material: Clay/Silt Frequency - 330 KHz
Normalized
Material Depth Gain Gain Signal Signal Level Cor. Relative To Absorp.
Below Bot. Setting Level Level db 1 volt db Water db/meter
cm. hrs. db volts db
Water
Sediment
Sediment
Sediment
Sediment
-10
5
30
33
60
630
1500
1500
1700
1500
66
83.4
83.4
84
83.4
5
3.75
3.25
4.6
1
13.9
11.5
10.2
13.3
0
52.1
71.9
73.2
70.7
83.4
0
19.8
21.1
18.6
31.3
0
271.2329
289.0411
254.7945
428.7671
Mean Loss 22.7
Mean Absorption/Meter 310.9589
Analysis Log for Absorption Analysis
Figure 6-6
corabsOS
-------
Sheetl
CORE ABSORPTION SUMMARY SHEET
Cores missing were sand or two short for analysis.
Mean Mean
Core No. Absorp Absorb Density Bot. Loss Diff. B.L + Sign Ampl. Pollution
Core Tube db/m g/cmA3 db db Percent. Ratio Factor
5
6
7
10
12
18
19
22.7
18.7
22.5
21.4
32.4
29.5
27.7
310.9
256.1
308.4
292.8
443.2
404.1
379.4
1.29
1.18
1.39
1.53
1.23
1.53
1.20
11.37
11.37
6.65
12.04
7.12
6.57
5.11
8.62
10.62
10.85
1.96
13.88
7.42
15.89
27.43
27.51
13.23
22.80
67.08
31.37
10.04
0.141
0.15
0.171
0.763
0.39
0.265
0.207
10
10
10
5
7
10
10
-p.
oo
Figure 6-7
corabsum
-------
Charts
Delta Bottom Loss Ms. Observed Absorption
10
15 20
Observed Absorption
30
35
Figure 6-8
corabssum - dev from std.B.L.
-------
Chartl
100
90
80
70
O)
OJ
- ป
0)
ฐ c
D>
C/)
V)
10
0
Sign Percentage Vs. Observed Absorption
0
Seriesl
10 15 20
Observed Absorption (db)
Figure 6-9
25
30
35
corabssum- ampl. ratio
-------
Charts
Ampl. Ratio Vs. Observed Absorption
0.9
0.8
0.7
0.6
o
a
a
E
oy
0.3
0.2
0.1
10
15 20
Observed Absorption
25
30
35
Fi gure 6-10
corabssum - ampl. ratio
-------
7.0 PRELIMINARY AREA FINDINGS
At the completion of the calibration (Volume I), and core analysis (Volume II),
sufficient data existed to prepare initial summarized cross-section and area plots of
depositional sediment distribution with indications of areas of possible pollution/gas
distribution in the Elizabeth Park and Black Lagoon survey areas. The following
subsections will provide this summary. Final cross sectional survey line plots of the
study areas describing sediment distribution by density grouping (sand, silt, clay etc.) are
presented in Volume III. Also presented in Volume III are estimates of the volume and
location of depositional sediment. The information presented illustrates the form of
preliminary site data before extensive data interpretation of the seismic cross-sections
was undertaken.
7.1 Elizabeth Park Summary
Figure 7-1 is the summary overview of Elizabeth Park survey area. The plan view
was digitized from the NOAA maps for the region. The dot-dashed lines represent the
water depth contours, the water depth contour interval is 1.82 meter. Areas of high
'Pollution Factor' have 'P' and areas of medium 'Pollution Factor' have a small 'p'.
Areas of high fluff are designated by 'F', and thin layers of fluff by 'f. Note that a small
T is missing from drawing to the top right of the intersection of sectional lines 'A and
B'. The sectional plots are shown on the bottom and to the right of the plan view. In the
cross-sectional views, the bottom depth profile is given as a solid line and the
depositional sediment depths are shown with a dashed line. The difference in depth
between the solid and dashed lines indicates the depositional sediment thickness. All
depths are in meters.
The main deep water portion is almost free of depositional sediment, with only a
thin layer on the top right and top left of the plan view. In the top right area there is a thin
layer of fluff on top indicating that the shoaling at the bottom portion of the plan view
forms a river current void allowing the particles to settle to the bottom forming
depositional sediment.
The Elizabeth Park channel is polluted, as shown by sediment core analysis. There
is a sand and rock shoal at the entrance of the channel which effectively forms a water
current void allowing the contaminated sediment to settle behind the shoal.
52
-------
T7
a a) *ป
NOTE 2' Pollution
-------
7.2 Black Lagoon Summary
Figure 7-2 is the summary overview of Black Lagoon survey area. The plan view
was digitized from the NOAA maps for the region. The dot-dashed lines represent the
water bottom contours, the water bottom contour interval is 1.82. Areas of high
'Pollution Factor' have 'P' and areas of medium 'Pollution Factor' have a small 'p'.
Areas of high fluff are designated by 'F', and thin layers of fluff by T. The sectional
plots are shown on the bottom and to the right of the plan view. The water bottom depth
profile and shoreline is given as a solid line and the polluted sediment zones are shown
with a dashed line. The difference between the solid and dashed lines is the depositional
sediment thickness. All depths are in meters.
The area consists of a large sand shoal in the middle right of the plan view. This
shoal effectively makes the portion to the left of the shoal a settling pond. This
hypothesis is confirmed by the existence of fluff on the bottom. The heavier particles,
sand and silt, predominantly settle just to the left of the sand shoal. The lighter clay
particles are deposited along the shore and in the small bay on the top left of the plan
view. This small bay is surrounded with a sand ridge (dotted line) which traps the
contaminated depositional sediment within the small bay. Eddy currents cause the clay
particles to be carried into this small bay.
In the center and deeper area, there are various pockets of depositional sediments.
These pockets are on the north side of shallower bottom features. An example of this is
the bottom rise at the intersection of the Sectional B line with the bottom of the plan.
This variation in depositioal sediment pockets was confirmed by the detailed coring
program. There is no deposition on the deeper side of the shoal that is adjacent to the
main channel. Currents must be sufficient to flush any deposits in this area.
The discovery of fluff on the bottom is extremely important in understanding the
sedimentation rates of the pollutants. It is strongly suggested that micro-current meter
surveys be conducted to confirm the settling pond concept. These fluff deposits exhibited
in the seismic records and were confirmed in the cores.
54
-------
PQ
2
a
i*
i
u
LJ
NOTE 4i C = CLAY
SS = SILTY/SAND
SL = SILT
NOTE 3' Fluff Pollution (P-Hlgh,p-MecO
NOTE li CDNTDURS 8 1,82 M INTRV
SECTION A-A
CAULFIELD ENGINEERING
ELK. LAGDPN - DVERVIFW
JOB'2060
DRN BY
DDC
DATE'
3/19/96
SHEET
SCALE
REVi
DVG. ND, gQ60-BLKSL
Figure 7-2
-------
8.0 CONCLUSIONS AND RECOMMENDATIONS
The detailed analysis carried out has confirmed the following:
Calibration Verification - The calibration procedures carried out in Volume I of
this project were confirmed. The observed bottom loss at non-polluted sites
matched theoretical bottom loss for these sediment types within the quality
assurance program criteria. The offset from theoretical bottom loss was only -
1.35 db with a standard deviation of 1.326 db.
Acoustic Properties - The acoustic properties derived from the observations
confirmed relationships between these properties and the gross pollution/gas
content. The deviation of observed bottom loss from standard marine sediment
bottom loss appeared proportional to the amount of pollutant and/or gas in the
sediment. Further research is needed before this hypothesis can be confirmed.
Gas content affected the reflection sign of the bottom signal. The percentage of
phase reversal was grossly proportional to the level of pollution/gas in the
Trenton Channel sediments, suggesting that the areas of high pollution had
higher gas content. In addition, it was observed that gas containing sediments
had a higher reflection coefficient (bottom loss) than the same sediment
without gas.
Independent On-Site Core Velocity and Absorption - These independent
measurements confirmed the acoustic property relationships. A gross measure
of absorption is the energy loss from the first to the second layer corrected for
reflection coefficients. This has been approximated by a term called the
amplitude decay ratio in this report. Areas of high pollution had a lower
amplitude ratio, with the amplitude of the second layer being much smaller
than the first. Absorption losses are caused primarily by gas content and by
changes in the bonding of the grains of the sediments (pollution) and the
sediment porosity (water content) (Hamilton, 1972)
A prototype core velocity/absorption system was used in the field on the cores
immediately after retrieval of the cores from the bottom. These measurements
independently confirmed the observed trends seen in the seismic data. A
second independent Core Velocity/Absorption System used by the USAGE
confirmed that the absorption was abnormally high.
56
-------
Spatial Variability - The spatial variability of sediments in the Trenton Channel
was confirmed. The variation was as small as two meters in some cases. This
core/seismic analysis confirmed sediment structure changes spatially, within
meters, in the Trenton Channel. This variation was due in part to the complex
current structures and geology, and in part to the anomalous sediments. This
variation led to extensive additional processing of the data in order to obtain
meaningful results.
Sediment Deposition Mechanism The discovery of fluff on top of the
sediments suggests possible deposition. Detailed processing of the acoustic
data confirmed the existence of suspended fluff just above and on the bottom.
This strongly suggested that current patterns in areas such as Black Lagoon
generated a settling pond, concentrating sediment particles that are suspended
in the river flow. These fluff and suspended sediments occurred in all
depositional areas and were most prevalent in Black Lagoon.
Analysis of these data indicate that special arrays should be assembled for future
surveys to narrow the effective beam pattern. This would allow better handling of the
spatial variation problems. Also, a higher frequency system, such as 24 KHz would
allow better definition of the fluff layers.
The large amount of data processing required, even eliminating the boat handling
and electrical problems, was due to the high spatial variation in these sediments. The
Acoustic Core0 procedure, discussed in this report, is a method for the economical
definition of these sediments. The cost of coring at the close spacing required, due to
spatial variation, would be enormous.
57
-------
9.0 BIBLIOGRAPHY
The following documents have been used in the preparation of this report.
Breslau, L.R, 1965, "Classification of Sea-Floor Sediments with a Ship-borne Acoustical
System", Proc. Symp, "Le Petrole et la Mer", Sect. I, No. 132, pp 1-9, Monaco,
1965, (Also: Woods Hole Oceanographic Institute Contrib. No. 1678, 1965).
Caulfield Engineering, 1995, "Micro Survey-Acoustic Core and Physical Core Inter-
relations with Spatial Variation - Trenton Channel of the Detroit River, Field
Activities and Calibration Documentation", Volume I, Caulfield Engineering,
December 30, 1995, Job No. 2060.
Caulfield Engineering, 1997, "Micro Survey-Acoustic Core and Physical Core Inter-
relations with Spatial Variation - Trenton Channel of the Detroit River, Normal
and Contaminated Sediment Distribution Maps", Volume III, Caulfield
Engineering, December 30, 1995, Job No. 2060.
Caulfield, D. D., and Yim, Y.C., 1983, "Predictions of Shallow Subbottom Sediment
Acoustic Impedance Sediment while Estimating Absorption and Other Losses",
Journal of the Canadian Society of Exploration Geophysicists 19(1), 44-50.
Farara, D.G., and Burt, A.J., 1993, BEAK Consultants Report: Environmental
Assessment of Detroit River Sediments and Benthic Macroinvertebrate
Communities - 1991. Ontario Ministry of the Environment and Energy, London,
Ontario.
Giesy, J.P., Graney, R.L., Newsted. J.L., Rosiu, C.J., Benda, A., Kreis, Jr., R.G. and
Horvath, F.J. 1988, Comparison of Three Sediment Bioassay Methods using
Detroit River Sediments. Environ. Toxicol. Chem. 7:483-498.
Hamilton, E. L., 1970, "Reflection Coefficients and Bottom Losses at Normal Incidence
Computed from Pacific Sediment Properties", Geophysics 35, 995-1004.
Hamilton, E. L., 1972, "Compressional-wave Attenuation in Marine Sediments",
Geophysics 37(4), 620-646.
Helstrom, C. W. , 1960, "Statistical Theory of Signal Detection", Pergamon Press, New
York.
58
-------
Long, E.R. and L.G. Morgan. 1990. The Potential for Biological Effects of Sediment-
sorbed Contaminants Tested in the National Status and Trends Program. NOAA
Tech. Memo. NOS OMA 62. National Oceanic and Atmospheric Administration,
Seattle, Wa. 174pp.
Michigan Department of Environmental Quality (MDEQ). 1987. Stage 1 Report:
Remedial Action Plan for Detroit River Area of Concern. Surface Water Quality
Division, Lansing Michigan.
Officer, C. B., 1958, "Introduction to the Theory of Sound Transmission", McGraw-Hill,
New York.
Persaud, D., Jaagumagi, R.. and Hayton, A. 1993. Guidelines for the Protection and
Management of Aquatic Sediment Quality in Ontario. Water Resources Branch,
Ontario Ministry of the Environment, Toronto, Ontario.
Urick. R. J., 1983, "Principles of Underwater Sound", 3rd ed., McGraw-Hill, New York.
U.S. Environmental Protection Agency and Environment Canada (USEPA and EC).
1988. Final Report: Upper Great lakes Connecting Channels Study Volume 2.
December 1988. pp. 447-591.
59
-------
APPENDIX Bl
DETAILED EXAMPLES OF ANALYSIS
AT EACH CORE SITE
AVALIABLE FOR REVIEW AT U.S.EPA/CBSSS,
Grosse lie, Mi.
-------
APPENDIX B2
SUMMARY OF ACOUSTIC PROPERTIES
AT EACH CORE SITE
B2-1
-------
Sheets
ACOUSTIC PROPERTIES AT CORE SITES
Core Site 5
Density =
Core Leng
1.249
92.5
cm.
Std. Marine B. L.
Pollution Factor =
20
10
System/
Process
CAL1
3.5 -ms
3.5-crys.
7.0-ms
7.0-crys.
ACRS1
3.5 - ms
3.5 - crys.
7.0-ms
7.0 - crys
Bot.Loss
(db)
11.129
11.625
Std. Dev.
2.922
1.143
Ampl.
Decay
(ratio)
0.141
Absorp.
per meter
(db)
Sign
+/- %
27.43
Comments
Only one observat.
frequency/receiver
CD
ro
i
ro
Means
Set Stdev.
11.377
0.350725
2.0325
1.257943
0.141
27.43
Caulfield Engineering
-------
Sheets (2)
ACOUSTIC PROPERTIES AT CORE SITES
Core Site 6
Density =
Core Leng
1.18
101.5 cm.
Std. Marine B. L.
Pollution Factor =
22
10
System/
Process
CAL1
3.5-ms
3.5-crys.
7.0 -ms
7.0-crys.
ACRS1
3.5-ms
3.5 - crys.
7.0 - ms
7.0 - crys
BotLoss
(db)
11.129
11.625
Std. Dev.
2.922
1.143
Ampl.
Decay
(ratio)
0.141
Absorp.
per meter
(db)
Sign
+/- %
27.43
Comments
Only one observat.
frequency/receiver
CD
f\>
I
CO
Means
Set Stdev.
11.377
0.350725
2.0325
1.257943
0.141
27.43
Note: Same data as for Core 5
Caulfield Engineering
-------
Sheet3 (3)
ACOUSTIC PROPERTIES AT CORE SITES
Core Site 7
Density =
Core Leng
1.39
85.85 cm.
Std. Marine B. L.
Pollution Factor =
17.5
10
System/
Process
CAL1
3.5 -ms
3.5-crys.
7.0 -ms
7.0-crys.
ACRS1
3.5-ms
3.5 -crys.
7.0 - ms
7.0 - crys
Bot.Loss
(db)
7.2911
6.002
Std. Dev.
0.6875
2.2015
Ampl.
Decay
(ratio)
0.171
Absorp.
per meter
(db)
Sign
+/- %
13.23
Comments
Only one observat.
frequency/receiver
oo
r>o
i
Means
Set Stdev.
6.64655
0.911531
1.4445
1.07056
0.171
13.23
Caulfield Engineering
-------
Sheets (4)
ACOUSTIC PROPERTIES AT CORE SITES
Core Site 8
Density =
Core Leng
2.00
0
Std. Marine B. L.
Pollution Factor =
8.2
0
System/
Process
CAL1
3.5 -ms
3.5-crys.
7.0 -ms
7.0-crys.
ACRS1
3.5 - ms
3.5-crys.
7.0 - ms
7.0 -crys
Bot.Loss
(db)
8.954
8.811
Std. Dev.
1.843
3.046
Ampl.
Decay
(ratio)
0.874
Absorp.
per meter
(db)
Sign
+/- %
50.62
Comments
Only one observat.
frequency/receiver
CO
ro
Means
Set Stdev.
8.8825
0.101116
2.4445
0.850649
0.874
50.62
Caulfield Engineering
-------
Sheets (5)
ACOUSTIC PROPERTIES AT CORE SITES
Core Site 9
Density =
Core Leng
2.20
0
Std. Marine B. L. =
Pollution Factor =
7.50
0
System/
Process
CAL1
3.5-ms
3.5-crys.
7.0 -ms
7.0-crys.
ACRS1
3.5 - ms
3.5 - crys.
7.0 - ms
7.0-crys
BotLoss
(db)
10.07
9.19
Std. Dev.
2.39
1.87
Ampl.
Decay
(ratio)
0.507
Absorp.
per meter
(db)
Sign
+/- %
30.17
62.25
Comments
Only one observat.
frequency/receiver
oo
ro
Means
Set Stdev.
9.63
0.622254
2.13
0.367696
0.507
46.21
22.68399
Caulfield Engineering
-------
Sheets (6)
ACOUSTIC PROPERTIES AT CORE SITES
Core Site 10
Density =
Core Leng
1.53
37.0
cm.
Std. Marine B. L.
Pollution Factor =
14.0
5
System/
Process
CAL1
3.5 -ms
3.5-crys.
7.0 -ms
7.0-crys.
ACRS1
3.5 - ms
3.5 - crys.
7.0 - ms
7.0 - crys
Bot.Loss
(db)
12.48
11.61
Std. Dev.
2.16
2.6
Ampl.
Decay
(ratio)
0.763
Absorp.
per meter
(db)
Sign
+/- %
22.8
Comments
Only one observat.
frequency/receiver
DO
rv>
i
Means
Set Stdev.
12.045
0.615183
2.38
0.311127
0.763
22.8
Caulfield Engineering
-------
Sheets (7)
ACOUSTIC PROPERTIES AT CORE SITES
Core Site 11
Density =
Core Leng
2.00
0
Std. Marine B. L.
Pollution Factor:
8.2
0
System/
Process
CAL1
3.5 -ms
3.5-crys.
7.0 -ms
7.0-crys.
ACRS1
3.5 - ms
3.5 -crys.
7.0 - ms
7.0 - crys
Bot.Loss
(db)
9.68
8.66
8.49
7.691
6.53
7.99
10.57
8.33
Std. Dev.
2.69
0.854
1.398
2.81
0.727
1.21
Ampl.
Decay
(ratio)
0.537
0.469
0.548
0.638
Absorp.
per meter
(db)
Sign
+/- %
96.31
29.41
69.6
73.52
Comments
Sign Noisy
CD
ro
i
CO
Means
Set Stdev.
8.323
1.218994
1.3998
0.832954
0.551667
0.08456
67.21
27.81593
Massa Means
Massa Setdev.
0.5425
0.007778
82.955
18.88682
Caulfield Engineering
-------
Sheets (8)
ACOUSTIC PROPERTIES AT CORE SITES
Core Site 12
Density =
Core Leng
1.23
66.04 cm.
Std. Marine B. L.
Pollution Factor =
21
7
System/
Process
CAL1
3.5 -ms
3.5-crys.
7.0 -ms
7.0-crys.
ACRS1
3.5 - ms
3.5 -crys.
7.0 - ms
7.0 - crys
Bot.Loss
(db)
9.49
7.56
4.95
11.41
5.528
3.792
Std. Dev.
2.47
2.99
3.18
1.43
1.92
0.66
Ampl.
Decay
(ratio)
0.475
0.343
0.352
Absorp.
per meter
(db)
Sign
+/- %
73.52
60.65
68.29
Comments
CO
IN)
Means
Set Stdev.
7.121667
2.916626
2.108333
0.964353
0.39
0.07375
67.48667
6.472498
Massa Means
Massa Setdev.
0.409
0.093338
67.085
9.100464
Caulfield Engineering
-------
Sheets (9)
ACOUSTIC PROPERTIES AT CORE SITES
Core Site 13
Density =
Core Leng
2.20
0
Std. Marine B. L.
Pollution Factor =
7.5
0
System/
Process
CAL1
3.5-ms
3.5-crys.
7.0 -ms
7.0-crys.
ACRS1
3.5 - ms
3.5-crys.
7.0-ms
7.0 - crys
Bot.Loss
(db)
8.94
13.24
8.26
13.44
9.042
8.5
8.811
13.00
Std. Dev.
1.5
1.54
0.63
0.78
0.30
3.046
Ampl.
Decay
(ratio)
0.433
1.00
0.555
1.606
Absorp.
per meter
(db)
Sign
+/- %
95.09
80.13
34.78
Comments
0 - Very Noisy
DO
ro
i
Means
Set Stdev.
10.40413
2.353033
1.299333
098645
0.8985
0.530893
70
31.4052
Massa Means
Massa Setdev.
0.494
0.086267
87.61
10.57832
Caulfield Engineering
-------
Sheets (1O)
ACOUSTIC PROPERTIES AT CORE SITES
Core Site 14
Density =
Core Leng
2.00
7.62 cm.
Std. Marine B. L.
Pollution Factor:
8.2
0
System/
Process
CAL1
3.5 -ms
3.5-crys.
7.0 -ms
7.0-crys.
ACRS1
3.5 - ms
3.5 -crys.
7.0-ms
7.0 - crys
Bot.Loss
(db)
10.127
9.507
9.322
8.66
10.5
6.48
9.375
Std. Dev.
4.32
4.37
3.62
2.217
2.595
Ampl.
Decay
(ratio)
0.661
0.684
0.433
0.747
Absorp.
per meter
(db)
Sign
+/- %
83.33
39.21
82.53
79.98
Comments
17.95(Boat Moved
for bottom loss
O3
ro
Means
Set Stdev.
9.138714
1.31357
3.4244
0.984916
0.63125
0.137075
71.2625
21.41603
Massa Means
Massa Setdev.
0.547
0.16122
82.93
0.565685
Caulfield Engineering
-------
Sheets (11)
ACOUSTIC PROPERTIES AT CORE SITES
Core Site 15
Density =
Core Leng
1.45
58.4
Std. Marine B. L. =
Pollution Factor =
15.0
5
System/
Process
CAL1
3.5 -ms
3.5-crys.
7.0 -ms
7.0-crys.
ACRS1
3.5 - ms
3.5 - crys.
7.0 - ms
7.0-crys
Bot.Loss
(db)
12.80
11.78
10.58
10.86
16.96
13.00
11.88
14.54
Std. Dev.
5.46
4.4
2.3
3.46
1.03
1.05
1.057
Ampl.
Decay
(ratio)
0.747
0.888
0.832
0.6915
Absorp.
per meter
(db)
Sign
+/- %
34.55
30.39
58.82
Comments
no sign - noisy
03
I
Iซ
IN3
Means
Set Stdev.
12.80
2.102787
2.68
1.800608
0.789625
0.087405
41.25333
15.35471
Massa Means
Massa Setdev.
0.7895
0.060104
32.47
2.941564
Caulfield Engineering
-------
Sheet3 (12)
ACOUSTIC PROPERTIES AT CORE SITES
Core Site 16
Density =
Core Leng
1.22
16.5 cm.
Std. Marine B. L.
Pollution Factor =
21
7
System/
Process
CAL1
3.5 -ms
3.5-crys.
7.0 -ms
7.0-crys.
ACRS1
3.5 -ms
3.5 - crys.
7.0 - ms
7.0 - crys
Bot.Loss
(db)
12.87
12.79
11.031
12.664
13.14
13.25
12.823
12.29
Std. Dev.
1.22
5.96
4.832
3.125
0.40
4.57
3.21
Ampl.
Decay
(ratio)
0.803
0.460
0.629
0.789
Absorp.
per meter
(db)
Sign
+/- %
53.42
48.14
78.86
62.74
Comments
soft spot small
hard spot near
boat movement
causes high variance
plus gas content
DO
ro
i
Means
Set Stdev.
12.60725
0.700445
3.331
1.991813
0.67025
0.160863
60.79
13.47426
Massa Means
Massa Setdev.
0.716
0.123037
66.14
17.9888
Caulfield Engineering
-------
Sheets (13)
ACOUSTIC PROPERTIES AT CORE SITES
Core Site 17
Density =
Core Leng
1.40
90.1 cm.
Std. Marine B. L.
Pollution Factor =
18.0
9
System/
Process
CAL1
3.5 -ms
3.5-crys.
7.0 -ms
7.0-crys.
ACRS1
3.5 - ms
3.5 -crys.
7.0 - ms
7.0 - crys
Bot.Loss
(db)
6.502
7.92
3.0428
8.794
8.543
7.03
2.208
8.59
Std. Dev.
3.011
3.5
0.736
2.99
1.569
1.38
Ampl.
Decay
(ratio)
0.14
0.425
0.159
0.338
Absorp.
per meter
(db)
Sign
+/- %
35.29
55.81
27.45
59.8
Comments
Site 17sameSite 18
for acoustic data
ro
ro
i
Means
Set Stdev.
6.578725
2.575311
2.197667
1.112263
0.2655
0.138791
44.5875
15.6791
Massa Means
Massa Setdev.
0.1495
0.013435
31.37
5.543717
Caulfield Engineering
-------
Sheets (17)
ACOUSTIC PROPERTIES AT CORE SITES
Core Site 18
Density =
Core Leng
1.53
92.0 cm.
Std. Marine B. L.
Pollution Factor:
14.0
9
System/
Process
CAL1
3.5 -ms
3.5-crys.
7.0 -ms
7.0-crys.
ACRS1
3.5 - ms
3.5 - crys.
7.0 - ms
7.0 -crys
Bot.Loss
(db)
6.502
7.92
3.0428
8.794
8.543
7.03
2.208
8.59
Std. Dev.
3.011
3.5
0.736
2.99
1.569
1.38
Ampl.
Decay
(ratio)
0.14
0.425
0.159
0.338
Absorp.
per meter
(db)
Sign
+/- %
35.29
55.81
27.45
59.8
Comments
Site 18 same Site 17
for acoustic data
CO
IN3
I
Means
Set Stdev.
6.578725
2.575311
2.197667
1.112263
0.2655
0.138791
44.5875
15.6791
Massa Means
Massa Setdev.
0.1495
0.013435
31.37
5.543717
Caulfield Engineering
-------
Sheets (14)
ACOUSTIC PROPERTIES AT CORE SITES
Core Site 19
Density =
Core Leng
1.20
69.2 cm.
Std. Marine B. L.
Pollution Factor =
21
10
System/
Process
CAL1
3.5 -ms
3.5-crys.
7.0 -ms
7.0-crys.
ACRS1
3.5 - ms
3.5-crys.
7.0 - ms
7.0 - crys
BotLoss
(db)
5.45
4.32
3.26
4.43
7.016
7.812
3.125
5.4687
Std. Dev.
2.64
5.956
1.184
2.074
0.796
Ampl.
Decay
(ratio)
0.221
0.26
0.142
0.205
Absorp.
per meter
(db)
Sign
+/- %
11.76
60.78
8.33
47.05
Comments
oo
ro
i
i'
CTl
Means
Set Stdev.
5.110213
1.674478
2,53
2.047925
0.207
0.049105
31.98
25.97894
Massa Means
Massa Setdev.
0.1815
0.055861
10.045
2.425376
Caulfield Engineering
-------
APPENDIX B3
CORE SITES CROSS-SECTIONS
B3-1
-------
OBSERVATION
NORTHING
EASTING
CORE LENGTH
DENSITY
EOT. LOSS
AMPL. DECAY
PERCENT.
CORE 5/6
CORE 5
1.00 METERS
Ref.Fllei CR510001
CORE 6
LJ
(J
0.43 _,
1.18 _
1.93 -
2.64 .
3.37 _
4.10 J
SEDIMENT
POLLUTION FACTOR HIGH
LEGEND
FOAM/FLUFF
CLAY
SILTY CLAY TD
CLAYEY SILT
SILT
SILTY SAND TO
SANDY SILT
SAND
HARD/COMPACT
POLLUTED
SEDIMENT
CAULEIELD ENGINEERING
CDRE 05/06-SUMMARY SHEET
JOB' ฃ060
CRN BY
DDC
DATE-
SHEET
DVG,
SCALE
REVr
-------
OBSERVATION
NORTHING
EASTING
CORE LENGTH
DENSITY
EOT. LDSS
AMPL. DECAY
PERCENT.
CORE 7
CORE 7
0.763 M
ReF. File' CR520003
I
t~
a.
u
PI
0.43 _
1.18 -
1.92 _
2.64 _
3.37 _
4.10 J
SEDIMENT
POLLUTION FACTOR HIGH
LEGEND
FDAM/FLUFF
CLAY
SILTY CLAY TO
CLAYEY SILT
SILT
SILTY SAND TO
SANDY SILT
SAND
HARD/COMPACT
POLLUTED
SEDIMENT
CAULFIELD ENGINEERING
CORE 07 - SUMMARY SHETT
2060
DRN BY
DDC
DATEi
2/26/96
SHEET
SCALE
REVi
DVG, ND, gQ6Q-CRQ5
-------
DBSERVATIDN
CORE 8
NORTHING
EASTING
CORE LENGTH
DENSITY
BDT. LOSS
AMPL. DECAY
PERCENT.
