-===
    Pro'fessional Service Industries
    =======================
    It
    is to be noted that, whereas the test borings are drilled and sampled by experienced
    drillers, it is sometimes difficult to record changes in stratification within narrow limits.
    In the absence
    of foreign substances, it is also difficult to distinguish between discolored
    soils and clean soil fill.
    Soil Conditions
    Boring B-1 - The subsurface soil conditions consist
    of an upper stratum of fine sand,
    an intermediate stratum of clayey sand, and a deeper stratum of silty clay.
    From the mudline
    to an approximate depth of six (6) feet, an upper stratum of
    medium sand with shells was encountered. Standard penetration values (N) obtained within
    these soils ranged from one (1) to four (4) blows per foot. These soils are non-plastic and
    contain between 12 and
    23 percent silt and clay size particles as indicated by minus #200
    sieve tests.
    From six (6) feet below the mudline, to a depth
    of 7.5 feet, an intermediate stratum
    of clayey sand was encountered. A standard penetration value (N) obtained within these
    soils
    was two (2) blows per foot. These soils contain approximately 42 percent silt and clay
    size particles as indicated by minus
    #200 sieve tests.
    From 7.5 feet below the mudline and extending
    to a depth of nine (9) feet, a stratum
    of silty clay was encountered. A standard penetration value (N) obtained within these soils
    was four (4) blows per foot. These soils are high in plasticity as indicated by an Atterberg
    limit test. The tested liquid limit was 53 percent and plasticity index
    (PI) was 31. These
    soils contain approximately 22 percent sand size particles as indicated by a minus
    #200 sieve
    test.
    Boring B-2 - The subsurface soil conditions consist
    of an upper stratum of fme sand,
    intermediate strata
    of clayey sand and silty clay, and a deeper stratum of sandy clay.
    From the mudline
    to
    an approximate depth of six (6) feet, an upper stratum of fine
    sand was encountered. Standard penetration values (N) obtained within these soils ranged
    from zero (0) to one (1) blow per foot. These soils are non-plastic and contain between five
    (5) and 14 percent silt and clay size particles as indicated by minus #200 sieve tests.
    From six (6) feet below the mudline, to a depth
    of 10.5 feet, intermediate strata of
    clayey sand and silty clay were encountered. Standard penetration values (N) obtained
    within these soils ranged from one (1)
    to
    11 blows per foot. These soils are low in
    plasticity as indicated by Atterberg limit tests. Liquid limits ranged from 24 to 27 percent
    and plasticity indicies
    (PI) ranged from seven (7) to 12.
    5
    ,.
    ,.

    ,.
    "
    Professional Service Industries
    =========================
    From 10.5 feet below the mudline and extending to a depth of 13.5 feet, a stratum
    of sandy clay was encountered. Standard penetration values (N) obtained within these soils
    averaged
    10 blows per foot. These soils are low in plasticity as indicated by Atterberg limit
    test. The tested liquid limit was 34 percent and plasticity index
    (PI) was 13. These soils
    contain approximately
    50 percent sand size particles as indicated by a minus #200 sieve test.
    Boring B-3 - The subsurface soil conditions consist
    of a stratum of silty clay.
    From the mudline
    to an approximate depth of 10.5 feet, an upper stratum of silty
    clay was encountered. Standard penetration values
    (N) obtained within these soils ranged
    from zero
    (0) to 11 blows per foot. These soils are high in plasticity as indicated by
    Atterberg limit tests. Liquid limits averaged
    68 percent and plasticity indicies (PI) averaged
    29. These soils contain between one
    (1)
    and eight
    (8)
    percent sand size particles as
    indicated by minus
    #200 sieve tests.
    Boring
    B-4
    - The subsurface soil conditions consist
    of an upper stratum of clayey
    sand and fme sand and a deeper stratum
    of silty clay.
    From the mudline to an approximate depth
    of six (6) feet, an upper stratum of clayey
    sand and fine sand
    was encountered. Standard penetration values (N) obtained within these
    soils ranged from zero
    (0) to three (3) blows per foot. These soils are generally non-plastic
    and contain between one
    (1) and 34 silt and clay size particles as indicated by minus #200
    sieve tests.
