HomeMy WebLinkAboutNCD003200383_19870527_Koppers Co. Inc._SERB PA SI_Site Inspection Report - Part II (References)-OCRKEYSTONE
['.\\'lROS~tESTAL Rl-::SOLRC[S, 1:--,:c.
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436 Seventh Avenue, Suite 1940, Pinsburgh. PA 15219
CERTIFIED l'iAIL-RETURII RECEIPT REQUESTED
Dear l·lr. Berry: )
January 6, 1937
State of llorth Carolina
Dept. of llatural Resources and ·
Comr.1unity Development
3800 Barrett Drive
P.O. 8ox 27687
Raleigh, llorth Carolina 27611-7637
ATTEIITION: MR. E.L. BERRY
SUBJECT: Jionitori ng ·Well Construction P.ermit
'9l-0255°v/llc0236 r·
On October 27, 1986, your office issued the above-referenced permit to
Koppers Co., Inc. for construction of monitoring wells at our facility
in \•!ake County, 1/orth Carolina. These 1·1ells t·1ere constructed by
Wilson Engineering Associates under the supervision of Steven A. Colton.
'. huve cnclc~-ed the foll01·1ing infornation <:oncerning these 11ells:
o Well Construction Records (using Form GW-1).
o \·!e 11 Boring Logs.
o Analytical results of soil and groundwater samples.
If you have any questions on this subject, please contact me at this office.
Thank you for your cooperation in this matter.
1-ii1S/bj
Enclosure
cc: J. R. Campbell
S. Colton
C. Cramer
1·1/0 attachments
Sincerely yours,
ilartin IL Schlesinger
Assistant Pro9ram 11anager
Previously Operated Properties
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I KEYSTONE
EN\'IRONMENTAL RF.SOURCES, INC.
Ref. 8 , Encl. 1 ,
I 440 College Park Dr., Monroe,ille, PA 15146 ----------------
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I NORTH CAROLINA DEPARTMENT OF NATURAL RESOURCES ANO COMMUNITY DEVELOPMENT
DIVISION OF ENVIRONMENTAL /v4.ANAGEMENT -GROUNDWATER SECTION
P.O. BOX 27687 -RALEIGH,N.C. 27611, PHONE (919) 733-5083
FOR OFFICE USE ONL y
Quad. No. _______ Serial No. ___ _
I . WELL CONSTRUCTION RECORD
IDRILLING CONTRACTOR W,/so" [.,,311,e~r, ... ) Assoc,~tes
rRILLER REGISTRATION NUMBER __ .:c.g..::.~-1-'------
1. WELL LOCATION: (Show sketch of the location below)
I Nearest Town: JVlo,-r,sv,lf~) ;V C.
Ko ooers Roa.cl, Mar,.,s v,lk.
(Road.Community, or S~bdivision and Lot No.}
I. owNER /'(oppers Co . .r ... c..
ADDRESS tn3ineereJ WoqJ S,,sfe;,,,S,R,t:.5'f
,M Il g (Street or Ro~te No.) ' _orr,sv1 c. ;v.c I City pr Town State Zip Code
3. DATE DRILLED 'R/J/P6 usE OF WELL Monitor,~.,
I TOTAL DEPTH 25" CUTTINGS COLLECTED @°Yes □ No
. DOES WELL REPLACE EXISTING WELL? 0 Yes [i;YNo
6. STATIC WATER LEVEL: /3.30 FT. 0 above TOP OF CASING o t.Ybelow · I TOP OF CASING IS /. 0 FT. ABOVE LAND SURFACE .
... YIELD (gpm): ______ METHOD OF TEST _______ _
8 WATER ZONES (deoth): -----------------
9. CHLORINATION: Type Amount
.I CASING:
From
I From
From
Depth
____ To 0
Diameter
Wall Thickness
or Weight/Ft.
2" FL-'=---
____ To ___ Ff. ___ _
----TO---FL----
Material
PVC
I. GROUT:
Depth Material Method
From _o __ To_2 __ FL Ce..,.,ent -t-6enfon,te Powder
I From _2..=-_ To 't FL Seo.I -Be~tor1e. Pel/efs
.•. SCREEN:
I Depth Diameter Slot Size Material·
From_5=-_To 25° Ft. 2 in.0.010 in. PVC
FrJm ____ To ___ Ft. ____ in. ___ in.
l From To ___ Ft. ____ in. ___ in.
! , . GRAVEL PACK:
II Depth Size
'f To 2 S-Ft. -~6~'-' __ From
Material
50.,..J.
From ____ To ___ . Ft. _____ _
Lat. _______ long. ____ Pc __
Minor Basin ____________ _
Basin Code ____________ _
Header Ent. _______ GW-1 Ent.-
STATE WELL CONSTRUCTION
PERMIT NUMBER: 'II -02.~5"-w'M-02.3b
County: Wc.,,Ke
Depth DRILLING LOG
From To Formation Descriotion
If adCitional space is needed use back of :crm.
LOCATION SKETCH
(Show direc!ion and distance from at least two State Roads,
or other map reference points)
See
=
1· REMARKS:-------------------------------------------
1 DO HEREBY CERTIFY THAT THIS WELL WAS CONSTRUCTED IN ACCORDANCE WITH 15 NCAC 2C. WELL CONSTRUCTION
STANDARDS. AND THAT A COPY OF THIS RECORD H EEN PRO.)llDED?,) Jj,_fWELL OWNER.
U. (~ 12 23 26
SIGNATURE OF CONTRACTOR OR AGENT DA TE
GW· 1 Revised 11/84 Submit original to Division al Environmental Management and copy to well owner.
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I MONITORING WELL LOG
PROJECT Ralkigh, NC WELL NO. MW-1
I S. A. Colton DRILLING METHOD Hollow Stem Auger GEOLOGIST I ----
DRILLER Soil Testing Services DATE 8/7/86
I
GROUND ELEVAl\ION
TOP OF WELL.---'------
DEPTH OF WELL\ (ft)
GROUND WATER DEPTH (ft):
AT COMPLETION -----
AFTER HOURS
I CASING MATERitL 2" PVC SCREEN 20' of 0.010" slots
STRAT SAMPLE I
DEPTH DEPTH DESCRIPTION
Brown, clayey SILT, tr f sand, tr weathered rock
fragments, tr m quartz fragments, tr roots (0-1.5')
Mottled Brown and gray silty CLAY, tr f sand,
tr f rock fragments.
I Red/brown Clayey SILT (weathered bedrock), tr
kiltstone fragments, tr f sand
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Bottom of Boring -26.5 feet
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GRAVEL PACK
BENTONITE
BACK FILL
CONCRETE ':'!."':.\ ~ :..1,
· SCREEN ----------
CONSTRUCTION
... :
·.•·: ... . '
... ','
''
: .:
•',.
SHEET OF
·•,·
,•,•
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I I NORTH CAROLINA DEPARTMENT OF N~ nJRAL RESOURCES AND COMMUNITY DEVELOPMENT
DIVISION OF ENVIRONMENTAL MA.NAGEMENT -GROUNDWATER SECTION
I
P.O. BOX 27667 -AALEIGf'-N.C. 27611, PHONE (919) 733-5063
r------------,~ FOR OFFICE USE ONL y
Quad. No. _______ Serial No. ___ _
I WELL CON~TRUCTION RECORD
lRILLING CONTRACTOR \.v; )So" [ .-iB I neet,n) A 5S o, I ~te S
'RILLER REGISTRATION NU~BER __ _::g..:.~:_I..:._ ____ _
1. WELL LOCATION: (Show sketch t the location below)
I Nearest Town: ;V\o.-r1s v,ift:) JV C.
/:iopners R.oa.d., /Vlorhsv,lk.
(Road, Community, or S~bdivision land Lot No.)
I OWNER /'(oppers Co. Xnc.,
ADDRESS f: ri31neere.t. W'oqJ 5vsfe.M s. R,t. 5'f
/1/1 //" (Street or R~te No.) ✓ . ~orr,sv, c. I !:!:...C.
'
City or/ Town I State Zip Code
DATE DRILLED sh, U, USE OF WELL Mon;tor,~:1 rt I ;;t
I TOTAL DEPTH 2'f:. 5 CUTTINGS COLLECTED @'Yes □ No
DOES WELL REPLACE EXISTING 0ELL? 0 Yes G2"No
6. STATIC WATER LEVEL: ,,;.oo I FT. □ above TOP OF CASING,
I ul'below
'
TOP OF CASING IS ~2,..__-;
1
-FT. ABOVE LAND SURFACE.
YIELD (gpm): METHOD OF TEST i WATER ZONES (deoth); ---~\ ____________ _
9. CHLORINATION: Tyoe ___ .,.I __
I CASING:
From
I From
From
I GROUT:
From
Depth
~Q~_To s-
Amount
Diameter
--, JI
Wall Thickness
or Weight/Ft.
]'-..... =---
----TO ---~'----
----TO Fl.----
Material
p Ve:
Depth Material Method
I From
"'· SCREEN:
0 To__;_2._F!'-Ce,-.,enT <t-Behfon,te Powder
2 To 'f Ft. Seo.I -Geat.,ite. Pellet's
_I Depth
From _~ __ To 2 If-
Diameter
Ft. 2
I
Slot Size Material
in.0.010 in. PVC.
FrJm ____ To ___ Ft. ____ in. ___ in. __ _
I From ____ To ___ FJ. ____ in. ___ in. __ _
I
~-GRAVEL PACK: I
Depth ! Size u. -1 From / To 21f;5 Ft. __ ..>e6c...'_' __ -~--I
Material
So.,-,d.
From ____ To ___ Ft. _____ _
Lat. Long. ____ Pc __
Minor Basin ____________ _
Basin Code ____________ _
Header Ent. _______ GW-1 Ent.-
STATE WELL CONSTRUCTION
PERMIT NUMBER: ~l-02.SS--\./'M-023!,
County:
Depth
From
Jdc...Ke
To
DRILLING LOG
Formation Description
If additional space is needed use back of form.
LOCATION SKETCH
(Show direction and distance lrom at least two State Roads,
or other mao reference points)
5ee s,te
I. REMARKS: I
I .
I DO HEREBY CERTIFY THAT THIS WELL WAS CO~ST UCTED IN ACCORDANCE WITH 15 NCAC 2C, WELL CONSTRUCTION
STANDARD_S, AND THAT A COPY OF THIS RECORD HA PROVJCJ'D TP°JT\;'f, \\'ELL OWNER. / / I c:: u. ~~ IL; 23!..Jt
SIGNATURE OF CONTRACTOR OR AGENT 'DA TE I
GW-1 Revised I 1 /84 Submit original to Division of Environmental Management and copy to we11 owner.
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I MONITORING.WELL LOG
PROJECT Ri{ieigh, NC WELL NO. MW-2
I DRILLING METHOD Hollow Stem Auger GEOLOGIST S. A. Colton
I -----'-----DRILLER Soil Testing Services DATE 8/7 /86
I GROUND ELEVATION __ _
TOP OF WELL_--'-\ ____ _
GROUND WATER DEPTH (ft):
DEPTH OF WELLl (ft)
I
CASING MATERI¼L
I
AT COMPLETION -----
AFTER HOURS
2" PVC SCREEN 19' of 0.010" slots
DESCRIPTION
Brown clayey SILT, tr f sand, tr siltstone fragments,
roots 0-1.5', 9-10.5'
Mottled gray /green/yellow /orange clayey SILT,
(weathered bedrock)
Bottom of Boring -26.5 feet
GRAVEL PACK
BENTONITE
BACK FILL
CONCRETE
· SCREEN -----
CONSTRUCT! ON
·.·.·
.:.
':,
SHEET ___ OF __ _
I . I NORTH CAROLINA DEPARTMENT OF NA1TURAL RESOURCES AND COMMUNITY DEVELOPMENT
DIVISION OF ENVIRONMENTAL MANAGEMENT -GROUNDWATER SECTION
I
FOR OFFICE USE ONL y
P.O. BOX 27687 -RAl..ElG~,N.C. 27611, PHONE {911il) 733-5083
I I WELL CONSTRUCTION RECORD
'°RILLING CONTRACTOR N )So" ["'BI ,,eef,r,) Ass QC/~ te s
'RILLER REGISTRATION NU~BER __ .:..g-"'-~-f _____ _
I .
1. WELL LOCATION: (Show sketch ol the localion below)
I Nearest Town: MO r-r15 v,ift.) ,N'. C.
fio oaer• P-.oa.d.. Morh s v,l/e
(Road~ Community, or S~bdivision land Lot No.)
lowNER K:oppers Co. X"c..
ADDRESS [ r,~11,ePreJ Wood S,,steM s, (<t. 5'f
,1;1 //; (Street or Ro~te No.) '
L!'.!.0 rr,sv• -. I !'!:._C. I I State Zip Code
3 DA TE DRILLED // 'i6 USE OF WELL /Vl On ;tor I "J
I TOTAL DEPTH /5', ' cutTINGS COLLECTED @°Yes □ No
DOES WELL REPLACE EXISTING WELL? □ Yes [id"No
6. STATIC WA TEA LEVEL: 7. 'Fr I FT. D ,above TOP OF CASING, -, I [i3""below ·I TOP OF CASING Is ---=.,_,"---'-i-FT. ABOVc cAND SURFACE .
., YIELD (gpm): METHOD OF TEST --------'--
' I WATER ZONES (dep1hl: ---~1-------------
9. CHLORINATION: Type Amount
CASING: I Depth Diameter Wall Thickness or Weight/Ft. Material
From 0 I From
,-t;" 2"
-"'----To ~-r·-=---
----To ___ 11 ___ _
PVC.
From ----To ---FL----
II GROUT: II Depth Material Method
From -~0 __ To /. ~
I From
~-SCREEN:
/. ~ To 5, ~
F( (e;viei,t ,t-/3e1-ito",te P.wder
Ft Seo.I -Be~t"iie. Pellet's
I From
Depth Diameter Slot Size Material
15': 5'" I 2 in.0.0I0 PVC. To F,t. in.
Fr.:,m ___ _ To Ft. in. in.
I From ___ _
'-3. GRAVEL PACK:
To Ft. in. in.
I
I
I Depth ! Size
From 3, 5" To ft;'_ r Ft. 6 If i--"----
Material
So...,J.
From ____ To ___ Ft.~-----
Ouad. No. _______ Serial No. ___ _
Lat. _______ Long. ____ Pc-
Minor Basin ____________ _
Basin Code~------------
Header Ent. _______ GW-1 Ent.---
STATE WELL CONSTRUCTION
PERMIT NUMBER: '11 -02.55""-l.'A-0l3!,
County: VVc:.)f e
Depth DRILLING LOG
From To Formation Description
If additional space is needed use back at form.
LOCATION SKETCH
(Show direction and distance from at !east two State Roads,
or ·other map reference points)
see .s,-fp v,,«p
1· REMARKS: \
I DO HEREBY CERTIFY THAT THIS WELL WAS CONST CTED IN ACCORDANCE WITH tS NCAC 2C. WELL CONSTRUCTION
ST ANDAROS, AND THAT A COPY OF THIS RECORD HAS ROVIDU. TO LL OWNER.
SIGNATURE OF CONTRACTOR OR AGENT R
GW· t Revised 11/84 Submit original to Division of Environmental Management and copy to well owner.
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MONITORING.WELL LOG
PROJECT_..:..Ral=e::::Jigo..:h.:i..,..:..N:...::C,.___ ____________ _ WELL NO. MW-3
GEOLOGIST S. A. Colton I DRILLING METHOD _ _:_:H:.::oll:c:o=-w"--=S..:.te::cm;:.:_:_A:..:ug=er'-----
DRILLER Soil TestingServices DATE
GROUND ELEVATION. ___ _ GROUND WATER DEPTH (ft):
TOP OF WELL ____ _ AT COMPLETION -----
DEPTH OF WELL (ft) AFTER HOURS
CASING MATERIAL 2" PVC SCREEN 10' of 0.010" slots
8/11/86
GRAVEL PACK :~•.;.•:·
BENTONITE
BACK FILL
CONCRETE
· SCREEN ----------
DESCRIPTION CONSTRUCTION
Yellow/brown SILT, tr f sand, tr frock fragments, roots
Brown/red to gray/purple clayey SILT, tr f sand
Gray/purple to brown clayey SILT,
(weathered bedrock), tr f sand
Bottom of Boring -21.5 feet
SHEET OF ------
I NORTH CAROLINA DEPARTMENT OF NATURAL RESOURCES ANO COMMUNITY DEVELOPMENT
DIVISION OF ENVIRONMENTAL MANAGEMENT -GROUNDWATER SECTION FOR OFFICE USE ONL y
P.O. BOX 27687 -AALEIGH.N.C. 27611, PHONE (919) 733-5083
I WELL CONSTRUCTION RECORD
-RILLING CONTRACTOR NI So" [ ,;i« 1 rieer,") A 5S Qc ,~ 1e S
'RILLER REGISTRATION NUMBER _.,_c..g~~-I _____ _
1. WELL LOCATION: (Show sketch al the location below)
I Nearest Town: ;V'\o.--r,s,v,llt) ;t,'. C.
Ko one rs Roa.cl, Ma{f1 ! v,lk.
(Road.Community, or S~bdivision and Lot No.)
I OWNER ___,_,K"'-'o+f-1-f...:.ec..r=-s _C=-=o"--. _X_n_c._,_ ______ _
ADDRESS t ri3me•reJ. \A/99J S;,sfe.M s. R,t:. 5'f
All lie (Street or ~OJte No.l ' ~orr,sv1 t-!:...C.
State Zip Code I City pr Tlwn
3. DATE DRILLED ?/''ft6 USE OF WELL /'.1/onil'or,~.,
I TOTAL DEPTH /'If. r;. CUTTINGS COLLECTED G'.i"Yes □ No
DOES WELL REPLACE EXISTING WELL? 0 Yes W"No
6. STATIC WATER LEVEL: 9.40 FT. Q,above TOP OF CASING,
2 IXl below I TOP OF CASING IS_cc.c. ___ FT. ABOVE LAND SURFACE.
,. YIELD (gpm): ______ METHOD OF TEST
•'WATER ZONES (depth):-----------------
9. CHLORINATION: Type Amount I CASING:
Depth
Wall Thickness
Diameter or Weight/Ft. Material
I
0 From -~--To
From. ____ To ___ Ft. ___ _
2" Ft. --'=---fVC
From To Fl.----
Depth Material Method I GROUT:
From ~o~_ To_l_c.__Ft. (er,,eht -1-Behton,te P.whr
I From ~2~_Ta_'+'--_Ft. Seo.I -Bento»ite. Pe/(efs
~-SCREEN:
I Depth
From s-To /7
Slot Size Material
~~-Ft.~2~_in.O.O/O in, PVC
Diameter
Fr.:>m To Ft. ____ in. ___ in.
From To ___ Ft, ____ in. ___ in.
GRAVEL PACK:
Depth Size Material
From lf-To /8,,!;-Ft. __ 6,,__11 __ Sa.nd.
From ____ To ___ Ft. _____ _
Quad. No. _______ Serial No. ___ _
Lat. Long, ____ Pc __
Minor Basin ____________ _
Basin Code ____________ _
Header Ent. _______ GW-1 Ent.-
STATE WELL CONSTRUCTION
PERMIT NUMBER: 'll-02.5S--1.',.._-023!,
County:
Depth
From To
DRILLING LOG
Formation Description
___ ___,Se=e o;H:c,,_ l he cl. , heet"
If adCitional space is needed use back of !urm.
LOCATION SKETCH
/'I\,/-'f
{Sh.ow direction and distance from at least two State Roads,
or other map reference points)
1· REMARKS: ·.
I DO HEREBY CERTIFY THAT THIS WELL WAS CONSTRUCTED IN ACCORDANCE WITH 15 NCAC 2C, WELL CONSTRUCTION
STANDARD_S, AND THAT A COPY OF THIS RECORD ~ROC!°ED ~WELL OWNER. I 1./2.J/J b I SIGNATURE OF CONTRACTOR OR AGENT . I DA TE
·Gw-1 Revised 11/84 Submit original to Division ol Environmental Management and copy to well owner.
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MONITORING'WELL LOG
PROJECT __ R_al_e_,ig"-h-'-,_N_C'----------------WELL NO, MW-4
DRILLING METHOD Hollow Stem Auger GEOLOGIST S. A. Colton
DRILLER Soil Testing Services DATE 8/14/86
GROUND ELEVATION __ _ GROUND WATER DEPTH {ft):
TOP OF WELL ____ _ AT COMPLETION. ____ _
DEPTH OF WELL (ft) AFTER HOURS
CASING MATERIAL 211 PVC SCREEN 12' of 0.01011 slots
DESCRIPTION
Brown clayey SILT, tr f sand, roots
Brown silty CLAY, tr f sand
Yellow/brown to brown clayey SILT, tr to little
emf sand
Red/brown to purple/maroon clayey SILT
(weathered bedrock), tr f sand
GRAVEL PACK :~•.;.•:'
BENTONITE
BACK FILL
CONCRETE
· SCREEN ----------
CONSTRUCTION
Purple/maroon clayey SILT and SAND (weathered bedrock)
Bottom of Boring -24 feet
SHEET ___ OF __ _
I NORTH CAROLINA DEPARTMENT OF NATURAL RESOURCES ANO COMMUNITY DEVELOPMENT
DIVISION OF ENVIRONMENTAL MANAGEMENT -GROUNDWATER SECTION
P.O. BOX 27687 -RALEIGH,N.C. 27611, PHONE (919) 733-5083
FOR OFFICE USE ONLY
Ouad. No. _______ Serial No.
I WELL CONSTRUCTION RECORD
lRILUNG CONTRACTOR w, ls0" [ "'B, nee,.,.,,) A 5S oc ,~ ie s
'RILLER REGISTRATION NUMBER --=-g--=-~-1-'-------
1. WELL LOCATION: (Show sketch ol the location below)
I Nearest Town: ;V\of"ri5 V11ft.) fa'. C.
Koppers R.oa.cJ.1 /1/lor,.,s v,!k,
(Road, Community, or Subdivision and Lot No.)
I owNER K'oppers Co . .r.,,c._
ADDRESS f: ri3ineere.t. WoqJ SvsteM s. R.t:. 5'f
,1,1 /Je_ (Slreet or R9yte No.) ~orr,sv, ;v. c: I Cito:,' ]"o't" State Zip Code
3. DATE DRILLED -~a+L'-'---"~b __ USE OF WELL l'llonitor,~.,
I TOTAL DEPTH 25-~' CUTTINGS COLLECTED Gives O No
DOES WELL REPLACE EXISTING WELL? □ Yes w"No
6. STATIC WATER LEVEL: 8. 0':) FT. 0 above TOP OF CASING.
'
2 l,l'below TOP OF CASING IS-. __ ._ .. ,-FT. ABOVE LAND SURFACE .
. YIELD (gpm): .. METHOD OF TEST _______ _ I WATER ZONES (dep1h): -----------------
9. CHLORINATION: Type
I CASING:
Depth
From 0 To ~
I From To
From To
B GROUT:
From
Depth
0 To I
(I From ___ _
~-SCREEN:
To 3
I Depth
From s-To 2.~
FrJm To
From To
GRAVEL PA CK:
Depth
l
I From 3 To 25"°
From To
REMARKS:
Amount
Wall Thickness
Diameter or Weight/Ft. Material
FI. 2" f'VC
Fl.
Ft.
Material ' Method
Fl. Cer-ie1it v-6ei,,fon,te Powder
Fl. Seo.I -(3e"tonite. Pe /let
Diameter Slot Size Material
FI. 2 in. 0. 010 in. eve.
Fi. in. in.
Ft. in. in.
Size Material
FI. 6 If s 0,. r, cl..
Ft.
----Lat. Long. ____ Pc __
Minor Basin _____________ _
Basin Code ____________ _
Header Ent. _______ GW-1 Ent.-
STATE WELL CONSTRUCTION
PERMIT NUMBER: '/I -02.55""-WM• 0231,
County: Jdc...Ke
Depth DRILLING LOG
From To Formation Description
---~S""'e'-"e c,Jf., c /.,e ci s hee t
II additional space is needed use back of form.
LOCATION SKETQH
(Sh_ow direction and distance from at least two State Roads,
or other map relerence points)
see srfe /'>'lC..p
I
I
I DO HEREBY CERTIFY THAT THIS WELL WAS CONSTRUCTED IN ACCORDANCE WITH 15 NCAC 2C. WELL CO STRUCTION
STANDARDS. AND THAT A COPY OF THIS RECORD HA~ PROVIDED TO WELL OWNER. ~ a. ,1. 23 i
SIGNATURE OF CONTRACTOR OR AGENT DATE
GW· 1 Revised 11/84 Submit original to Division of Environmental Management and copy to well owner.
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MONITORING.WELL LOG
PROJECT Raleigh, NC
DRILLING METHOD Hollow Stem Auger
WELL NO. MW-5
GEOLOGIST S. A. Colton
DRILLER Soil Testing Services DATE 8/1/86
GROUND ELEVATION. ___ _ GROUND WATER DEPTH (ft):
TOP OF WELL ____ _ AT COMPLETION -----
DEPTH OF WELL (ft) AFTER HOURS
CASING MATERIAL 2" PVC SCREEN 20' of 0.010" slots
10
DESCRIPTION
Brown cla e SILT. tr f sand tr frock fra ments FILL
Light Brown SILT, tr f sand (FILL)
Brown to maroon/purple clayey SILT, tr f sand,
.J.<:::-..::::S.l-tr light brown silt laminae
Bottom of Boring -2_6,5 feet
GRAVEL PACK :~•-:.•:·
BENTONITE
BACK FILL
CONCRETE
· SCREEN -----
CONSTRUCTION
· ..
.. ·.
SHEET OF ------
I NORTH CAROLINA DEPARTMENT OF NA nJRAl RESOURCES AND COMMUNITY DEVELOPMENT
DIVISION OF ENVIRONMENTAL MANAGEMENT -GROONOWATEFI SECTION FOR OFFICE USE ONL y
P.O. BOX 27887 -RALEIGH,N.C. 27811, PHONE (919) 733-5083
I WELL CONSTRUCTION RECORD
'RILLING CONTRACTOR 'Mlso" r,,.,,,neer, ... ) Asso,,~tes·
'RILLER REGISTRATION NUMBER __ :=.g..:.~c_l__:__ ____ _
1. WELL LOCATION: (Show sketch ol the location below)
I Nearest Town: ;V\of"r,sv,lfr.) ;V C.
Koppers P-.oo.c/..: Mor,..,s v,lk,
(Road. Community, or Subdivision and Lot No.)
I OWNER I'( Q ppers Co. .r nc..
ADDRESS [ n3lneeteJ. W99J S,,steri S, R.t:. 5't
,1,1 //" (Street or Ro~te No.) ' L.'.'...!orr,sv, c. ;v.c. I City lr Tor,n State Zip Code
3. DATE DRILLED ?~2.~{?(, USE OF WELL ///Qnitor1nJ
I TOTAL DEPTH 2. 'i/' _ CUTTINGS COLLECTED @°Yes O No
DOES WELL REPLACE EXISTING WELL? 0 Yes Ci6No
6. STA TIC WATER LEVEL: Cf_ 'i/9 FT O above TOP OF CASING
2 · Gtbelow ' Ii TOP OF CASING IS -'---FT. ABOVE LAND SURFACE.
"YIELD (gpm): ______ METHOD OF TEST I WA TEA ZONES (depth):
9. CHLORINATION: I CASING:
From 0
I From
From I GROUT:
From 0
I From Lf
SCREEN:
I From 8.
Fr .:im I From
. GRAVEL PACK:
I From &
From
Type
Depth
Amount
Diameter
Wall Thickness
or Weight/Ft. Material
To g 2" -'"--Ft.-'=---PVC.
To ___ Ft. ___ _
To ---Fl.----
Depth Material Method
To 4-Ft. (e;,,e,.,t ~ /3e,.,fon,te P.wder
To 6 Ft. Seo.I -Ge~to.,ite. Pelle~
Depth Diameter Sloi Size Material
To 2~ Ft. 2 in. 0. 010 in. eve
To Ft. in. in.
To Ft. in . in.
Depth Size Material
To 2°l? Ft, 61/ So.-,.,J..
To Ft.
Quad. No. _______ Serial No. ___ _
lat. Long. ____ Pc __
Minor Basin ____________ _
Basin Code ____________ _
Header Ent. _______ GW-1 Ent.-
STATE WELL CONSTRUCTION
PERMIT NUMBER: '/l-02.SS"-w'M-023!,
County:
Depth
From To
DRILLING LOG
Formation Oescricfion
JI additional space is needed use back ol fc,rm.
LOCATION SKETCH
(Show direction and distance from at least two State Roads,
or oth8r map reference points)
I REMARKS:----------------------------------------------
1 DO HEREBY CERTIFY THAT THIS WELL WAS CONSTRUCTED IN ACCORDANCE WITH 15 NCAC 2C. WELL CONSTRUCTION
ST ANDARD_S, AND THAT A COPY OF THIS RECORD ~ROQDED ~ WELL OWNER. t 2./z ] /J' 6 I SIGNATURE OF CONTRACTOR OR AGENT DA TE
GW· l Revised 11/84 Submit original to Division of Environmental Management and copy to well owner.
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MONITORING.WELL LOG
PROJECT Raleigh, NC
DRILLING METHOD Hollow Stem Auger
WELL NO. MW-6
GEOLOGIST S. A. Colton
DRILLER Soil Testing Services DATE 7 /28/86
GROUND ELEVATION ___ _ GROUND WATER DEPTH (ft):
TOP OF WELL ------AT COMPLETION ____ _
DEPTH OF WELL (ft) AFTER HOURS
CASING MATERIAL 2" PVC SCREEN 17' of 0.010" slots
DESCRIPTION
Brown clayey SILT, tr f sand, tr fm rock fragments
Brown CLAY and SILT, tr f sand
Red/Brown clayey SILT, tr f sand, some gray/green silty
CLAY ockets
Maroon clayey SILT (weathered bedrock), tr f sand
Gray/green to gray/brown SILT and CLAY,
tr f sand
Gray/Brown clayey SILT (weathered bedrock), tr f sand
Bottom of Boring -29 feet
GRAVEL PACK
BENTONITE
BACK FILL
CONCRETE
· SCREEN ----------
CONSTRUCTION
..... ·•: •,,
·.· .. · ...
. ...
... . "
.......... · ...... ·_.:.-.. : .. •, ·.· .. . . ::::;.:· ..... .
SHEET ___ OF __ _
I NORTH CAROLINA DEPARTMENT OF NATURAL RESOURCES AND COMMUNITY DEVELOPMENT
DIVISION OF ENVIRONMENTAL MANAGEMENT -GROUNDWATER SECTION FOR OFFICE USE ONLY
P.O. BOX 27687 -RALEIGH,N.C.27611, PHONE (919) 733-5083
I WELL CONSTRUCTION RECORD
lRILLING CONTRACTOR 1,,vi {$0>1 [ "'§ 1 neet,., Ass cc I .. te S
'RILLER REGISTRATION NUMBER g ~ 7
1. WELL LOCATION: (Show sketch of the location below)
I Nearest Town: J\l\o..-r,s vii(~) ;V C.
Konners Roa.d.. Moff",sv,lfe.
(Road. Community, or S~bdivision and Lot No.}
I OWNER K'oppers Co . .rnc..
ADDRESS f..,5,..,eereJ WcqJ Si,sfeMS,R.t:.5'f :1~ //,; [Street or R9~te No.) ' L.."..!orr,sv1 c. ;V.C.
'
City OJ T!wn Stale Zip Code
. DATE DRILLED ?f6U6 USE DF WELL Monitor,aJ
I TOTAL DEPTH 2 S-' CUTTINGS COLLECTED fil Yes □ No
DOES WELL REPLACE EXISTING WELL? □ Yes GJ"No
5. STATIC WATER LEVEL: {/.23 FT. □ above TOP OF CASING,
GY"below I roP OF CASING Is _2 ___ FT. ABOVE LAND suRFACE.
,. YIELD (gpm): ______ METHOD OF TEST _______ _ I WATER ZONES (depth):-----------------
9. CHLORINATION: Type Amount . E CASING:
I
Fror,l
From
From I GROUT:
From
I From
"· SCREEN:
0
0
S.!:
Wall Thickness
Depth Diameter or Weight/Ft. Material
To Cj_j Ft. 2" PVC
To Ft.
To Ft.
Depth Material Method
To 5'. t; Ft. Ce rne n t <t-(3e,,fon,te P, wd.er
To 7.,, Ft. 5e0-I-Be~t,.,,te Pelle~
Depth Diameter Slot Size Material I From 9. !:" To2'+.r-Ft. 2 in.0.010 in. PVC..
FrJm ____ To ___ Ft. ____ in. ___ in.
From To Ft. ____ in. ___ in. , I .. _ GRAVEL PACK:
I Depth Size
From _7._._~ __ To 2 5" Ft. -~6_'_1 __
Material
So..nd..
From ____ To ___ Ft. _____ _
Ouad. No. _______ Serial No. ___ _
Lat. Long. ____ Pc __
Minor Basin ____________ _
Basin Code ____________ _
Header Ent. _______ GW-1 Ent.-
STATE WELL CONSTRUCTION
l"l\o/-7 PERMIT NUMBER: ')I -02.55"-W'M-023!,
County:
Depth
From To
DRILLING LOG
Formation Descriotion
---~5e"=e. cd@chrd sherT
tf additional space is needed use back of lcrm.
LOCA TtON SKETCH
(Show direction and distance from at least two State Roads,
or ·other map reference points)
see s,fe
•· REMARKS:
t DO HEREBY CERTIFY THAT THIS WELL WAS CONSTRUCTED IN ACCORDANCE WITH 15 NCAC 2C. WELL CONSTRUCTION
STANDARDS, AND THAT A COPY OF THIS RECORD HAS N PROVID$P. TO E WELL OWNER. /
C,{ I 1-2]/]6 I SIGNATURE OF CONTRACTOR OR AGENT ATE
GW· 1 Revised 11/84 Submit original to Division of Environmental Management and copy to welt owner.
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MONITORING·WELL LOG
PROJECT Raleigh, NC WELL NO. Mw-7
DRILLING METHOD __ H_o_ll..co_w_S_t_e_m_A_u__,g,__e_r ___ _ GEOLOGIST S. A. Colton
DRILLER Soil Testing Services DATE
GROUND ELEVATION. ___ _ GROUND WATER DEPTH {ft):
TOP OF WELL ____ _ AT COMPLETION ____ _
DEPTH OF WELL (ft) AFTER HOURS
CASING MATERIAL 2" PVC SCREEN 15' of 0.010" slots
DESCRIPTION
Qray Br.o n me) ROCK fragments, wood chips, httle silt flLL
Brown SILT and CLAY, tr f sand
8/6/86
GRAVEL PACK :~•.:,•:·
BENTONITE
BACK FILL
CONCRETE
· SCREEN -----
CONSTRUCTION
Light purple to red/brown clayey SlL"J<weathered bedrock),
tr f sand, some me sand 17 .5-19'
'\
... ·.·,·
·.•,
·,'.,
Bottom of Boring ~ 26 feet
SHEET ___ OF __ _
I NORTH CAROLINA DEPARTMENT OF NATURAL RESOURCES AND COMMUNITY DEVELOPMENT
DIVISION OF ENVIRONMENTAL MANAGEMENT -GROUNDWATER SECTION FOR OFFICE USE ONL y
P.O. BOX 27687-RALEIGH,N.C, 27611, PHONE (919) 733-5083
I WELL CONSTRUCTION RECORD
.DRILLING CONTRACTOR Wilson f.-i81neer, .. ., Ass~,,~1es
RILLER REGISTRATION NUMBER ___ g_~_I _____ _
1. WELL LOCATION: (Show skelch of the location tielow)
I Nearest Town: /Vlorr,s V11ft.) JV C.
11'.o poers R.oo.cl., Mor,., s v,lk,
(Road, Community, or S~bdivision and Lot No.) I OWNER _:__:K's...:o=-;:f:.+P....:e.c.-r=-.5 _.::CC-'o"-. _x_,.,_'-~·~-------
ADDRESS f Y13me•reJ. \.v99J Si,sfe,.,, s. R.t:. 5'f
,1,1 //f. (Streel or Ro~•• No.) '
I L.."..!orr,5v1 t:::...C.
City Pf /T.own State Zip Code
3. DATE DRILLED 'tilt ?6 USE OF WELL ldonitor,a}l ,1 I ;;t
I TOTAL DEPTH 2{, CUTTINGS COLLECTED Grves O No
DOES WELL REPLACE EXISTING WELL? □ Yes Gl'No
6 STATIC WATER LEVEL· 7.50 FT. 0 above TOP OF CASING, ·I TOP OF CASING IS· __ 2. ___ FT. AroeiI~_wAND SURFACE.
7. YIELD (gpm): ______ METHOD OF TEST _______ _
I WATER ZONES (depth): -----------------
9. CHLORINATION: Type Amount I CASING: Wall Thickness
Depth Diameter or Weight/Ft. Material
0 6 2" f Ve: From To Ft. I From To Ft.
From To Ft. I GROUT:
Depth Material Method
From 0 To 3 Ft. (e,..e1-1t ,t-/3e1-1fon,te P.wder
I From 3 To ~ Ft. Seo-I -GeHtonite. Pe 1/e-fs
12. SCREEN:
I Depth Diameter Slot Size Material
From 6 To 2~. r; FI. 2 in.0.0I0 in. eve.
Fr.:im To Ft. in. in.
I From To Ft. in. in.
13. GRAVEL PACK:
11 Deplh Size Material
From S" To 2b FI. 6 I( So.,.,J.
From To Ft.
I REMARKS:
Quad. No. _______ Serial No. ___ _
Lat. Long. ____ Pc __
Minor Basin _____________ _
Basin Code ____________ _
Header Ent. _______ GW-1 Ent.-
STATE WELL CONSTRUCTION
PERMIT NUMBER: ~I -02.5S"-l.'M-02.3!,
County:
Depth
From
k:ic.}fe
To
DRILLING LOG
Formation Description
____ .,,Se...,.e 0--ft-a.cl,rJ. Sheet"
11 additional space is needed use back of form.
LOCATIQN SKETQH
(Show direction and distance from at !east two State Roads,
or other map reference points)
see sde mo.p
I SIGNATURE OF CONTRACTOR OR AGENT DAT
GW-1 Revised 11/84 Submit original to Division of Environmental Management and copy to well owner.
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MONITORING.WELL LOG
PROJECT Raleigh, NC WELL NO. MW-8
ORI LL! NG METHOD __ H_o_ll_o_w_S_t_em_A_ug--"-e_r ___ _ GEOLOGIST S.A. Colton
DRILLER Soil Testing Services
GROUND ELEVATION ----
TOP OF WELL ____ _
DEPTH OF WELL (ft)
CASING MATERIAL
STRAT SAMPLE
DEPTH DEPTH
2" PVC
DATE
GROUND WATER DEPTH (ft):
AT COMPLETION'------
AFTER HOURS
SCREEN 201 of 0.010 slots
DESCR I PT! ON
Black fm ROCK fragments, little fmc sand, tr silt
10
Brown CLAY and SILT, tr fm sand, tr f rock
fragments
8/4/86
GRAVEL PACK :~•.;.•:·
BENTONITE
BACK FILL
CONCRETE
· SCREEN ----------
CONSTRUCTION
......
..
Red/Brown clayey SILT, tr f sand, tr frock fragments,
tr laminae of light green clay
20
Red/Brown clayey SILT (weathered bedrock),
light green laminae 14.5-16.5'
Bottom of Boring -26.5 feet
.. ·. ,·
SHEET ___ OF __ _
I NORTH CAROLINA DEPARTMENT Of NA TIJRAL RESOURCES AND COMMUNITY DEVELOPMENT
DIVISION OF ENVIRONhEHTAL MANAGEMENT -GROUNOWATER SECTION
FOR OFFICE USE ONL y
P.O. BOX 27687 -RAL.EIGH,N.~.27e11, PHONE (919) 733-5083
I WELL CONSTRUCTION RECORD
I .
DRILLING CONTRACTOR wi/so" ["131rieet,") Assce1~tes
RILLER REGISTRATION NUMBER __ g=-.;:.~_I;__ ___ _
1. WELL LOCATION: (Show sketch of the location below) I Nearest Town: Mcr"r15 v,({~) /V C.
h'.o noers R.oo.cl, /lllorr,s v,lk,
(Roa[ Community, or S~bdivision and Lot No.) I OWNER K'oppers Co . .Inc..
ADDRESS [ n31neereJ.. WooJ Si,sfer1 s. (<.'C. 5'f
I /110 rr,5v1f le (Street or ~c No.)
City:/ or/Town ·State Zip Code
3. DATE DRILLED 'J))_~b USE OF WELL Mon;tor,aJ
I TOTAL DEPTH 2/1
CUTTINGS COLLECTED U1Yes O No
DOES WELL REPLACE EXISTING WELL? 0 Yes GJ"No
I STATIC WATER LEVEL: (;.Jj FT. 0 above TOP OF CASING,
2 Gl""below
TOP OF CASING IS.-""'---FT. ABOVE LAND SURFACE.
7. YIELD (gpm): ______ METHOD OF TEST
I WATER ZONES (depth): -----------------
9. CHLORINATION:
•· CASING:
Type ____ _ Amount
Wall Thickness
Diameter or Weight/Ft.
I
Depth
From _O~ __ To ,5-2" Ft.~=---
From ____ To ___ Ft, ___ _
From ____ To FL----
Material
f Ve.
1· GROUT: Depth Material Method
From I From
12. SCREEN:
0 To /,!;"
/. 5"" To 3. 5"
Ft. Cer<>ei,T ,t-f3e,.fon,te P,wder
Ft. Seo.I -Be.t,.,ite. Pellefs
I
I
Oeprtt
From S-To 2. I ----
Diameter Slot Size Material
Ft._2=..._in.0.010 in. PVC..
FrJm ____ To ___ Ft. ____ in. ___ in.
From To Ft. ____ in. ___ in.
13. GRAVEL PACK:
Depth Size
3. !,-2 6 6 11
From To Ft. ---''----I Materiat s 0-r-.d.
From ____ To ___ Ft. _____ _
Quad. No. _______ Serial No. ___ _
Lat. Long. ____ Pc_
Minor Basin ____________ _
Basin Code ____________ _
Header Ent. _______ GW-1 Ent.-
STATE WELL CONSTRUCTION
PERMIT NUMBER: o/l -02.SS--I-IM-02.31,
County: Wc. ){ e
Depth DRILLING LOG
From To Formation Description
-----'-"'-e o.'ltc..d,eci. Sheet
If additional space is needed use back ol form.
LOCATION SKETCH
(Show direction and distance from at least two State Roads,
or ·otheir map relerence points)
See
I· REMARKS:-------------------------------------------
1 DO HEREBY CERTIFY THAT THIS WELL WAS CONSTRUCTED IN ACCORDANCE WITH 15 NCAC 2C, WELL CONSTRUCTION
STANDARDS, AND THAT A COPY OF THIS RECORD HA~EN PROVIDED T~~ WELL OWNER. / j
I ~ y'. ~ /2. ZJ[jt
SIGNATURE OF CONTRACTOR OR AGENT 'oA TE
GW·I Revised 11/84 Submit original to Division al Environmental Management and copy to well owner.
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MONITORING.WELL LOG
PROJECT Raleigh, NC WELL NO. MW-9
DRILLING METHOD Hollow Stem Auger GEOLOGIST S. A. Colton
DRILLER Soil Testing Services DATE
GROUND ELEVATION ----GROUND WATER DEPTH (ft):
TOP OF WELL ____ _ AT COMPLETION -----
DEPTH OF WELL (ft) AFTER HOURS
CASING MATERIAL 2" PVC SCREEN 16' of 0.010 slots
DESCRIPTION
Brown clayey SILT, tr f sand
8/5/86
GRAVEL PACK :~•.;.•:'
BENTONITE
BACK FILL
CONCRETE
· SCREEN ----------
CONSTRUCTION
Mottled Brown and gray/green SILT and CLAY, tr f sand,
tr f rock fragments
Mottled Brown and gray/green clayey SILT, tr f sand
Brown clayey SILT (weathered bedrock), tr f sand,
tr m rock fragments (25-26.5')
Bottom of Boring -26.5 feet
:·,
·,·
.. · ... . '
··.:
SHEET OF ------
I NORTH CAROLINA OEPARThENT Of NATURAL RESOURCES AND COMMUNITY DEVELOPMENT
DIVISION OF ENVIAONJ.ENTAL MANAGEMENT -GROUNDWATER SECTION FOR OFFICE USE ONL y
P.O. BOX 27687 -RALEIGH.N.C. 27611, PHONE {918) 733-5083
I WELL CONSTRUCTION RECORD
•□RILLING CONTRACTOR Mlso" r,,,,,,eet,..,) Assoe1Ates
•□RILLER REGISTRATION NUMBER __ ..::.g...:c~_I _____ _
1. WELL LOCATION: (Show skelch ol lhe lo ca lion below)
I NearesI Town: ;1/lof"r15 V1fft) JV C.
Koppers R.o~d) Marr,s v,lk,
(Road, Community, or Subdivision and Lot No.)
I OWNER ____,_,K'c..:o+f+fc..::.e.:...r:c.5 _.o=C:..::o"-. --'-.I_n_c._,. _______ _
· ADDRESS f v,3meereJ W'ooJ S,,sfer1 s. R.t. 5'f
/1/1 lie_ (Streel or Ao~le No.) ' ~orr,sv, f'!:...C. I Cit/y or/Town State Zip Code
3. DATE DRILLED 'I? 5" 86 USE OF WELL Monitor,,,,, r 1/ -;t
I·. TOTAL DEPTH 215 CUTTINGS COLLECTED Gl'Yes O No
DOES WELL REPLACE EXISTING WELL? 0 Yes GJ"'No
6. STATIC WATER LEVEL:. /5','f,l_ FT. 0 above TOP OF CASING, '1. Gd"below I TOP OF CASING IS--~ FT. ABOVE LAND SURFACE .
... YIELD (gpm): ______ METHOD OF TEST _______ _
1· WATER ZONES (deplh): -----------------
9.
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CHLOAINA TION: Type Amount
CASING:
From
From
From
GROUT:
From
Depth
-=---To 0 21
Diameter
Wall Thickness
or Weight/Ft.
2" Ft._=--
____ To ___ Ft. ___ _
----To FL----
Material
I' Ve:
Depth Material Method
0 To / 7 ----
' From
. SCREEN:
/7 ____,___:__To I 9
Ft. (e,.,,e,,t.-6e .. t,a,te P,wd.er
Ft. Seed -Be~t,,,ite. Pellefs
I Depth
From_2_I __ To 28
Diameter Slot Size Material
Ft.__::2=-_in.0.01O in. PVC.
Fr.:,m ____ To ___ Ft. ____ in. ___ in .
I From To Ft. ____ in. ___ in.
.. 3. GRAVEL PACK:
I Depth Size
1'1 28 6" From ---'---To Ft. ----'"------
Material
So.nd.
From ____ To ___ Ft. _____ _
Quad. No. ______ Serial No. ___ _
lat. Long. ____ Pc_
Minor Basin _____________ _
Basin Code ____________ _
Header Ent. _______ GW-1 Ent.-
STATE WELL CONSTRUCTION
PERMIT NUMBER: 11 -02.S'S--w'M-02.31, ,,.,,.'w'-/0
County: Wc..h'e
Depth DRILLING LOG
From To Formation Oescriotion
___ ....;St.Ee=...e o. tt«, l,e ol s lieef-
If additional space is needed use back of lorm.
LOCATION SKETCH
(Show direction and distance from at least two State Roads,
or ·oth0r map reference points)
see srfe rv,o.p
f· REMARKS:----------------------------------------------
1 DO HEREBY CERTIFY THAT THIS WELL WAS CONSTRUCTED IN ACCORDANCE WITH 15 NCAC 2C, WELL ONS AUCTION
ST ANDAADS, AND THAT A COPY OF THIS RECORD HAS ,§E~_PAOVIDED TO WELL OWNER. ~U. l22•J'/ I SIGNA TUAE OF CONTRACTOR OR AGENT DATE
GW-1 Revised 11 /84 Submit original to Division of Environmental Management and copy to well owner.
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MONITORING.WELL LOG
PROJECT Raleigh, NC WELL NO. MW-10
DRILLING METHOD Hollow Stem Auger/Wash Rotary GEOLOGIST S. A. Colton
DRILLER Soil Testing Services DATE
GROUND ELEVATION ----GROUND WATER DEPTH (ft):
TOP OF WELL AT COMPLETION -----------
DEPTH OF WELL {ft) AFTER HOURS
CASING MATERIAL 2" PVC SCREEN 7' of 0.010" slots
STRAT SAMPLE
DEPTH DEPTH DESCRIPTION
Maroon/Brown clayey SILT, tr f sand, roots,
light green clay pockets. 1.5-3 .0'
8/5/86
GRAVEL PACK
BENTONITE
BACK FILL
CONCRETE
· SCREEN ----------
CONSTRUCTION
Maroon/Brown, gray/purple to yellow/brown clayey SILT
(weathered bedrock), tr f sand
(0 -10.5' sample descriptions taken from Boring B-4)
10
20
Bottom of Boring -28.5 feet
SHEET ___ OF __ _
I NORTH CAROLINA DEPARTMENT OF NATURAL RESOURCES ANO COMMUNITY DEVELOPMENT
DIVISION OF ENVIRONMENTAL MANAGEMENT -GROUNDWATER SECTION FOR OFFICE USE ONL y
P.O. BOX 27687 -RALEIGH.N.C. 27611, PHONE (919) 733-5083
I WELL CONSTRUCTION RECORD
'RILLING CONTRACTOR W, /so" f .-i31 Mef-1") Assoc ,~ies
'RILLER REGISTRATION NUMBER ---'--g_i_7 _____ _
1. WELL LOCATION: (Show sketch of !he location b·elow)
I Nearest Town: /V\or-r,5 v,/{L} /v. C.
h:o Peers Ro"cl.. Morr,s v,l[e
(Road, Community, or S~bdivision and Lot No.)
I owNER -'--'K''---'o+fl+P...ce_r=--s _C=--.co..,_. _.r_,..._c.~·--------
ADDREss I: f"~ ,rieereJ. Woo cl Srsfer1 s. R.t:. 5't ,1,1 //; (Street or Ro~te No.l ' L.!'..!orr,sv, c. &C. I Ci~ p
1
r
9
Tp:;
6
n State Zip Code
3. DATE DRILLED o/i {~ USE OF WELi. Monitor,~.,
I TOTAL DEPTH '31. !: _ CUTTINGS COLLECTED Cia'Yes □ No
DOES WELL REPLACE EXISTING WELL? □ Yes l:it'No
6. STATIC WATER LEVEL: /I{. 5'lf FT. Q_,above TOP OF CASING.
'
2 w below
TOP OF CASING IS-'~--FT. ABOVE LAND SURFACE.