NO CORE
SAND t GRAVEL
CORE 8
Ref. Fllei CR530007
I
I-
n.
4.10 _,
4.83 .
5.56 .
6.28 .
7.02 J
LEGEND
SEDIMENT
POLLUTED
SEDIMENT
FOAM/FLUFF
CLAY
SILTY CLAY TD
CLAYEY SILT
SILT
SILTY SAND TD
SANDY SILT
SAND
HARD/COMPACT
NDN-CDNSDLIDATED SAND,GRAVEL,RDCK,CLAY
ND POLLUTION
CONSOLIDATED MATERIALS
CAULFIELD ENGINEERING
CORE 08 - SUMMARY SHEET
JDBi ฃ060
DRN BY
DDC
DATEi
SCALE
SHEET
REV.
DVG. NG.
-------
OBSERVATION
CORE 9
NORTHING
EASTING
CORE LENGTH
DENSITY
EOT. LOSS
AMPL. DECAY
PERCENT.
NO CORE
SAND t GRAVEL
CORE 9
Ref. File' CR540003
LEGEND POLLUTED
SEDIMENT SEDIMENT
FOAM/FLUFF
CLAY
S1LTY CLAY TO
CLAYEY SILT
SILT
SILTY SAND TO
SANDY SILT
SAND
HARD/COMPACT
ul
o
-------
OBSERVATION
CORE 10
NORTHING
EASTING
CORE LENGTH
DENSITY
BDT. LOSS
AMPL. DECAY
PERCENT.
111ฐ
0.37 M
CORE 10
Ref. Flle> CR5400E3
LEGEND
SEDIMENT
POLLUTED
SEDIMENT
FOAM/FLUFF
CLAY
SILTY CLAY TD
CLAYEY SILT
SILT
SILTY SAND TO
SANDY SILT
SAND
HARD/COMPACT
m
X-'fC
u
<
u.
X
(-
Q.
6.28 _
7.03 _
7.65 -
8.11 -
8.56 J
.it :
MEDIUM POLLUTION - OIL
ND POLLUTION
CONSOLIDATED MATERIALS
6.00 M
CAULFIELD ENGINEERING
CORE 10 - SUMMARY SHEET
JDBigQ60
DRN BY
DDC
DATE'
a/26/96
SCALE
SHEET
REV.
DVG, ND. gQ60-CRin
-------
OBSERVATION
CORE 11
NORTHING
EASTING
CORE LENGTH
DENSITY
BDT. LOSS
AMPL. DECAY
PERCENT.
| I FLUFF
ND CDRE ONLY SAND GRAVEL
CORE 11
Ref. File' BCR10031
SEDIMENT
LEGEND
FOAM/FLUFF
CLAY
SILTY CLAY TD
CLAYEY SILT
SILT
SILTY SAND TD
SANDY SILT
SAND
HARD/COMPACT
<
L.
a;
6,28 _
7.02 _
7.65 -
8.11
8.56 J
FLUFF LAYER DN TOP
NDN CONSOLIDATED MATERIALS
ND POLLUTION
CONSOLIDATED MATERIALS
POLLUTED
SEDIMENT
0.60 M
CAULFIELD ENGINEERING
CDRE 11 - SUMMARY SHEET
JOB' ฃ060
DRN BY
DDC
DATE'
E/E6/96
SHEET
SCALE
REV.
DVG, ND, 2Q6Q-CR11
-------
OBSERVATION
NORTHING
EASTING
CORE LENGTH
DENSITY
EOT. LOSS
AMPL. DECAY
+ PERCENT.
CORE 12
CORE 12
0.66 M
Ref. File. BCR10036
SEDIMENT
LEGEND
FDAM/FLUFF
CLAY
SILTY CLAY TD
CLAYEY SILT
SILT
SILTY SAND TD
SANDY SILT
SAND
HARD/COMPACT
I
I-
O.
6.28 _,
7,02 J
7.65 J
8.11 J
B.56 J
MEDIUM POLLUTED CLAY
NON CONSOLIDATED MATERIALS
ND POLLUTION
CONSOLIDATED MATERIALS
1.00 M
CAULFIELD ENGINEERING^
CORE 12 - SUMMARY SHEET
JOB' 2060
DRN BY
DDC
DATE-
2/26/96
SHEET
REVi
DVG. ND. 2060-CRlg
-------
OBSERVATION
CORE 13
NORTHING
EASTING
CORE LENGTH
DENSITY
EOT. LOSS
AMPL. DECAY
PERCENT.
ND CORE ROCK/GRAVEL
CORE 13
Ref. File. BCR10056
SEDIMENT
LEGEND
FDAM/FLUrr
CLAY
SILTY CLAY TD
CLAYEY SILT
POLLUTED
SEDIMENT
SILT
SILTY SAND TO
SANDY SILT
SAND
HARD/COMPACT
I
t-
O.
6.28 _
7.oa .
7.65 -
e.n .
8.56 J
i "' ' * ,.'"' ." '
._ . ^- f
SAND/GRAVEL
NDN CONSOLIDATED MATERIALS
ND POLLUTION
CONSOLIDATED MATERIALS
0.52 M
CAULFIELD ENGINEERING
CDRE 13 - SUMMARY SHEET
JDB'gQfeO
DRN BY
DDC
DATE.
E/26/96
SHEET
SCALE
REV.
DVG, ND, gQ60-CRi^
-------
OBSERVATION
NORTHING
EASTING
CORE LENGTH
DENSITY
EOT. LOSS
AMPL. DECAY
PERCENT.
CORE 14
T
0.15 M
CORE 14
RcF.
BCR10060
.
Of
38
I
(-
D-
SEDIMENT
LEGEND
FDAM/FLUFF
CLAY
SILTY CLAY TD
CLAYEY SILT
SILT
SILTY SAND TD
SANDY SILT
SAND
HARD/COMPACT
POLLUTED
SEDIMENT
5.56 _,
6.28 .
7.02 .
7.65 .
8.11 J
.
SAND/GRAVEL
ND POLLUTION
NDN CONSOLIDATED MATERIALS
CONSOLIDATED MATERIALS
0.52 M
CAULEIELD ENGINEERING
CORE 14 - SUMMARY SHEET
JDS' 2060
DRN BY
DDC
DATE.
g/86/96
SHEET
SCALE
REV.
DVG. ND. gQ60-rRi4
-------
OBSERVATION
NORTHING
EASTING
CORE LENGTH
DENSITY
BDT. LOSS
AMPL. DECAY
+ PERCENT.
CORE 15
CORE 15
0.58 M
Ref, File. BRC200H
LEGEND PDLLUTtD
SEDIMENT SEDIMENT
1
FDAM/FLUFF
CLAY
SILTY CLAY TD
CLAYEY SILT
SILT
SILTY SAND TD
SANDY SILT
SAND
HARD/COMPACT
5.56 _,
6.28 _
X
I
O-
7.65 -
8.11 J
LOW POLLUTION
NDN CONSOLIDATED MATERIALS
CONSOLIDATED MATERIALS
0.30 M
CAULFIELD ENGINEERING
CORE 15 - SUMMARY SHEET
JOB' 2060
DRN BY
DDC
DATE'
2/28/96
SCALE
SHEET
REV.
DVG, ND, gQ60-CR15
-------
DBSERVATIDN
NORTHING
EASTING
CDRE LENGTH
DENSITY
BDT. LDSS
AMPL. DECAY
+ PERCENT.
CDRE 16
CDRE 16
0.16 M
Ref File' BRC20030
Ul
0
:.-)
FDAM/FLUFF
CLAY
SILTY CLAY TD
CLAYEY SILT
SILT
SILTY SAND TD
SANDY SILT
SAND
HARD/COMPACT
6.28 _
7.03 J
7.65 J
8.11 J
8.56 J
f.
POLLUTION WITH FLUFF
ND POLLUTION - ADDITIONAL ROCKS
NON CONSOLIDATED
0.53 M
IS
CAULFIELD ENGINEERING!
CDRE 16 - SUMMARY SHEET
JDBigQ60
DRN BY
DDC
DATE'
SHEET
REV.
DVG. ND. 2060-CGRE16
-------
SEDIMENT
DBSERVATIDN
CDRE 17
CORE 18
NORTHING
EASTING
CDRE LENGTH
DENSITY
BDT, LOSS
AMPL. DECAY
PERCENT.
1.000 METERS
CDRE 17/18
LEGEND
FDAM/rLUFF
CLAY
S1LTY CLAY TD
CLAYEY SILT
SILT
SILTY SAND TD
SANDY SILT
SAND
HARD/COMPACT
oc
ILJ
~
3.65 _
4.38 .
5.11
5.83
6.56
7.29 J
sNNNVS- POLLUTION FACTOR HIGH
POLLUTED
SEDIMENT
-0.405 M
CAULFIELD ENGINEERING
CDRE 17/18 SUMMARY SHEET
JOB' ฃ060
CRN BY
DDC
DATE'
2/25/96
SCALE
SHEET
DVG, ND, g06Q-CR
?EVi
7/18
-------
OBSERVATION
NORTHING
EASTING
CORE LENGTH
DENSITY
BDT, LOSS
AMPL. DECAY
PERCENT.
CORE 19
CORE 19
0.60 METERS
Ref. File' BCR40034
LEGEND POLLUTED
SEDIMENT SEDIMENT
FOAM/FLUFF
CLAY
SILTY CLAY TD
CLAYEY SILT
SILT
SILTY SAND TD
SANDY SILT
SAND
HARD/COMPACT
3.65 -,
4.38
LJ
O
Li.
ง~ 5.11
IUJ
ง1 5.83
6.56 -
\ POLLUTION FACTOR HIGH
-0.405 M
CAULFIELD ENGINEERING
CDRE 19 - SUMMARY SHEET
JDBi 2060
DRN BY
DDC
DATE.
3/18/96
SCALE
SHEET
REV.
DVG. ND. g06Q-CnRri9
-------
APPENDIX B4
IN FIELD CORE VELOCIMETER DATA
B4-1
-------
Sheetl
ESTIMATED IN FIELD CORE VELOCITY ANALYSIS
CORE NO:
Core Dens ity:
Core Material:
Est.
Material Depth
Below Bot
cm.
Page 1
POLLUTION FACTOR:
Sample Diameter:
1.29
Clay/Silt
From
Xmit
Position
cm.
Core Bot.
Receiver
Position
cm.
Frequency - 330 KHz
Distance IstArr. 2nd Arr. 3rd Arr.
Xmt-Rec. Delta T Delta T Delta T
cm. micro-sec, micro-sec micro-sec
System IstArr.
Offset Velocity
micro-sec m/sec
10
0.073
2nd Arr.
Velocity
m/sec
3rd Arr.
Velocity
m/sec
Water
Sediment
-10
5
103.5
103.5
103.5
103.5
103.5
103.5
103.5
103.5
89
89
89
89
87.5
103.5
101.5
102
102.5
104
105
106
107
89
90
91
89
90
7.3
7.569016
7.452516
7.368175
7.317103
7.452516
7.716217
8.095678
7.3
7.368175
7.569016
7.3
7.716217
100
110
60
80
mov->
90
mov->
mov->
36
60
36
36
36
100
140
160
145
144
96
100
100
108
96
10
10
10
10
10
10
10
10
Mean velocity
160
176
179
160
Mean Veloi
10
10
10
10
10
:ity
811.1111
756.9016
1490.503
1052.596
931.5645
2807.692
1473.635
2911.16
2807.692
2967.776
2484.172
1688.562
1490.503
1714.715
1812.465
1423.309
2546.512
2456.058
2523.005
2234.694
2691.703
2481.806
2433.333
2219.33
2239.354
2433.333
CD
ro
corvet - core O5 1
-------
Sheetl (2)
ESTIMATED IN FIELD CORE VELOCITY ANALYSIS
CORE NO:
Core Dens ity:
Core Material:
Est.
Material Depth
Below Bot
cm.
Page 2 POLLUTION FACTOR:
Sample Diameter:
1.29
Clay/Silt
Frequency - 330 KHz
10
0.073
From Core Bot.
Xmit
Position
cm.
Receiver
Position
cm.
Distance IstArr. 2nd Arr. 3rd Arr.
Xmt-Rec Delta T Delta T Delta T
cm. micro-sec, micro-sec micro-sec
System
Offset
micro-sec
1 st Arr.
Velocity
m/sec
2nd Arr.
Velocity
m/sec
3rd Arr.
Velocity
m/sec
Sediment
Sediment
35
60
65.5
65.5
65.5
65.5
65.5
65.5
65.5
33
33
33
64
63.5
63
62.5
68.5
66
65.5
32
34
35.3
7.452516
7.569016
7.716217
7.892401
7.892401
7.317103
7.3
7.368175
7.368175
7.653757
150
170
140
170
135
150
100
176
180
210
180
210
240
205
195
160
200
10
10
10
10
10
10
10
Mean velocity
Mean Velo
10
10
10
sity
Core Mean Velocity
540.644
482.2635
493.2751
818.6861
. ***
1335.709
1392.777
1183.86
954.4048
1123.077
938.2512
1194.839
1473.635
1208.488
1173.912
1531.321
oo
I
CO
corvel - core 05-2
-------
Sheet2
ESTIMATED IN FIELD CORE VELOCITY ANALYSIS
CORE NO:
Core Dens ity:
Core Material:
Est.
Material Depth
Below Bot
cm.
Page 1
1.
Clay/Silt
From
Xmit
Position
cm.
POLLUTION FACTOR:
Sample Diameter:
18
Core Bot.
Receiver
Position
cm.
Frequency - 330 KHz
Distance IstArr. 2nd Arr. 3rd Arr.
Xmt-Rec. Delta T Delta T Delta T
cm. micro-sec, micro-sec micro-sec
System
Offset
micro-sec
IstArr.
Velocity
m/sec
10
0.073
2nd Arr.
Velocity
m/sec
3rd Arr.
Velocity
m/sec
Sediment
Sediment
30
10
71.5
71.5
71.5
71.5
71.5
71.5
71.5
89
89
71.5
73
73
74
70.7
70
69.5
87.8
89
7.3
7.452516
7.452516
7.716217
7.343705
7.452516
7.569016
7.397973
7.3
mov->
mov->
mov->
mov->
mov->
mov->
144
136
140
152
142
168
164
160
164
250
10
10
10
10
10
10
10
Mean velocity
10
10
Mean Velocity
Core Mean Velocity
1634.328
1774.409
1719.811
1630.187
1669.024
1415.035
1474.484
1796.08
1479.595
1422.078
1450.836
1623.458
1576.878
CO
-p.
corvel - core06 Page 1
-------
Sheets
ESTIMATED IN FIELD CORE VELOCITY ANALYSIS
CORE NO:
7 Page 1
POLLUTION FACTOR:
Sample Diameter:
10
0.073
Core Dens ity:
Core Material:
Est.
Material Depth
Below Bot
cm.
1.39
Silt/Clay
Frequency
- 330 KHz
From Core Bot.
Xmit
Position
cm.
Receiver
Position
cm.
Distance
Xmt-Rec.
cm.
1st An-.
Delta T
micro-sec.
2nd Arr.
Delta T
micro-sec
3rd Arr.
Delta T
micro-sec
System
Offset
micro-sec
1st Arr.
Velocity
m/sec
2nd Arr. 3rd Arr.
Velocity Velocity
m/sec m/sec
Water
& Fluff
Sediment
-10
5
93.8
92
92
92
92
92
92
81
81
81
81
93
94.7
92.5
91
89.8
86.7
97.8
82
79.9
79.4
78.3
7.343705
7.783315
7.317103
7.368175
7.624303
9.021086
9.323626
7.368175
7.382412
7.473286
7.783315
88
96
92
92
100
120
108
72
110
70
mov->
112
210
144
140
10
10
10
10
10
10
10
Mean velocity
Mean Velo
***** ****
10
10
10
10
city
941.5006
905.0367
892.3297
898.5579
847.1448
820.0988
951.3904
1188.415
L738.2412
1245.548
L893.7227
2167.11
1107.362
1673.124
1796.15
1416.564
**********
CD
I
in
corvel - core 07 - Page 1
Page 1
-------
Sheet3 (2)
ESTIMATED IN FIELD CORE VELOCITY ANALYSIS
CORE NO: 7 Page 2
Core Dens ity: 1.39
Core Material: Silt/Clay
Est. From Core Bot.
Material Depth Xmit Receiver
Below Bot Position Position
cm. cm. cm.
Distance
Xmt-Rec.
cm.
POLLUTION FACTOR:
Sample Diameter:
Frequency - 330 KHz
IstArr. 2nd Arr. 3rd Arr. System
Delta T Delta T Delta T Offset
micro-sec, micro-sec micro-sec micro-sec
IstArr.
Velocity
m/sec
10
0.073
2nd Arr. 3rd Arr.
Velocity Velocity
m/sec m/sec
Sediment
Sediment
Sediment
20
40
55
65
65
65
65
40
40
19
64
64.7
67.8
63.1
36.7
39
21
7.368175
7.306162
7.818568
7.543209
8.011242
7.368175
7.569016
68
60
72
mov->
60
60
50
128
144
mov->
138
112
80
250
180
10
10
10
10
Mean velocity
10
10
Mean Velocity
10
Mean Velocity
Core Mean Velocity
Core Mean Velocity Without Last Layer
1270.375
1461.232
1261.059
1602.248
1473.635
1892.254
1873.265
1635.708
1767.94
1639.63
2167.11
1747.665
3243.864
2568.059
1842.978
1601.285
1628.868
2218.591
DO
I
CTl
corvel - core 07 Page 2
-------
Sheet4
ESTIMATED IN FIELD CORE VELOCITY ANALYSIS
CORE NO:
Core Dens ity:
Core Material:
Est.
Material Depth
Below Bot
cm.
Page 1
1.53
Silty/Sand
From Core Bot.
Xmit Receiver
Position Position
cm. cm.
POLLUTION FACTOR:
Sample Diameter:
Frequency - 330 KHz
Distance IstArr. 2nd Arr. 3rd Arr. System
Xmt-Rec. Delta T Delta! Delta! Offset
cm. micro-sec, micro-sec micro-sec micro-sec
IstArr.
Velocity
m/sec
5
0.073
2nd Arr.
Velocity
m/sec
3rd Arr.
Velocity
m/sec
Water
Some
Fluff
Sediment
Sediment
-15
8
20
50
50
50
29.4
29.4
29.4
25
25
13
13
50
52.2
48.1
30.1
26.2
31
27.5
25
15
12.5
7.3
7.624303
7.543209
7.333485
7.970571
7.473286
7.716217
7.3
7.569016
7.317103
93
101
52
56
52
48
42
48
42
104
190
94
160
94
96
98
150
98
10
10
10
Mean velocity
10
10
10
10
10
Mean Velocity
10
10
Mean Velocity
Core Mean Velocity
879.5181
837.8355
1746.068
1732.733
1779.354
2030.583
2281.25
1991.846
2286.595
2433.288
1257.201
1351.961
2619.102
1594.114
2669.031
2691.703
2488.636
2163.257
1621.932
2494.467
2098.71
2130.984
DO
->
I
corvel-corel0-Page 1
-------
Sheets
ESTIMATED IN FIELD CORE VELOCITY ANALYSIS
COR
Core
Core
ENO: 12
Dens ity:
Material:
Est.
Material Depth
Below Bot
cm.
Page 1
POLLUTION FACTOR:
Sample Diameter:
1.23
Clay/Tr. Gravel
From
Xmit
Position
cm.
Core Bot.
Receiver
Position
cm.
Frequency - 330 KHz
Distance IstArr. 2nd Arr. 3rd Arr.
Xmt-Rec. Delta T Delta! Delta T
cm. micro-sec, micro-sec micro-sec
System
Offset
micro-sec
IstArr.
Velocity
m/sec
7
0.073
2nd Arr.
Velocity
m/sec
3rd Arr.
Velocity
m/sec
Water
+ Chalk
Material
Sediment
Sediment
-10
22
42
61
61
61
61
42
42
42
42
22
22
60
62.8
59.5
57.8
42.5
42
40.5
39
20.5
22
7.368175
7.518643
7.452516
7.970571
7.317103
7.3
7.452516
7.892401
7.452516
7.3
93
96
92
96
104
120
100
120
120
120
10
10
10
10
887.7319
874.2609
908.8435
Mean Velocity
10
10
10
10
Mean Velocity
10
10
Mean Velocity
Core Mean Velocity
850.826
2543.799
1303.659
1990.909
2484.172
2152.473
1869.595
2032.504
1990.909
2011.707
1940.651
CO
oo
corvel - core 12- Page 1
-------
Sheets
ESTIMATED IN FIELD CORE VELOCITY ANALYSIS
CORE NO: 18 Page 1 POLLUTION FACTOR:
Sample Diameter:
Core
Core
Dens ity:
Material:
Est.
Material Depth
Below Bot
cm.
1.53
Sandy/Silt
From Core Bot.
Xmit Receiver
Position Position
cm. cm.
Frequency - 330 KHz
Distance IstArr. 2nd Arr. 3rd Arr.
Xmt-Rec. Delta T Delta T Delta T
cm. micro-sec, micro-sec micro-sec
System
Offset
micro-sec
IstArr.
Velocity
m/sec
9
0.073
2nd Arr.
Velocity
m/sec
3rd Arr.
Velocity
m/sec
Water
+ Chalk
Material
Sediment
Sediment
-10
28
66
81.3
81.3
81.3
81.3
66.6
66.6
66.6
26.7
26.7
26.7
82
83
79
81.4
66.2
65.2
64.2
26.7
26
23
7.333485
7.495332
7.653757
7.300685
7.310951
7.433034
7.6844
7.3
7.333485
8.184131
100
100
96
88
94
96
96
95
104
130
130
90
120
145
175
100
10
10
10
10
814.8316
832.8147
848.9168
Mean Velocity
10
10
10
Mean Velocity
10
10
10
Mean Velocity
Core Mean Velocity
937.3014
884.885
893.5349
848.8372
862.7629
2340.474
1873.833
1342.174
2741.607
2027.191
1496.904
1622.222
1333.361
2728.044
1479.045
1487.975
oo
corevel - core 18 - Page 1
-------
Sheet?
ESTIMATED IN FIELD CORE VELOCITY ANALYSIS
CORE NO:
Core Dens ity:
Core Material:
Est.
Material Depth
Below Bot
cm.
Page 1
1
Clay/Silt
From
Xmit
Position
cm.
POLLUTION FACTOR:
Sample Diameter:
2
Core Bot.
Receiver
Position
cm.
Frequency - 330 KHz
Distance IstArr. 2nd Arr. 3rd Arr.
Xmt-Rec. Delta T Delta T Delta!
cm. micro-sec, micro-sec micro-sec
System
Offset
micro-sec
1 st Arr.
Velocity
m/sec
10
0.073
2nd Arr.
Velocity
m/sec
3rd Arr.
Velocity
m/sec
Water
Sediment
Sediment
-8
5
25
53
53
53
53
38.5
38.5
38.5
20.5
20.6
20.6
53.1
53.6
54.1
52.2
41.7
39
37
20.6
19.5
18.5
7.300685
7.324616
7.382412
7.343705
7.970571
7.317103
7.452516
7.300685
7.382412
7.596052
94
98
98
94
92
92
96
102
102
108
140
140
136
140
170
150
150
140
150
124
10
10
10
10
869.1292
832.3427
838.9104
874.2506
Mean Velocity
10
10
10
Mean Velocity
10
10
10
Mean Velocity
Core Mean Velocity
972.0208
892.3297
866.5717
793.5527
802.436
775.1073
1684.773
1690.296
1757.717
1694.701
1280.265
1494.482
1567.951
1596.968
^1231.72
1684.773
1581.945
1998.961
1272.796
1252.258
CD
I
t'
o
corvel - core 19- Paae 1
-------
APPENDIX B5
IN FIELD CORE ABSORPTION DATA
B5-1
-------
SheeM
CORE RELATIVE ABSORPTION ANALYSIS
CORE NO:
POLLUTION FACTOR 10
Sample Diamter: 0 073
meters
CO
en
Core Density: 1.29
Core Material. Clay/Silt Frequency - 330 KHz
Normalized
Material Depth Gain Gain Signal Signal Level Cor. Relative To Absorp.
Below Bot. Setting Level Level db 1 volt db Water db/meter
cm. nrs. db volts db
Water
Sediment
Sediment
Sediment
Sediment
-10
5
30
33
60
630
1500
1500
1700
1500
66
83.4
83.4
84
83.4
5
3.75
3.25
4.6
1
13.9
11.5
10.2
13.3
0
52.1
71.9
73.2
70.7
83.4
0
19.8
21.1
18.6
31.3
0
271.2329
289.0411
254.7945
428.7671
Mean Loss
Mean Absorption/Meter
22.7
310.9589
corabsOS
-------
Sheetl (2)
CORE RELATIVE ABSORPTION ANALYSIS
CORE NO:
Core Density:
Core Material:
1.29
Clay/Silt
POLLUTION FACTOR
Sample Diamter:
Frequency - 330 KHz
10
0.073 meters
CD
01
1
CO
Normalized
Material Depth Gain Gain Signal Signal Level Cor. Relative To Absorp.
Below Bot. Setting Level Level db 1 volt db Water db/meter
cm. hrs. db volts db
Water
Sediment
Sediment
from core 5
30
10
630
1500
1400
66
83.4
82.9
5
3.5
5
13.9
10.8
13.9
52.1
72.6
69
0
20.5
16.9
0
280.8219
231.5068
Mean Absorption/Meter 256.1644
corabslO
-------
Sheetl (7)
CORE RELATIVE ABSORPTION ANALYSIS
CORE NO:
POLLUTION FACTOR 10
Sample Diamter: 0 073
meters
DO
ui
I
Core Density. 1.39
Core Material: Silt/Clay Frequency - 330 KHz
Normalized
Material Depth Gain Gain Signal Signal Level Cor. Relative To Absorp.
Below Bot. Setting Level Level db 1 volt db Water db/meter
cm. hrs. db volts db
Water
Sediment
Sediment
Sediment
Sediment
-10
5
20
44
60
900
1730
1730
1730
1730
74.9
84.3
84.3
84.3
84.3
5
3
2
0.8
0.3
13.9
9.5
6
-1.9
-10.5
61
74.8
78.3
86.2
94.75
0
13.8
17.3
25.2
33.75
0
189.0411
236.9863
345.2055
462.3288
Mean Loss 22.5125
Mean Absorption/Meter
308.3904
corabsOT
-------
Sheen (3)
CORE RELATIVE ABSORPTION ANALYSIS
CORE NO:
10
Core Density:
Core Material:
1.53
Silty/Sand
POLLUTION FACTOR
Sample Diamter:
Frequency - 330 KHz
5
0.073
meters
CO
en
i
en
Normalized
Material Depth Gain Gain Signal Signal Level Cor. Relative To Absorp.
Below Bot. Setting Level Level db 1 volt db Water db/meter
cm. hrs. db volts db
Water
Sediment
Sediment
-11
9
24
630
1300
1300
66
82.5
82.5
5
4
2
13.9
12.04
6
52.1
70.46
76.5
0
18.36
24.4
0
251.5068
334.2466
Mean Loss 21.38
Mean Absorption/Meter 292.8767
corabslO
-------
Sheetl (4)
CORE RELATIVE ABSORPTION ANALYSIS
CORE NO:
Core Density:
Core Material:
12
1.23
Clay/Tr Gravel
POLLUTION FACTOR
Sample Diamter:
Frequency - 330 KHz
0.073 meters
oo
in
Normalized
Material Depth Gain Gain Signal Signal Level Cor. Relative To Absorp.
Below Bot. Setting Level Level db 1 volt db Water db/meter
cm. hrs. db volts db
Water
Sediment
Sediment
-6
22
42
730
1700
1700
72
84.3
84.3
4.5
2
0.1
13.06
6
-20
58.94
78.3
104.3
0
19.36
45.36
0
265.2055
621.3699
Mean Loss 32.36
Mean Absorption/Meter 443.2877
corabs12
-------
Sheetl (5)
CORE RELATIVE ABSORPTION ANALYSIS
CORE NO:
18
Core Density:
Core Material:
1.53
Sandy/Silt
POLLUTION FACTOR
Sample Oiamter:
Frequency - 330 KHz
10
0.073 meters
Normalized
Material Depth Gain Gain Signal Signal Level Cor. Relative To Absorp.
Below Bot. Setting Level Level db 1 volt db Water db/meter
cm. hrs. db volts db
Water
Sediment
Sediment
Sediment
-10
10
20
45
730
1730
1730
1730
75
84.3
84.3
84.3
5
2
0.56
0.1
13.9
6
-4.9
-20
61.1
78.3
89.2
104.3
0
17.2
28.1
43.2
0
235.6164
384.9315
591.7808
CD
tn
i
Mean Loss 29.5
Mean Absorption/Meter 404.1096
corabs18
-------
Sheet! (6)
CORE RELATIVE ABSORPTION ANALYSIS
CORE NO:
Core Density:
Core Material.
19
1.2
Clay/Silt
POLLUTION FACTOR
Sample Diamter:
Frequency - 330 KHz
10
0.073 meters
Normalized
Material Depth Gain Gain Signal Signal Level Cor. Relative To Absorp.