    From six
    (6) feet below the mudline and extending, a stratum of silty clay was
    encountered. Standard penetration values
    (N) obtained within these soils ranged from seven
    (7) to 12 blows per foot These soils are high in plasticity as indicated by an Atterberg limit
    test. The tested liquid limit was
    77 percent and plasticity index (PI) was 34. These soils
    contain approximately five (5) percent sand size particles as indicated
    by minus #200 sieve
    tests.
    CONTAMINATION
    ASSESSMENT
    Analytical test results indicate concentrations of Total Petroleum Hydrocarbons
    (TPH) in the four (4) composite soil samples collected from soil boring locations B-1, B-2,
    B-3, and B-4. The levels
    of TPH concentration encountered in the soil samples from soil
    boring locations B-1 and B-2 are those typically associated with the biodegradation
    of
    naturally occurring organic matter and do not represent an adverse environmental concern.
    6
    :
    "
    I
    I
    I
    !

    PROFESS. NAL SERVICE lNDUSTRll
    J
    INC.
    RECORD OF SUBSURFACE EXPLORATION
    oject Name:
    Boring:
    B-2
    1995 Marina Dredging Project
    Date of Boring:
    November 16. 1995
    S't
    ;1. B.
    T
    -
    Heads
    -
    Corous Christi
    ,
    Texas
    Pro'ect
    J
    No
    ..
    .
    326
    -
    55415
    DESCRIPTION
    DEPTH
    SAMPLE
    N
    Qu
    Qp
    He
    REMARKS
    SURFACE
    -
    -
    -
    f- Water
    -
    -
    I-
    -
    -
    f-
    -
    -
    Mudline
    =
    5 feet below water surface
    I
    5
    I
    I
    r- FINE/MEDIUM SAND, tanish gray, wet, very loose.
    -
    SS-l
    WH
    26.6
    -#200=5X
    -
    I-
    -
    -
    SS-2
    WR
    25.2
    -#200=7l:
    f-
    -
    r-
    Same as above, some clay.
    -
    SS-3
    WH
    23.5
    -#20D=14X
    -
    I
    FINE/MEDIUM SAND, gray. wet, very loose.
    10
    I
    SS-4
    1
    24.9
    -#20D=10X
    I
    1---
    -
    r-
    CLAYEY SAND,
    gray, very moist, very
    loose,
    CSC).
    -
    SS-5
    1
    0.5
    37.3
    ll=27l:
    -
    \
    PI=12
    ,...
    -
    -
    SILTY CLAY, with sand, gray, very moist, stiff.
    SS-6
    11
    1.0
    33.1
    -
    -#200=37l:
    -
    I
    SANDY
    CLAYEY
    CLAY,
    SAND,
    grayish
    gray. very
    tan,
    moist,
    moist,
    loose,
    stiff.
    eSC).
    15
    I
    -
    SS-7
    SS-8
    10
    8
    0.25
    2.25 21.5
    19.4
    PI=7
    ll=24X
    I
    -
    -
    -
    -#200=50:1
    - Same as above, cel).
    -
    SS-9
    10
    2.5
    20.7
    ll=34X
    PI=13
    -
    -
    Total Depth of Boring
    =
    18.5 ft below water surface
    -
    -
    I
    WH = Weight of Hammer
    WR = Weight of Rod
    20
    I
    I
    -
    -
    -
    -
    -
    -
    -
    -
    -
    -
    -
    -
    I
    I
    I
    I-
    -
    -
    f-
    -
    -
    I-
    -
    -
    I-
    -
    -
    I
    I
    I
    -
    -
    -
    .'-
    -
    -
    -
    -
    -
    -
    -
    -

    PSl/Corpus Christi
    385-5P196-0024
    Page 6 of 17
    ~A~
    d: 11160-02
    BASEINEUTRAL ANO ACID EXTRACT ABLES BY
    GC/MS
    Slient 10:'
    B-2 Compo
    Matrix: Soil
    ~nalyte
    Results
    Units
    Method
    MOL/OF.