YIELD (gpm): ______ METHOD OF TEST -------~
.WA TEA ZONES (depth): -----------------
9. CHLORINATION: Type Amount ti CASING:
Depth Diameter
Wall Thickness
or Weight/Ft. Material
From __ Q __ To 2/.r Ft. 2" ('Ve I From ----To ___ Ft. ___ _
From To FL----
Depth
,.GROUT:
From _a=--To I 7
I From --'-/_7 __ To I 9
,, SCREEN:
Material Method
Ft. (er,,e,.t"" Be .. fo.,,te P.wder
Ft. 5eo-.l -Be"t..,ite. Pellet's
I Depth Diameter Slot Size Material
From 21. :;-To "J/. 5' Ft. 2 in.0.0/0 in. PVC..
Fr .Jm To Ft. in. in. I From To Ft. in. in.
GRAVEL PACK:
I Depth Size Material
From / 9 To "]I. f; FI. 6 // So. ... cl.
From To Ft.
Quad. No. _______ Serial No. ___ _
Lat. Long. ____ Pc __
Mlnor Basin ____________ _
Basin Code ____________ _
Header Ent. _______ GW-1 Ent. __ _
STATE WELL CONSTRUCTION
PERMIT NUMBER: 'II -02.!iS--w'M-02.31,
County:
Depth
From To
See
DRILLING LOG
Formation Description
II additional space is needed use back of le.rm.
LOCATION SKETCH
(Show direction and distance from at least two State Roads,
or ·other mac reference points)
See sife
I REMARKS:-------------------------------------------
1 DO HEREB_ Y CERTIFY THAT THIS WELL WAS CONSTRUCTED IN ACCORDANCE WITH 15 NCAC 2C, WELL CONST,RUCTION
STANDARDS. AND THAT A COPY OF THIS RECORD HA BEEN PROVIDED TO E WELL OWNER. ' /_ a 12. zt r6 I SIONA TURE OF CONTRACTOR OR AGENT DATE'
G'N· 1 Revised 11/84 Submit original to Division of Environmental Management and copy to well owner.
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MONITORING.WELL LOG
PROJECT Raleigh, NC
DRILLING METHOD Wash Rotary
WELL NO. MW-11
GEOLOGIST s. A. Colton
DRILLER Soil Testing Services
GROUND ELEVATION __ _
TOP OF WELL ____ _
DEPTH OF WELL (ft)
CASING MATERIAL 2" p1;c
DATE 8/19/86
GROUND WATER DEPTH (ft):
AT COMPLETION -----
AFTER HOURS
SCREEN 10' of 0.010" slots
GRAVEL PACK
BENTONITE
BACK FILL
CONCRETE
· SCREEN ----------
STRAT SAMPLE
DEPTH DEPTH DESCRIPTION CONSTRUCTION
Brown cla e SILT tr f sand, roots
Brown clayey SILT .. ,ith white SILT and CLAY laminae,
Brown/Red clayey SIIT (weathered bedrock), tr f sand
10 (0-10.5 feet sample descriptions taken from Boring B~2)-
20
Bottom of Boring - 3 2 feet
SHEET ___ OF __ _
I NORTH CAROLINA DEPARTMENT OF NATURAL RESOURCES_ ANO COMMUNITY DEVELOPMENT
DIVISION OF ENVIRONMENTAL MANAGEMENT -GROUNDWATER SECTION FOR OFFICE USE ONLY
P.O. BOX 27687 -RALEl~.N.C. 27611, PHONE (918) 733-5083
I WELL CONSTRUCTION RECORD
~RILLING CONTRACTOR w, {50>1 [...,BI Mer,") Asso, ,~tes
'RILLER REGISTRATION _NUMBER ---=-g~~_I ____ _
1. WELL LOCATION: (Show sketch of the location below)
I Nearest Town: JVlo,-r,s v,lfr) ;V. C.
Koppers Roa.d.1 Marr,iv,lk.
(Road, Community, or Subdivision and Lot No.}
I ER /-(opgers Co . .r .. c...
A
ODWDNRE S S I=-l=-t r,~ineerec! W'99J Si,sfe;,,, s, R.t:. 5't
,M II ; (Slreel or Ro~te No.) '
I _orr,sv, c. !:!:_C.
City pr Tpwn State Zip Code
3. DATE DRILLED lf49/86 USE OF WELL /\IJQoitor,aJ
I TOTAL DEPTH 30. . CUTTINGS COLLECTED @°Yes O No
DOES WELL REPLACE EXISTING WELL? □ Yes Cid'No
6. STATIC WATER LEVEL: / b · 3 9 FT. 0 9bove TOP OF CASING, 2. uJ"below I TOP OF CASING IS ____ FT. ABOV; LAND SURFACE.
7. YIELD (gpm): _____ METHOD OF TEST ______ _
I WATER ZONES (dep1h): ----------------
9. CHLORINATION: Type Amount
I CASING:
From 0
I From
Wall Thickness Diameter or Weight/Ft. Material
2" f VC: Ft._~--
----To ___ ft. ___ _
Depth
To J.0 ----
From ----To ---Fl.----
Depth Material Method I. GROUT:
From ~O __ ro t 5", S' Ft. Ce ,.,,e 11 t ,i-6e,,fon,te P. wder
!5".5' To /7,5'" Ft. Se<>-1-Be~t.,,ite. Pellets I
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From
SCREEN:
From 2.0
From
From
GRAVEL PACK:
From / 7. 5"
From
REMARKS:
Depth
To ]O Ft.
To Ft.
To Ft.
Depth
To 10 Ft.
To Ft.
Diameter Slot Size Material
2 in.0.0I0 in. PVC
in. in.
in. in.
Size Material
6 It So..,J.
Quad. No. ______ Serial No. ___ _
Lat. Long. ____ Pc_
Minor Basin ____________ _
Basin Code ____________ _
Header Ent. ______ GW-1 Ent.-
STATE WELL CONSTRUCTION
PERMIT NUMBER: '11 -02.55"-WM-02.3E.
County:
Depth
From
ldc...Ke
To
DRILLING LOG
Formation Description
----~e oitacl,eJ sl,ee-r
II additional space is needed use back of !arm.
LDC A TION SKf.K!:i
(Show direction and distance from at least two State Roads,
or 'other map reference points)
5 ee
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I DO HEREBY CERTIFY THAT THIS WELL WAS CONSTRUCTED IN ACCORDANCE WITH 15 NCAC 2C. WELL CONST UCTION
STANDARDS. AND THAT A COPY OF THIS RECORD HA B EN PROVIDED TO E LL OWNER.
SIGNATURE OF CONTRACTOR OR AGENT DATE
GW-1 Revised 11/84 Submit original to Division at Environmental Management and copy to well owner.
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MONITORING·WELL LOG
PROJECT _ _::Ral=e"'ig"'h-'-''-"N.:cC=--· ______________ _ WELL NO. MW-12
GEOLOGIST S. A. Colton DRILLING METHOD \\ash Rotary -----~------
DRILLER Soil Testing Sel"Vices DATE
GROUND ELEVATION. ___ _ GROUND WATER DEPTH (ft):
TOP OF WELL. ____ _ AT COMPLETION. ____ _
DEPTH OF WELL (ft) . AFTER HOURS
CASING MATERIAL 2" pyr, SCREEN 10' of 0.010" slots
STRAT SAMPLE
DEPTH DEPTH DESCRIPTION
8/19/86
GRAVEL PACK
BENTONITE
BACK FILL
CONCRETE
· SCREEN -----
CONSTRUCTION
Red/Brown clayey SILT, tr f sand, tr frock fragments,
roots
10
20
30
Red/Brown clayey SILT (weathered bedrock),
tr f sand
(0-12.5' sample descriptions taken from Boring B-1)
Bottom of Boring -30.5 feet
. . ... . ..
. . . . . . .
.. . . . . ... ..
.. ... . . . . . ..
•:,::
·.·•
..
SHEET _ __;,_OF __ _
I
I KEYSTONE
[t-.VIROSMENTAL RESOURCES, INC.
Ref. 8, Encl. 2
I 440 College Park Dr., Monroeville, PA 15146 -----------------
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MONITORING.WELL LOG
PROJECT Raleigh, NC WELL NO. MW-1
DRILLING METHOD Hollow Stem Auger GEOLOGIST s. A. Colton --C..C..:c:.c....cc..:.c;.;..;.c.;__ __ _
DRILLER Soil Testing Services DATE 8/7/86
GROUND ELEVATION.___ GROUND WATER DEPTH (ft):
TOP OF WELL_____ AT COMPLETION ____ _
DEPTH OF WELL (ft) AFTER HOURS
CASING MATERIAL 2" PVC SCREEN 20' of 0.010" slots
DESCRIPTION
Brown, clayey SILT, tr f sand, tr weathered rock
fragments, tr m quartz fragments, tr roots (0-1.5')
J.lottled Brown and gray silty CLAY, tr f sand,
tr f rock fragments.
Red/brown Clayey SILT (weathered bedrock), tr
siltstone fragments, tr f sand
Bottom of Boring -26.5 feet
GRAVEL PACK :~•.:,•:·
BENTONITE
BACK FILL
CONCRETE
· SCREEN ----------
CONSTRUCTION
.. . ••,
.',,: . ,'
SHEET OF
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,·,,
--------
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MONITORING.WELL LOG
PROJECT Raleigh, NC WELL NO. MW-2
DRILLING METHOD Hollow Stem Auger GEOLOGIST S. A. Colton
DRILLER Soil Testing Services DATE 8/7 /86
GROUND ELEVATION ----GROUND WATER DEPTH (ft):
TOP OF WELL AT COMPLETION -----------
DEPTH OF WELL (ft) AFTER HOURS
CASING MATERIAL · 2" PVC SCREEN 19' of 0.010" slots
12
DESCRIPTION
Brown clayey SILT, tr f sand, tr siltstone fragments,
roots 0-1.5', 9-10.5'
Mottled gray /green/yellow /orange clayey SILT,
(weathered bedrock)
Bottom of Boring -26.5 feet
GRAVEL PACK
BENTONITE
BACK FILL
CONCRETE
· SCREEN
CONSTRUCTION
.;.
. =·
SHEET OF ------
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MONITORING.WELL LOG
PROJECT Raleigh, NC
DRILLING METHOD Hollow Stem Auger
WELL NO. MW-3
GEOLOGIST s. A. Colton
DRILLER Soil Testing Services DATE
GROUND ELEVATION __ _ GROUND WATER DEPTH (ft):
TOP OF WELL _____ _ AT COMPLETION -----
DEPTH OF WELL (ft) AFTER HOURS
CASING MATERIAL 2" PVC SCREEN 10' of 0.010" slots
8/11/86
GRAVEL PACK :~•-:.•:·
BENTONITE
BACK FILL
CONCRETE
· SCREEN ----------
DESCRIPTION CONSTRUCTION
Yellow /brown SILT, tr f sand, tr f rock fragments, roots
Brown/red to gray/purple clayey SILT, tr f sand
Gray/purple to brown clayey SILT,
(weathered bedrock), tr f sand
Bottom of Boring -21.5 feet
SHEET ___ OF __ _
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MONITORING.WELL LOG
PROJECT __ R_al_e~igh~,_N_c ______________ _ WELL NO. MW-4
GEOLOGIST S. A. Colton DR I LUNG METHOD __ H_oll_ow_S_t_em_A_u~g~e_r ____ _
DRILLER Soil Testing Services DATE 8/14/86
GROUND ELEVATION GROUND WATER DEPTH (ft): ----
TOP OF WELL AT COMPLETION -------------
DEPTH OF WELL (ft) AFTER HOURS
CASING MATERIAL 2" PVC SCREEN 12' of 0.01011 slots
STRATA SAMPLE
DEPTH DEPTH
><--
-
.. 10;,::,--.,_;.--+>< I-
-><-. --
zn ><---
DESCRIPTION
Brown clayey SILT, tr f sand, roots
Brown silty CLAY, tr f sand
Yellow/brown to brown clayey SILT, tr to little
emf sand
Red/brown to purple/maroon clayey SILT
(weathered bedrock), tr f sand
GRAVEL PACK
BENTONITE
BACK FILL
CONCRETE
·i.j
,s;.:.~,f-~~
;-.!":'~.:.;,
· SCREEN ----
"
..
--
..
..
--
--. -
..
CONSTRUCTION
,,, ,✓
y\ ,.,,',. . ' ,, ,,
I
., ·-... .. •-·:·
....... -:·.·:
.. : ', ~ :.\·
·:.<: -;·:·•:·.
': ·: ·•-.·· •,• ·-· :·:: _:_·;:
,, . ·.·.
-·:·-·.·.• ,,. -.. -.
,., --:.:; .-. . .. -·-.... •:, . :·
:·?\~/(
--------
-----
---
--
-
---
Purple/maroon clayey SILT and SAND (weathered bedrock) -
--..
-
-
--
--
--
-Bottom of Boring -24 feet ---------
-------
--.
..
---..
--
--
---
-
---
---
---
--
--
SHEET ___ OF __ _
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MONITORING.WELL LOG
PROJECT __ R_al_e~ig~h~,_N_C ________________ _ WELL NO. MW-5
GEOLOGIST S. A. Colton DRILLING METHOD Hollow Stem Auger
DRILLER Soil Testing Services DATE
GROUND ELEVATION ----GROUND WATER DEPTH (ft):
TOP OF WELL AT COMPLETION -----------
DEPTH OF WELL (ft) AFTER HOURS
CASING MATERIAL 2" PVC SCREEN 20' of 0.010" slots
DESCRIPTION
8/1/86
GRAVEL PACK :~•.:.•:·
BENTONITE
BACK FILL
CONCRETE
· SCREEN
CONSTRUCTION
Brown clave SILT tr f sand, tr frock fra ments FILL
Light Brown SILT, tr f sand (FILL)
Brown to maroon/purple clayey SILT, tr f sand,
-l<"--....::,.1-tr light brown silt laminae
10 Maroon/purple to gray clayey SILT (weathered bedrock),
-k--=--·tr f sand, little m rock fragments 25.5-26.5'
Bottom of Boring -26.5 feet
... ·.•
·•.·.
:•.
. '•
••.·
SHEET ___ OF __ _
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MONITORING.WELL LOG
PROJECT Raleigh, NC
DRILLING METHOD Hollow Stem Auger
WELL NO. MW-6
GEOLOGIST S. A. Colton
DRILLER Soil Testing Services DATE 7/28/86
GROUND ELEVATION ----GROUND WATER DEPTH (ft):
TOP OF WELL ____ _ AT COMPLETION. ____ _
DEPTH OF WELL (ft) AFTER HOURS
CASING MATERIAL . 2" PVC SCREEN 17' of 0.010" slots
DESCRIPTION
Brown clayey SILT, tr f sand, tr fm rock fragments
Brown CLAY and SILT, tr f sand
Red/Brown clayey SILT, tr f sand, some gray/green silty
CLAY ockets
Maroon clayey SILT (weathered bedrock), tr f sand
Gray/green to gray/brown SILT and CLAY,
tr f sand
Gray/Brown clayey SILT (weathered bedrock), tr f sand
Bottom of Boring -29 feet
GRAVEL PACK
BENTONITE
BACK FILL
CONCRETE
· SCREEN ----------
CONSTRUCTION
. ·,
• ..
. : .
·' : ,::
':.
SHEET ___ OF __ _
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MONITORING.WELL LOG
PROJECT Raleigh, NC WELL NO. M w-7
DR ILL! NG METHOD __ H_o_ll_o_w_S_t_e_m_A_u~g~e_r ___ _ GEOLOGIST S. A. Colton
DRILLER Soil Testing Services DATE
GROUND ELEVATION ----GROUND WATER DEPTH (ft):
TOP OF WELL. ____ _ AT COMPLETION -----
DEPTH OF WELL (ft) AFTER HOURS
CASING MATERIAL 211 PVC SCREEN 15' of 0.01011 slots
DESCRIPTION
Gray Bro n mc)ROCK fragments, wood chips, lI ttle silt FILL
Brown SILT and CLAY, tr f sand
8/6/86
GRAVEL PACK :~•.:.•:"
BENTON I TE
BACK FILL
CONCRETE
· SCREEN ----------
CONSTRUCTION
Light purple to red/brown clayey SIL7<weathered bedrock),
tr f saner: some me sand 17.5-19'
... ·,,.
Bottom of Boring.-26 feet
SHEET ___ OF __ _
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MONITORING.WELL LOG
PROJECT Raleigh, NC
DRILLING METHOD __ H_o_ll_o_w_S_t_em_A_ug-"--e_r ___ _
WELL NO. MW-8
GE OL OG IS T S.A. Colton
DRILLER Soil Testing Services DATE
GROUND ELEVATION __ _ GROUND WATER DEPTH (ft):
TOP OF WELL ____ _ AT COMPLETION -----
DEPTH OF WELL (ft) AFTER HOURS
CASING MATERIAL 2" PVC SCREEN 20' of 0.010 slots
DESCRIPTION
Black fm ROCK fragments, little fmc sand, tr silt
Brown CLAY and SILT, tr fm sand, tr f rock
fragments
8/4/86
GRAVEL PACK
BENTONITE
BACK FILL
CONCRETE
· SCREEN
{(~~~J"It··
':!."':.':. f✓• ----------
CONSTRUCTION
.. .
..
: . ....
" .
Red/Brown clayey SILT, tr f sand, tr frock fragments,
tr laminae. of light green clay
... . •,•
. ,,
Red/Brown clayey SILT (weathered bedrock),
light green laminae 14.5-16.5'
Bottom of Boring -26.5 feet
"·, ',•
..
•,•
..
•,'.
SHEET ___ OF __ _
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MONITORING.WELL LOG
PROJECT Raleigh, NC WELL NO. MW-9
DRILLING METHOD Hollow Stem Auger
DRILLER Soil Testing Services
GEOLOGIST __ S._A_._c_o_I_to_n ___ _
DATE
GROUND ELEVATION ----GROUND WATER DEPTH (ft):
TOP OF WELL AT COMPLETION -----------
DEPTH OF WELL (ft) AFTER HOURS
CASING MATERIAL 2" PVC SCREEN 16' of 0.010 slots
DESCRIPTION
Brown clayey SILT, tr f sand
8/5/86
GRAVEL PACK :~•.;.•:·
BENTONITE
BACK FILL
CONCRETE
· SCREEN ----------
CONSTRUCTION
Mottled Brown and gray/green SILT and CLAY, tr f sand,
tr_f rock fragments
Mottled Brown and gray/green clayey SILT, tr f sand
Brown clayey SILT (weathered bedrock), tr f sand,
tr m rock fragments (25-26.5')
Bottom of Boring -26_.5 feet
SHEET ___ OF __ _
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MONITORING.WELL LOG
PROJECT Raleigh, NC WELL NO. MW-10
DRILLING METHOD Hollow Stem Auger/Wash Rotary GEOLOGIST S. A. Colton
DRILLER Soil Testing Services
GROUND ELEVATION. ___ _
TOP OF WELL'------
DEPTH OF WELL (ft)
CASING MATERIAL . 2" PVC
DATE
GROUND WATER DEPTH (ft):
AT COMPLETION. ____ _
AFTER HOURS
SCREEN 7' of 0.010" slots
8/5/86
GRAVEL PACK
BENTONITE
BACK FILL
CONCRETE
· SCREEN ----------
STRATA SAMPLE
DEPTH DEPTH DESCRIPTION CONSTRUCTION
10
Maroon/Brown clayey SILT, tr f sand, roots,
light green clay pockets. 1.5-3 .0'
Maroon/Brown, gray/purple to yellow/brown clayey SILT
(weathered bedrock), tr f sand
(0 -10.5' sample descriptions taken from Boring B-4)
Bottom of Boring -28.5 feet
SHEET ___ OF __ _
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MONITORING.WELL LOG
PROJECT Raleigh, NC
DR I LL! NG METHOD __ ...:.W:..:a:::.sh:..:....:.R:.c:o-'-'ta'-r-"-y _____ _
WELL NO. MW-11
GEOLOGIST S. A. Colton
DRILLER Soil Testing Services
GROUND ELEVATION ----TOP OF WELL ____ _
DEPTH OF WELL (ft)
CASING MATERIAL 2" P\'C
DATE
GROUND WATER DEPTH (ft):
AT COMPLETION -----
AFTER HOURS
SCREEN 10' of 0.010" slots
8/19/86
GRAVEL PACK
BENTONITE
BACK FILL
CONCRETE
· SCREEN ----------
STRAT SAMPLE
DEPTH DEPTH DESCRIPTION CONSTRUCT! ON
Brown cla e SILT tr f sand roots
Brown clayey SILT .. ,jth white SILT And CLAY IRr!linae,
Brown/Red clayey SIIT (weathered bedrock), tr f sand
(0-10.5 feet sample descriptions taken from Boring B~2)
20
. · .
Bottom of Boring -32 feet·
. SHEET OF --------
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MONITORING WELL LOG
PROJECT _ _:::_Ral=e::iig,:_h2,..:.N:..::C:_ ____________ _ WELL NO. MW-12
GEOLOGIST s. A. Colton DRILLING METHOD:...____::\\as=h:...:R::.o:..:t=a..:.ry,__ _____ _
DRILLER Soil Testing Services DATE 8/19/86
GROUND ELEVATION. ___ _ GROUND WATER DEPTH (ft):
TOP OF WELL. ____ _ AT COMPLETION. ____ _
DEPTH OF WELL (ft) AFTER HOURS
CASING MATERIAL
STRAT SAMPLE
DEPTH DEPTH
10
20
30
2" PVC SCREEN 10' of 0.010" slots
DESCRIPTION
Red/Brown clayey SILT, tr f sand, tr f rock fragments,
roots
Red/Brown clayey SILT (weathered bedrock),
tr f sand
(0-12.5' sample descriptions taken from Boring B-1)
Bottom of Boring -30.5 feet
GRAVEL PACK ;~-.;.•:"
BENTON I TE
BACK FILL
CONCRETE
· SCREEN ----------
CONSTRUCT! ON
.. ,
'• ..
·.·.·
... ..
,',
· .. . .
SHEET ___ OF __ _
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BORING LOG
PROJECT Raleigh, NC BORING NO. B-1 ---
DRILLING METHOD Hollow Stem Auger GEOLOGIST s. A. Colton ---------DRILLER Soil Testing Services DATE 7/21/86
DESCRIPTION
Red/Brown clayey SILT, tr f sand, tr frock fragments, roots 0-1.5'
4
Red/Brown to Maroon clayey SILT (weathered bedrock), tr f sand
5
10----
Bottom ·of Boring -12.25 feet
SHEET OF
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5
10
BORING LOG
PROJECT Raleigh, NC ----------------DRILLING METHOD Ho))ow Stem Anger
DRILLER -Soil Testing Services
DESCRIPTION
Brown clayey SILT, tr f sand, roots
BORING NO. 8--2
GEOLOGIST s. A. Colton
DATE 7/24/86
Brown clayey SILT with white SILT and CLAY laminae, tr f sand
Brown/red clayey SILT (weathered bedrock)
Bottom of Boring -9.1 feet
SHEET OF
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5
10
BORING LOG
PROJECT Raleigh, NC BORING KO.
DRILLING METHOD Hollow Stem Auger GEOLOGIST s. A. Colton
DATE 7/24/86
DESCRIPTION
Brown clayey SILT, tr to some sand, tr f rock fragments
Red/Brown SILT and CLAY, tr f sand
Red/Brown clayey SILT (weathered bedrock), tr f sand,
tr f rock fragments
Bottom of Boring -9.3 feet
SHEET OF
B--3
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BORING LOG
PROJECT __ R-al_e~ig~h~•~N___:C _________ _
DRILLING ME1'HO'D Hollow Stem Auger
DRILLER Soil < Testing Services
DESCRIPTION
BORING NO. C-4
GEO LOG I ST S. A. Colton
DATE 7/24/86
Maroon/brown clayey SILT, tr f sand, roots, light green
clay pockets (1.5-3')
Maroon/brown clayey SILT (weathered bedrock), tr f sand
SHEET 1 OF 2
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BORING LOG
PROJECT Raleigh, NC ----~------------
.DRILLING METHOD Hollow Stem Auger
DRILLER Soil Testing Services
STRATA SAMPL
DEPTH DEPTH DESCRIPTION
BORING NO. 8-4
GEOLOGIST S. A. Colton
DATE 7/24/86
Maroon/brown clayey SILT ( weathered bedrock), tr f sand
Bottom of Boring -22 feet
25
SHEET 2 OF 2 ----
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5
10
BORING LOG
PROJECT Raleigh, NC BORING NO, B-5
DRILLING METHOD Hn))nw Stem Auger GEO LOG I ST S. A. Colton
DRILLER Soil Testing Services DATE 7/21/86
DESCRIPTION
Brown clayey SILT, tr f sand, t fm siltstone fragments (Fill)
Lt. Brown SILT, some fm rock fragments, tr f sand, (Fill)
Brown silty CLAY, tr f sand
J?rown/Maroon SILT and CLAY, tr f sand
Maroon clayey SILT (weathered bedrock), tr f sand, tr rock fragments
SHEET_j_OF __ 2_
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BORING LOG
PROJECT ___ R_al_e_i~g~h~,_N_C _________ _
DRILLING METHOD Ho))ow Stem Auger
DRILLER Soil Testing Services
STRATA SAMPL
DEPTH DEPTH DESCRIPTION
BORING NO. B-5
GEOLOGIST S. A. Colton
DATE 7/21/86
Maroon clayey SILT (weathered bedrock), tr f sand, tr rock fragments
25
Bottom of Boring -25 feet
SHEET 2 OF 2
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BORING LOG
PROJECT Raleigh NC BORING NO. B-6
DRILLING METHOD Hollow Stem Auger GEOLOGIST S. A. Colton ----'----'----'------
DRILLER Soil Testing Services DATE 7/22/86
ST!<ATA SAMPL
DEPTH DEPTH
5
10
DESCRIPTION
Light Brown SILT, some fm rock fragments
Black, red brown siltv CLAY tr f sand
Brown CLAY and gray SILT, tr f sand, tr f gravel
Brown silty CLAY, tr f sand
Maroon clayey SILT (weathered bedrock), tr f sand
Bottom of Boring -10.5 feet
SHEET OF
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10
BORING LOG
. PROJECT Raleigh, NC
DRILLING METHOD Hollow Stem Auger
DESCRIPTION
Wood chips
Light Brown silty CLAY, tr f sand
Light Brown clayey SILT, tr f sand
Brown/green SILT and CLAY, tr f sand
BORING NO. B-7
GEOLOGIST S. A. Colton ---------DATE 7/2] /86
Red/brown clayey SILT (weathered bedrock), tr f sand
Bottom of Boring -10.25 feet
SHEET OF
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BORING LOG
PROJECT Raleigh, NC
DRILLING METHOD Hollow Stem Auger
DRILLER Soil Testing Services
BORING NO.B-1O
GEOLOGIST S.A . Colton
DATE 7/22/86
STRATA DESCRIPTION
5
Brown clayey SILT to light hrown silt (Fill)
Maroon clayey SILT (weathered bedrock), green clay laminae (7 .5-8.0)
tr f sand
Gray clayey SILT (weathered bedrock), tr f sand, tr f rock fragments
SHEET 1 OF 2 ----
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BORING LOG
. PROJECT __ ~R~al~e~ig~h~7~N~C~---------
DRILLING METHOD Hollow Stem Auger
DRILLER Soil Testing Services
STRATA SAMPL
DEPTH DEPTH DESCRIPTION
BORING NO. B-10
GEOLOGIST S.A. Colton
DATE 7/22/86
Gray clayey SILT (weathered bedrock), tr f sand, tr f rock fragments
Bottom of Boring -24.0 feet
25
SHEET 2 OF 2 ----
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10
BORING LOG
PROJECT · Raleigh, NC ·
DRILLING METHOD Hollow Stem Auger
DRILLER Soil Testing Services
DESCRIPTION
BORING NO. B-11
GEOLOGIST S.A. Colton
DATE 7 /25/86
Brown clayey SILT, tr f sand, tr f rock fragments roots
Mottled light brown silty CLAY and red/brown clayey SILT, tr f sand
Red/Brown clayey SILT, tr f sand
Mottled Red/brown clayey SILT and It. green silty CLAY, tr f sand
Red/Brown clayey SILT, tr f sand
Red/Brown clayey SILT (weathered bedrock), tr cf sand
Bottom of Boring -9.75 feet
SHEET OF
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10
BORING LOG
. PROJECT Raleigh, NC
DRILLING METHOD Hollow Stem Auger
DRILLER Soil Testing Services
DESCRIPTION
BORING NO. B--12
GEOLOGIST s. A. Colton
DATE 7/25/86
Brown, clayey SILT, tr f sand, tr f rock fragments
Light Brown silty CLAY, tr f sand
Brown SILT and CLAY, tr c sand
Light Brown/green silty CLAY, tr f sand
Light Brown CLAY and SILT, tr c sand, tr f rock fragments
Red/brown SILT and Lt. green CLAY, tr f sand
Bottom of Boring -10.5 feet
SHEET OF
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BORING LOG
PROJECT Raleigh, NC ----------------BORING No.B-14
GEO LOG I ST s. A. Colton DRILLING METHOD Hollow Stem Auger
DRILLER
STRATA SAMPL
DEPTH DEPTH
5
10
Soil Testing Services DATE 7/25/86
DESCRIPTION
Augered through fill (Lt. Brown SILT, tr f sand)
First sample at 2.5 feet ,,
Gray/brown CLAY and SILT, tr f sand, tr frock fragments
Brown/green silty CLAY, tr fm sand, tr frock fragments
Gray clayey SILT, tr f sand
Brown SILT and CLAY, tr f sand
Bottom of Boring -7 feet
SHEET OF
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BORING LOG
PROJECT Raleigh, NC BORING NO.B-15
GEOLOGIST S.A. Colton DRILLING METHOD Hollow Stem Auger
DRILLER Soil Testing Services DATE 7/25/86
DESCRIPTION
Brown CLAY and SILT tr f sand tr frock fra ments (Fill)
Light Brown SILT, little f sand, tr m rock fragments
(!.5-3.0 feet) (Fill)
Mottled Brown and green SILT and CLAY, tr f sand,
tr rock fragments (6-7 .5 feet)
Light Brown clayey SILT, tr fm sand
Mottled Red SILT and Green CLAY, tr f sand
Red/brown clayey SILT, tr f sand
Red/brown clayey SILT (weathered bedrock), tr f sand
Bottom of Boring -10.25 feet
SHEET OF
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Rj1leigh, NC
, Soil Analyses
(17 5-1792-77)
Attached are rest4ts of analyses on
September 26, 19&6'at the Raleigh site.
RDH:da
Attachment
cc: M. J. Dvorsky
R. L. Weightman
S. Colton
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IABLE 2, SUMMARY OF ORGANIC COMPOUNC,S
===========-----------==---------------
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I.: . ' I KEYSTC1NE ENV ! F1)NMENTAL RE·;ouRCE·~ ===============--=--------=================----=== ,:~==-= ~ _ :u~~~~ -~: = ~:~:~~: _ ::'~:~~~i==---ORODLJi:ED ON 11/10/8•5 AT 13:25 . ----------===========-=-----·~AMPLE # IN.960095 I I I rN3•c,0096 I I RSLT.LNE ----------------------------------------2,3,5.6Tet-•:1-pnen01 2., 4, 1~,Tr i cn 1-.:i(op•1en<:i i 2,4-Dicn1oroot1~~01 2,4-Oimett1v1pne1101 2,4-0i11itropt1e~0: ,2-ct1 ! oroi:it1eno 1 2-N i t·roo11~no l a,0-Oinitro-0-cre~oi "4-N it r-)!=dlen•) ! acn1oro3m!tt1v1011en0i PentaCt11()fOOl~~!l(,I -pr1en•:,, 2,3,5.15T~t-•:1-o~~t~Oi 2,4,0Tr1c1~1oroot,~n<)1 2,4-Di•:n1oroon~•101 2,4-Dimett1v1one,1,~1 2, 4-'D in.•: :•)pr-1e:-i•:• 1 12-Ct1 1 (,ro~•nerio: 2-N; r_ roeine'.-it:) 1 4,5-C>,rlitro-0-·:r~S(·' 4-N it ropt1,en,:; ! 4Cnloro31ne:nv1~111~!1,: i'P~nte.cti l 0:'"<):'.:1/1-0::n,::, l .ot,en•.:) 1 ✓-70. 0 ·70. ') 35,0 ?':· .' 7•J. 0 :44 ·35 O t;'..'3} 7t:, . 0 ,3 i. 3 ·35 0 715 :::--:, 4 ' ·:'-. 7,) . ') ,:··35 0 ·35. •.j . 7(1 . ,:, 4 l,:J ?-:"· 0 7 ,:i ·) , 7(, t) ' 3~. •,) 2·:-,4 ~ ,,, 1 I £1..b•:)11-=: r·-:: ~-u t ,: $ .3 re r· e 01:, r t. "= ,:-J 1 ·1 ,_J •:) . ' ~'. ,~, . I I I I I I I I ·=-OURCE 915-4.5-6 815-4.5-6 815-4 S-6 815-4 3-0 815-4.5-6 a{S-4.5~~ 915-4.5-6 ✓ 515-4 5-0 815-4.~-~ ~. a1S-4.5-6 81=,-4.5-:-.6 9·15-4.':,-t:i 91:',-9-1C• :", 8 1-:--.... ~-·1,). =· = 1 s-•;,-1 o.:: 3 ·\ 5 -.;, --1 0 . 5 5 I ~--'~1 -1 l) . 5 3 1.:·-~,--,0. s 8 ~ :.-.;.;-1 0. ,5 °?-i 5 -·:::' -I O . 5 / / 31:-;1-10 :, 3 ., 5 -'~• - 1 ,) . 3 ·I:,--,~~--1 i), : ' / -· 3 I 5--~•-1 •') .-5-::" DA<3E 8 =========
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BOUNDARY
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SCALE (FEET}
100 100 200 300
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LOCATION HAP
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KOPPERS COMPANY, me.
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SAMPLE ~ 1---------N860002
RN860003
-N860004
N860005
N860006
RN860007
IN860008
N860009
RN860010
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KEYSTONE ENVIRONMENTAL RESOURCES
PRODUCED ON 10/24/86 AT 10,36 PAGE
SOURCE DESCRIPT DATE-COL DATE-REC
---------------------------------------------------
\I/ELL M\11-4 MONITORING \1/E L LS 09/09/86 09/10/86
\1/E LL M\11-6 MONITORING WELLS 09/09/86 09/10/86
\1/E LL M\11-7 MONITORING WELLS 09/09/86 09/10/86
\1/E LL M\11-8 MONITORING WELLS 09/09/86 09/10/86
\I/ELL M\11-10 MONITORING \1/E LL S 09/09/86 09/10/86
\1/E LL M\11-11 MONITORING WELLS 09/09/96 09/10/86
WELL M\11-12 MONITORING \1/E L LS 09/09/86 09/10/86
\1/E LL FB MONITORING WELLS 09/09/86 09/10/86
\1/E LL TB MONITORING WELLS 09/09/86 09/10/86
m· ' m KEYSTONE ENVIRONMENTAL RESOURCES =•••••••••••====z==•==••••••=••••=••==•=•••••••••• TABLE 1: SUMMARY OF ANALYTICAL DATA PRODUCED ON 10/24/86 AT 10:41 PAGE· 1····•=••=••············-···•===•=•=•=•== ==•=•===•======~==•========== ======== SAMPLE# RSLT.LNE SOURCE 1--------------------------------------------------CHEMICAL OXYGEN DEMAND ---------------RN860002 COD (Total), mg/L: 40.0 IRN860003 RN.860004 RN86000:5 RN860006 IRN860007 RN860008 RN860009 COD <Total>, mg/L·: 50.0 COD ( TO ta I > , mg/ L : < 1 0 . 0 coo <Total>, mg/L: 50.0 coo <Total>, mg/L: 35.0 coo (Total>, mg/L: 40.0 coo <Total>, mg/L: 20.0 coo ( TO ta I > , mg/ L: < 1 0. 0 I CONDUCTIVITY · RN860002 cona. ,umnos/cm RN860003 cona. ,umnos/cm II RN860004 cona. , umnos/cm IIRN860005 cona. ,umnos/cm 1508 1796 1778 RN860006 cona. ,umnos/cm 951 990 1200 1 185 0.00 o. oo· RN860007 II RN960008 II RN860009 RN9600 1 0 . I PHENOL RN860002 RN860003 cona. , umnos/cm cona. , umnos/cm cona. ,umnos/cm cona. , umnos/cm Pneno I mg/L: Phenol mg/L: IRN860004 Pnenol mg/L: RN860005 Phenol mg/L: RNS60006 Pnenol mg/L: 0.005 0.006 0.005 0.005 (0.005 0 . 0 1 1 <0.005 <0.005 R~860007 Phenol mg/L: DRN960008 Phenol mg/L: RN860009 Pnenol mg/L: TOTAL ORGANIC CARBON H RN960003 TOC, mg/L: 3.85 RN860006 TOC, mg/L: 3. 15 RN860008 TOC, mg/L: 3.74 I RN860004 TOC, mg/L: 4.70 RN860002 TOC, mg/L: 5.47 RN860007 TOC, mg/L: 6. 19 RN960005 TOC, mg/L: 9. 17 I RN860009 TOC, mg/L: < 1. 00 pH RN860002 PH, un ts 8. 1 I RN860003 PH, un ts 7.4 RN860004 PH, un ts 7.7 RN860005 PH, un ts 7. 1 D RN860006 PH, un ts 6.4 RN860007 pH, un ts 7.7 RN860008 PH, uni ts 7.5 RN860009 PH, uni ts 7.3 I RNS60010 PH, uni ts 7.8 I WELL MW-4 WELL MW-6 WELL MW-7 WELL MW-8 WELL MW-10 WELL MW-11 WELL MW-12 WELL FB . 'I WELL MW-4 ~;f· WELL MW-6 WELL MW-7 WELL MW-8 WELL MW-10 WELL MW-11 WELL MW-12 WELL FB WELL TB WELL MW-4 \I/ELL M\11-6 \I/ELL MW-7 \I/ELL M\11-8 \I/ELL M\11-10 \I/ELL M\11-11 \I/ELL M\11-12 \1/E LL FB WELL MW-6 WELL M\11-10 \I/ELL MW-12 WELL M\11-7 WELL M\11-4 \I/ELL M\11-11 \1/E LL M\11-8 WELL FB WELL M\11-4 \I/ELL MW-6 \I/ELL MW-7 WELL MW-8 WELL MW-10 WELL MW-11 \I/ELL MW-12 \I/ELL FB \I/ELL TB
KEYSTONE ENVIRONMENTAL RESOURCES
· •ABLE 1: SUIYMARY OF ANALYTICAL DATA PRODUCED ON 10/24/86 AT 10:41
l======~=·s•=•a••••••••a•=•============== =======•=•==•===============•
PAGE 2
SAMPLE >It ASL T. LNE SOURCE 1---------
TOTAL DISSOVLED SOLIDS
~
RN860002
N860003
N860004
RNB60005
mg/L,
mg/L,
mg/L,
TDS @103
TDS @103
TDS @103
C
C
C
947
1133
1320
675
635
1020
WELL
WELL
WELL
< M\1/-4
)\ll f'7 I MW-6
M\1/-7
I N860006
N860007
AN860008
rN860009
I
I
I
I
I
I
I
I
I
I
I
mg/L,
mg/L,
mg/L,
mg/L,
mg/L,
TDS @103
TDS @ 163
TDS @103
TDS @103
TDS @103
C
C
C
C
C
870
38.0
\I/ELL
WELL
WELL
WELL
\1/E LL
MW-8
MW-10
MW-11
M\IJ-12
FB
I
I
'AMPLE .to ---------CHLORIDE
RN860002
IN860003
N860004
RN860005
IJN860006
N860007
RN860008
IEN860009
LUORIDE
N860002
RN860003
INB60004
N860005
RN860006
llt860007 NB60008
RN860009 f ITRATE
· N860002
NB60003
RN960004
ltNB60005
N960006
RNB60007
IFNB60009
NB60009
NITRITE
tNS60002
N860003
N960004
RNB60005
lt860006
NB60007
RN860008
IN860009
ULFATE
RN860002
EN860003
NB60004
NB60005
RN860006
tN860007
NB6000B
RN860009
I
I
KEYSTONE ENVIRONMENTAL RESOURCES
PRODUCED ON 10/24/86 AT 10:41 PAGE 1
m•aam:iaaa
RSLT. LNE SOURCE
-------------------------------------------------------
cn1oriae, mg/L: 136 \I/ELL M\1/-4
cn1oriae, mg/L: 330 \1/E LL M\1/-6
Chloride, mg/L: 253 \1/E LL M\1/-7
cn1oriae, mg/L: 68.0 \I/ELL M\1/-8
cn1oriae, mg/L: 126 \I/ELL M\1/-10
tn 1or i ae, mg/L: 97.0 \1/E LL M\1/-1 1
cn1oriae, mg/L: 107 \1/E LL M\1/-12
cn1oriae, mg/L: < 1 . 00 \1/E LL FB
F1uorioe, mg/L: 0.610 \1/E LL M\1/-4
Fluoriae, mg/L: 0.500 \1/E LL M\1/-6
Fluoride, mg/L: 0.520 \1/E LL M\1/-7
Fluoriae, mg/L: 0.290 WELL MW-8
Fluoriae, mg/L: 0 .310 WELL M\1/-10
Fluor i ae. mg/L: 0.680 WELL M\1/-1 1
Fluoride, mg/L: 0 540 WELL M\1/-12
Fluoriae, mg/L: 0 ~ 1 1 0 WELL FB
Nitrate as N, mg/L: <0.100 WELL M\1/-4
Nit.rate as N, mg/L: .<0.100 WELL M\1/-6
Nitrate as N' mg/L: <0. 100 WELL M\1/-7
Nitrate as N, mg/L: < 0. 1 00 WELL M\11-8
Nitrate as N, mg/L: < 0. 1 00 \I/ELL M\1/-10
Nitrate as N • mg/L: < 0. 100 11/E LL M\1/-1 1
Nitrate as N, mg/L: < 0 . 1 00 WELL MW-12
Nitrate as N, mg/L: < 0. 1 00 WELL FB
Nitrite as N, mg/L: <0.010 WELL MW-4
Nitrite as N, mg/L: <0.010 WELL MW-6
Nitrite as N, mg/L: (0.010 WELL M\1/-7
Nitrite as N, mg/L: (0.010 WELL MW-8
Nitrite as N • mg/L: <0.010 WELL MW-10
Nitrite a5 N • mg/L: <0.010 WELL M\1/-11
Nitrite as N, mg/L: <0.010 WELL M\&1-12
Nitrite as N, mg/L: <0.010 WELL FB
SUifate, mg/L: 24.7 WELL M\1/-4
Sulfate, mg/L: (10.0 WELL M\1/-6
Sulfate, mg/L: · (10.0 \1/E LL M\1/-7
Sulfate, mg/L: <10.0 WELL MW-B
sulfate, mg/L: < 10. 0 WELL M\1/-10
SUifate, mg/L: 153 \1/E LL M\1/-11
sulfate, mg/L: 45.5 WELL M\1/-12
Sulfate, mg/L: <10.0 11/E LL FB
SAMPLE*
1------.---
RSEN IC
RN860002
'
N860003
N860004
N860005
RN860006
lt N860007
N860008
RN860009
lf'N8600l0
fFALCIUM
RN860002
~
N860003
N860004
N860005
RNS60006
~NS60007
flqNS60008
RN860009
lf'lN8600l0
IFHROMIUM
RN860002
tRN860003
N860004
NS60005
RN860006
IRNS60007
RNS60008
RN860009
DRN8600l0
MAGNESIUM
RN860002
RN860003
nRN860004
HRN860005
RN860006
IRN860007
RN860009
RN860009
IRNS60010
6
R
I
KEYSTONE ENVIRONMENTAL RESOURCES
PRODUCED ON 10/24/86 AT 10:47 PAGE
RSL T. LNE SOURCE
-------------------------------------------------------
Arsenic, mg/L: <0.010 \I/ELL M\11-4
Arsenic, mg/L: <0.010 \1/E LL M\1/-6
Arsenic, mg/L: <0.010 \1/E LL M\11-7
Arsenic, mg/L: <0.010 \I/ELL M\1/-9
Arsenic, mg/L: <0.010 \1/E LL M\11-10
Arsenic, mg/L: <0.010 \I/ELL M\11-1 1
Arsenic, mg/L: <0.010 \1/E LL M\11-12
Arsenic, mg/L: 0.011 \1/E LL F'S
Arsenic, mg/L: <0.010 \1/E LL TB
ca1c ·um, mg/L: 25.5 \1/E LL M\11-4
Cale um, mg/L: 57.9 \1/E LL MW-6
Cale um, mg/L: 50.4 \1/E LL M\11-7
Cale um, mg/L: 41 . 0 \I/ELL MW-9
ca1c um, mg/L: 53.3 \1/E LL M\11-10
Cale um, • mg/L: 45.4 \1/E LL M\11-11 .
ca1c um, mg/L: 36.7 \1/E LL M\1/-12
Cale ium, mg/L: < 1 . 00 \I/ELL F'B
Calcium, mg/L: < I . 00 \1/E LL TB
cnrom i um, mg/L: <0.050 \1/E LL M\11-4
cnromium, mg/L: (0.050 \I/ELL MW-6
cnromium, mg/L: <0.050 \1/E LL M\11-7
Chromium, mg/L: (0.050 \1/E LL MW-8
cnro,n:um, mg/L: <0.050 WELL M\11-10
cnromium, mg/L: <0.050 \1/E LL M\11-11
cnromium, mg/L: <0.050 \1/E LL MW-12
cnromium, mg/L: <0.050 \1/E LL F'B
cnromium, mg/L: <0.050 \1/E LL TB
Magnesium, mg/L: 35.2 \1/E LL M\11-4
Magnesium, mg/L: 53.9 \1/E LL MW-6
Magne5ium, mg/L: 64.9 \1/E LL M\1/-7
Magnesium, mg/L: 31 . 1 \I/ELL M\11-9
Magnesium, mg/L: 38.2 \1/E LL M\11-10
Magnesium, mg/L: 32.4 \1/E LL M\11-I I
Magnesium, mg/L: 33.2 \I/ELL M\11-12
Magnesium, mg/L: < 1 . 0 \1/E LL F'S
Magnesium, mg/L: (1.0 \1/E LL TB
i! KEYSTONE ENVIRONMENTAL RESOURCES
I .-2a•==•••••••••••••••••••s••====== ==m=• .
SAMPLE~ RSLT.LNE
PRODUCED ON 10/24/86 AT 10:47
SOURCE I, TABLE 3: SUl>'MARY OF METALS DATA
1--------------------------------------------------
POTASSIUM
RN860002
---------------
I RN860003
RN860004
RN860005
RN860006
IRN860007
RN860008
RN860009
II RN860010
IISOO I UM
RN860002
IRN860003
RN860004
RN860005
RN860006
IRN860007
RN860008
RN860009
IRN860010
H
n
I
I
I
I
I
I
I
Potassium,
Potassium,
Potassium,
Potassium,
Potassium,
Potassium,
Potassium,
Potassium,
Potassium,
mg/L:
mg/L:
mg/L:
mg/L:
mg/L:
mg/L:
mg/L:
mg/L:
mg/L:
soaium, mg/L: 140
soaium, mg/L: 184
soaium, mg/L: 150
9.85
3.37
7.69
3.30
4.62
7.47
5.48
< 1 . 00
< 1. 00
soaium, mg/L: 53.2
sodium, mg/L: 44.2
soaium. mg/L: 82.0
soaium, •,ng/L: 56.7
soaium, mg/L: < 1 . 00
soaium, mg/L: < 1 . 00
II/ELL M\11-4
IIIE LL M\11-6
II/ELL M\11-7
II/ELL Mlll-8
II/ELL M\11-10
11/E LL MIii-1 1
IIIE LL M\11-12
11/E LL FB
11/E LL TB
II/ELL M\11-4
II/ELL Mlll-6
11/E LL M\11-7
11/E LL M\11-S
11/E LL MIii-10
11/E LL M\11-11
11/E LL Mlll-12
11/E LL FB
11/E LL TB
PAGE 2
======-==
I
KEYSTONE ENVIRONMENTAL RESOURCES
SAMPLE* RSLT.LNE
l;~~;~~~;;o~~;~;~-;~-;;;-~;~~;;-~~~----------------
RN860002 Pentacn1oropneno1 57.1
lf'lN860003
rN860004
RN860005
0RN860006
11Fi°N860007
IIRN860008
RN860010
Pentacn1oropneno1 163
Pentacn1oropneno1
Pentacn1oropneno1
Pentacn1oropneno1
Pentacn1oropneno1
Pentacn1oropneno1
Pentacn1oropneno1
< 1. 00
1 1 . 4
71. 2·
< 1 . 00
< 1. 00
< 1 . 00
gAoove resu1ts are reportea in Ug/L.
I
I
n
I
I
I
I
I
I
I
I
SOURCE ---------------
\I/ELL M\11-4;,
\I/ELL M\11-61 ..