Below Bot. Setting Level Level db 1 volt db Water db/meter
cm. hrs. db volts db
Water
Sediment
Sediment
Sediment
-10
5
15
28
1130
1730
1730
1730
80
84.3
84.3
84.3
5
2.5
0.15
0.1
13.9
7.9
-16.4
-20
66.1
76.4
100.7
104.3
0
10.3
34.6
38.2
0
141.0959
473.9726
523.2877
CO
en
i
CO
Mean Loss 27.7
Mean Absorption/Meter 379.4521
corabs19
-------
FINAL REPORT
MICRO SURVEY - ACOUSTIC CORE AND
PHYSICAL CORE INTER - RELATIONS WITH
SPATIAL VARIATION,
TRENTON CHANNEL OF THE DETROIT RIVER
VOLUME III
NORMAL AND CONTAMINATED SEDIMENT
DISTRIBUTION MAPS
Prepared
June 25, 1997
By
David Caulfield
Caulfield Engineering, Incorporated
Oroville, WA
And
John C. Filkins
U.S. Environmental Protection Agency, Office of Research and Development
National Health and Environmental Effects Research Laboratory
Mid-Continental Ecology Division-Duluth
Community Based Science Support Staff
9311 Groh Rd., Grosse He, MI 48138
-------
This report was prepared for the U.S. Army Engineers Waterways Experimental Station
under contract No. DACW39-95-C-0070. This report meets one of the deliverables for
the Interagency Agreement. DW96947730-01-0, between U.S. ACOE/Waterways
Experimental Station and U.S. EPA/Great Lakes National Program Office and U.S.
EPA/National Health and Environmental Effects Research Laboratory/Mid-Continental
Ecology Division-Duluth/Cornmunity Based Science Support Staff.
11
-------
CONTENTS
PREFACE v
1.0 INTRODUCTION 1
1.1 Background 1
1.2 Site Overview 2
1.3 Project Overview 3
2.0 DATA INTERPRETATION PROCEDURES - LAYER SELECTION 5
2.1 Layer Identification Steps 6
2.1.1 Stepl: Diffraction 6
2.1.2 Step 2: Amplitude Analysis 10
2.1.3 Step 3: ACRS Plots 21
2.1.3.1 Step 3.1: ACRS Envelope Plot 21
2.1.3.2 Step 3.2: ACRS Pick Plot 21
2.1.4 Step 4: Integrating the Three Layer Picking Technique 25
2.1.5 Step 5: Survey Line Layer Cross-Section 25
3.0 DATA INTERPRETATION PROCEDURES SEDIMENT
IDENTIFICATION 30
3.1 Stepl: Matching the Sediment Layers to the Cores 30
3.2 Step 2: Bottom Loss Processing 31
3.3 Step 3: Contamination, Bottom Loss, and Plus Sign Percentage 33
3.4 Analysis Summary 42
4.0 DISCUSSION OF RESULTS 46
4.1 Cross-Sections for Black Lagoon Site 46
4.2 Cross-Sections for Elizabeth Park Site 47
111
-------
4.3 Cross-Sections for Elizabeth Channel 49
4.4 Estimating Sediment Volumes - Black Lagoon 51
4.4.1 Step 1: Data Sampling and Contour Plots Generation 51
4.4.2 Step 2: Dealing with Extrapolated Grid Values 54
4.4.3 Step 3: Two Volume Estimates for Black Lagoon 54
4.5 Estimating Sediment Volumes - Elizabeth Park 65
5.0 CONCLUSIONS AND RECOMMENDATIONS 77
6.0 BIBLIOGRAPHY 79
APPENDIX Al. CROSS-SECTIONAL PLATES Al-1
APPENDIX A2. MATLAB PROGRAMS A2-1
A2.1 Bottom Loss Computations A2-2
A2.2 Phase Computations A2-6
A2.3 Layer Thickness Contour Routine A2-10
A2.4 Scales Survey Lines Routine A2-19
A2.5 Volume Estimate Routine A2-24
A2.6 Depth Contour Routine A2-27
A2.7 Elizabeth Park Layer Contour Routine A2-33
APPENDIX A3. TECHNICAL TERMS AND SOFTWARE DISPLAY
DESCRIPTIONS A3-1
A3.1 Acoustic Impedance A3-2
A3.2 Reflectivity A3-2
A3.3 Bottom Loss A3-2
A3.4 Sonar Equation A3-3
A3.5 Windows CAL1 Routine A3-3
A3.6 Acoustic Core Reflection/Sign (ACRS) Routine A3-6
A3.6.1 Correlation Display A3-6
A3.6.2 ACRS Full Wave Envelope Display A3-8
A3.7 Diffraction Examples A3-10
A3.8 Envelope Layer Detection A3-10
IV
-------
PREFACE
This document is Volume III of a series of reports on portions of the Detroit
River's Trenton Channel sediment distribution. The previous volumes covered the
following:
Volume I Field Data Acquisition and Calibration (Caulfield Engineering,
December 30. 1995). This report summarizes field acquisition and
calibration procedures.
Volume II - Core Analysis and Summary Findings (Caulfield Engineering,
March 23, 1996). This report relates the acoustic properties of the
sediments to the physical properties of the cores at selected sites.
Volume III provides final outputs identifying depositional sediment layer cross-
sections as well as estimated dredging volumes for depositional sediments thicker than 1
meter and as an option, thicker than 0.5 meters. This is done for the two major sites.
Black Lagoon and Elizabeth Park. Also provided are bathymetric contours and
depositional sediment thickness contours. A critical result of this study shows that some
depositional sediments are very thin, less than 0.5 meters, and bounded by rocks and
sand. These layers may be too thin to dredge and are not included in the volume
estimates.
Because of the spatial variation and contaminated nature of the sediments, and the
many thin layers found, new special analysis techniques were required. This volume
summarizes these new analysis techniques necessary to extract information regarding the
nature and distribution of the sediment.
The overall mapping and analysis program was carried out under the supervision
of Darla McVan and Terry Waller, Hydraulic Analysis Branch (HAB), of the Hydraulic
Structure Division (HSD) of the Waterways Experimental Station, U.S. Army Corps of
Engineers, Vicksburg, MS. This project was a cooperative effort with the U.S.
Environmental Protection Agency, Mid-Continental Ecology Division-Duluth,
Community Based Science Support Staff, Grosse He, MI. John Filkins provided
technical review and guidance for the USEPA.
v
-------
1.0 INTRODUCTION
1.1 Background
Significant deposits of contaminated sediment occur in many waterways near
urban centers, including those of the Great Lakes basin. Some of these deposits have
accumulated for decades and reflect historic loadings of pollution from cities, industry
and agricultural runoff. These deposits continue to contaminate benthic and pelagic
organisms through various transport and fate processes. The removal, treatment and
disposal of these contaminants may be extremely costly.
A cost effective and rapid means of mapping the distribution of sediments in
harbors and rivers is required to facilitate the remedial decisions facing environmental
managers. Models are being developed to predict the potential for sediment erosion in
harbors and rivers. An accurate prediction of sediment resuspension by these models
requires accurate mapping of sediments.
Both the Army Corps of Engineers/Water Ways Experimental Station (USACE-
WES) and the U.S. Environmental Protection Agency/Office of Research and
Development/Mid-Continent Ecology Division/Community Based Science Support Staff
(USEPA/MED/CBSSS) have research interest in mapping sediment in harbors and rivers
by acoustic profiling. In 1994 the Great Lakes National Program Office, The Michigan
Department of Natural Resources and USEPA/MED/CBSSS conducted a sediment
survey by contract with Caulfield Engineering using the Acoustic Core0 system. The
survey of the Detroit River's Trenton Channel demonstrated that the Acoustic Core0
system has the potential for mapping the sediment in harbors and rivers of the Great
Lakes. The 1994 survey results identified high spatial variance in sediment distribution
and possible gas content in these sediments. The acoustic method required optimization
for use in shallow water (2ft to 30 ft) and areas which exhibit a high degree of sediment
spatial variability.
The USEPA requested that USAGE-WES optimize the Acoustic Core0 system.
Two sites in the Trenton Channel, Elizabeth Park and Black Lagoon, were selected for
micro-surveys to demonstrate the Acoustic Core0 system and to confirm the 1994
observations. The request required survey grids of very closely (5-10 meters) spaced
observation lines with high ping repetition rates. In addition, ground truth piston cores
were to be taken at calibration sites and other sites of interest. The data were to be
acquired and processed with the Caulfield Engineering Acoustic Core suite of software.
-------
Final project outputs were to include identification of the location and volume of
depositional sediment, survey line cross section plots of horizontal and vertical sediment
distribution by density group, and to specify the acoustic properties of the possible
contaminated sediments.
Volume I of this report summarizes the field acquisition and system calibration
procedures, and Volume II of this report provides the relationship of the sediment's
acoustic properties and the properties to the cores taken at selected sites. Volume III
provides final outputs identifying sediment layer cross-sections, surface contour plots and
estimated dredging volumes for the thicker sediment layers.
The standard Acoustic Core0 analysis software (AC60) which predicts acoustic
impedance was inadequate to delineate the differences between hard packed sediments
and possible contaminated sediments. New analysis procedures and software, Windows-
based Calibration and Acoustic Core Reflection/Sign, were necessary to identify the
differences. This report will summarize the procedures used in identifying the layering.
Final results closely match the piston cores taken by Caulfield Engineering and the
earlier vibra-cores taken by the USEPA.
The high spatial variation was also confirmed and is illustrated in the
accompanying cross-section drawings. Detailed discussion is provided on both the
analysis procedures and the spatial variance problems.
1.2 Site Overview
The Detroit River has been identified by the International Joint Commission as an
Area of Concern due to a number of water quality problems, including contaminated
sediments and degraded benthic communities. In addition, the river is also listed under
the Michigan Environmental Response Act (P.A. 307, 1982 as amended) due to
contaminated sediments.
Sediment studies conducted under the Upper Great Lakes Connecting Channels
Study (USEPA and EC, 1988) and other research activities, documented sediments
contaminated with metals, PCBs, and oil and grease (Farara and Burt, 1993) in multiple
locations in the Detroit River and Trenton Channel. Impaired uses relating to
contaminated sediments, as identified in the Detroit River Stage 1 Remedial Action Plan
(MDEQ, 1987), include restrictions on dredging activities, degraded benthic
communities, exceeding Michigan Water Quality Criteria for fish consumption
advisories, and increased incidence of fish tumors.
The Trenton Channel is located in the lower Detroit River between Grosse He and
the Michigan mainland, Plate 33. It is approximately nine miles in length and carries 21
percent of the total river flow, with an average velocity of 1.08 to 1.9 ft/sec. The Detroit
River and Trenton Channel, a heavily industrialized area and a major navigation route,
-------
has been identified as severely degraded in terms of water and sediment quality and
benthic communities (USEPA and EC, 1988). Numerous point sources in the area
include steel plants, waste water treatment plants and chemical and automotive
manufacturing industries. Concentration of arsenic, nickel, PCBs, and oil and grease in
Trenton Channel sediments have been found to exceed the recommended guidelines for
sediments (Long and Morgan, 1990; Persaud et al., 1993). Data from various sediment
Toxicity tests conducted showed sever impacts compared to other Detroit River locations
and reference stations for a number of biota tested (Giesy et al., 1988).
1.3 Project Objectives
The primary objective of the USEPA-USACE-Caulfield Engineering effort was
the acquisition of micro-survey data using the Acoustic Core0 System and the processing
and analysis of selected results and sites to determine what the sediment stratigraphy in
near shore areas of the Trenton Channel. Two specific sites were chosen to demonstrate
soft sediment mapping, allowing the calculation of volume estimates. Volume III
provides the cross-sectional plots for these data, maps identifying surficial sediment
deposition by density group and contours of sediment thickness with estimates of
depositional sediment volumes. Volume II of this series of reports provided the geo-
acoustic relationships with the core data.
This project uses the Acoustic Core0 suite of software to identify and map the
gross distribution of these sediments as presented in this report. Piston core data is
required to calibrate the acoustic process. It is important to note that the exact
relationship of engineering geo-acoustic properties of the sediments to the various types
of pollutants is not known. It is only known that pollutants and or micro-gas bubbles
contained in sediment may change the acoustic properties, and in some cases radically,
from standard marine sediments. Volume II has shown that as the gross contaminants
(observed from the chemical analysis of the USEPA vibra-cores collected in 1994)
increase, the deviation of the bottom loss for similar non-contaminated marine sediments
also increases.
The tasks listed in the interagency agreement between EPA and ACOE included:
> Optimize the Acoustic Corer for use mapping, in shallow water (2ft-30ft),
where sediments exhibit a high degree of heterogeneity .
> Demonstrate the accuracy of the Acoustic Corer to characterize sediment type
and map the distribution of sediment type at depth. The demonstration should
take place at three sites (shallow, medium and deeper water depths) in the
Trenton Channel, Detroit River.
> Collect and conduct the necessary geophysical characterization of sediment
cores needed for calibration and validation of the acoustic corer.
-------
> At the demonstration sites, provide mapping of the distribution of the soft
sediment.
> Provide a written report on the Acoustic Corer Optimization, describing the
rational, approach and results.
> Provide a survey report on the demonstration site surveys. This report is to
include:
1. A description of the Acoustic Corer and the fundamentals of operation
2. The survey design
3. Results of the survey
4. Graphical mapping of the sediment distribution for each site
5. A calculation of the volume of soft sediment at each site
All requests summarized were met. Because of some boat logistics problems
during data acquisition, data formatting of the final results hi GIS type ASCII formats
was impossible under the project scope. However, all Auto-Cad, Matlab, and Acoustic
Core Reflection/Sign files were supplied.
Without the detailed quality assurance program carried out during the field
exercises this project would not have succeeded. The quality assurance program enabled
absolute calibrations of the sound sources, which in turn allowed for the quantitative
identification of the sediment types.
-------
2.0 DATA INTERPRETATION PROCEDURES -
LAYER SELECTION
Due to the many unique aspects of the sediment found in the study sites as well as
operational problems encountered with the survey vessel, data interpretation procedures
required significant manual participation in application of the Acoustic Core sediment
identification programs. These unique aspects and problems are summarized as follows:
Acoustic Impedance (Appendix A3.1) - The acoustic impedance of
contaminated sediments is higher than the same non -contaminated sediment.
The impedance of severely contaminated clays is approximately the same as
sand. This means that the material identification with impedance alone (the
standard Acoustic Core AC50/60 program) will not work in contaminated
sediments.
Spatial Variability - In normal marine sediments, the horizontal spatial
variation is usually measured in tens of meters (McGee et al., 1995, Figure
45). However in this riverine site, the contaminated sediment structures
exhibited horizontal spatial variation measured in meters. An entirely new
method to handle computation of bottom loss (impedance) and the signal
properties on a trace-by-trace basis rather than a subfile basis was needed.
Two new Windows-based programs were developed by Caulfield Engineering
to handle these variations. They are the CAL1 (Expanded Calibration Routine,
Appendix A3.5) and the ACRS1 (Acoustic Core Reflection/Sign routine,
Appendix A3.6). The application of these programs to the generation of
cross-sections is covered in this report. Minor problems occurred with the
ship handling during data acquisition. These problems prevented full
integration of navigation data with the seismic files, causing extensive
manual data collation to tie these sets of data together during data reduction.
Also, steering difficulties prevented the survey lines from overlapping
properly, which necessitated further manual review of the data to compare the
results from the different seismic frequencies. Detailed processing corrected
for all ship handling effects on data variability.
Large Variation in Sediment Layer Thickness - In both survey sites, the layer
thickness varied from tenths of meters (O.lm) to several meters (2.0 m). High
frequency pingers were required for the thin layers and a low frequency
boomer was necessary to penetrate the highly sound absorbing
contaminated/gas containing sediment layers. Center sound source
-------
frequencies used were 700 Hz (Boomer), 3500 Hz and 7000 Hz (ORE Finger).
At 7000 Hz, the ping length was longer in time than the acoustic travel time
for the layer thickness of the very thin layers, which prevents these very thin
sediment layers from being easily resolved. In such cases manual layer
identification was required, as outlined in Appendix A3.8. The procedures
used are discussed in this report.
Hard Pan Characteristics - Glacial till type structures became exposed on the
sediment surface when there was no overlying sediment cover. The glacial till
was composed of packed sand and varying size rocks. These rocks caused
seismic scattering and generated diffraction which added to the spatial
variation. These phenomena were identified and separated from the layer
data. At this time automated programs do not exist to handle this case and
manual interpretation is required.
Many of the interpretation techniques used in this work were based on extensions
of standard geophysical procedures used in deep seismic interpretation and integrated
with the Caulfield Engineering material identification algorithms. With much diligence
each problem was identified, addressed, and the results were verified with the calibration
procedure and new Acoustic Core routines.
2.1 Layer Identification Steps
The first step in the generation of the area cross-section plots is to pick the major
layers. As discussed above, there were several problems associated with identification of
these layers. This section delineates the various procedures and phenomena used in
isolating the true layers. These procedures overcame all the major problems. For
discussion purposes, the 7 KHz data were used. The 3.5 KHz and boomer data were
used selectively to confirm deeper layers in high absorptive contaminated areas.
2.1.1 Step 1: Diffractions
Rocks often act as point reflectors and scatter the acoustic energy in all directions.
This is shown by "diffraction tails" which show up in the acoustic records. Figure 1 is
the CAL1 software display of a data set that has strong diffractions. Refer to Appendix
A3.8 for a review of diffraction patterns on seismic cross-sections. Some of these
diffractions have been highlighted in Figure 2. Figure 3 highlights further steeply
dipping coherent energy diffractions in this acoustic record. This coherent "apparent
noise" is due to diffraction tails originating earlier in time. These diffractions are
generated because of the beam width of the seismic source receiver combination coupled
with the forward motion of the boat. These diffractions, if there are many rock scatters,
forms this apparent noise chatter in the seismic cross-section. With many rocks one has
overlapping diffractions patterns that generates a noisy looking record. See Appendix
A3.8 for a discussion of diffraction.
-------
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-------
Figure 4 is the ACRS software "pick" plot display of the same data set. The
"pick" plot displays the layers identified through the use of correlation techniques.
Appendix A3.6.1 discusses the generation of these "pick" plots. The Bottom Losses
(BL), Appendix A3.3, are plotted at the bottom right of the Figure. In the acoustic data, a
strong and isolated diffraction is marked and the corresponding severe bottom loss
variation is highlighted. Notice the extreme variation in bottom loss of 20 db within a
few traces.
The existence of rocks at the surface is indicated by the characteristic parabolic
shape of the diffraction and the correspondingly widely varying bottom losses. Further,
the lower extent of sediment, the upper surface of the hard pan, can be found by noticing
where, in time (time representing depth), the rocks appear.
Figure 5 is the CAL1 software plot of the seismic data nearest where Core 9 hit
rocks. The acoustic data has been highlighted to show some high lighted interpreted
diffractions. Figure 6 is the ACRS software "pick" plot for the same data set which
exhibits the severe bottom loss variation indicative of rocks and hard pan. The non-
highlighted seismic records can be seen in this figure, for comparison.
While the diffractions on the cross-section display in Figure 5 are much weaker
than in Figure 1. they are also more abundant. Interpreting them is more difficult, in part
because they interfere with each other, and the diffraction signal tails are weaker than the
normal incidence bottom signal. However, the basic diffraction shapes, the deep coherent
chatter, and the rapidly varying bottom loss allow identification of the hard pan either on
the surface or below the sediment layer.
2.1.2 Step 2: Amplitude Analysis
The envelope of an acoustic trace can be found by rectifying the trace and
connecting the peaks of the signal. Appendix A3.8 provides a step by step example for
the trace envelope construction. An alternate procedure is talcing the value of each
positive and negative peak and plotting them on both sides of the trace as shown in
Figure 7. The envelope is found by smoothly connecting all the peaks, indicated by a +
on the amplitude plot, from both sides of the trace. See Figure 8. Figures 7 and 8 are
CAL1 software plots of a simple trace where the only significant reflection is the
reflection from the sediment surface (labeled S) and its multiple (labeled M) on Figure 8.
In practice, this is seldom the case. Usually, there is more than one reflection
produced by the bottom and sub-bottom layers. Because the source has a narrow band
width, the wavelets are relatively long and unable to resolve thin layers. With thin layers
there are two significant reflections and the reflections overlap within the acoustical
travel time of the source sound wavelet. See Appendix A3.8 Figure A3.8-5. Even though
the interference effects complicate determining when the second reflection begins, the
layers can be resolved with detailed effort. In future projects it is recommended that
10
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S(s) = 95.16
N[h) = -82.07
Ndi = 0.
D1 =0.
Nw1 = 0.
Nw2 = 0.
Sg1 = 0.
sdS1 = 0.
Sg2 = 0.
sdS2 = 0.
sdSs = 0.
sdNhyd = 0.
BL = 0.
sdBL = 0.
R = 0.
sdR = 0.
Proc No: = 5
CAL display for
production data near
Core 9, which hit rocks
Figure 5
-------
D:\2117\E703\E7030062.DAT
4.98-n,
0
1
-lev-'
ms. 4
00
15.481
5
. V-v,
RER D:\ACOUr~'C\R270EC02.ASC
012345
S(s]=95.16
N(h)= -82.07
N(a)=19.4
SRD=1.5
SG=1.
Sep= 3.5
BTr= 7.
ABL- -5.7809
i sdBL= 4.5458
SNo=0
PF=0
r-0.0
BL
Acoustic core
reflection/sign
(ACRS) display
showlng variable
bottom loss near
Core 9
Figure 6
Vert. Disp=X2
Core 9 (a pprx1ma te)
-------
D:\2117\E703\E7030070.DAT
0
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N(h) = -82.07
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Ndi = 0.
D1 =0.
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D2 = 0.
Nw2 = 0.
Sg1 = 0.
sdS1 = 0.
Sg2 = 0.
sdS2 = 0.
sdSs = 0.
sdNhyd = 0.
BL = 0.
sdBL = 0.
R = 0.
sdR = 0.
CAL plot of simple trace
Peaks plotted on both
sides of trace
-------
D:\2117\^703\E7030070.DAT
ljan.JLiilฃli
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Ndi = 0.
D1 =0.
Nw1 = 0.
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Nw2 = 0.
Sg1 = 0.
sdS1 = 0.
Sg2 = 0.
sdS2 = 0.
sdSs = 0.
sdNhyd = 0.
BL = 0.
sdBL = 0.
R = 0.
sdR = 0.
CAL plot showlng
envelope of s1mp1e
reflectlon
12<48i Disp.Gain=1 Stack No=1 Vert. Disp
Trace No.= 21 ProcNo: =
Figure 8
-------
a higher frequency source (12 kHz or 24 kHz) with shorter wave lengths be used when
thin layers are expected. This will minimize the work required to resolve these thin
layers. It is important to note that the data from cores collected prior to this survey
suggested thicker deeper layers. Based on the pre-survey core analysis, very thin layers
were not anticipated and source wavelets and frequencies were chosen to resolve both
the thin and deep layers but not the very thin layers.
The envelope of a trace with two reflections is shown in Figure 9. The envelope
collapses where they touch because of the interference. The beginning of the second
reflection was taken to be one wavelength (equivalent time) before the first positive
maxima in the second envelope. Appendix A3.8 Figure A3.8-1 illustrates the need for
this correction for the proper wavelet onset (start) time. In cases of more severe tuning,
individual estimates were made by referring to the source wavelet as an aid in
determining peak locations.
For each data file, the beginning of each reflection was determined for the central
trace of three sub-files (remember that each sub-file equals 40 pings) 0, 2, and 4. In
practice, the reflections were picked and marked at the dominant wavelength after the
start of the wavelet. These picks or marks were shifted a constant wavelength distance
up later in the analysis. This shift of one wavelength was required as the pick was at the
maximum and not the weaker start of the wavelet. See Figure 10 and Appendix A3.8.
The diffractions and the bottom loss were also noted. See Figure 11. Usually the
interpretation was made by connecting the beginning of the reflections using the
coherence of the wave fronts as much as possible and while noting the length of the
wavelet. There were four (4) major cycles in each wavelet allowing identification of the
wavelet. In Figure 12, the coherence of the wave fronts in adjacent traces were of little
assistance in determining the upper layer thickness because the surface reflection was
much stronger than the second reflection. The truncation of the upper layer was taken at
the lateral position where the fourth wave front of the wavelet faded out due to
interference effects. The coherence was much more useful in mapping the second layer
because of the similar strength of the second and third reflections. The point of
termination of the second layer was partly determined by the bottom losses which started
to exhibit diffraction style behavior as the observable diffraction hyperbolas approached
the surface. In essence, knowing the shape of the reference wavelet (Figure A3.8-1), both
in number of cycles and envelope shape, one can use this reference and compare it to the
actual seismic trace. Coherence between the reference and the actual trace allowed
selection of the layer travel time. When wavelet overlapping occurs in thin sediments,
wave form distortion also helped in identifying the travel time.
The above discussion demonstrates the need to use higher frequency sound sources in
future surveys to help resolve thin layers. At higher frequencies where the wavelength is
short compared to the layer thickness the trace envelope will look like Figure A3.8-4
allowing easier identification of the thin layers. At higher frequencies the pulse length is
shorter and the travel time (distance) is smaller between the wave front cycles of the pulse
allowing easier definition of thin layers.
16
-------
D:\2117\E703\E7030063.DAT
0 I 1 I 2 | 3
2 -6.0 , Ampl. +6.0
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D2 = 0.
Nw2 = 0.
Sg1 = 0.
sdS1 = 0.
Sg2 = 0.
sdS2 = 0.
sdSs = 0.
sdNhyd = 0.
sdBL = 0.
R = 0.
sdR = 0.
CAL plot demonstrati i
wavelet interference
Dominant wavelength
i s At>
15.481 Djsp
-------
D:\2117\BP01\BP010025.DAT
0 | 1 | 2 | 3
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Nw2 = 0.
Sg1 = 0.
sdS1 = 0.
Sg2 = 0.
sdS2 = 0.
sdSs = 0.
sdNhyd = 0.
BL=0.
sdBL = 0.
R = 0.
sdR = 0.
Trace No.= 21 Proc No: = 5
CAL plot demonstrating
ampl1tude picks and
d1ffract ions
Figure 10
-------
D:\2117\PP01 \BP010025.DAT
0 | 1 | 2 I 3
ns. _L
5.5-1-
RER D:\ACOITTIC\R270EC02.ASC
0 1 2 3 4 5
S(s]=95.16
N(h)= -82.07
N(a)=17.2
SRD=1.5
SG=1.
Sep= 3.5
BTr= 5.
ABL= -5.6709
sdBL= 4.0244
ACRS "Pick plot"
demonstrating variable
bottom loss from
di ffractions
1 I1 .-
^ ;
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nr- t
Vert. Disp=X2
Figure 11
Variable
bottom loss
-------
D:\2117\BP01\BP010025.DAT
5. T
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-
Interpretation
of layers
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N(h] = -82.07
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Ndi = 0.
D1=0.
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D2 = 0.
L^ V
Nw2 = 0.
Sg1 = 0.
sdS1 = 0.
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sdBL = 0.
R = 0.
sdR = 0.
No=1 Vert. Disp=X2 Trace No.= 21 Proc No: = 5
CAL plot Interpretation
usi ng amp!i tude picks ,
coherence and
di ffractions
Figure 12
-------
2.1.3 Step 3: ACRS Plots
Caulfield Engineering's ACRS program generates two kinds of plots (Appendix
A3.6.1 and A3.6.2). The first uses a correlation algorithm to pick three events on each
trace (refer back to Figure 11). Each pick is found versus time and evaluated for phase
inversion, a + 1 indicates that the reflection has experienced no phase inversion and -1
indicates that it has. The plot is a display of the picks in time along with the phase value.
The phase value is shown by either a solid bar (-1) or a hatched bar (+1). See Figure
A3.6-1 in Appendix A3.6. The bottom loss is also calculated and displayed, as already
introduced in the diffractions discussion. The numeric data from this display is saved to
an ASCII computer file. The second plot. Figure 13, displays the full wave rectified trace
envelopes (Figure A3.6-2), in a gray scale display. These two displays are called the
ACRS Pick plot and the ACRS Envelope plot, which will now be described in summary.
The details of both plots are discussed in Appendix A3.6 Both these plots were
interpreted separately to verify the amplitude layer detection interpretation.
2.1.3.1 Step 3.1: ACRS Envelope Plot
The ACRS envelope plot. Figure 13 right hand cross-section, offers assistance in
showing the existence of surface sediment deposits and their lateral termination. When
the surface envelope is very consistent over many traces, this indicates a uniform layering
effect (label U), and indicates a sediment deposit. The left side cross-section of both
displays in Figures 13 and 14 demonstrate that the seismic cross-section is also uniform
for sediment layering. The compacted materials, in contrast, produce an inconsistent
"broken" effect (labeled B). In addition, fluff deposits showed as a weak signal above the
bottom (labeled F).
The envelope plot is limited as the display is biased to a wavelet envelope length.
See Appendix A3.8 for the shape of the envelope wavelet. When the indicated sediment
layer shows as the thickness of the wavelet envelope, it may be quite thin. Also, if the
surface reflection is quite strong, the ACRS Envelope plot will not provide a clear lower
second layer (labeled NCS in Figure 13). If the layer is thicker than a wavelength, it is
displayed, but is a weak signal as is shown in Figure 13 (labeled WL). The manual layer
interpretation results, as described in Appendix A3.8, are highlighted in Figure 14. The
data does not suggest a gradual surface pinch out, but it does show the end of both layers.
Also, the consistency of the upper region is broken when the bottom loss data plot
indicates diffraction behavior, wide bottom loss variation.