    :lASE NEUTRAL EXTRACTABLES
    N-Nitrosodimethylamine
    <330
    uglkg
    SW 8270
    330/1
    9is (2-chloroethyl) ether
    <330
    uglkg
    SW 8270
    330/1
    1,3-Dichlorobenzene
    <330
    uglkg
    SW 8270
    330/1
    Extraction Date:
    lA-Dichlorobenzene
    <330
    uglkg
    SW 8270
    330/1
    11120/95
    Benzyl alcohol
    <330
    uglkg
    SW B270
    330/1
    Analysis Date:
    1,2-Dichlorobenzene
    <330
    ug/kg
    SW 8270
    330/1
    11122/95
    3is (2-chloroisopropyl) ether
    <330
    ug/kg
    SW 8270
    330/1
    Analyst: SP
    N-Nitroso di-n-propyl amine
    <330
    ug/kg
    SW 8270
    330/1
    Hexachloroethane
    <330
    ug/kg
    SW 8270
    330/1
    Nitrobenzene
    <330
    ug/kg
    SW 8270
    330/1
    Isophorone
    <330
    ug/kg
    SW 8270
    330/1
    Bis (2-choloroethoxy) methane
    <330
    ug/kg
    SW 8270
    330/1
    1,2,4- Trichlorobenzene
    <330
    uglkg
    SW 8270
    330/1
    Naphthalene
    <330
    ug/kg
    SW 8270
    33011
    4-Chloroaniline
    <330
    ug/kg
    SW 8270
    33011
    Hexachlorobutadiene
    <330
    ug/kg
    SW 8270
    330/1
    2-Methylnaphthalene
    <330
    uglkg
    SW 8270
    330/1
    Hexachlorocyclopentadiene
    <330
    ug/kg
    SW 8270
    330/1
    Iloronaphthalene
    <800
    uglkg
    SW 8270
    80011
    2-I .... jtroaniline
    <330
    ug/kg
    SW 8270
    330/1
    Dimethylphthalate
    <330
    uglkg
    SW 8270
    330/1
    2,4-Dinitrotoluene
    <330
    uglkg
    SW 8270
    330/1
    Acenaphthylene
    -::330
    ug/kg
    SW 8270
    33011
    3-Nitroaniline
    <800
    uglkg
    SW 8270
    80011
    Acenaphthene
    <330
    uglkg
    SW 8270
    330/1
    Dibenzofuran
    <330
    uglkg
    SW 8270
    33011
    2,6-Dinitrotoluene
    <330
    uglkg
    SW 8270
    330/1
    Fluorene
    <330
    uglkg
    SW 8270
    330/1
    4-Chloro phenyl phenyl ether
    <330
    uglkg
    SW 8270
    33011
    4-Nitroaniline
    <800
    uglkg
    SW 8270
    800/1
    Diethyl phthalate'
    <330
    uglkg
    SW 8270
    330/1
    Di-n~Butylphthalate
    <330
    uglkg
    SW 8270
    330/1
    N-Nitrolsodiphenylamine
    <330
    uglkg
    SW 8270
    330/1
    . 4-Bromo phenyl phenyl ether
    <330
    uglkg
    SW 8270
    330/1
    Hexachlorobenzene
    <330
    ug/kg
    SW 8270
    330/1
    Phenanthrene
    <330
    uglkg
    SW 8270
    330/1
    Anthracene
    <330
    uglkg
    SW B270
    330/1
    Fluoranthene
    <330
    uglkg
    SW 8270
    330/1
    Pyrene
    <330
    uglkg
    SW 8270
    330/1
    Butylbenzyl phthalate
    <330
    uglkg
    SW 8270
    330/1
    Benzo (a) anthracene
    <330
    uglkg
    SW 8270
    330/1
    Chrysene
    <330
    uglkg
    SW 8270
    330/1
    Bis (2-ethylhexyl) phthalate
    <330
    ug/kg
    SW B270
    330/1
    - T-Dichlorobenzedine
    <330
    uglkg
    SW 8270
    330/1
    . n-Octylphthalate
    <330
    ug/kg
    SW 8270
    330/1
    Benzo- (b)
    fluor~nthene
    <330
    ug/kg
    SW 8270
    330/1
    tllsil
    (continued)

    PSl/Corpus Christi
    385-5P196-0024
    Page 7 of 17
    LAu #:
    111 60-02
    BASE/NEUTRAL AND ACID EXTRACTABLES BY GCIMS (cont.)