\1/E LL M\11-7
\1/E LL M\IJ-e:
\1/E LL M\11-10 '·. \1/E LL M\11-11
\1/E LL M\11-12
\1/E LL TB
SAMPLE#
l~;;;;;;--
RNB60003
INB60004
N860005
N860006
RNB60007
I N86000B
N860009
RN860010
D
I
n
I
I
I
I
I
I
I
I
I
RSL T. LNE
1sopropy1
1sopropy1
1sopropy1
1sopropy1
1 sopropy I
1sopropy1
1sopropy1
1sopropy1
1sopropy1
KEYSTONE ENVIRONMENTAL RESOURCES
PRODUCED ON 10/28/86 AT 07:22 PAGE
SOURCE
Etner,ug/L: {100 WELL MW-4
Etner,ug/L: {100 WELL MW-6
Etner,ug/L: {100 WELL MW-7
Etner,ug/L: < 100 WELL MW-8
Etner,ug/L: < 100 WELL MW-10
Etner,ug/L: (100 WELL MW-11
Etner,ug/L: < 100 WELL MW-12
Etner,ug/L: (100 WELL FB
Etner,u9/L: (100 WELL TB
·1
I
"
KEYSTONE ENVIRONMENTAL RESOURCES
···········•·=•=••••=••=•==•===••==•=====7=•=••==
. TA.BLE OF CONTENTS PRODUCED OM 10/24/86 AT 10: 56
I= ••••• -.~.; •• --• ----.-· •••••• ---•=•. = --= ---==== = = =. -= ·11. •= =. = = === = = =• = -
SAMPLE • 1----------
RN860035
RN860036
IRN860037
RN860038
RN860039
n
I
I
I
u
H
n
I
I
I
I
I
RN860040
SOURCE ---------------
\I/ELL MIii-1
\1/E LL M\11-2
\1/E LL M\11-3
\1/E LL M\11-5
\I/ELL M\/J-9
FB
DESCRIPT DATE-COL DATE-REC
------------------------------------
MONITORING \I/EL LS 09/10/86 09/11/86
MONITORING \I/EL LS 09/10/86 09/11/86
MONITORING \1/E LL S 09/10/86 09/11/86
MONITORING WELLS 09/10/86 09/11/86
MONITORING \I/ELLS 09/10/86 09/11/86
MONITORING WELLS 09/10/86 09/11/86
PAGE
===zi====
I
I KEYSTONE ENVIRONMENTAL RESOURCES
PRODUCED ON 10/24/86 AT 10,57 PAGE
ISAMPLE * RSLT.LNE . --------------------------------------------------
CHEMICAL OXYGEN DEMAND
RN860035 COD (Total), mg/L, 50.0
IRNS60036 COD (Total), mg/L, 75.0
RN860037 COD (Total>, mg/L, 20.0
RN860038 COD (Total), mg/L, 52.0
URN860039 COD (Total), mg/L, 15.0
RN860040 -coo < Tota I),
CONDUCTIVITY
m9/L, <10.0
RNS60035 cone. ,umnos/cm 1580
IRN860036 cone. ,umnos/cm 1350
RN860037 cone. ,umnostcm 750
RN860039 cone. ,umnos/cm 550
IRN860040 cone. ,umnos/cm 0.00
PHENOL
RN860035 Pnenol mg/L, <0.005
URN860036 Pneno1 mg/L, <0.005
RN860037 Pner.i? 1 ,:ng/L, ·0.0211
RN860038 Pneno t, mg/L, <0.005
RNS60039 Pneno1, mg/L, <0.005
IRNS60040 Pneno1, mg1L, <0.005
TOTAL ORGANIC CARBON
RN860035 TOC, mg/L, 10.77
IRNS60036 TOC,
RN860037 TOC,
mg/L, 5.53
mg/L, 41. 66
RN860038 TOC, mg/L, 4.33
IIRN860039 TOC, mg/L, 4.98
mg/L, 1 . 06 IIRN860040 TOC,
TOTAL DISSOLVED SOLIDS
RNS60035
IIRN86003<3
IIRN860037
RN860038
IRN860039
RN860040
pH
I
RN860035
RN860036
RN860037
RNS60039
IRN860040
I
I
I
mg/L,
mg/L,
mg/L,
mg/L,
mg/L,
mg/L,
TDS
TDS
TDS
TDS
TDS
TDS
pH, uni ts
pH, units
pH, units
pH, units
pH, units
@103 C
@103 C
@103 C
@103 C
@103 C
@103 C
7. 1
7.5
6.7
7.2
6.3
1000
832
650
975
480
68.0
SOURCE ---------------
\I/ELL M\11-1
\I/ELL M\11-2
\1/E LL M\11-3
\1/E LL M\11-5
WELL M\11-9
FB
\I/ELL M\11-1
\I/ELL M\11-2
\I/ELL M\11-3.
\1/E LL M\11-9
FB
\1/E LL M\11-1
WELL M\11-2
\1/E LL M\11-_3 -~
\1/E LL M\11-5
WELL M\11-9
FB
\I/ELL M\11-1
\liELL M\11-2
WELL M\11-3 . ...--------
'IIE LL M\11-5
WELL M\11-9
FB
WELL M\11-1
WELL M\11-2
WELL M\11-3
WELL M\11-5
WELL M\11-9
FB
\I/ELL MW-1
WELL M\11-2
WELL M\11-3
\1/E LL M\11-9
FB
I
I
IISAMPLE <I
11----------
CHLORIDE
RN860035 t N860036
N860037
RN860038
lf"N860039
lf'N860040
FLUORIDE
RN860035 IRN860036
RN860037
RN860038
IIRN860039
IRN860040
NITRATE
IRN860035
RN860036
RN860037
RN860038
RRN860039
HRN860040
NITRITE
IRN860035
RN860036
RN860037
IRN86003,3
RN860039
RN860040
SULFATE
IRN860035
RN860036
RN860037
IRN860038
RN860039
RN860040
I
I
I
I
I
KEYSTONE ENVIRONMENTAL RESOURCES
PRODUCED ON 10/24/86 AT 11:00 PAGE 1
==-=t==== ..
RSL T. LNE SOURCE ---------------
cn1oriae, mg/L: 102 WELL M\11-1
cn1oriae, mg/L: 53. 0 WELL M\11-2
cn1oriae, mg/L: 53 .0 WELL M\11-3
cn1oriae, mg/L: 223 WELL M\11-5
cn1oriae, mg/L: 33.0 \I/ELL MW-9
cn1oriae, mg/L: < 1 . 00 FS
F 1uor i de, mg/L: 0. 44°0 \I/ELL M\11-1
Fluoriae, mg/L: 0.540 \1/E LL M\11-2
F1uoriae, mg/L: 0,700 WELL M\11-3
Fluoride, mg/L: 0.480 \I/ELL M\11-5
Fluor.ice, mg/L: 0.490 WELL M\11-9
Fluoride, mg/L: 0.350 FB
Nitrate a:s N, mg/L: < 0. 100 WELL M\11-1
Nitrate as N, m9/L: < 0. 100 WELL M\11-2
Nitrate as N, mg/L: <0. 100 WELL M\11-3
Nitrate as N, mg/L: < 0 . 100 \1/E LL MW-5
Nitrate as N, mg/L: < 0. 1 00 WELL MW-<?
Nitrate as N • m•~/L: <0. 100 FS
Nitrite as N, mg/L: <0.010 WELL MW-1
Nitrite. as N, mg/L: <0.010 •,.;ELL M\11-2
Nitrite as N, mg/L: (0.010 \I/ELL MW-3
Nitrite as N, mt;i/L: <0.010 \I/ELL M\11-5
Nitrite as N, mg/L: <0.010 WELL M\11-9
Nitrite as N, mg/L: <0.010 FB
su1fate, m9/L: 27.3 WELL M\11-1
Sulfate, mg/L: 36.8 \I/ELL MW-2
Sulfate, m,;J/L: 22.7 WELL M\11-3
SUifate, mg/L: 23,0 \1/E LL M\11-5
su1fate, mg/L: 30,6 WELL M\11-9
SUifate, mg/L: 15,8 FB
I
I
SAMPLE*
l;;;~~~---
RN960035
IN860036
N960037
N960039
RN960039
I N960040
ALCIUM
RN960035
I N960036
N860037
RN960039
l:'!N960039
N960040
HROMIUM
RN860035
ltN860036
itNS60037
RN860038
IN860039
N860040
AGNES I UM
i N860035
N860036
N860037
RN860038 I N860039
N860040
POTASSIUM
~
N660035
N86Q0:36
N860037
RN860038 I N860039'
N860040
SODIUM
i):,NS60035
lisN860036
RN860037
lfN860038
rN860039
RN860040
I
I
I
KEYSTONE ENVIRONMENTAL RESOURCES
PRODUCED ON 10/24/86 AT 10:59 PAGE
:a:a=:11:11==•
RSL T. LNE SOURCE ---------------
Ar3enic, mg/L: <0.010 \I/ELL M\11-1
Arsenic, mg/L: 0.018 \1/E LL M\11-2
Arsenic, mg/L: (0.010 \1/E LL M\11-3
Arsenic, mg/L: <0.010 \I/ELL M\11-5
Arsenic, mg/L: <0.010 \I/ELL M\11-9
Arsenic, mg/L: <0.010 FB
calcium, mg/L: 35.9 \1/E LL M\11-1
Calcium, mg/L: 23.5 \1/E LL M\11-2
Calcium, mg/L: 17.0 \1/E LL M\11-:3
ca1c ;um, mg/L: 46.9 \1/E LL M\11-5
Calcium, mg/L: 22.4 \1/E LL M\11-9
Calcium, mg/L: < 1 . 00 FB
cnromium, mg/L: <0.050 \I/ELL M\11-1
cnromium, mg/L: <0.050 \I/ELL M\11-2
cnromium, mg/L: ,-o. 050 \I/ELL MW-3
cnromium, mg/L: <0.050 l<iE LL M\11-5
Chromium, mg/L: <0.050 \I/ELL M\11-9
cnromium, mg/L: <0.050 FB
Magnesium, mg/L: 31. 0 \1/E LL M\11-1
Magnesium, mg/L: 26.8 \1/E LL M\11-2
Magnesium, mg/L: 20.4 WELL M\11-3
Magnesium, mg/L: 51. 9 \1/E LL MW-~
Magnesium, mg/L: 9.75 \I/ELL M\11-9
Magnesium, m,;i/L: < 1 . 00 FB
Potassium, mg/L: 9.25 \1/E LL M\11-1
Potassium, mg/L: 5.55 \1/E LL M\11-2
Potassium, mg/L: 6. 65 \I/ELL M\11-3
Potassium, mg/L: 9.59 \1/E LL MW-5
Potassium, mg/L: 3.63 \1/E LL M\11-9
Pota55ium, mg/L: < 1 . 00 FB
soaium, mg/L: 233 \I/ELL MW-1
Sodium, mg/L: 207 \I/ELL M\11-2
SOdium, mg/L: 149 \I/ELL M\11-3
SOOium, mg/L: 180 WELL M\11-5
SOdium, mg/L: 56.8 \1/E LL MW-9
SOOium, mg/L: < 1 . 00 FB
I
I KEYSTONE ENVIRONMENTAL RESOURCES
PRODUCED ON 10/24/86 AT 11:01
SAMPLE~ RSLT.LNE SOURCE
1;~~;~~~;;0;~;~;:-;~-;;;-~;~~;~-~~~----------------
RN860035 Pentacn1oropneno1 <1.00/
-
N. 860036 P.entacn Io ropneno 1 < 1 . oo
N~60037 Pentacn1oropneno1 5.85
N86003B Pentacn I oropneno 1 : -411
RNB60039 Pentacn1oropneno1 4.28
IIN860040 Pentacti I oropneno I . 1. 96
lloove results are reportea in ug/L.
I
I
I
I
u
H
I
I
I
I
I
I
I
WELL M\11-1
\I/ELL
\1/E LL
\I/ELL
-WE L. L
FB ~
MW-2
M\li-3,/
Mw-5:?--
M\i/-,,,.('
' )
PAGE
• I
I KEYSTONE ENVIRONMENTAL RESOURCES
TABLE 5: SUMMARY OF ANALYTICAL DATA
lla::z=•••=~•~•••••••••••••••a•••=••=======•
PRODUCED ON 10/27/86 AT 12:01
SAMPLE .. RSLT.LNE SOURCE
~~;~;;;;------------------------------------------
RN860036
11:N860037
ll:N860038
RN860039
RN860040
I
I
I
I
I
u
H
I
I
I
I
I
I
I
1sopropy1
1sopropy1
1sopropy1
1sopropy1
1sopropy1
1sopropy1
Etner,ug/L: (100
Etner,ug/L: < 100
Etner,ug/L: <100
Etner,ug/L: (100
Etner,ug/L: < ·100
Etner,ug/L: <100
' \I/ELL M\11-1
\1/E LL M\11-2
\1/E LL M\11-3
\I/ELL M\11-5
\1/E LL M\11-9
FB
PAGE
===cia::a:a
I
I KEYSTONE ENVIRONMENTAL RESOURCES
"ABLE OF CONTENTS 11 1
_ c =::1::,.'c:11 •• • :ir •:a••••••••••=-•==: a a a==-:a :::1 =
PRODUCED ON 10/24/86 AT 10:52 PAGE
r=•a-. .
SAMPLE ,I
It---------N860029
RN860030
~N860031
N860032
N860033
RN860034 I
I
n
I
I
I
I
I
I
I
I
I
I
I
SOURCE ---------------
\I/ELL \II-1
\1/E LL \11-2
\1/E LL \11-3
WELL \11-4
\I/ELL W-5
\1/E LL \11-14
DESCRIPT DATE-COL DATE-REC
------------------------------------
MONITORING \I/EL LS 09/ 10/,S6 09/11/86
MONITORING \I/ELLS 09/10/86 09/11/86
MONITORING \I/ELLS 09/10/86 09/11/86
MONITORING \I/ELLS 09/10/86 09/11/86
MONIT!)RING WELLS 09/10/86 09/11/86
MONITORING \I/ELLS 09/10/86 09/11/86
I
I KEYSTONE ENVIRONMENTAL RESOURCES
SAMPLE* RSLT.LNE l~:;~~~;~-;x~~~~-~~~~~~-----------------------------
RN860029 COD (Total), mg/L: <10.0
IRN860030 COD (Total), mg/L: (10.0
RN860031 COD
RN860032 COD
<Total>, mg/L: (10.0
<Total>, mg/L: -20. 0
RN860033 COD <Total>, mg/L: (10.0
nRN860034 .. COD
llcoNDUCT Iv I TY
<Total>, mg/L: 25.0
RN860029 II RN860030 II RN860031
RN860032
IRN860033
RN860034
PHENOL
RN860029
0RN860030 II RN860031
cone. , umnos/cm
cone. , umnos1cm
cone. , umnos/cm
cone. ,umnos1cm
cone. , umnos1cm
cone. ,umnos/cm
670
530
520
1000
350
1 130
Pnenol, mg/L: <0.005
Pnenol, mg/L: <0.005
Pneno1, mg/L: <0.005
RNS60032 Pnenol, mg/L: (0.005
(0.005
(0.005 IRNS60033 Pneno 1 , mg/L:
RNS60034 Pnenol, mg/L:
TOTAL O_RGAN IC CARBON
IRN860029
RN860030
RN860031
RN860032
IRN860033
RN860034
TOC, mg/L:
TOC, mg/L:
TOC, mg/L:
TOC, mg/L:
TOC, mg/L:
TOC, mg/L:
< 1 . 00
< 1 . 00
< 1 . 00
1 . 65
< 1 . 00
2.00
TOTAL DISSOLVED SOLIDS
IRN860029
RN860030
RN860031
I RN860032
RN860033
RN860034
pH
I RN860029
RN860030
RN860031
I RN860032
RN860033
RN860034
I
I
I
mg/L, TDS @103 C
mg/L, TDS
mg/L, TDS
mg/L, TDS
mg/L, TDS
mg/L, TDS
pH, uni ts
pH, un I ts
pH, units
pH, units
pH, uni ts
pH, ·uni ts
@103
@103
@103
@103
@103
C
C
C
C
C
7.4
7.4
7.5
7.2
7.5
7. 1
386
308
290
630
264
742
SOURCE ---------------
\I/ELL \II-1
\1/E LL 111-2
\1/E LL 111-3
\1/E LL 111-4
\I/ELL 111-5
\I/ELL \11-14
\1/E LL \II-1
\I/ELL 111-2
\1/E LL 111-3
\1/E LL \11-4
\1/E LL 111-5
\I/ELL \II-14
\1/E LL Ill-1
\I/ELL 111-2
\1/E LL 111-3
\I/ELL 111-4
\I/ELL \II-5
WELL W-14
\I/ELL \II-1
\I/ELL W-2
·WELL 111-3
\I/ELL W-4
\1/E LL W-5
\1/E LL W-14
\I/ELL \II-1
WELL 111-2
WELL W-3
WELL IJl-4
\1/E LL W-5
WELL W-14
IJIE LL W-1
IJIEL L IJl-2
\I/ELL 111-3
WELL IJl-4
WELL 111-5
WELL W-14
I
I
SAMPLE#
1~~;;~~~--
RN860029
'
N860030
N860031
N860032
RN860033
I N860034
LUORIDE
RN860029
-
N860030
N860031
N860032
tN860033
N860034
ITRATE
RN860029
I N860030
N860031
RN860032
-
N860033
N860034
!TRITE
RN860029 I N860030
N860031
RN860032
lfN860033
lflN860034
SULFATE
'
~
N860029
N860030
N860031
RN860032
lt N860033
N860034
I
I
KEYSTONE ENVIRONMENTAL RESOURCES
PRODUCED ON 10/24/86 AT 10:54
RSLT.LNE ----------------------------------------
cn1or oe, mg/L:
cn1or oe, mg/L:
cn1or oe, mg/L:
cn1or oe, mg/L:
29.0
16.0
23.0
126
cn1or oe, mg/L: 14.0
cn1or oe, mg/L: 141
Fluorioe, mg/L: 0.150
Fluorioe, mg/L: 0.150
Fluori0e, mg/L: 0.310
Fluorioe, mg/L: 0.150
Fluorioe, mg/L: 0.150
Fluorioe, mg/L: 0.400
Nitrate as N, mg/L:
Nitrate as N, mg/L:
Nitrate as N, mg,~,
Nitrate as N, mg/L:
Nitrate as N, mg/L:
Nitrate as N, mg/L:
Nitrite as N, mg/L:
Nitrite as N, mg/L:
Nitrite as N, mg/L:
Nitrite as N, mg/L:
Nitrite as N, mg/L:
Nitrite as N, mg/L:
Sulfate, mg/L: 12.5
Sulfate, mg/L: 23.2
sulfate, mg/L:
Sulfate, mg/L:
SUifate, rng/L:
sulfate, mg/L:
14.6
16.3
1 1 . 9
25.2
< 0 . 1 00
0.254
1. 60
< 0. 100
0.978
< 0 . 1 00
<0.010
<0.010
(0,010
<0.010
<0.010
<0.010
SOURCE ---------------
\I/ELL \11-1
\I/ELL \11-2
\1/E LL \11-3
\1/E LL \11-4
\I/ELL \11-5
\I/ELL \11-14
\1/E LL \II-1
\I/ELL \11-2
\1/E LL \11-3
\I/ELL \11-4
\1/E LL \11-5
\1/E LL \11-14
\1/E LL \11-1
\1/E LL \11-2
\1/E LL \11-3
\1/E LL \11-4
\1/E LL \11-5
\1/E LL \11-14
\1/E LL \11-1
\1/E LL \11-2
\1/E LL W-3
WELL W-4
WELL W-5
WELL W-14
WELL W-1
WELL W-2
WELL W-3
WELL W-4
WELL W-5
WELL W-14
PAGE 1
I
I
SAMPLE* l;;;;~~~---
RNS60029
IRN860030
RN860031
RN860032
RN860033
IIRN860034
llcALCIUM
RN860029
IRN860030
RN860031
RN860032
IRN860033
RN860034
CHROMIUM
RN860029
IRN860030
RN860031
RN860032
IRN860033
RN860034
MAGNESIUM
IIRN860029
IIRN860030
RN860031
RN860032
IRN860033
RN860034
POTASSIUM
I RN860029
RN860030
RN860031
I RN860032
RN860033
RN860034
SODIUM
I RN860029
RN860030
RN860031
I RN860032
RN860033
RN860034
I
I
I
KEYSTONE ENVIRONMENTAL RESOURCES
RSL T. LNE
Arsenic, mg/L: <0.010
Arsenic, mg/L: <0.010
Arsenic, mg/L: (0'.010
Arsenic, mg/L: <0.010
Arsenic, mg/L: <0.010
.Arsenic, mg/L: <0.010
calcium, mg/L: 53.0
Cale ium, mg/L: 36. 1
calcium, mg/L: 36.7
Calcium, mg/L: 97.9
calcium, mg/L: 31. 5
Cale ;um, mg/L: 1 17
cnromium, mg/L: <0.050
cnromium, mg/L: <0.050
cnromium, mg/L: ~0.050
cnromium, mg/L: <0.050
cnromium, mg/L:
cnromium, mg/L:
Magnesium, mg/L:
Magnesium, mg/L:
Magnesium, mg/L:
Magnesium, mg/L:
Magnesium, mg/L:
Magnesium, m•J/L:
Potassium, mg/L:
Potassium, mg/L:
Potassium, mg/L:
Potassium, mg/L:
Potassium, mg/L:
Potassium, mg/L:
<0.050
<0.050
29.4
21. 4
19.9
28.5
14.9
22. 1
1. 90
1. 47
2.03
2.38
2.52
1. 37
SOOium, mg/L:
SOOium, mQ/L:
soo;um, mg/L:
sooium, mg/L:
sooium, mg/L:
soaium, mg/L:
12.6
13.2
16.0
27.0
15 . 1
24. 1
PRODUCED ON 10/24/86 AT 10:55 PAGE
SOURCE ---------------
\I/ELL \11-1
WELL \11-2
WELL \11-3
\I/ELL \11-4
\1/E LL \11-5
\1/E LL \11~14
\1/E LL \II-1
WELL \11-2
\1/E LL \11-3
\1/E LL \11-4
\1/E LL \11-5
\I/ELL \11-14
WELL \11-1
WELL \11-2
WELL \11-3
WELL \11-4
\I/ELL \11-5
WELL \11-14
WELL \11-1
\I/ELL \11-2
\I/ELL \11-3
WELL \11-4
\I/ELL \11-5
\I/ELL \11-14
\1/E LL \II -1
\1/E LL \11-2
\I/ELL \11-3
\I/ELL \11-4
WELL \11-5
WELL W-14
WELL \II -1
\1/E LL \11-2
\1/E LL \11-3
\I/ELL \11-4
\I/ELL \11-5
WELL \II-14
I
I KEYSTONE ENVIRONMENTAL RESOURCES
PRODUCED ON 10/24/86 AT 10:57 PAGE
SAMPLE• RSLT.LNE SOURCE
l;~~:~:~~;o;:;~~~ ;~-;;;-~;~~,;;-;~~----------------
RN860029 Pentacn1oropneno1· <1.00
rN860030
rN860031
RN860032
Pentacn1oropneno1
Pentacn1oropneno1
Pentacn1oropneno1
< 1 . 00
< 1 . 00
< 1 . 00
RN860033 Pentacn1oropneno1 c1.oo t N860034 Pentacn1oropneno1 <1.00
I
I
I
I
I
I
I
I
I
I
H
D
I
oove results are reporteo in ug/L.
\I/ELL \11-1
\1/E LL \11-2
\1/E LL \11-3
\I/ELL \11-4
\1/E LL \11-5
\1/E LL \11-14
I
I
•
•
SAMPLE # ----------
RN860029
RN860030
IRN860031
RN860032
RN860033
IRN860034
I
I
I
I
n
n
I
I
I
I
I
RSL T. LNE
1 sopropy I
1sopropy1
1sopropy1
1sopropy1
1sopropy1
1sopropy1
KEYSTONE ENVIRONMENTAL RESOURCES
PRODUCED ON 10/28/86 AT 07, 11 PAGE
SOURCE
Etner,ug1L, (100 \I/ELL 111-1
Etner,ug/Lc < 100 \I/ELL \11-2
Etner,ug1L, < 100 \I/ELL \11-3
Etner,ug1L, < 100 \I/ELL \11-4
Etner,ug/Lc < 1 00 \I/ELL 111-5
Etner,ug/Lc < 100 \I/ELL W-14
,I ' ' I KEYSTONE ENVIRONMENTAL RESOURCES as===a=•=========•==========c======•============== "ABLE OF CONTENTS PRODUCED ON 10/24/86 AT 11,00 PAGE l=••=•=•===c•=====•=•==••·•-========•=== ===========•================= ======== SAMPLE# SOURCE DESCRIPT t--------------------------------------------N860041 WELL W-6 MONITORING WELLS RN860042 lN860043 N860044 N860045 RN860046 IN860047 N860048 RN860049 I I I I u R I I I I I I I WELL W-7 MONITORING WELLS WELL W-8 MONITORING WELLS WELL W-10 MONITORING WELLS WELL W-12 MONITORING WELLS WELL W-13 MONITORING WELLS WELL W-15 MONITORING WELLS FB MONITORING WELLS TB MONITORING WELLS • DATE-COL DATE-REC ----------------09/11/86 09/12/86 09/ 1 1 /8<:, 09/12/86 0')/ 11 /86 09/ 12/,S6 09/11/86 09/12/86 09/11/86 09/12/86 09/11/85 09/12/85 09/11/86 09/12/86 09/11/85 09/12/85 09/11/86 09/12/86
,I
I ,
I KEYSTONE ENVIRONMENTAL RESOURCES
.PRODUCED ON 10/24/86 AT 11:03
l~~~~~~~~-~x::::-~::~~~-----------------------------
SOURCE ---------------
RN860041 COD (Total J, mg/L: 25.0
IRN860042 COD
RN860043 COD
RN860044 COD
IRN860045 COD
RN860046 'COD
RN860047 COD
RN860048 COD
IIRN860049 COD
llcoNoucT1v1Tv
cTotalJ,
<Tota1>,
cTotalJ,
<Total>,
<Total>,
CTOtalJ,
<Total>,
<Total>,
mg/L: 15.0
mg/L: 15.0
mg/L: 10.0
mg/L: 15.0
m,;i/L: ·12. 0
mg/L: (10.0
mg/L: <10.0
mg/L: < 10. 0
RN860041 cono. ,umnos;cm 1 100
IRN860042
RN860043
RN860044 . 1RN860045
RN8600'46
RN860047
RN860048 nRN860049
PHENOL
RN860041
IRN860042
RNS60043
RNS60044
cona. , umnos 1,:m
cono. . L1mnos1cm
cono. . L1mnos1cm
cona . ,umnos/cm
cono. ,umnos/cm
cono. ,umnos1cm
cono. ,umnos;cm
cono. ,umnos1cm
Pnenol mg/L:
Ptieno I m9 / L :
Pnenol mg/L:
P11eno 1 mg/L:
Pher.c• mg/L:
Pnenot mg/L:
750
550
850
500
' -330
390
< 1 . 00
1. 00
0 .007
<O .005
<O .005
(0,005
<0.005
(0,005
RNS60045
IRN960046
RNS60047 Pnenot mg/L: <0.005
RN860048 Pneno t , m,;i; L: <0.005
<0.005 I R.N860049 Pneno 1 , m,;i / L:
TOTAL ORGANIC CARBON
RNS60041 TOC, mg/L: 8.63
IRN860042 TOC, mg/L: 2.38
RM860043 TOC, mg/L: 4,94
RM860044 TOC, mg/L: 2. 14
IRNS60045 TOC, mg/L: 1 . 17
RN860046 TOC, mg/L: 1. 39
RN860047 TOC, mg/L: < 1. 00
RN860048 TOC, mg/L: < 1 . 00 I RN860049 TOC, mg/L: < 1 . 00
I
I
I
WELL \1/-6
\I/ELL W-7
WELL 111-8
\I/ELL 111-10
WELL 111-12
\I/ELL \l/~13
\I/ELL W-15
FB
TB
WELL 111-6
WELL 111-7
WELL 111-8
\I/ELL w-10
WELL w-12
WELL \1/-13
WELL 111-15
FB
TB
WELL 111-6
';/ELL 111-7
WELL \1/-9
WELL w-10
WELL \1/-12
WELL W-13
WELL W-15
F8
TS
WELL \1/-6
WELL 111-7
\1/E LL W-8
WELL W-10
WELL w-12
WELL 111-13
WELL W-15
FB
TB
PAGE
' I I ,
I KEYSTONE ENVIRONMENTAL RESOURCES
PRODUCED ON 10/24/86 AT 11,03
SAMPLE# RSLT.LNE SOURCE
l;;;~~;~;;o~:;;-;;:~~;-----------------------------
RN860041 mg/L, TDS @103 C 744
'
N860042 mg/L, TDS @103 C 564
N860043 mg/L, TDS @103 C 408
N860044 mg/L, TDS e{o3 C 604
RN860045 mg/L, TDS @103 C 386 IN860046 mg/L, TDS @103 C 260
N860047 366 mg/L, TDS @103 C
RN860048 38.0 mg/L, TDS @103 C
1~860049
RN860041
IN860042
N860043
N860044
RN860045 I N860046
N860047
RN860048
IN860049
I
I
I
n
I
I
I
I
I
mg/L, TDS
pH, units
pH, uni ts
pH, uni ts
pH, units
pH, uni ts
pH, units
PH, ·uni t':3
PH, units
PH, units
@103 C 48.0
7. 1
7.5
7.6
7.2
7.4
7.5
6.5
7.4
7.4
•
\I/ELL \11-6
\1/E LL W-7
WELL W-8
WELL \11-10
\1/E LL \11-12
\I/ELL \11-13
WELL \11-15
FB
TB
\1/E LL \11-6
\1/E LL \11-7
WELL W-8
\I/ELL \11-10
\1/E LL \11-12
\I/ELL \11-13
\I/ELL W-15
FB
TB
PAGE 2
========
,I
\
I KEYSTONE ENVIRONMENTAL RESOURCES
PRODUCED ON 10/24/86 AT 11,05 PAGE
SAMPLE >It RSLT.LNE SOURCE
•-----------------------------------------------------------------
CHLORIDE
RNB60041 cn1orioe, mg/L, 126 WELL W-6
IRN860042 cn1orioe, mg/L, 78.0 \1/E LL W-7
RNS60043 cn1orioe, mg/L, 53.0 WELL W-8
RN860044 cn1orioe, m•J/L, 68.0 \I/ELL W-10
RN860045 cn1orioe, mg/Lc 24.0 WELL W-12
IRN860046 -cn1orioe, mg/L, 16.0 \I/ELL \li-13
RN860047 en 1or i oe, mg/L, 19.0 WELL W-15
RN860048 cn1orioe, mg/L, < 1 . 00 F'S
IRN860049 cn1orioe, mg/L, < 1 . 00 TB
FLUORIDE
RN860041 F'luorioe, mg/L, 0.400 WELL W-6
IRN860042 F'luorioe, mg/L, 0.300 WELL W-7
RN860Q43 F'IUOri0e, mg/L, 0.240 WELL W-8
RN860044 F1uorioe, mg/L, 0.230 WELL w-10
IRN860045 F'luoriae, mg/L, 0.200 WELL W-12
RN860046 FI uor i 1::'!, mg/L, 0.280 \liE LL W-13
RN860047 Fluor.ice, mg/L: 0.200 WELL W-15
RNS60048 Fluorid,ei mg/L, 0. 130 F'S
IRN860049 F'luorioe, mg/L, 0. 120 TB
NITRATE
RN860041 Nitrate as N, mg/L, 0. 176 WELL W-6
IRN860042 Nitrate as N, m9 IL , (0, 100 WELL W-7
RNS/30043 Nitrate as N, mg/L, (0. 100 WELL w-s
RN860044 Nitrate as N; mg/L, (0. 100 WELL W-10
RN860()45 Nitrate as N, mg/L, 0.330 WELL w-12
IRN860046 Nitrate as N, mg/L, <0. 100 \I/ELL IJ./-13
-RN860047 Nitrate as N, mg/L, 0. 125 11/E LL W-15
RN860048 Nitrate as N, m,J/L, < 0 . 1 00 F'S
IRNS60049 Nitrate as N, mg/L, < 0. 100 TS
NITRITE
RN860041 Nitrite as N' mg/L, <0.010 WELL W-6
IRN860042 Nit r te as N, m91L, <0.010 'JIELL W-7
RN860043 Nit r te as N, mg/L, <0.010 WELL w-s
RN860044 Nitr fe as N, mg/L, <0.010 WELL W-10
IRN860045 Nitr te as N' mg/L, <0.010 WELL W-12
RN860046 Ni tr te as N, mg/L, <0.010 WELL W-13
RN860047 Nitr te as N, mg/L, (0.010 WELL W-15
RN860048 Nltr te as N, mg/L, <0.010 F'S I RN860049 Nitrite as N' _mg/L, (0.010 TB
SULFATE
RN860041 Sulfate, mg/L, 24.8 WELL W-6 I RN860042 SUifate, mg/L, 19.9 WELL W-7
RNS60043 Sulfate, mg/L, 19.3 WELL w-s
RN860044 Sulfate, mg/L, 1 S. 1 \I/ELL W-10
RN860045 Sulfate, mg/L, 1 6. 9 WELL IJJ-12 I RN860046 Su I fate, mg/L, 16.7 \I/ELL W-13
RN860047 SUifate, mg/L, 12.2 WELL W-15
RN860048 Sulfate, mg/L, 12.2 F'S I RN860049 sulfate, mg/L, <10.0 TB
I \ '
I
SAMPLE# 1----------
:0.RSENIC
RN860041
IRN860042
FN860043
RN860044
I
RN860045
RN860046
RN860047
RN860048
•
CALCIUM
RN860041
RN860042
IRN860043
RN860044
RN860045
RN860046
IRN860047
RN860048
CHROMIUM
IRN860041
RNE60042
RN860043
RN860044
IRN860045
RN860046
RN860047
IRN860048
MAGNESIUM
RN860041
IRN860042
RN860043
RN860044
IRN860045
RN860046
RN860047
IRN860048
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KEYSTONE ENVIRONMENTAL RESOURCES
PRODUCED ON 10/24/86 AT 11,05 PAGE
RSL T. LNE SOURCE
-------------------------------------------------------
Arsenic, mg/L, <o·.010 WELL W-6
Arsenic, mg/L, <0.010 \I/ELL \11-7
Arsenic, mg/L, <0.010 \1/E LL W-8
Arsenic, mg/L, <0.010 WELL W-10
Arsenic, mg/L, <0.010 \I/ELL \11-12
Arsenic, mg/L, (0.010 \I/ELL W-13
Arsenic, m9/L, <0.010 WELL \11-15
Arsenic, mg/L, <0.010 FB
ca1c ium, mg/L, 48,9 \1/E LL \11-6
Calcium, mg/L, 34.2 \I/ELL W-7
Calcium, mg/L, 36.5 WELL \11-8
CalciUm, mg/L, 5 1 . 0 WELL w-10
Calcium, mg/L, 60.4 WELL W-12
Calcium, mg/L, 34.7 WELL \11-13
Calcium, mg/L, 37. 1 WELL W-15
ca I c·i um, mg/L, < 1 . 00 FB
cnromium, mg/L, (0,050 \1/E LL \11-6
cnrom1um, mg/L, (0.050 \1/E LL \11-7
cnromium, mg/L, (0.050 \1/E LL \11-8
Chromium, m9/L, (0,050 \I/ELL W-10
cnromium, mg/L, (0.050 \I/ELL IJ/-12
cnromium, m•;i/L, <0.050 WELL W-13
cnromium, mg/L, <0.050 WELL W-15
cnromium, mg/L, <0.050 FB
Magnesium, mg/L, 32.8 WELL W-6
Magnesium, mg/L, 39.2 \1/E LL lJ,i-7
Magnesium, mg/L, 30.9 WELL W-8
Magnesium, mg/L, 16.6 WELL w-10
Magnesium, mg/L, 20.3 WELL w-12·
Magnesium, mg/L, 14.6 \I/ELL W-13
Magnesium, mg/L, 20.6 WELL W-15
Ma,;ines i um, mg/L, ,: 1 . 00 FB
' . '
I
liAMPLE # ~;~;;;~~~-
RN860041
il"N860042
.,N860043
RN860044
t N860045
N860046
N860047
RN860048
li30DIUM
ll=!NS60041
RN860042
lf'<N860043
rN860044
RN860045
t N860046
N860047
N860048
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KEYSTONE ENVIRONMENTAL RESOURCES
PRODUCED ON 10/24/86 AT 11:05 PAGE 2
aa•====:111
RSL T. LNE. SOURCE
Potassium, mg/L: 3. 12 \I/ELL \11-6
Potassium, mg/L: 5.06 \1/E LL \11-7
Potassium, mg/L: 3.57 \I/ELL \11-8
Potassium, mg/L: 5.82 \1/E LL \11-10
Potassium, mg/L: 2.34 \1/E LL w-12
.Potassium, mg/L: 1. 03 \I/ELL W-13
Potassium, mg/L: 1. 89 WELL \11-15
Potassium, mg/L: < 1 . 00 FB
SOOium, mg/L: 71. 7 . \I/ELL W-6
SOOium. mg/L: 59.3 WELL \11-7
SOOium, mg/L: 30.4 WELL \11-8
SOOium, mg/L: 59. 1 \1/E LL W-10
S0Oium, mg/L: 36.7 \I/ELL W-12
SO0ium, mg/L: 12.6 \I/ELL W-13
socJium, mg/L: 9 52 \I/ELL W-15
SOOium, mg/L: <, . -:o FB
I
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' .
KEYSTONE ENVIRONMENTAL RESOURCES
•
ABLE 4, SUl\'1MARY OF ORGANIC COMPOUNDS PRODUCED ON 10/24/86 AT 11,07 PAGE
-=••=o•••••••••••••••============ =•=-•a=-..
'
AMPLE# RSLT.LNE ------------------------------------------------
ENTACHLOROPHENOL BY EPA METHOD 604 _
RN860041 Pentacn I oropneno 1 · C:.-1. 22,'
IN860042 Pentacn1oropneno1 :'.37,9 .-
N860043 Pentacn1oropneno1 I 5.37
RN960044 Pentacn Io ropneno I ,-:-7 17
IN960045 Pentacn1oropneno1
N860046 Pentacn1oropneno1
N860047 Pentacn1oropneno1
RN.60049 Pentacn1oropneno1 loove results are reportea in
I
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I
'--\ 3. 86
.. 5. 17 .' \ 3. 49 "
··,3. 44
ug / c-.
SOURCE
\I/ELL \11-6
,\i/E-LL \11-7 ')
\1/E LL \11-8
/.VE.LL \11-10 ·1
\I/ELL w-12
\1/E LL \11-13
\I/ELL \11-15
FB
1.·
' I
SAMPLE#
l~;;;;~~--
RNae0042
li':NBe0043
li':NS60044
RN860045
EN8'5004e
N860047
N860048
RN860049
I
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I
.1
I
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I
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I
RSL T. LNE
1sopropy1
1sopropy1
1sopropy1
1sopropy1
1sopropy1
1sopropy1
-·1 sopropy 1
1sopropy1
1sopropy1
KEYSTONE ENVIRONMENTAL RESOURCES
PRODUCED ON 10/27/86 AT 12:05 PAGE
z:===='=<=•
SOURCE
Etner,ug/L: < 100 \I/ELL 111-e
Etner,ug/L: <100 \1/E LL \11-7
Etner,ug/L: (100 \1/E LL \11-8
Etner,ug/L: (100 \I/ELL \11-10
Etner,ug/L: < 100 \I/ELL \11-12
Etner,ug/L: < 100 \I/ELL \11-13
Etner,ug/L: (100 \1/E LL \11-15
Etner,ug/L: (100 FB
Etner,ug/L: < 100 TB
I
11
11
IJ
11
11
IJ
11
11
11
Ref. 9
Interoffice Correspondence
AUG :' ·1 1880
Mr. T. A. Marr To ________________ _ From __ ~_1r_._K_._D_. _H_e_p_n_e_r ______ _
Location __ P_1_· t_t_s_b_u_r_g_h_-_F_P_G _____ _
Sediment anc.l Well Water Subject ______________ _
Samples -Raleigh Plant
(823-1716)
Location Monroeville -WQE
Dat1: __ Au_g_u_s_·t_._2_6_,_1_98_0 ______ _
Five (5) samples of sediment and well water, taken in conjunction
with North Carolina State and Federal EPA representatives on Jply 211, HIBO.'
,,ere received by the Water and Wastewater Analysis Laboratory on July 28,
1980 for pentachlorophenol analyses.
The attached Table 1 presents laboratory sample numbers, sources
of: the samples and pentachlorophenol content.of the water and sediments.
Please note the well water results are presented in mg/Liter, while the
sediment concentrations are in mg/Kg of dried material.
R. D. Hepner
RJJll:klf
cc: Mr. P. n. Smith
Mr. I}. L. Davies
Mr. w. J. Baldwin
Mr. P. A. Perr
1-lr. J. l~inz
Mr. R. Dingman
Dr. A. C. Middleton
I ·_,.,,,.
/ I
I
I!
11 --Lab 10 No. II )--! ~ .)
I
,) !M
. I
I( •)r, ,._
I;
--
1/Y''
'.17
----
Ii--
··-II ~j
1r-·
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//
TAllLE l
FOREST PRODUCTS GROUP
KOPPERS CCMPANY, INC.
RALEIGH, NC
SAMPLE COJ.JJ•:CTTON DATA
Samnle / Date
Source
.. We I I, ca·st of steel shop ' .
~ledl in well south of
pl:mt
l~i I kcrson constn1cti on
wcl I, cast of plant
Sediment -cast discharge
point
Scd it11c11t -Medlin pond,
soi,th or pl ant
North Carolina :ind Federal EPA
Descriotion / Collected
"0.058 mg/L y 7/24/80
<,0.0004 mg/L "
<. 0. 0004 mi,:/L "
0.674 mg/Kg "
0.114 mg/Kg "
WATER QUALITY ENGINEERING
MONROEVILLE RESEARCH CENTER
Received
7/28/80
"
"
"
"
.
,
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To
Location
Subject
Interoffice Correspondence
Mr. T. A. Marr From Mr, R, D, Hepner
Pittsburgh Location Monroeville
Water and Soil Sam11les Date October 29, 1980 Raleigh, NC
(823-1716)
Water samples from the pond, eight wells, three pits and ·six soil
samples .from the pond, collected September 11, 1980,' by Mr. J. B.
Gillespie, were received September 16, 1980, by the Water & Waste-
water Analysis Laboratory.
Ref. 10
Sample Collection Data are presented in Table l, while Table 2 presents
a Summary of Analytical Data. All data for water samples are in mgiliter,
while results of PCP analyses on the six soil samples from the pond are
in mg/Kg on a dry basis.
RDH:ss
Attachments
cc: Mr. P. D. Smith
Mr. D. L. Davies
Mr. W. J. Baldwin
Mr. R. A. Perr
Mr. J. Heinz
Dr. A. C. Middleton~·
Mr. J. A. Quagliotti
'"It;;/~~
R. D. Hepner
I
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ab
J~e No. Source
1213 Pond
Well #6 . 214
1215 Well #9
216 Well #10.
C-217 vie 11 #11
218 Well #12
C-219 Well #13
(220 Well #14
Well #15 l,-221
222 PIT-A
--223 Pit-G
224 Pit-I
225 Pond Soil
-Pond Soi 1 1226
227 Pond Soil
r_?'>O Pond Soi 1
~29 Pond Soil
I
. ~230 Pond Soi 1 ;-:
'
.lectcd by: J. Gillespie I
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#1
#2
#3
#4
#5
#6
TABLE l
FOREST PRODUCTS GROUP
KOPPERS COMPANY, INC.
RALEIGH, NC
SAMPLE COLLECTION DATA
Sample Date
Descrintion Collected
9/11/80.
9/11/80
9/11/80
9/11/80
9/11 /80
9/11 /80
9/11 /80
9/11/80
9/11/80
9/11/80
9/11/80
9/11 /80
9/11/80
9/11/80
9/11 /80
9/11 /80
9/11/80
9/11/80
WATER QUALITY ENGINEERING
MONROEVILLE RESEARCH CENTER
Received
9/16/80
9/16/80
9/16/80
9/16/80
9/16/80
9/16/80
9/16/80
9/16/80
9/16/80
9/16/80
9/16/80
9/16/80
9/16/80
9/16/80
9/16/80
9/16/80
9/16/80
9/16/80
..
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11
'
PARAMETER RNC
I Organic Carbon
I ,_ D. -5-dav
lical Oxygen Demand
-1 Oxv2en Demand
.,ls I[ r, (os CaC03)
to pH= 4.5 M.O.
o pH = 8. 3 PHT.
' . in i ty /as CaC09 )
to pH= 8.3 PHT.
~p_H = 4.~ M.O.
I E . d ... ~s, •vaporate
Tota I -103° C
ixed -550• c
olatile-550° C '
ws, Suspended
\lotal -103° C
!ixed -550° C
Volatile-550° C
[~-Dissolved
tal -180° C
:,,Fixed ~ 550° C
elaUle-550° C
I lus, Settleable, ml/L
-5 Minutes
, Hour
>r .. Units
l;:tivjty .... 11ml10s/cm
i,
11itv, Unit<;
r:ldehyde
-:
f~iiJ
213
6.8
46
<l
35
<0.005
113
145
<0.5
.00056
TABLE 2
FOREST PRODUCTS GROUP
KOPPERS COMPANY, INC
RALEIGH, NC
SUMMARY OF ANALYTICAL DATA
o,_0 . (, t;..,,J 7 c,u--,/ 0 0 CJ.)• I/ r_,!,i)-1~~ (>LL' ;(3 ,',u,.;/ •./ ' (i,o-/b~
214 215 216 217 218 219 220 221
7.4 6.9 7.2 7.3 7.4 7.6 7.4 7.3
43 34 59 36 34 21 27 20
6.0 5.0 3.0 <1 <1 4.0 4.0 <l
35 85 5 1 70 7 <1 <1
<0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <Q.005 <0.005
764 285 471 457 328 207 430 268
'
800 470 750 780 450 270 600 400 .
<0.5 <0.5 <0,5 <0.5 <0.5 <0.5 <0.5 0.5
/.012-: '--,, -.00059 6.? .': 046"' .00059 .00068 .00052 .001
I
11
rcsults in mg/liter unless otherwise noted._
WATER QUALITY ENGINEER I NG
MONROEVILLE RESEARCH CENTER
TABLE 2
FOREST PRODUCTS GROUP
KOPPERS COMPANY, INC.
RALEIGH, NC
SUMMARY OF ANALYTICAL DATA ~ · <-t·c1 o .,,y ~~-"-,:,,~,.
;/, ! 6 P ,r J. I cl. ~'.: 1./ ···--··
RNC I PARAMETER
.--------;----1r---t-----t---t---.Jf--+---i--l---~I-----
222
I -T I I 223 I 224 22s I 226 221 228 229 230
l Orl!a n ic Carbon
I .u. -5-dav
llcal Oxv~en Demand
'-· Oxygen Demand
ls
1ity (as
to PH=
CaC03)
4.5 M.O.
8,3 PHT. IO pH -
, inity (as CaCOs)
to pH= 8;3 PHT.
10 PH -4.5 M.O.
L~\s, Evaporated
"otal -103° C llixed -550° C
. lo lat ile-550° C
rs, Suspended
lbtal -103° C
·xed -550° C
Volatile-550° .c
~. Diss~lved
._btal -180° c
I ix<!cl a·· 550° C
olatile-550° c
. I / .us, Settlenble, ml L
15 Minutes
I Hour
I . ,r, Units
lttivity . .umhos/cm
.. Jit·-. .-. UnitB .
'1:ldehyde 2
.0018 .0022 .42 .074 .031 .072 .11 ·. 076)
1,------t---'-------t----t--t----'--l--+---+--+---+----l---
in m!;/liter unless otherwise nuted.
230 -results in mg/Kg (ppm) WATER QUALITY ENGINEERING
MONROEVILLE RESEARCH CENTER
11
I
11 i
Ir !
11
11
11
I\
1, .,
11
-j
11
I:
'
0
W-13
. : ____ _:
W-14
0
OW-4
.o
W-15
0
0
W-3
OW-9
0
W-1
1-------. : ______ : 0 W-11
0 100'
Q MONITORING
WELL
\ 6 BACKHOE PIT
(_1-: )
LOCATION OF POND SEDIMENT SAMPLES AND BACK HOE PITS ~
I' Ii
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11
II
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11
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I(.:,
l<OPPERS
Interoffice Correspondence ·
To __ _.:.::Mr,_.,.~R::..•_:A.:.:·:.....:...P;::.er,_.,r'--------
Location Pittsburgh
From __ -'-'M,._r.,_. __,_R.,_.._,._D._. _._H..,e"'p...ene__,r _____ _
Location •.· .. Monroeyi 11 e
Subject --.!.:R~a..,.;l e,:_i~geche--S~o~i,._,l~Sa,.,m"'p:..:.l.:,.e=-s ___ _
(823-1716)
Date --' _ _,_M.,,,au.y_7......_. __.l_,_9""80..____· ______ _
fEV.2
Samples of dirt_collected at the Raleigh (Morrisville) Plant on
March 19 and Apr.il 3, 1980, have been extracted and analyzed for
their pentachlorophenol contents by a gas chromatographic technique.
Results are indicated on the attached letters you sent to me indicating
sources of the soils.
RDH:ss
Attachments
cc: Mr. W. J. Baldwin
Mr. D. L. Davies
Mr. T. A. Marr
Mr. P. D. Smith
Dr. G. Kitazawa
Dr. A. C. Middleton.,__...----
Mr. J. Heinz ·
Mr. R. Dingman
i
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To
Location
Subject
Interoffice Correspondence
R. D. Hepner From R. A. Perr
Location Pittsburgh MRC
Raleigh Samples • Date March 21, 1980
I am having the Raleigh, North Carolina plant send
you the-follow:ing:11 samples of dirt.that were taken
.March 19, 1980'. ~ /1:'-
,r C/7, ,;,~ /l -~ . . ~i'o ooo ,<2//(.. 79 ),_.__ War_ehouse -Ba 1 -South Side Surface
11 /0' 2 . Ware house -B~t:.;c4,_:-~S~o:c:,u~t~h:.,_!:S~i:.!d~e~S:c:,u=.r..::fc!:a:.::c:.::e:__ _______ <4,.!,i;,~o:c:,o:::._ __
/-/ _ .. 3 .. _-'\:Jarehouse -Bay #7 -Middle Surface 'f/O
I'" 4. Warehouse -Bay #1 -South Side Clay Layer .;-
II
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11
II
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11 '
,rj ·-5. _Warehouse -Bay #4 -South Side Clay Layer .Ji
J1/'_6~iw..rehouse -Bay #7 -Middle Clay Layer s~->
rf ;f,,-Lagoon Sludge '\ /.; 0 1 ooo
~c, _8. Dirt near lagoon sludge ) 1, o>,oO
J>'/ 9 . Sand Fi 1 ter / k ~o-c Ji .,l_0~Sur face near ol d'_p_e_n_t,,_a-rn'"i•-x-ctc-a_n_k.---,,----------7 J .,;~'.:, o o
,i) 11. . Surface near old cellon building ) J. 900 / .