2.1.3.2 Step 3.2: ACRS Pick Plot
The ACRS Pick plot picks the top of sediment layers if the layer is thicker than
the wavelet, and it is very effective at picking diffractions (labeled D in Figure 15). In
fact, a diffraction hyperbola that is weak enough to be in doubt in the seismic record, can
often be detected with the picked data by the ACRS Pick plot.
21
-------
D:\2117\BP01\BP010025.DAT
RER D:\ACOUnT
-------
D:\2117\BP01 \BP010025.DAT
RER D:\ACOUf~'*ป>..../ ,/"'-.H ,-'
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Lateral termination
of two layers
1
Broken
envelope
SNtFO
PF-0
S[s)=95.16
N|h)= -82.07
N(a]=17.2
3RD-1.5
SG=1.
Sep11 3.5
BTr= 5.
ABL= -5.6709
sdBL- 4.0244
ACRS "Envelope plot
interpretation
Figure 14
Vert. Disp=X2
-------
D:\2117\$P01 \BP010025.DAT
REF: D:\ACOITTIC\R270EC02.ASC
5. T
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S(s)=95.1G
N[h)= -82.07
N(a]-17.2
SRD=1.5
SG=1.
Sep= 3.5
BTr= 5.
ABL= -5.6709
sdBL= 4.0244
ACRS "Pick plot"
of the same data
as Figures 10 - 14
Figure 15
-------
This ACRS Pick plot has a similar limitation as the ACRS Envelope plot. It cannot pick
within twice the dominant wavelength equivalent distance. This limitation was due
solely to the project time available and was not a theoretical limit. The ACRS Pick plot
is effective in establishing a second deeper layer and following the diffractions to the
surface. Figures 15 and 16 are examples of this case. The upper layer is seen to be
thinning out during subfile 0 (layer labeled "Top of the 2nd...." in Figure 16), but the
display does not follow it afterwards. The diffractions can be followed to the surface on
the right of Figure 16 (labeled SD). The variance in the bottom loss confirms this
observation.
2.1.4 Step 4: Integrating the Three Layer Picking Techniques
Each of the three interpretations is traced onto a grid of the same scale created on
a transparent sheet. At this time, the wavelength correction is made to the amplitude
analysis interpretation to correct for the peak offset (see Appendix A3.8). Figure 17
shows the equivalent distance (time) of one wavelength (lambda sub zero). Figure 18
shows the three integrated interpretations. The solid line is the amplitude analysis and the
cross marks the amplitude picks corrected for the one wavelength effect. The dashed line
is from the ACRS envelope plot, and the dotted line from the ACRS pick plot.
The final layer identification was made by integrating all of three interpretations
and is the result of interpretation by an experienced technician. Step 5 provides the
reference for relating Figure 18 to the final cross-section. Consistency was used to
suggest correctness and small differences were averaged. This plot represents one file of
one line. The process is repeated for all the files on a given survey line in the chosen
survey site. The Bottom Loss was also traced, in its own box, just below the combined
plot as a reference interpretation aid.
2.1.5 Step 5: Survey Line Layer Cross-Section
When the layer identification for all the files for one line was completed, each file
layer interpretation was digitized and placed in an AutoCad drawing to produce the line
layer cross-section. The layer data in Figure 19 plotted between BPO10025 and
BP10026 is an example of a cross-section layer drawing, without the material type being
identified, and developed from the examples given in Figures 11 through 17. The
material type was then processed and inserted. Section 3 of this report summarizes the
steps for material classification.
25
-------
D:\2117\BP01 \BP010025.DAT
5. T
0
1
4
RER D:\ACOUfnC\R270EC02.ASC
012345
ms.
ro
S[s)-95.16
N(h)= -82.07
Top of the 2nd
layer indicated
SG=1.
Sep= 3.5
BTF 5.
Diffraction ABL=-5.6709
sdBL- 4.0244
SD
ACRS "Pick plot1
interpretation
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-------
D:\2117IRP01 \BP010025.DAT
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S(s) = 95.16
N[h) = -82.07
N(a) = 17.2
Ndi = 0.
D1 -0.
Nw1 = 0.
D2-0.
Nw2 = 0.
Sg1 = 0.
sdS1 = 0.
Sg2 = 0.
sdS2 = 0.
sdSs = 0.
sdNhyd = 0.
BL = 0.
sdBL = 0
*VF U Ip-f ka \f
R = 0.
sdR = 0.
CAL plot displaying
adjustment of amplitude
pick times
-------
ro
CO
100
0
FILE:
BPOl 0025
LINE NO.: Black Lagoon 8
FREQUENCY: 7 kHz
t ซ
Amplitude analysis
Envelope
Pick plot
Amplitude Picks
Bottom loss
Display showing
integration of the 3
interpretations and
bottom loss
Figure 18
-------
Data File: BP010023 BP010024 BP010025
Subfile: 01234501234501234
, , A .+ + + + + + + 4
4- 4- 4- -f > 4- > 4- + ^
72.895.67N 72.919.14N 72.945.62N
4.098.773.75E 4.098.782.61E 4.098.782.51E
n
Depth -
(meters)
-5 -
ro
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BP010026
50123
-4- -f 4-4- 4 A
72.965.08N
BP010027
1 5 0
^-4--*-
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72.984.
4.098.789.49E 4.098,796.
i:
Ref. File: BP01
Line no1 08
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BP010028
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rL i 1 i
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4.098.804.59E
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Figure 19
-------
3.0 DATA INTERPRETATION PROCEDURES -
SEDIMENT IDENTIFICATION
The final procedure in the generation of the site cross-sections was identification
of the sediment type (material) and estimation of the selected sediment potential
contamination. A set of data from Elizabeth Park site has been chosen to illustrate the
procedures for sediment identification. As a precursor to these final procedures, the
calibration process was completed (volume 1), and the regional data base was generated
from the core data and simultaneous acoustic survey data (volume 2). These documents
should be reviewed and referred to while reading this section. The final sediment type
selection was determined by the following steps.
3.1 Step 1: Matching the Sediment Layers to the Cores
The sediment layer types were first selected from core information, and the data
base generated in the core analysis (volume 2). The layers determined from acoustic
interpretation nearest the cores were made to have the same sediment type as observed in
these cores. These changes were then extrapolated, by review of the acoustic records, to
the layers in adjacent lines. This approach is the historical interpretation procedure, and
works well when the sediment deposits extend laterally and are of a uniform nature.
However this technique requires many cores.
At the Elizabeth Park site, the number of cores which could be collected were
limited, the sediment deposits were very localized, and exhibited extreme lateral
variations. What would normally have been a reasonable horizontal distance (10 to 20
meters) in a normal delta type sediment was, for this project, too great a distance. Black
Lagoon and Elizabeth Park were both affected by this problem of high spatial variances.
As a result of the high spatial variance at the Elizabeth Park site, a 100 square
meter site, five attempts were made to collect sediment samples and only one core
exhibited a sediment layer. Three piston cores (8, 9 and 10) were collected inside the
actual boundaries of the outer Elizabeth Park survey site. Cores 8 and 9 exhibited only
hardpan in the core nose cone and no sediments layers were found. Core 10 was the only
core which exhibited a sediment layer.
The lack of more detailed core information in Elizabeth Park necessitated the full
application of the new acoustic patented sediment identification procedures first shown in
the Core Analysis Report, (volume 2). At this site the new software was put to the test
30
-------
using fully the bottom loss and sign information from the ACRS software (Appendix
A3.6) to classify the sediments. These same procedures were also used at the Black
Lagoon site. However, at this site more cores were available and the analysis was easier.
3.2 Step 2: Bottom Loss Processing
The bottom loss measurements were full of random fluctuations depending on site
location. This is because the layers were variable both in thickness and lateral extent, and
the acoustic energy was diffracted by rocks at some locations. To make matters more
complex, normal averaging over a subfile (40 traces) or a full data file (240 traces) was
not adequate at these sites to resolve the mixed bottom losses of the various materials
resulting from the spatial variation. This spatial variation was often exhibited by
combinations of two different sediments or, more often, the sediment next to the hard
pan. There were seldom enough similar sequential traces to get a good estimate by using
brute force statistical techniques alone. Occasionally during the collection of data for the
core data base program the boat was correctly anchored and normal statistical processes
worked well for the generation of the data base information.
To solve the problem for these cases of high spatial variation a moving average
filter was generated. This filter allowed derivation of a bottom loss measurement from
each trace weighted by its nearest trace neighbors. The process is also a valid statistical
procedure but more memory and computational intensive. What was new in this analysis
is that every trace received a bottom loss value. The extreme redundancy in this approach
resulted in a smoothed and stable curve ( Figure 20).
The process of obtaining this data was as follows:
Bottom Loss The bottom loss was calculated by Caulfield Engineering's
ACRS (Appendix A3.6) program and the output text file was saved for each
data file.
Line Data These bottom loss ASCII files were grouped together so that there
was one file with all the bottom loss values for each line. A program was
written which reads these values into Matlab for processing. See Program
Listings 1 and 2, Appendix A2.1.
Smoothing Filter - The "smoothing" process, Program Listing 2, averaged the
Bottom Loss value in question with the 20 traces before it, for the desired
trace position in the line, and the 20 traces after it. This average is output as
the smoothed bottom loss value for that position in the line was used in the
calculation. This approach outputs as many averaged bottom loss values as
the number of values in the input data set. At the ends of the line, this
symmetry is broken because of no further data, so from trace 21 to trace 41 in
the last subfile bottom losses for each of these traces are filled with the mean
31
-------
Bottom Losses for: LOS
10
o>
32
"55
CD
.c
"o
o
E
V)
200
400 600 800
Trace Number
Standard Deviation Curve
1000
1200
Smoothed bottom loss
200
400 600 800
Trace Number
1000
1200
Bottom Loss Display
Smoothed bottom losses wi
standard deviation calcul.
by moving average techniq1
32
Figure 20
-------
value of Bottom Loss at trace 21. This number of 41 traces for the smoothing,
found by trial and error, provided the optimum smoothing for these sites.
Note that other sites might require different smoothing functions depending on
the sonar equipment employed and the regional spatial variations. Refer to
Figure 20 to view the display of this process output.
Standard Deviation Analysis - This smoothing was not quite sufficient in itself
for the sediment classification, because the lateral variations were so extreme.
The program also calculated the average standard deviation of the same
bottom loss values. The average standard deviation was useful for
differentiating hardpan from sediment deposits and was not influenced by the
thinness of the bed, a few rocks within the layer, or similar random factors. In
essence the layer "irregularities" were used as additional data points to
augment the sediment classification process. Refer to Figure 20 to view the
bottom loss standard deviation.
An example of the application of these procedures is provided in Figure 21 and
Figure 22. Figure 21 is a draft cross-section and Figure 22 is the bottom loss working
analysis sheet used to provide the deposited sediment identification. The process which
used both sedimental and textural differences for analysis can be summarized for this
example as follows:
The lateral extent of the layer was determined from the cross-section (traces
801 -1050).
This range of the lateral extent was found on the Bottom Loss Graph (Figure
22) and indicated by the bold line on the bottom curve between the two
vertical dark lines.
The standard deviation was studied and its local minimum point found.
The standard deviation curve should have a flat spot here.
The smoothed bottom loss, again on the bottom curve between the two
vertical dark lines in Figure 22, corresponding to this local range of flat
minimum standard deviation values was the best estimate of a deposited
sediment.
This technique allowed the identification of depositional sediment layers though
they were thin and spotty. The severe scattering of the sound from the hard pan allowed
for identification of these layers.
3.3 Step 3: Contamination, Bottom Loss, and Plus Sign
Percentage
The existence of contamination (pollution) and/or gas bubbles may affect the
bottom loss as established in the volume II, section 4.3.2. The summary data from this
report is reproduced in Figure 23 and illustrates the deviation of study site sediment
33
-------
OJ
Data File: E703
Subfile:
-<
71.3
4,098.4
n
U
Depth ~
(meters) -
-5 -
m
Geographical Position -
0007 E703
D 1 2 3 4 5 (
> + + + + + <
79.28N 71.4(
93.47E 4.098.4
r-t^-^'-" '' '. ,..".*' r1
0008 E7030009
51234501 2
^ 4. 4. 4. -4- 4- 4- 4- 4-
34.66N 71.428.89N
97.44E 4.098.508.45E
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Ref. File: E703
Line no: 03
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SBIIEMT
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E7030010
34501 23
71.456.56N
4.098.520.44E
.'- -' -*'.' 1 !*.*
;. 'N.-*'*;-
E7030011 E7030012
4501 23450
**** + + + + +
71.485.48N 71.499.35N
4.098.530.38E 4.098.560.60E
'-..J V
1
LEGEND
BA9C SM. KSOBT10H
FDAH/nifT
OUY
3.TT OAT IB OA1R1 SLT
SLT
SLIT SAW TO SWOT SLT
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1 1
Traces 801-1050 1091-1130
LATERAL DISTANCE SCALf;
CAULFIELD ENGINEERING
ELIZABETH PARK. E703/UNE 3
urn rr. stuii OMC.
HV 1:500 16/1/97
X8 HOt DIG NQ CJOO nL
2117 qE703-3
Cross section showing lateral limits
of sediment layers.
Figure 21
-------
Bottom Losses for: LOS
200
400 600 800
Trace Number
1000
1200
33
w
TJ
0)
.C
4 '
O
o
E.
200
400 600
Trace Dumber
800
1000
t
1200
Average over
limited B.L. range
Bottom loss plot showing
lateral limits of sediments.
Valid range of bottom loss is
subset with small stable S.D.
Figure 22
35
-------
k
o
u
re
u.
c
_o
"3
o
0-
-5
Estimated Pollution Factor Vs. Delta Bottom Loss
1 *1
10
Q
g
4
o
* ป >i -
00 0.
00 5.00 10.00 15.00 20
I + Series'!
.00
Std. Marine - Observed Bottom Loss (db)
(Delta Bottom Loss)
Graph showing effect of pollution
on bottom loss.
Caulfield Engineering
Figure 23
36
-------
bottom loss values from standard marine sediment bottom loss values plotted versus
gross pollution level found in the Trenton Channel USEPA cores. This gross pollution
level is an arbitrary value derived by assuming the USEPA core with the highest quantity
and diversity of foreign elements of chemical, oils, and metals had the highest pollution
level and then scaling down as fewer foreign elements were found in the cores. With the
bottom loss smoothing and standard deviation approach described above, site
depositional sediment areas were determined and located. Noting that these anomalous
sediments in the Detroit River differ from standard marine sediments by varying degrees,
calculated bottom loss magnitude values, in themselves, are not enough to decide the type
of sediment, only differentiation of depositional sediment from hard pan. The variation
of bottom loss within that sediment made it impossible for proper sediment identification
unless additional information was available.
Caulfield Engineering's ACRS program also measured the phase value of each
major reflector in the trace, in terms of+1 or -1, where the values were determined from
doing the cross-correlation of the source wavelet with bottom trace (Appendix A3.6).
The sign shows that the first reflection was reflected normally, as in the non anomalous
case, or with a 180-degree phase inversion as with the anomalous sediment case. The
phase shift occurred because of the gas content of the sediments. These values became
meaningful by using statistics over a number of traces to calculate the plus sign
percentage, the calculation of the percentage of traces which are NOT phase inverted.
The smoothing approach used in the bottom losses calculations was modified slightly to
produce a similar plot of the plus sign percentage and its standard deviation (Figure 24).
See Program Listings 3 and 4, Appendix A2.2, and Figure 24. This example uses the
same range of traces (41) to compute the moving average of the plus sign percentage
along the survey line used to filter the bottom loss measurements. Figure 25 shows the
Plus Sign Percentage output (darken line between traces 800 and 1000) for the surface
layer discussed in the bottom loss computations discussed above.
The Core Analysis Report (volume 2, section 4.3.4) shows the plot of Plus Sign
Percentage versus Change in Bottom Loss and the plot of Pollution Factor versus
Change in Bottom Loss. Figures 26 and 27 reproduce these figures from that report.
Linear Regression was used with these data sets to determine the minimum squared error
relationships to develop functional relationships (equations) for the data in each of these
Figures. These equations were then represented as functions of the Plus Sign Percentage:
DeltaBL = 25.23 - 0.4325 * PSP
PF = 17.7765 -0.2746* PSP
where:
DeltaBL = Change in Bottom Loss of study site sediments
PSP = Plus Sign Percentage
PF = Pollution Factor
37
-------
Values=+l ,-1
200
Plus Percent for: LOS
co
400 600 800
Trace Number
1000
1200
100
J 5Ta n cliff d " "dif 71 Tt t OT(
200
400 600 800
Trace Number
1000
1200
Plus percentage display calculat
from moving average process.
Figure 24
38
-------
-1
Plus Percent for: LOS
200
400 600
Trace Number
800
1000
0
200
400 600
Trace Number
800
Plus
over
t
1000 f 1200
percent averaged
the same range
as BL
Plus percentage plot showing same
restriction in trace number as in
bottom loss determination.
39
Figure 25
-------
Plus Percent vs Change in Bottom Loss
90
! I
80
70
60
c
-------
Pollution Factor vs Change in Bottom Loss
-2
468
Delta Bottom Loss
10 12 14 16
Graph demonstrating relationship
between pollution factor and
change in bottom loss.
41
Figure 27
-------
The Plus Sign Percentage, the Change in Bottom Loss and the Pollution Factor
were then calculated for each layer in each line. The percentage of traces which are not
phase inverted is inversely proportional to the change in bottom loss. The measured
bottom loss was then corrected, by this change in bottom loss to determine an estimate of
the non-anomalous bottom loss (BL)o. Table 1 presents these summarized computations
for the lines at Elizabeth Park, a 100 meter square site. Note that the arithmetic
complement of the plus sign percentage (100 - PSP) is the correct value for PSP used
because of a small sign bug in the ACRS program.
The non-anomalous bottom loss value, bottom loss corrected for changes in study
site bottom loss allows the sediments to be identified, as to type, by comparing it with the
standard marine sediments curve, developed by Hamilton (see Table 2). Table 2 has been
reproduced from Volume 2. These approaches produced layer type determination. These
estimated sediment types matched the independent interpretation in adjacent survey lines.
Also, the estimated sediment types agreed with the cores and seemed reasonable given
the flow and currents of the river.
The calculation of the pollution factor itself was a useful double check, because
some values were outside the established range from 0 to 10. These outliers were reset to
the extreme edge of the range (either 0 or 10) and a correction was made to the calculated
non-pollution bottom loss value based on the slope of the regression curve. Such values
were given an unconfidence level (Unconf) reflecting the amount they exceeded the
range. This was considered when making the sediment type assignment. The
unconfidence level is listed in Table 1 on the far left column headed as Unconf. These
out of range values only arose due to the extremely small data set available for the
generation of the functional relationships between acoustic variables and the core
information.
3.4 Analysis Summary
The results discussed in this report are based on the calibration and core analysis
carried out in Volumes 1 and 2 of the project. Therefore, it is important to note that the
procedures and equations developed are site dependent. As further data is acquired at
additional core sites, the relationships discussed can be improved. The success of the
project was the result of the piston cores and acoustic data being acquired simultaneously
under strict quality assurance programs.
An additional parameter, the absorption as a function of frequency, could not be
used in an analytical manner for the final sediment identification. The difficulty with the
vessel handling prevented production data position overlap at the different source
frequencies. This added information would have provided further confidence in the
sediment type selection.
42
-------
Table 1
Zero Pollution Bottom Loss and Pollution Factor calculations
Queen Elizabeth Park
Line 01
Trace Range
161-200
371-400
415-465
466-500
521-561
635-650
Line 03
Trace Range
181-240
401-440
641-690
761-800
951-1020
1091-1130
1161-1200
Line 05
Trace Range
1-40
121-160
381-561
601-680
871-980
1071-1100
1161-1200
Line 07
Trace Range
1-40
201-240
281-320
541-600
641-680
721-760
801-840
881-960
990-1050
1101-1140
1201-1240
1351-1440
PSP
65
65
65
65
80
55
PSP
40
67
73
60
85
l_ 95
PSP'
35
35
35
35
20
45
PSP'
60
33
27
40
15
c
85 1 15
PSP
65
75
55
22
92
65
57
PSP
85
75
65
50
30
40
65
75
77
93
83
60
PSP'
35
25
I
I
BL
0.00
-5.50
-10.50
-7.50
-5.50
-6.00
BL
-2.50
DeltaBL
10.09
10.09
10.09
10.09
16.58
(BL)o
-10.09
-15.59
-20.59
-17.59
-22.08
5.77[ -11.77
DeltaBL
(BL)o
-0.72| -1-78
-9.00 10.96 -19.96
-10.00| 13.55 -23.55
-5.00J 7.93
-4.00I 18.74
-12.93
-22.74
-0.50 23.07 -23.57
-6.00 18.74 -24.74
BL
-4.50
-4.00
45 -3.00
78 j -4.50
8
35
43
PSP'
15
25
35
50
70
60
35
25
23
7
17
-3.00
-1.50
-7.00
BL
-2.00
-6.00
J_ 1.00
-2.50
-4.50
-1 1 .00
-1 1 .00
-9.00
-4.00
-9.00
-5.00
DeltaBL
10.09
14.42
PF
8.17
8.17
8.17
8.17
12.28
5.42
PF
1.30
8.71
10.36
PF
8.17
8.17
8.17
8.17
10.00
5.42
(BL)o'
-10.09
-15.59
-20.59
-17.59
-16.80
-11.77
PF
1.30
8.71
10.00
6.79I 6.79
13.66
16.40
13.66
I
(BL)o
-14.59
-18.42
5.77 -8.77
-8.51 4.01
21.77 -24.77
10.09
6.63
DeltaBL
18.74
14.42
10.09
3.61
-5.05
-11.59
-13.63
(BL)o
-20.74
-20.42
-9.09
-6.11
0.54
-0.72J -10.28
10.09| -21.09
14.42
15.28
22.20
-23.42
-19.28
-31.20
17.88 -22.88
PF
10.00
10.00
10.00
PF
8.17| 8.17
10.91
5.42
-3.64
15.58
8.17
5.97
PF
13.66
10.91
8.17
4.05
-1.45
1.30
8.17
10.91
11.46
15.85
13.11
40j -8.00I 7.93 -15.93 6.79
10.00
5.42
0.00
10.00
8.17
5.97
PF
10.00
10.00
8.17
4.05
0.00
1.30
8.17
10.00
10.0C
10.0C
10.0C
(BL)o'
-1.78
-19.96
-22.72
-12.93
-14.29
-8.76
-16.29
(BL)o'
-14.59
-16.31
-8.77
-4.42
-11.87
-11.59
-13.63
(BL)o'
-12.29
-18.31
-9.09
-6.11
-2.80
-10.28
-21.09
-21.31
-15.91
-17.67
-15.6S
6.79 -15.9C
Unconf
3
Unconf
1
4
7
4
Unconf
1
i
6
Unconf
L
43
-------
TABLE 1 concluded
Line 09
Trace Range
41-120
361-440
521-660
691-720
721-820
861-920
961-1000
1041-1080
PSP
45
55
50
55
65
57
80
73
1121-1160 80
|
Line 11
Trace Range
201-240
401-480
1081-1120
1241-1280
1521-1560
Line 13
Trace Range
1-40
91-200
211-240
271-400
811-850
901-960
Line 14
Trace Range
PSP
80
75
66
60
70
PSP
95
95
80
75
65
52
PSP
PSP'
55
45
50
45
35
43
20
27
20
PSP1
20
25
34
40
30
PSP'
5
5
BL
-0.50
0.00
-2.50
-6.00
-2.00
-3.50
-6.50
-7.50
-5.50
BL
-3.00
-5.00
-1.00
-2.00
-6.00
BL
1.00
1.00
20| -4.00
25
35
48
PSP'
-1.50
-3.00
-1.50
BL
|
DeltaBL
1.44
5.77
3.61
5.77
10.09
6.63
16.58
13.55
16.58
DeltaBL
16.58
(BL)o
-1.94
-5.77
-6.11
-11.77
-12.09
-10.13
-23.08
-21.05
-22.08
(BL)o
-19.58
14.42| -19.42
10.53
L 7.93
12.26
DeltaBL
23.07
23.07
16.58
14.42
-1 1 .53
-9.93
-18.26
(BL)o
-22.07
-22.07
-20.58
-15.92
10.09| -13.09
4.47
DeltaBL
-5.97
(BL)o
PF
2.67
5.42
4.05
5.42
8.17
5.97
12.28
10.36
12.28
PF
12.28
10.91
8.44
6.79
9.54
PF
16.40
16.40
12.28
10.91
8.17
4.60
PF
The reflections of the data at the beginning of the line were clipped.
601-720
60 1 40) -2.00I 7.93
-9.93
I
PF
2.67
5.42
4.05
5.42
8.17
5.97
10.00
10.00
10.00
PF
10.00
10.00
8.44
6.79
9.54
PF
10.00
10.00
10.00
10.00
8.17
4.60
PF
6.79 6.79
(BL)o'
-1.94
-5.77
-6.11
-11.77
-12.09
-10.13
-17.80
-20.22
-16.80
(BL)o'
-14.30
-17.31
-11.53
-9.93
-18.26
(BL)o'
-7.26
-7.26
-15.30
-13.81
-13.09
-5.97
(BL)o'
-9.93
Unconf
3
1
3
Unconf
3
1
Unconf
7
7
2
1
Unconf
Table 1 Symbols
PSP - Plus Sign Percentage
PSP' - Complement PSP
BL - Bottom Loss (db)
Delta BL - Observed BL minus Normal Sediment (NS) BL
(BL)o - Normal Sediment BL extracted from Observed BL
(BL)o' - Corrected for end points
PF - Pol 1ution Factor
PF' - Pollution Factor corrected for end points
Unconf - Unconfidence factor
-------
TABLE 2
Bottom Loss - Standard Marine Sediments
Material
Density Bottom Impedance
Loss
Sand-Coarse
Sand-Medium
Sand-Fine
Sand-Very Fine
Silty-Sand
Silt
Sand-Silt-Clay
Sandy-Silt
Clayey-Silt
Silty- Clay
Clay
Fluff
2.03
2.01
1.98
1.91
1.83
1.6
1.58
1.56
1.43
1.42
1.26
1.1
7.8
8.3
8.6
9.1
9.9
12
12.1
13.5
15.2
16.1
20.6
23
3734.7
3508.7
3443.3
3254.5
3063.3
2611.1
2493.9
2420.1
2198.9
2157.1
1891.1
1600
Bottom Loss vs. Density
Standard Marine Sediments
y = 0.0022X4 - 0.0464X3 + 0.4045X2 - 0.7418x + 8.2664
R2 = 0.9899
Density (gm/cmA3)
45
-------
4.0 DISCUSSION OF RESULTS
The cross-sections for the Black Lagoon and Elizabeth Park, each a 100 meter
square site, are presented along with a transect running into Elizabeth Park Channel.
Bathymetric and sediment layer thickness contours are provided with estimates of
volumes of depositional sediment which might be dredged. The results are presented for
each major site and then an example is given on the procedures used for the computations
of sediment volumes. The wide variations in spatial distribution are confirmed.
4.1 Cross-Sections for Black Lagoon Site
Plates 1 and 2, Appendix A1, are the ship navigation tracks for the Black Lagoon
Site. Two plates were used to display the survey lines, as the number of survey lines
were too many to place on one plot. Each survey line is identified by a four character
code (BP01) and a line number. In Plate 1, the circle with a cross in the center represents
the location, along each survey line of the zero subfile number of each data file. Plates 3
through 17 are the cross-sections plots of the survey line acoustical data displaying
sediment type and layer identification. Each subfile position is indicated on the top of the
plate by a circle with a cross through it. The navigation location for all zero subfiles is
also given. The 7 KHz data and tracks were used as the prime data source. If core data
was available along a track, two plates are presented. The first plate of the set plots the
cross-section with the core position indicated (see Plate 3), and the second plate shows
the cross-section with the core stratigraphy superimposed on the cross-section (see Plate
4). A comparison of the core stratigraphy superimposed on the acoustical stratigraphy
provides a visual demonstration of the close agreement between acoustical data and
physical core characterization.
The Eastern most survey line on Plate 3 (data file BPO10001-subfile 1) shows
considerable fluff on the seismic record. This was confirmed by the core data. This area
had the most fluff of any site surveyed. Not all of the fluff appeared on the seismic
records. For this fluff to exist there must be a very low current flow. It is suggested that
as the current flows, the shadow of the sandbar causes an interruption in the flow
allowing the sediments to deposit. Further, because of these phenomena, it is
hypothesized that Black Lagoon could be a settling pond for the river flow. All of this
pollution and sediments could not have originated at this site. Small amounts of fluff
were also detected along the center line of this site above the polluted sediments.
In summary, the survey line cross section illustrates a thin sediment layer near the
surface, often less than a meter in thickness, often demonstrating a high degree of spatial
46
-------
variation. Layers of silt, silty sand, sandy silt, sand, clay and foam/fluff at the water
sediment interface were observed. In some locations the hard compacted sediment, hard
pan, is exposed at the surface. The overlay of core stratigraphy on the acoustical
stratigraphy demonstrated close agreement.
Plate 18 is a distribution map of surface depositional sediments by density group
types. Figure 28 is a color printout of this same distribution map. The spatial variations
in sediment type are confirmed showing sediment deposition in various pockets. Fine
grain soft sediment, silt or clay, seem to have been deposited along the shore line. The
heavier sediments, silty-sands are deposited along the Eastern side of the site out toward
the center of the channel in areas of stronger current.