    Slient 10: B-2 Compo
    Matrix: Soil
    Analvte
    Results
    Units
    Method
    MOL/OF
    BASE
    NEUTRAL EXTRACTABLES
    Benzo (k)
    fluoranthene
    <330
    ug/kg
    SW 8270
    330/1
    8enzo- (a) pyrene
    <330
    ug/kg
    SW 8270
    330/1
    Indo (1 ,2,3-cd) pyrene
    <330
    ug/kg
    SW 8270
    330/1
    Dibenzo (a,h) anthracene
    <330
    ug/kg
    SW
    8270
    33D/1
    Senzo (g,h,i) perylene
    <330
    ug/kg
    SW 8270
    330/1
    ACID EXTRACTABLES
    Phenol
    <330
    ug/kg
    SW 8270
    330/1
    2-Chlorop.henol
    <330
    ug/kg
    SW 8270
    330/1
    2-Methylphenol
    <330
    ug/kg
    SW 8270
    330/1
    4-Methylphenol
    <330
    ug/kg
    SW 8270
    330/1
    2-Nitrophenol
    <330
    ug/kg
    SW 8270
    330/1
    2A-Oimethylphenol
    <330
    ug/kg
    SW 8270
    330/1
    Benzoic acid
    <330
    ug/kg
    SW 8270
    330/1
    2A-Oichlorophenol
    <330
    ug/kg
    SW 8270
    330/1
    4-Chloro-3-methylphenol
    <330
    ug/kg
    SW 8270
    330/1
    6-Trichlorophenol
    <330
    ug/kg
    SW 8270
    330/1
    2,4,5- Trichlorophenol
    <330
    ug/kg
    SW 8270
    330/1
    2A-Oinitrophenol
    <800
    ug/kg
    SW 8270
    800/1
    4-Nitrophenol
    <800
    ug/kg
    SW
    8270
    800/1
    4,6-Dinitro-2-methyl phenol
    <800
    ug/kg
    SW 8270
    800/1
    Pentachlorophenol
    <800
    ug/kg
    SW 8270
    800/1
    PESTICIDES
    Alpha-BHC
    <330
    ug/kg
    SW 8270
    330/1
    8eta-BHC
    <330
    ug/kg
    SW 8270
    330/1
    Gamma-BHC
    <330
    ug/kg
    SW
    8270
    330/1
    Delta-BHC
    <330
    ug/kg
    SW 8270
    330/1
    Heptachlor
    <330
    ug/kg
    SW 8270
    330/1
    Aldrin
    <330
    ug/kg
    SW 8270
    330/1
    Heptachlor epoxide
    <330
    ug/kg
    SW 8270
    330/1
    Endosulfan I
    <330
    ug/kg
    SW 8270
    330/1
    Dieldrin
    <330
    ug/kg
    SW 8270
    330/1
    .4A'-DOE
    <330
    ug/kg
    SW 8270
    330/1
    Endrin
    <330
    ug/kg
    SW 8270
    330/1
    Endosulfan II
    <330
    ug/kg
    SW 8270
    330/1
    4A'-DDD
    <330
    ug/kg
    SW 8270
    330/1
    Endrin aldehyde
    <330
    ug/kg
    SW 8270
    330/1
    Endosulfan. sulfate
    <330
    ug/kg
    SW 8270
    330/1
    4A'-DDT
    <330
    ug/kg
    SW 8270
    330/1
    irin Ketone
    <330
    ug/kg
    SW 8270
    330/1
    4
    tho
    xychlor
    <330
    ug/kg
    SW 8270
    330/1
    ln~;l
    I!!."".

    _~
    . .': 111 60-02
    ::;lient 10: B-2 Camp.
    \nalyte
    lenzene
    ~oluene
    =thylbenzene
    Total Xylenes
    rotal VOAs
    .v1TBE
    o.nalyte
    Total Recoverable
    Petroleum Hydrocarbons
    Analyte
    Total Arsenic
    T
    -I Barium
    1.