Please analyze these samples to determine if they are
contaminated with pentachlorophenol and if so please
determine the concentration of the contamination for
each sample-.
'Please handle this expeditiously
very interested in these results
RAP:cg
cc·: T. A. Marr
P. D. Smith -Raleigh 4
as possible, we are .. ~::;·e:··
Raymond A. Perr
l~t,✓ J/.1-?/10
1\~lllC-79'~ f 9 -
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II
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II
II
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ll
II
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II
Interoffice Correspondence
To R. D. Hepner From_.....;.R"'"';_A_.:.._P_e;:..r..;.r;;;__ _______ _
Location_MR~~C ___________ _ Location Pittsburgh -K-927
Subject Raleigh Samples • Date _ __:A.:.1P:..:r:..:i::.:l=---7'--'-, ..:l::.:9:..:8:..:0:.._ _____ _
In addition to the 11 samples of dirt I had the Raleigh
plant send you in the niiddle of March,· I am having them
send you the following ,12. samples of dirt that were
taken April 3, 1980.:
· J:1/C-<j;; 12 Warehouse -Bay #1 So~th Side ; tf3
v·~3-Warehouse B~t2 Center --SsfO
;,;. }_4_~areI:iouse BE:y_jf• . ..;_3'-'?~o"'uc:.ct=,:h~s=i~-~d-e----------'-----"",x~;i'-'o=----
i; 15 Wareh9.11se -Bay #LC""e"'n .. t,.,,e,...r~ _____________ __,.__./c...J<-=.D:.::D:__
fY J._6_]:luried Lagoon -Surface " Jl.70
1.r J..7 Buried Lagoon -1' d~lch·-=----------------·,_/.::SD:=.t....C:..:0:..:0:_ __
?J J_8_Burie9-Lagoon -2,-depth
7) 19 Lake Bottom at shore
W· _2!) New Surface between old penta mix and building
77.21 New Surface between penta mix and road
/'" .22_Center 1 Road -near Penta Mix
/C/ 23 Rear Building
zo
I .Joo
.l/P..:,
J"f 3J, ooo __ _
/.SU
Please also analyze these samples to determine if they are
contaminated with pentachlorophenol and if so please determine
the concentration of the contamination for each-sample.
~~19~·-·
Raymond A. Perr
RAP:cg
cc:·· T.·A. Marr
P. D. Smith -Raleigh
Ii
1(;t1{-i
I I
vJ c..s ~ t,
(· ,._ ,I' (Jo/~<>
II
II
, REV. 2
. ·.
Ref. 12
R{OPPERS
Interoffice Correspondence
To Mr. R. A. Pe""'r..,_r ________ _ From ___ .Mr.....:__R~ Q _ _Jjepne.L.-
It Location Pittsburgh Location Monroev i 11 e
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Subject Raleigh Sam._pl_e_s ______ _ -ran:11ro, Date _ ____:A.:.:U:...9c:::U-=-S-=-t-=2'--'l'-',_.:._l ::..:98::..:0:,.._~-----
Ref: " -Your letter of,June 30, 1980-regarding 55 dirt samples.
Soil samples from various areas of the Raleigh Plant were received
July l, 1980, for extraction of pentachlorophenol and analysis of dried
extracts. Analysis-was carried out by a derivatization-gas chromato-
graphic technique. Identification was made from retention data only.
Sources of soil and lake bottoms samples: and penta contents are pre:
sented below:
A. \•larehou·se ·samplE:s·
Lab Sample No.
RNC-132
133
134
135
136
137
138
139
--8; Ce 11 on Samples
Lab Sample No.
RNC-140
141
142
143
144
145
146
147
148
149
150
151
152
. l 53
Your Number
l
2
11
. 18
15
28
32
33
Your Number
100
l 01
102
103
98
99
115
113
114
131 ,
132 ·
125,
126 -
124
PCP, mg/Kg
4 ,ooo--
1 ,800
2,800
180
310
110
31
780
PCP, mg/Kg_
230
65
110
120
43
1110
4,700
l ,800
l , l 00
14
3. l
3.2
100
270
I .
Ii
I,
I
11
11 '
11
11
11 . I
11
11
IJ
11
11
IJ
11
lo I
Ii
. --..-
Mr. R. A. Perr -2-
C. ,lake Bottoms Samples
Lab Sample No. Your Number
RNC-154
155
156
157
141
142
143
144
D .. Lagoon Samples\
Lab Sample No. Your Number
RNCc 158 38,
159 39 1
160 40,
161 41 '
162 46 ,
163 4 7 •
164 60
165 61
166 62
167 63
168 64
169 65
170 68
171 69
172 70
17 3 71
174 721
175 73 ·
176 74
177 75
178 76
179 77
180 80
1131 Bl
182 88 ~
183 89 •
lM 96
185 97
Note: Results are in mg/Kg dried soil.
R. D. Hepner
RDH:ss
cc: Mr. T. A. Marr
Mr. P. D. Smith
Mr. W. J. Baldwin
Mr. J. Heinz
Dr. A. C. Middleton
Mr. 0. L. Davies
Mr. R. Dingman
August 21 , 1980
PCP, mg/Kq
12
6. l
11
20
PCP, mq/Kg
13
13
7.4
0 .Bl
17
43
5,500
220
220,000
38,000
24,000
960
70,000
6,500
450
3.4
160
39
9.4
l.6
64
7.4
6,000
l. 5
170
5.6
3,400
150,000
I·/,, ), ,·
11
11 !
11
11
11
11
'
11
11
I
I
11
11
IJ
1,
11
IJ
11
I:
11
I ------Ref·; 13.
RALEIGH SOIL INVESTIGATION
· OLD 1./'GOON-AREA
... , ..
Collect samples in each bcring
at: 0.5', 1.5', 3', 6'
.
0
'}-0 / r ◊
o/
~ 0
'v 0 y
◊ 0
0\ ◊
0
0 ~ ◊-"ti 1\
0
~) ,t I
v
~
Pond -----
0 Analyze samples at 0.5' and 1.5'
"' □ Analyze samples at 0.5', 1.5', 5 1 ·'
6, Analyze samples at 0.5', 1.5', 3', 1
'v
◊
Outline of old lagoons
:<··
Scale l" • 40'
Ii
11 TABLE 1
FORMER LAGOON SOIL SAMPLES
(PENTACHLOROPHENOL RESULTS mg/Kg)
11
RALEIGH, NC
JUNE, 1981
11 Location Surface 0-1.0' 1.5-2.5' 3.0-4.0' 6.0-7.0'
B-1-A 0.021 0.037
11 B 0.046 0.064
C-~ 0.43· 0.88 0.058
D 0. 26. 0.021
Ii E 10.0 · 0.068
B-2-A 0.048 0.051
B. 390.0 2.8 10.0
11 C 730.0 0.22
I D 1100. 0 0.080
E 190.0 0.60 0.25
11 B-3-A, 0. 20 · 0.048 0. 065° I B· 0.40 1.0 0.25
11 c,' 8100.0 ✓ 7. 7 · 0.43 0.071
D' 0.21 0.076 0.091
E 0.22 0.83
11 B-4-A 900.0 1.8 0.21 0.12
B 0.82 0.15 0.21 0.15
C 1200.0 1300.0 0.67 8. 90 0.10
I/ D 0.13 0.13 57.0 1.0
E 64.0 0.24 0.27
11 _B-5-A 0.13 0.12 0.17
B 830.0 2.5 0.13 0.11 0.15
C 10.0 o. 73 3.8 0.13
D 250.0 0. 78 0.17 0.11
IJ. E 3200.0 2.3 0.085 0.085
B-6-A 0.38 0.42 0.16 11 B 850.0 2.7 0.12 0.43
C 1100. 0 2.7 0.49 1.1 0.14
D 0.38 0.11 4.3 0.11
11
E 460.0 8.5
B-7-A 410.0 0.25 0.36 1. 1 2.9
B 2400.0 3.3 7.8 1.0 ., C 940.0 28.0 3.6 1. 7
D 0.51 0.077 0.37
E 2.5 0.94
11 B-8-A 77 .0 0.12 0.038
B 26.0 0.23 1. 3 0.012
11 C 830.0 26.0 0.16 1. 7 0.0ll
D 0.057 0.012 0.02
E 130. 0 2.7 5.1
11
I
Ii
It
Ii Location
B-9-A
B Ii C
D
E
Ii B-10-A
B
11 C
D
E
111 B-11-A
B
C
11 D
E
11 B-12-A
B
C
D
11 E
Ii
11 j
,11
11
11
11
11 JBG:ss
10/4/84
ll 1
TABLE 1 (Cont.)
FORMER LAGOON SOIL SAMPLES
(PENTACHLOROPBENOL RESULTS mg/Kg)
RALEIGH, NC
JUNE, 1981
Surface 0-1.0' 1.5-2.5' 3.0-4.0'
35.0 0.032 0.022
5.1 0.034
0.065 0.10
30.0 0.017
71.0 2.1
750.0 3.3 0.072
2.2 2.4
2700.0 0.48
6.0-7.0'
0.025
0.034
0.060
0 .. 026
I: I
11
11
11
Ii
11
11
11
11
11
11
11
IJ
11
I!
'
0
0
.43
0
0
0
0 0
390
0 .,
0 8r, (_g
p 0
190
0 . 0
RALEIGH LAGOON AREA
Penta Concentrations at the Surface
900
0
0
/ --------,loo
' 0
\
\
"' 0 '
0
Results in mg/Kg
JUNE, 1981
410 Q_
0
830 /
,-.
/ 0 0 / 0 I
0
"' ~
\ "' ,
830/ ' ""-~ 1100 0 ,
/ ------0 -)
/ --I , ~ -/ 0 0 0
3200
130 0 0 0 0
r" "\)
35
0
0
0 750
0
0 0
0
0
0 0 0
0 0 0
0 0 0
0 0 0
0 0 .. 0
RALEIGH LAGOON AREA
Penta Concentrations at a Depth of 3.0 Feet
0
0
/ ,...______
8. cJ
' 0
\
\
"" 0 ' 57
0
'
Results in mg/Kg
JUNE, 1981
o_
0
r--' /
/ 7.8~
0 0 / Q
I "--.. 1.1, 3.6 ' "'ci\ 0
0
~
\
I
0, 3.8 r---: ,
____ .,;
I
' o4.3 ~ _/ 0 0
0 0 0 0
_··o.
0
0
0
0
0
0 0
Ii
11
11
11
It
11
11
11
11 ,1 ,i
~l
~I
~I
~
111
111
111 ,.,
0
0
0
0
10
0
0 0
2.8
0 0
730 7.7
0 0
· 1100
0 0
0 .. 0
RALEIGH LAGOON AREA
Penta Concentrations at a Depth of 0.5 Feet
l.8
0
0
,'"'-,_
1~0
' 0
\
\
\,_,,
0 '
64
0
'
Results in mg/Kg
JUNE, 1981
77
0-" 0 0
2.5 r--' 850 ' 2 4 , ooo"--"26-.__ ' 0 /
0 ' I " 0 ', )
I 1-Q,__
' 2. ~ 940 26 /
'---, 0 0 ,
/ -------0 0, ,
' ... ___ .,,.I
250 I , ~ _/ () 0 0
2.3 460 2.5 2.7 0 0 0 0
0
5. 1
0
0
30
0
71
0
t'c.1'\)
3.3 2.2 0
0 0
0
0
0
0
0
0
10
0
0
0
0
0
0
0
. ·o
RALEIGH LAGOON AREA •
Penta Concentrations at a Depth of 1.5 Feet
Results in mg/Kg
JUNE, 1981
0 0 -
0
0
0
0
r-----' / 2.7 I 3.3""
0
" I , 2-{ 2.8
0
o "--o\ 0
/ ----0, --_.)
0
0
8.5
0
0
0
0
5. l
0
0
0
0
0
2. 1
0
1,
D
I
I
1,
1,
I
I
I
I.
I
I
I
I
I
I
I
I
I
0
0
0
0
0
0
0 0
0 0
.o 0
0 .. 0
RALEIGH LAGOON AREA
Penta Concentrations at a Depth of 6.0 Feet
0
0
I ~----I ' I
0
\
\
\
' 0 ' 1. 1
0
Results in mg/Kg
JUNE, 1981
0 2.9
0
,,--..
1 0 0 I " / "" ,
------'-
'
---------~ 1. 7 0 / ----!! -I -I , ~ ,/ 0
0 0 0
0
' '-._
0 '· i ,
I , ~, : /
0
0
/
0
0
0
0
0 0
0
0
Ir j
Steel
Shop
"' 0 0
' F
'
'
•IRRIGATION FIELD BEHIND STEEL SHOP
RALEIGH, NC
Scale l" = 40'
Soil Samples Collected at
Surface, 0.5', 1.5-2.5', 3.0-4.0'
. JUNE, 1981''
l.F.-1
I F -_2
l.F.-3
I.-F.-4
I.F.-5 ..
100 •
I I
I TABLE 2 '
11 SOIL IRRIGATION FIELD
11
JUNE, 1981
'
11 Pentachloroehenol
Deeth Results
11
(ft) mg/kg
toi0·
11
I.F.-1 Surface '· . 0-1.0 0.033
1.5-2.5 i:cii,Ji-J
11 3.0-4.0 0.053
11 l.F.-2 Surface 0.061
0-1.0 0.016 I ,---/ ,',, 1 5-2.5 (,2. 0 \,
3.0-4.0 0.033
I.F.-3 Surface (r19)·
0-1.0 0.025 ·
1.5-2.5 0.024
3.0-4.0 0.039
I. F. -4 Surface 0.056
0-1.0 0.019
1.5-2.5 .010
3.0-4.0 0.045
I.F.-5 Surface 0.12
0-1.0 0.022
1.5-2.5 0.014
3.0-4.0 0.021
I
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I
I
I
I
To
Location
Subject
KEYSTONE
£:-.'\'IROSME:-.T AL RESOL!RCF.S, INC.
Interoffice Correspondence
M. J. Dvorsi<.y From R. D. Hepner
K-19 Location i•lonroeville
Raleigh, NC Date '.•larch 17, 1987
(1792-77-00)
Raleigh soil samples collected July 15, 1986 have been tested for J per.~achlorophenol as requested. Results are attached.
?.DE/nw
Attachments
cc: M. Schlesinger
s. Colton
B. Fisher
R. D. Hepner
Ref. 14
I
I
I TABLE OF CONTENTS
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SAMPLE #
----------
87010142
87010143
87010144
87010145
87010146
87010147
SOURCE ---------------
A-8
8-7
C-3
C-6
D-4
E-8
SPECTRIX MONROEVILLE
PRODUCED ON 03/17/87 AT 09,50 PAGE
DESCRIPT DAT-COL DATE-REC
------------------------------------
SOI LS 07/15/86 01/13/87
SOI LS 07/15/86 01/13/87
SOI LS 07/ 15/86 01/13/87
SOI LS 07/15/86 01/13/87
SOI LS 07/15/86 01/13/S7
SOI LS 07/15/86 01/13/87
I
I SPECTRIX MONROEVILLE
I TABLE 1, SUM~ARY OF ORGANIC COMPOUNDS PRODUCED ON 03/17/87 AT 09,53 PAGE
I SAMPLE * ----------RSLT.LNE
PENTACHLOROPHENOL <EPA METHOD 8040)
87010142 Pentacn1oropneno1 ~6ioo
I 87010143 Pentacn1oropneno1. 309000
87010144 Pentacn1oropneno1. 1670
87010145 Pentacn1oropneno1 .16500~
I 87010146 Pentacn1oropt1eno1. 4020
· 87010147 Pentacn1cropneno1. ,136000
Tne aoove results are reportea in ug/Kg. I Al I iaentifications are from retention aata only.
I
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I
I
n
R
I
SOURCE
A-8
8-7
C-3 (',°4 Ji
C-6
D-4
E-8
/ RALEIGH, NORTH CAROLINA
I
I
I
I
F0:2MER LAGDON AREA
l b.EA A . I
__;xcA VA TED i2" OF SOIL l ---.
-~~~GHO~-T INSCRIBED I;-
l;EA B. _·· -I
£XCAVATED 36" OF SOIL>--
IHROUGHOUT INSCRIBED I
REA. .
~
0 'ro /
'? . -_o-
LEGEND:
0. SOIL SURFACE SAMPLES
TAKEN AT EACH
LOCATION (48 SAMPLES)
y
0
\~
0 0 0
0
\
I
I
I
I
I
I
I
I
I
I
o ( f ff --_.,._ '-Q 0/
¾
0
,,
I '. (0
)
I \. 0 ---."-..:...,,.,,,,,,-
\
0 ,
'
0
. :..r.,
OUTLINE OF OLD
LAGOON
R. A. FISHER
8-18-36
I F.IG. 11 .
.. -~
FIELD GUIDE TO THE GEOLOGY OF
THE DURHAM TRIASSIC BASIN
By
George L. Bain
and
Bruce W. Harvey
r·--
; -----............
I
\·
\,., \, \ \
Carolina Geological Society
Fortieth Anniversary Meeting
October 7-9, 1977
.__ ·,
I
iJ"'"> ' \ \ ''l l
·1 f
·,., I .
,._./
r\ . .r·--. . \ , .
i
I
i (
' Ref. 15
\..,.
with contributions from:
D. Canady
V. V. Cavaroc
E. I. Dittmar
R. C. Hope
Paul Olsen
J.M. Parker, Ill.
F. M. Swain
Dan Textoris
Norm Tilford
Walt Wheeler
~o\,OGI(,
j.,.~c,-.,,~~
0 . -~ !:J v -,.
/937
I
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ii
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•'·'.;:l ...
. I:
FIELD GUIDE TO TIIE
GEOLOGY OF TIIE
DURHAM TRIASSIC BASIN
NORTII CAROLINA
by
. 1 George L. Bain
and
2 Bruce W. Harvey
With Contributions
D. s. Canady v. V. Cavaroc
E. I. Dittmar
R. C. Hope
P. E. Olsen
J. M. Parker,
F. M. Swain
D. A. Textoris
N. R. Tilford w. H. Wheeler
1u.s. Geological Survey, Ral~igh, N.C.
2 Campbell College,· Buies Creek, N. C.
From:
III
i ,,
I
J II I ' ' . . ' ... ·, . • ,. ' . . ,· , _ , 'l I · , · · • . · · · · ' "
.. ii~
~1_
1
;
11
1·.\,· ' ; ·' ,,.
•.;-t-<\ti. ,1 'i,·.· , .• ,.,. J \:;-, ·;c :;,
·,;i ..
COVER PI--K)TO: !"JISTRIBUTIOtJ OF EAST COAST TRIASSIC BA.SINS
■ EXPOSED TRIASSIC BA.SINS
l I BURIED TRIASSIC BASINS
. ~f' ; io., tift. This publicati?n was prepared in cooperation with the U.S: Geolo~ical Survey and ii,, printed through the North Carolina State Government Printing Office by the /:~i-:.: Cco~ogy and Mineral Res~urces Section, Department of Natural Resources and Com-
/: . , munny Development.
~· /\·•
ii ;-,: l.a~u~ by: Benjamin J. McKenzie
ml,· Add1t1onal copies available from: ~At: Department of Natural Resources f, Community Development J;'. Division of Earth Resources
;td, Geoloi;y and Mineral Resources Section
,,,.,1 P. 0. Box 27687
\fi Raleigh, North Carolina 27611 ~ f.1
I
I
and ly
,y
I .on.
1 climate·
I
'lf" the
,.Dent
I
1ich 11
Leal
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I
GEOLOGY OF THE DURHAM-WADESBORO BASIN
General Relationships
Triassic basins are distributed along the Atlantic Seaboard from Nova
Scotia to the subsurface of Florida (fig. 1). They extend eastward beneath the
Cenozoic cover onto the Continental Shelf where they continue to be discovered by
exploratory drilling and geophysical work. The Durham-Wadesboro basin extends
almost across Nort_h Carolina, was filled with continental elastics in Late
Triassic, and is the southernmost exposed of this series formed from Late Triassic
to Early Jurassic in tectonically negative areas.
The East Coast Triassic basins are mostly half grabens and/or tilted full
grabens. In North Carolina, the Durham-Wadesboro basin is bounded on the east
and southeast by high angle normal faults traditionally known as the Jonesboro
Fault. The basin trends southwestward from near the North Carolina-Virginia
line to a point a short distance across the North Carolina-South Carolina line.
It is about 226 km long and averages about 16 km in width. The Durham-Wadesboro
basin· is traditionally divided into four substructures which from north to south
are: Durham basin, Colon cross-structure, Sanford (or Deep River) basin, and
Wadesboro basin. Most of the present study has concentrated on the Durham sub-
structure. The Durham-Wadesboro basin is ?urrounded and: presumed unde:rla-iri ],y
the crystalline Piedmont·complex contposed of acid igneous intrusives, fueta-
volcanics, ·metasediments, and high-rank metamorphic rocks·. Conti!}ental sedj,ments
preserved in the Durham-Wadesboro basin include maroon to grey fanglomerate,
conglomerate, feldspathic sandstone, graywacke, argillite, ·siltstone, mudstone;
black shale, and minor amounts of chert and coal\
The Triassic sedimentary mass was intruded by diabase dikes and sills
in Late Triassic and Earl"y Jurassic time) Individual dikes are spaced about -one
km apart and_ range from 0.3 to 20 min width and up to 16 km in length. Dikes
trend north, northwest, northeast, and east, but are predominantly north and
northwest.
4
.' 1111!!1
' ' ' I \ I \ \\J .f \ .
\ ' \ \ \ N,H.:. \-----
' f-' I
FIGURE I.
WINSTON-SALEM •
NORTH
CHARLOTTE ---·
• ELIZABETH CITY
JONESBORO FAULT
.CAROLINA
COLON CROSS-STRUCTURE
.. / ... ~ SANFORD BASIN .....
WADESBORO BASIN
LOCATION MAP OF DURHAM-WADESBORO TRIASSIC BASIN
-
I
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z
Cl)
<(
III
ti
Cl)
Cl)
~i
0:::
l-
o
0:::
0
III
Cl) w
0 <t.
3
I
--~
<(
:c . a:
::::,
0
IL
0
o..'
<(
~
z
0
I-
'<(
0. g
w a:: ::::,
(!)
LL
The basin is further faulted longitudinally and transversely creating in-
dividual horsts and grabens that are as small as 1 km by 3 km. Most are tilted
to the east and southeast; a few are tilted to the north. Vertical displacement
along the
as 600 m.
largest known intra-basin fault is at least 300 m and perhaps as much
All known faults are high angle and normal. Diabase dikes crossing
the eastern border are right-laterally offset. More extensive strike slip is
suspected but has not been demonstrated.
Sedimentation and Stratigraphy
The sedimentary pile preserved in the Durham-Wadesboro basin contains rock.
types whose lithologic variety, mineralogy, and inherent depositional structures
reveal much about its tectonic origin and evolution, pa.leotopography, climate,
and sediment dispersal patterns. ·
The alluvial fans, the angularity of the sand, the poor sorting of the fines,
the size of the boulders in the fanglomerates, and the freshness of the
feldspar in the Durham basin all point to short transport distance from an ele-
vated source area to a nearby valley floor or graben of low relief. The deposi-
tional environment was not unlike modern deposition in the intermontane basins of
the Basin and Range Province or of the Salton Trough of Southern California.
Typically in this environment alluvial fans formed as a direct result of a
sharp break in slope and a corresponding decrease in stream competency. The
decrease in stream competency _was further aggravated by loss of water through the
permeable alluvium by ".sieving". The resulting high· ratio of rock detritus to
water at the fan surface created shallow braided streams that slowly (?) progr_aded
the coarse p:::-,:,ximal fan deposits over the finer distal ones. Individual facies
within the·fan are quite localized and were caused by intermittant faulting and
attendant increased relief, by meandering bifurcating channels, and by varia-
bility of stream discharge.
Braided streams on the fan surface created longitudinal and transverse bars
which migrated downstream. Sedimentary features. of both the upper and lower flow
regime are characteristic -i.e., parallel laminae, thin lenticular shales, many
6
• I 11 I . • ·, " •, ". ,-' • , . ! '
-
..
-
SW
L C A A T Son/orO
R E
N M' r-----t I I Cymnock
A 8
N ~ P11~,n
LEGEND
Formotion contoct
Foul ts
........... Fossiliferous shole
Diabase dikes
-Di □bose sills
~ Ton ark.osic
~ fluv1ol foc1es
SANFORD
BA SIN
J J "' •
Red muds1one -sandstone -
conQlomerate focies, undifferentiated
0000
0000
0000
ArgilliJe -graywacke-
congld:~erate facies
61m Wester\, border"
.. conglomerate
Cl) X ;:r -r-
DURHAM BASIN
J J "' ...
J J ~ • "' z
g
0-,...
~ ~ "' ' ;! ,,,
"' X ~ "' "
r··
,·v,.-,s···1 ~~j
CHAPEL HILL\,.-,, ······,,,., «v,,:.,
NE
36 15
"' liiiiiiil . 0. -
::,
36 00
KOPPERS CO• , INC·
NC DOO32OO383
[77 Eastern border c_onglomerate -
~ fang!omerate facies . ---·------------
~ Chert -limestone -
~ mudstone facies
-
Coal -black
shale facies
C,R~,r 1i1;li5Y>'
0 "' ' "'
PITTSBORO
NFORD
·(\/ -·.:. :: :-··.·· .. : . '
FIGURE 2.
RECONNAISSANCE GEOLOGIC MAP
OF THE
DURHAM TRIASSIC BASIN
NORTH CAROLINA
I 250,000
~s ==jhae"'"""''5:a~ou~==::::;s~~s~~===='=~10 M'
= F 10 15Km.
I
IFonta\
; (1969
,Ddis-·
•Bils ar
, Late 'I
1fgnost·
I
lfir
IJ, be
!'
l (?) ;
l alents
iJ Durha.
t},e a ·
I
~gan t becani~
tween th
1trine;
obabf
'
e. trad A dle 0£
;1 lf-graben I .;
,.
I
This simple tripartate division based on coal does not hold up even within
the Durham-Wadesboro basin. The'.chert in the Moncure area was not penetrated in
the Sears No. 1 test well at New Hill even though correlation of the basal 350 m
of the Sears well with the basal section of the Groce No. 1 well west of Sanford
shows that the Sears well was within 90 m of being through the Pekin. Although
the lower section of the Sears well correlates with part of the lower section of
the Groce No. 1 well, the Cumnock is very thin or absent in the Sears well. The
upper ·section of both wells are in entirely different facies.
The position of the fanglom~rate at the surface along the down-faulted
side of the Durham and other basins is frequently cited as evidence for continued
pe:-iodic movement aloni the downthrown side .. Recent resistivity, gravity, and
aeromagnetic evidence show that the basin floor "steps up" near the border fault
making at least some of the surface-exposed fanglomerates early and in a basal
position. In fact, part of the eastern side of the Sanford basin now mapped as
Sanford Formation is most probably Pekin in age. Thus, the evidence for or
against continued movem.en·t through Durham deposition may be <,roded away. The
presence of the basal conglomerate does indicate strong initial relief and may
indicate only the time of maximum local relief between Piedmont and basin floor.
Provenance
The Durham-Wadesboro basin is surrounded by crystalline rock.s of the· North
Carolina Piedmont. The northern part of the basin lies between the Carolina
slate belt to·the west and the Raleigh pluton'ic-gn:iss belt to the east; The
southern half of the basin is entirely within the slate belt. The slate belt
is a low-rank metamorphic complex (greenschist) of·silicic land wastes and
felsic to mafic pyroclastics which has an overall andesitic composition
(McCauley, 1961). Individual rock types include: slate (laminated argillite),.
graywacke, tuff breccia, crystal lithic tuffs, flows, and phyllite.
The Raleigh plutonic-gneiss belt has an ·acid plutonic core surrounded by
gneisses, schists, phyllites, graywackes, and quartzites ranging up to the
almandine-amphibolite metamqrphic facies (Parker, 1968). The Raleigh side of
the basin contains some pegmatite. Both provinces are intruded by many quartz
veins.
13
Few studies have attempted to determine the specific source area or char-
Dittm,
borde1
acter of the Durham-Wadesboro basin parent material. Whitehead (1962) conclude, bci'rexJ .,
from.a study of the major rock types exposed at the surface in the Sanford·basit south·
that the grain composition indicated a metamorphosed Precambrian .sediment sourc, at;·-pr•
now largely eroded away. More specifically, he proposed that the source litho-Patte1
logy consisted predominantly of moderate-rank metamorphic rocks accompanied .. by ·c·;oss·
low-rank metamorphic granitic and interbedded.volcanic rock. Klein (1969)
found sedimentation from both sides of the basin based on K-Ar and paleocurrent
measurements.
point:
Liggon (1972), from examination of a 448-m core_ from near. Gulf in the :::~-
Sanfor.d basin, concluded that the source area was comprised of rocks of the .,, . .i.
quartz-albite-muscovite-greenschist metamorphic facies.·
Reinemund (1955) fou.nd. that the conglomerate and sandstone at the base of
the section in the Sanford basin contained clasts identical to metamorphic rock
types outcropping in the Slate Belt west of the basin. Crossbedded arkosic
sandstone and schist arenite channel deposits indicated to him that streams flo>
ed from the west and northwest into the basin on the west side (base of section)
and from the southeast in the middle and upper part of the section. He also
noted an increase in coarseness in the Sanford Formation to the southeast, an
increase in arkose toward a c.arboniferous (?) granite pluton to the southeast,
and an abundance of muscovite in the Triassic from rock types·exposed on the
east side of the basin.
Bell, and others (1974) reported that the Wadesboro basin shows no eastwari
coarsening of sediments toward the southeast, ·although an arkosic conglomerate
clearly deri.ved from a granite along the eastern border occurs near the western
border. Randazzo, Swe, and Wheeler (1970) found that arkose (K feldspar) conte1
increases to the east in the Wadesboro basin.
It is therefore obvious only that there was coarse sediment contribution
from both sides of the Durham-Wadesboro basin. The available paleocurrent data
14
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1 the
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fa.se of
rphic ro~i ... fsic •i
treams fl
11 secti~
fl also , ·l 115t, an~
caheast_}
on the J_ I .· '.i1
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Dittmar indicate that streams depositing the alluvial fans along the southeast
border flowed. into the basin more or less at right angles to tfte border as might
be expected. Dittmar's work in the coarse tan arkosic facies shows a strong
south-southwest direction. His data from the other facies are not sufficient
at present to draw a tentative conclusion about their paleocurrent directions.
Patterson's work also indicated a strong southwest direction• across the Colon
cross-structure. As stated above, Reinemund found a few indicators at the base
pointing toward the southeast.
15
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DIABASE DIKES OF THE EASTERN
PIEDMONT OF NORTH CAROLINA
.by
E. R. Burt, P.A. Carpenter, 111, .
,R .. D. McDaniel, and W. F. Wilson
NORTH CAROLINA
DEPARTMENT OF NATURAL RESOURCES AND COMMUNITY DEVELOPMENT
DIVISION OF LAND RESOURCES
GEOLOGICAL SURVEY SECTION
RALEIGH
1978
Ref. 16
I
'f
Index map of North Carolina showing
area of investigation.
-l!!!!!!!!!I 11!!!!!!!!!!1 _. ---==
_,.__,___✓,a
iiiil -
-'
E. R. Burt, P. A. Carpenter 111
. ' ' R. D. McDaniel, and W. F: Wilson·
4 O Scale 4 •=:iiiiic:::liiic::====:::i. .... iiiiiiii .... iiil8 mile,
- - -
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//
Region J Geology:
A Guide· For North Carolina
Mineral Resource Development
And Land Use Planning
by
William F. Wilson
P. Albert Carpenter Ill
Geof ogy Series 1 y
North Carolina Geological Survey Section
1975
revised
1981
North Carolina Department of Natural Resources & Community Development
Ref. 17
l, _ _____,_---ir------------------~·
')"'-<~\? .J... I \Y
C-,'t--::;'"\
~ .. ···-·-··· ~-';-\
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Triassic Basin Rocks
Sedimentary rocks of the Durham and Deep River
Triassic basin occur in long, narrow, north-. to
northeast-trending "ha!f-grabens". These sediments
-commonly dip ently to the east or southeast and .
are up to 10,0 0 feet thick. The basins occupy an
area 5 to 20 mil s wide and are bounded to the east
by the Jonesbo o fault and to the west by metamor.
phosed volcani and sedimentary rocks of the slate
belt. Numerous northwest-trending faults crosscut
the sediments, particularly in Lee County. These
faults develop d during late Triassic or early
Jurassic time.
The Triassic ediments are divided into three for-
mations; from o dest to youngest, they are: the San-
ford Formation, the Cumnock Formation, and the
Pekin Formatio . These formations consist of clays
stone. siltsione shale_. sandstone. conglomerate,
!Ind fanglomera e, Intrusive into the sediments are
diab.:i_se i:llkes, · hich occur_ thr<;>ughout the _basin,
and diabase sill • which are abundant in the Durham
area.
Floodplain a luvium: The floodplains include
those areas tha are subject to frequent flooding.
Floodplains in t e crystalline rocks are predomi-
nantly narrow. F oodplains broaden in areas under-
lain by Triassic sedimentary rocks and become
more extensive t the southeast as the drainage dis-
sects sediments of the Coastal Plain.
Floodplain all vium consists of unconsolidated
sediment ,:Of va ying thickness. The material is
primarily dark-b wn to gray silt, sand, and clay with
some gravels a d coarse boulders occasionally
intermixed.
Gravels: The t rrace deposits in the Deep River
region include d posits of clay, sand, and gravel.
These units con ist dominantly of friable silty or
sandy clay and ubordinate amounts of sand and
gravel. Pebbles and cobbles in the gravel consist of
white or gray quaftz and occasionally of pre-Triassic
metamorphic roc~s and Triassic rocks. The gravels
constitute a smal part of the terraces but residual
accumulations o sandy gravel are present where
the terrace mater als have been extensively eroded.
Sanford Form lion fanglomerate: The fanglom-
erate ranges from jumbled accumulations of angular
and subangular rock fragments with little sand-
stone matrix to scattered, isolated blocks em-
bedded in a pre ominantly sandstone matrix. The
fanglomerate us ally shows little or no bedding.
Fragments of all t e pre-Triassic metamorphic and
igneous rock ty es exposed southeast of the
Triassic basin oc ur in the fanglomerate. Adjacent
to the Jonesboro fault, fragments up to 8 feet in
6
width occur. but. generally, in a northwest direction
they become finer grained and more regularly bed-
ded. The unit contains lenticular beds of relatively
fragment-free sandstone and siltstone and local
beds of conglomerate.
Sanford Formation: The Sanford Formation is
variable in composition. It contains few distinctive
beds and no subdivisions that can be traced for any
distance. The lower two-thirds of the formation con-
sists of lenticular beds of red or brown claystone,
siltstone, and sandstone, with occasional inter-
layering of beds of arkosic sandstone. The silt-
stones and claystones are mixtur~s of quartz, clay
minerals, sericite, chlorite, and iron oxides. Sand-
stones consist primarily of quartz and feldspar and
contain a few rock fragments. Coarse-grained sand-
stones and conglomerates are also present. The up-
per one-third of the formation is the fanglomerate
unit.
Cumnock Formation: The Cumnock Formation
consists of claystone. siltstone. shale, and sand-
stone and contains two coal beds; the Cumnock bed
and the Gulf bed. These coal beds. approximately
200 to 260 feet above the base of the formation, are
underlain by light-gray, medium-dark-gray, and
dark-greenish-gray siltstone and fine-grained sand-
stone that contain small amounts of claystone and
shale. The coal beds are overlain by medium-light-
gray to black shale with small amounts of claystone.
siltstone, and sandstone. The shale is irregularly
calcareous and carbonaceous.
The claystones and siltstones are mixtures of
quartz, clay minerals, sericite. chlorite, and iron ox-
ides. The sandstones are primarily quartz and feld-
spar with rock fragments. They are normally uncon-
solidated but, locally, cemented by calcite and silica.
Pekin Formation: The Pekin Formation is strati-
graphically the lowermost of the three Triassic for-
mations. The unit consists of yellowish-gray or gray-
ish orange, medium-or coarse-grained, cross-
bedded arkosic sandstone; red, brown, or purple,
fine-and medium-grained, crossbedded sand-
stone; and lenticular beds of red, brown, or purple
claystone, siltstone, and fine-grained sandstone.
The siltstones and claystones are composed of
quartz, clay minerals, sericite, chlorite, and iron ox-
ides. The sandstones are primarily quartz and feld-
spar, contain rock fragments, and are normally
friable but locally are cemented by calcite or silica.
Pekin Formation basal conglomerate: The basal
conglomerate consists of a heterogeneous assem-
blage of cemented and uncemented masses of con-
glomerate containing local lenses of conglomerate
and coarse-grained sandstone. Grain size, composi-
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tion, color, and thickness of the unit changes abrupt-
ly, The congtmerate contains angular to sub-
rounded to ro nded pebbles, cobbles and boulders
of volcanic an igneous rocks and quartz, usually in
a sandstone ~atrix, One portion of the unit, called
"millstone grit{' is a firmly cemented quartz con-
glomerate composed of subangular or sub-
rounded, gray, pink or colorless quartz pebbles and
less abundant fragments of tuff embedded in a
silica-cemente, , dark-yellowish sandstone matrix,
',Dia,base dik s and sills: Diabase dikes of Triassic
age intrude se imentary rock sequences through-
out the Durha basin, The diabase sills are restrict-
ed to Triassic sedimentary sequences in Durham
County, The dikes exhibit a high degree of ,
spheroidal we thering, and some can be traced
overland by th -presence of spheroidal boulders,
Diabase sills ar recognized in somewhat the same
manner with I e exception that their outcrop pat-
terns are muc more extensive, Size, length, and
thickness of th dikes and sills is varied, and many
are discontinuo s along the surface,
The unweath red rocks are black, medium to fine-
grained and ar composed of labradorite feldspar,
augite, olivine, magnetite, and some secondary
chlorite, clay, a d limonite,
Weathering p oduces a brown to dark-brown soil
with residual b ulders which are easily traceable
where exposed on the surface,
I
Piedmont Rock
The Piedmon rocks of Region J vary widely in
their types, compositions, ages, and areal distribu-
tion (Plate 1), Lok-rank metamorphic rocks of a pre-
dominantly vole nic-sedimentary origin, intruded by
igneous rocks f various compositions and ages,
form a broad n rtheast-trending interlayered rock
sequence, This ck sequence extends from the ex-
treme southwe tern corner of Chatham County
through Orange County into the northern half of
Durham County, This rock sequence is but a small
part of a compl x belt of rocks that extends for a
length of appro imately four hundred miles from
central Georgia to southeastern Virginia, In North
Carolina, this s quence of rocks is known as the
Carolina slate b it,
The rocks loc ted just east of the Jonesboro fault
in Wake Count)\}are a complex interlayered and
interfingered se uence of high-and low-grade
metamorphic ro ks oriented in a northeast-trend-
ing belt known locally as the Raleigh belt These
rocks were or ginally a volcanic-sedimentary
sequence that va ,ied greatly in their types, composi-
tions and area distribution, Included in this
sequence are p yllites, metatuffs, flow rocks, and
7
mafic and felsic gneisses and schists, Within this
interlayered sequence are a series of altered ultra-
mafic rocks that are located in the northern part of
the county,
This rock sequence reflects several episodes of
deformation during which igneous intrusions of
various compositions, sizes and ages were em-
placed, The most extensive intrusion is a granitic
pluton, the Rolesville batholith, that crops out in
northwestern Johnston County and covers a large
area in eastern Wake County, The metamorphic
_sequence is also dissected by pegmatite dikes and
numerous diabase dikes of various lengths and
widths,
Younger alluvial and marine sediments, many of
which form terraces of different widths and eleva-
tions, occupy much of Johnston County and south-
ern and extreme eastern Wake County,
Floodplain alluvium: The' floodplains include
those areas that are subject to frequent flooding,
Floodplains in the crystalline rocks are predomi-
nantly narrow, because of steep gradients, resistant
rock types and rolling topography, Floodplains
broaden in areas underlain by Triassic sedimentary
rocks and become more extensive to the southeast
as the drainage disse.cts sediments of the Coastal
Plain, ,~
Floodplain alluvium consists of unconsolidated
sediment of variable thickness, The material con-
sists primarily of dark-brown to gray silt, sand and
clay with some gravels and coarse boulders oc-
casionally intermixed,
Argillites: The light-to medium-gray to brown,
fine-grained argillites are epiclastic rocks with well-
developed bedding, some of which is closely
spaced, imparting a laminated appearance, These
argillites are composed predominantly of quartz,
chlorite, and sericite, Cleavage is both bedding
plane and slaty with the latter being more prevalent,
Sections or slabs '/,-inch thick can easily be cleaved
from this rock type, The laminated bedding in-
dicates quiet-water deposition below wavebase, The
argillites were apparently derived from positive
areas of pre-existing volcanic flows and pyroclastic
rocks which were then weathered, eroded, trans-
ported, and deposited in a quiet-water environ-
ment,
In outcrop, the laminated argillites weather to a
light-gray to buff-brown color. The cleavage and
foliation planes accelerate the weathering processes
which causes the argillites to form broad areas of
slightly undulating topography_
Arkoses: The arkoses are fine-to medium-
grained, light-gray-to buff-colored epiclastic rocks
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PHlSICAL FACTORS AFFECTING GROUND WATER RECOVERY IN REGION J
In the area, round water from all rock types is
generally of ace ptable quality for domestic use pro-
vided it is free of surface pollution. Some of the
physical factors which affect the quantity of avail-
able water in lh area are described below.
Rock Texture
Rock texture efers to the size, shape, and ar-
rangement of the component particles of a rock.
Coarse-textured I rocks generally are more per-
meable than fine textured rocks and consequently,
may be better a uifers.
Fracture Planes n Rock
The interstices n many of the rocks in the area are
secondary fractu es. Wells drilled at places where
fractures or tract re systems such as joints or zones
of shearing are etter developed will yield more
water than wells rilled into more massive rocks.
Cleavage and Sc istosity
Cleavage· planes nd planes of schistosity are im-
portant avenues I ground water movement and
storage in the are . They usually dip at some angle
to the horizontal hich allows water to percolate by
gravity down dip atng these schistose and cleavage
planes. Yields ar greater where schistose and
cleavage planes a e plentiful, especially where dif-
ferential rock mo ement along these planes has
caused some deg ee of separation.
Quartz Veins and iabase Dikes
Quartz is a har , brittle mineral that fractures
easily from stress caused by slight crustal move-
ments. Quartz vein in the area are generally more
fractured than the enclosing rock, and hence, are
better aquifers. Geperally the veins are vertical or
dip at nearly vertlcal angles. A well that is to
penetrate an inclin d vein should be located away
from the outcrop a ea in the direction in which the
vein dips. The pres nee of a quartz vein can be de-
tected even in deepl weathered areas by the train of
loose quartz fragm nts on the soil.
Dikes are tabular ock boaies of intrusive igneous.
roe~, They are not ~sually good aquifers, but often the host rock adjace t to them may have been made
more permeable b fractures resulting from the
!Orc_e of intrusion an heat.•Many wells near Triassic
diabase dikes in the Triassic sedimentary rocks are
above average pro~ucers. These dikes sometimes
form underground !ms which obstruct the natural
movement of groun water, causing the water table
to be closer to the s rface on one side of the dike.
44
Topography
Topography is one of the most useful criteria in
determining the relative water-bearing characteris-
tics of the underlying rocks.
In general, wells drilled on hills or other upland
areas are less apt to yield the desired quantity of
water than wells drilled in draws or other depres-
sions.
(1) Hills and upland areas readily shed much
water from precipitation as surface runoff. As a
result, there is less seepage into the ground to
become ground water. On the other hand, the
lowlands obtain influent seepage directly from
precipitation and also from upland surface runoff.
(2) The direction of movement of the ground
water is toward the valleys where part of it dis-
charges into streams. In addition, influent seep-
age may occur from upland rock slopes beneath
the residual material. The more impervious the
bedrock, the more readily \s water deflected down
the slope along this contact.
(3) Wells located in lowlands may salvage
some of the water that would be lost naturally by
discharge from the underground reservoir. There
the depressed water level resulting from pump-
ing, if near a discharge area, prevents further dis-
charge out of the area.
(4) Wells on hills penetrate the water table at a
greater depth than those in lowlands. When a well
on a hill is pumped, the water table is lowered as a
cone of depression, the center of the cone being
at the well. As pumping continues the cone may
grow larger and deeper but its span is limited
because of the topography and because of the
relatively low permeability of rocks at progres-
sively greater depth below the surface. The yield
of wells under these conditions is not great. On
the other hand, wells in lowlands, even though
penetrating the same rocks as those on uplands,
intersect the water table near the ground surface.
Thus, the water table can be lowered a greater
distance by pumping than in a well of the same
depth on a hill. The fact that the static and pump-
ing water levels lie nearer the ground surface than
in wells on hills results in the pumping level lying
in a more permeable zone; hence the intake area
is broader and the yield of the well is larger.
(5) In many places hills exist because the rocks
there have a greater resistance to erosion than in
the valleys, this resistance being due in many
places to poor jointing. Joints and fractures
facilitate entrance of ground water, which
promotes chemical decay and permits mechan-
ical erosion. Thus depressions such as draws or
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valleys sug est that the rock underlying the
depressions has more openings through which
ground wate can move than the rock underlying
the hills.
Thickness of eathered Material
Chemical we thering of rock is facilitated by the
infiltration and movement of water. Therefore, a
45
thick mantle of saprolite may be an indication that
the underlying rock has joints, fractures, or pores
which contain ground water. Saprolite is usually
porous, although not necessarily very permeable, so
that a thick mantle of saprolite has a large storage
an"d recharge potential.
GROUND WATER IN REGION J
General Statement
Water loca~ed in the saturated zone of the earth's
crust and su~1 plied by precipitation in the form of
rain or snow is called ground water. Many differing
factors contr I the amount of ground water available
from any one location. The two most important fac-
tors are the alnount of annual precipitation available .
for supply an~ recharge and the ability of the rocks
~nd soils to a;sorb, store and transmit the precipita-
tion. Other f ctors which have a direct effect on
ground wate supply are rainfall intensity topog ' -
raphy; climatE and types and densities of vegetation
cover within , n area.
Porosity, , hich is the percentage of the bulk
volume of a rock or soil that is occupied by in-
tersticies, an< permeability, which is the ability of
rock and soil ypes to transmit ground water, varies
from place t, place (Tables 2-7). Secondary in-
terstices, sue as joints, cleavage, schistosity, and
solution chan els, are the most important features
responsible f ,r transporting water in crystalline
rocks. Secondary features afford avenues control-
ling the amount and the movement of ground water
within an area.
The soil type or types within the area have a direct
relationship to the amount of precipitation ab-
sorbed into the ground water zone. Tightly com-
pacted clays act as impermeable barriers ac-
celerating the run-off of precipitation. Loose sandy
loams and sandy clay loams can absorb the
precipitation and transmit it to the aquifers.
In general, the ground water of the region is
steadily moving under the influence of gravity from
recharge areas to discharge areas. In this area, the
ground-water . table usually slopes toward the
streams and rarely falls below their level. This al-
fords a continuous discharge which maintains the
flow of the streams during dry periods and adds to
. their flow during wet periods. This is also evident in
springs and seeps which could be good sources of
water provided no septic systems or farms are in the
immediate vicinity.
TABLE 2: WAKE COUNTY WATER QUALITY
Water Quality As CaCOa ppm
--(Number of Wells)
Rock Groups Number 'Average Yield_ 'Average Depth Soft Moderately Hard Hard
Of Wells < Gal./Min.: (Feet) 0-60ppm 61~120 ppm 120-180 ppm
Intrusive Rocks 77 20 137 Predominantly Soft
Mica Gneisses
and Schists 80 19 147 Predominantly Soft to Moderately Hard
Metavolcanic Rock, 23 27 212 Soft to Moderately Hard
Phyllite 11 14 183 Soft to Moderately Hard
.Triassic rocks
(undifferentiaied) 57 ( 5 -158 Moderately Hard to Hard .•
. P.•" p • TABLE 3: JOHNSTON COUNTY WATER QUALITY
Water Quality As CaCOa ppm
(Number of Wells)
Rock Groups Number Average Yield Average Depth Soft Moderately Hard Hard
Of Wells Gal./Min. (Feet) 0-60ppm 61-120 ppm 120-180 ppm
Intrusive Rocks 13 NA• NA" 8 5 0
Predominantly Soft to Moderately Hard
Mica Gneisses 6 1 0 and Schists 7 NA" NA" Soft
Metavolcanic Rocks 16
(undifferentiated) 3 0
19 NA" NA• Predominantly Soft
Coastal Plain 18 NA" NA" 13 5 0
Predominantly Soft
• Data not available 16
TABLE 10: PHYSICAL CHARACTERISTICS OF ROCK GROUPS
SUSCEPTABILITY u ROCK GAO s SOIL ASSOCIATIONS NATURAL DRAINAGE TO PERMEABILITY•• SHRINK-SWELL•• EROSION CHARACTERISTICS
Felsic and Mafic Gnel '"" Appling -Cecil Well Moderate Moderate Sllght Schists. Granite Gnel
Felslc and Malle Gnel
Granite Porphyries an Appling -Louisburg Wall to Excessive Moderate Moderate to Rapid Slight Pegme!ltas.
Talc.Chlorlte Schists, Helena -Appling Well to Moderately Wen Moderate to Severe Moderate to Slow Slight Soapstone, Serpentln
Felslc Flow Rocks, Goorgevllle -Herndon Well -Moderate to Slow Slight Pyrocle.stlcs end Epic!
M aflc Volcanlcs, And tlclo Tlrzah (Davidson) Basaltic Flow Rocks an Eflend (Mecklenburg-Enon) Moderately Well lo Well Moderate to Severe Slow to Moderate Slight to Moderate PyrocluUcs. Georgeville
Intrusive rock, Dlorltn d Lignum -Iredell Well to Moderately Well Moderate to Severe Slow to Very Slow Moderate to Severa Gabbroa. Herndon
Triassic Rocks White Store -CreedmOOr (
\undlrtoren~ted) · • .. Mayodan '·>-!odoratelyWell ~e to Very Severe S~o~ to Ve~ Slow Moderate to Severe '-, . . ,
Coastal Plain, Poorty Dr ned. Lynchburg -Rains Well to Poor Slight to Moderate Moderate Sllght Nor1olk
Coastal Plain, High Marl e Nor1olk -Wagram Well to Excessive SUghl to Moderate Rapid to Very Rapid Sllght Terraces.