The depth and surface area of potentially dredgeable sediments have been
estimated for Black Lagoon as follows:
Sediment Layer Greater Than Volume of Dredgeable Sediment
1 meter 3070 cubic meters
0.5 meters 5430 cubic meters
4.2 Cross-Sections for Elizabeth Park Site
Several seismic survey lines were run in the Elizabeth Park site using different
frequencies. Plate 19, Appendix Al displays these survey line. Plates 20 through 29
show the survey line cross section plots of acoustically characterized sediment layers.
Again, the 7 kHz data were used as the prime data source with the other frequencies being
used to aid interpretation. Cross sectional plots of survey lines with core data are again
presented in sets with the second plate showing the core stratigraphy as an overlay of the
acoustically developed stratigraphy.
The northern portion of this site contained anomalous depositional sediment of
silty-sands and clay. However this site exhibited less anomalous depositional sediment
than Black Lagoon as measured by the deviation of site sediment bottom loss values from
the standard marine sediment bottom loss values. This is reasonable as the river floor is
more uniform in this area as compared to Black Lagoon indicating the potential for more
uniform sediment erosion by water current and less tendency for pockets of sediment
deposition to form. As in Black Lagoon, thin layers of fluff were again found in the
northeast portion of the site.
In general the east survey lines exhibited large areas of hard compacted sediment
exposed at the sediment surface with some sediment deposition occurring where
depressions in the hard pan provided a protected area for deposition. Such a case is
47
-------
Color map of Black Lagoon sediment classifications
Figure 28
MflHM
LEGEND
M9C SOL DBOrm
nut/nor
CUY/9LTY OAY
CUT (M SUAUV MB
SHY SNB ID SMBV SLT
an MB ON ซJT SMB
SMDONWYSMB
0 10 20m
LATERAL DISTANCE SCALE
CAULFIELD ENGINEERING
LACK LAGOON SEDIMENTS
HV Is"1*1-mnn /MIEii5/j/97
DM ff
-------
exemplified in plate 20 "E7010009" subfile 04 and 05 at the location of core 10.
Movement west towards shore exhibited an increase in the number of sediment pockets
and an increase of depositional sediment surface area. The Elizabeth park site on the
whole exhibited fewer and thinner layers of depositional sediment than Black Lagoon.
Plate 30 is a distribution map of depositional surface sediments. Figure 29 is a
colored version of the same map. The spatial variations are confirmed with depositional
sediments located in various pockets. However, a comparison with the surface map for
Black lagoon shows the increased presence of surface hard pan. Along the southwestern
shore line, the fine grained sediments seem to have been sparsely deposited with most of
the depositional sediments being silts or clays. The heavier sediments, silty-sands are
deposited along the northern and northeastern side of the site. The depositional
sediments are also relatively thin in this site with most of the sediments being trapped in
bottom depressions.
The estimated dredge volumes for Elizabeth Park were as follows:
Sediment Layer Greater Than Volume of Dredgeable Sediment
0.5 meters 210 cubic meters
0.25 meters 530 cubic meters
4.3 Cross-Sections for Elizabeth Park Channel
Several seismic survey lines were run down the center of the Elizabeth Park North
Channel site using different frequencies. The channel is a shallow narrow tributary
entering the Trenton Channel. The shallow water depth and the narrowness of the
channel width allowed only multiple passes over a center line running down the channel.
The boomer, 700 Hz frequency, data were used to obtain the cross-section for the
Channel (Plate 31). The boomer was needed to provide sufficient energy to penetrate the
sediments which exhibited a high degree of sound adsorption possibly due to high
concentrations of contaminants/gas in the sediment areas from file EB030023 to
EB030029 on Plate 31. The intermediate sediment layering in areas away from the cores
is estimated from the low frequency, low resolution data. The navigation map for this
line is shown in Plate 19.
The channel has a very shallow hard pan section at the mouth where the channel
enters into the Trenton Channel. This exposure of hard pan is the result of the erosion by
the higher current velocity. Plate 31 file EB030029 - file EB030031 displays the location
of the hard pan. Moving up the Elisabeth Park channel the effects of the Trenton Channel
current decrease and sediment deposition occurs. Deposits of clay overlying silt which
overlies silty sand represents the primary layering. However, one area of silt exposed at
the surface over lying silty sand was also encountered. This decrease in current velocity
has allowed the fines, contaminated silt and clays, to accumulate in the Channel as shown
49
-------
Color map of Elizabeth Park sediment classifications.
Figure 29
on
O
NORINM
nta
TUSH)
nan
n,m
TUB
7X470
71,410
n4eo
71.440 - -
71.430 - -
71.4M - -
71.4X1 - -
71400 - -
TUB - -
TUB - -
7VJ70 - -
TUB - -
nyo
-\ 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1
! ! ! I IS
I I I 1 i II i I
LEGEND
0 10 20m
LATERAL DISTANCE SCALE
CAULFIELD ENGINEERING
EUZABETH PARK SEDIMENTS
DC
SCAIE
1:1000
20/1/97
-------
in Plate 31. The cores for the site are shown in the adjacent plate, Plate 32. A
comparison of core stratigraphy to acoustically estimated density group stratigraphy once
again demonstrates close agreement.
Depositional sediment volume estimates where made by noting that the available
surveyed Channel length, where sediment deposits occurred, is approximately 18 meters
long. Also, it was assumed that there was a linear change of hard pan depth to each of the
nearby shorelines, which averaged 10 meters on each side of the survey line. The mean
sediment thickness of 2.1 meters occurred along the center of the survey line between
files EB030023 and EB030029. These assumptions yielded a calculated total dredgeable
volume of 378 cubic meters.
4.4 Estimating Sediment Volumes - Black Lagoon
Because this is the first time for the application of the techniques discussed in this
report and combined with the ship handling problems, many of the procedures were
accomplished through semi-manual processing. Using Black Lagoon as an example, the
step by step procedures used and the results are presented in the following subsections.
4.4.1 Step 1: Data Sampling and Contour Plots Generation
The AutoCAD plots were used to construct ASCII (TEXT) files, Figure 30,
containing the position coordinates and the water depth and thickness of sediment in
meters at that position. In Figure 30 "Top" refers to the water depth to the sediment
surface and "Bottom" is the depth from the surface to the bottom of the depositional
sediment layer. A data set for each of the cross-sections in the Black Lagoon site was
constructed following this format. These data sets were then used to create several plots.
A Matlab program, FLAYER3.M, was constructed to generate the contour plots
of the sediment thickness. Appendix A2.3 provides a listing for this program. The data
is first interpolated onto a grid and then plotted as contours. Figure 31 shows the output
plot with all the contours of sediment thickness shown in quarter meter increments. For
ease of plotting computations, the Northing and Easting position coordinates were
adjusted to show only the last 4 digits. To convert to the true Northing scale, add 70,000
meters to the listed Northing, and to convert to the true Easting scale, add 4,090,000
meters to the listed Easting. A five-meter increment was chosen for the interpolated grid
size of the plot. This grid size generated coupled with the mean depositional sediment
thickness hi the grid generated a cube with a given volume. Summing the volumes in
each grid, cube produced the total computed dredgeable volumes. Smaller grid spacing
values produced no significant improvement in resolution; however, larger grid spacing
values degraded the detail.
51
-------
Northing
72863.75
72868.16
72872.56
72879.09
72885.62
72891.48
72897.33
72906.55
72915.77
72927.81
72939.85
72952.83
72965.80
72977.70
72989.60
73001.25
73012.87
73015.44
73018.00
73022.15
73026.31
73029.86
73033.41
73034.68
73035.96
Easting
4098790.87
4098793.02
4098795.17
4098796.34
4098797.51
4098800.42
4098803.33
4098809.52
4098815.71
4098816.77
4098817.83
4098818.42
4098819.00
4098822.01
4098825.02
4098831.25
4098837.49
4098839.58
4098841.67
4098842.44
4098843.21
4098841.72
4098840.24
4098836.85
4098833.45
Top
5.3
4.9
4.6
4.5
4.4
4.3
4.0
3.8
3.5
2.9
1.9
1.1
1.0
1.1
1.6
2.0
2.5
3.0
3.3
3.7
4.0
4.1
4.2
4.2
4.3
Bottom
6.7
6.3
5.9
5.9
5.8
5.6
5.3
5.1
4.8
5.4
2.5
1.1
1.0
1.1
1.6
4.1
4.3
4.5
4.6
4.7
5.0
5.1
5.2
5.3
5.4
List of geographic coordinates and
top & bottom of sediments for line 2
Figure 30
52
-------
3040
3020-
3000
2980 /-/-/-A- + -"
0)2960
2940
2920 K--^3
2900
2880-
Black Lagoon Sediment Contours (in meters)
2860
8700 8720 8740 8760 8780 8800 8820 8840 8860
Easting Contour inverval is 0.25 m
Add 70,000 m to Northing
Add 4,090,000 m to Easting
Contour map of Black Lagoon
sediment thickness.
Contours from 0.00 to2.25 m
53
Figure 31
-------
As an aid in planning dredging activities, the above plot was re-plotted for
sediment thickness contours greater than 1 meter, Figure 32, and for sediment thickness
contours greater than 0.5 meter, Figure 33. These two minimum depths were targeted as
probable practical dredging limits.
Only the contours within the survey boundary have correct values. The
extrapolation techniques produce some data corruption outside of the survey area.
Another Matlab program, FLINES.M (Appendix A2.4), was generated to display the
extent of the survey lines on the same scale as the contours. Figure 34 shows this output.
The extent of the valid contour data is determined by connecting adjacent ends of lines to
enclose the area of the survey as shown in Figure 35. The extent of the valid contours is
displayed by superimposing the outer bound data of Figure 35 onto the contour plots as
shown in Figures 36 and 37.
4.4.2 Step 2: Dealing with Extrapolated Grid Values.
The dredging volume estimates are calculated from the interpolated grid values
saved to disk by Program Listing 5, Appendix A2.3. Figure 38 illustrates a listing of
some of these values, as output by MATLAB, in ASCII format. The information is the
Easting, Northing, and sediment thickness on a regularly spaced grid line. The data set
was reformatted as shown in Figure 39. The data has been changed from exponential
format into fixed decimal for easier reading. More importantly a fourth value is added to
indicate whether the point was inside or outside of the survey area. A value of 1 means
that the position is inside the survey area, whereas a zero indicates an extrapolated data
point. Data was accumulated in these formats for the entire site and then used to compute
the volumes of sediment.
4.4.3 Step 3: Two Volume Estimates for Black Lagoon
Sediment thickness contouring using a depositional sediment thickness criteria of
1 meter or greater identified 3 depositional areas. In Figure 40 these areas are labeled la,
Ib, and 2. Figure 41 shows 7 depositional areas selected using a sediment thickness
contour interval criteria of greater than a 0.5 meter. Volume estimates were calculated
for each of these areas using the Matlab program, Listing 7 (Appendix A2.5). This
program calculates the total volume subject to the following constraints:
A specified range of Northing values.
A specified range of Easting values.
The thickness must be greater than the minimum contour interval criteria
selected.
The program uses the flag encoded information in the input data set to
automatically reject values outside of the survey area. When a given data point satisfies
the criteria, the sediment depth is added to a running total. Finally, when there are no
54
-------
3040
Black Lagoon Thick Sediment Contours (greater than 1 m)
2880
2860
8700 8720 8740 8760 8780 8800 8820 8840 8860
Easting Contour inverval is 0.25 m
Contour map of Black Lagoon.
Sediment depth of 1.0 m or more
55
Figure 32
-------
Black Lagoon Thick Sediment Contours (greater than 0.5 m)
3040
3020
3000
2980 /-/-/-,
0)2960
2940
2920
2900
2880
2860
8700 8720 8740 8760 8780 8800 8820 8840 8860
Easting Contour inverval is 0.25 m
Contour map of Black Lagoon.
Sediment depth of 0.5m or more
56
Figure 33
-------
3040
3020
3000
2980
0)2960
Ic
i
22940h
2920
2900
2880
plot map of lines 02 - 22
2860
8700 8720 ' 8740 8760 8780 8800 8820 8840 8860
Easting
Geographical extent of Black
Lagoon Survey Lines.
57
Figure 34
-------
plot map of lines 02 - 22
3040
3020
3000
2980
c?2960
2940 -
2920
2900
2880
2860
8700 8720 8740 8760 8780. 8800 8820 8840 8860
Easting
Geographical extent of data integrity.
58
Figure 35
-------
3040
3020
Black Lagoon Thick Sediment Contours (greater than 1 m)
2880
2860
8700 8720 8740 8760 8780 8800 8820 8840 8860
Easting Contour inverval is 0.25 m
Geographical extent of valid
contours, 1m and greater.
59
Figure 36
-------
Black Lagoon Thick Sediment Contours (greater than 0.5 m)
3040
3020
3000
2980 /-/-/-,
c?2960
2940
2920 -/---
2900 --
2880
^2860
8700 8720 8740 8760 8780 8800 8820 8840 8860
Easting Contour inverval is 0.25 m
Geographical extent of valid
contours greater than 0.5m.
60
Figure 37
-------
Easting
Northing
Layer Thickness
8.7350000e+003
8.7350000e+003
8.7350000e+003
8.7350000e+003
8.73'50000e+003
8.7350000e+003
8.7350000e+003
8.7350000e+003
8.7350000e+003
8.7350000e+003
8.7350000e+003
8.7400000e+003
8.7400000e+003
8.7400000e+003
2.9900000e+003
2.9950000e+003
3.0000000e+003
3.0050000e+003
3.0100000e+003
3.0150000e-)-003
3.0200000e+003
3.0250000e+003
3.0300000e+003
3.0350000e+003
3.0400000e+003
2.8600000e+003
2.8650000e+003
2.8700000e+003
4.7742731e-001
1.8752866e-001
4.3373187e-001
9.7079171e-001
1.3096406e+000
1.43647696+000
1.36344786+000
9.7386564e-001
9.7317738e-001
1.44570036+000
2.0303591e+000
1.31038926-001
7.3050225e-002
3.3442422e-002
List of MATLAB output.
Thickness interpolated/extrapolated into
a uniform grid.
61
Figure 38
-------
Easting Northing Thickness Inside/Outside Flag
8735.00
8735.00
8735.00
8735.00
8735.00
8735.00
8735.00
8735.00
8735.00
8735.00
8735.00
8740.00
8740.00
8740.00
2990.00
2995.00
3000.00
3005.00
3010.00
3015.00
3020.00
3025.00
3030.00
3035.00
3040.00
2860.00
2865.00
2870.00
0.48
0.19
0.43
0.97
1.31
1.44
1.36
0.97
0.97
1.45
2.03
0.13
0.07
0.03
1
1
1
1
1
1
1
0
0
0
0
0
0
0
Regular grid data in fixed decimal
format with a validity flag.
Valid data is inside the survey.
62
Figure 39
-------
3040
3020
Black Lagoon Thick Sediment Contours (greater than 1 m)
2880
2860
8700 8720 8740 8760 8780 8800 8820 8840 8860
Easting Contour inverval is 0.25 m
Suggested dredging sites based
on 1.0m mini mum depth.
63
Figure 40
-------
Black Lagoon Thick Sediment Contours (greater than 0.5 m)
3040
3020-
3000
2980 /-/-/-.
0)2960
2940
2920 L-/'
2900 --
2880
^2860
8700 8720 8740 8760 8780 8800 8820 8840 8860
Easting Contour inverval is 0.25 m
Suggested dredging sites based on
0.5m mini mum depth.
Figure 41
64
-------
more points to consider, the sum total depth is multiplied by the grid increment in both
the Northing and Easting directions to give the volume estimate. The results are echoed
back to the MATLAB Command window where they were printed as shown in Figure 42.
A safety margin of 10 percent was added and the numbers were then rounded off. This
safety margin was used to compensate for the fact that an interpolation cube consisting of
grid size and sediment thickness might have missed some sediments because of the high
spatial variability in the sediment structures. Figures 43 and 44 show estimated volumes
using, 1 meter and O.Smeter contour criteria, respectively.
For discussions above, the volume estimates were prepared in a semi-manual
manner. With better ship handling in the future and improved navigation interfaces,
much of this semi-manual work can be automated. However, the present manual data
base and procedures will allow calibrations of future automated programs. The correct
automation procedures will depend on the spatial variations expected and knowledge of
the optimum grid size before hand. As shown earlier in this report, the spatial variations
were much greater than expected and prevented the immediate use of off the shelf
software.
Figure 45 illustrates the bathymetry for the Black Lagoon site a product of the
Matlab program. The Matlab program, FWDEP.M (Appendix A2.6), was used to
generate these contours. The bathymetry of the Black Lagoon study site illustrates the
sand bar located in the north east corner which the sediment density group analysis
identified as silty sand over slightly more compacted silty sand and sand. Moving in
toward shore, deeper water and sediment depositional areas are encountered .
4.5 Estimating Sediment Volumes - Elizabeth Park
The Matlab programs developed above for Black Lagoon were only modified for
the different data set names, and then used to generate the estimated sediment volumes
for the Elizabeth Park site. Program Listing 9 is provided in Appendix A2.7 to illustrate
the different data set name changes. No sediment thickness contours greater than 1 meter
were found at the Elizabeth Park site, therefore a minimum contour interval of 0.25 meter
and 0.5 meter were selected. The sediment contour plots for these contour intervals are
shown in Figures 46 and 47. It is expected that dredging a layer of thickness 0.25 meters
is unrealistic. The plot was provided to give a better understanding of the area. The
actual survey line positions, shown in Figure 48, were plotted to determine the site for
contouring boundary.
Figures 49 and 50 shows the contours within the limits of the actual survey data
for both the minimum 0.5 meter and 0.25 meter minimum thickness contouring
respectively. The areas of sediment deposition are highlighted and the volume estimates
calculated. The 0.25 contour criteria, Figure 50, identified a small number of sediment
deposits in the center of the survey site that are not highlighted. These deposits were
identified as sand and not included in the dredging volume computations.
65
-------
ป fvol
northmin.2 =
2890
northmax2 =
2935
eastmin2 =
8710
eastmax2 =
8735
minthick2 =
0.5000
thick2 =
12.5900
vo!3 =
314. 7500 =
Output from program fvol for Area 3 of Black Lagoon
and target thickness of 0.5m. 10% is added and result
is rounded off.
66 Figure 42
-------
3040
Black Lagoon Thick Sediment Contours (greater than 1 m)
2880
2860
8700 8720 8740 8760 8780 8800 8820 8840 8860
Easting Contour inverva! is 0.25 m
Total value = 3070m3
Volume estimates for suggested
dredging sites. (Based on- 1m
target . )
67
Figure 43
-------
Black Lagoon Thick Sediment Contours (greater than 0.5 m)
3040
3020
3000
2980 /-/-/-,
0)2960
2940-
2920 --
2900 --
2880
^2860
8700 8720 8740 8760 8780 8800 8820 8840 8860
Easting Contour inverval is 0.25 m
Total volume = 5430m3
Volume estimates for suggested
dredging sites. (Based on 0.5m
target depth .)
Figure 44
68
-------
3040
3020
3000
2980
0)2960
22940
2920
2900
2880 --
Black Lagoon Water Depth Contour Plot (in meters)
2860
8700 8720 8740 8760 8780 8800 8820 8840 8860
Easting
Black Lagoon Bathymetric Contours.
69
Figure 45
-------
Elizabeth Park Thick Sediment contour plot (over 0.5 m)
1520
1500
1480
1460
en
_c
f 1440
o
1420
1400
1380
1360
O
i i
8
i i
8420 8440 8460 8480 8500 8520 8540 8560 8580
Easting (Contour Interval is 0.1 m)
Contour map of Elizabeth Park.
Sediment depth over 0.5 meters.
70
Figure 46
-------
1520
1500
Elizabeth Park Thick Sediment contour plot (over 0.25 m)
1380
1360
8420 8440 8460 8480 8500 8520 8540 8560 8580
Easting (Contour Interval is 0.1 m)
Contour map of Elizabeth Park.
Sediment depth over 0.25 m.
71
Figure 47
-------
Elizabeth Park Survey Lines 01-14
1520
1500
1380
1360
8420 8440 8460 8480 8500 8520 8540 8560 8580
Easting
Geographical extent of Elizabeth Park survey lines.
72
Figure 48
-------
1520
1380
1360
Elizabeth Park Thick Sediment contour plot (over 0.5 m)
1500 T r-/--X. -*-->
8420 8440 8460 8480 8500 8520 8540 8560
Easting (Contour Interval is 0.1 m)
8580
Total volume = 210m3
Suggested dredging sites with
volume estimate, based on target
.thickness of 0.5m.
73
Figure 49
-------
Elizabeth Park Thick Sediment contour plot (over 0.25 m)
1520
1500
1380-
1360
8420 8440
8460 8480 8500 8520 8540
Easting (Contour Interval is 0.1 m)
8560 8580
Tota1 volume = 530m3
Suggested dredging sites with
volume estimate, based on target
depth of 0.25m .
74
Figure 50
-------
The water depth contours for the Elizabeth Park survey area are displayed in
Figure 51. The bathymetry of this site indicates a relatively uniform decrease in water
depth moving to the southwest.
75
-------
1520
1500
Elizabeth Park Water Depth (in meters)
1380
1360
8420 8440 8460 8480 8500 8520 8540 8560 8580
Easting (Contour Interval is 1 m)
Elizabeth Park Bathymetric Contours.
76
Figure 51
-------
5.0 CONCLUSIONS AND RECOMMENDATIONS
The Acoustic Core0 System is capable of mapping in shallow water where
sediments exhibit a high degree of spatial variation. Existing software was modified and
additional software written to meet the challenge of acoustically mapping sediments in
shallow waters where sediments exhibit spatial variability and contain micro gas bubbles.
In future surveys it is recommended that a higher frequency source be used as an
aid in resolving the thin layers. Also, it is recommended that wider bandwidth sources,
such as chirps or sparkers, be used to better resolve the bottom reflection sign. This will
accelerate the data reduction procedures. The low frequency sound sources employed on
this survey will still have to be used to determine the depth of thicker potentially
contaminated gas containing sediments, as these sediments are extremely absorptive.
At sites where sediment cores were collected, sediment core stratigraphy was
compared to the acoustically estimated density group stratigraphy and generally good
agreement was seen. There was agreement between acoustical data and cores collected
the year before.
The Caulfield Engineering plotting software demonstrated the ability to create
cross section plots of acoustical data expressed as sediment density groups (sand, silt,
clay etc.). The cross section plots provide a tool, usable by managers, for the
visualization of depositional sediment distribution and volume. This type of survey and
mapping provides the reconnaissance tool needed in designing and implementing cost
efficient assessment of contaminated sediments.
Two sites on the Detroit River, Trenton Channel were surveyed during this
demonstration project. Sediment deposits of the Elizabeth Park site were very localized
and exhibited extreme lateral variability. Hard compact sediment is often exposed with
depositional sediment thickness ranging from 0 to about 1 meter with a volume of around
530 m3.
Depositional sediment dominates the surface area of the Black Lagoon site with
some areas of exposed rock and hard compact sediment. Depositional sediment is less
localized and exhibits less spatial variability than the Elizabeth Park site. Depositional
sediment thickness ranged from 0 to about 2.25 meters with a volume of about 3,070 m3.
The project demonstrated the existence of sediment fluff or foam overlaying some
of the surface sediments. This fluff was found both by the piston cores and in the high
77
-------
frequency acoustic records. The role of this fluff in the transport of contaminants and
its' effect on sediment resuspension should be further studied.
The deviation of contaminated sediment acoustical properties from standard
marine sediments may provide a tool for the acoustical identification of contaminated
sediments. With the availability of selected core sites in which the contamination has
been chemically measured and the physical geotechnical soil properties have been
determined, a data base relating the acoustic properties of the sediments to the physical
and chemical sediment properties can be constructed. With additional research this data
base might be used to quantitatively determine the thickness and lateral distribution of the
contaminated sediments. It is critical for the success of such a program that the data be
acquired with a detailed quality assurance program which allows absolute determination
of the source level and the source wavelet shape. Additional research is needed in this
area.
For long term research, it is suggested that a laboratory procedure be assembled to
start measuring the acoustic properties of each type of contaminant when combined in
marine clays. This will enable the construction of more detailed data bases of acoustic
properties versus the types of contaminants.
78
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6.0 BIBLIOGRAPHY
The following documents have been used in the preparation of this report.
Breslau, L.R, 1965, "Classification of Sea-Floor Sediments with a Ship-borne Acoustical
System", Proc. Symp, "Le Petrole et la Mer", Sect. I, No. 132, pp 1-9, Monaco,
1965, (Also: Woods Hole Oceanographic Institute Contrib. No. 1678, 1965).
Caulfield Engineering, 1995, "Micro Survey-Acoustic Core and Physical Core Inter-
relations with Spatial Variation - Trenton Channel of the Detroit River, Field
Activities and Calibration Documentation", Volume I, Caulfield Engineering,
December 30, 1995, Job No. 2060.
Caulfield Engineering, 1996, "Micro Survey-Acoustic Core and Physical Core Inter-
relations with Spatial Variation - Trenton Channel of the Detroit River, Core
Analysis and Summary Findings", Volume II, Caulfield Engineering, March 23,
1996, Job No. 2060.
Caulfield, D. D., 1991, "Digital Field Shallow Seismic Acquisition Systemฎ, Version
DF25 Manual", (computer program and manual, IBM-PC), Caulfield
Engineering, Oyama, BC, Canada.
Caulfield, D. D., and Yim, Y.C., 1983, "Predictions of Shallow Subbottom Sediment
Acoustic Impedance Sediment while Estimating Absorption and Other Losses",
Journal of the Canadian Society of Exploration Geophysicists 19(1), 44-50.
Farara, D.G., and Burt, A.J., 1993, BEAK Consultants Report: Environmental
Assessment of Detroit River Sediments and Benthic Macroinvertebrate
Communities - 1991. Ontario Ministry of the Environment and Energy, London,
Ontario.
Giesy, J.P., Graney, R.L., Newsted, J.L., Rosiu, C.J., Benda, A., Kreis, Jr., R.G. and
Horvath, F.J. 1988, Comparison of Three Sediment Bioassay Methods using
Detroit River Sediments. Environ. Toxicol. Chem. 7:483-498.
Hamilton, E. L., 1970, "Reflection Coefficients and Bottom Losses at Normal Incidence
Computed from Pacific Sediment Properties", Geophysics 35, 995-1004.
Hamilton, E. L., 1980, "Geoacoustic Modeling of the Sea Floor", Journal of the
79
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Acoustical Society of America, 68(5), 1313-1340.
Helstrom, C. W. , 1960, "Statistical Theory of Signal Detection", Pergamon Press, New
York.
Long, E.R. and L.G. Morgan. 1990. The Potential for Biological Effects of Sediment-
sorbed Contaminants Tested in the National Status and Trends Program. NOAA
Tech. Memo. NOS OMA 62. National Oceanic and Atmospheric Administration,
Seattle, Wa. 174pp.
McGee, R. G., Ballard, R. F., and Caulfield, D.D., 1995, "A Technique to Assess the
Characteristics of Bottom and Subbottom Marine Sediments", Technical Report
DRP-95-3, U.S. Army Engineer Waterways Experiment Station, Vicksburg, MS.
Michigan Department of Environmental Quality (MDEQ). 1987. Stage 1 Report:
Remedial Action Plan for Detroit River Area of Concern. Surface Water Quality
Division, Lansing Michigan.
Officer, C. B., 1958, "Introduction to the Theory of Sound Transmission", McGraw-Hill,
New York.
Persaud, D., Jaagumagi, R., and Hayton, A. 1993. Guidelines for the Protection and
Management of Aquatic Sediment Quality in Ontario. Water Resources Branch,
Ontario Ministry of the Environment, Toronto, Ontario.
Urick, R. J., 1983, "Principles of Underwater Sound", 3rd ed., McGraw-Hill, New York.
U.S. Environmental Protection Agency and Environment Canada (USEPA and EC).
1988. Final Report: Upper Great Lakes Connecting Channels Study Volume 2.
December 1988. pp. 447-591.
80
-------
APPENDIX Al
CROSS-SECTION PLATES
All Auto-Cad Drawing Prepared for this Report are
Contained in this Appendix
Al-l
-------
Plate 1
Mtnwc
0 10 20m
LATERAL DISTANCE SCALE
CAULFIELD ENGINEERING
-
DM tf.
BUCK LAGOON
HV
1:1000 j"^7/1/97
0*0ป ' "~ feim'Kr.
BLLAGMAP j
-------
Plate 2
>
I'
CO
73.CHO
UOJO .
ji.ua
71010 -
71000 .
TZ.WO
7ZMO
71170
7ZNO
7J.MO .
71MO -
71*20
Tt,*IO
71100
nan -
ntta
run
TZ.MO
nxe -
H 1 1 1III 1II 1 f-
ง I I I I ง I
i $ I $ I I I
I i
USTMC
H 1 1
0 10 20m
LATERAL DISTANCE SCALE
CAULFIELD ENGINEERING
not
BLACK LAGOON-PART 2
HV
MHO-
2117
SCซlt
1:1000
OAK.
J7/1/97
CMO'St'"
BLLAG-2
-------
Plate 3
Data File:
BP010000
Subfile: 0
Geographical Position
1 2
BP010001
0
BP010002
5 0
72.863.75N
4.098.790.87E
Depth
(meters)-
72.965.80N
4,098,819.00E
73.035.96N
1.098.833.45E
Ref. File: BP01
Line no: 02
LEGEND
NORM.