    .1
    Cadmium
    Total Chromium
    Total Lead
    Total Mercury
    Total Selenium
    Total Silver
    Results
    <10
    <10
    <10
    <10
    <10
    <10
    Results
    16.0
    Results
    <0.6
    12
    <0.6
    1.9
    5.00
    <0.02
    <0;6
    <1.00
    PSI/Corpus Christi
    385-5P196-0024
    Page 5 of 17
    PURGEABLE AROMATICS
    Matrix: Soil
    LOW LEVEL
    Units
    Method
    MOL/OF
    ug/kg
    SW 8020
    1011
    Extraction Date:
    ug/kg
    SW 8020
    1011
    NA
    ug/kg
    SW 8020
    1011
    Analysis Date:
    ug/kg
    SW 8020
    10/1
    11/28/95
    ug/kg
    SW 8020
    -/-
    Analyst: WH
    ug/kg
    SW 8020
    1011
    Units
    Method
    Analysis Date
    Analyst
    MOL
    mg/kg
    EPA418.1
    11/20/95
    RM
    10.0
    METALS ANALYSIS
    Units
    Method
    Analysis Date
    Analyst
    mg/kg
    SW 7060
    11/22/95
    MC
    mg/kg .
    SW 7080
    11/27/95
    JS
    mg/kg
    SW 7130
    11/20/95
    JS
    mg/kg
    SW 7190
    11/20/95
    JS
    mg/kg
    SW 7420
    11/21/95
    JS
    . mg/kg
    SW 7471
    11/27/95
    JS
    mg/kg
    SW 7740
    11/22/95
    MC
    mg/kg
    SW 7760
    11/22/95
    JS

    PROFESS. NAL SERVICE lNDUSTRll
    J
    INC.
    RECORD OF SUBSURFACE EXPLORATION
    oject Name:
    Boring:
    B-2
    1995 Marina Dredging Project
    Date of Boring:
    November 16. 1995
    S't
    ;1. B.
    T
    -
    Heads
    -
    Corous Christi
    ,
    Texas
    Pro'ect
    J
    No
    ..
    .
    326
    -
    55415
    DESCRIPTION
    DEPTH
    SAMPLE
    N
    Qu
    Qp
    He
    REMARKS
    SURFACE
    -
    -
    -
    f- Water
    -
    -
    I-
    -
    -
    f-
    -
    -
    Mudline
    =
    5 feet below water surface
    I
    5
    I
    I
    r- FINE/MEDIUM SAND, tanish gray, wet, very loose.
    -
    SS-l
    WH
    26.6
    -#200=5X
    -
    I-
    -
    -
    SS-2
    WR
    25.2
    -#200=7l:
    f-
    -
    r-
    Same as above, some clay.
    -
    SS-3
    WH
    23.5
    -#20D=14X
    -
    I
    FINE/MEDIUM SAND, gray. wet, very loose.
    10
    I
    SS-4
    1
    24.9
    -#20D=10X
    I
    1---
    -
    r-
    CLAYEY SAND,
    gray, very moist, very
    loose,
    CSC).
    -
    SS-5
    1
    0.5
    37.3
    ll=27l:
    -
    \
    PI=12
    ,...
    -
    -
    SILTY CLAY, with sand, gray, very moist, stiff.
    SS-6
    11
    1.0
    33.1
    -
    -#200=37l:
    -
    I
    SANDY
    CLAYEY
    CLAY,
    SAND,
    grayish
    gray. very
    tan,
    moist,
    moist,
    loose,
    stiff.
    eSC).
    15
    I
    -
    SS-7
    SS-8
    10
    8
    0.25
    2.25 21.5
    19.4
    PI=7
    ll=24X
    I
    -
    -
    -
    -#200=50:1
    - Same as above, cel).