Coastal Plain, Side Slo
Moclftl"otely Well to and Lower Bevatlona ol ~h GIiead Moderate Moderately Stow Moderate MarlneTftl"racoa. Somewhat Poor
AOOd Plain Alluvium, Ch-ada -Wehadkee Somewhat Poor to Poor Slight to Moderate Moderate to Slow Sllght to Moderate Low Lying Terraces. Roanoke
•• Theao values are deter lned mainly by the soil's texture, structure and clay types.
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SLOPE ST BILITY *
D'tot5'(VE TICAL)
MAXIMUM PERM~NENT SLOPES
NOT REQUIRING PERMANENT
RETAININGS UCTUAES~
1.5to 1:ov r 15ft.
2.Sto 1
1.Slo t;o r 15ft.
2.Slo 1
t.Sto t;ov 15 It
2.Sto 1
Ito
1101
1 to t;ove 1 '"· 2to 1
,-3to 1;Sp 101-
' , Investigations var 1511.
\Individual de gnreq.
2to1:ove 1511
3to 1
2101:overt '"· 3101
2to 1:over '"· 3101
2 to 1: over '"· 3to 1
PHYSICAL CHARACTERISTICS OF ROCK GROUPS-CONTINUED
DEPTH OF SOIL SOLUM
(lnchn)
18 In. to 40 in.
12 In. to -40 In.
14 In. to 36 in.
181n.to401n.
18 In. to 40 In.
14 In. to 40 In.
18In.to36ln.
30 In. to 42 In.
30 In. to 42 In.
20 in. to 36 In.
30 In. to 42 In.
AVERAGE THICKNESS OF
SAPROLITIC BEDROCK
(F .. t)
Variable
Varlablo
Varlable
Variable
Variable
Variable
-·verlabte
Variable
Variable
Variable
Variable
DEPTH TO BEDROCK
(Feel)
Surface to 100ft. plus
Surface to 100 ft. plus
Sur1aceto 100ft. plus
Surface to 100 ft. plus
Surface to 100ft. plus
Surface to 50 ft.
Variable
5ft.to 100ft.
Variable
Variable
Variable
• 75 to 60% ot Inform ion obtained from highway slope design. II exceulve amounts ol ground water occ~r. Individual slope
designs ere required
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FOUNDATION REQUIREMENTS
FOR HEAVY LOAD-BEARING STRUCTURES
1. Pilings
2. Deep Footings 15 ti.
3. Shallow Footings
1. PIiings
2. Deep Footings 15 ti. ,: Shallow Footings
1. Pilings
2. Deep Foo1lngs 15 It.
3. Shallow Footings
1, PIiings
2. Deep Footings 15 ft.
3. Shallow Footings
1. Plllngs
2. Deep Footings 15 ft.
3. Shallow Footings
1. Pilings
2. Deep Footings 15 It.
3. Shallow Footings
1. Shallow Footings
2. Deep Footings 15 It.
.3._f:'lllngs _.
1, ~lllngs
2. Shallow Footings
1. Plllngs
2. Shallow Footings
1, Pilings
2. Shallow Footings
1. Pilings
2. Shallow Footings
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IL INTERPRETATIONS -GENERAL SOIL MAP FOR REGION J, NORTH CAROLINA
Potential For
Dwellings with
Sewerage Septic Tank Camp Soil Associations Systems Filter Fields Sites
1. APPLING -CECIL Good Fair: MP Good
2. GEORGErLLE-HERNDON Good Fair: MP Good
!3_ .• --WHITES ORE-CREEDMOOR -MAYODAN Poor: LS, SS 'P.oor: SP-Poor: SP, C
4. NORFOL -WAGRAM Good Good Good
5. LIGNUM I REDELL -HERNDON Poor: LS, SS Poor: SP Poor: SP, C
6. CHEWAC A -WEHADKEE -ROANOKE Poor: F, W Poor: F, W Poor: F, W
7. HELENA APPLING Fair: LS, SS Fair: SP Fair: SP
8. APPLING LOUISBURG Good Fair: MP Good
9. LYNCHBU G -RAINS -NORFOLK Poor: LS, W Poor: W Fair: W
10. GILEAD Fair: SS Poor: SP Fair: SP
11. GEORGEV LLE-DAVIDSON-MECKLENBURG Good Fair: MP Good
Good is the rat ng given soil associations that have soil properties for the rated use. The number of un-favorable prope ties are minor and can be overcome easily. Good performance and low maintenance can be expected.
Fair is the ratin given soil associations that have a moderate number of unfavorable soil properties for the rated use. The u· favorable soil properties can be overcome or modified by special planning, design or main-tenance. During ome part of the year the performance of the structure or other planned use is somewhat less desirable than f r soils rated Good.
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Small Local
Picnic Play Commercial Roads and General
Areas Grounds Buildings Streets Agriculture Woods
Good Fair: S Good Fair: LS Good Good
Good Fair: S Good Fair: LS Good Good
Good Poor: S, SP Poor: SS, LS Poor: LS, SS Fair: LP Good
Good Fair: S Good Good Good Good
Good Poor: SP Poor: SS, LS Poor: LS, SS Poor: LP Fair: LP
Fair: F, W Fair: F, W Poor: F, W Poor: F, W Fair: LP Good
Good Fair: S, SP Fair: SS, LS Fair: LS, SS Good Good
Good Fair: S, RO Good Fair: LS, R Good Good
Fair:W Poor:W Poor: LS, W Poor: LS, W Good Good
Fair: S Poor: S Poor: S Fair: S, SS Fair: LP Fair: LP
Good Fair: S Good Fair: LS Good Good
Poor is the rating given soil associations with soil properties generally unfavorable for the rated use. The soils
in these associa\riions generally require major soil reclamation, special design, or intensive maintenance. Some
of these soils, h wever, can be improved by reducing or removing the soil feature that limits use, but in most
situations it is di ficult and costly to alter the soil or to design a structure so as to compensate for these adverse
soil properties.
Legend: ~ LS Low Strength SS -Shrink-swell R -Depth to Rock (Soil shallowness)
·SP. Slow percolation ; RO -Rock outcrops C -Too clayey
s Slope F -Flooding MP -Moderate percolation
LP Low productivity W-Wet
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,0
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" m l'l C: " n m V>
0 .,,
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8 C: z --< -<
BU LETIN 86
NORTH CAROLI ~
DEPARTMENT O NATURAL RESOURCES AND COMMUNITY DEVELOPMENT
DIVISION OF LA D RESOURCES
GEOLOGICAL SU VEY SECTION
Col i'ec
G C t11 Ref. 18 . • "1 .
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Bulletin 86
GE I LOGY AND MINERAL RESOURCES
OF WAKE COUNTY
By
John 1\,1. Parker, Ill
Raleigh 1979
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COVER PHOTO: FALLS OF THE ilEUSE, WAKE COUNTY, NORTH CAROLINA
additional copies of this publication are available from:
North Carolina Department of Natural Resources
and Corrmunity Development
Division of Land Resources
Geological Survey Section
P. 0. Box 27687
Raleigh, North Carolina 27611
Photographs by Jim Page
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TRIASSIC SEOIMErlTARY ROCKS
General Description
Along thew tern side of Wake County lies a thick sequence of red to gray sedimentary rocks of Late
Triassic age. Th se rocks dip easterly at low angles in most places and are abruptly bounded on the east
by the Jonesboro ault. "This great fracture extends northeast from near Corinth (in Chatham County) to
Holly Springs, th n more northerly to pass beb1een Apex and Cary and west of Leesville, continuing to the
Neuse River where it resumes a generally northP.ast course into Granville County (see pl. 1). The Triassic
rocks extend ·12 t 15 r.ii1es westward into central Durham and eastern Orange and Chatham counties. This area
of Triassic rocks is the Durham basin, a term applied (Prouty, 1928) to that part of the Deep River Triassic
belt lyin~ northe
The Deep Riv
st of its constriction near the Cape Fear River (see 1953 Geologic Map of tL C.).
r area is one of about
extend northeastwa d fror.i South Carolina
a dozen large ancl small similar belts in eastern florth America that
to flova Scotia; additional buried Triassic belts are known beneath
the Coastal Plain.
1892) from their o
Sanford (or Cumnoc
The sedimentary rocks composing thern have been named the Newarl': Group (see Russell,
currcnce at Nei,,1ark, N. J. The Deep River basin has been studied in most detail in the
) basin (Car.ipbell and Kimball, 1923; Reinemuncl, 1955) because of the minable coal there.
Investigations in• he Durham sub-hasin that are pertinent in part to Wake County include those of Kerr
(1874 and 1875), Searer (1927), Prouty (1931), Johnson and Straley (1935), Murray (1937), Harrington
(1951), Oavenport •1955), Hooks and Ingram (1955), Ballard (1959), Charles (1959), Grannell (1960), Bain
(1966 and 1972), ad Custer (1966a, 1%66, and 1967).
The Triassic diments in the Durham basin were deposited on a land surface formed by prolonged sub-
aerial erosion of e metamorphic and igneous rocks of the region. Structures and topography that resulted
from mid-to late-P leozoic tectonic activity were worn down to develcp a pen~plain extending across the
present Piedmont re ion. This fairly flat land surface was displaced in late Triassic time by great north-
trending faults tha created elongate basins in which enormous volumes of sediment were subsequently trapped.
The sub-Triassic no confonnity now separates rocks of greatly contrasting character and age. The noncon-
formity is visible long the west side of the Durham basin but is deeply buried everywhere in ~lake County.
Rock Types
The Triassic s dimentary rocl':s consist al~ost entirely of elastic types, ranging from comglomerate to
claystone. Most of the sediment is ·poorly sorted, so that specimens contain a l'lide range of sizes and kinds ,·
of constituents. P 3ominant are silty sandstones and mudstones. Gedding is irregular in form and thi~~-
ness, and various ro k types commonly grade abruptly into one another both laterally and vertically. Coarser
types in many places fill scoured ·channels whose bottoms cut sharrly across underlying material. Cross-
bedded sandstone is orm,on.
~ecause of the ariability of these sediments throughout ~lake County and the extensive and general
nature of the presen study, it has not been feasible to divide ther.1 into formal stratigraphic units. Sub-
divisions based on~ ass lithology were made by Grannell (1960) for a strip extending westward from Raleigh-
Durham airport. In \lake County he distinguished the Sanford Formation with upper, conglomerate division and
lower, sandstone div11sion and the Cumnock Forr.1ation nearby in Durham County. In the present report essen-
tially the same thre lithologic belts are delineated on the basis of distinctive, though not necessarily
dominant, components. The belts recognized are, from east to west, a fanglomerate belt, a sandstone-mudstone
belt, and a limestone chert belt. They are proposed for local convenience and may not be valid•at a
distance, though they are consistent with studies in the Sanford basin and with a more intensive investiga-
tion now underway in he Durham basin (Bain, G. L., oral comounication).
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Fan lomerat belt. Characteristic of the rocks along the east border of the Durham basin is coarse and poorly sort d conglomerate. It consists of pebbles, cobbles, and boulders of many rock types jumbled to-gether in a argillaceous, silty, sandy matrix. The rock fragments are subangular, subrounded, and rounded, and consist of vein quartz, phyllite, metavolcanic rocks, epidote-quartz rock, gneisses, and granite. All these types ccur within a mile or two east of the Jonesboro fault. The presence in the fanglomerate of many fragile pieces of phyllitc indicates they were transported relatively short distances and not subjected to vigorous brasion in stream beds. The local abundance of any one type correlates with its presence to the east. Fr example, hematite ironstone blocks have been observed in the fanglomerate only along SR 1837
' just north o U. S. Highway 70; this is three quarters of a mile west of the iron-rich quartzite in western Umstead Park Rock fragments a foot thick are common. Prouty (1931, p. 480 and fig. 3) reported boulders more than 8 eet in diameter along Sycamore Creek, a locality now submerged by the upper lake in Umstead
Park. Slabs of metavolcanic rocks as much as 8 hy 11 feet may be seen along Haley1 s Branch! half a mile north of Int rstate Highway 40 and west of SR 1650; these lie a thousand feet west of their nearest source. Granitic bou ders up to 2 1/2 feet in diameter occur along SR 1805 a quarter of a mile north of N. C. Highway 98 in Durham County ahout three quarters of a mile west of the county line. The best exposure of the fan-glomerate is t a quarry in the southwestern corner of the county on the west side of Buckhorn Creek a quarter of a ile north of the county line. Exposures are also good along the Southern Railway half a mile to a mile sou h of Morrisville.
Argillac ous sandstones and mudstones are interbedded with the conglomerate layers, and all grade into one another 1 terally and vertically. Some sandstone layers include isolated pebbles or cohbles. Bedding is indistinct in the conglomerates and irregularly lenticular in the finer grained sediments. Most of the rock in this elt is red from hematite.
The west rn limit of the fanglomerate belt (pl. 1) has been placed as far west as layers containing
abundant pebb es were observed; the accidents of exposure have doubtless affected this delineation. Its
width ranges rom about a quarter of a mile near the northern edge of the county to about 4 miles west of Holly Springs In the eastern portion of the belt, conglomeratic rock seems to make up more than half of
the exposurestto the west this becomes perhaps a tenth.
Conditio s of deposition for such coarse and variable red beds are regarded as being those of terres-trial alluvial fans along a steep scarp, where heavy rains alternated with drier tires. The streams are presuqed to h e been intennittent and during flood so heavily charged with suspended fine sediment that slaty rock fra ments were buoyed up and protected from complete disintegration during transport of several miles. The co rsest material may have moved essentially as landslides. The relief along this former scarp is discussed l ter in connection with the development of the depositional basin. The possibility of glacial conditions bei g responsible was considered by some early workers; Russell (.1892, p. 47-53) evaluated and rejected this ypothesis.
Sandstone-muds one belt. The fanglomerate belt merges westward, by decrease in coarse elastics, into a belt consisting chi fly of 5andstone, siltstone, mudstone, and claystone. Here gray to buff sandstones become
common, interb dded with typical red beds. The gray sandstones are better sorted than most of the· red ones and contain mu h feldspar and muscovite mica (micaceous ar~ose). Gray and buff arkose is especially common in the area we
inent in the s
t and southwest of Are.x, where it is a component in the fanglomerate belt
ndstone-mudstone helt. Red mudstone and gray claystone are also connnon.
as ~,e 11 as predom-
Thin layers of moderately well sortP.d conglomerate containing suhrounded quartz pebbles occur locally. In the southwestern corner of the c unty laminated clay and silt and purplish siltstone and shale are noted. The westward trend in Uake County, then, is to~1ard finer grained and less iron-stained sediment and to more distinct layering. The sandstone-rn Qstone belt is 3 miles or more in width and in most places extr.nds beyond the western edge of the county.
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An extensiv suite
igneous and meta orphic
Jonesboro fault i'n Wake
of minerals exists in the Triassic sediments, reflecting the wide variety of adjacent
source rocks. Duhling (1955) sampled Sycamore and Crabtree Creeks just west of the
Courity and reported 24 minerals of which quartz was corrunonest.
epidote and kyanite were ubiquitous in the heavy fraction.
Ilmenite occurred in all fractions,
The clay r.iin
1955); kaolin and
while
rals in the red beds are predominantly illite and montmorillonoids {Hooks and Ingram. vermiculite are minor. Hematite is the only crystalline iron oxide mineral present~ it occurs as fine pa ticles disseminated evenly in the clay and as irregular coatings on many sand grains. Variations in the reddish brown colors of the rocks are believed to be due to variations in particle size and degree of agg omeration of hematite. Hooks and Ingram (1955) conclude that the sediment was derived chiefly from red ateritic soils and partially weathered bed rock in a deeply dissected region.
The depositi nal conditions for the sandstone-mudstone belt are presumed to have been an alluvial plain along a com lex of low-gradient streams wi~h wide floodplains. The sedime"nts formed as channel fil-lings. overflows
and Custer, 1968)
regional directio
eets, and natural levees. Study of paleocurrent directions (Custer, 1966a, 1966b; Leith
utilizing cross~bedding, imbricate pebbles, and scour channel axes. indicates that the of stream flow in the Durham basin was to the.northeast.
Li~estone-chert belt. A narrow belt containing thin lenses of limestone and chert cuts across the western corner of the coun y in the vicinity of the conman boundary of Hake, Chatham, and Durham counties, about 5 miles northwest of Morrisville. The predominant rock in the belt is red mudstone with fine-grained red sandstone. Discon inuous thin layers and lenses of impure gray limestone are best developed west and-north of Nelson (in Durh m County), where they have been known f0r more than a century (Mitchell, 1842, p. 131; Enmons, 1856, p. 2 3; and Kerr, 1875, p. 187-188). This limestone has been described by Grannell (1960, p. 26) and Custer 1966b, p. 15-16 and 1967). The fine-grained limestone has numerous brown and red specks. It is exceerlingly l'.lpure, the insoluble residue of quartz, clay, mica, and or~anic matter averaging •32 per-cent. Microscopic curved laminations and round aggregates suggest organic structures. Impure limestone nodules are numero s in the old quarry of the Triangle Brick Company (in Wake County) east of fl. C. ~:ighway 55 and in roadcuts long that highway half a mile to the south. The irregular nodules range in diameter up to about 4 inches ad occur in layers and in isolated clumps. In the quarry four layers were noted in a 25-foot section of mud tone (Parker, 1966, r. 92). Attempts by the author to trace the limestone west of N. C. Highway 55 failed; he deposit may pinch out here.
The sandstone ·n this belt has considerable calcareous cement. Hard. little-weathered specimens from the quarry display 'luster mottling" as a result of coarse crystallization of the calcite cement. Areas of rrore ·than a square nch show a single cleavage surface studded with enclosed sand grains. Spherical con-cretions one to thr e inches in diameter of calcite-cemented sandstone are fairly common in the Triangle Brick Ccmpany quarr
Lenses of gray chert and of red-hrown jasper also occur in this belt. So111e chert is directly in contact with limestone. but some occurs separately. This siliceous rock occurs mainly in Durham County, but one locality has been n ted 2 l/2 miles north of Morrisville along N. C. Highway 54 and SR 1637. Dark gray to blackish shale is a sociated with the limestone and chert in places.
The limestone ad chert are presumed to have been deposited in s□all, scattered lakes and swamps on the alluvial plain, erhaps through the agency of sir.Jple plants. \Jheeler and Textoris (1971) report algal structures, ostracod s, and burrows. They regard the limestone as having originally been calcareous tufa fanned in a playa la e.
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Fossils
The Tr assic sedimentary rocks in Wake County contain fossils in only a few places. The princ~pal
known local ties are the quarries of the Triangle Brick Company 3 miles north of Carpenter on both sides of
N. C. llighw y 55. Abundant remains of plants and fish are associated with numerous, fragile ostracodes.
Swain and Bown (1972 1 p. 1-3 and pl. 2) describe three species of the genus Darwinula, associated with the
conchostrac n Howellites berryi.
A cast of part of a psuedosuchian reptile (Stegomus sp.) was found in 1965 in the Triangle Brick
C001pany old quarry east of N. C. Highway 55 (Parker, 1966, p. 92). This roughly conical segmented fossil is
about 7 inc es long and from l to 3 inches in diameter. The surface shows parts of nine overlapping trans-
verse curve and laminated plates that are the remains of dernal scutes of the carapace. A few similar
specimens h ve been described from Triassic rocks in Connecticut (Lull, 1953, p. 79-89) and tlew Jersey
(Jepsen, 19 1).
Prouty (1931, p. 478 and fig. 4) reported crustacean remains from a locality half a mile west of Nelson;
this is in urham County about 1 1/2 miles north of the county line. These fossils included smooth shelled
ostracodes, as well as phyllopods (branchiopods) of the genus Estheria (Cyzicus). Hope and Patterson
(1969b) rren ion the presence of Cyzicus in both the Durham and Sanford basins in the Pekin and Cumnock
Formations ut not in the Sanford Formation.
Plant emains are abundant in the Sanford sub-basin of the Deep River basin in association with, the
Cumnock coa at many localities and in the underlying Pekin Formation at the brick shale quarry 1 mile north
of Gulf. T ey have been studied in considerable detail by Emmons (1856, 1857), Fontaine (1883, 1900),
Hope and Pa terson ( 1969a, 1970), Del avoryas and Hope ( 1971), and Schultz and llope ( 1973).
Age and Correlation
The fl ra indicates a Late Triassic age for the rocks of the Deep River basin. The ostracode fauna is
consistent ith this detennination. The rocks are assigned a ~arnian, Norian, and possibly Rhaetian age
(Van Houten, 1969, p. 8-9}, a duration of 15 to 20 million years.
Correl tion of the rocks of the Durham basin with the three formations recognized in the Sanford basin
(Campbell ad Kimball, 1923; Reinemund, 1955) will remain speculative until detailed work is done between
the two sub basins. In the Sanford basin, the Triassic rocks include the Pekin Fo)T.lation at the base, the
Cumnock Fo ation -with coal heds -in the middle, and the overlying Sanford Fomation. In the Durham
basin the l ·meStone-chert belt is likely to be roughly equivalent to the Cumnock Fonnation, and, if so, the
sandstone-dstone helt and the fanglomerate belt are correlative with the Sanford Formation. The question
of whether he three parallel lithologic belts are really superposed formations is to be discussed in con-
sidering t development of the depositional basin.
Structure
Regional al'\d ·local dip. The Triassic sedimentary rocks in Wake County and throughout the Durham basin dip
generally ~stward (pl. l). Bedding in most places strikes north-northeast and dips 5 to 10 degrees east-
. ward. Tru strike and dip are commonly uncertain because of uneven bedding surfaces, lenticular and grada-
tional lay rs, channel scours, and .cross lar.iination. The strata are essentially horizontal in many places.
At numerou scattered localities the rocks strike east-northeast and even northwest, and dips as high as 25
to 30 degr es are recorded. These abnonnal attitudes seem not to be systematically distributed and are not
the conseq ence of folding. They probably result from local drag related to minor nonnal faults (described
later) and to diabase dikes. For example, a dike on ti. C. Highway 55 about 1.5 miles south of Upchurch and
0.4 mile n rth of SR 1601 trends eastward through nearly horizontal strata; the beds north of the dike dip
5 degrees outh for about 30 feet, and those to the south dip 15 degrees south for about 40 feet.
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Prouty (1931~ p. 482) states that the ·dip is steeper in the west portion of the basin than in the east.
Reinemund (1955, p. 81) found the same situation in the Sanforn basin. Stewart and others (1973, p. 100)
conclude from their seismic reflection data that the beds at depth below the Triangle Brick Company quarry
in western ~ake County dip eastward at not less than 20-22 de9rees and perhaps as much as 35 degrees but
that the basement surface is horizontal. These conclusions are difficult to reconcile with one another and
with surface observations. Near the east side in the borrler fanglomerates, low dips to the west occur
sparingly.
The average angle of southeastward dip in the basin has been variously estimated as 20 degrees {Kerr,
1875, p. 141), perhaps 15 degrees (Russell, 1892, p. 94), at least 15 degrees near Durham (Prouty, 1931,
p. 484), 15 degrees (Mann and Zablocki, 1961, p. 196), and about 15 degrees (Bain, 1966, p. 90). My own
impression favors an average dip of about 10 degrees to east-southeast.
Form and thickness of the deposits. The body of Triassic sedimentary rocks of the Durham basin forms an
elongate prism with triangular vertical cross-section; it tapers out to the northeast and thins to the
southwest (beyond Wake County). Along its west side the prism thins to zero thickness in most places
where the rocks lie nonconformably on older crystalline basement. On the east side the prism ends abruptly
against the Jonesboro fault. The deposits are inferred to thicken eastward because at the surface the bed-
di_ng planes dip almost consistently in that direction.
The t__hid:ness of these rocks is not known anywhere in or near Wake County because no well or dril.l
holes have penefrated through them. A 285-foot well drilled at Raleigh-Durham airport and a 497-foot well
at Triangle Brick Ccxnpany were entirely in Triassic rocks (May and Thomas. 1968, p. 102 and 105). A well
drilled about 1885 in Durha~ (Venable, 1887; Prouty, 1931, p. 481) to a depth of 1650 feet did not pass
completely throu9h the Triassic rocks.
An estimate of thickness may be made by considering the width of outcrop and rate of dip,_ though
several uncertainties affect its validity. The strata in most places dip gently eastward, but the amount
and direction of dip vary consideraCly in places. The average dip is estimated to be about 10 degrees a
little south of east. The old deep well in Durham was some 2 miles from the west border of the Triassic
rocks and hence indicates a minimun eastward dip of the basement of 9 degrees. The width of the basin being
about 15 miles, a 10 degree dip would give a thickness at the east side of about 14,000 feet. As pointed
out by Prouty (1931, p. 484), the normal faults that are known to be prese~t may have repeated beds and
increased the apparent thickness. Further, the beds that crop out in the western part of the basin may not
continue down dip to the" east side, but instead they probably grade into others. Hence, the true thickness
may be more or less than 14,000 fe"et. -~c.Kee_and others (1959, pl. S) give the m,3,xi~mum thicknes_s iri th_e-
Durham basin as "10,IJOO .:!:. feet'~--
Two gravity profiles have been run across the Durham basin in Wake County (Mann and_ Zablocki, 1961)
along U. S. Highways 70 and 64. Interpretation of the residual anomaly values indicated that the maximum
thickness of sediment near the east side of the basin was 3100 feet along U. S. Highway 70 and 6500 along
U. S. "Highway 64. Some uncertainty existed whether the value employed (O. l) for the difference in density
between Triassic rocks and the metamorphic rocks outside the basin was appropriate, so the absolute th~ck-
ness values may be in doubt. The data do imply that the thickness doubles in about 11 miles between the
two traverses.
Stewart and others (1973) made a seismic measurement of depth tci basement-at the Triangle Brick Company
quarry at the western edge of Wake County. Their results, though tentative owing to uncertainty as to
velocity values for the rocks, indicate the thickness of seciiments at that point to be 6000 .:!:. 500 feet. If
this thickness of 6000 feet is accepted, the rate of thickening from the west edge of t:1e Triassic rocks to
this point is about 860 feet per mile. This is almost the same as the minimum value indicated by the old
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deep well in Durham. If this thickening rate is projected eastward to the Jonesboro fault, the thickness
at the east side will be about 12,500 feet. More recent investigation by seismic reflection-refraction
traverses (Bain and Stewart, 1975), however, indicates that the thickness adjacent to the Jonesboro fault is
6000-7000 feet and that the maximum thickness, probably in excess of 9000 feet, appears to be in the middle
of the basin rather than along the east side.
The Triassic sedimentary rocks, then, probably are 12,000 to 13,000 feet thick in the vicinity of the
Raleigh-qurham airport. The thickness must 9rarlually decrease northward along the east side of the sedi-
mentary prism into Granville County where the rocks taper out. To the southwest the thickness seems likely
to be about the same through much of Wake County until the constriction near the Cape Fear River is
approached. Reinemund (1955, p. 38-39) estimated that the sedimentary wedge along its southeast side in
the south end of the Durham basin on the east side of the Cape Fear River must be at least 6000 feet thick,
ranging between limits of 5300 and 7100 feet.
Jonesboro Fault. The great fracture that borders .the Triassic sediments on the east was named by Campbell
and Kimball (1923, p. 55-60) for the town near Sanford in Lee County. They seem to have been the first to
have recognized explicitly that the eastern boundary of the Newark rocks is a fault. Maps, sections, and
texts of Enrnons (1856), Kerr (1875), and Kerr and Hanna (1888) do not refer to the matter or do not make
clear whether a fault or an unconformity is intended. Russell (1892, p. ·94) states that the Newark ro,cks
l 1/2 miles west of Cary are "dipping westward and resting on the crystalline terrane from which they were
derived.11 This seems to imply a non-conformity, not a fault contact.
The fault passes in a generally northeast direction some 38 miles completely across Wake County; it
extends, in fact, nearly across the whole state. Its c6urse in Wake County has two major changes in direc-
tion; the northern part (5 miles) north of the Meuse River trends northeast, the middle section (26 miles)
north-northeast, and the southern portion (7 miles), southwest of Holly Springs, northeast again. Some
stretches of as much as 10 miles appear to be straight or gently curving, but elsewhere short, sharp zigzags
interrupt its course.
Angular bends in the border fault are especially well exposed in the vicinity where U. S. Highway 70
crosses the fault, at the intersection of SR 1837 (fin. 8). Though the positions of the fault trace as
mapped may not be ccmpletely accurate, exposures are so closely spaced that only minor revisions are
possible. The effect is an indentation as if the Jonesboro fault were offset westward about 900 feet along
two transverse faults striking east-northeast and southeast. Th_e inferred fault lying southwest of U. S.
Highway 70 probably extends southeastward to displace the magnetite quartzite in northern Umstead Park.
Both the Joneshoro fault and the quartzite show left lateral horizontal offset of about 1200 feet. No
evidence has been detected for continuance of the inferred fault north of the highway into rocks west or
east of the Jonesboro fault.
Irregularities are also clearly evidenced in northern Wake County along the Meuse River, Beaverdam, and
Little Beaverrlam Creeks. The trace of the border fault in much of this stretch lies beneath floodplain
alluvium, so its exact position cannot be mapped. North and west of the Neuse River and Beaverdam Creek,
from the county line to a point half a mile north of the junction of Little Beayerdam Creek, all exposures
are of Triassic sediments, while to the south and'east all are crystalline rocks. The fault boundary here
takes several sharp bends, including a three-quarter mile stretch striking south of east.
The structural picture here is complicated by the merging from the southwest of the Lick Creek fault
(Charles, 1959, map and p. 28, 34, 36) from within the Durham basin. Chief evidence for this fault is a
prominent topographic lineament along Lick Creek in Durham County and Smith Creek in Granville County
(though these two streams are not directly aligned). The courses of the Lick Creek fault and the Jonesboro
border fault, thus, seem to coincide across the northern neck of Wake County. Charles suggests that the
Lick Creek fault offsets the Jonesboro fault about 9 miles northeastward in this area. The abrupt zigzag
49
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Figure 8.
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LEGEND
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OC-~= =--f' =::; =----=~-_..,_~~~~--a. -=-~r-=-"';..:---~ -"---~ -.. ·· f phyllite
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Geologic map of trace of the Jonesboro fault in the vicinity where
it crosses U. S. Highway 70, at intersection of SR 1837, western
Wake County, N. C.
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bends in the border fault, however, argue strongly against significant strike-slip displacement here.
Resolution of this problem is beyond the scope of this report since it involves extensive study in adjacent
counties.
Russell (1892, p. 94) cited a notch in the outline of the Newark rocks as mapped by Kerr (1875) near.
Cary that Russell thought probably indicated faults. This notch was eliminated, however, in Holr.1es 1 revi-
sion ( 1887) of the map ( Kerr and llanna, W88) . This area was later investigated by Golds ton and Stuckey
(1930); their results are considered later under topographic features. The course of the fault at this
locality is now mapped as straight.
Although some of the ahrupt bends in the Jonesboro fault may have been ca.used by cross-faulting, it
' is likely that most of them, especially those at small angles, reflect irregularities in the original
te~sional fracturelthat initiated faulting.
The actual fault surface is exposed almost nowhere. Its trace was mapped (pl. 1) between exposures of
Triassic sediments {to the west) and those of various metamorphic and igneous rocks, spaced a few tens to
a few hundreds of feet apart. Thus, in many places considerable latitude remains for revision of its loca-
tion and details of fonn. Its position is readily observed, however, in the d.itches on SR 1837 about 500
feet northeast of U. S. llighway 70 (fig. 8) and along SR 1435 northeast of Apex.
The best exposure of the fault that is known is at the bend in SR 1902 in Durham County, 0.7 mile west
of Wake County and about 500 feet east of Laurel Creek. Here shattered. mctavolcanic rocks may be observed
in contact with steeply tilted Triassic pebbly sandstone and mudstone. The fault plane dips 80 degrees west
over a vertical exposure of about 5 feet; no other site was found where its dip could be measured, though
it is clearly near vertical. The fault contains 4 to 5 inches of clay gouge. The Triassic rocks abut
sharply against the fault surface, where they are nearly vertical. 1:owever, within 20 feet to the west they
dip about 35 degrees west, and within 1000 feet the dip is 5 degrees west. At this site the Triassic strata
are clearly cut off eastward by post-depositional faulting. Thou9h the basin of deposition is regarded as
due to faulting -on the evidence of the fanglomerates, as discussed later -it is clear that some further
displacement followed the laying down of the strata exposed here.
The minimum amount of dip slip on the Jonesboro fault is indicated by the thickness of Triassic sedi-
ments adjacent to it, some 12,000 feet in west-central Wake County. This value must be increased by what-
ever thickness of rJewark rocks may have been eroded since their deposition, which may be considerable,
though no basis of judgment seems to be available.
Evidence of strike slip is scanty. The possibility of extensive horizontal offset along the postulated
oblique Lick Creek fault in northern Hake County (Charles, 1959) has been noted. Further, in Chatham
County a mile east of Corinth and 3 miles southwest of \~ake County near the crossing of tl. C. Highway 42
and the tlorfolk Southern Railway a·large north-northwest striking diabase dike appears to have been offset
right laterally about 1000 feet. (This locality was brought to the writer's attention by J. L. Stuckey.)
Whether the diabase constitutes severed segments of a single dike, or two separate dikes each ending at the
fault, has not been proven. If the former interpretation is correct, the observation documents a kind of
tectonic episode hitherto unrecognized in the region.
Faults within the basin. The tlewark rocks are visibly displaced by small faults at several places, and
similar unexposed faults of various magnitudes are likely to be numerous. Observed faults are confined
to single outcrops and cannot be traced along strike. They seem to be steeply dipping normal faults, and
most strike nearly north or west.
A good exposure may be seen in western \Jake County in the parking lot of Hennis Trucking terminal on
the southwest side of U. S. Highway 70 half a mile east of the county line. The fault strikes N. 85° W.
and dips 83 degrees north. Correlation of the strata on the two sides of the fault is not certain, but the
51
hanging wall (north side) seems to have dropped about 12 feet.
southwest on the hanging wall and 14 degrees on the footwa11.
known leads to the inference that such orientations elsewhere
from faulting or intrusion of diabase dikes.
The strata strike N. 35° W. and dip 4 degre~s
This abn?nnal attitude where faulting is
probably are local disturbances resulting
Another small normal fault with dip slip of about one foot is exposed in a road cut on SR 1624 one
mile west of Carpenter (on M. C. Highway 55).
An east-trending normal fault was uncovered during excavation at the Shearon Harris nuclear power plant
site near the southwest corner of the county. The strata here dip 10-15 degrees eastward, and the fault
dips about 75 degrees to the. south. Several diabase dikes have been displaced as well as the Newark strata.
Dip slip is reported (Carolina 'Power and Light~company, 1975, p. II -7-8) to be between 80 and 100 feet and
strike slip between 0.5 and 13 feet. This fault has been traced by trenching_.fox._mo.r:e. _than a mile along
strike.
Bain and Stewart (1975) deduced from seismic surveys that the bottom of the Durham basin is broken into
horsts and grahens a mile or more in extent and having relief of more than 1000 feet. These faults probably
also affect the overlying Newark rocks, which are considerably faulted.
Joints. The Newark rocks in Wake County are broken by a multitude of fractures. Though some exposures show
many good joints, systematic jointing is on the whole poorly developed. In more firmly cemented sandstone
layers some joints are approximately planar for a few feet, but these colllllonly merge into curved and irregu-
lar surfaces. Fractures in mudstone and claystone are curved and short. The range in strike and dip is
usually considerable in any one outcrop or small area. No joints were observed that displayed plumose
surfaces.
Watson and Laney (1906 1 p. 231-232) report that exposures of sandstone northwest of Morrisville have dis-
tinct sets of joints (N. 60° U., N. 45° E., and N-S at one place, and tl. 30° W. and ft 60° E. at another).
Likewise, Prouty (1931, p. 483) stated that two rectangular systems of joint sets exist in the Durham basin,
namely, N. 15-35° E. and II. 45-70° W. and a less important one N. 65-70° E. and N. 10-15° Ii. Grannell (1960,
p. 37-40) described a numerous and consistent set of vertical joints near Lowes Grove (in Dur:1am County) that
strikes N. 15° W. Throughout the rest of the area he mapped, mainly in Durham County, scanty data showed
much scatter in strike with two concentrations at N. 45° E. and ti. 80° E. My own experience indicates that
the regularity of jointing in the Newark rocks in Wake County is too slight to merit detailed investigation.
The generally poor development of joints is probahly accounted for by the high clay content of even
the sandstones, which makes them less brittle, and because the region has been subjected to vertical warping
movements since the rlcwark rocks were deposited rather than compression, which would be evidenced by assoc-
iated folds.
Development of the Depositional Basin
The elongate basin in which the Triassic sediments were deposited is regarded as having resulted from
faulting. It seems to have been a half graben produced by intermittent dropping of the block west of the
Jonesboro fault relative to the stationary or upraised block to the east. The sinking block tilted downward
to the east and may have been recurrently bowed up along its western side. Rapid erosion of the higher·
lands both east and west of the half grahen supplied sediment to fill the lowland. Intermittent slip on
the bounding fault renewed the differences in eleva~ion that energized the transfer of rock material from
adjacent higher ground into the trough.
The possibility that the trough of deposition was produced by down-bending of the crust rather than by
faulting has been stressed by Campbell and Kimball (1923, p. _60-61). Under this proposal, displacement on
the Jonesboro fault post-dated all or most of the period of deposition. Had this been the situation,
52
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however, the Newark sediments must have first filled the bottom of the downwarped trough and in time must
have spread farther and farther out to west and east dipping toward the basin axis. Furthennore, downwarp-
ing could hardly have produced the strong local relief needed for developing the fanglomerate known all
along the east side and not elsewhere. Had the basin been a downwarped trough split lengthwise by post-
depositional normal faulting, the upthrown eastern half being eliminated by later erosion, no possible
location of the bounrlar:y·fault through the center or eastern half of the basin would have resulted in the
observed relations, that is, fanglomerates to the extreme eastern margin, finest sediment near the middle,
and coarser sediment again on the west side.
side of the Durham basin clearly points to an
The coarse a·nd poorly s·orted sediment along the entire east
abrupt scarp. The fanglomerate at the northern end of the
basin in Granvi"lle co·u·nty where the Triassic rocks thin out must be stratigraphically lower and older than
that in central Wake County. The continuity of the fanglomerate along the east side of the basin seems to
imply continuity of a scarp throughout the depositional period. Hence, it is argued that the basin was in-
augurated and maintained by faulting. This interpretation is based, of course, on features observed at the
present ldnd surface. Should future data from depth indicate some different kind and sequence of deposits
in the subsurface, modification of the half-graben concept will be required. A similar close dependence of
sediment type on tectonic activity is described by Randazzo and others (1970). in the \~arlesboro Triassic
basin some 80 miles to the southwest.
Let us assume, then that the basin was initiated by faulting 1-'Jith a steep scarp along the east side,
that it remained stationary for a long or short time while sediment accumulated, and that as time went on
the basin was abruptly deepened or renewed many times by recurrent slip along the Jonesboro fault. During
any one period of stability the basin would tend to fill up with coalescing alluvial fans spreading westward
from the scarp, with finer fluvial and lake deposits in the middle, and with elastics of intermediate grain
size on the gentle west slope· (fig 9-A). As the successive scarps were reduced by erosion, the alluvial fans
must have extended up on the margin of the upthrown block, but renewed faultin~ would have cut off·these
extensions along the fault line and their material would subsequently have been redeposited in the basin.
The increment of sediment accumulated between times of faulting should be thickest in the east, and probably
thicker in the middle (the low part of the basin) than on the west, where some earlier deposits would tend
to be eroded and shifted farther into the trough. Original dips should be westward on the east side,
horizontal in the middle, and eastward along the west flank. Renewed slip on the east border fault would
tilt the trough down to the east and provide space for another similar incremental wedge of sediment on top
(fig. 9-D). This inferred rotation of the trough, rather than a vertical drop, would steepen the eastward
dips. lessen or reverse the westward dips (Prouty, 1931, p. 485), and tilt horizontal beds eastward; this
accords with observations at the present land surface that the strata dip generally but variably eastward.
The Durham·basin, then, would have heen filled by the stacking of a series of similar incremental wedges of
varying thickness. The wedges are likely to have extended farther an~ farther westward with time as the
basin filled but to have been cut off sharply on the east by the fault. Post depositional displacement on
the Jonesboro fault seems clearly to have occurred also, as was described earlier. Discontinuous faults
along the west side of the Durham basin ·(see Harrington, 1951) are presumed to be of this date.
According to this concept of the depositional and tectonic history, the stratigraphic division of the
Triassic rocks in the Sanford basin into three fonnations (Pekin, Cumnock, and Sanford) would not apply in
the Durham basin as time units. Each would be ·a lithofacies grading laterally into others and persisting
upward through the whole sediment prism across time boundaries. The apparent superposition of the units, as
now indicated by the generally eastward dips, would be an effect of progressive tectonic tilting during
deposition. The eastward dipping sandstones at the west edge of the hasin are no doubt older than those a
little to the east that dip the same way, but it is suggested that those western layers do not persist
across the bottom of the basin as components of a sandstone time stratigraphic unit. Instead it is felt
53
f
PEKIN
FACIES
CUMNOCK
FACIES
A. First depositional increment
SANFORD
FACIES
-. '".·
PEKIN CUMNOCK SANFORD J
FACIES FACIES FACIES ~-----~------.-_____ ...,._ ____ .,,... ___ ~-=-----c,c-:=,=,7/ --
\ \ ) l
B. Multip],e increments and ,post-depositional erosion
Figure 9. Serial cross sections representing probable conditions of
dePosition of Triass·ic sediments in Durham basiny N. C.,
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II
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II
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that at each time level in the sequence "Pekin" facies grades eastward into "Cumnock" facie·s· and that in
turn into "Sanforrl" facies.
Peneplanation during later Mesozoic and perhaps subsequent times has heveled the Triassic deposits and
removed an unknown thickness. Harrington (1951, p. 155) concluded from an analysis of normal faults along
the west border near Chapel Hill that a thickness of 131)0 to 1800 feet of Triassic rocks had been removed
at that point. McKee and others (1959, pl. 9) indicate that 2-3000 feet were eroded from the Newark rocks
in the [)urham basin.
55
---POSTeNEWARK __ (POST-TRIASSIC) DIABASE DIKES-
'D.jkes of dark ign~~us rock fill fractures in many of the metamorphic rocks, in the Rolesville' batholith,
"and in-the Tri~ssic sedimentary ro~ks': Cretaceous and younger sediments overlie some of them unconformably.
These dikes, then, record an episode of crustal fracturing and intrusion of basic magma during a time of
crustal extension that occurred after accumulation of the Newark sediments and prior to their being eroded
and transgressed by Coastal Plain deposits. Annstrong and Besancon (1970) give K/Ar dates for most of the
dikes, sills, and flows studied in eastern North America of about 200 m.y., though some were older. This
makes them Triassic and contemporaneous with sedimentation, a situation not confirmed hy local observatfons.
Paleomagnetic studies (De Boer, 1967) indicate that the dikes were intruded during the Jurassic period, a
conclusion concurred in by Sutter (1976).
Though many of these intrusions in steeply dipping foliated rocks are locally conformable, sill-like
bodies, all are here referred to as dikes because the general character of the group is discordant to older
structures. Sills have not been observed by the author in the Triassic sedimentary rocks in Wake County,
but they are known nearby in Durham and Granville Counties and in the Sanford area.
Many diabase dikes have strong positive expression on the aeromagnetic maps, some are only faintly
expressed, and some have no effect. These relations are described in a separate section of this report.
The aeromagnetic maps have heen invaluable in tracing many dikes between widely spaced outcrops and through
sediment-covered areas.
The dikes are generally distributed across the county. They seem to be equally numerous in the crys-
talline ~nd Triassic areas, though large dikes are most coli1ITlon east of Raleigh. Their locations are shown
on the general geologic map (pl. 1) and on figure 10, which also records measured thicknesses. Some two
dozen major dikes have been recorded, and many other thin ones have been noted; many more can be found.
Most of them trend north-northwest though a significant number strike north and nearly east-west. Without
exception thP.y dip almost vertically.
Thicknesses range from less than a foot to as much as 200 feet. The largest dike discovered has been
traced along a smoothly curved, northward course through Garner, east Raleigh, and Millbrook for a distance
of 15 miles. Its thickness varies from about 50 to 200 feet. Its southern end is in adamellite, but for
most of its length, it lies in various gneisses to the west of the pluton. In Garner along U. S. Highway
70 several small dikelets a few inches thick parallel the east contact within 10 feet of it. At least three
dikes in the Rolesville hatholith are 100 feet thick in places. The longest dike known extends N. 1n° W.
from the Johnston County line near Shotwell for 18 miles to near Wake Forest.
No dikes have been traced to or across the Jonesboro fault in Hake County. However, a south-ti:-endillg~-..
dike at Morrisville has been traced ·to within a mile of the fault. An east-trending dike north of Apex
extends within 2 miles or less, and a south-trending dike in easternmost Durham County just north of N. C.
Highway 98 extends to within at least a mile of the fault and may possibly cross it.
Most dikes are tabular with locally uniform thicknesses. Individual dikes show marked but gradual
variations in thickness along strike. A few thin dikes in granite are irregular in fonn, having right angle
bends in one or both contacts. Offshoots a~ few inches thick are not uncommon. In a few localities two or
more nearly parallel dikes occur within a few feet of one another, probably the result Of oblique splitting
of one dike into two. Actual intersections of dikes have not been observed, but several instances of
dikes with strongly divergent trends indicate that this may occur, though forking seems roore likely.
sions of wall rock are comparatively rare.
nearby
Inclu-
The diabase is black, massive, and generally fine grained; in the larger dikes the texture is medium
grained, and in the thinner ones it is aphanitic. Large dikes have aphanitic borders and coarser interiors.
The rock is distinguished from other dark rocks in the area -such as hornblende gabbro and amphibolite -
by narrow, lath-like crystals of dark feldspar whose cleavage surfaces in fresh rock may be recognized with
56
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a hand lens. A11 exposures are weathered, and the diabase saprolite is typified by coiicentrically exfoli-
ated rock spheroids embedded in dark brown~ plastic clay. Most spheroids contain remnant cores of fresh
rock. The outcrop strips of the dikes are marked discontinuously by dark spheroidal boulders in and on the
soil that range in diameter from a few inches to several feet.
Diabase consists chiefly of plagioclase feldspar, pyroxene, olivine, o1d opaque minerals.
microscopic study indicates that labradorite originally composed about 50 percent of the rock,
Preliminary
augite 30 to
35 percent, olivine 10 to 20 percent, and magnetite-ilmenite 3 to 5 percent. Secondary alteration has pro-
duced varying amounts of serpentine and chlorite at the expense of olivine and augite. The texture is inter-
granular or subophitic, with anhedral pyroxene and olivine lying between or partially enclosing tabular
p1agioclase. Radiating groups of feldspar crystals are common.
Hennes (1964) has shown that dolerite (diabase) in the Deep River basin varies greatly in composition.
He recognized four classes; in these~ olivine rangeri from O to 54 percent, au~ite from 5 to 49 percent,
p1agioclase from 34 to 70 percent, micropegmatite from Oto 27 percent, and opaque minerals from 2 to 6
percent. Weigand and Ragland (1970) distin~uished four chemical types: l1) olivine nonnative: (2) quartz
nonnative with low Ti02; (3) quartz normative with high Ti0 2; and (4) quartz nonnative with high iron.
Variations in Wake County diabase have not been investigated in detail, but judging from preliminary petro-
graphic study, minor color differences in saprolite, and marked differences in magnetic effects, they also
rrust have a ·wide range of composition.
All dike contacts are sharply distinct. Contact metamorphic effects have been noted only near dikes
in Triassic sedimentary rocks. The typical red color of sandstone, siltstone, an~ ·shale has been chang_ed
to black at and near the contacts.,.) The effect is most marked near the dikes and gradually dies out at dis-
tances equal to about half the dike thickness. This ·is readily observ~d at the dike that cross~s N. C.
Highway 54 a quarter of a mile.southeast of Morrisville. The change presumably is due to recrystallization
of hematite pigment in the sediments to magnetite under higher temperature.
A dike 2 miles northwest of Apex that crosses N. C. Highway 55 at a point 1.3 miles north of U. S.
Highway 64, includes a slab of sandstone that has been partially recrystallizerl. The vertical dike strikes
east-west, is about 20 feet thick, and cuts throu~h Triassic brown pebbly arkose and laminated claystone.
The sandstone inclusion is 8 to 12 inches thick and stands vertically in the middle of the dike. It has
been bleached white and is now a hard hornfels in which original elastic texture is still obvious. The
fine-9rained matrix, however, has been recrystallized so that sand 9rains an~ quartz pebbles are completely
surrounded by fine fibers of sanidine radiating from their surface; small flakes of chlorite (?) fill the
intervening space.
Detailed petrographic and chemical studies of similar dikes in nei~hhoring counties to the west and
southwest have been made by Hennes (1964), Justus (1966), Ragland and others (1968), Reinemund (1955), Singh
(1963), and Weigand and Ragland (1970). Sills or possibly buried lava flows in Triassic sedimentary rocks
in Granville and Ourham Counties have been described by Koch (1967a; 1967b). A vein of laumontite about 4
inches thick is reported (Furbish, 1965) in a dike 3.5 miles west.of Wake County.
The diabase dikes in the county show little consistent relation to other structures. The commonest
joints in the metamorphic and i~neous rocks are near east-west, while most dikes strike north-northwest.
The dikes also seem independent of foliation, though in places they are concordant. In the Triassic rocks
the dikes parallel the local joints in small areas but show nllch greater regional consistency in orientation
than does the poorly developed jointing. This lack of consistent parallelism suggests that many or most
joints (except those filled with quartz veins) were not present until after the time of dike intrusion. As
previously su~gested, jointing probably occurred at various times during recurrent re9ional uplifts.
The distribution of Triassic dikes in the eastern United States and their re9ional variations in
orientations have been described by King (1961; 1971). He showed that between Alabama and North Carolina
57
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the dikes strike northwest, while farther to the northeast they swing consistently clockwise through north
to northeast. They are sharply discordant to all earlier trends, even to Triassic trends. The Wake County
dikes fit this regional pattern.