SDMNT
BASC SOL otsanni
rom/nar
cur
SLIT OAT ID CUttY SLT
sir
art SAW m Mior ai
U - 1.4
U- M
P01EN1W.
POUVID)
sawm
5 10m
LATERAL DISTANCE SCAtฃ
CAULFIELD ENGINEERING
LAGOON. BPQ1/UNE 2
HV
JQSM>
2117
CMDMc
1:500
'15/1/97
CMPIHIT.
DBP01-2-A
-------
Plate 4
Data File:
BP010000
Subfile: 0
Geographical Position
1 2 3
BP010001
0
BP010002
0
72.863.75N
4.098.790.87E
0
72.965.80N
4,098,819.00E
73.035.96N
4.098.833.45E
Depth
(meters)-
-5 -
ป$w$ss-.ซ; %l.i;Ji-*f5>v'V^">vJi
--' "v.i?v<; ^fffay^tfr-i
Ref. File: BP01
Line no: 02
LEGEND
NOMM.
SEDtOfl
B*3C soi oacnmoN
mu/nar
cur
SLIT CUr ID CUWT 9LT
sir
S.TT SMป TO JปWT Sir
ooqrr
- U
IJ - 1.4
IJ- U
POIOflW.
POU/ltD
sonar
5 10m
LATERAL DISTANCE SCALE
CAULFIELD ENGINEERING
BLACK LAGOON. BP01/LINE 2
HV
2117
1:500
"15/1/97
CAtOllC.
bBP01-2-B
-------
Plate 5
I
cr>
Doto File: BP010006 BP010007 BP010008
Subfile: 0123450 1 2 3 4 5 0
72.880.39N 72.933.80N 73.018.45N
4.098.787.82E 4.098.803.27E 4.098.829.19E
n
Depth ~
(meters)
-5 -
10
" v.\WA.VJAWJ kVvVv LUT-r0?
IU
Ref. File: BP01
Line no: 04
SSSS^ilpl^^
^^^^^^^^^ ^.*w^r .4 v-.^.rL. ^JTr^^s^^^
^^T-Tiv^i-.'v1 '/ .''"'' ''* ''"*'*' :'-ซ':'"-'' ';f"- :"?' v:*-:!.-/^'^
LEGEND o 5 10m
.
MMN. 8A9C SOI OBCHPKM KNOT NUUIED i ITTDII nicnurr CVMI r
SBMNT ปi/cc SOMNT LATERAL DISTANCE SCALE
.::.;-: row/hifr ::::::-.
^^ <ป*T 1jฐ-|J ^ง*
^^ surr cut ro CUYEY ai u - 1.4 %ป/'%
^S *' "-" ซ CAULFIELD
"$%%& art SWB ID SWOT ai u - u 5888งง niir-' """' "~*~^
ENGINEERING
WA'-i ปป 'ป-" .15^' BLACK LAGOON, BP01/LINE 4
.: :.. Hซo/toypAci >ซ .v;.,: "ป"ซ .... ซซif
MV
1:500 14/1/97
JOB HO: DK NO CWI) Of-
2117 oBPOI-4
-------
Plate 6
3ป
1
Data File: BP010013 BP010014
Subfile: 012345012
72,877. 75N 72,91 7.86N
4.098.778.64E 4.098, 791. 51E
n
Depth
(meters) -
-5 -
m
^ '*- ^^T^' .*' - <' . ;-ป-rfcz^A
,N
3
4-
BP010015 BP010016
450123450
4. -f 4-4-4-4-4-4-4-
72.964.49N 73.000.60N
4.098.796.99E 4,098,81 4.71 E
-ซ*
iu
Ref File- BP01
Line no: 06
WMAl
sowar
^^
Msjffl
yXJyjy
vte^'J-'
<ฃ
.?.ซ: :^-:} .".''''
LEGEND n 5 inm
BASC SOL KSCKFmM
nmt/nar
CUY
SUY cur n OAYCY SIT
SLT
SUY MM W MWT SLT
SMO
HARD/CflrACT
POIWlut ^>^^^^a
DOSTT POUJU1ED
f./. stMon LATERAL DISTANCE SCALE
1.0 - U ^^
U - 1.4 %^% |
ซ- M CAULFIELD ENGINEERING
u - 14 5ปSป nnr-
u -u ;^<^v BLACK LAGOON, BP01/LINE 6
. ,, ... am tr. suit Mil'
'" > .-.< U\l l.cnn ic /< Ini
i ' 1. OWU l-J/ \ / 3 (
M titi VKttt CAM HE
2117 pBPOI-6
-------
Plate 7
Geographical Position ^-
Data File: BP010023 BP010024 BP010025 BP010026 BP010027 BP010028
Subfile: 01234501 23450123450123450123450
72.895.67N
4.098.773.75E
72.919.14N
4.098.782.61E
72.945.62N 72.965.08N 72.984.82N 73.005.66N
4,098,782.51E 4.098.789.49E 4,098,796.07E 4.098.804.59E
Depth
(meters)
i
oo
-5 -
Ref. File: BP01
Line no: 08
LEGEND
MMN.
SEMINT
U9C SOI OBCXnON
na/nar
cua
art cur m cuirr SLT
airv sow n> turn sit
HWD/ttWACT
KN91Y
fi/x
ramiw.
raiUID
SOWHT
0 5 10m
LATERAL DISTANCE SCAtฃ
CAULFIELD ENGINEERING
MWBY
BLACK LAGOON. BP01/LINE 8
HV
x*w>
2117
owm
1:500
tssr
10/1/97
atuni.-
pBPOI-8
-------
Plate 8
Geographical
->
Data File: BP010036 BP010037 BP010038 BP010039 BP010040 BP010041 BP010042
Subfile: 01 234501 23450123450123450123450123450
Depth
(meters)
vo
72.887.30N
4.098.759.54E
72.907.08N
4.098.769.02E
72.930.54N 72.950.97N 72.967.55N 72.984.78N 73.002.43N
4.098.768.86E 4.098.771.72E 4.098.778.09E 4.098.784.51E 4.098.793.36E
0
-5 -
-10
LEGEND
Ref. File: BP01
Line no: 10
Fฐ**/mfF
sirr OAT w OATtr SIT
SLTYSUWWWeYSLT
HMD/COrACT
totan
1.4 - U
'ป-'ป
poraiui
fauna*
0 5 10m
LATERAL DISTANCE SCMf
CAULFIELD ENGINEERING
mil- ~~~
BLACK LAGOON. BP01/LINE 10
HV
>
2117
SOIL-
1:500
BAIL-
L5/l/?7_
cwofit"
pBPOMO
-------
Plate 9
Geogrophlcol Position
Data File: BP010050 BP010051 BP010052 BP010053 BP010054 BP010055 BP010056
Subfile: 0123450123450123450123450123450123450
Depth
(meters)
3=-1
t'
I
5.
72.898.74N 72.916.89N 72.935.18N 72.951.50N 72.968.75N 72.9B2.87N 73.003.33N
4.098.754.02E 4.098.759.15E 4.098.760.27E 4.098.766.05E 4.098.766.95E 4.098.778.69E 4.098.783.60E
0
-5 -
-^ฃB2ฃ
Jt-lV
li*
Ref. File: BP01
Line no: 12
LEGEND
MRVAl
SHOT
BASK SOL DCCRPIKW
RMH/IUfF
OAT
SLIT OAT n OArtT SIT
SLT
9LIY SMI) ID SMUT 9LT
SMO
HMD/toaMCT
1.0 - IJ
IJ - 1.4
P01DIIIAL
NUUTED
SHOT
0 5 10m
LAHRAL DISTANCE SCALf
|_CAI^nELD_EM!NEERiN_G..
feLACK LAGOON. BP01/LINE 12
wTf
HV
2117
XHL
1:500
BMC
15/1/97
U0> l
pBPOt-12
-------
Plate 10
Geographical Position
Data File: BP010065 BP010066 BP010067 BP010068 BP010069 BP010070 BP010071
Subfile: 01 234501 234501 23450123450123450123450
Depth
(meters)
72.897.59N
4.098.742.99E
0
-10
72.919.78N
4.098.747.08E
72.941.95N
4.098.753.07E
72.963.97N
4.098.758.67E
72.983.87N
4.098.764.28E
73.002.70N
4.098.774.91E
73.020.25N
4,098.781.99E
Ref. File: BP01
Line no: 14
NORM.
SBMNT
LEGEND
sac soi otswFuon
S1TY OAY TO OAYtT SIT
art s*ป ID swcr ai
KH3TT
POTOIIUL
PCUU1OI
SEM4KI
1.0 - IJ
t.ซ - IJ
1J-1I
0 5 10m
LATERAL DISTANCE SCALE
CAULFIELD ENGINEERING
BLACK LAGOON, BP01/LINE 14
OAlE"
HV
2117
1:500
15/1/97
CMOFU:
pBPOI-14
-------
Plate 11
Geographical Position
Data File: BP010078 BP010079 BP010080 BP010081 BP010082 BP010083 BP010084 BP010085
Subfile: 01234501234501 234501 23450000000123450123450
Depth
(meters)
72.894.10N 72.909.2BN
4.098.730.35E 4.098.733.31E
72.927.76N 72.946.25N
4,098,739.95E 4.098.747.22E
72.966.65N 72.983.29N 72.999.65N 73.014.80N
4.098.750.29E 4.098.757.00E 4.098.759.77E 4.098.768.21E
Ref. File: BP01
Line no: 16
NonuL
SHOT
LEGEND
vac soi OCSCHPTOI
nm/nar
MTT cur ro cutn ai
*T
siir ซ> TO swr a?
HMO/UXPACT
oanrr
im/ec
- IJ
P01ENML
XDKMT
0 5 10m
LATERAL DISTANCE SCALE
CAULFIELD ENGINEERING
5j.ACK_LAGOON. BP01/LINE. 16
WefT"""
HV
2117
*"* r.500 1^16/1/97
cworu.-
DBP01-J6A
-------
Plate 12
Geographical Position
Data File: BP010078 BP010079 BP010080 BP010081 BP010082 BP010083 BP010084 BP010085
Subfile: 01234501234501 234501 23450000000123450123450
Depth
(meters)
CO
72.894.10N 72.909.28N
4.098.730.35E 4.098.733.31E
72.927.76N
4.098.739.95E
72.946.25N
4.098.747.22E
72.966.65N 72.983.29N 72.999.65N 73,014.80N
4,098,750.29E 4.098.757.00E 4.098.759.77E 4.098.768.21E
Ref. File: BP01
Line no: 16
WMUL
SMCNI
LEGEND
M9C SDL OtSOPIW
cur
ปIY OAT ID OA1CY 3.1
91TT SAW TO SNOT 9.T
CW3IT
fn/te
1.0-M
1J - 1.4
U-IJ
>u
raiDnui
pouuini
SOMNT
0 5 10m
LATERAL DISTANCE SCAlฃ
CAULFIELD ENGINEERING
LAGOON. BP01/LINC 16
HV
2117
SCAlt
1:500
PAlt
16/1/97
CMBFIL
PBP01-16B
-------
Plate 13
Geographlcd Position >
Data File: BP010094 BP010095 BP010096 BP010097 BP010098 BP010099 BP010100
Subfile: 01234501 234501234501 234501 23450123450
Depth
(meters)
72.897.36N 72,913.00N
4.098.719.31E 4.098.726.00E
72.932.39N 72.952.02N 72.972.09N
4.098.732.52E 4.098.737.50E 4.098.742.20E
72.993.15N 72.008.81N
4,098,747.11E 4.098.752.62E
Ref. File: BP01
Line no: 18
.
SOMHI
LEGEND
BASK SOL KSOWiai
arr CUT TO OAKY at
S1TT tMO ID SWOT O.T
OCN9TY
ปn/ec
1.0 - I.J
pomnw.
POU1IID)
SOWNT
0 5 10m
LATERAL DISTANCE SCALE
CAULEIELD ENGINEERING
""'BLACK LAGOON, BPOI/UNE is
HV
2)17
1.-500
16/1/97
cfSnlS
PBP01-18A ,
-------
Plate 14
Geographical Position
Data File: BP010094 BP010095 BP010096 BP010097 BP010098 BP010099 BP010100
Subfile: 01234501 234501234501 23450 1 23450123450
Depth
(meters)
72.897.36N 72.913.00N 72.932.39N 72.952.02N 72.972.09N
4.098.719.31E 4.098.726.00E 4.098.732.52E 4.098.737.50E 4.098.742.20E
72.993.15N 72.008.81N
4.098J47.11E 4.098.752.62E
Ref. File: BP01
Line no: 18
LEGEND
NOUN.
9MCMT
BA9C SOL OCStnPKM
rota/nun
OAT
sin OAT ID OJUEY ai
SIT
an uw n MM>Y JIT
SMB
HAป/DOP*CI
POTDfWl
FOLD IB
SCDKNT
tJ- M
>U
0 5 10m
LATERAL DISTANCE SCALE
CAULFIELD ENGINEERING
"JLACK LAGOON. BPQ1/LINB: 18
HV
k
2117
sow.
1:500
OIC NO
_J6/1/97
cซto'nฃ " ~
PBP01-18B
-------
Plate 15
Geographical Position
Data File: BP010108 BP010109 BP010110 BP010111 BP010112 BP010113 BP010114
Subfile: 01234501 234501 234501 23450123450123450
Depth
(meters)
i
t-
o
72.897.04N 72.916.20N 72.940.74N 72.963.55N 72.987.12N 73.006.70N 73.026.01N
4.098.711.92E 4.098.716.55E 4.098.722.84E 4.098.731.33E 4.098.736.28E 4.098.743.45E 4.098.754.81E
LEGEND
Ref. File: BP01
Line no: 20
Nonui
snuoi
BASK sat ocsamoH
raui/tuFF
SUV CUT TO OAYPf SIT
SM
SITT SW 10 SWOT SIT
s*"ฐ
mem
<ซ-ซ
M - u
porniui.
POUUTED
SEDtor
v>j;C^
0 5 10m
LATERAL DISTANCE SCALฃ
CAUL-FIELD ENGINEERING
""BLACK LAGOON. BPOI/LINE 20
HV
xen
2117
OWHO:
1:500
16/1/97
auป ntt
pBPOI-20
-------
Plate 16
Geographical Position
Data File:
Subfile:
Depth
(meters)
BP010122 BP010123 BP010124 BP010125 BP010126
01234501234501234501 2345
1234501234501234
+ + + + + + + + + + + * + + + +
72.910.57N
4.098.704.34E
72.934.52N
4.098.714.92E
72.959.40N
4.098.719.10E
72.981.22N
4.098.726.95E
73.012.09N
4.098.732.81E
BP010127
50
73.033.1 6N
4.098.748.89E
Ref. File: BP01
Line no: 22
NOMAL
sonar
LEGEND
vac soi OBOFW*
mm/run
OAT
3LTI 0-ปT 10 0>ซY ปI
SIT
an SAW TO SWOT SIT
DOOTT
jm/ce
nnonw.
PCUUTO
SEDMNT
1.0 - U
t.J - 1.4
1.4 - U
U- U
>M
0 5 10m
LATERAL DISTANCE SCAtฃ
CAULRELD ENGINEERING
ILACK LAGOON. BPOI/UNE 22 ^__
:16/1/97
HV
JOB NO
2117
SCAlt
1:500
CACOflL
PBP01-22A
-------
Plate 17
Geogrophicol Position ^-
Data File: BP010122 BP010123 BP010124 BP010125 BP010126
Subfile: 0123450123450123450 1 2 3 4 5 Q 1 2
Depth
(meters)
I
t'
oo
72.910.57N
4.098.704.34E
72.934.52N
4.098.714.92E
72.959.40N
4.098.719.10E
72.981.22N
4,098,726.95E
73.012.09N
4.098.732.81E
BP010127
450
+ + +
73.033.16N
4.098.748.89E
Ref. File: BP01
Line no: 22
LEGEND
NCRHII
Wtf.
iH
BA3C Sd KSOPIOI
ait OAT TO CLAYEY 9LT
9LT
Sin SAW) ID SNOV 9LT
OW3TY
jm/ce
1.0 - IJ
IJ - 1.4
1.4 - IJ
1.1 - U
IJ-U
raronw.
POUUHD
StMOT
0 5 10m
LATERAL DISTANCE SCALE
CAULFIELD ENGINEERING
"llACK LAGOON._BP_qiAINEJ2 _
!16/1/97
HV
2117
oปc ซo-
1:500
'(Src
PBP01-22B
-------
Plate 18
NOR1HMC
vsm
LEGEND
0 10 20m
LATERAL DISTANCE SCALE
CAULFIELD ENGINEERING
BLACK LAGOON SEDIMENTS
HV
2117
1:1000
15/1/97
two nฃ
color-map
-------
Plate 19
no
o
0 10 20m
LATERAL DISTANCE SCALE
CAULFIELD ENGINEERING
mut
Elizobeth Park
HMIT
HV
2117
1:1000
17/1/97
CMป Flฃ
Elizomop
-------
Plate 20
3=-
i"
ro
H- >
Data File: E7010007 E7010008
Subfile: 01 234501
+ + + +
71.377.77N 71.422.79N
4.098.508.94E 4,098,51 4.86E
n
Depth ~
(meters)
-5
in
" '' ''-"" '
'' ^TV-
IU
Ref. File: E701
Line no: 01
2
v :.
Ncnui.
.*.*..*.'.*.
fyfyfy
Ww
%%%%%'
tf&m.
v'ttVi^
k- ' .* '.
3 4
* - '*.' * .' ** '**>**
LEGEND
BA9C SO. tCSOtCKM
RWlAUlfF
OAT
SLTT OAT TD OMtV SLT
SLT
3LTY SMO TO SNOT O.T
SAND
HMOAnfACT
E7010009 E7010010
5 01 23450
71.467.93N 71 .505.21 N
4.098.531.80E 4.098.558.52E
^
CORE 10
4-
.:^--^-:;??S?^
0 5 10m
1 PBBM 1
F
KNSTT i
fm/ec 1
1JJ - U ^
U - M *
1.4 - U i
U - t J v
U-U ,
>u
VEN1W.
'GUiTTD)
EDMXT LATERAL DISTANCE SCALE
;X;>>X
^J^^-
M CAULFIEL
^^^ "rfrifi"
3 ENGINEERING
^^ ELIZABETH PARK. E701/UNE 1
C* ?- ow ปr sc
HV
ซฃ BATE
1:500 16/1/97
JM MO OK HQ OttO Fit
2117 qE701-1A
-------
Plate 21
Geographical Position
Data File: E7010007
Subfile: 01
E7010008
34501
E7010009
501
E7010010
50
Depth
(meters)
71.377.77N
4.098.508.94E
71.422.79N
4.098.514.86E
71.467.93N
4.098.531.80E
71 .505.21 N
4.098.558.52E
i
ro
Ref. File: E701
Line no: 01
LEGEND
NORMAL
SEMEHT
*.".".*.*.*.".
fy/fa
$/W
y%%%%
wjsfft.
v?K&'j
- ' ' .
tASC SO. HSOSTtt
nuu/nifr
CLAY
SLTY OAT ro OAirr SIT
SLT
SLTT SAM) TO SAMTT SIT
SAM)
HAB>/ttaPACT
DOOTY
f"/ซ
|Jซ- U
U - 1.4
U- U
U- U
U- U
>u
rOIXTML
poui/ta
snen
:::x:::::::
^&
^%
i^^^^
riC*>ป;
t'- . ;
0 5 10m
LATERAL DISTANCE SCALฃ
CAULFIE
"""ELIZABETH
"""' HV
JMMO
2117
LD ENGINEERING
PARK. E701/LJNE 1
JCAiฃ
1:500
mCNQ
^16/1/97
CADDFU:
^gE701-1B
-------
Plate 22
I"
1
ro
GO
Geographical Position -
^~
Data File: E7030007 E7030008 E7030009
Subfile: 01234501 23450
.b.,$..4-44 + + + + "f~f + 4'
1 2
4 4
71.379.28N 71.404.66N 71.428.89N
4.098.493.47E 4,098.497. 44E 4.098.508.45E
n
Depth ~
(meters)
-5 -
]4^2^7:'-^v7>'s~5?r=*
;.-. :< '? V :,v. >>
.. . '.'^K^;.
' ' ' r* '-!- ' .^S^
-.' '^PTT
".
Ref. File: E703
Line no: 03
.'* -7^"
* ' V' 4 '
seaan
y$fy
$<$
%%M/tfa
7JX#$
VrjX ^r:
k- ;- .' '.
E7030010
34501
44-4-44-
71.456.56N
4.098.520.44E
":.-", T^CSS7^
,:--.::-;.,v
2 3
f 4-
E7030011 E7030012
4501 23450
* * * * + 4- 4
* + 4-
71.485.48N 71.499.35N
4.098.530.38E 4.098.560.60E
. - ' ' '
LEGEND
IA9C SOL DESXPTIM
FOAU/furr
OAT
StTt OAT ID OA1EY SLT
SIT
SLIT SAM) ID SHOI SLT
SAND
HARD/COWACT
ooamr
ปป/cc
IJJ-U
U - 1.4
U- U
U - 1.1
U - U
>2J
. ^
PCKX1W.
POUU1ED
SOWNT
NS^
^^^^
i^Pra
--^*-^n.
i .'"''
Ssugjwpj
-*-'* *ฑ.\ '
^sf^g^g^"--' -.Vf^1-..-" <"-.-' ;
f4; .''*" '
0 5 10m
LATERAL DISTANCf SCA1F
CAULFIELD ENGINEERING
mL
ELIZABETH PARK. E703/UNE 3
an tr SCAII: oiit
HV 1:500 16/1/97
JOB MQ me Ha CADD ru.
2117 qE703-3
-------
Plate 23
Geographical Position
Data File: E7030020 E7030021 E7030022 E7030023 E7030024 E7030025
Subfile: 01 234501234501 234501 234501 23450
71.399.70N
4.098.482.63E
Depth
(meters)
>
I
ro
71.417.82N 71.435.47N 71.451.79N 71.470.75N 71.486.80N
4,098, 489.67E 4.098.49Z93E 4.098.50101E 4.098.508.89E 4,098,521.68E
Ref. File: E703
Line no: 05
NORMAL
SEUCNT
LEGEND
ASC S*. ttSOFWH
mm/nor
aปr
SLIT OAT IV OAIEY SLT
SLTY VM> ID satn a.r
SUB
HADOA'X'ACT
COI91Y
KTDHW.
PGUinED
SEDMENT
0 5 10m
LATERAL DISTANCE SCALE
CAULFIELD ENGINEERING
"luZABETH PARK. E703/LJNE 5
HV
2117
1:500
OAJC
16/1/97
CMB nt
-------
Plate 24
Geogrophicol Position
Data File: E7030033 E7030034 E7030035 E7030036 E7030037 E7030038 E7030039
Subfile: 0 1 2 3 4 50123450123450123450123450123450
71.388.12N
4.098.469.25E
0
Depth
(meters)
71.409.66N 71.424.74N 71.440.41N 71.457.12N 71.473.97N 71.489.88N
4,098,479.63E 4,098.486.71E 4.098.491.53E 4.098.498.53E 4.098.504.38E 4.09B.51Z23E
Ref. File: E703
Line no: 07
LEGEND
sncxr
M9C SOL K5OP1OI
SITT O*T TO OJHEY SLT
SLTT SMC TO MOT SU
sue
HWO/COPACT
HM9TT
fn/ec
i J - 1.4
u-ii
>U
muna>
SBUENT
0 5 10m
LATERAL DISTANCE SCALE
CAULFIELD ENGINEERING
""ELIZABETH PARK. E703/UNE 7
HV
2117
SCAU
1:500
nc ซ
wit
16/1/97
cซo at
oE703-7
-------
Plate 25
Geogrophicd Position
Data File: E7030046 E7030047 E7030048 E7030049 E7030050 E7030051
Subfile: 01234501234501234501 234501 23450
. *- + "*" "*""*'"*""*''*"'*''*'-*--*--f-*-^i.
Depth
(meters)
i
ro
CD
71.378.68N
4.098.464.00E
0
-5 -
-10
71.400.63N
4.098.462.44E
71.423.01N
4,098.471.44E
71.447.33N
4.098.480.72E
71.470.84N
4.098.491.45E
71.494.91 N
4.098.504.24E
Ref. File: E703
Line no: 09
LEGEND
SDMKT
FDMi/nirr
OAT
a.n OAT TO OAIET a.i
SIT
SLTT SMB TO SWOT SB.T
tun/GnpACT
Doarr
fl/K
KKXTM.
0 5 10m
LATERAL DISTANCE SCALฃ
CAULFIELD ENGINEERING
""EUZABETH PARK.E703/UNE 9
aw re
HV
2117
1:500
16/1/97
cun nc
QF70.3-Q
-------
Plate 26
Geographical Position
Data Eile: E7030057 E7030058 E7030059 E7030060
Subfile: 0 1 2 3 4 5 0123450123450
Depth
(meters)
i
ro
^j
E7030061 E7030062 E7030063 E7030064
0123450123450 1 2 3 4 5 0
+ + + + +
71.358.64N
4.098.453.34E
0
71.3fi9.70N 71.409.14N 71.431.20N
4.098.451.63E 4.098.459.89E 4.098.465.25E
71.451.27N 71.468.02N 71,4fl1.59N
4.098.474.09E 4.098.480.85E 4.098.487.16E
-5
71.509.65N
4.098.492.64E
-10
Ref. File: E703
Line no: 11
&=ฃ
LEGEND
FOMI/FUIT
OAT
SLTT OAT TO OArtY SIT
StT
SUIT SMQ TO SAHDT SLT
SAป
HASD/tWACT
DOHTY
POltMlW.
HUUTtD
SEDMKI
0 5 10m
LATERAL DISTANCE SCAiฃ
CAULFIELD ENGINEERING
nxt
ELIZABETH PARK
W It
HV
k
2H7
1:500
tult
OK Mt
17/1/97
CADDFU:
QE7Q3-11A
-------
Plate 27
Geographical Position
Data File: E7030057
Subfile: 0 1
Depth
(meters)
71.358.64N
4.098.453.34E
i
ro
CD
E7030058 E7030059
3 4 5 012345012
x + -f + + + + + + + + +
71.3B9.70N
4,098. 451.63E
71.409.14N
4.098. 459.89E
E7030060
3450
71.431.20N
4,098,465.25E
E7030061 E7030062 E7030063 E7030064
0123450123450 1 2 3 4 5 0
+ + + + + + + +++++++ + + + + + "*"
71.451.27N 71.468.02N 71.481.59N
4,098.474.09E 4.098.480.85E 4.098,487.16E
71.509.65N
4.098.49Z64E
-10
Ref. File: E703
Line no: 11
Nonut.
snen
LEGEND
BASC SOLtBCSPHCN
SLTT QAT TO OA1E1 a.T
sirr SAW TO swot SLT
suo
HWD/tXIPtCT
ooom
fn/ec
racnw.
poumD
anon
IJ) - IJ
u - 1.4
0 5 10m
LAMALDISTANCE SCALE
ฃAULFIELD ENGINEERING
"EUZABETH PARK. E703/UNE 11
HV
2117
1:500
17/1/97
CADOflt
OE703-11B
-------
Geogrophicol Position
Plate 28
Doto File: E7030070 E7030071 E7030072 E7030073 E7030074
Subfile: 0 1 2 3 4 5 0123450123450123450
Depth
(meters)
ro
UD
71.362.56N
4,098,438.63E
71.400.06N
4,098,447.11E
71.427.95N
4.098.451.54E
71.455.34N 71.473.59N
4.098.463.78E 4,098,477.59E
Ref. File: E703
Line no: 13
LEGEND
MOMUL
SEMEHT
8A3C Sd DESOPTXX
air OAT TO OAirr sii
SLT
art wo TO SWOT SLT
SAND
HAfD/tOPACT
poionw.
POUimB
staen
0 5 10m
UTCRAL DISTANCE SCALf
CAULFIELD ENGINEERING
TlJZABETti PARK. E703/UNE 13
HV
i
2117
1:500
cuit
17/1/97
CMDFlt
QE703-13
-------
Plate 29
Geogrophico! Position
Dato File: 1/030080 E7030081
Subfile: 01 234501
E7030082 E7030083
2 3 4 5 0123450
Depth
(meters)
GO
o
71.385.5IN
4,098,431.37E
71.419.93N
4,098,440.49E
71.453.42N 71.467.40N
4.098.455.73E 4.098,473.14E
LEGEND
Ref. File: E703
Line no: 14
NOMAL
ZEMXI
MSC SOL tESaPHW
FDAu/furr
OAT
SLTT CUT TO CLAYEY SIT
SLTT MO ID SWOT SLT
HN9TT
fn/ct
POTDdlAL
PCU1/1CD
SHUNT
0 5 10m
LAMAL DISTANCE SCALE
AULFIELD ENGINEERING
PARK.E703/UNE 14
cm rr.
HV
2117
1:500
17/1/97
-------
Plate 30
>
('
CO
71.510 - -
71,500 - -
71.4B - -
71.470 --
71.490 - -
71.450 --
71.440 - -
7I.4JO - -
71.4M - -
71.4)0 - -
71.400 - -
7IJK - -
71JBO - -
7IJ70 - -
7UW - -
7IJBO - -
7U40 -
LEGEND
10 20m
LATERAL DISTANCE SCALฃ
H 1 1 1 1 1 1 1 1 h
H 1 1 1
\\l\\\\\\\
i i
OHM
CAULFIELD ENGINEERING
Wlf
ELIZABETH PARK SEDIMENTS
own
DC
tarn.