    -
    SS-9
    10
    2.5
    20.7
    ll=34X
    PI=13
    -
    -
    Total Depth of Boring
    =
    18.5 ft below water surface
    -
    -
    I
    WH = Weight of Hammer
    WR = Weight of Rod
    20
    I
    I
    -
    -
    -
    -
    -
    -
    -
    -
    -
    -
    -
    -
    I
    I
    I
    I-
    -
    -
    f-
    -
    -
    I-
    -
    -
    I-
    -
    -
    I
    I
    I
    -
    -
    -
    .'-
    -
    -
    -
    -
    -
    -
    -
    -

    PSl/Corpus Christi
    385-5P196-0024
    Page 6 of 17
    ~A~
    d: 11160-02
    BASEINEUTRAL ANO ACID EXTRACT ABLES BY
    GC/MS
    Slient 10:'
    B-2 Compo
    Matrix: Soil
    ~nalyte
    Results
    Units
    Method
    MOL/OF.
    :lASE NEUTRAL EXTRACTABLES
    N-Nitrosodimethylamine
    <330
    uglkg
    SW 8270
    330/1
    9is (2-chloroethyl) ether
    <330
    uglkg
    SW 8270
    330/1
    1,3-Dichlorobenzene
    <330
    uglkg
    SW 8270
    330/1
    Extraction Date:
    lA-Dichlorobenzene
    <330
    uglkg
    SW 8270
    330/1
    11120/95
    Benzyl alcohol
    <330
    uglkg
    SW B270
    330/1
    Analysis Date:
    1,2-Dichlorobenzene
    <330
    ug/kg
    SW 8270
    330/1
    11122/95
    3is (2-chloroisopropyl) ether
    <330
    ug/kg
    SW 8270
    330/1
    Analyst: SP
    N-Nitroso di-n-propyl amine
    <330
    ug/kg
    SW 8270
    330/1
    Hexachloroethane
    <330
    ug/kg
    SW 8270
    330/1
    Nitrobenzene
    <330
    ug/kg
    SW 8270
    330/1
    Isophorone
    <330
    ug/kg
    SW 8270
    330/1
    Bis (2-choloroethoxy) methane
    <330
    ug/kg
    SW 8270
    330/1
    1,2,4- Trichlorobenzene
    <330
    uglkg
    SW 8270
    330/1
    Naphthalene
    <330
    ug/kg
    SW 8270
    33011
    4-Chloroaniline
    <330
    ug/kg
    SW 8270
    33011
    Hexachlorobutadiene
    <330
    ug/kg
    SW 8270
    330/1
    2-Methylnaphthalene
    <330
    uglkg
    SW 8270
    330/1
    Hexachlorocyclopentadiene
    <330
    ug/kg
    SW 8270
    330/1
    Iloronaphthalene
    <800
    uglkg
    SW 8270
    80011
    2-I .... jtroaniline
    <330
    ug/kg
    SW 8270
    330/1
    Dimethylphthalate
    <330
    uglkg
    SW 8270
    330/1
    2,4-Dinitrotoluene
    <330
    uglkg
    SW 8270
    330/1
    Acenaphthylene
    -::330
    ug/kg
    SW 8270
    33011
    3-Nitroaniline
    <800
    uglkg
    SW 8270
    80011
    Acenaphthene
    <330
    uglkg
    SW 8270
    330/1
    Dibenzofuran
    <330
    uglkg
    SW 8270
    33011
    2,6-Dinitrotoluene
    <330
    uglkg
    SW 8270
    330/1
    Fluorene
    <330
    uglkg
    SW 8270
    330/1
    4-Chloro phenyl phenyl ether
    <330
    uglkg
    SW 8270
    33011
    4-Nitroaniline
    <800
    uglkg
    SW 8270
    800/1
    Diethyl phthalate'
    <330
    uglkg
    SW 8270
    330/1
    Di-n~Butylphthalate
    <330
    uglkg
    SW 8270
    330/1
    N-Nitrolsodiphenylamine
    <330
    uglkg
    SW 8270
    330/1
    . 4-Bromo phenyl phenyl ether
    <330
    uglkg
    SW 8270
    330/1
    Hexachlorobenzene
    <330
    ug/kg
    SW 8270
    330/1
    Phenanthrene
    <330
    uglkg
    SW 8270
    330/1
    Anthracene
    <330
    uglkg
    SW B270
    330/1
    Fluoranthene
    <330
    uglkg
    SW 8270
    330/1
    Pyrene
    <330
    uglkg
    SW 8270
    330/1
    Butylbenzyl phthalate
    <330
    uglkg
    SW 8270