The presence of numerous north-trending dikes implies a suhstantial east-west extension of the earth's
crust in this region at the time they were intruded. Tabulation of 22 principal dikes in a 10-mile wide
strip extending 38 miles from east to west across the middle of the county gives an aggregate dike thickness
of 945 feet. This total thickness indicates an average crustal expansion of 24 feet per mile (or 0.5
percent). This fracturing and extension is_ believed to be an aspect of continental rifting as North America
and Africa separated when the Uorth Atlantic ocean basin was initiated during the Jurassic period (De Doer,
1967; May, 1971).
59
Pleistocene epoch. The highest of these terraces is limited on the west by the Coates scarp with toe eleva-
tion of about 255 feet (Daniels and others, 1966, p. 178-180). This scarp on the uplands lies east of Wake
County though fluvial counterparts extenrl up the Neuse drainage into the county. The presence of this
marine topographic feature so near Wake County raises the possibility that still higher stands of the sea
may have been responsible for erosional surfaces and upland sediment across l-Jake County. Though this con-
cept cannot be rejected, the fluvial origin is favored by the variable elevations and heterogeneous
character of the sediment.
A thorough investigation of terraces on'upland ridges and valley sides, together with their superficial
sediments, is needed to elucidate the erosional and perhaps tectonic history of the region during late
Cenozoic time. All these features are aspects of the development of the e.xisti_ng valley system and are
remnants of earlier landscape stages having different stream positions. The higher level surfaces are the
older, and the formation of lower levels has involved partial destruction and modification of earlier land
fonns as the shifting drainage cut deeper into the peneplain. Much of this valley shaping occurred during
the Pleistocene epoch when stream gradients and base level of erosion varied with sea level fluctuations
controlled by waxing and waning of the continental glaciers.
Topographic Divisions
Though the land forms across Wake County seem generally about the same, closer observation shows inter-
esting differences related to the four principal geologic sub-areas. Some of these differences are readily
apparent to an observer outdoors, while others require the larger vie~ provided by contour maps. Each area
has some distinctive features not shared by the others. These geomorphic divisions generally grade into one
another though sharp boundaries are evident locally.
Metamorphic area. The central and northern parts underlain chiefly by metamorphic rocks are a litt1€ more
hilly than elsewhere. Local relief is coounonly as much as 100 feet from upland to adjacent stream, and
many slopes are steep. The highest areas in the county are irregular patches veneered with upland fluvial
(?) sediment (pl. 4 and fig. 14) rising above 500 feet at Apex, Cary, Leesville, Six Forks, and Purnell.
They are situated-along the western side of the metamorphic area, Cary and Leesville being just east of the
Jonesboro fault and Apex just west. They 1 i e in a be 1t some five mil es wide that trends about M. 35 ° E.
The belt joins the Cape Fear-Neuse divide at Apex (elevation 510 feet), making an angle with it of about 40
degrees. No other areas reaching 500 feet are within 12 to 20 miles westward, on the west side of the
Triassic area. The significance of these remnant topographic highs is uncertain.
Some small tributary streams ln the metamorphic area tend to flow along north-northeast lines parallel
to the foliation of the rocks; examples include much of House Creek and Beaverdam Creek in west Raleigh,
Lower Barton Creek, and Richlands Creek west of Wake Forest. Their positions and courses probably are con-
trolled by strongly contrasting resistence to erosion of adjacent rock layers. Larger streams and many
smaller ones, however, flow across the foliation direction.
Adam Mountain at Bayleaf is a small monadnock in this belt that results from a partly silicified soap-
stone body. It is isolated by small cre~ks on the east, west, and north sides above which it rises over 200
feet to a surrrnit elevation of 478 feet. This height, however, is only about 40 feet above the level of the
general upland nearby. Although soapstone is mechanically soft, it is resistant to chemical weathering.
This body contains much siliceous rock, thus pennitting it to project above more thoroughly decomposed
feldspathic gneisses. Iron Mountain back of Stony Hill Church is a similarly steep knob resulting from
limonite-rich siliceous rock in an ultramafic body.
Jrfa'ssic sedimentary" area./ The Triassic area in western Wake County is not only a structural basin but is
also a topographic lowland as was recorded long ago by Mitchell {1842, p. 130). Elevations along the west-
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ern side of the adjacent metamorphic belt commonly exceed 500 feet, while within the Triassic basin few
uplands reach 450 feet. and most of the area lies below 400 feet. The highest points in the Triassic area
in Wake County are about 510 feet at Apex and about 500 feet at a point 2 miles north-northwest of Leesville.
Both of these points are just west of the Jonesboro fault; the fonner is also on the Cape Fear-Neuse divide
(fig. 14). Elevations of the upland surfaces within the Triassic basin in anrl near Wake County decrease
regularly westward, while those in the metamorphic and 9ranitic areas decrease eastward. This can perhaps
be partly accounted for as general slopes toward the major rivers. but the belt of hi9hs north of Apex does
not coincide with the drainage divide. These isolated topographic highs may be remnants of a_fonner drain-
age divide between the areas underlain by metamorphic and Triassic rocks. Their significance, however, re-
mains an enigma whose solution will require regional study.
A sharp topographic break marks in places the Jonesboro fault, the eastern limit of the Triassic rocks.
Crabtree Creek has a floodplain half a mile wide northeast of Morrisville in Triassic rocks, but after cros-
sing the Jonesboro fault near 1-401 its valley narrows to a rocky gor~e in the metamorphic rocks. Like-
wise, the Neuse River in northern Wake County meanders through a floodplain a mile wide in Triassic rocks
but becomes a narrow, steep sided vallP..V in the metamorphic rocks. In this vicinity several streams follow
the Jonesboro (or Lick Creek) fault~ these include the upper part of Little Beaverdam Creek, the lower part
of Beaverdam Creek, the Neuse River at N. C. Highway 50, lower Lick Creek, and lower Laurel Creek. A dis-
tinct fault-line scarp exists for l 1/2 miles north and 2 1/2 miles south of the point where the Neuse River
crosses the fault. Small streams that drain westward down this scarp have unusually steep gradients in the
crystalline area and extensive outcrops of hard rock. The dam site for the reservoir on Beaverdam Creek
extends across the Jonesboro fault just north of the Neuse. This ~nvolves contrasting foundation conditions
along the northeast and southwest oarts of the dam, as well as the remote possibility of earthquake dama9e.
A fault scarp 2 miles west of Cary was described by Goldston-and Stuckey (1930), but this is not con-
finned by the writer1 s recent work. The earlier observations were made without the benefit of a contour
base map. The Jonesboro fault in this vicinity cuts N. 20° F.. rliagonally across Coles Branch. the ridge to
the west, and also northward across the unnamed valley north of N. C. Highway 54.
of the fault is detected here or elsewhere to the southwest in Wake County except
No topographic expression
for the probably fortu-
itous coincidence of the primary drainage divide with the fault between Apex anrl Holly Springs and the fact
that Jim Branch near Burt nearly follows the fault trace.
The significance of the
graphy along the Neuse River
general lower altitude of the Triassic lowland, the abrupt changes in topo-
and Crabtree Creek valleys \'/here they cross the Joneshoro fault. and the belt
' .
of sediment-covered hilltops above 500 feet elevation near the west s1de of the crystalline area is presently
unclear.
hence may
that they
The Triassic rocks are commonly regarded as more
lower level. The
readily eroded
great depth of have been worn to a relatively
also should be readily eroded. Outcrops of hard rock, however,
crystalline areas but essentially absent in the Triassic. A greater rate
produce a subsequent drainage pattern with streams parallel to the belt.
than the crystalline rocks and
saprolite on the latter suggests
are connnon along streams in the
of erosion in the Triassic should
Major tributaries of the Cape Fear
River in the basin have this relation. In the wide expanse of lower country between the 500-foot elevations
east and west of the basin, at sites 0.5 to 6 miles west of the Jonesboro fault, patches of upland sediment
lie on ridge crests at elevations ranging from 330 to 370 feet. Though this might su~gest downfaulting of
the basin since peneplanation, it may instead indicate it was worn lower during that process. Regional
study is required.
Granitic area. The eastern granitic part of the county is somewhat subdued, rolling country. Hilltops tend
to be broad, gently sloping, dome or shield shaped. Local relief is co1m1only less than 100 feet, and steep
slopes are rare. Little River, Buffalo Creek, Marks Creek, and Poplar Creek, all in granite. have straight,
80
Co11ection6L .
G. c. Nicholson
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·._ Cai lectlonofl /
G. C. Nicholson
Ref. 19 .
GEOLOGY AND GROUND-WATER RESOURCES·
IN THE RALEIGH AREA
NORTH CAROLINA
DIVISION OF GROUND WATER
GROUND WATER BULLETIN NO. 15
North Carolina
Department of Water Resources
RALEIGt_,
NOVEMBER
1968
''
l ;,;
,:_{
.\I
. GEOJ_,OGY AND GROUND-WKfER RESOURCES
IN TIIE RAJ_,EIGH Al{EA
NOR1,H CAJ{OLINA
By
V. JEFF MAY
HYDRAULIC ENGINEER, U.S. GEOLOGICAL SURVEY
CHEMICAL QUALITY OF WATER SECTION
By
J. D. THOMAS
CHEMIST, U. S. GEOLOGICAL SURVEY
GROUND WATER BULLETIN NUMBER 15
NORTH CAROLI NA
DEPARTMENT OF WATER AND AIR RESOURCES
George E. Pickett, Director
Division of Ground Water
Harry M. Peek, Chief
PREPARED COOPERATIVELY BY THE GEOLOGICAL SURVEY
UNITED STATES DEPARTMENT OF THE INTERIOR
AND THE NORTH CAROLINA
DEPARTMENT OF WATER AND AIR RESOURCES
GEDIDGY
TRIASSIC ROCKS
Triassic sedimentary rocks underlie large areas in western Wake and
southern Granville Counties. The rocks comprise part of the Triassic
,J.:rhwn basin which is one of the three sub di visions of the Triassic Deep
n,,;er basin as divided by Prouty (1931). Triassic rocks in the Raleigh
,,-,-rc,a include buff arkosic sandstones, red to maroon argillaceous sandstones,
,.ur11le to maroon shales, and coarse fanglomerate. The source areas for
~''"""' sedimentary rocks were the pre-Triassic metamorphic and granitic rocks
west of the basin for the interbedded sediments, and the pre-Triassic rocks
east of the basin for the fanglomerate. The Jonesboro fault forms the
eastern contact of Triassic rocks with pre-Triassic rocks. In Granville
County the western contact is an erosional surface.
Interbedded sandstone and shale can be seen at location WK-8 (figs. 5
and 13). Here the sandstone is essentially composed of quartz, feldspar,
and iron oxide. The thick interbedded shales have weathered to a dark-red
clay leaving the thinner sandstone beds as nearly horizontal ledges. The
sandstone beds range in thickness from less than 1 foot to about 3 feet and
can be traced for several miles along N. C. State Highway 55 north of Apex •
. , ' .,, " . .,._,
.-. ('\ • .,;\i\ ,,_ ,'"""'L):•
I ,,\~,),_,;<~;:i;f ·•••~~ dit~~~Jflf
Figure 13.--Interbedded Triassic sandstone and shale,
8 miles north of Apex, Wake County.
Buff arkosic sandstone (loc. G-9, fig. 5) is the predominant Triassic
rock type in Granville County. Angular fragments of feldspar and subrounded
to angular quartz grains are the chief constituents of this rock. Mica
composes about 5 percent of the rock. The angularity of the quartz and
feldspar indicates a relatively close source area, perhaps the granodiorite
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GROUND WATER IN THE MLEIGH AREi\
which borders the Triassic on the northwest side of the basin. The com-
position of the arkosic sandstone also indicates that granodiorite was the
chief source rock.
Basal beds of arkosic sandstone interbedded with maroon to purple
shales unconformably overlie pre-Triassic rocks along the western edge of
the Triassic basin in Granville County. Angular fragments of shale are in
the lower part of the sandstone beds where the sandstones overlie the shale.
At places the sandstones contain conglomeratic lenses of small, well-rounded
pebbles.
Fanglomerate crops out along the eastern edge of the Durham basin forming
a belt that is as much as l mile wide in places (loc. WK-9, fig. 5). It is
composed of angular rock fragments and rounded to subrounded boulders, ·cobbles,
and pebbles in a heterogeneous mixture. Boulders l foot in diameter are
common. The interstices between the larger fragments and boulders are filled
with ~and, silt, and small pebbles.
· Dense bla-ck .diabase dikes intrude the Triassic sedimentary rocks;, They
strike at small angles east and west of north and range in thickness from a
few inches to several tens of feet.
At some localities in Wake County, Triassic rocks are unconformably
overlain by unconsolidated sands and clays which at one location are cross-
bedded. These sands and clays are thin and may represent outliers of Coastal
Plain sediments of Cretaceous age.
The Triassic sediments were deposited in a subsiding basin, probably
during a period of moist to humid climatic conditions (Reinemund, 1955, p. 53).
The T.riassic beds dip towards the--Jones.boro fault at an average of 12
degrees, and strike approximately parallel to the fault plane. Vertical
displacement of the fault is at least the maximum thickness of the strata.
This was determined by Reinemund (1955, p. 27) to be about :10,000 feet, The
thickness of Triassic rocks that has been removed by erosion is unknown, but
the maximum vertical displacement was no doubt much greater than the maximUl!l
thickness of the strata now present. The-fault plane dips west and northwest
at about 65 degrees.
Soils formed from weathering of the shales are blackish-red to purple
clay-soils. The arkosic sandstones weather to light-brown, sandy loam-soils
that resemble soils formed from felsic intrusions. Fanglomerate weathers to
dark-red soils which can be recognized by the abundant residual cobbles.
TUSCAWOSA FORMATION
Smith and Johnson (1887, p. 95-116) proposeii the name Tuscaloosa for
sediments of Cretaceous age exposed at Tuscaloosa, Alabama. Cooke (1936,
p. 19) first applied· the name Tuscaloosa to Cretaceous equivalents in North
Carolina.
-32 -
. GROUNDaWATER HYDROlfJGY
In general, ground water is steadily moving under the influence of
,·:·o:,ity from recharge to discharge areas. The rate at which it moves ranges
·-···oi:i a few feet a day to a few feet a year (Meinzer, 1942, p. 449), varying
.'i:•ectly with the hydraulic gradient and with the size and arrangement of
:,'.1e interstices.
Ground water may be discharged naturally by several methods. In humid
"-:·eas, such as the Raleigh area, where the water table slopes toward the
sc,eams and rarely falls below the level of them, there is a continuous
seepage which maintains the flow of the streams in dry periods and adds to
c,,e flow during wet periods. Where the water table is close to the surface,
ciiere is heayy discharge by evaporation and transpiration during the spring
"-~d summer months. Springs and seeps are also areas of natural ground-water
discharge.
THE OCCURRENCE AND MOVEMENT OF GROUND WATER
The amount of water that can be stored in the rocks and soil is con-
crolled by the size, shape, and number of pore spaces they contain. The
rocks of the earth's crust, including soils and other weathered materials,
contain pore space or interstices that are filled with water in the zone of
saturation. These interstices range in size from the microscopic pores in
clays to cavernous openings in some limestones and dolomites. Unconsolidated
sediments, such as gravel, sand and clay, contain primary pores between the
,indi victual grains. When these sediments are consolidated, s_uch as the
'r,iassic sedimentary rocks, the total volume of pore space is reduced by
compaction and cementation of the sediments. In crystalline rocks such as
granite, schist, and gneiss, the volume of primary pore space between
. individual components is very small. Most of the water in these rocks is
contained in secondary interstices which were formed after the rock was
, lithified. The· mo.st. important secondary interstices in the Raleigh area
,_include joints, planes of cleavage and scJ::listosity, and solution channels.
In the igneous and metamorphic rocks that underlie most of the Raleigh
area, many of the interstices are formed or enlarged by normal weathering
processes at or near the earth's surface. With_depth,. the size and abundance
of interstices decreases, consequently most ground water is in the upper
100-to 200-foot-zone of the earth's crust. Several.types of interstic~s
are shown in figure 14. The path of water along interstices in some rock
types is shown in figure 15.
Porosity is the ratio of the volume of the interstices to the total
volume of the rock expressed as a percentage. The porosity of different
rocks is variable. Clays commonly have a porosity of 50 percent or more.
In some crystalline rocks such as granite, the porosity may be less than
1 percent.
Specific yield is the ratio of the volume of water a saturated rock
will yield by gravity to the total volume of rock and is usually stated as
a percentage.
-35 -
-· -- - - --- - - - --
I.:
·A-Primary interstices in
well-sorted sedimentary
deposit.
s::-Pr_i_~or-Y interstices-;in
poorly sorted sedimentary:.
:aep_osit.· ·-
-C-·Primary interstices· in
sedimentary rock. Porosity
hos .been greatly reduced'
by cementing material-.
0-Secondary intertices as
solution cavities.
E-Secondary. interstice·s
as fractures. .
F-·s·econdory interstices as
tr,fotures formed· by
G -Secondary interstices
olori9 foliation planes,
i ptfusion·.
:·Figure 14. --Diagram illustrating sev~ra.L types of interstices.
&J.#!gf/'U'" •.
~-.c.-~1/4.;1~~'-: .. -.. _ _ --·
----Unweathered rock
'--....
A.--Woter moves along frocture~S
formed by intrusion>
B. --Water moves along fractures
in rock
GROUND-WATER HYDROIJ1GY
Well
C.--Water moves along foliation
planes and joints
Figure 15.--Diagrams illustrating movement of water along
secondary interstices.
A rock unit or formation that can yield usable quantities of water to
wells is called an aquifer. The relative ability of an aquifer to transmit
water is called its permeability. Porosity and permeability are not
necessarily related. The porosity of a rock depends only upon the volume
of the interstices in relation to the total volume of the rock, whereas the
permeability depends upon the size and shape of the interstices, the degree
to which these are conne_cted, and the size and shape of the interconnections.
Clay with a porosity of 50 percent may yield little or no water because the
pores are so small that the water is held in place by molecular attraction.
On the other hand, clean well-sorted sands or gravels may have less porosity
but yield larger quantities of water because the pores are larger and
interconnected. The permeability of sands or gravels is greatly decreased~
when clay or silt is mixed with them, or when they are consolidated by ·
compaction and addition of a cementing material. ·
The top surface·of this zone of saturation is known as the water table.
The water table is not a stationary, flat surface, as the name implies, but
is a fluctuating, irregular surface that locally parallels the topography.
The general relation of the water table to the topography is shown in
figure 16.
Rocks or unconsolidated material that contain unconfined water in the
zone of saturation are water-table aquifers. An artesian aquifer contains
water in the zone of saturation that is confined under pressure, the pressure
being greater than atmospheric pressure. Brown (1959, p. 16, 17) explains
ground-water occurring under artesian conditions as follows: "Water entering
an artesian aquifer where it crops out or is overlain by permeable material
percolates downdip by gravity, eventually passing a line beyond which the
aquifer is filled to capacity and is both overlain and underlain by relatively
impermeable beds. Because the weight of the water updip in an artesian
aquifer exerts pressure on the water downdip in the same aquifer, the hydro-
static pressure increases progressively in a downdip direction. Thus the
water level in a well that taps an artesian aquifer stands above the top of
the aquifer and the weight of the column of water in the well counterbalances
-37 -
GH0UND WA'l'EH IN 'l'HE HALEIGH AR.FA
Dikes are tabular rock bodies of intrusive igneous rock., They are not
usually good aquifers, but often the host rock adjacent to them may have been
made more permeable by fractures resulting from the force of intrusion and
'heat. Many wells near Triassic diabase dikes in the Triassic sedimentary
:rocks are above average producers.'. These dikes sometimes form underground
dams which obstruct the natural movement of ground water, causing the water
table to be closer to the surface on one side of the dike.
Topography
Topography is one of the most useful criteria in determining the relative
water-bearing characteristics of the underlying rocks.
In general wells drilled on hills or other upland areas are less apt to
yield the desired quantity of water than wells drilled in draws or other
depressions. The reasons for this are stated by LeGrand and Mundorff (1952,
p. 18-19) as follows:
"(1) Hills and upland areas readily shed much water from·
precipitation as surface runoff. As a result, there is less seepage
into the ground to become ground water. On the other hand, the low-
lands obtain influent seepage directly from precipitation and also
from upland surface runoff.
"(2) 'l'he direction of movement of the ground water is toward
the valleys where part of it discharges into streams. In addition,
influent seepage may occur from upland rock slopes beneath the
residual material. 'l'he more impervious the bedrock, the more readily
is water deflected down the slope along this contact.
"(3) Wells located in lowlands may salvage some of the water
that would be lost naturally by discharge from the underground
reservoir. There the depressed water level resulting from pumping,
if near a discharge area, prevents further discharge out of the area.
"(4) Wells on hills penetrate the water table at a greater
depth than those in lowlands. When a well on a hill is pumped, the
water table is lowered as a cone of depression, the center of the
cone being at the well. As pumping continues the cone may grow
larger and deeper but its span is limited because of the topography
and because of the relatively low permeability of rocks at pro-
gressively greater depth below the surface. The yield of wells under
these conditions is not great. On the other hand, wells in·lowlands,
even though penetrating the same rocks as those on uplands, intersect
the water table near the ground surface. 'l'hus, the water table can
be lowered a greater distance by pumping than in a well of the same
depth on a hill. The fact that the static and pumping water levels
lie nearer the ground surface than in wells on hills results in the
pumping level lying in a more permeable zone; hence the intake area
is broader and the yield of the well is larger.
-44 -
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. . . . . . . . .
. ROCK UNITS AND ·wATER-BEARING PROPER'rIES
•rable 11. --Swnmary of the principal map units and their
water-bearing properties
Description
Gray to white sands, in
places arkosic, with inter-
bedded clay lenses. Pebbly
beds at base at some local-
ities. Maximum thickness
in Wake County about 80
feet.
Water-bearing properties
Water stored in primary interstices
between sand particles. Yields
adequate amounts for domestic use
to dug and bored wells. Water
commonly contains objectionable
amounts of iron.
Includes buff colored arkosic •Rocks made impermeable by compaction
sandstones, and red to '-and cementation. Water is stored in
maroon argillaceous sand-and moves along j~int and fracture,
stones and shales. Coarse planes~ Difficult to obtain adequate
fanglomerate.near the amounts of water for domestic use at
Jonesboro fault forms the many places. Most favorable loca-
eastern boundary of the tions for wells are in proximity to
basin. diabase dikes. Average yield of 84
drilled wells is 6 gpm. Fifteen of
the 84 wells yield 1 gpm or less.
Water at many places is moderately
hard to hard.
Light to pinkish gray medium-
to coarse-grained biotite
granite. Associated with
the granite are many
coarse-grained dikes which
have intruded the host
rocks.
Coarse-grained porphyritic
biotite granite showing a
weak gneissic structure of
rudely alignei orthoclase
feldspar crystals and
biot_ite. Feldspar crystals
up to 2 inches in length
are set in finer-grained
groundmass of quartz and
bioti te.
Water is stored in and moves along
steeply dipping joints and nearly
horizontal sheeting fractures.
Aiequate domestic supplies can be
obtainei from drilled wells at most
places. Favorable locations may
yield small industrial and municipal
supplies. Average yield of 217
wells is 17 gpm. Water is soft and
low in iron; quali.ty suitable for
domestic and most industrial pur-
poses.
Water circulates through widely-spaced
joints and ·sheeting fractures. Has
about the same water-bearing pro-
perties as the finer grained biotite
granite described above. Average
yield of five drilled wells is 16
gpm. Water is soft and low in iron.
-55 -
GROUND WA'rER IN TJIE RALEIGH AREA
WAKE COUNTY
(Area: 864 square miles; population in 1960: 169,082)
GEOGRAPHY
Wake County, in the southern part of the Raleigh area, is the largest and most densely populated county in );he area. It is bounded by Johnston, Harnett, Chatham, Durham, Granville, and Franklin Counties. Raleigh, population 93,117 is the capital of North Carolina, and largest city in the area of investigation. Other population centers in the county include Cary, Apex, Garner, Wendell, Zebulon, Fuquay Springs, Rolesville, Wake Forest, and Holly Springs.
The county is the most industrialized county in the area, and most industries are located in or near Raleigh. Major industries are in the fields of electronics, research, textiles, lumber and wood products, iron and steel, and food and drink processing. Raleigh is the center of State government and several colleges are located in the city. Income from the sale of farm and dairy products is important to the economy of the rural areas of the county; tobacco is the chief crop.
Wake County lies mostly within the Piedmont physiographic province, an uplifted and-partially dissected peneplain. The topography is gently rolling and interstream areas are usually broad and flat. The most rugged topography is near the larger streams where relief is generally between 50 and 100 feet per mile. No hills stand out prominently above the general upland surface. The Fall Zone, a boundary between the Piedmont and Coastal Plain provinces, passes through the southern part of Wake County.
The Neuse River and its tributaries drain about 80 percent of the county-. The remaining 20 percent in the southwestern part of the county is drained by tributaries of the Cape Fear River. The Neuse River and many of its larger tributaries are antecedent streams which flow in a southeastern direction. The directions of the smaller stream courses are controlled primarily by regional structure and relative resistance to erosion of the underlying rocks.
GEOLOGY
Rocks of the mica gneiss unit are exposed both east and west of the large granite pluton. The lar"gest area underlain by these rocks is a north trending zone through the central part of the county west of the granite. The rocks consist principally of biotite-feldspar gneiss, quartzitic gneiss, garnetiferous biotite gneiss, and interbedded gneiss and schists. Near the main mass of granite, the biotite-feldspar gneiss is prominently banded. Light colored bands are composed mostly of orthoclase feldspar and quartz; darker bands are composed of biotite, quartz, and minor amounts of feldspar. The banded appearance is accentuated by textural differences; the biotite-rich zones are consistently finer grained than are the feldspar-rich zones. Quartzitic gneiss is exposed west of the banded gneiss as a northeast-trending zone that underlies most of the western part of the city of Raleigh •
. -98 -
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. COUNTY DESCRIPrJ:ONS
The gneiss is composed of disseminated granular quartz and biotite mica,
Schists are interbedded with the quartzitic gneiss and some of the schist
beds are graphitic. Garnetiferous biotite gneiss interbedded with biotite
schist and gneiss crop out extensively in northwestern Wake County.
Foliation and bedding strike northeastward and at most places, dip to
the northwest.
Two northeast-trending zones of hornblende gneiss are interlayered
with rocks of the mica gneiss unit. A third unit underlies a small area in
southern Wake County. The gneiss is composed of hornblende and feldspar,
but also contains accessory amounts of quartz and mica. The two larger
units appear to be conformable with rocks of the mica gneiss unit, and
perhaps are metamorphosed mafic extrusives or sediments. The small horn-
blende gneiss unit is a coarse massive rock in which·gneissic texture is
poorly developed. It is not conformable with enclosing rocks and is most
likely a metamorphosed mafic intrusion.
Several elongated soapstone bodies crop.out in northwestern Wake
County. Typically the soapstone is a massive to schistose pale-green
rock composed of talc, chlorite, and several iron·and magnesium bearing
accessory minerals. Many of the bodies are aligned so that apparently
they are thicker masses of one continuous body. The suite of minerals in
the soapstone is common to ultramafic rocks that have been hydrothermally
altered.
A relatively narrow northeast-trending belt of metavolcanic rocks is
exposed in the western part of the county. These rocks have been metamorphosed
into low-rank phyllites, but fragments are discernible within some of the
rocks and on their weathered surfaces. The rock is a white to cream metatuff
in which quartz grains (beta quartz ? ) are· prevalent. Interlayer.ed with this
rock type are thin zones of green schistose rock which contain no.visible
primary features. All of the rocks have well developed cleavage which strikes
northeast and dips steeply northwest.
Green to light-tah phyllite crops out as a narrow tongue extending north-
ward from beneath Coastal Plain sediments in southern Wake County to near the
center of the county. Phyllite also underlies a small area in northeastern
Wake County. The rock is composed predominantly of fine sericite, chlorite,
and argillaceous material. Foliation is parallel to uniform color banding
which appears to be relict.bedding. Foliation and bedding strike northeast.
The thick mantle of soil which overlies the phyllite at most loca.lities
obscures the contact relationship between it and adjacent rocks. The
phyllite may be part of the Carolina Slate Belt of volcanic and sedimentary
rocks with which it has been previously mapped (N. C. State Geologic Map, 1958).
Medium~grained biotite granite, probably of Paleozoic age, underlies·most
of the eastern one-half of the county. It is part of a large granite pluton
that underlies most of Franklin County, and parts of adjacent counties which
are not included in the area of investigation. A smaller granite body is
exposed underlying Cretaceous sediments in southern Wake County. Typically,
the granite is light to pinkish gray, and is composed chiefly of orthoclase
feldspar, biotite, and quartz. Plagioclase feldspar is a common accessory
mineral. In Wake County the granite has intruded rocks of the mica gneiss
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GROUND WATER IN THE RALEIGH AREA
unit and many coarse-grained dikes associated with the granite extend into these rocks. Sheeting, joint fractures, and exfoliated granite boulders are common. A veneer of light-colored granular saprolite covers much of the area underlain by the granite.
A small body of crystalline rock which is composed predominantly of plagioclase feldspar, chloritized biotite, and quartz crops out in north-western Wake County. In composition, the rock is more closely related to the granodiorite which is exposed.north and northeast of the body than to the granite to the west.
Interbedded sandstone and shale of the Newark Group of Triassic sedi-mentary rocks underlie large areas in western Wake County. The beds occur within the Triassic Durham Basin and dip gently eastward toward the Jonesboro fault which forms the eastern boundary. A coarse fanglomerate composed of boulders, cobbles, pebbles, and angular rock fragments forms a belt along the eastern edge of the fault. Vertical displacement of the fault is at least the maximum thickness of the strata in the basin which was determined by Reinemund (1955, p. 27) to be approximately 10,000 feet. Many diabase dikes, probably of Late Triassic·age, have intruded the rocks. Near Bonsal in southwestern Wake County, a thin mantle of unconsolidated sands and clays of Cretaceous(?) age unconformably overlie Triassic rocks.
Coastal Plain strata unconformably overlie metamorphic and intruded rocks in southern Wake County. No fossils were found to occur in these unconsolidated sediments; they have been designated as part of the Tuscaloosa Formation of Cretaceous age on the basis of lithology and stratigraphic position with respect to sediments of known Cretaceous age outside of. the Raleigh area. The formation in Wake County is composed predominantly of gray to white sand, and interbedded lenticular lenses of clay. Quartz and concretions of iron oxide are common at the top of clay lenses·.
A mixture of shell fragments and sand occurs over a small area one mile north of highway U.S. 70 at the Wake-Johnston County line (oral communication, Dr. J.M. Parker, III, of the N. C. State College Geology Department). According to Richards (1950, p. 14), this outlying deposit is part of the Castle Hayne limestone of Eocene age.
GROUND WATER
Raleigh, Apex, and Wake Forest obtain their municipal water supplies from surface sources. Outside of these towns, all domestic and industrial water supplies are obtained from ground-water sources. Seven towns and several residential developments use wells as a chief source of water supplies.
Dug and bored wells are common sources of domestic supplies in the rural areas. Yields of 10 to 15 gpm can be obtained from the saprolite overlying granite or from the unconsolidated Coastal Plain sediments. The soil over-lying Triassic rocks generally will yield 3 to 5 gpm to dug or bored wells.
·COUNTY DESCRIPI'IONS"
Data on 286 wells in Wake County are given in table 27. Average yields,
depths, and other pertinent infonnation for 260 drilled wells are compared
below in table 26.
TL!ble 26. --Summary of data on wells in Wake County
Map
Unit
Hornblende
Gneiss
Number
of
wells
12
•Mica Gneiss SO*·
Phyllite 11
Meta-
volcanic
Sequence 23
Granite 77
Triassic
rocks ·57
All wells 260
Hill 55
Flat 129*·
Slope 49
Draw 27
*Includes one well
ACCORDJNG TO ROCK TYPE
Average
depth
(feet)
199
147
183
212
137
158
157
Yield (gpm)
Per foot
Range Average of well
1-50 17 0.09
.5-295 19 .13
4-2:'i 14 • 08
2.5-150 27 .13
0-82 20 .15
0-20 5 • 03
0-295 17 .11
ACCORDING TO TOPOGRAPHIC IDCATION
134 0-75 15 0.11
161 0-295 15 . 09
133 • 5-50 13 .10
223 1-150 36 .16
275 feet deep, tPsted , at 295 gpm.
Percent of
wells
yielding 1 gpm
or. less
8.3
6.2
0
0
2.6
16
6.5
9.1
7.7
2.0
3.7
According to table 26, the rocks of the metavolcanic unit, granite, and
rocks included in the mica gneiss unit·, in that order, are the best aquifers.
The average yield and yield per foot of well for wells in these rock types
in Wake County are considerably higher than the same averages for all wells
in these rock types in the area of investigation. This is because most
industries and municipalities which use ground water are located in Wake
County and most obtain their water from these rocks. ·Triassic ,ocks are
t.he poorest aquifers, having an average) yield of 5 gpm and an average yield.
per foot 6f we11· of 0.03 gpm. ·The relatively less permeable nature of the
Triassic rocks is shown by the large percentage (16 percent) of wells that
yield l gpm or less. Wells which yield 10 to 20 gpm are common in all of
the rocks in the county except the Triassic rocks. The reported yield of
several wells was greater than 50 gpm. However, in most instances the yield
was detennined by bailer tests of short duration and, consequently, may be
somewhat inaccurate. In general, wells penetrating granite or metamorphic
rocks will at most places yield adequate amounts of water for domestic use.
Where larger yields are desired, wells should be located where ground-water
conditions are most favorable. Visible features which indicate favorable
ground-water conditions include fracture zones, quartz veins, deeply weathered
areas, intruded dikes', and topographically low areas such as draws or depres-
sions. 'l'he best yielding wells in Triassic rocks are located near diabase' dikes.··
-101 -
I I' I
1
11
it
11.
'ii I I'
I
0 N
l!!!!!!!I
385
380
375
'.J en :,;; 370
A
M-10
378.94
T
SILT AM1 CLAY
w Jt£A THEREO SILTSTONE > 0 m 365 <
I-w w 360 !:
z 0 355 H I-< > w 350 _J w
345
340
M-10 -WELL DESIGNATION
378. 94 -ELEVATION . ,---
~ -h'ELL SCREEN
THJS CROSS SECTION 0£PICTS SWSI.IRFACE CCWOfTIONS AT LOCATialS SHOJt'N BASED ON SIT£ IMVESTifiATia-lS.
st.BStRFACE COMJITICWS AT OTJER LOCATI(N'IS HAY OIFrER
FRa'I CONDITitlVS OCCLRRIN6 AT THESE SITES.
M-7
374.25 · M-6
372.58
JfcATHERED SILTSTONE
HORIZONTAL SCALE
(FEET) ca
0 200
M-5
370.02 M-4 TT
20X VERTICAL EXAGGERATION
M-3
366.39
T
M-2
37.t.49
T
A'
385
380
375
'.J "' 370 :,;;
w > 0
365 m < SILT AND CLAY
KEATHERED
SILTSTONE
I-w
360 w !:
z
355 0 H I-< >
350 w _J w
345
340
FIGURE
GEOLOGIC CROSS SECTION A-A '
RALEIGH. NC
KOPPERS COHPANY. INC.
- - -
8-U
B 3B4.00
T 385
380
375 SILT AND CLAY
'.J en :,: 370 w > 0 m 365 <(
B-7 8-9
374. 00 374. 00 M-9
372.05 =11
KOO{]
CHIPS K001J
CHIPS
B-12~ 370. oo B-i5 T 368.00
SILT
AlVO
CLAY
~
,_ lt'EA 1rlER£lJ SIL TS TONE
w w 360 !=-
z 0 355 H ,_
<( > w 350 ...J w
345
340
•
NOTES
B-11 -Jr'ELL D€SI6NATION
384. 00 -ELEVATION r-~ -WELL SCREEN
THIS CROSS SECTitw 0£PICTS Sl.SSIIFACE ca,DITIONS AT LOCATIONS SHOKN BASED O"I SITE INVESTIGATIONS. SUBStRFACE COMJITIONS AT OTHER LOCATIONS NAY DIFFER
FRON Cfl,/OJTIONS occtRRING AT TIES£ SITES.
I!!!!!!! l!!!!!I m=
HORIZONTAL SCALE
{FEET)
~ 0 200
EOX VERTICAL EXAGGERATION
KEATHERED SILTSTONE
I
I
M-1
370.00
T
B'
385
380
375
370
365
360
355
350
345
340
FIGURE
'.J (/) :,:
w > 0, m
<( ,_
w w !=-
z 0 H ,_
<( > w ...J w
GEOLOGIC CROSS SECTION B-B'
RALEIGH. NC
KOPPERS COHPANY, INC. BS.J2.J5J
-
0
l!!!!!!!!I
o ..
11111
" " '--.. '\
l!!l!!I
c::::::::J
c::=::::J
c::::::J
PROPERTY BOUNDARY
/ I_ /IJ
·~~~~ .
• -,l_ 0 ._,,,-/
\ -9 q
' I / \>. ' f / ~-1
\
'✓-'3'.?,-, '-I -\ • ,, '-~,---' __ , I
h.'-!:)cAM-10 '\ . ,}'~ ~jl;,.,;,<~ --' ;,,
Y .a., ' ,, , " , v"-" y ' '_,, c do I ' " / ,1-D:',' / v-·'o,, \_.s,✓-----,, ,\ ,,~.,.--,, ,-----, ,_,,, ,, ,_.._
/ -' / , -/ / ' ,., y < " " , ,, M,
'It .,..-,\ '1 ,..,...,.., r ,,.---,, ,, / ,,--\\ \ -r:..";,
CEH£TARY~
aa liiiiil
~ '~v> \'-,.,..,...,,,
' '
-
+ I\
W-12 I\
-
!00
-
SCALE (FEEn
0 100 200 300
-- - - - -
0
FIGURE i
.LOCA lt'Ell
RALEIGH/:,~o;:lI;~llE.
KOPPERS COMP.I.NY l • "'·
- -
•
~
◊<?
~
l!!!!!!!I l!l!!!PJ
c:=i
[==:J
c=i
Q_
0 V() ,1
o ..
" " '\
l!l!l!!I lilliil
I :D: I ' I I -I
I I
L, i
I I
I ',
' I
liilil
SCALE (FEET)
100 0 100 200 300
- - - - -
c:J
·•-· •
CEHETAIIY~
--
LOCATION HAP
RALEIGH/MORRISVILLE.
KOPPERS COMPANY ' • INC.
- -- -
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FROM:
KE:
File
Pat DeRosa po
Koppers Co., lnc.
NC D00320U383
24 April l':187
I spoke by telephone with Ed Berry, Hydrogeology Regional
Supervisor, Raleigh Regional Office, Groundwater Section, NC Division of
Environmental Management (91~) 733-2314, regarding hydrogeologic conditions
within 3 miles of the subject site. Mr. Berry provided the following
information:
1. Depth to groundwater -The average depth to groundwater is
approximately 10-20' below land surface (bls) in the area of the
site.
2. Depth of residential wells -Bored wells have an average depth
of 30-35' and are 20-30" in diameter. These wells are generally
concrete pipe-cased and water enters through the joints in the
concrete. Drilled wells average approximately 150' deep. These
are generally steel-cased down to rock (approximately 20'-30')
and open-hole for the remainder of the well.
3. Continuous confining layers -There are no distinct confining
layers below the site which are continuous over a 3 mile
radius. The underlying Triassic sediments have relatively low
permeability except in those zones where diabase dikes and
fractures occur. Diabase dikes within 3 miles of the site
provide a hydraulic connection between the land surface and the
various water-bearing zones throughout the aquifer. Open-hole
wells and improperly filled abandoned well holes also connect
the water-bearing zones.
PJJ/tb/0374b
Ref. 22
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FROM:
RE:
File
Pat DeRosa If:>
Koppers Co, Inc.
NCD003200383
May 4, 1987
I spoke by telephone with Marty Schlesinger, Keystone Environmental
Resources, (KER) (412) 227-2690 regarding the subject site, Mr. Schlesinger
is Assistant Program Manager handling Koppers previously operated properties.
Mr. Schlesinger provided the following information:
1. Depth of casing for wells Wl-W8 -approximately 20 ft.
2 Volume of former lagoons -
50' X 50' X 2,5' = 6,250 cu. ft.
30' X 45' X 2,5' = 3,375 cu. ft.
Total = 9,625 cu. ft.
3. Containment-Lagoons were unlined with no diking, no diversion
system, and no leachate collection system.
4. Use-The total volume deposited is unknown, however, it is
estimated that the lagoons were filled at least one time.
PD/pw/0384b
Ref. 23
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FROM:
RE:
File
Pat DeRosa /?J)
Koppers Co., Inc.
NCD003200383
May 5, 1987
I spoke by telephone with Rick Jones, Water System Operator, Town of
Cary, (919) 469-4095, to confirm information from our earlier conversation
regarding Cary's water distribution system. Mr. Jones indicated that Cary
purchases approximately 3.5 mgpd from Raleigh and uses an additional 300,000
gpd from wells. Each well is chlorinated at the well head and treated water
is piped directly into the distribution system. A water line from Raleigh
runs through Cary to serve Morrisville. This water line continues up Hwy. 54
to Airport Blvd. out to RDU Airport. The water carried by this line does not
mix with well water entering the system in Cary.
PD/pw/0384b
Ref. 26
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April 30, 1987
TO: File
FROM: Pat DeRosa f[>
RE: Koppers Co,, Inc.
NCD 003200383
On April 14 and April 30, 1987, I spoke by telephone with Peter
Bine, Town Administrator, Town of Morrisville, (919) 469-1426, regarding the
source and extent of the Town of Morrisville water supply system. Mr. Bine
indicated that Morrisville purchases water from Raleigh which draws its raw
water from Falls Lake Reservoir, Water is piped from Raleigh through Cary
along Hwy. 54 to Morrisville. All residents within the town limits of
Morrisville have access to city water. North of Morrisville, the water line
continues up Highway 54 and turns onto Airport Road (SR 3015)* to RDU
Airport. Any homes along this line may access city water.
Morrisville's line has also been extended from Hwy. 54 to serve the
Belk's Warehouse on Church St. (SR 1637) and Adam's Concrete on Koppers Road.
This extension, however, does not serve any additional residences. The Mobile
City MHP off Hwy. 54 is also served.
*Note that SR 3015 and SR 1002 have exchanged names since the 1981
photorevision of the USGS 7,5' quads.
PD/pw/0384b
Ref. 28
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TO:
FROM:
RE:
File
Pat DeRosa ff)
Koppers Co., Inc.
NC D003200383
24 April 1987
I spoke by telephone with Mike Cable, Engineering Section, City of
Durham Wdter Supply (919) 683-4326 regarding the extent of water distribution
lines within 3 miles of the subject site. I described the area to Mr. Cable
and he said the only service in that area was on Old Raleigh Road to 1000 ft.
south of Hwy. 54. No lines branch off that road to serve adjoining areas.
The only other line from Durham goes to the RDU airport and has no residential
service.
PD/tb/0374b
Ref. 31
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FROM:
RE:
File
Pat DeRosa ~
Koppers Co. Inc.
NC DOO32OO383
14 April 1987
I spoke with Don Williams, Environmental Engineer, Water Supply
Branch, NC DHR, (919) 486-1191 regarding community water supply systems in
Wake County within 3 miles of the subject site. Mr. Williams confirmed that
Cary's water lines run through Morrisville to RDU Airport. Morrisville is
served by Raleigh through Cary. Mr. Williams said that the only other
community system within 3 miles is located at Howards Rest Home on SR 1624
approximately 3 miles west of Morrisville. This system uses groundwater from
wells which lie within 3 miles of the subject site. He indicated the location
of this system on the USGS quadrangle map.
PD/tb/O373b
Ref. 32
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TO:
FROM:
RE:
File
Pat DeRosa t{D
Koppers Co. Inc.
NC D003200383
14 April 1987
I spoke by telephone with Bob Hallisey, Environmental Engineering
Technician, Water Supply Branch, NC DHR, (919) 486-1191 regarding community
water supply systems in Durham County within 3 miles of the subject site.
Mr. Hallisey said that the only community system which might serve that area
is the City of Durham Water Supply. He suggested I contact Billy Walker, City
of Durham, Engineering Section, for additional information about the extent of
water distribution from Durham.
PD/tb/0373b
Ref. 33
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April 30, 1987
TO: File
FROM: Pat DeRosa
RE: Koppers Co., Inc. NCD003200383
I spoke by telephone with Mr. Troy Howard, owner of Howards Rest
Home near Carpenter, N.C., (919) 467-1610, to verify groundwater usage. He
said that the well currently used is 160' deep with 48' of galvanized steel
casing to rock. The well serves approximately 75 people. The well was
drilled by Acme Well Co. out of Durham, N.C., (919) 544-1940.
PD/pw/0384b
Ref. 34
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3 April 1987
TO: File
FROM: Pat DeRosa ~
RE: Koppers Co., Inc. NC D003200383
On March 19, 1987, a meeting was held to discuss the results of
groundwater water samples collected from off-site wells surrounding the
Koppers Co., Inc. site in 1-brrisville. A summary of these results and a list
of attendees at the meeting is attached. Due to conflicting data, it was
decided that the NC CERCLA Unit would resample the off-site wells previously
sampled, along with some additional wells. Samples would be split with
Koppers and the State's samples would be analyzed by the North Carolina State
Laboratory of Public Health.
Residents or representatives at the 10 previously sampled locations
were contacted by phone on March 19, 1987 to request permission to collect
additional well samples on March 20, 1987. Permission to collect samples was
obtained for all 10 wells, plus 1 new well, listed on the attached sheet.
Residents were notified that they would be contacted in 2 weeks with the
sample results.
On March 20, 1987, NC CERCLA Unit personnel Pat DeRosa and Mary
Giguere met with Marty Schlesinger, Keystone Environmental Resources and
Serraphino Franch, Wake County Health Department to conduct off-site well
sampling around the subject site. The 10 wells previously sampled were
res amp led along with the following 3 "new" wells:
Well No.
10
11
12
Name
Deli Box Restaurant
Watson Burroughs residence
L.A. Lyons
Person Contacted
Scott Beerman
Gladys Burroughs
Barbara Lyons
The locations of these additional wells are marked on the attached
map.
Samples were collected by the NC CERCLA Unit using containers
provided by the State Laboratory of Public Health. Wells were purged for
15 minutes except at the Crowe residence at the owners request. Four 40-ml
VOA bottles and 2 - 2 liter jars wrapped in foil were used to collect water
samples at each well. Samples were split with Koppers. All samples were kept
on ice in coolers until delivery to the labs. Koppers samples were delivered
to Compuchem in RTP for analysis. The State's samples were delivered to the
State Laboratory of Public Health for analysis.
PD/tb/0210b
Attachments (6)
Ref. 35
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19 March 1987
TO: File
FROM: Pat DeRosa ~.:)
RE: Koppers Co., Inc. NC D003200383
Residents or representatives at the following 11 homes or businesses
were contacted by phone to obtain permission to collect well samples on
March 20, 1987. Permission was granted.
Well No.
0
1
2
3
4
5
6
7
8
9
10
Name/Phone
Louis Barbee residence
(919) 467-8920
John Medlin residence
(919) 467-7621
George Harding residence
(919) 467-~ &''1'15
Mack Baker residence
(919) 467-8130
Roy Medlin residence
(919) 467-8437
Triangle Materials
(919) 469-2222
(919) 832-0594
Wilkerson Construction Co.
(919) 467-1829
James Crowe residence
(919) 467-8603
Shiloh Baptist Church
(919) 469-0790
(919) 544-4016
William Barbee residence
(919) 4&9 0790-"1, r-or,<,,
Deli Box Restaurant
(919) 467-4163
Person Contacted
Cheryl Barbee
John Medlin
George Harding
Mrs. Baker
Roy Medlin
Phil Ritchie,
Triangle Materials
Bob Ritchie,
Carolantac Realty
Dot Strickland
James Crowe
Nathanial Mayo
Mrs. Barbee
Scott Beerman
I PD/tb/0210b
I
Ref. 36
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TO: File
FROM: Pat DeRosa P't
RE: Koppers Co., Inc.
15 December 1986
I spoke by telephone with the following residents to obtain permission
to sample their wells. These residents or businesses use groundwater from
wells surrounding the subject site.
1. John Medlin residence -467-7621
Mrs. Medlin said she would be glad to have us sample her well
providing we would send her a copy of the results. The Medlin well
is located south of Koppers and serves 1 house and 2 trailers.
Mrs. Medlin said she would try to find out the total depth and
casing depth of the well.
2. George Harding residence -467-8445
Mr. Harding gave us his permission to sample the well at his home.
Mr. Harding's home is located at the end of Church Street,
southwest of the site. The total depth and depth of casing in the
well was unknown.
3. Mrs. Baker residence -Could not obtain phone number.
4. Roy Medlin residence -Could not obtain phone number.
5. Triangle Materials -469-2222
This business rents the property from Carolantac Realty, 832-0594.
The receptionist at Triangle Materials indicated that some
employees there do use the well water for drinking. They also have
bottled water available. Mr. Bob Ritchie at Carolantac Realty gave
us his permission to sample the well at Triangle Materials.
Mr. Ritchie did not know the depth of the well, however, he
suggested I call Reliable Pump Co. (266-5792) since they had
recently worked on the pump. Reliable did not know the well depth
but estimated it to be at least 220 ft. The well is southeast of
the site along Hwy. 54.
6. Wilkerson Construction -467-1829
I spoke with Joe Wilkerson concerning the use of well water at his
facility. He said that well water was used for washing equipment
and flushing toilets at Wilkerson, however, it was not used for
drinking. He estimated the well on site to be 400-450 ft. deep
with a 2,000 gallon storage tank. He said the well pumps about
1/2 gallon per minute and is cased down to 20-30 ft. Currently,
however, the pump is broken and therefore we could not sample the
well at this time. The well is east of Koppers just across from
Hwy. 54.
Ref. 37
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7. James Crowe residence -467-8603
Mrs. Crowe gave us permission to sample the well at her residence
on Hwy. 54, east of Koppers. She estimated that the well was
180-200 ft. deep but said it was a "weak" well. She asked that we
not purge her well for fear that it would run dry.
8. Shiloh Church -Did not contact.
9. William Barbee residence -467-0876
Mr. Barbee gave us permission to sample the well at his home. He
estimated that the well was approximately 100 ft. deep and cased
down to 25-30 ft. Mr. Barbee's well is located northwest of
Koppers on Church Street.
I PD/tb/0323b
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FROM:
RE:
File
fut~sa~
Koppers Co., Inc.