2117
SCMfc
1:1000
NG NOt
MIL , ,
20/1/97
ELIZCOLM
-------
Plate 31
Data File:
Subfile:
Depth
(meters)
I
CO
ro
Geographical Position
EBOJ0024 EBOJ0025 EB030026
000
71.407.77H 71.408.62H 71.412.89N 71.415.78N 71.419.39N 71.4Z153N 71,427.831 71.4M.68N 71.427.20N 71.415.24N
4.M8.J40176E 4.098J52.40E 4.098.362-I7E 4.098J7127E 4.098.38St16E 4.098,3N-5Z 4.098.4I5.IOE 4.098,4JI.976E 4,098,450.55E 4,098,463.J4E
-10
Ref. File: EB03
BOOMER LINE
NOTE:
LOW FREQUENCY BOOMER DATA
SEDIMENT LAYERS INTERPRETTED
FROM CORES
LEGEND
NORUAI.
samoa
BA3C SOUSSCRPIKN
FDMl/fUfF
OAT
O.1Y OAT ID OA1TY 9.T
a.TT SMO 10 SMCT 9.T
UM1
HMD/COUPACT
WIDflUL
PCU1/TED
SEHCMT
5 10m
LATERAL DISTANCE SCALE
ฃAULEIELD ENGINEERING
ELIZABETH PARK/BOOMRE UNE
oxer
HV
i
2117
SCALE:
1:500
DA1E
24/1/97
CADOFlฃ
rDEB03-A
-------
Plate 32
Data File:
Subfile:
Depth
(meters)
CO
00
Geographical Position
EBOJOOU EBOJ0024 EBOJ0025 EBOM026
0000
71.407.77N 71.4MLSM 71.41189N 71.415.7BN 71.419.39N
4,09a.J40.76E 4,094152.40E 4,09ซ.mj7E 4,09ซ,J7127E 4.098.M5.16E
71.42J.55N
71.4I7.KW
4.09a,4l5.1CE
71,4M.68N
4.098.4J1.976E
71.4Z7JON
71.41S24N
Ref. File: EB03
BOOMER LINE
NOTE:
LOW FREQUENCY BOOMER DATA
SEDIMENT LAYERS INTERPRETTED
ROM CORES
LEGEND
HOtUAL
ZDUNT
BASC sa. OOCRPIICN
RMM/fUJF
OAT
air cut ra OAITT S.T
9.TY SMO TO SANDY SLT
SAW
HAJO/COPACT
POTtNTW
POiintD
10m
LATERAL DISTANCE SCALฃ
CAULEIELD ENGINEERING
""ELIZABETH PARK/BOOMER LINE
HV
1:500
C.
27/1/97
CAOO nt
rpRFfH-R
-------
TRENTON CHANNEL STUDY AREA
N
City of Gibraltar
Elizabeth Park Site
Lake Erie
*ป
h-*
CO
STATUTE MILES
Plate 33
Trenton Channel
Study Area
-------
APPENDIX A2
METLAB ANALYSIS PROGRAMS
The Major Metlab Program Listings Prepared for the
Analysis of the Data is Contained in This Appendix.
These Program Listings have been Broken into Sub-
Appendices for Easier Reference
A2-1
-------
Appendix A2.1
Bottom Loss Computations
Program Listing 1 - Bottom Loss Batch File
Program Listing 2 - Bottom Loss Plotting Routine
A2-2
-------
PROGRAM LISTING #1
BLS.M
% program name : bis
% program : bottom loss plots
% comments : this is the batch engine driver
% to produce various bottom loss plots
% any number can be run with printing
% define constants
m = 20;
pf=0;
% program runs
a = 'L03';
fbls2(a,m,pf);
%fbls2(a,m,pf);
%a = 'L03';
%fbls2(a,m,pf);
%a = 'L05';
%fbls2(a,m,pf);
%a = 'L07';
%fbls2(a,m,pf);
%a = 'L09';
%fbls2(a,m,pf);
%a = 'Lll';
%fbls2(a,m,pf);
%a = 'L13';
%fbls2(a,m,pf);
%a = 'L14';
%fbls2(a,m,pf);
% end of batch engine driver
A2-3
-------
PROGRAM LISTING #2
FBLS2.M
function fbls2(a,m,pf)
% function name : fbls
% function : bottom loss
% description : this function generates bottom loss
% plots for one line
% load the bottom loss data data
eval(['load c:\brian\e70x\' a '.bis ;']);
eval(['bl = ' a ';']);
bl = bl';
[temp n] = size(bl);
xbl= 1 : n;
% calculate average and standard deviation for
% every point except at the edges.
for i = m + 1 : n m;
bltemp(l : 2 * m + 1) = bl(i - m : i + m);
blav(i) = mean(bltemp);
blsd(i) = std(bltemp);
end;
% for the both edges use the closest symmetric calculation
% this is the same as using the 2*m + 1 values starting at
% the edge
for i = 1 : m;
blav(i) = blav(m + 1);
blsd(i) = blsd(m+l);
end;
for i = n - m + 1 : n;
blav(i) = blav(n - m);
blsd(i) = blsd(n - m);
end;
% plot bottom losses and processed bottom losses
figure(2);
grid;
subplot(2,l,l), plot(xbl,bl);
title(['Figure XXX Bottom Losses for :' a]);
ylabel('BL (raw)1);
grid;
A2-4
-------
subplot(2,1,2), plot(xbl,blav,xbl,blsd);
ylabel('smoothed stdev1);
grid;
xlabel(V);
ifpf=l;
print;
end;
% end of function
A2-5
-------
Appendix A2.2
Phase Computations
Program Listing 3 - Phase Batch File
Program Listing 4 - Phase Plotting Routine
A2-6
-------
PROGRAM LISTING #3
PHP.M
% program name : php
% program : phase plus plots
% comments : this is the batch engine driver
% to produce various phase plus plots
% any number can be run with printing
% constants
m = 20;
pf=0;
% program runs
a = 'L03';
fphp2(a,m,pf);
%a = '
%fphp2(a,m,pf);
%a = 'LOS1;
%rphp2(a,m,pf);
%a = 'L05';
%fphp2(a,m,pf);
%a = 'L07';
%fphp2(a,m,pf);
%a = 'L09';
%rbhp2(a,m,pf);
%a = 'Lll';
%fphp2(a,m,pf);
%rphp2(a,m,pf);
%a = 'L14';
%fphp2(a,m,pf);
% end of batch engine driver
A2-7
-------
PROGRAM LISTING #4
FPHP2.M
function fphp2(a,m,pf)
% function name : fphp2
% function : phase plus
% description : this function generates phase plus
% plots for one line
% load the phase plus data
eval(['load c:\brian\e70xV a '.php ;']);
eval(['pp = 'a';']);
pp = PP';
[temp n] = size(pp);
xpp = 1 : n;
pp2(l :n) = pp(l, 1 :n);
clear pp;
PP =PP2;
% process the phases +- where there is symmetical data
for i = m + 1 : n - m;
pptemp(l : 2 * m + 1) = pp(i - m : i + m);
ppav(i) = mean(pptemp);
temp = ppav(i);
% adjust so the range is 0 to 100.
temp = temp/2+ 0.5;
temp = temp * 100;
ppav(i) = temp;
end
% use the nearest symmetric value for edges.
for i = 1 : m;
ppav(i) - ppav(m + 1);
end;
for i = n - m + 1 : n;
ppav(i) = ppav(n - m);
end;
% calculate the standard deviation too
for i = m + 1 : n - m;
pptemp(l : 2 * m + 1) = ppav(i - m : i + m);
ppsd(i) = std(pptemp);
end;
A2-8
-------
% edge effects for SD
for i = 1 : m;
ppsd(i) = ppsd(m+l);
end;
for i = n - m + 1 : n;
ppsd(i) = ppsd(n - m);
end;
% plot phase sign percents
figure(l);
grid;
subplot(2,l,l), plot(xpp,pp);
title(['Figure XXX Plus Percent for :' a]);
ylabel('individual phases');
grid;
subplot(2,1,2), plot(xpp,ppav,xpp,ppsd);
ylabel('stdev plus percent');
grid;
xlabel('x');
ifpf=l;
print;
end;
% end of function
A2-9
-------
Appendix A2.3
Layer Thickness Contour Routines
Program Listing 5 - Layer Thickness Contour Plot Routine
A2-10
-------
PROGRAM LISTING #5
FLAYERS3.M
function flayers3
% function name : flayersS
% function : layers contour
% description : this function generates a contour plot
% for the layers
% it also writes the interpolated grid
% to an ascii (text) file
% first read the data from disk and store in arrays
% load line 02
load c:\brian\autocadt\bl02bj.txt
hld = b!02bj;
hid = hid1;
[temp n02] = size(hld);
north02(l : n02) = hld(l, 1 : n02);
north02 = north02 - 70000;
east02(l : n02) = hld(2, 1 : n02);
east02 = east02 - 4090000;
top02(l : n02) = hld(3, 1 : n02);
bot02(l : n02) = hld(4, 1 : n02);
dpth02 = bot02 - top02;
clear hid;
% load line 04
load c:\brian\autocadt\bl04bj.txt
hld = b!04bj;
hid = hid1;
[temp n04] = size(hld);
north04(l : n04) = hld(l, 1 : n04);
north04 = north04 - 70000;
east04(l : n04) = hld(2, 1 : n04);
east04 = east04 - 4090000;
top04(l : n04) = hld(3, 1 : n04);
bot04(l : n04) = hld(4, 1 : n04);
dpth04 = bot04 - top04;
clear hid;
A2-11
-------
% load line 06
load c:\brian\autocadt\bl06bj.txt
hid = bl06bj;
hid = hid';
[temp n06] = size(hld);
north06(l : n06) = hld(l, 1 : n06);
north06 = north06 - 70000;
east06(l : n06) = hld(2, 1 : n06);
east06 = east06 - 4090000;
top06(l : n06) = hld(3, 1 : n06);
bot06(l : n06) - hld(4, 1 : n06);
dpth06 = bot06 - top06;
clear hid;
% load line 08
load c:\brian\autocadt\bl08bj.txt
hld = bl08bj;
hid = hid1;
[temp n08] = size(hld);
north08(l : n08) = hld(l, 1 : n08);
northOS = northOS - 70000;
east08(l : n08) = hld(2, 1 : n08);
eastOS = eastOS - 4090000;
top08(l : n08) = hld(3, 1 : n08);
bot08(l :n08) = hld(4, 1 : n08);
dpthOS = botOS - topOS;
clear hid;
% load line 10
load c:\brian\autocadt\bllObj.txt
hld = bl!0bj;
hid = hid';
[tempnlO] = size(hld);
northlO(l : nlO) = hld(l, 1 : nlO);
northlO = northlO - 70000;
eastlO(l :nlO) = hld(2, 1 :nlO);
eastlO = eastlO - 4090000;
toplO(l :nlO) = hld(3, 1 :nlO);
botlO(l :nlO) = hld(4, 1 : nlO);
dpthlO = botlO-toplO;
clear hid;
% load line 12
load c:\brian\autocadt\bll2bj.txt
hld = bll2bj;
A2-12
-------
hid = hid';
[tempn!2] = size(hld);
north!2(l : n!2) = hld(l, 1 : n!2);
north!2 = north!2 - 70000;
east!2(l :n!2) = hld(2, 1 :n!2);
east!2 = east!2- 4090000;
top!2(l :n!2) = hld(3, 1 : n!2);
bot!2(l :n!2) = hld(4, 1 : n!2);
dpthl2 = botl2-top!2;
clear hid;
% load line 14
load c:\brian\autocadt\bll4bj.txt
hld = bl!4bj;
hid = hid';
[temp n!4] = size(hld);
north!4(l : n!4) = hld(l, 1 : n!4);
northH = north!4 - 70000;
east!4(l :n!4) = hld(2, 1 : n!4);
eastl4 = east!4-4090000;
top!4(l : n!4) = hld(3, 1 : n!4);
bot!4(l :n!4) = hld(4, 1 : n!4);
dpth!4 = bot!4-topl4;
clear hid;
% load line 16
load c:\brian\autocadt\bll6bj.txt
hld = bll6bj;
hid = hid';
[temp n!6] = size(hld);
north!6(l : n!6) = hld(l, 1 : n!6);
northl6 = north!6 - 70000;
east!6(l :nl6) = hld(2, 1 :n!6);
eastl6 = east!6-4090000;
top!6(l :n!6) = hld(3, 1 : n!6);
bot!6(l :n!6) = hld(4, 1 : n!6);
dpthl6 = botl6-top!6;
clear hid;
% load line 18
load c:\brian\autocadt\bll8bj.txt
hld = b!18bj;
hid = hid1;
[tempnl8] = size(hld);
north!8(l : n!8) = hld(l, 1 : n!8);
A2-13
-------
northl8 = northl8-70000;
east!8(l :n!8) = hld(2, 1 :n!8);
eastl8 = east!8-4090000;
topi 8(1 :n!8) = hld(3, 1 :n!8);
bot!8(l :n!8) = hld(4, 1 :n!8);
dpthl8 = botl8-top!8;
clear hid;
% load line 20
load c:\brian\autocadt\bl20bj.txt
hld = b!20bj;
hid = hid1;
[temp n20] = size(hld);
north20(l : n20) = hld(l, 1 : n20);
north20 = north20 - 70000;
east20(l : n20) = hld(2, 1 : n20);
east20 = east20 - 4090000;
top20(l : n20) = hld(3, 1 : n20);
bot20(l : n20) = hld(4, 1 : n20);
dpth20 = bot20 - top20;
clear hid;
% load line 22
load c:\brian\autocadt\bl22bj.txt
hld = b!22bj;
hid = hid';
[temp n22] = size(hld);
north22(l : n22) = hld(l, 1 : n22);
north22 = north22 - 70000;
east22(l : n22) = hld(2, 1 : n22);
east22 = east22 - 4090000;
top22(l : n22) = hld(3, 1 : n22);
bot22(l : n22) = hld(4, 1 : n22);
dpth22 = bot22 - top22;
clear hid;
% put all the data into 3 long vectors
nn04 = n02 + n04;
nn06 = nn04 + n06;
nn08 = nn06 + n08;
nnlO = nn08 + nlO;
nnl4 = nnl2 + nl4;
A2-14
-------
nn20 = nnl8 + n20;
nn22 = nn20 + n22;
x(l :n02) = east02(l : n02);
x(n02 + 1 : nn04) = east04(l : n04);
x(nn04 + 1 : nn06) = east06(l : n06);
x(nn06 + 1 : nn08) = east08(l : n08);
x(nn08 + 1 : nnlO) = east 10(1 : nlO);
x(nnlO + 1 : nn!2) = east 12(1 : n!2);
x(nn!2 + 1 : nn!4) = east 14(1 : n!4);
x(nn!4 + 1 : nn!6) = east 16(1 : n!6);
x(nn!6 + 1 : nn!8) = east!8(l : n!8);
x(nn!8 + 1 : nn20) = east20(l : n20);
x(nn20 + 1 : nn22) = east22(l : n22);
y(l :n02) = north02(l : n02);
y(n02 + 1 : nn04) = north04(l : n04);
y(nn04 + 1 : nn06) = north06(l : n06);
y(nn06 + 1 : nn08) = north08(l : n08);
y(nn08 + 1 : nnlO) = northlO(l : nlO);
y(nnlO + 1 : nn!2) = north!2(l : n!2);
y(nn!2 + 1 : nn!4) = north 14(1 : n!4);
y(nn!4 + 1 : nn!6) = north!6(l : n!6);
y(nn!6 + 1 : nnl8) = north!8(l : n!8);
y(nn!8 + 1 : nn20) = north20(l : n20);
y(nn20 + 1 : nn22) = north22(l : n22);
z(l : n02) = dpth02(l : n02);
z(n02 + 1 : nn04) = dpth04(l : n04);
z(nn04 + 1 : nn06) = dpth06(l : n06);
z(nn06 + 1 : nn08) = dpth08(l : n08);
z(nn08 + 1 : nnlO) = dpthlO(l : nlO);
z(nnlO + 1 : nn!2) = dpth!2(l : n!2);
z(nn!2 + 1 : nn!4) = dpth!4(l : n!4);
z(nn!4 + 1 : nn!6) = dpth!6(l : n!6);
z(nn!6 + 1 : nn!8) = dpth!8(l : n!8);
z(nn!8 + 1 : nn20) = dpth20(l : n20);
z(nn20 + 1 : nn22) = dpth22(l : n22);
clear east02;
clear east04;
clear east06;
clear eastOS;
clear eastlO;
clear east 12;
clear east!4;
clear east 16;
clear east 18;
A2-15
-------
clear east20;
clear east22;
clear north02;
clear north04;
clear north06;
clear northOS;
clear northlO;
clear north!2;
clear north!4;
clearnorthl6;
clearnorthlS;
clear north20;
clear north22;
clear top02;
clear top04;
clear top06;
clear topOS;
clear top 10;
clear top 12;
clear top 14;
clear top 16;
clear top 18;
clear top20;
clear top22;
clear bot02;
clear bot04;
clear bot06;
clear botOS;
clear botlO;
clear bot 12;
clear bot!4;
clear bot!6;
clear bot 18;
clear bot20;
clear bot22;
clear dpth02;
clear dpth04;
clear dpth06;
clear dpthOS;
clear dpth 10;
cleardpth!2;
clear dpth!4;
cleardpth!6;
cleardpthlS;
clear dpth20;
A2-16
-------
clear dpth22;
%for i = 1 : 86;
% xi(i) = i*2;
%end;
%fori=l :91;
% yi(i) = i*2;
%end;
%xi = 8698 + xi;
%yi = 2858 + yi;
% defined desired regular grid coordinates
for i = 1 : 35;
xi(i) = i*5;
end;
for i = 1 : 37;
yi(i) = i*5;
end;
xi = 8695 + xi;
yi = 2855+yi;
% interpolate the data onto the regular grid
zi = griddata(x,y,z,xi,yi);
%% save the resampled data to disk
%fori=l :35;
%forj = l :37;
% k=j + (i- 1)*37;
% a(2,k) = yi(j);
% a(3,k) = zi(k);
% end;
%end;
%a = a'
%save c:\brian\code\thick.txt a -ascii
% make contour plot
v = [0.5 0.75 1 1.25 1.5 1.75 2 2.25 2.5];
figure(l);
grid;
cs = contour(xi,yi,zi,v);
axis('square');
axis([8700,8880,2860,3040]);
title('Black Lagoon Thick Sediment Contours (greater than 0.5 m)');
ylabel(TSforthing');
A2-17
-------
grid;
xlabel('Easting Contour inverval is 0.25 m1);
clabel(cs,'manual');
% end of function
A2-18
-------
Appendix A2.4
Scaled Survey Lines Routine
Program Listing 6 - Sealed Survey Line Map Routine
A2-19
-------
PROGRAM LISTING #6
FLINES.M
function flines
% function name : flines
% function : lines
% description : this function generates a map plot
% of all the lines
% load line 02
load c:\brian\autocadt\bl02bj.txt
hld = b!02bj;
hid = hid';
[temp n02] = size(hld);
no02(l :n02) = hld(l, 1 : n02);
no02 = no02 - 70000;
ea02(l : n02) = hld(2, 1 : n02);
ea02 = ea02 - 4090000;
clear hid;
% load line 04
load c:\brian\autocadt\bl04bj.txt
hld = b!04bj;
hid = hid';
[temp n04] = size(hld);
no04(l :n04) = hld(l, 1 : n04);
no04 = no04 - 70000;
ea04(l : n04) = hld(2, 1 : n04);
ea04 = ea04 - 4090000;
clear hid;
% load line 06
load c:\brian\autocadt\bl06bj.txt
hld = b!06bj;
hid = hid';
[temp n06] = size(hld);
no06(l :n06) = hld(l, 1 : n06);
no06 = no06 70000;
ea06(l :n06) = hld(2, 1 : n06);
ea06 = ea06 - 4090000;
clear hid;
A2-20
-------
% load line 08
load c:\brian\autocadt\bl08bj.txt
hld = bl08bj;
hid = hid1;
[temp n08] = size(hld);
no08(l :n08) = hld(l, 1 : n08);
no08 = no08 - 70000;
ea08(l :n08) = hld(2, 1 : n08);
ea08 = ea08 - 4090000;
clear hid;
% load line 10
load c:\brian\autocadt\bllObj.txt
hld = bllObj;
hid = hid';
[temp n 10] = size(hld);
no 10(1 :nlO) = hld(l, 1 : nlO);
nolO = nolO-70000;
ealO(l :nlO) = hld(2, 1 :nlO);
ealO = ealO-4090000;
clear hid;
% load line 12
load c:\brian\autocadt\bll2bj.txt
hld = b!12bj;
hid = hid';
[temp n!2] = size(hld);
no!2(l :n!2) = hld(l, 1 : n!2);
no!2 = no!2-70000;
ea!2(l :nl2) = hld(2, 1 : n!2);
ea!2 = ea!2-4090000;
clear hid;
% load line 14
load c:\brian\autocadt\bll4bj.txt
hld = bll4bj;
hid = hid';
[temp n!4] = size(hld);
no!4(l :n!4) = hld(l, 1 : n!4);
no!4 = no!4-70000;
ea!4(l :n!4) = hld(2, 1 : n!4);
eal4 = ea!4-4090000;
clear hid;
% load line 16
A2-21
-------
load c:\brian\autocadt\bll6bj.txt
hld = bl!6bj;
hid = hid';
[tempnl6] = size(hld);
no!6(l :n!6) = hld(l, 1 : n!6);
no!6 = no!6-70000;
ea!6(l :n!6) = hld(2, 1 :n!6);
eal6 = ea!6-4090000;
clear hid;
% load line 18
load c:\brian\autocadt\bll8bj.txt
hld = bl!8bj;
hid = hid';
[tempn!8] = size(hld);
no!8(l :n!8) = hld(l, 1 :n!8);
nol8 = no!8-70000;
ea!8(l :n!8) = hld(2, 1 :n!8);
eal8 = ea!8-4090000;
clear hid;
% load line 20
load c:\brian\autocadt\bl20bj.txt
hld = b!20bj;
hid = hid';
[temp n20] = size(hld);
no20(l :n20) = hld(l, 1 : n20);
no20 = no20 - 70000;
ea20(l : n20) = hld(2, 1 : n20);
ea20 = ea20 - 4090000;
clear hid;
% load line 22
load c:\brian\autocadt\bl22bj.txt
hld = b!22bj;
hid = hid';
[temp n22] = size(hld);
no22(l :n22) = hld(l,l : n22);
no22 = no22 - 70000;
ea22(l : n22) = hld(2, 1 : n22);
ea22 = ea22 - 4090000;
clear hid;
% make map plot
figure(l);
A2-22
-------
grid;
plot(ea02,no02,ea04,no04,ea06,no06,ea08,no08,eal 0,no 1O.eal 2,no 12,eal 4,no 14,eal 6,no 16,eal 8
,nol 8,ea20,no20,ea22,no22);
title('plot map of lines 02 22');
axis('square');
axis([8700,8880,2860,3040]);
ylabelCNorthing');
grid;
xlabel('Easting');
pf=0;
ifpf=l;
print;
end;
% end of function
A2-23
-------
Appendix A2.5
Volume Estimate Routine
Program Listing 7 - Sediment Thickness and Position
Information Converted to Volume Estimates
A2-24
-------
PROGRAM LISTING #7
FVOL.M
function fvol
% function name : fvol
% function : volume calculation
% description : this function calculates the volume of
% sediment within a given range of Northings
% and Eastings. The sediments must also
% be thicker than a practical dregging minimum
% and be within the actual survey boundries.
%
% the result is simply echoed to the matlab
% command window.
% load thicknesses
load c:\brian\code\thick3.txt
hld = thick3;
hid = hid';
[temp n] = size(hld);
north(l : n) = hld(2, 1 : n);
east(l :n) = hld(l, 1 : n);
thick(l :n) = hld(3, 1 : n);
inflg(l : n) = hld(4, 1 : n);
clear hid;
% set range data
minthick= 1.0;
eastinc = 5;
northinc = 5;
eastmin = 8750;
eastmax = 8810;
northmin = 2990;
northmax = 3040;
% calcuate the volume
vol = 0;
for i = 1 : n;
ifinflg(i)=l;
if east(i) >= eastmin;
A2-25
-------
ifeast(i)<=eastmax;
if north(i) >= northmin;
if north(i) <= northmax;
if thick(i) >= minthick;
vol = vol + thick(i);
end;
end;
end;
end;
end;
end;
end;
% echoing to matlab window
northmin2 = northmin
northmax2 = northmax
eastmin2 = eastmin
eastmax2 = eastmax
minthick2 = minthick
thick2 = vol
vol = vol * northinc * eastinc;
vo!3 = vol
% end of function
A2-26
-------
Appendix A2.6
Depth Contour Routine
Program Listing 8 - Bathymetric Contour Generation
A2-27
-------
PROGRAM LISTING #8
FWDEP.M
function fwdep
% function name : fwdep
% function : water depth
% description : this function generates a contour plot
% for the water depths
% load line 02
load c:\brian\autocadt\bl02bj.txt
hld = b!02bj;
hid = hid';
[temp n02] = size(hld);
north02(l : n02) = hld(l, 1 : n02);
north02 = north02 - 70000;
east02(l : n02) = hld(2, 1 : n02);
east02 = east02 - 4090000;
top02(l : n02) = hld(3, 1 : n02);
clear hid;
% load line 04
load c:\brian\autocadt\bl04bj.txt
hld = b!04bj;
hid = hid';
[temp n04] = size(hld);
north04(l : n04) = hld(l, 1 : n04);
north04 = north04 - 70000;
east04(l : n04) = hld(2, 1 : n04);
east04 = east04 - 4090000;
top04(l : n04) = hld(3, 1 : n04);
clear hid;
% load line 06
load c:\brian\autocadt\bl06bj.txt
hld = b!06bj;
hid = hid';
[temp n06] = size(hld);
north06(l : n06) = hld(l, 1 : n06);
north06 = north06 - 70000;
east06(l : n06) = hld(2, 1 : n06);
A2-28
-------
east06 = east06 - 4090000;
top06(l : n06) = hld(3, 1 : n06);
clear hid;
% load line 08
load c:\brian\autocadt\bl08bj.txt
hld = b!08bj;
hid = hid1;
[temp n08] = size(hld);
north08(l : n08) = hld(l, 1 : n08);
northOS = northOS - 70000;
east08(l : n08) = hld(2, 1 : n08);
eastOS = eastOS - 4090000;
top08(l : n08) = hld(3, 1 : n08);
clear hid;
% load line 10
load c:\brian\autocadt\bllObj.txt
hld = bllObj;
hid = hid';
[tempnlO] = size(hld);
northlO(l : nlO) = hld(l, 1 :nlO);
northlO = northlO - 70000;
eastlO(l :nlO) = hld(2, 1 : nlO);
eastlO = eastl 0-4090000;
toplO(l :nlO) = hld(3, 1 : nlO);
clear hid;
% load line 12
load c:\brian\autocadt\bll2bj.txt
hld = b!12bj;
hid = hid1;
[tempnl2] = size(hld);
north!2(l : n!2) = hld(l, 1 : n!2);
north!2 = north!2 - 70000;
east!2(l : n!2) = hld(2, 1 : n!2);
east!2 = east!2 - 4090000;
top!2(l :nl2) = hld(3, 1 : n!2);
clear hid;
% load line 14
load c:\brian\autocadt\bll4bj.txt
hld = bll4bj;
hid = hid';
[temp n!4] = size(hld);
A2-29
-------
north!4(l : n!4) = hld(l, 1 : n!4);
northH = north!4 - 70000;
east!4(l :n!4) = hld(2, 1 : n!4);
eastl4 = east!4-4090000;
topi4(1 :n!4) = hld(3, 1 : n!4);
clear hid;
% load line 16
load c:\brian\autocadt\bll6bj.txt
hld = bll6bj;
hid = hid';
[temp n!6] = size(hld);
north!6(l : n!6) = hld(l, 1 : n!6);
north!6 = north!6 - 70000;
east!6(l :n!6) = hld(2, 1 : n!6);
east 16 = east 16 - 4090000;
top!6(l :n!6) = hld(3, 1 : n!6);
clear hid;
% load line 18
load c:\brian\autocadt\bll8bj.txt
hld = b!18bj;
hid = hid';
[tempn!8] = size(hld);
north!8(l : n!8) = hld(l, 1 :n!8);
northlS = northlS - 70000;
east!8(l :n!8) = hld(2, 1 :n!8);
eastl8 = east!8-4090000;
topi8(1 :n!8) = hld(3, 1 : n!8);
clear hid;
% load line 20
load c:\brian\autocadt\bl20bj.txt
hld = b!20bj;
hid = hid';
[temp n20] = size(hld);
north20(l : n20) = hld(l, 1 : n20);
north20 = north20 - 70000;
east20(l : n20) = hld(2, 1 : n20);
east20 = east20 - 4090000;
top20(l :n20) = hld(3, 1 : n20);
clear hid;
% load line 22
load c:\brian\autocadt\bl22bj.txt
A2-30
-------
hld = b!22bj;
hid = hid1;
[temp n22] = size(hld);
north22(l : n22) = hld(l, 1 : n22);
north22 = north22 - 70000;
east22(l : n22) = hld(2, 1 : n22);
east22 = east22 - 4090000;
top22(l : n22) = hld(3, 1 : n22);
clear hid;
nn04 = n02 + n04;
nn06 = nn04 + n06;
nn08 = nn06 + n08;
nnlO = nn08 + nlO;
nnl2 = nnlO + n!2;
nn!6 = nn!4 + n!6;
nn22 = nn20 + n22;
x(l :n02) = east02(l : n02);
x(n02 + 1 : nn04) = east04(l : n04);
x(nn04 + 1 : nn06) = east06(l : n06);
x(nn06 + 1 : nn08) = east08(l : n08);
x(nn08 + 1 : nnlO) = eastlO(l : nlO);
x(nnlO + 1 : nn!2) = east!2(l : n!2);
x(nn!2 + 1 : ml 4) = east 14(1 : n!4);
x(nn!4 + 1 : ml 6) = east 16(1 : n!6);
x(nn!6 + 1 : ml 8) = east!8(l : n!8);
x(nn!8 + 1 : nn20) = east20(l : n20);
x(nn20 + 1 : nn22) = east22(l : n22);
y(l :n02) = north02(l : n02);
y(n02 + 1 : nn04) = north04(l : n04);
y(nn04 + 1 : nn06) = north06(l : n06);
y(nn06 + 1 : nn08) = north08(l : n08);
y(nn08 + 1 : nnlO) = northlO(l : nlO);
y(nnlO + 1 : m!2) = north!2(l : n!2);
y(nn!2 + 1 : ml 4) = northl4(l : n!4);
y(nn!4 +1 : ml 6) = north!6(l : n!6);
y(nn!6 + 1 : ml 8) = north!8(l :n!8);
y(nn!8 + 1 : nn20) = north20(l : n20);
y(nn20 + 1 : nn22) = north22(l : n22);
22(1 :n02) = top02(l : n02);
z2(n02 + 1 : nn04) = top04(l : n04);
z2(nn04 + 1 : m06) = top06(l : n06);
A2-31
-------
z2(nn06 + 1 : nn08) = top08(l : n08);
z2(nn08 + 1 : nnlO) = topi0(1 : nlO);
z2(nnlO + 1 : nn!2) = top!2(l : n!2);
z2(nn!2 + 1 : nn!4) = top!4(l : n!4);
z2(nn!4 + 1 : nn!6) = topi6(1 : n!6);
z2(nn!6 + 1 : nn!8) = topi8(1 : n!8);
z2(nn!8 + 1 : nn20) = top20(l : n20);
z2(nn20 + 1 : nn22) = top22(l : n22);
for i = 1 : 35;
xi(i) = i*5;
end;
for i = 1 : 37;
yi(i) = i*5;
end;
xi = 8695 + xi;
yi = 2855+yi;
%fori=l : 18;
%xi(i) = i*10;
%end;
%fori = l : 19;
%yi(i) = i*10;
%end;
%xi = 8690 + xi;
%yi = 2850 + yi;
z2i = griddata(x,y,z2,xi,yi);
v2 = [1 2 3 4 5 6 7];
% make contour plot
figure(l);
grid;
cs = contour(xi,yi,z2i,v2);
axis('square');
axis([8700,8880,2860,3040]);
title('Black Lagoon Water Depth Contour Plot (in meters)');
ylabelCNorthing');
grid;
xlabel('Easting');
clabel(cs,'manual');
% end of function
A2-32
-------
Appendix A2.7
Elizabeth Park Layer-Contour Routine
Program Listing 9 - Example of Program Changes for Site
Input
A2-33
-------
PROGRAM LISTING #9
FLAYERQE.M
function flayerqe
% function name : flayerqe
% function : layers contour qe park
% description : this function generates a contour plot
% for the layers
% for queen elizabeth park
% read the data from disk
% load line 01
load c:\brian\autocadt\qe01bj.txt
hld = qe01bj;
hid = hid';
[temp nOl] = size(hld);
no01(l :n01) = hld(3, 1 : nOl);
noOl =no01 -70000;
ea01(l :n01) = hld(4, 1 :n01);
eaOl =ea01 -4090000;
top01(l :n01) = hld(5, 1 : nOl);
bot01(l :n01) = hld(6, 1 : nOl);
diffOl =bot01 -topOl;
clear hid;
% load line 03
load c:\brian\autocadt\qe03bj.txt
hld = qe03bj;
hid = hid1;
[temp n03] = size(hld);
no03(l :n03) = hld(3, 1 : n03);
no03 = no03 - 70000;
ea03(l : n03) = hld(4, 1 : n03);
ea03 = ea03 - 4090000;
top03(l : n03) = hld(5, 1 : n03);
bot03(l : n03) = hld(6, 1 : n03);
diff03=bot03-top03;
clear hid;
% load line 05
A2-34
-------
load c:\brian\autocadt\qe05bj.txt
hld = qe05bj;
hid = hid1;
[temp n05] = size(hld);
no05(l : n05) = hld(3, 1 : n05);
no05 = no05 - 70000;
ea05(l : n05) = hld(4, 1 : n05);
ea05 = ea05 - 4090000;
top05(l :n05) = hld(5, 1 : n05);
bot05(l : n05) = hld(6, 1 : n05);
diffD5 = bot05-top05;
clear hid;
% load line 07
load c:\brian\autocadt\qe07bj.txt
hld = qe07bj;
hid = hid1;
[temp n07] = size(hld);
no07(l :n07) = hld(3, 1 : n07);
no07 = no07 - 70000;
ea07(l : n07) = hld(4, 1 : n07);
ea07 = ea07 - 4090000;
top07(l : n07) = hld(5, 1 : n07);
bot07(l : n07) = hld(6, 1 : n07);
difTO7 = bot07 - top07;
clear hid;
% load line 09
load c:\brian\autocadt\qe09bj.txt
hld = qe09bj;
hid = hid';
[temp n09] = size(hld);
no09(l :n09) = hld(3, 1 : n09);
no09 = no09 - 70000;
ea09(l : n09) = hld(4, 1 : n09);
ea09 = ea09 - 4090000;
top09(l : n09) = hld(5, 1 : n09);
bot09(l : n09) = hld(6, 1 : n09);
diff09 = bot09 - top09;
clear hid;
% load line 11
load c:\brian\autocadt\qel lbj.txt
hld = qellbj;
hid = hid';
A2-35
-------
[tempnll] = size(hld);
noll(l :nll) = hld(3, 1 :nll);
noil = no 11 -70000;
eall(l :nll) = hld(4, 1 :nll);
eal 1 = eal 1 - 4090000;
topi 1(1 :nll) = hld(5, 1 :nll);
botll(l :nll) = hld(6, 1 :nll);
diffll=botll -topll;
clear hid;
% load line 13
load c:\brian\autocadt\qel3bj.txt
hld = qe!3bj;
hid = hid';
[temp n!3] = size(hld);
no!3(l :n!3) = hld(3, 1 :n!3);
no!3=no!3-70000;
ea!3(l :n!3) = hld(4, 1 :n!3);
eal 3 = eal 3-4090000;
top!3(l :n!3) = hld(5, 1 : n!3);
bot!3(l :n!3) = hld(6, 1 : n!3);
difT13 = botl3-topl3;
clear hid;
% load line 14
load c:\brian\autocadt\qel4bj.txt
hld = qe!4bj;
hid = hid';
[temp n!4] = size(hld);
no!4(l :n!4) = hld(3, 1 : n!4);
no!4 = no!4-70000;
ea!4(l :n!4) = hld(4, 1 : n!4);
eal4 = ea!4-4090000;
top 14(1 :n!4) = hld(5, 1 : n!4);
bot!4(l :n!4) = hld(6, 1 : n!4);
diffl4 = botl4-topl4;
clear hid;
nn03=n01 + n03;
nn05 = nn03 +n05;
nn07 = nn05 + n07;
nn09 = nn07 + n09;
nnll =nn09 + nll;
nnl3 = nnll +n!3;
A2-36
-------
x(l :n01) =
x(n01 + 1 :
x(nn03 + 1
x(nn05 + 1
x(nn07 + 1
x(nn09 + 1
x(nnl 1 + 1
x(nn!3 + 1
clear eaOl;
clear ea03;
clear ea05;
clear ea07;
clear ea09;
clear eal 1 ;
clear eal 3;
clear eal 4;
= ea01(l
:n01);
nn03) = ea03(l :
:nn05)
:nn07)
:nn09)
: nnll)
: nn!3)
:nn!4)
= ea05(l
= ea07(l
= ea09(l
= eal 1(1
= ea!3(l
= eal 4(1
n03);
: n05);
: n07);
: n09);
: nil);
:n!3);
:n!4);
y(l :n01) = no01(l
y(n01 + 1 : nn03) =
y(nn03 + 1 : nn05):
y(nn05 + 1 : nn07):
y(nn07 + 1 : nn09):
y(nn09+ 1 :nnll):
y(nnll + 1 :nn!3)
y(nn!3 + 1 : nn!4)
clear noOl;
clear no03;
clear no05;
clear no07;
clear no09;
clear noil;
clearno!3;
clear no 14;
no03(l :
no05(l
no07(l
no09(l
= no!3(l
= no!4(l
n03);
: n05);
: n07);
: n09);
: n!4);
zl(l :n01) =
zl(n01 + 1 :
zl(nn03 + l
zl(nn05 + 1
zl(nn07+l
zl(nn09 + 1
zl(nnll + 1
zl(nnl3 + l
clear topOl;
clear top03;
clear top05;
= top01(l :n
nn03) = top03(l : n03);
: nn05) = top05(l : n05);
:nn07) = top07(l : n07);
:nn09) = top09(l : n09);
:nnll) = topi 1(1 :nll);
:nnl3) = topl3(l : n!3);
:nnl4) = top!4(l : n!4);
A2-37
-------
clear top07;
clear top09;
clear topi 1;
clear topi3;
clear top 14;
z2(l :n01) =
z2(n01 + 1 :
z2(nn03 + 1
z2(nn05 + 1
z2(nn07 + 1
z2(nn09 + 1
z2(nnl 1 + 1
z2(nn!3 + 1
clear botOl;
clear bot03;
clearbotOS;
clear bot07;
clear bot09;
clear botll;
clear bot!3;
clear bot!4;
z3(l :n01) =
z3(n01 + 1 :
z3(nn03 + 1
z3(nn05 + 1
z3(nn07 + 1
z3(nn09 + 1
z3(nnll + 1
z3(nn!3 + 1
clear difiTOl;
clear diff03;
clear diffOS;
clear difTO7;
clear diff09;
clear diffl 1;
cleardifflS;
clear diffl 4;
fori=l :31;
xi(i) = i*5;
end;
fori=l :33;
= i*5;
= bot01(l :n
nn03) = bot03(l : n03);
:nn05) = bot05(l : n05);
:nn07) = bot07(l : n07);
:nn09) = bot09(l : n09);
:nnll) = botll(l :nll);
:nnl3) = bot!3(l :n!3);
:nnl4) = bot!4(l : n!4);
= diff01(l
nn03) = diff03(l : n03);
: nn05) = diff05(l : n05);
: nn07) = diff07(l : n07);
:nn09) = diff09(l : n09);
:nnll) = diffl 1(1 :nll);
:nnl3) = diffl3(l :n!3);
: nn!4) = diff!4(l : n!4);
A2-38
-------
end;
xi = 8420 - 5 + xi;
yi = 1360-5 + yi;
zi = griddata(x,y,z3,xi,yi);
fori=l :31;
for j = 1 : 33;
k=j + (i 1)*33;
a(2,k) = yi(j);
a(3,k) = zi(k);
end;
end;
a = a';
save c:\brian\code\thickqe.txt a -ascii
clear a;
v=[.5.6.7.8J;
% make contour plot
figure(l);
grid;
cs = contour(xi,yi,zi,v);
axis('square');
axis([8420,8580, 1 360, 1 520]);
title('Queen Elizabeth Park Thick Sediment contour plot (over 0.5 m)');
ylabel('Northing');
grid;
xlabel('Easting (Contour Interval is 0.1 m)');
%clabel(cs,'manuaT);
% end of function
A2-39
-------
APPENDIX A3
TECHNICAL TERMS AND SOFTWARE
DISPLAY DESCRIPTIONS
This Appendix Provides the Definitions of Technical
Terms and Software Display Layouts in Their Order of
Occurrence in the Report
A3-1
-------
A3.1 Acoustic Impedance
Acoustic Impedance (Z) is defined as:
Z = rho*c (A3.1-1)
where
rho = density (gm/cmA3)
c = velocity (m/second)
The Acoustic Impedance is related to the reflectivity ( R) by:
Z= (1+R)/(1-R) (A3.1-1)
This equation assumes that the sound wave is plane and is normal (perpendicular)
incident to the reflecting layer.
A3.2 Reflectivity
The layer reflectivity is a measure of the ratio of the signal amplitude reflected
back from a given layer. For normal incidence (perpendicular) cases the reflectivity ( R)
is a function of the two layers Impedance's (Z). The equation of normal incidence is:
R = (Z2 Z,)/(Z2+Zi) (A3.2-1)
where
Zi = Impedance of the incident layer
Za = Impedance of the reflecting layer
A3.3 Bottom Loss
The bottom reflectivity is often expressed in decibels for ease of reference in data
tables and because the sonar equation for bottom reflectivity is easier to handle when the
terms are in decibels. The equation of bottom loss (BL) is :
BL = 20*log(R) (A3.3-1)
where
R = bottom - water interface reflectivity.
Note that the term bottom loss is normally used to refer to the water-bottom
interface, hence the term bottom loss. The subbottom layer reflectivities can also be
expressed in decibels. See Sonar Equation (Section A3.4). The bottom loss is often
A3-2
-------
reported as a positive number in text and tables. However, it is important to note that it is
a negative number as the log of a fraction (reflectivity) is negative.
A3.4 Sonar Equation
The Sonar Equation is used in the survey system calibration routines and for the
computation of bottom loss. The general sonar equation for the computation of bottom
loss (BL) in decibels (db) is:
BL = SL-SR Nw-Nhyd + NA + DI (A3.4-1)
where
SL = sound source level of the survey pinger
SR = signal received at the output of the survey receiver
Nw - 20 * log (Range, meters), db (transmission loss due to spherical
spreading along the path of sound propagation)
Nhyd = survey receiver sensitivity, db
NA = receiver amplifier gain, db
DI = directivity index, db
A3.5 Windows CAL1 Routine
Besides providing source and receiver system calibration, the CAL1 calibration
routine is useful during layer identification and material verification steps. In particular,
the wave form of a given trace in a subfile can be displayed allowing confirmation of the
proper selection of a given layer. Also, independent verification of bottom loss
(reflectivity) can be obtained. Figure A3.5-1 provides a summary of the CAL1 display.
Each major element of the display is numbered and described below.
1. File Name - The file name being processed is displayed here. The file
consists of 6 subfiles labeled 0 to 5. Each file subfile contains the
navigation data at the start (left side) of the subfile. These navigation points
are noted on the final cross sections with a circle with a cross through it.
2. SubFile Number Label - Each subfile is given a label number of 0 to 5.
3. Current Processed SubFile - The current subfile being processed by the
Sonar Equation (Section A3.4) is replicated in this column with the
amplitude for the selected trace number being shown to the right of this
column (7).
4. Time Scale Lines - The time scale lines (in milliseconds) is given on the left
of the figure.
5. Time Offset - The program has the ability to offset the start time by a given
millisecond offset. In this case the offset is 2 milliseconds from the key start
time. This offset is provided so that the bottom display can be moved up
and down.
A3-3
-------
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R(ซi) = 9K1fi Source Level (db)
N(h) = "8E.07 Receiver Sensitivity (db)
Wffl] r 1ft 8 Amplifier Gain (db)
1 9
Ndl = 0. Directivity Index (db)
TRJ-J1_^---J-JUUL--_-l^-_1JU-jm
m- 1 K in9 Bottom Dist. *2 (m)
fthi/1 = ??194'| Bottom Trans. Loss (db)
D2 = 28.1 89 Multiple Dist*2 (m)
Nw? = ?ft. Multiple Tran.Loss (db)
Sn1 = 10K7? Mean Sig. Level Bott. (db)
SdS1 = 3.041 7 Std. Bottom Signal
Sfl2 = -1 1 .47 Mean Sig. Level Mult.(db)
8dS2 = 2.2026 Std. Multiple Signal
sdSs = 0. Std. Source Level
SdNhvd = 0. Std. Receive Level
BL - -8 4786 Mean Bottom Loss
firfRI =4.?7fifi Std. Bottom Loss
R - 0.41 844 Mean Refl. Coef.
8dR = 0.1 8437 Std. Refl. Coef.
1 Drno Mr.' - C
14
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\15
\16
CAL1 Routine Display
-------
6. Seismic Cross Section - The positive half wave rectified total file cross
section is provided. This total display covers all the subfiles in the file.
7. Amplitude Trace - The actual wave form of the Trace No. 21 is displayed.
The program can display any selected trace in the subfile from trace 1 to
trace 40. The positive side of the wave form is to the right and the negative
portion of the wave form is to the left. This display is useful when
attempting to resolve closely spaced layers.
8. Bottom Arrival Time - Showing the strongest bottom reflection signal for
the selected subfile which corresponds to the start of the amplitude signal
(9).
9. Bottom Amplitude Signal Provided to reference the bottom signal
discussed in item (8).
10. Water-Bottom Interface - Showing the point of selection of the water-bottom
interface for the total file cross-section.
11. Source Ringing - This coherent signal is part of the ringing from the source
ping. Its only use is to confirm that the timing is consistent.
12. Multiple - The bottom multiple occurs because the bottom signal has
reflected twice off the bottom. This multiple signal and the bottom signal
data can be entered into the software by selecting these respective signals
';++" and "xx" (18) and solving the Sonar Equation (column (19)) for
bottom loss and reflectivity. This procedure is used to calibrate the Acoustic
Core Reflection/Sign (ACRS) routine.
13. Display Gain - The display gain can be varied to improve visual review of
the amplitude data shown in the center of the Figure.
14. Stack Number - The stacking of up to 8 adjacent traces can be accomplished
to improve the Signal-to-Noise. In this particular case, the bottom spatial
variance is high and stacking is not used.
15. Vertical Display - The time scale can be expanded to examine in more detail
various sections of the seismic cross-section. In this particular display no
vertical expansion was done.
16. Trace Number - The amplitude of any one of the subfile traces can be
displayed. In this particular case, trace 21 is displayed. There are 40 traces
in each of these subfiles.
17. Process Number - There are five different possible solutions of the sonar
equation. That is for source level, receiver level, etc. In this particular
display we are solving for bottom loss (reflectivity) by way of process
number 5.
18. Signal Selection Marks - The first reflection signal "+ +" and the second
reflection signal "x x" marks are used to indicate the travel time regions
where the computer program searches for the largest signal for current
computation. In this particular case the bottom and multiple signals are
selected.
19. Sonar Equation Terms - This column of the display shows the processed
results from the sonar equation solution. Each term is identified and mean
and standard deviation of the computations are provided. The computations
A3-5
-------
are done for all traces in the selected subfile. The source and receiver
standard deviations are zero for this case as these were input into the sonar
equations as known values.
A3.6 Acoustic Core Reflection/Sign (ACRS) Routine
The ACRS program is used to identify layers in complex structures and as an aid
in bottom classification (material type). The program uses the Sonar Equation for the
computation of the bottom loss terms. For the Trenton Channel study two display modes
were used, correlation display and full wave rectified display. These displays are
discussed in the following sub-sections.
A3.6.1 Correlation Display
Figure A3.6-1 illustrates the output display for the correlation mode of operation
of the ACRS routine. The right portion of the display, the correlation output, is also
called the pick plot. The correlation display (5) is generated by performing the cross-
correlation of the source wavelet with each seismic trace. When the correlation level is
above the mean noise, a layer pick is made. The sign of the pick is dependent on the
phase of the signal at that layer with respect to the wavelet phase. A negative phase is
shown with dashed lines (7) and a solid line (8) is for positive phase. The phase changes
if there is gas content in the bottom. The routine also solves the Sonar Equation in
Section A3.4 and generates the bottom loss value for each trace as well as the overall file
mean and standard deviation bottom loss values. The keyed number items are as follows:
1. File Name - The file name being processed is displayed here. The file
consists of 6 subfiles labeled 0 to 5. Each file subfile contains the
navigation data at the start (left side) of the subfile. These navigation points
are noted on the final cross sections with a circle with a cross through it.
2. Wavelet Reference File Name - This file was originally generated by the
CAL1 routine during the calibration of the source. It contains an exact
replica the source wave form.
3. SubFile Number Label - Each subfile is given a label number of 0 to 5.
4. Normal Cross-Section - The left hand portion of the display is the normal
seismic half wave rectified seismic cross-section.
5. Correlation Cross-Section - The right half seismic display is of the
correlation pick plots of the bottom layers with optimum signal-to-noise.
The automated correlation processing has a vertical resolution limit of one
wavelet. That is, if a layer is identified it cannot pick another layer within
the equivalent travel time of the ping transmit period. This is not a
theoretical limitation, but rather a software limitation at the present time.
This display is of great help when spatial variance is high as is shown in this
plot.
6. Water-Bottom Interface - Water bottom interface for standard cross-section.
A3-6
-------
0
13
ms.
:D
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15.5.
P010081.DAT
1 | 2 | 3
REF: D:VACOUriqriC\R27BEC02.ASC
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-------
7. Water-Bottom Interface (Correlation Negative Sign) - The water bottom
interface with the broken lines indicating a negative phase change at the
layer interface.
8. Water-Bottom Interface (Correlation Positive Sign) - The water bottom
interface with the solid line indicating a positive phase at the layer interface.
The phase sign displays are also available on the subbottom layers.
9. Subbottom Layer - Illustrating the identification of a subbottom layer with
the correlation pick plot routine. Another subbottom layer exists and is
picked below this layer. If diffraction signals or if the signal to noise is bad
the record appears incoherent (15). Incoherent data is ignored during
interpretation.
10. Bottom Loss Plot - The bottom loss for each trace in the entire file (all
subfiles) is computed and plotted. Note the typical high variance of the
bottom loss due to spatial variance.
11. Bottom Loss Scale - The bottom loss scale ranges from 0 to -25 db.
12. Vertical Display As in the CAL1 routine the seismic section can be
expanded and displayed. This particular display has been expanded by a
factor of two from the original.
13. Time Scale - The time scale (depth) is given in milliseconds increments.
14. Time Scale Offset - The entire display can be shifted vertically by changing
the Time Scale Offset with respect to the transmit key (time zero). An offset
of 5 milliseconds is shown in the Figure.
15. Diffraction and Incoherent Reflectors - See Item 9 above.
16. Sonar Equation Processing - This column presents the solutions for the
bottom loss and the input variables used in the computation of the bottom
loss. Each variable is labeled. The average bottom loss (ABL) is the mean
bottom loss for all traces in all subfiles. Likewise, the standard deviation
bottom loss is over all traces for all subfiles.
All processed data including bottom loss, travel time to picked layers, and
reflection sign values are stored in ACSII data for processing at a later time.
A3.6.2 ACRS Full Wave Envelope Display
Figure A3.6-2 is the second ACRS display used for layer identification. Item (1)
is the normal half wave cross-section as shown on the left hand portion of the Figure.
Item (2) is the same data displayed as a full wave rectified envelope traces. The
individual traces are constructed by full wave rectifying the seismic trace (moving the
negative signals to the positive side of the trace) and then connecting the peaks of this
resultant signal. The latter being referred to as the envelope.
All other parameters on Figure A3.6-2 are identical to the data presented in Figure
A3.6-1 and have not been reproduced on Figure A3.6-2.
A3-8
-------
D.12117\P"
0
15.5-
.DAT
2 | 3 | 4
RER D:\ACOU'vqc\R27QEC02,ASC
01 2345
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sdBL- 4.5756
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ACRS Full Wave Envelope Display
Fi gure A3 . 6-2
-------
The full wave envelope is helpful in confirming layer identification. It also is an
excellent confirmation of the acoustic complexity of the bottom due to spatial variance.
A3.7 Diffraction Examples
Diffractions are caused by the combination of wide beam patterns on the seismic
systems and very hard concentrated reflection targets (rocks). The Trenton Channel hard
pan consisted of compact clay, sand and rocks of various sizes. These rocks on the
surface of the hard pan generated diffraction patterns across the seismic record.
Figure A3.7-1 illustrates how the diffraction pattern is generated by a wide beam
pattern source as the ship moves across a hard target. The top portion of the figure shows
the ship in three positions. Position 1 is when the beam pattern first intersects the hard
target (rock). Because the reflection from the rock is so hard, the reflection is high even
though it is on the fringe of the beam pattern. Position 2 shows the ship directly over the
target, and Position 3 shows the ship with the back end of the beam pattern just leaving
the target.
The bottom portion of Figure A3.7-1 shows a simplified seismic cross-section
generated as the ship moves over the target. The normal bottom is shown which
replicates the true bottom, and the diffraction pattern generated because of the hard target
is also shown. In many cases of Trenton Channel there were many rocks on the bottom
making a noise pattern of diffraction patterns. The top of the diffraction pattern will be of
course the top of the hard pan for the Trenton Channel. This information was used to
confirm the hard pan during interpretation.
In a normal harbor survey that does not exhibit high spatial variations, the data
can be stacked which suppresses the diffraction patterns. This could not be undertaken in
the Trenton Channel because of the high spatial variance. Another, more expensive
solution for minimizing diffraction patterns is to use much narrower beam patterns.
However, the low frequencies involved when doing subbottom profiling has prohibited
using these narrow beam patterns because of high cost of large arrays. Consideration
should be given to these narrower beam patterns to aid in resolving the bottom because of
spatial variation observed when encountering contaminated sediments.
A3.8 Envelope Layer Detection
The resolution of thin layers can be aided through wave form envelope analysis.
A thin layer is defined as any layer whose thickness converted to travel time is thinner
than the transmit wavelet. This section will review the generation of the trace envelope
and illustrate the resulting envelopes from a thick and thin layer.
Figure A3.8-1 illustrates the calibrate source wavelet for 7 KHz used for the
Trenton Channel survey. The travel time length of the wavelet is approximately 1
millisecond that corresponds to a normal minimum layer resolution of 0.75 meters. This
A3-10
-------
SHIP POSITION 1
SHIP POSITION 2
SHIP POSITION 3
Water Surface
3>
DJ
i
SPHERICAL
WAVE FRONT
VERY HARD
REFLECTOR
Bottom
TT1 I I IN I I I I I
Trigger 0
Bottom
DIFFRACTION PATTERN
PHYSICAL MODEL
SEISMIC CROSS-SECTION
CAULFIELD ENGINEERING
TITIE:
DIFFRACTION EXAMPLE
DRN BY.
H.V.
JOB NO:
2117
SCA1C:
DRAWNC NO:
DATE:
24/3/97
CADD Fill:
Figure A3.7-1
-------
10r
7KHz Reference Signal
en
"o
"5.
< -2
-6-
-8
-10
10
Time (ms)
7 KHz Reference Wavelet
Figure A3.8-1
-------
wavelet is the reference signal employed in the generation of the correlation displays in
the ACRS routines.
A simulated seismic trace, Figure A3.8-2, was constructed by convoluting the
reference wavelet with ideal reflecting layers shown on the bottom of this Figure. Note
that the signal peaks about 1.5 wavelengths from its onset. For interpretation purposes, a
one (1) wave length shift from the peak to the actual bottom travel time was employed
and is noted in the text. See Figure 17 of the main report.
For the next step in preparation for the generation of the signal envelope, the
seismic trace is full wave rectified as illustrated in Figure A3.8-3. As can be seen from
this Figure the full wave rectified trace is constructed by moving the negative portion of
the signal to the positive side of the trace.
Figure A3.8-4 illustrates the trace envelope that can be derived from the rectified
trace by either low pass filtering (the technique employed here) or by peak detection.
These techniques are well established and are used in AM radio signal detection. It is
clear that for this Case 1, a 2.25 meter thick layer, that the layers are identified and do not
overlap.
The same procedure was used for a 0.33 meter thick layer (approximately 1 foot),
Case 2, and the results from the envelope detection for these two layers is shown in
Figure A3.8-5. As can be seen from this Figure a resolution of even 0.5 feet is not
unreasonable. This technique was employed to aid in the resolution of overlapping
layers. The ACRS correlation program could not employ these techniques as the prime
purpose of the ACRS program was to recover the reflection sign. For these overlapping
layers the sign computations are uncertain with the present program. Project time was not
available to fully automate the procedures discussed here into the ACRS program.
A3-13
-------
10
Reflection Signal from 2 Layers 2.25 meters Separation
I ฐ
Q.
-2-
-6
-8
layer
layer 2
-10
Time (ms)
10
15
Simulated Seismic Trace from Ideal Reflectors
Figure A3.8-2
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10
Full Wave Rect. Signal from 2 Layers 2.25 Meters Separation
8r
2 >
45 o
a.
I -2-
-6r
-8
layer 1
layer 2
-10
10
Time (ms)
Trace Full Wave Rectification
15
Figure A3.8-3
-------
10
8r
6-
o
I ฐ
"5.
< -2
-8
-10'
Envelope Rect. Signal from 2 Layers 2.25 Meters Separation
layer 1
layer 2
10
Time (ms)
Trace Envelope - Case 1
Figure A3.8-4
15
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Envelope Rect. Signal from 2 Layers 0.33 Meters Separation
10
8-
o
I
"a.
< -2
-10
layer 1
-8 h I layer 2
0 5 10 15
Time (ms)
Trace Envelope - Case 2
Figure A3.8-5
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EPA 905/R-99/003 Mar. 1999
c.l
Micro survey: acoustic core and physical core
inter-relationship with spatial variation, Trenton
Channel of the Detroit River
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