NC DOO32OO383
5 December 1986
I spoke with William Paige and Gary Babb (NC RCRA Unit) about the current status of this site. They have received no further information beyond the renotification filed by Koppers in February 1986.
I spoke by telephone with Charlie Beck, former plant manager at Kopper's Morrisville (919) 467-6151. Mr. Beck indicated that Koppers sold part of the property to Unit Structures, Inc. (as of September 5, 1986) for whom Mr. Beck now works. The part of the site where the treatment and contamination occurred is still owned by Koppers Co., Inc. To the best of his knowledge, Mr. Beck indicated that Koppers had removed contaminated soil from the site and shipped it to SCA in July-August 1986. He did not know whether post-cleanup soil and well sampling had been conducted. He said that city water was not yet available at the site and he believed neighboring residents were still on wells. Unit Structures is still using the old Koppers wells for process water and toilets. However, bottled drinking water is brought in. Mr. Beck suggested I contact Mike Dvorsky (412) 227-2684 or David Kerschner (412) 227-2677 at Kopper's Pittsburgh, PA office for further information.
PD/tb/O176b
Ref. 39
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FROM:
RE:
File
Pat DeRosa@
Koppers Co., Inc.
NC D003200383
May 6, 1987
On April 28, 1987, I spoke by telephone with Bob Stewart, Plant
Manager, Unit Structures in Morrisville, NC (919) 467-6151 regarding the
subject site. Unit Structures operates the old Koppers plant and Mr. Stewart
recently replaced Charlie Beck as plant manager. Mr. Stewart has worked at
the site since the 1960's. Of the entire 52 acre property, Koppers retained
10 acres and sold the rest to Unit Structures in September 1986.
The Koppers pond is currently hooked up to supply the hydrant and
sprinkler system for fire protection at Unit Structures. It has no
recreational or process water uses. The pond is approximately 3 to 4 acres in
size and 6-7' deep in the middle. It was originally a low area which was
dammed on the southeast side to form a pond. The overflow outlet in the
southwest corner of the pond empties to a ditch which flows south under
Koppers' road (SR 1635) to the John Medlin property. Flow from the pond is
non-continuous.
Bottled water is currently used for drinking water at Unit
Structures. Well #1, near the main office, supplies water for toilets and
non-drinking usage. Well #2, northwest of the old laminating plant is used in
the manufacturing process and for plant toilets.
On May 6, 1987, I spoke with Mr. Stewart again to verify ownership
history of the site. Mr. Stewart said that Unit Structures originally
purchased the site from Cary Lumber Co. in 1959. Cary Lumber operated a
sawmill on site. Unit Structures operated the sawmill and glue-laminating
process on site from approximately 1959-1962. The property was sold to
Koppers in 1962.
PD/tb/0374b
Unit Structures, Inc.
P.O. Box 23215
1413 Evergreen Rd.
Louisville, KY. 40223
Ref. 40
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TO:
FROM:
RE:
File
Pat DeRosa f){J)
Koppers Co., Inc.
NCD 003200383
May 1, 1987
On April 30, 1987, I spoke by telephone with Victor Lynn, County
Extension Chairman, Wake County Agricultural Extension Service (919) 755-6100,
regarding irrigation within 3 miles of the subject site. Mr. Lynn said he was
not aware of any irrigation wells in Wake County. He was also not aware of
any irrigation from Crabtree Creek between Morrisville and Umstead Park.
On May 1, 1987, I spoke by telephone with Toby Bost, Agricultural
Extension Agent, Durham County (919) 688-2240 regarding irrigation wells
within 3 miles of the site in Durham County. Mr. Bost said that irrigation in
that area is generally from ponds. He was not aware of any groundwater use
for irrigation.
PD/pw/0384b
Ref. 41
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April 29, 1987
TO: File
FROM: Pat DeRosa fJ>
RE: Koppers Co., Inc.
NCD003200383
I met with David Hedberg, Statistical Research Analyst, Wake County
Planning Department (919) 755-6047, to determine whether a significant
increase in population within 3 miles of the subject site had occurred since
1981. Population data from the Wake County Tax Department Real Estate File,
updated January 20, 1987, was used. A circle representing a 3 mile radius
around the site was overlain on the Wake County property maps. The total
number of residential units within property maps intersected by the 3 mile
radius were summed. Units within incorporated areas served by municipal water
system were subtracted. The remaining number of units was determined to be
535. By multiplying 535 units x 3.8 persons/unit, the total population using
groundwater was estimated at 2,033.
PD/pw/0384b
Ref. 42
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TO:
FROM:
RE:
File
Pat DeRosa J>b
Koppers Co., Inc.
NCD 003200383
April 30, 1987
I spoke by telephone with Mrs. John Medlin regarding usage of the
Medlin pond, (919) 467-7621. She said that her pond receives seasonal,
non-continuous overflow from Koppers pond. Overflow from the Medlin pond is
also non-continuous, occurring only in the winter months. The Medlins fish
from the pond and also use the pond to irrigate a 2 acre field and garden
space in the summer months.
PD/pw/0384b
Ref. 43
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TO:
FROM:
RE:
File
Pat DeRosa f>j)
Koppers Co, Inc.
NCD003200383
May 1, 1987
I spoke with Dick Caspar, Water Supply Branch, NC DHR, (919)
733-2321, regarding water supply intakes on Crabtree Creek. He said there
were no intakes along Crabtree Creek downstream of Morrisville, The nearest
downstream intake is on the Neuse River more than 40 miles southeast of
Morrisville. This intake serves the City of Smithfield in Johnston County,
N.C.
PD/pw/0384b
Ref. 44
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Ms. Pat Derosa
United States Departlnent of the Interior
FISH AND WILDLIFE SERVICE
ENDANGERED SPECIES FIELD STATION
100 OTIS STREET, ROml 224
ASHEVILLE, NORTH CAROLINA 28801
June 21, 1985
Solid and Hazardous Waste Management Branch Environmental Health Section
North Carolina Department of Human Resources P. 0. Box 2091
Raleigh, North Carolina 27602
Dear Ms. Derosa,
Ref. 45
In response to your telephone conversation with John Fridell on May 30, 1985, we are enclosing the following items of information:
A.
B.
c.
D.
North Carolina county distribution records of Federally listed; proposed and status review species,
map of the critical habitat of the threatened spotfin chub (Hybopsis monacha),
map of the critical habitat of mountain golden heather (Hudsonia montana), and
copy of the U.S. Fish and Wildlife Service interagency Section 7 consultation process guidelines (included for your information)
0
The abbreviations following the species names on the North Carolina species distribution records (A. above) indicate Federal status, i.e., E -endangered, T -threatened, PE -proposed endangered, PT·-proposed threatened and SR -under status review. Status review species are not legally protected under the Endangered Species Act. However, they are subject to being listed and agencies should be cognizant of their potential presence in a project area.
Since additions and deletions are made to the list of species on a regular basis, questions regarding updates of the list should be made to this office.
We hope this information will be of use to you. If we can be of any further assistance,• please call John Fridell or Nora Murdock at (704) 259-0321.
Sincerely yours,
\ \ , ;'\ C), (\ . v-ulttl ... \ . \~
Warren T. Parker
Field Supervisor
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5/78
NORI'H CAroLINA -Critical Habitat
Hyl:xlpsis nonacha, "spotfin chub"
1-'a=n and swain Counties. Little Tennessee River, lll3.in channel fran
the backwaters of Fontana Lake upstream to the North Carolina-{;eorgia
state line.
"' S• a\n C"· -----=-M;:;c;.-
Frank Ii o ✓,
C:lal Co. ?_ .....__ '1arun Lu.
______ : \ ~ Rabun Co.
Townt1 t:o.
>;ORTH CAROLl:-A ------------GEORGIA
' ,,.---
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NORTH CAROLINA -Critical Habitat
Hudsonia montana, "mountain golden heather"
Burke County. The area bourded by the following: on the west by the 2200' contour; on the east by the Linville Gorge Wilderness Boundary
11/80
north from the intersection of the 2200' contour and the Shortoff Mountain Trail to where it intersects the 3400' contour at "The Chimneys"--then follow the 3400' contour north until it reintersects the Wilderness Bourdary--then follow the Wilderness Boundary again northward until it intersects the 3200' contour extending west from its intersection with the Wilderness Boundary until it begins ta turn south--at this point the Boundary exterds due east until it intersects the 2200' contour.
•• M,IH to /: ~--··
'. -~
PISGAH
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Spotfin Chub
--
Mountain Golden
Heather
1 inch= approx. 53 miles
-- -- --- --·-CRITICAL HABITATS OF FEDERALLY LISTED
ENDANGERED SPECIES ·rN NC
SURRY STOKES ROCKING•
H•M
ADKIN ORS_YtH GUllfOAD
KOPPERS CO., INC.
NC D003200383
---
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12 August 1986
TO: CERCLA Unit Staff
FROM: Pat DeRosa ~
RE: Critical Habitats of Federally Listed Endangered Species in N.C.
I spoke by telephone today with John Fridell, US Fish and Wildlife
Service (704) 259-0321 to request an update on critical habitats in NC.
Mr. Fridell informed me that the only change since our previous correspondence
of June 21, 1985 has been a "Proposal to List the Cape Fear Shiner as an
Endangered Species with Critical Habitats" in NC: (FR Vol. 51, No. 133,
July 11, 1986). A copy of the proposed rule is attached for your information.
PD/tb/022lb
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Federal Register / Vol. 51, No. 133 / Friday, July 11, 1986 / Proposed Rules 25219
c-
R m c~ X 100 F.q. !SA-A
7. Bibliography
1. American Society for Testing and
Materials. Annual Book of ASTM Standards.
Part 31: Water, Atmospheric Analysis.
Philadcphia, Pennsylvania. 1974. p. 4~Z.
2. Blosser, R.0., H.S. Oglesby, and A.K.
Jain. A study of Alternate S02 Scrubber
Designs Used for TRS Monitoring. National
Council of the Paper Industry for Air and
Stream Improvement, Inc., New York, New
York. Special Report 77--05. July 1977.
3. Curtis, F .. and C.D. McAlister.
De\·elopment and Evaluation of an ·
Oxidation/Method 6 TRS Emission Sampling
Procedure. Emission Measurement Branch,
Emission Standards and Engineering
Division, U.S. Environmental Protection
Agency, Research Triangle Park, North
Carolina·21n1. February 1980.
4. Gellman, I. A Laboratory and Field Study
of Reduced Sulfur Sampling and Monitoring
Systems. National Council of the Paper
lndustry for Air and Stream Improvement,
Inc., New York, New York. Atmospheric
Quality Improvement Technical Bulletin No.
81. October 1975.
5. Margeson. J.H .. J.E. Knoll. M.R. Midget~
D.B. Ferguson, and P.J. Schworer. A Manual
Method for TRS Determination. Jownal of Air
Pollution Control AssociatiOn. 35:1280-1286:
December 1965.
[FR Doc. 86-15268 Filed 7-10-IIB; 8:45 am]
BIL.UNG CODE 65&0-50-11
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
Endangered and Threatened Wildlife ·
and Plants; Proposal to List the Cape
Fear Shiner as an Endangered Species ·
with Critical Habitat
AGENCY: Fish and Wildlife Service.
Interior.
ACTION: Proposed rule.
SUMMARY: The Service proposes to list
the Cape Fear shiner (Notropis
mekistocholas) as an endangered
species with critical habitat m1der the
Endangered Species Act of 1973, as.
amended. This fish has recently ·
undergone a reduction in range and
population. It is currently known from ·
only three small populations in the Cape
Fear River drainage in Randolph. Moore,
Lee, and Chatham Counties. North
Carolina. Due to the species' limited
distribution, any factor that degrades
habitat or water qua!ity in the short
river reaches it inhabits-e.g .• land use
changes, chemical spills, wastewater
discharges, impoundments, changes in
stream flow, or increases in agricultural
~unoff-could threaten the species'
survivial. Comments and information
pertaining to this proposal are sought
from the public.·
DATES: Comments from all interested
parties must be received by September
9, 1986. Public hearing requests must be
received by August 25. 1986.
ADDRESSES:.Comments and materials
concerning this proposal should be sent
.to Field Supervisor, Endangered Species
Field Office, U.S. Fish and Wildlife
Service, 100 Olis Street Room 224.
Asheville, North Carolina 28801 ..
Comments and materials receiv·ed will
be available for public inspection, by
appointment, during normal business
hours at the above address.
FOR FURTHER INFORMATION CONTACT:
Richard G. Biggins, at the above address
(704/259--0321 or.ITS 672--0321).
SUPPLEMENTARY INFORMATION:
Background
The Cape Fear shiner (Noropis
mekistocholas), the only endemic fish
known from North Carolina's Cape Fear
River drainage, was discovered in 1962
and described by Snelsori (1971). This ·
fish has been collected from nine stream
reaches in North Carolina (Bear Creek.
Rocky River, and Robeson Creek,
Chatham County; Fork Creek. Randolph
County; Deep River, Moore and
Randolph Counties: Deep River, ·
Chatham and Lee Counties; and Cape
Fear River, Kenneth Creek, and Parkers
Creek, Harnett County (Snelson 1971, .
W. Palmer and A. Braswell, North
Carolina State Museum of Natural
HistOry, personBi' Comnu.inication' igss;·
Pattern and Huish 1985, 1986). Based on
a recently completed Service-funded
· study (Pattern and Huish 1965, 1986)
involving extensive surveys in the Cape
Fear River Basin (including all historic
sites) and a review of hisiorical fish
collection records from the Cape Fear,
Neuse, and Yadkin River systems, the
fish ls now restricted to only three
populations. The strongest population
(101 individuals collected in 1984 and·
1985) ls located around the junction of
the Rocky River and Deep River in
Chatham and Lee Counties where the
fish inhabits the Deep River from the
upstream limits of the backwaters of
Locks ville Dam upstream to the Rocky
River then uJ)stream from the Rocky
River to Bear Creek and upstream from
Bear Creek to the Chatham County Road
2156 Bridge. A few individuals were
collected just downstream of the
Locksville Dam. but because of the
limited extent of Cape Fear shiner
habitat at this site, it is not believed this
is a separate population. Instead, it is
thought these fish represent a small
number of individuals that periodically.
drop down From the popul_ation abov~
Locksville Dam pool.
The second population, represented
by the collection of a specimen near
State Highway Bridge 902 in Chatham
County, is located above the Rocky
River Hydroelectric Dam. This
popula lion was historically the best. but
the area yielded onIY the one specimen
after extensive surveys by Pattern.and
Huish (1985). The third population was
found in the Deep River system in
Randolph and Moore Counties. This.
population is believed lo be small
(Pattern and Huish 1985, .1986). Three
individuals were found above the ·
Highfalls Hydroelectric Reservoir; one
in Fork Creek, Randolph County, and.
two in the Deep River, Moore County. .
The species was also found downstream
of the highfalls Dam. However, the .
extent of suitable habitat in this stream
reach is limited, and ii is thought that· .. ·
these individuals likely result from ..
downstream movement from above the
reservoir where Cape Fear shiner
habitat is more _extensiv.e~ ,· · .·_ ., .
The Caper Fear shiner is smaU.-rarely ·.
. exceeding z inches in length. The fish's
.body is flushed with a pale silvery .. ··.
yellow, and a black band.runs along its
sides (Snelson 1971). The fins are
yellowish. and somewhat pointed. The:,: ·
upper lip is black. and .the lower lip .· ·
bears a thin black bar along its.margin,
The. Cape Fear shiner, lll)like .most other •
members of the large· g_enlls tJo}rofais~ ,·. ·· ....
feeds extensiv~ly_in plallt m<1:teriel, an~ '·. ·. ·-.' :
its digestive tract is mo9,ified for this .. :i : ·· ·· .. ._ .. ·
diet by having ail elongated, convoluted·
. intestine. The species is generally
associated with gravel, cobble, and
boulder substates and has been
observed to inhabit slow pools, riffles;
and slow runs (Snelson 1971, Pattern·
and Huish 1985). In these habitats, the
species is typically associated with
schools of other related species, but it is
never the numerically domin!lnt .species.
Juveniles are orten found in slackwater,
among large rock outcrops in mid-
stream, and in flooded side channels ..
and pools (Pattern and Huish 1985). No
information is presently available on
breeding behavior, fei::undity, or
longevity.
The Cape Fear shiner may always
have existed in low numbers. However,
its recent reduction in range and its
small population size (Pattern and Huish
1985, 1986) increases the species'
vulnerability to a catastrophic event,
such as a toxic chemical spill. Dam
construction in the Cape Fear system
has probably had the most serious
impact on the species by inundating the
species' rocky riverine habitat. Dams
25220 Federal Register / Vol. 51, No. 133 / Friday. July 11, 1986 / Proposed Rules
presently under study by the U.S.
Department of the Army, Corps of
Engineers (COE), for the Deep River and changes in flow regulation at existi!lg
hydroelectic facilities could further threaten the species. The deterioration
of waler quality has likely been another factor in the species' decline. The North
_Carolina Department of Natural
Resources and Community Development (1983) classified waler quality in the Deep River, Rocky River, and Bear
Creek as good to fair, and referred to the Rocky river below Siler City as an area where their sampling indicates
degradation. That report also stated: "Within the Cape Fear Basin, estimated average ann·ual soil losses from
cropland ranged from 3 tons per acre in the lower basin lo 12 tons in the
headwaters." The North Carolina Slate
Division of Soil and \\' ater Conservation
· c0nsiders 5 tons of soil loss per acre as the maximum allowable. . . . The Cape Fear shiner was one of 29. ·
fish species included in a March 18, 1975, Notice of Re,iew published by the Service in the Federal Register (40 FR 12297). On December 30, 1982, the · Service announced in the Federal···
Register (47 FR 58454) tbat tbe Cape . · Fear shiner, along witb 147 other fish specieS,'WSS being considered for.":
possible addition to tbe list of Endangered and Threatened Wildlife. On April 4, 1985, the Service notified
Federal, Sta_te, and local governmental
agencies 8.nd interested parties that the Asheville Endangered Species Field Station Was reviewing the species'·
status. That notification requested · -infonnation ori the species' status·and · threats to its continued existence.
Twelve responses to the April 4, 1985,
notification were received. The COE, Wilmington Distric~ North Carolina
Division of Parks and recreation, · Natural Heritage Program: and the North Carolina State Museum of Natrual" · ·.-History provided for tbe species.
. Concern for the species' welfare w"a.s
-.also expressed by private individuals: : The other respondents provided no information on threats, and did not take a position on the soecies' status. The Cape Fear shiner Was included in the · Services' September 18, 1985, Notice of re,iew of Vertebrate Wildlife (50 FR
37958} as a category 1 species, indicating that the Service had substantial
biological data to support a proposal to list the species as endangered or threatened. ·
Summary of FaCtors Affecting the Species :
Section 4(a)(l) of the Endangered
Species Act (16 U.S.C. 1531 et seq.) and regulations (50 CFR Part 42-1)
promulgated lo implement the listing provisions of the Act set forth the
procedures for adding species to the Federal Lists. A species may be
determined to be an endangered or
threatened species due to one or more of
the five factors described in section 4{a)[l)c These factors and their
application to the Cape Fear shiner
(Notropis mekistocho/as) are as foilows:
A. The present or threatened
destructioil,· mod1fication, or. curtailment
of its habitat or range. A review of
historic collection records (Snelson 1971,
W, Palmer and A. Braswell personal communication 1985), along with recent survey results (Pattern and Huish 1985, 1986), indicates that the Cape Fear
shiner is presently restricted to only three populations (see "Background"
section). Three historic populations have
apparently been extirpated (Pattern and Huish 1985, 1986). Robeson Creek,
Chatham County, was believed lost when Jordan Lake flooded part of the creek. The reasons· for the loss of ·
populations from Parkers Creek and·
Kenneth Creek in Harnett County are
not known. The shiner has also not been rcc.ollected (Pattern and Huish 1985) from ihC Cape Fear. River· in Harnett · County. ·However, review of historical -and current collection reCords i-evCals· · that only· One specimen ha·s ev€r been : collected from Ibis river, and tbe fish likely was a stray individual from an . upstreain or tributary population. Since · much of the Deep, Haw. and Cape Fear
Rivers and their major tributaries has been impounded for hydroelectric .. power: and much o(tbe rocky sho~l habitat inundated, other populations
and populatio·n segments that were
never di~covered pave likelY been lost to. these reservoirs .. ·
·_ Of the three remaining populations,
only the one located around the · confluence of the Deep and Rocky Rivers in Chatham and Lee Counties
(inhabiting a total of about 7.3 river -miles).appears strong (Pattern and-Huish 1985). The second population in the Rocky River. above tbe Rocky River hydroelectric facility, was !he source of tbe type specimens used to describe the species (Snelson 1971). Historic records (W. Palmer and A. Braswell. personal
communication 1985} reveal that
collections of 15 to 30 specimens could be expected in this stretch of the Rocky River (Slate Roule 902 or Chatham
County Road 1010 Bridge) during a sampling visit in the late 1960s ar:.d early 1970s. Pattern and Huish (1985) sampled the Rocky River throughout this reach on numerous occasions and were able to collect only one specimen." The reason for the apparent decline in this
population is unknown. The third population, localed in the Deep Rh·e; system in Moore a·nd Rundolph
Counties, is represented by the
collection of six individuals (Pattern nnd
Huish 1986). Three in<li\'iduals were
taken from below tr.e dam. As the
available habitat below the dam is·
limited. it is believed these fish Ore mig:-ants from the upstream population.
• Potential threats to· the species and its habitat could come from such activities as road construction, stream cha.noel · · modification, changes in stream flows for hydroelectric power,'impoundments,
land use changes, wastewater
discharges, and other projects_ it1.the
watershed if such 8.ctivities ·are not ·
planned and implement wi".h the
survival of the species and the protection of its habitat in mind. The . species is also potentially threatened by two U.S. Army Corps of Engineers.
projects presently under rCview for the Deep River. The Randleman Dam · project would consist Of a resef1{oir 9f . tbe Deep Rh-er in Randolph County, · above known·cape Fesl" shiner" h3_bitat.·
The Howards Mill Reservoir would be on the Deep River in Moore' ilnd
Randolph Couniies and would flood presently use_d Cape Fear shiner habitat. B. O'Veru/i/ization for comm.el"Cia/,
, recreatlonc/, ::ci!:1r.tific, or educDlionQJ
purp0ses. Most of the pi-esCnt rarlge· of ... · the Cape Fear shiner is ·relatively
inaccessible and overutilization_of the . species has not been and is not .
expected.to be a problem. . , ... ,
C. Disease or predation. Although tlie
Cape Fear shiner is undoubtedly
consumed by predatory animals, there is no evidence that th~s predation is a: · threat to the species.
D. The inadequacy of existing
regulatory mechanisms. No;th Carolina
Stale law (Subsection 11:,...272.4)
prohibits collecting wildlife and fish for scientific Purposes without a State permit. However. this State law does no·r • protect the species' habitat from .the
potential impacts of Federal actions.
Federal listing will pro\·ide protection for the spedes under the Endangered
Species Act by requirir.g a Federal permit to take the species and requiring Federal agencies to consult with the Ser\'ice when p:ojects they fund, authcrize, or carry out may affect the
species.
E. Other natural or mar.made factors
affecting its conlinL·ed existence. The major portion of the best Cape Fear
shiner population is located at the
juncticn of the Deep and Rocky Rivers
in Chatham and Lee Counties. A mnjor
toxic chemical spill at the U.S. Highv:ay
15-105 Bridge upstream of this site on
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Federal Register / Vol. 51, No. 13~ ·, Friday, July 11, 1986 / Proposei R'ules 25221
the Rocky Ri\'er could jeopardize this
population, and as the other populations
are extremely small and tenuous, the species' ·survival could be threatened.
The Service has carefully assessed the best scientific and commercial
information available regarding the past.
present, and future threats laced by this species in determining to propose this rule. Based on this evaluation, the preferred action is to list the Cape Fear shiner (Notropis mekistocho/as) as an
endangered species. Because of the
species' restricted range and vulnerability of these isolated
populations to a single catastrophic
accident. threatened status does not
appear to be appropriate for this species
{see "Critical Habitat" section for a discussion of why critical habitat is being proposed for the Cape Fear
. shiner). ·
Critical Habitat
Critical habita~ as defined by section 3 of the Act means: (i) The specific areas within the geographical area occupied ·
by a species, at the time it is listed in
8.ccordance with the Act, on which are found those physical or biological
features (I) essential to the conservation·
of the species and (II} that may require
special management considerations or
protection, and (ii) specific areas outside the geographical area occupied by a species at the time it is listed, upon a
determination that such areas are essential for the conservation of the' species. . . .
Section 4(a)(3} of the Act requires that
critical habitat be designated to the · maximum extent prudent and
determinable concurrently ·with the
determination that a species is
endangered or threatened. Critical
habitat is being proposed for the Cape Fear shiner to include: (1)
Approximately 5 miles of-the Rocky
River in Chatham County, North . Carolina: (2) approximately 8 miles of Bear Creek, Rocky River, and Deep
River in Chatham and Lee Counties,
North Carolina; (3) approximately 8
miles of Fork Creek and Deep River in Randolph and Moore Counties, North Carolina.
(See "Regulation Promulgation"
section for this proposed rule for the
precise description of critical habitat.) These stream sections contain gravel,
cobble, and boulder substrates with
pools, riffles, and shallow runs for adult
fish and slackwater are.is with large
rnck outcrops and side channels and
pools for juveniles. These areas also provide water of good quality with
1;~Jr.tively low silt loads.
Section 4(b}(8) requires, for any
pruposcd or final regulation that
designates critical habitat, a brief
description and evaluatioil of those
activities (public or private) that may.
adversely modify such habitat or may be affected by such designation.
Activities which presently occur within the designated critical habitat include,
in part, fishing, boating, ·scientific
research, and nature study. These
activities, at their present use level. do not appear to be adversely impacting
the area.
There are also Federal activities that
do or could occur within the Deep River Basin and that may be affected by
protection of critical habitat. These
activities include~ construction of
impoundments (in particular, U.S. Anny Corps of Engineers reservoirs under study for the upper Deep River}, stream
alterations, bridge and road. ·
construction, and discharges of
municipal and industrial wastes, and hydroelectric facilities. These activities could, if not.carried out with the protection of the species in mind,
degrade the water and substrate quality
of the Deep River, Rocky River, Bear
Creek, and Fork Creek by increasing siltation, water temperatures, organic pollutants, and extremes in water flow. If any of these activities may affect the
critical habitat area and are the result of
a Federal action, section 7(a)(2) of the Act, as amended, requires the agency to consult with the Service to ensure that actions they authorize, fund, or_ carry · out, are not likely to destroy or .
adversely modify critical habitat. · . Section 4(b)(2) of the Act requires the Service tO consider e·conomic and othe·r
impacts of designating a particular area
as critical habitat. The Service will consider the critical habitat designation
in light of all additional relevant
information obtained at the time of final rule,
Available to Conservation Measures
Conservation measures provided to species listed as endangered or
threatened under the Endangered
Species Act include recognition,
recovery actions, requirements for Federal protection, and prohibitions
against certain practices. Recognition
through listing encourages and results ln conservation actions by Federal, State, and private agencies, groups, and
individuals. The Endangered Species
Act provides for possible land
acquisition and cooperation with the States and requires that recovery
actions be carried out for all listed
species; Such actions are initiated by-the
Service following listing. The protection
required of FederaJ agencies and the.
prohibitions against takillg and harm are
discussed, in part, below.
Section 7(a} of the Act, as amended,
requires Federal'agencies to evaluate·
their actions with respect to· aily species that is propOsed or listed as endangered
or threatened and with respect to it critical habitat, if ariy is being proposed
or designa_ted. Regulations i_mplementing
this intcragency cooperation provision of the Act are codified at 50 CFR Part 402 (see revision al 51 FR 19926: June 3, 1986). Section 7(a}(4) requires Federal
agencies to confer informally with the Service on any action that is likely to jeopardize the continued existence of a proposed species or result in the
destruction or adverse modification of
proposed critical habitat. If a species is
subsequently listed, section 7{a}(2} ·
requires Federal agencies to ensure that activities they 8uthorize, fund. or carry out are not likely to jeopardize the · •. continued existence of such a species or to destroy or adversely modify its
critical habitat U a Federal action may
affect a listed species or its critical
habitat, the responsible Federal agency
must enter into consultation with the
Service. The Service is presently aware
of only two Federal actions under consideration (Randleman and How8rds Mill Reservoirs} that may affect the · species and the proposed critical . habitat The Service has been in contact--with the U.S. Anny Corps of Engineers
concerning the potential impacts of, , . .-. these projects on ·the species ·and its : :"':· ·
habltat. The Act.arid implementing ·' :'° ·· ..
regulations found at 50 CFR 17.21 set· forth 8 serieS ·of gen_er.il prohibitions· and·~:._·: .. exceptions that apply to alle_ndaI1gei-ed · .
wildlife. These prohibit[ons, in part, :, ... . make it illegal ·for any person subjeci· to
the jurisdiction of the United Stales to
take, import Or export. s~ip in interstate ... . · commerce in.the' course of c·omm.ercial :. ·
activity, or sell or offer for sale In
interstate or foreign commerce any
listed species. It also is illegal to . prossess, sell, deliver, c8.rry, transpOrt,
or ship any such wildlife that has been
taken illegally. Certain exceptions . · ·
would apply to agents of the Service and
State conservation agencies.
Permits may be issued to carry out
otherwise prohibited activities involving
endangered wildlife species under
certain circumstances.· Regulations
governing permits are at SO CFR 17.22 and 17.23. Such permits are available for scientific purposes, to enhance the
propagation or survival of the species,
and/or for incidental take in connection
with otherwise lawful acti\•ities. In some
instances, permits may be issued during
a specified period of time to relieve
undue economic ~ardship that would be
suffered if such relief were not available.
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25222 Federal Register / Vol. 51, No. 133 / Friday, July 11, 1986 / Proposed Rules
Public Comments Solicited
The Service intends that any final
action from this proposal will be as
accurate and as effective as possible.
Therefore, any comments or suggestions
from-the public, other concerned
governmental agencies, the scientific
community, industry,_or any other
interested party concerning any aspect
of this proposal are hereby solicited.
Comments particularly are sollght
concerning: ·
(1) Biological, commercial trade, or
other relevant data concerning any
threat (or lack thereof) to this species;
(2) The location of any additional
populations of this species and the
reasons why any habitat should or
should not be determined to be critical
habitat as provided by section 4 of the Act· .
(j) Additional information·~oncerning
the range and distribution of this
species; ·
(4) current or planned activities in the
subject area and their .possible impacts
on this species; and
(5) Any foreseeable economic-and ·
. other impacts resulting from the.
. proposed designation.of critical habital
Final promulgation of the regulations
on this species will take into -· .. ,: .
· coll.sideration the comments and any -· .
additional information receiVed by the •
Service, and ·s_uch Communications may ..
lead to adoption of a finalregulation · ·
that differs from.,this proposal.
Sciootffic name
The Endangered Species Act provides
for a public hearing on this proposal, if
requested. Requests must be filed within
45 days of the dale of the proposal. Such
requests must be made in writing and
addressed to the Endangered Species
Field Office, 100 Otis Street. Room 224,
· Asheville. North Carolina 28801.
National Environmental Policy Act
The Fish and Wildlife Service has
determined that an Environmental
Assessment. as defined under the
authority of the National Environmental
Policy Act of 1969, need not be prepared
in connection with regulatiOns adopted
pursuant to section 4(a) of the
Endangered Species Act of 1973, as
amended. A notice outlining the
Service's reasons for this dcterminatiori
was published in the Federal Register on
October 25, 1983 (48 FR 49244).
References Cited
North Carolina Department of Natural
Resources and Commuµity oevelopment.
1983. Status of Water Resources in the
Cape Fear River Basin. 135 pp.
Pattern, G.B., and M.T. Huish. 1985. Status
sllrVey of the Cape Fear shiner {Notropis ...
mekistocho/as). U.S. Fish and Wi,ldlife_ .
Service Contract No. 14-16-0009-1522._'44 ·
pp.
Potterri. G.B .• and M.T. Huish. 1986.
Supplement to the status survey of the ·
Cape Fear.shiner {Notropis mekistoCho!aS}.
U.S. Fish and Wildlife Service Contract No.
14-1~1522. 11 pp.
Snelson, F.F. 1971. Notropis mekistocholos. R
new cyprinid fish endemic to the Cape Fear
River basin, North Carolina. Copeia
197~:449-462.
Author
The primary author of this proposed
rule is Richard G. Biggins, Endangered
Species Field Office, 100 Otis Street.
Room 224, Asheville, North Carolina
28801 (704/259--0321 or ITS 672-0321).
Llst of Subjects in 50 CFR Part 17
Endangered and threatened·wildlife;
Fish, Marine· mammals. PlantS . . ,
(agriculture]. · · ... · ·. · .. ·
· Proposed Regulations Promulgation.
PART 17-{AMENDEDJ
Accordingly, it is hereby proposed to
amend Part 17, Subchapter B of Chapter
I, Title 50 of the Code of Federal
. Regulations, as set forth below: . . .
1. The authority citation for Part 17-, ·
continues to read as follows: ·
Authority: Pub. L 93-205, 87 St~t. 884; Pub.
L 94-,!59. 90 Stal 911; Pub. L 95-002;92 Stal
3751: Pub. L 96-159, 93 Stat. 1225; Pub. L 97-
304, oo s_t~L 1411 (18 u.s._c. 1531 et seq.) .. :_
2.11 iil,-proposed to amend § 17.ll(h] ..
· by adding the following, in alphabetical
order tinder '.'FISHES," to the Llst of• · ' ·
Endangered and Threatened Wildlife: • . . . . .. ·'··· :. .
§ 17 .11 Endangered ~nd threat~ned ·
· wildlife. ·
• •
(h) • ~ •
. HlstOlic range
Vertebrate
""""'"""'--endangered or ·.When listed Critical . .....,.
threat600d
F1SHt:s
SNnor.".CapeFear·_· ~··~--Notropis~•---~.~(NC)-~----·Entirc, ____ •---17.95(e) NA
3: It Is furth~r pr~po~~d to iim~nd
§ 17.95(e) by adding critical habitat of
the "Cape Fear shiner," in the same.
alphabetical order 3s the species occurs
in § 17.ll(h). . .
§ 17.95 Critical habitat-fish and wildlife.
(e) ~ • •
. . .
Cape Fear Shiner·:
(Notropis mekistocholas)
(1) North Carolina. Chatham County.
Approximately 4.1 niiles of the Rocky
River from North Carolina State ·
Highway 902 Bridge downstream to
_Chatham County Road 1010 Bridge;
(2) North Carolina. Chatham and Lee
Counties. Approximateiy 0.5 mileS of .
Bear Creek, from Chatham County Road
2156 Bridge downstream to the Rocky
River, th~n downstream in the Rocky
River (approximately 4.2 miles] to the
· ·· · Deep River, then· dowristream in fue .
Deep River (approximately'2.6) in
Chatham and Lee Counties, to a point
0.3 river miles bClow the Moncure, North
Carolina, U.S. Geological Survey Gaging
Station; and . ·
(3) North Carolina. Randolph and
Moore Counties. Approximately 1.5 · ' .
miles of Fork Creek, from a poi~t 0.1
creek miles upstream of Randolph
County Road 2873·Bridge downstream to
the Deep River then downstream
appoxiffiately 4.1 miles to the Deep
River in Randolph and Moore Counties.
North Carolina, to a point 2.5 river miles
below Moore County Road 1456 Bridge.
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Federal Register / Vol. 51, No. 133 /. Friday, July 11, 1986 / Proposed Rules 25223
Constituent elements include clean
streams with gravel, cobble,_and boulder
substrates with pools, riffles, shallow
runs and slackwater areas ~ith large ·
rock outcrops and side channels and ~
pools with water of good quality with
relatlvelY low silt Joads.
Dated: May 30, 1986.
P. Daniel Smilb.. ·
Acting Assista'rit Secretary for Fish and .
Wildbfe and Pai-ks.. -. . . -
fFR Doc. a&-15&13 Filed 7-1{µ)6; a:4s a;,,J
BIUING CODE 431·)·5~
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W(l L RECORD
NORTH CAROLINA DEPARTMENT OF WATER ANO
DIVISION OF GROUND WATER
B BOX 2704B · IIALEl(;l_ N. C .
Reg. No. 7
I. To"" ,41.or.LiA..><.,...>...u,cc______ Co1,nty
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IWRlll CAROLINA DEPARTMENT OF NATUHAL ANU ECONOMIC RE:;OURCES
!wEl.L RECORD!
OFFICE OF WATER AND AIR RESOURCES
GROUND WATER DIVISION
P. 0. BOX 17687 ~ RALEIGH. N. C.17611
2.B.J.LJ.Jllic•~ '=nG _____ _
~ "" 1-00M -,-:::;---.-1.QJ MAI.IQU.0[.S(;_fi!J~TION
10-25-72 0 22 clny DATE: ~------11---__________ _
22 150 shnl,
___ TOU.l O[PTH _l.5.Q~.--RIG TVP[ OR M[THOO: -·~••<----lf---+---+-c---~-~--------
8,,--f011M.Ul()"4 SAMPLES
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Wlll!/1 U\HOLl:M i)t:i',\f!Wi:.'ll [IF fjl,i!IPM. t .. :; r.coi'i:1.1:1c
DIV]Slotl or [!N[ROW1[NTAL ~J,:M!ilJ'.L:n
GHOUN~WA 1 EH S[CT ION
r,o, ROX 27637 -RltL(!rJH, !I.(, :'./&11
Heater Well Co .
1. WT.I.!. 1,WAT!(\'l: ($ho..r Sl.t•tch o! the l<>CJt1on t,(')o..,)
ile11r"H T()'-'fl: ___ M_o_r_r_,_· _s_v_1_-_1_,_•~: _______ _ c0 ,.,,1 .,. , W_a_k_•--== 0 ______ _
~orr~ll's trove Rd. near ·Airport·
IRo.,d,Co,,.,.,unily or :;ul,divi~ion and l.Ot so, l
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1. ,-m,nss, 304 Cary St., Car:1..-1 N.C. 27511
4. Tlll'oc.;li.APli~: ~ val l,•y, slope, hilltop, flat (c i,cle om•,
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!:0!·:111 CAROLINA DEPMiTMEIH OF NATUHAL ANO ECONOMIC RESOURCES
lv<El.L RECOR!~
OFFICE OF WATER ANO AIR RESOURCES
GROUND WA (ER DIVISION P. 0. BOX 17687 -RALEIGH, N, C. 2;511
Al!(JHlss·_B,_t_!. . .1.-' Box 255, Morrisville,_ H -••..
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OFFICE OF I/ATER AND AIR llESOURCES lwELL R[CORoj GROUND WATER DIVISION
P. 0. BOX 27687 -RALEIGH, N. C. 2/GI I
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WELL fE.:D GD!-'J-'l.ETJ.OH: Hr.1.i ,_ ekut,ch
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of tho
a.cco1u1
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\IEU Li:CATION:
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Drav a l.:,cetloo sketch showing the <l!reetio11 and dh1t.orieo of U,o
well to ,t least two (2) nearby roferen,:e po1nt.n nuch u roe.di,
intersectiono and atre&IICI. Idontl!'y rOllda with ~tote Hlghv&y ro.i1
ideritifica tion mimbere. · .//
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WELL HEJ. D Cr.+il'I.ETION:
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Dra11 a. okatch of _tJ:iq voll bo,,hu tohtr,11na c.uiJi,t., J...tbf' 1•1,,1,,c:,
eeaJ.e, ventp~ 4000110 port, ,irout, l!IU'.I encloour-. • . '
==,=,=====================---WELL LO'.ATION: Drav a locati:m sketch 11b(Ning the directio:i end d1eit..nc:• of'~
well to at lou1t tvo (2) 1~arby refere1.ce po I nte our.h u road•,
int,sraecti..:,118 and etreau. ldent1fy roadi, w1th !it.ate IHM'.lrw7 rt.ad
ident1fic6tion ouabere.
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rrnrn11 CAHOLINA ll[PAllTMENT OF NATURAL Alli) ECONOMIC f·:ESOUflCES
OFFICE OF WATER ANO AIR RESOURCES
GROUND WATER DIVISION lwELL RECORD!
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fWal,, veOto, acc11t10
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pori, v.rout, ail'\ n1,0)01>uro.
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\JELL LC :ATION:
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=:=··==:="--'====---·======================== =· WELL ~OiATION: Ora\./ a J:,ci;tlon aketch aho..,in,g ·tho din,cttvn 111u1 tl\11tA1.i:c, t,r ti,Q
veil to 1;1t least two (2) 'nearby refurei.ce polr,t.:i riucL ,u, rm"'•llf,
intersec'!.1c,1a aJld str8&Jlt. Identify ro1:1.du 1.dt/1 5t.UJ Hll(ln.o.,r rot.ll identiffrat:i.0n nu.mbors.
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lwD .. L REC01,oj
OFFICE OF WIITER AIW Alll RESOURCES
GROUND WATER DIVISION
P. 0. BOX 17687 -RALEIGH, N. C. 2761 I
R(ll NO
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DOf.S T•HS '!Wfll. fl[f'l,'C( AN OISTING lll'f.LL~ __ •c•co __ ,1-.,_lo9 __ 1--c',scoc...+-"'c"cecl l rock
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t<AV[ YOU 1'-FOlh,•EO TH[ "'ELL 01\IN[R OF TII[
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ae !tla, ·vent.a, uccoue po!'.t, g:-uut, uud uncl.ouur11. ,·,,'
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WEL:, 101::ATION: Draw a location sketch a·hoving the direction and d1atanco or tho
well to at .least two (2} nearhy refarence pointe ouch e.11 rocuJa,
interaect.io:ie and atreams. Identify roads with State 1!1ghwo)' .. r_ot.,t
identifit:a t lull nw:nbere. ·
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1/0lilll CAHOLINA OErARTMENT OF NATUHAL AND ECONOMIC llESOJllCES
!wn.L RECORD!
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OFFICE OF WATER ANO Alll RESOURCES
GROUND WATER DIVISION
I'. 0. BOX 27687 -RALEIGH, N. C.17611
'-':•~"0! -cemcnl ~ pump l-----
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\..'ELL l!E. D COMPLETlON: Dr11Y ,1 olc.otch of the VfJll hon1 ll)1(1,dr1rf.: ,·nid:16', 1"-""'l' llJd1.,_·,
15a1Us. vonto, acn11:10 pvrt, grouL, 11,1d ouclu11111"0,
= =•======================== WELL ~O{ lTION; Drav a locutim ale.etch ah<)·.ring th,i d\rvctlu,, t1.1.,J {11tH4:w.,, ,,J' tl.u
vell to at lo1et tvo (2) nearby rri!'ur,,i,c,, v,!r:tri i,1Jt:); 11,r-:·,,,.,111,
1ntoreect1,ma and et.rea.ma. Td.ont1fy ron.,w 'J! t). ::t,s\,1 l!!l{li'"'"Y re .. ,.:
identifies :.io 1 11WDbera 1
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' r,::'.U'1't,!l'~tl',~~ 1 /!'J!i r• ~g!e"l.Y,:¥:r.:i,-.r;rtr,,-~'7~~~~'~'°!' !""l',~~t.""M" ,:"7,17'!',t;;:"", --.f~'i r...-· ......... "~t,, ! ..• , .· :iA'::-~.-•."'::>;.-r•--... ~, .· .-,_ . :· 'f•. •; ., -.
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r:Olml C/dl0!.IIU1 D[FAlml[IIT OF IIIITUR/11. llillJ l:CIJIIUl,IIC RE,OURCES
lwELL RECORD!
OFFICE OF WATER AND AIR RESOURCES
GROUND WATER DIVISION
Wei I I J P. 0. BOX 17687 -RALEIGH, 11. C. 1161 I
-~~~Of'lfHCT~ llt:a_~er Well CL1., Im:. l.lG. /10
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W(LL CONs:RuCTION P(R ... IT NO
Wake Counly:
'54 _________ o..oaron~I~ !lo ·~t.; ,.. .. lr -------. ---···-·· ( i:l<iad' ;· C.o,,,.......,1Y-j' !~&·.r;;;r;;;;;--;,;J "[01 No
1· t"".Nt:~_!.£E1'ers Company, nc.
AOC•1<Lss·.l'_._ __ ,_i,_f1:l1X B1 Hort·isville 1 N, C. 2756
f\_ __ t<J'lh,o
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1--~----~~ _c __ l_•~Y. _______ _ om 9-28-72
(J;,.'t-~ 1><1'> .-1.ll.-Hlf'LACI.. <1-. t•ISIING "'f.LL7
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'.,•A•t: "'I.A';tJ"l!l ____ ,. __________________ ,I
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\./ELI. HE,D COKPLETION1 Or,tw ~}Lotoh o~ U• w.,,,l} hoe.d -hurr.,~i'f: 1:•itl•-G, l"-'111)• 1•11,1,,.-1 OH.la, vent.11, o.cooaa pc.ll't., arout., and cmclooura.
WELJ. LOCATION: Draw a lo,:11tion alr.otch 11howirl8 tha d1roct101i •nd 1.HolA11co v( U1•
well to at lt1u1t two (2) 11oarby rererttace ~1r.tn cmcl, u rc..o1a,
intersection,, and atrea.m,i. Identity roadt1 with :it.ate 1!1ftl'lll1 rtAil
identific11tic,n OU14bore.
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NOHTII CAROLINA DEPIIRll.l[NT OF NATURAL ANO ECONOMIC RESOJRCES
OFFICE OF W/1TER AND AIR RESOURCES
GROUND \'/ATER DIVISION
r. 0. BOX 17687 -RALEIGH. N. C. 2761 I fleat,:r \./,:1 l Company, Inc. I ~~'.\~~~~-r~~------... -~~-~~~--'e's'.· -'','s_~-----~~T..'.!_;;:TtON...f.ff""IT NO
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WELL [.Q.'ATION1 Draw a luoa~ion aketch 11h0\o--fng Uui d1 .. oct1nu u.:1 d1•tonco ur U>.
+•.:--vell to ut. ::eaet tvo (2) Marby reforaoca po1nto our.h u road•,
interHct,101111 and atreaJU. Idonttr, reed• v1lh St.a.to Ht1tN&7 rc:..•l
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·~~·.
North Carolina Department of Human Resources
Division of Health Services
P.O. Box 2091 • Raleigh, North Carolina 27602-2091
1~ --~------I
I Ref. 47 I
James G. Martin, Governor
Phillip J. Kirk, Jr., Secretary Ronald H. Levine, M.D., M.P.H.
Ms. Denise Smith
EPA NC CERCLA Project Officer
EPA Region IV Waste Division
345 Courtland Street, N.E.
Atlanca, GA 30365
Dear Ms. Smith:
SUBJECT: Summary Trip Report
22 January 1987
Koppers Co., Inc. NC D003200383
Hwy. 54 West
Morrisville, NC 27560
Site Investigation, December 17, 1986.
State Health Director
Tne Koppers Co., Inc. site is located on a 53 acre tract on Hwy. 54
West in Morrisville, NC. A company called Unit Structures first produced
glued-laminated wood products on this site around 1955 until 1962. Koppers
purchased the site in 1962 and continued the glue-laminating process. From
1968 to 1975, Koppers used the southeast portion of the site for wood
treatment with pentachlorophenol (PCP). Wood treatment was discontinued on
site around 1976, however, laminated wood production continued. The plant was
sold in September 1986. Koppers retained 10 acres of the original site
including the areas where PCP contamination was known or likely to have
occurred. The remainder of the site has been sold back to Unit Structures.
Koppers notified as a generator, transporter at this site. However, no Part A
application for interim status was filed and no closure permits have been
issued.
Wastewater lagoons from the PCP treatment process were closed by
Koppers in 1976. The liquid from the lagoons was sprayed over a portion of a
field in the northeast corner of ·the property and the sludges were mixed with
soil surrounding the lagoons. Soil samples collected by Koppers in the spring
and fall of 1980 led to the removal of PCP contaminated soil from the site.
Subsequent studies have been conducted by Koppers and US EPA Region IV. To
date, PCP has been measured in soil, groundwater, and pond sediment on site.
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Ms. Denise Smith
22 January 1987
Page 2
The northern portion of the site drains to a ditch which crosses under the railroad tracks and Hwy. 54 and flows to the northeast. The rest of the site drains to Koppers pond. The pond has an outlet to the south which drains to another pond on residential property across the road. City water is not.available in the area immediately surrounding the site. Residents and business are dependent on private wells for water supply.
NC CERCLA Unit personnel Pat DeRosa and Mark Durway initiated a site inspection of the Koppers site on December 19, 1986. Since an on-site inspection was postponed awaiting a meeting with Koppers representatives, off-site well sampling was planned to address contaminant migration and potential public health concerns. We arrived at the site at approximately 1000 hours. We drove around the perimeter of Koppers property in order to identify and locate off-site wells previously sampled. Based on previous sampling, topography, and prior contact with off-site well owners, 6 wells were selected for sampling.
We began sampling at 1115 at Triangle ~laterials approximately .5 miles southeast of the site. This well should serve as a background groundwater sample. We subsequently sampled the residential wells at the homes of James Crowe, William Barbee, George Harding, John Medlin, and Louis Barbee. These wells were purged prior to sampling except where owners cautioned us against running the well dry. Samples were collected for volatile and extractable organics, inorganics, and low concentrations of acid extractable phenolics (i.e. PCP). Samples were preserved accordingly and submitted to the NC State Laboratory of Public Health for analysis.
On January 7, 1987, we returned to the site to meet with Koppers representative, Mike Dvorsky, and Jim Campbell and ~!arty Schlesinger of Keystone Environmental Resources (KER). KER works under contract with Koppers to provide laboratory services. We toured Koppers' portion of the site and obtained background information on the former PCP treatment operations. We also discussed site sampling and cleanup activities which had been conducted at the site to date. Additional sampling data and hydrogeologic information is forthcoming from Koppers and KER.
If you have any questions, please contact me at (919) 733-2801.
PD/tb/0338b
Sincerely,
~/J-e/V--
Pat DeRosa, Waste Management Specialist
CERCLA Unit
Solid and Hazardous Waste Management Branch Environmental Health Section
Fifth Editio11, 1984
North Carolina State Government
Statistical Abstract
North Carolina
Research and Planning Services
Office of State Budget and Management
-··-····-· -.
N u, N
F lgure 29
AVERAGE JULY TEMPERATURES
DEGREES FARENHEIT
N, C, _ Average
Maximum 87, 4 °
Minimum 65, 8°
{BASED ON 30 YEAR AVERAGE)
SOURCE: N.C. State University, Department of Marine, Earth and Atm::>spherlc Sciences, Office of the State
Climatologist,
-- - - - - - -------- -----
. ,~··
l~·:: .. ·-··
40
F lgure 28
AVERAGE JANUARY TEMPERATURES
DEGREES FARENHEIT
(BASED ON 30 YEAR AVERAGE)
N, C. Average
Maximum 50.7°
Minimum 29.0°
40
·,
I.·-··-·-··-·-·,:~"'"
SOURCE: N.C. State University, Department of Marine, Earth and Atrrospherlc Sciences, Office of the State
Climatologist, .
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42
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PUBLIC HEAL TH LIBRARY
DIVISION OF HEAL TH SERVICES
P. O. BOX 2091
RALEIGH, NORTH CAROLINA 27602
Edi led by JAMES W CLAY
DOUGLAS M. ORR, JR.
ALFRED W STUART
Forewad by JAMES E HOLSHOUSER, JR.
The University of Nortt1 Carolina Press · Chapel Hill
·-r
-----Figure 5.21. Prevailing Winds and Mean Annual
Wind Speed in N.C.
NE
Source: U.S. Department of Commerce, Climatic Summary of the
U.S .• 1972.
Noto: Wind speeds are noted in miles per hour.
Wind speeds have been averaged for each zone of
prevailing winds. Winds tend to diminish in speed
westward from the coast where sea breezes and offshore
storms contribute to velocities that average twelve miles
per hour. Throughout the Inner Coastal Plain and the
Piedmont, the mean wind speed is nine miles per hour,
and in the western counties, representative wind speeds
are seven and eight miles per hour. On a daily basis,
wind velocities are lowest before dawn and highest
around midafternoon. Seasonally, winter, with greater
temperature and pressure contrasts, shows the most
rapid air movement and sum·mer is the time of lowest
wind speeds.
Thunderstorms Thunderstorms are vertically de-
veloped storm systems that involve lightning and thun-
der. Produced by instability in the atmosphere, these
storms are sustained by the conversion of water vapor
· into rain and hail, which causes the release of enormous
amounts of energy. This energy results in vigorous
updratts of rapidly moving air. The intensity and turbu-
lence of an individual thunderstorm is related to the
degree of atmospheric instability and the supply of latent
energy released by the condensing of water vapor. In
structure, the typical thunderstorm is a collection of
convecti~e cells each averaging a mile or more ·in
diameter, A cell is comprised of columns of rapidly
rising airseparated and counterbalanced by downdratts
of slower moving air. Associated with thunderstorms and
their bulbous facade are heavy downpours of rain, hail,
gusty and squally winds, and of course. lightning and
thunder.
104
------Because thunderstorm development and frequency is
enhanced by (1) atmospheric instability that is linked to
high surface temperatures, (2) atmospheric moisture that
supplies the latent energy requirements, and (3) some
triggering device to start the convection process,
. thunderstorms occur more frequently in regions of warm
temperatures and high humidities. North Carolina·s
climate is conducive to thunderstorm development and
the state experiences violent local storms forty to fifty
days each year. For the United States, Florida and the
Gulf Coast lead in the number of days with thunder-
storms. Here. seventy to ninety days per year with
thunderstorms is normal. In the northern states and along
the West Coast, thunderstorm activity drops off because
of colder temperatures over land and coastal waters.
North Carolina's pattern of thunderstorm activity shows
fewest storms off the northeast coast where coastal
waters also are cooler. Inland, thunderstorms are more
frequent, increasing to fifty days as the Mountains are
approached. In the Mountains, the higher frequency of
storm activity (all types) and the triggering supplied by
mountain and frontal slopes results in the most thunder-
ous area to be found in the state (Figure 5.22).
Hurricanes In the latter half of the year. the United
States is visited by hurricanes. Originating over tropical
oceans as small cyclones, under favorable conditions
hurricanes become large, intense storm systems. Their
winds exceed seventy-five miles per hour and spiral
counterclockwise around an "eye" of very low pressure.
Sustained by the ocean that breeds them, these storms
are driven by the heat released from condensing water
vapor. Covering tens of thousands of square miles, ·
hurricanes move slowly and deliberately, at speeds
between fifteen and fifty miles pei hour, delivering
prodigious amounts of precipitation to areas over which
they pass. Moving out of the tropics, hurricanes of the
Atlantic Ocean generally invade the Gulf of Mexico, or
veer northward toward the middle latitudes, occasionally
penetrating the continent, or skirting the coastline as far
north as New England. Hurricanes are sea monsters and
diminish in intensity as they move inland and away from
their source of energy. Although capable of great
destruction, hurricanes nevertheless benefit the south-
eastern states to a substantial degree. As the eastern
states are subject to periodic summer droughts, the vast
amounts of water delivered to this region by these giant
tropical storms have served more than once to alleviate
or terminate the disastrous effects of drought conditions.
However, hurricanes are killer storms, and their long-
range benefits are obscured by the more obvious death.
destruction, and damage accompanying them. On the
average, the Atlantic Ocean generates six hurricanes a
-----Figure 5.22. Average Number of Days with
Thunderstorms
Number of Days
80 and above
60-80
40-60
20-4-0
below20
Source: Glenn T. Trewartha, Arthur H. Robinson, and Edwin H.
Hammond, eds., Elements of Geography, 5th ed. (New York:
McGraw-Hill Book Co., 1967).
year, but as many as eleven in one year have been
observed. North Carolina has experienced twelve espe-
cially disastrous hurricanes since 1900. Cape Hatteras,
extending as it does into the ocean, is affected by
hurricanes more than any other area of North Carolina·
(Figure 5.23). Its low-lying sandy surface is especially
vulnerable to the combined effects of high winds. high
tides, and flooding associated with these storms.
-•
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__ .---::·::.~:.:~ .'::;;::~
"'f'"" ,J "-'-'I>"• /,:;,,: .ff , -~ 1\
! ~ ;~it~(.,, ~ \ ;;t ,. l .,·-• · ;,:, i -:_0 ~I;~· 'DJ \; ·:.,. if,
~<~:~::::. ·::;.-;: .... /
North Carolina Department of Human Resources
Division of Health Services
P.O. Box 2091 • Raleigh, North Carolina 27602-2091
,·
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Ref. SO
James G. Martin, Governor
Bhillipc,lxKirk~ry
Ronald H. Levine, M.D., M.P.H.
David T. Flaherty
Secretary
MEMORANDUM
TO:
From:
April 15, 1987
Pat DeRosa
Solid and Hazardous Waste Branch
CERCLA Unit
Ted Taylor, Ph.D., Toxicologist<
Environmental Epidemiology Branc~
State Health Director
SUBJECT: Koppers Company -Off-site Groundwater Investigation
I have reviewed the DHS laboratory results taken from 13 wells surrounding the
Koppers Company at the Morristown site. Two chemicals used in the Koppers
wood-treating process, isopropyl ether (IPE) and pentachlorophenol (PCP),were
found at variable, but very low, concentrations in a number of the wells.
Five samples were co~pletely negative; the Crowe, John Medlin, Roy Medlin,
Louis Barbee residences and the Deli Box. IPE was found in the wells of
Wilkinson Construction (trace), William Barbee (1.4 ug/1), L. A. Lyons (16
ug/1), and the Shiloh Baptist Church (28 ug/1); the minimum detection limit
reported by EPA is 10 ug/1. The minimum detection limit for PCP by the EPA
derivatization method is reported to be 0.5 ug/1; however, the DHS laboratory
used a larger sample volume and was able to detect even lower concentrations.
The highest level of PCP detected was 0.02 ug/1 at the Shiloh Baptist Church.
Trace levels of PCP Oess than 0.02 ug/1) were also found at the residences of
Baker, Harding, William Barbee, and at TMI, Wilkinson Construction and Watson
Burroughs. Thus, the water at the Shiloh Baptist Church represents the "worst
case" for the purpose of evaluation of any health risks associated with
drinking water that is contaminated with IPE and/or PCP.
In the case of IPE, no relevant toxicological data are available on this
chemical as such; however, based on its structural similarity to diethyl ether
and to other ethers, the predicted toxicity of IPE would be expected to be very
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DeRosa Memorandum
Page 2
April 15, 1987
low. Tl1us, based on the present information, our best judgment suggests that
the concentrations of IPE found in the four wells do not represent a
significant health risk to people who consume this water. ·
In the case of PCP, many relevant studies have been published which indicate
that the levels found in the 7 wells do not represent a significant health
risk. However, a very recent unpublished toxicity study suggests that PCP may
cause cancer in laboratory mice; PCP did not cause cancer in rats. Thus, if
the mouse study is found to be valid, some caution would be warranted when PCP
is detected in drinking water at elevated concentrations, i.e. in the parts per
billion range.
RECOMMENDATIONS
1. Although PCP apparently produced tumors in mice, the dose given to the
animals was hundreds of thousands times higher than the dose that would be
received from drinking well water in this area. Thus, at this time, based
on the available information, the water from the wells surrounding the
Koppers site does not represent a significant health risk; normal usage of
water for drinking, cooking, bathing, may continue.
2. Since IPE and PCP were admittedlcy used in the Koppers process and since
off-site contamination has been demonstrated, further monitoring of private
wells should take place (probably at least at six-month intervals for the
near future). This will assure that citizens are not exposed to
unacceptable levels of chemicals should the levels be found to be
increasing in the future.
If you have any questions, please feel free to contact me at 3410.
TT:lp
c: Bill Meyer, Head, Solid and Hazardous Waste Branch
Perry Nelson, Chief, Groundwater Section
Wally Venrick, Head, Public Water Supply Branch
Greg Smith, M.D., M.P.H., Environmental Epidemiology Branch
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STONE
EN\'IRONMENT AL RESot:acrs. ISC.
436 Seventh Avenue, Suite 1940, Pittsburgh. PA 15219
Dear Ms. DeRosa:
March 5, 1987
N.C. Department of Human Resources
Division of Health Services
P. 0. Box 2091
Raleigh, N.C. 27602
ATTN: Pat DeRosa
Waste Management Specialist
Ref. 51
Keystone Environmental Resources has been contracted by Koppers to
conduct the environmental affairs associated with its former
Morrisville, N.C. Facility. In conjunction with the sale of this
property to Unit Structures Inc., an environmental base-1 ine study was
conducted. This included a survey of the off-site groundwater used for
human consumption,
The off-site survey consisted of three rounds of samples, taken from
n!ne pr!~!te ~!ter ~ells. The first round was sampled on October 24,
1936, and was analyzed by the Keystone Environmental Resources
Laboratory in Monroeville, Pa. The analysis included both conventional·
water quality parameters, and volatile organics, The latter was done
.using gas chromatography (GC).
A second round of samples were taken on November 20, 1986. Duplicate
samples were analyzed by the Monroeville Lab and by Spectrix
Laboratory in Houston, Texas. The Houston laboratory utilized GC/MS
{gas chromatography/mass spectrophotometry) for organic analysis. The
Monroeville Lab used a modified procedure in the extraction step prior
to GC analysis, using four liters of sample instead of the normal one
liter. A Koppers' method of analysis for pentachlorophenol was also
run in addition to the standard GC method.
The third round of sampling was conducted on January 14, 1987. The
samples were split between the Monroeville and Houston Laboratories,
and analyzed like the samples from round two. That is, 4L of sample
were extracted for organic analysii instead of the normal 1 L.
Both gis chromatography (GC) and gas chromatography/mass
spectrophotometry (GC/MS) are accepted methods of organic analysis
which can detect contamination at the ug/1 level (parts per billion).
Of the two methods, GC normally can detect organic compounds at lower
concentration levels, but does not positively identify the compound.
GC/MS provides a more positive identification of the compound but at a
slightly higher level of detection.
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Page 2
This difference in lower detection levels, and the actual
concentrations found, present some problems in the discussion of
contamination levels. It appears inappropriate to state a definite
concentration of a compound when the contamination levels are so low.
Consequently we will present the ranges of contamination levels, noting
that in each case, at least one round of sampling exhibited no
detectable contamination.
Based on the attached analytic data and interpretation, we feel that
two of the off-site wells tested produce water with trace levels of
industrial chemicals. These are Wells 05-8 (The Shiloh Baptist
Church) and Well 05-9 (William Barber Well). The range of constituent
levels are:
Well 0S-8 (Shiloh Baptist Church)
Pentachlorophenol
I sopropyl ether
Hell DS-9 (William Barber)
Isopropylether
8.8 to 28.8 ppb
(Avg. Detected 19.4 ppb)
26 to 85.5 ppb
(Avg. Detected 57.5 ppb)
13.3 to 17.5 ppb
(Avg. Detected 15.4 ppb)
Please note that the average values do not include several ''Not
Detected" analytical results.
The constituents were found at low levels and not consistently
detected in repeat sampling. The levels measured of these chemicals
are not associated with adverse health effects. The highest
concentrations found, 28 ppb pentachlorophenol, and 85 ppb
isopropylether, are not considered dangerous to the health of
individuals using ·the water on a daily basis for routine activities,
i.e., drinking, cooking, bathing, and laundry. Regulatory standards
have not been promulgated for either chemical in drinking water;
however, the U.S. EPA has issued a lifetime health advisory guideline
of 220 ppb for pentachlorophenol in drinking water. The most
stringent guideline established for pentachlorophenol in drinking
water is that of the State of California which has set a level of 3D
ppb on the basis of the taste and odor imparted by the contaminant on
the water.
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We have included the
for your inspection.
of custody documents
Page 3
analytical results
These include the
are available upon
from all the
QA/QC data.
request.
sampling rounds
The sample chain
We are looking forward to discussing this information with you next
week. Please call if you have anyquestions concerning this data.
Sincerely yours,
Martin M. Schlesinger, Assistant Program
Manager
Previously Operated Properties
&hll3M~
J. H. Butala,·o.A.B.T.
Manager, Toxicology and Product Registration,
Koppers Company, Inc.
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Page 4
ANALYTICAL INTERPRETATION
Wells 05-1 to 05-4
Round #1 -
1:c'-l'{l
Route #2 -
Well 05-5
These samples were filtered in a room which contained sawdust contaminated with Pentachlorophenol. Because PCP was not found in the other samples these are to be disregarded. ,
f r..-. 1\.(;...e. f ~ l ~-~J\
The~nti\)contamination found in Wells O,S-1 to
GS-~ 05-A' "'.'ere below !he~ concentrations in both the field and trip blanks and are therefore to be di s(oun"ted. · ------
The only constituent identified was PCP in round #3 by the Monroeville Lab at 0.6 ppb, using GC. However, the Houston Laboratory did not find the compound at a higher detection limit. Because this trace level 0as found only once, this figure should be discounted.
\•Jell 05-6
Unfortunately, the third sam~le round was destroyed in shipment. However, only a trace level of !PE was found by one lab during round #2. Based on the low level of !PE (1.46 ppb) and the lack of .confirmation, this figure should be discounted.
Hell 05-7
A trace level (8.6 ppb) of PCP was found via GC by the Monroeville Laboratory during the third round. However, the same laboratory did not find PCP using the more sensitive Koppers' method, nor was PCP found by the Houston Lab using GC/M5. Based on the level of contamination and the lack of confirmation in other rounds, this figure should be discounted.
Hell 05-8
Pentachlorophenol was found at trace levels (8.82-28.8), and confirmed by GC/M5 in two rounds of sampling. Additionally, !PE was found at 26_-85.5 ppb levels. Three pheno·lic compounds were identified in only one of the samples, but their presence was not confirmed.
STONE o-.!\it._ T _.,L RE.SOl!RCL\, 1-.c.
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Page 5
Well 0S-9
Isopropylether was found in two samples, but not confirmed by the
GC/MS. Concentrations were 13.3 and 17.5 ppb.
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TO:
FROM:
RE:
File
Pat DeRosa D-1' r Y
Koppers Co. Inc.
NCD003200383
May 8, 1987
I spoke by telephone with Marty Schlesinger, Keystone Environmental
Resources, (412) 227-2690, regarding permit and regulatory history at the
subject site. According to his records the only environmental permit held by
this facility is an Air Permit (#1320R4) issued by the State of NC under the
Clean Air Act. This permit was renewed in 1984. No permits are known to have
been held under RCRA or NPDES.
PD/pw/0384b
Ref. 52
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POTENTIAL HAZARDOUS WASTE SITE I. IDENTIFICATION oEPA SITE INSPECTION REPORT NCTATEl &' 5QQ~UM1DRO 383 PART 1 • SITE LOCATION AND INSPECTION INFORMATION
II. SITE NAME AND LDCA TION
01 SITE NAME IL&a1I. cOfflmOll. o,desc,t,11ve nMN1 of stteJ 02 STREET. ROUTE NO., OR SPECIFIC LOCATION 10!:;NTIFIEA
Koppers Co. Inc. Hwy. 54 West
OJ CITY 04 STATE I 05 ZIP CODE I 06COUNTY l0'~·r•g&r Morrisville NC 27560 Wake
09 COORDINATES
lw..a
110 TYPE OF OWNERSHIP (Ctt•e~ 0111J LATITUDE LONGITUDE G(A. PRIVATE O 8. FEDERAL DC. STATE OD. COUNTY OE. MUNICIPAL .35. SQ..49-SD 19 0 F. OTHER 0 G.UNKNOWN Ill. INSPECTION INFORMATION
01 DATE OF INSPECTION 02S1TESTATUS 03 YEARS OF OPERATION 12/17/82&1(_7/87 XJ ACTIVE "-' 1959 I current _UNKNOWN MONTH. OAY YEAR 0 INACTIVE BEGINNING YEAR ENDING YEAR 04 AGENCY PERFORMING INSPECTION /Cit.ck -'lfll1r -,oly/
0 A.EPA 0 8. EPA CONTRACTOR· 0 C. MUNICIPAL □ D. MUNICIPAL CONTRACTOR ~ E. STATE (N_,,e ot firm/ (N-Offlnn} 0 F. ST ATE CONTRACTOR □ G.OTHER /N.,,..olli¥m) tSll•th! 05 CHIEF INSPECTOR 06 TITLE 07 ORGANIZATION 06 TELEPHONE NO.
n~.--·~ 1"."1-_ _,_ ---,...--..... .;,:, l.; -.J 1<>1 J 733-2>tn7 09 OTHER INSPECTORS 10 TITLE 1 1 ORGANIZATION 12 TELEPHONE NO. Mark Durway Geologist NCDHR 191';\ 733-280;
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13 SITE REPRESENTATIVES INTERVIEWEO 14 TITLE 15AODRESS 16 TELEPHONE NO Marty Schlesinger Asst. Proj. M KER, Pittsburgh, PA. (412 227~2690
Jim Campbell Proj. Manager KER, Pittsburgh, PA. 1412j 227-2689
Mike Dvorsky Engineer Koppers, Pittsburgh, PA. 14121 227-2684
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17 ACCESS GAINED BY 18 Tl~E OF INSPECTION 19 WEATHER CONDITIONS (Cll..:ton•J
~Ef:IMISSION 1300 Overcost, approximately 60 F. 0 WARRANT
IV. INFORMATION AVAILABLE FROM
01 CONTACT 02 OF fAo•.-.e110,g..-u .. 1io,,/ 03 TELEPHONE NO.
Marty Schlesinger Keystone Environmental Resources 14121 227-2690 04 PERSON RESPONSIBLE FOR SITE INS~ECTION FOAM 05 AGENCY 060IT~ZATl02! 07 TELEPHONE NO. 080ATE Pat DeRosa NC OHR So 1 an Haz. 05 ,08,87 Waste Mng. Br. (919) 733-280 MONTH OAY YEAR EPA FOAM 2070-13 (7•81)
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POTENTIAL HAZARDOUS WASTE SITE I. IDENTIFICATION &EPA SITE INSPECTION REPORT 01 STATE,02StTENUMBER
PART 2 • WASTE INFORMATION NC D 003 200 383 I
II. WASTE ST ATES, QUANTITIES, ANO CHARACTERISTICS
0 1 PHYSICAL ST A TES /Ch•c• al r,,,,, apoJyJ 02 WASTE QUANTITY AT SITE 03 WASTE CHARACTERISTICS (Cfl•c• ,,,,,,1,wptyJ
/Ma.1su,es of "'J•I• quam,1,,.s
l¥A. TOXIC 0 A. SOLID lJ E. SLURRY must b" 111cep•nctenr1 !J E. SOLUBLE □ 1. HIGHLY VOLATILE
Ll B. POWDER. FINES Q(F. LIQUID TONS U 6. CORROSIVE (J F. INFECTfOUS 0 J. EXPLOSIVE
WC. SLUDGE I] G. GAS 0 C. RADIOACTIVE 0 G. FLAMMABLE 0 K. REACTIVE
CUBIC YARDS 356.48 CJ D. PERSISTENT 0 H. IGNITABLE 0 L. INCOMPATIBLE
U D. OTHER 0 M. NOT APPLICABLE
/SpflcllyJ NO.OF DRUMS
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Ill. WASTE TYPE
CATEGORY SUBST ANGE NAME 01 GROSS AMOUNT 02 UNIT OF MEASURE OJ COMMENTS
SLU SLUDGE
OLW OILY WASTE I
t'sOL"'I SOLVENTS ·sonronnlether IIPE\ *
(Pso") PESTICIDES Jentachlorophenol
occ OTHER ORGANIC CHEMICALS I
IOC INORGANIC CHEMICALS *IPE lS not a listea
ACD ACIDS ". nazarctous SUbS=,Ce
BAS BASES I
MES HEAVY METALS
IV, HAZARDOUS SUBSTANCES /See Append/• tor most frequat11lyc,1,.dCAS Numbers/
01 CATEGORY 02 SUBSTANCE NAME 03 CAS NUMBER 04 STORAGE/DISPOSAL METHOD 05 CONCENTRATION 06 MEASURE OF
CONCENTRATION I
PSD Pentachlorophenol 87865 Wastewater from TThW
SOL Isopropylether 108203 PCP treabnent
process was ri. I -anct ctisposeeu in
~llU _\ rqr O ll":'.11 u. H: ' LI,=, , --.-I
;rn,,,,+-=l,1
6 vrs. The once
filled vol. of I
laqoons ' --· -·
356.48 cu. yds. I
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V. FEEDSTOCK$ (SeeApp,.ndl• torCAS Numbers)
CATEGORY 01 FEEDSTOCK NAME 02 CAS NUMBER CATEGORY 01 FEEDSTOCK NAME 02 CAS NUMBER I
FDS FDS
FDS FDS
FDS FDS I
FDS FDS
VI. SOURCES OF INFORMATION 1c~e specitic ,,,,,,,,,,,en e.o SIBie 1,es. u,noie anatysrs, ,eporu)
References 2, 23-25, 30, 47 I
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EPA FORM 2070•13 (7•81)
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oEPA POTENTIAL HAZARDOUS WASTE SITE
SITE INSPECTION REPORT
PART 3. DESCRIPTION OF HAZARDOUS CONDITIONS AND INCIDENTS
11. HAZARDOUS CONDITIONS AND INCIDENTS
01 [)[A. GROUNOWATEACONTAMINATION 02 IXOBSEAVEO(DAW ) 978 ) 9861
03 POPULATION POTENTIALLY AFFECTED: app. 2169 04 NARRATIVE DESCRIPTION
I. IDENTIFICATION
01 STATEj 02 SITE NUMBER
~C · 1D 003200383
0 POTENTIAL 0 ALLEGED
Groundwater contamination with , PCP has been measured in on-site wells: May 6 ,-· 197;
(4); July 23, 1980 (7); July 24, 1980 (9); Aug. 21, 1980 (5); Sept. 11, 1980 (5,10);
Oct. 27, 1980 (5); June 2, 1984 (5); and Sept. 9-11, 1986 (8, 21).
01 ~ 8. SURFACE WATER CONTAMINATION 3
03 POPULATION POTENTIALLY AFFECTED: -~---
02.li!OBSEAVED(DATEc l9SQ
04 NARRATIVE DESCRIPTION
□ POTENTIAL 0 ALLEGED
PCP was measured in water from Koppers Pond on Oct. 27, 1980 (5). Pond sediment
contamination with PCP was measured April 11, 1980 (11); June 1980 (12); Sept. 11,
1980 (10); and Sept. 24, 1980 (6). Koppers pond overflows to Medlin Pond used for
01 0 C. CONTAMINATION OF AIR 02 0 OBSERVED(DATE: ._, i,,u, ... ,. Al:1.rr1.,..
03 POPULATION POTENTIALLY AFFECTED:··-____ _ 04 NARRATIVE DESCRIPTION
01 0 D. FIRE/EXPLOSIVE CONDITIONS 02 0 OBSERVED (DATE: _____ ) 0 POTENTIAL 0 ALLEGED
03 POPULATION POTENTIALLY AFFECTED: ____ _ 04 NARRATIVE DESCRIPTION
01 E}E. OIAECTCONTACT pp 638 0200BSERVED(DATEc _____ ) IE: POTENTIAL 0 ALLEGED ~ POPULATIQt:,IPOTENTIALLYAFFECTED: a • 04 NARRATIVE DESCRIPTION c;ome soil: rerroval has occured; however, contaminated soil renains on site near the
.steel shop, old lagoon area, and in the pone!. There are approxinBtely 638 residents
within 1 mile of the site.
~~ !~A~~~;~i:~t~~o:F~;c~~~: app. 10 acre
· . . (Aerni
02KJ OBSERVED (DATE: I/ I rlh& -~ 1 ~i)I
04 NA ARA TIVE DESCRIPTION
0 POTENTIAL D ALLEGED
On-site soil oontarili.nation with
(11); June 1980 (12); Sept. 11,
Sept. 26, 1986 (8).
PCP was measured: March 19, 1980 (11); .April 3; 1980.
1980 (10); June 1981 (13); July 15, 1986 (14); and
01 f.XG. DRINKING WATER CONTAMINATION 02 IS OBSERVED (DA'rE: _____ ) ® POTENTIAL O ALLEGED
03 POPULATION POTENTIALLY AFFECTED: app. 2169 04 NARRATIVE DESCRIPTION
Isopropylether; which was used on site, has been measured: in off-sitedrinking
water wells at approxinBtely 1-28 ppb. IPE, is not a CERCLA tisted hazardous sub-
stance, however, it rray indicate direction of contaminant migration.
01 DH. WORKER EXPOSURE/INJURY · 02 D OBSERVED (DATEc _____ ) D POTENTIAL D AU.EGED 03 WORKERS POTENTIALLY AFFECTED: ____ _ 04 NARRATIVE DESCRIPTION
01 0 I. POPULATION EXPOSURE/INJURY
03 POPULATION POTENTIALLY AFFECTED: ____ _
02 0 OBSERVED (DATEc _____ )
04 NARRATIVE DESCRIPTION
D POTENTIAl. D AU.EGED
EPA FORM 2070·13 (7•61)
r:
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POTENTIAL HAZARDOUS WASTE SITE I. IDENTIFICATION oEPA SITE INSPECTION REPORT 'hltATElfr 5/ffi~"lB'o'383 PART 3 • DESCRIPTION OF HAZARDOUS CONDITIONS AND INCIDENTS I II. HAZARDOUS CONDITIONS AND INCIDENTS (Conwwed/
01 0 J. DAMAGE TO FLORA 02 0 OBSERVED (DATE: I 0 POTENTIAL 0 ALLEGED 04 NARRATIVE DESCRIPTION I
01 0 K. DAMAGE TO FAUNA 02 □ OBSERVED (DATE: I 0 POTENTIAL 0 ALLEGED I 04 NAAAA TIVE DESCRIPTION tlnclvee namers! ot suecies!
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01 0 L. CONTAMINATION OF FOOD CHAIN 02 0 OBSERVED (DATE: I ll POTENTIAL · 0 ALLEGED I 04 NARRATIVE DESCRIPTION I
01 0 M. UNSTABLE CONTAINMENT OF WASTES 02 □ OBSERVED {DATE: l 0 POTENTIAL 0 ALLEGED (Sp1"s!R1mol/!S1andmo hqv,ds, Lna~inQ o,umsl I 03 POPUL.A TION POTENTIALLY AFFECTED: 04 NAARA TIVE DESCRIPTION
I 01 0 N. DAM.AGE TO OFFSlTE PROPERTY 02 0 OBSERVED (DATE: l 0 POTENTIAL 0 ALLEGED 04 NARRATIVE DESCRIPTION
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01 0 0. CONTAMINATION OF SEWERS. STORM DRAINS. WlNTPs 02 0 OBSERVED (DATE: l 0 POTENTIAL 0 ALLEGED 04 NARRATIVE DESCAJP,TION I
I 01 0 P. ILLEGAUUNAUTHOAIZED DUMPING 02 0 OBSERVED (DATE: l [J POTENTIAL 0 ALLEGED 04 NARRATIVE DESCRIPTION
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05 DESCRIPTION OF ANY OTHER KNOWN, POTENTIAL, OR ALLEGED HAZARDS I
Ill. TOTAL POPULATION POTENTIALLY AFFECTED: I IV. COMMENTS
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V. SOURCES OF INFORMATION {C,t,-so,.c,11<: ,,.1e1encu,., 0 • s1.r111 '""'· ump1,..,,...1~s,s, '"f'O'ISI I References 2, 4-14, 26-34, 40, 43. Laboratory results: Off-site groundwater samples jcollected 12-17-86, 3-20-87. NC S:tate Laboratory of Public Health, Raleigh, NC
• )Appendix B: Site investigation report: Koppers Co. Inc. May 1987. Pat DeRosa, NC,..,,.,,.., ; .Uflit ~le I NC, -·--·--· I
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POTENTIAL HAZARDOUS WASTE SITE I. IDENTIFICATION oEPA SITE INSPECTION N~TATE 1:02 SITE NUMBER D 003200383 PART 4 • PERMIT AND DESCRIPTIVE INFORMATION
II. PERMIT INFORMATION
01 TYPE OF PERMIT ISSUED 02 PERMIT NUMBER (Ch.c• d u,ar atJi,iy/ 03 DA TE ISSUED 04 EXPIAA TION DATE OS COMMENTS
DA. NP0ES
OB. UIC
i!!C. AIR 1320 R4 1984 -NC NRCD
~o. RCRA NC-D 00320038. ID# onlv no =nnit.
OE. RCAA INTERIM STATUS .
OF. SPCC PLAN
OG. ST A TE /Spec,tyl .
OH. LOCAL /Soec,iri
or. OTHER,sp.,;lfy/
bJ. NONE
Ill. SITE DESCRIPTION
01 STORAGEIOISPOSAL /Cfl•c• ,11,r,,r apply/ 02 AMOUNT 03 UNIT OF MEASURE 04 TREATMEN! (Check_, 1111111Pp/y/ OS OTHER
~A. SURFACE IMPOUNDMENT aEJ2. 356.48 cu. ~ds. 0 A. INCENERA TION
0 B. PILES . ~ A. BUILDINGS ON SITE 0 B. UNDERGROUND INJECTION
0 C. DRUMS, ABOVE GROUND □ C. CHEMICAUPHYSICAL
0 0. TANK, ABOVEGROUND 0 D. BIOLOGICAL
0 E. TANK, BELOW GROUND 0 E. WASTE OIL PROCESSING 06 AREA OF SITE .
0 F. LANDFILL 0 F. SOLVENT RECOVERY
IZG. LANDFAAM □ G. OTHER RECYCLING/RECOVERY ~? fAe,.•J 0 H. OPEN DUMP 0 H.OTHER
0 I.OTHER (Sp&<;JtyJ
(Sp•e•ly}
07 COMMENTS
. IV. CONTAINMENT
01 CONTAINMENT OF WASTES /Cll•e~on•!
0 A. ADEQUATE, SECURE 0 8. MODERATE 0 C. INAOEOUATE, POOR ~ D. INSECURE, ~NSOUND, DANGEROUS
02 DESCRIPTION OF DRUMS, DIKING. LINERS, BARRIERS, ETC.
Surface impoundments or lagoons were unlined with no diking, diversion system, or
leachate collection system. Liquid from lagoons was sprayed on field and sludge was
mixed into soil.
V. ACCESSIBILITY
01 WASTE EASILY ACCESSIBLE: IXYES 0 NO
· 02 COMMENTS
Site is unfenced, contaminated soil and pond ·are accessible.
VI. SOURCES OF INFORMATION (C/fe SIH,C,f1C1.t•1•ncu, •.i,. sl•telilu, •.mr,l••n.iysls, ,.p0t1_sJ
References 2,23,40,47,52.
EPA FOAM 2070-13 {7-81)
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POTENTIAL HAZARDOUS WASTE SITE I. IDENTIFICATION oEPA SITE INSPECTION REPORT 01 STATEl82 SITE NUMBER NC 003200383 PART 5 • WATER, DEMOG.RAPHIC, AND ENVIRONMENTAL DATA
II. DRINKING WATER SUPPLY
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01 TYPE OF DRINKING SUPPLY 02 STATUS 03 DISTANCE TO SITE {CllednltJplk;.at,/tt/
SURFACE WELL ENDANGERED AFFECTED MONITORED Upstream
COMMUNITY A.IX 8.0 A.0 8.0 C.~ A. > 3 fmi)
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NON-COMMUNITY c.o D.l<) D. Ill E.0 F.0 8. l 9 (mi)
Ill. GROUNDWATER
0 1 GROUNDWATER USE 1N VICINITY (Ch,.eko,,e/ I
m. ONLY SOURCE FOR DRINKING 0 8. DRINKING DC. COMMERCIAL, INOUSTRIAL, JRRIGATION 0 D. NOT USED, UNUSEABLE (Othe, source3 •"""bl•) {Umlt!JdO!l>er 5CM/tCH n.i/a°")
COMMERCIAL, INDUSTRIAL, IRRIGATION
/No other w•ter 1ources •-n,llabltt} I
2169 .19 02 POPULATION SERVED BY GROUND WATER 03 DISTANCE TO NEAREST DRINKING WATER WEU. (mi)
04 DEPTH TO GROUNDWATER 05 DIRECTION OF GROUNDWATER FLOW 06 DEPTH TO AQUIFER 07 POTENTIAL YIELD 08 SOLE SOURCE AQUIFER OF CONCERN OF AQUIFER 3.85 (ft) unknown. 3.85 'ft) unknown 0 YES JC] NO •(gpd).
09 DESCRIPTION OF WELLS /lrir:ludlnQ uHage, 4'eptlr, an<11or:•t.lolt relit/Ive to r,oi:wtation an,:1 """'fj'I used for process water and toilets on-On-site wells Wl and W2 (189' and 73 are
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site. Drinking water wells in the area average approximately 150' deep and are
generally cased down to 20-30 ft. with·the remainder open-hole. I
1 0 RECHARGE AREA 11 DISCHARGE AREA
[XYES COMMENTS 0 YES COMMENTS
0 NO On-site pond. 0 NO I
IV.SURFACE WATER
01 SURFACE WATER USE fCl>ec~o,u,/
0 A. RESERVOIR, RECREATION (xB. IRRIGATION, ECONOMICALLY □ C. COMMERCIAL, INDUSTRIAL 0 D. NOT CURRENTLY USED DRINKING WATER SOURCE IMPORTANT RESOURCES I
02 AFFECTED/POTENTIALLY AFFECTED BODIES OF WATER
NAME: AFFECTED DISTANCE TO SITE I
Ko~;r;:s Pond Ef 0 (mi) •• 77 ;n n~-..:J 0 .19 (mi) Crabtree Cr ' 0 ,] ,94 (mi) I
V. DEMOGRAPHIC AND PROPERTY INFORMATION
01 TOT Al POPULATION WITHIN 02 DISTANCE TO NEAREST POPULATION app. 200 ft. ONE ( 1) MILE OF SITE TWO (2lffii OF SITE THREE 1:11f]!-g5 OF SITE A. 638 · .037 1mi) 8. C. NO, OF PERSONS NO. OF ~ERSONS NO, OF PERSONS
03 NUMBER OF BUILDINGS W1THIN TWO (21 MILES OF SITE 04 DISTANCE TO NEAREST OFF·SITE BUILDING
514 .114 app. 600 ft. (mi)
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Th°I~LAt§N ~THm~g;r OF f~~1°cfen'tia'.Icrlpc'oflffiw-ftt1'ioQ'ffi:gf~~thdf·· 'Mb'fri.'1~1'!'T~ ur~e:} There are a few
service-oriented businesses and industrial sites which manufacture and distribute I
building.11aterials. Population density is low. Wells have a generaly low yield and
soils are unfavorable·for the operation of septic systems. I
EPA FORM 2070·13 (7•81) I
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POTENTIAL HAZARDOUS WASTE SITE I. IDENTIFICATION oEPA SITE INSPECTION REPORT Nt •r•1~ 88b~"!8'o':3 83 PART 5 • WATER, DEMOGRAPHIC, AND ENVIRONMENTAL DATA
VI. ENVIRONMENTAL INFORMATION
0 1 PERMEABILITY OF UNSATURATED ZONE /Cit.ck one/
D A. 1 o-6 -10-a cm/sec Kl B. 1 Q-4 -10-e cm/sec □ C. 1Q-4 -,o-3 cm/sec 0 D. GREATER THAN 10-3 cm/sec
02 PERMEABILITY OF BEDROCK (Cheek o,,e}
0 A. IMPERMEABLE 0 a. RELATIVELY IMPERMEABLE El C. RELATIVELY PERMEABLE 0 0. VERY PERMEABLE (Lenihan 10-6cm1s..:J · 110-4 -,o-6c,,..,uc) po-2 -,o-" cm1,ee1 (GrHt•rtti.n 10-2c,w1..::J
03 DEPTH TO BEDROCK Q,4 DEPTH OF CONT AMINA TED SOIL ZONE OS SOIL pH
20-30 7 UNK 'tt) (It)
06 NET PRECIPIT A TlON . 07 ONE YEAR 24 HOUR RAINFALL OB SLOPE
< (in) 3 (in)
SITE SLOPE I DIRECTION OF SITE SLOPE I TERRAIN AVERAGE SLOPE 0.4 ,. SE l Q " 09 FLOOD POTENTIAL 10
D SITE rs ON BARRIER ISLAND, COASTAL HIGH HAZARD AREA, RIVERINE FLOOOWAY SITE ISIN -YEAR FLOODPLAIN
11 OISTANCETOWETLANDS/S•"•"""mumJ 12 DISTANCE TO CRITICAL HABITAT /olMd""Q.,ed&p.cie•J
ESTUARINE OTHER > 1 (mil
A. > 2 (mi) B. ~ 1 (mi) ENDANGERED SPECIES: NA
13 LAND USE IN VICINITY.
DISTANCE TO:
RESIDENTIAL AREAS; NA TJONAUST ATE PARKS, AGRICULTURAL LANDS COMMEACIAUINOUSTRIAL FORESTS, OR WILDLIFE RESERVES PRIME AG LANO AG LANO
app . 600 ft.
A. . 114 (mi) . B. .19 (ml) C. NA (ml) 0 . .25 (ml)
14 DESCRIPTION OF SITE IN AELA!10N TO SURROUNDING TOPOGRAPHY
Relief at the site ranges from 385-365 ft. above mean sea level (20) . A railroad spur runs southwest across· the site. The area southeast of the spur, including the old Cellon treatment and lagoon area, drain to Koppers Pond. North and west of this spur, the site drains to a ditch which flows east under the railroad tracks toward Hwy. 54. Facility slope between the lagoon areai!/'115) and the north shore of Koppers Pond (B15) = (368-350) ~ 500 ft.= 0.4%. The terrain average slope between _the north shore of Koppers Pond and Medlin Pond = (368-350)/1000 ft. = 1.8%.
VII. SOURCES OF INFORMATION rc,r.,p,clllc,.1.,,ncn. ,.g .. ,111• /U-,. utnp1e1n~•ia. ,.potts/
References l,3,5,8,13,17,20-22,26-38,40,42,43,46,47.
EPAF0RM2070 13(7 811
oEPA POTENTIAL HAZARDOUS WASTE SITE I. IDENTIFICATION
SITE INSPECTION REPORT 01 STATE I 02 SITE NUMBER
"" n nn1?nn1A1 PART 6 ·SAMPLE AND FIELD INFORMATION
II. SAMPLES TAKEN
01 NUMBER OF 02 SAMPLES SENT TO 03 ESTIMATED DATE SAMPLE TYPE SAMPLES TAKEN RESULTS AVAJl..ABLE
GROUNDWATER off.-.si tE 50 State Lab. of Public Health, NC DHR available
SURFACE WATER
WASTE
AIR
RUNOFF
SPILL
SOIL
VEGETATION
OTHER
Ill. FIELD MEASUREMENTS TAKEN
01 TYPE 02 COMMENTS
IV. PHOTOGRAPHS AND MAPS
01 TYPE Q{GAOUNO O AERIAL I 02 IN CUSTODY OF NC I "H:k'I .n unn: ~LLe
(N1m11 o/ o,r,•rlilat,o,, or rldlvldv.lJ
03 MAPS 04 LOCATION OF MAPS ,
Xl YES NC CERCLA Unit Files, Raleigh, NC
· 0 NO
V. OTHER FIELD DATA COLLECTED (Prov1c1,,..,,,.11v,11mr1pr10nJ
12-17-87 6 wells sampled 6 P&T + IPE (2 wells)
6 Total inorganic -
6 Extractables -
6 PCP (to 1 ppb) -
03-20-87 13 wells sampled 13 P&T + IPE (4 wells)
13 PCP (to 1 pj)b) + PCP (7 wells)
VI. SOURCES OF INFORMATION /Chu sp1µ;;,1;,;,.,18,..,,c<tS. e.11 .. slate ,,16s, umpi6~n~lys,s, reports/
•Laboratory Results: Off-site groundwater samples collected 12-17-<>o, u.>-'ZU-8/.
NC State Laboratory of Public Health, Raleigh, NC. Appendix B, Site Investigation
Report: Koppers Co. Inc. May 1987. Pat DeRosa, NC CERCLA Unit, Raleigh, NC.
EPAFORM2070•13 7•81
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I POTENTIAL HAZARDOUS WASTE SITE I. IDENTIFICATION
oEPA SITE INSPECTION REPORT 01 STATE 102 SITE NUMBER NC D 003200383 PART 7-OWNER INFORMATION
II. CURRENT OWNER(S) PARENT COMPANY /llawlic•bleJ
I OINAME 02 D+ B NUMBER 08 NAME 09 O+B NUMBER
Koppers Co_ . Inc_ Koppers Co. Inc.
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03 STREET AOORESS/P.0. 8o•. RFD•. •re./ r•SICCOOE 10 STREET AOORESSrP.O. Bo•. RFDI, •re,) r 1 ~IC CODE P.O. Box A 436 Seventh Ave.
05CITY ·r6~2TE 07 ZlPCOOE 12CHY 113STATE 14 ZIP CODE
-Morrisville 27560 Pittsburgh PA 15219
OINAME 02 O+B NUMBER 06 NAME 09 D+B NUMBER I
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Unit Structures, Inc. Unit Structures, Inc.
OJ STREET ADORESSrP.O. Bo•. RFD•. ,rc.J 104SICCOOE 10 STREET AOORESS(P.0. Bo•. RFD•. ,1c.J 111SICCODE Hwy. 54 West P.O. Box 23215
05 CITY 106STATE 07 ZIP CODE 12CITY 11~ATE 14ZlPCODE Morrisville NC 27560 Louisville 40223
01NAME 02 O+B NUMBER 08NAME 09 D+B NUMBER
I 03 STREET AODRESSrP.0. Bo,. RFOI, •le,/ 104 SIC CODE 10 STREET ADDRESS (P.O.&•." RFOI, •tc.} 111SICCOOE
I 05 CITY 106STATE 07 ZIPCODE 12CITY ]13 STA~E 1 ◄ZIPCOOE
01 NAME 02 O+B NUMBER 08 NAME 09D+BNUMBER
I 03 STREET AOORESS/P.0. Bo•. RFDII, elc.J 104 SIC CODE 10 STREET AOORESS/P.O. Bo,, RFDII, elc./ r1~CCODE
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05CITY . 106STAT 07 ZIP CODE 12 CITY 113 STATE U ZIP CODE
Ill. PREVIOUS OWNER(S) rtisr1n<»r,ecer,trn11, IV. REAL TY OWNEA{S) /If i,,p1,cebie; hi moat ,ece,., fJrrl/
OINAME 02 D+B NUMBER OlNAME 02 o+e NUMBER
I Unit Structures-Inc.
03 STREET AODRESS/P.O. fJo•. RFD,, etc./ I o◄ s'.c co.oE 03 STREET AODRESS(P,O. Bo,, RFD,. •re./ . , I?◄ SIC CODE
P.O. Box 23215
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05 CITY 106:TE 07 ZIP CODE 05CITY 106 STATE 07 ZIP CODE
T-•,.:--~--:11,.._ ,In??"<
01NAME 02 O+B NUMBER 01NAME 02 D+B NUMBER
r,..,..,.. • T. ; "~ I 03 STREET ADOAESSfP.0. Bo•. RFD•. etc.} 10◄ SIC CODE 03 STREET ADDRESS (P.O. 8o•. RFD II, etc./ 10◄ SIC CODE
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05CITY 1°6STAT~ 07 ZIP CODE 05CITY 106STATE 07 ZIP CODE
01·NAME 02 D+B NUMBER 01 NAME 02 o+e NUMBER,
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03 STREET ADOAESS(P.0. &,, RFQ.11, etc.J lo~ s1ccooE 03 STREET ADDRESS tP.0. Bo•. RFD II, erc.J 10◄ SICCOOE
05CITY 106STATE 07 ZIP CODE 05 CITY 1°6STATE 07ZIPCODE
I V. SOURCES ·oF INFORMATION (C/lea(JeCIIIC ,ere,ences, e.o st•te /Mu, •.n1P'-e,..,..,1$, reporls/
References 40,2
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EPA FORM 2070•13 (7•61)
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POTENTIAL HAZARDOUS WASTE SITE I. IDENTIFICATION &EPA SITE INSPECTION REPORT 01 STATEI02 SITE NUMBER NC D003200383 PART 8 • OPERATOR INFORMATION I II. CURRENT OPERATOR /Pro>rld• If ditt•rent lrom o ... n..,} OPERATOR'S PARENT COMPANY f/fer,(lNc•bl•I 01 NAME /°2 O+B NUMBER 10NAME r 1 O+B NUMBE~
TTnit Structures I 03 STREET ADDRESS (P.O.&•. RFDII, .,c,J 104 SICCOOE 12 STREET ADDRESS (P.O. &u. RFD#, etc.J r3SlCCODE
Hwv. 54 west
05CffY ~: STATEI07 ZIP CODE 14CITY r 5 STATE 116 ZIP CODE Morrisville C 27560 I
08 YEARS OF OPERATION I 09 NAME OF OWNER 1986-Unit Structures/Koppers I Ill. PREVIOUS OPERA TOR($) (Lisi mo&!,~..,, first; PfDvld• only /ldllferM/ lrom owner/ PREVIOUS OPERATORS' PARENT COMPANIES r1t11PP1k•bl•J
01NAME I 02 D~B NUMBER 10NAME 111 D+BNUMBER
Kon=rs Co. Inc. I 03 STREET ADDRESS /P.O. Ba•. RFOI, ere./ 104 SIC CODE 12 STREET ADDRESS (P.O. Bo•. RFDI, etc.} 113 SIC CODE 436 Seventh Ave.
OS CITY r•sr,r,
1
o7ZIPCOOE 14CITY r5STATE
1
16ZIPCODE Pittsburgh PA 15219 I
OB '(EARS OF OPE~TION I 09 ~AME OF OWNER OU RING THIS PERIOD
1962-1986 Kon=rs Co. Inc.
01NAME I020+BNUMBER 10NAME I" O+B NUMBER Unit Structures, Inc.
03 STREET AODRESS/P.O. &11. RFDI, •le.} 104 SIC CODE 12 STREET ADDRESS (P.O. 8o•, RFOI, •tc,J 1'3 SICCOOE Hwy. 54 West
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05CITY 1·06STATEI07 ZIP CODE 14CITY r5 STATE
1
, a ZIP CODE Morrisville NC 27560
08 YEARS OF OPERATION I 09 NAME OF OWNER DURING THIS PERIOD
1959-1962 Unit Structures
I
01 NAME I 0~ 0+ B NUMBER 10NAME ·111 D+BNUMBEA Cary Lumber Co. I 03 STREET AODAESS{P.O. Bo.c, RFDI, •le.} 104SICCOOE 12 STREET ADDRESS (P.O. Bo•, RFOI, ere.} 113 SIC CODE
05 CITY re STATEI07 ZIPCOOE 14CITY -115 ~TATEi 16 ZIP CODE I
08 ~EA.RS OF OPEf'.'ATI~ I 09 NAME OF OWNER DURING THIS PERIOD
?-1959 I IV. SOURCES OF INFORMATION 1c1t• wKiflc ,.,.,..,cu .•. 0., 11e1e rr.,. sample .,..,sis. ,.pO(f~/
References 40,2
I
EPA FORM 2070-13 (7•81)
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I POTENTIAL HAZARDOUS WASTE SITE I. IDENTIFICATION oEPA SITE INSPECTION REPORT 01 STATEb2 SITE NUMBER ·
NC 003200383 PART 9· GENERATOR/TRANSPORTER INFORMATION
II. ON•SITE GENERA TOR
I 01 NAME 02 O+B NUMBER
I
OJ STREET ADDRESS (P.O. 8o•. RFDI, •tc./ I 04SICCODE
05 CITY 06 STATE 07 ZIPCOOE
I Ill. OFF-SITE GENERATOR(S)
01NAME 02 D+B NUMBER 01NAME 02 O+B NUMBER
I OJ STREET ADDRESS (P.O. 6o•, RFDII, etc.} I 04 SIC CODE 03 STREET ADDRESS (P.O. &u, RFOI, •tc.J 04 SIC CODE
I
05C1TY 06 STATE 07 ZJPCOOE OS CITY 1°6STATE 07 ZIP CODE
01NAME 02 D+B NUMBER 01NAME 02 D+B NUMBER
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03 STREET ADDRESS (P.O. ao., RFD,. •tc,J I 04 SIC CODE 03 STREET ADDRESS /P.O. Ba•, RFD 1, •rc.J 04 SIC CODE
05 CITY 06 ST A TE 07 ZIP CODE OS CITY 1°6 STATE 07 ZIP CODE
IV. TRANSPORTER(S)
01 NAME 02 D+B NUMBER 01 NAME 02 O+B NUMBER
I 03 STREET ADDRESS (P.O. Bo•, RFD1,,,rc.J I 0,4 SIC CODE 03 STREET ADDRESS (P.O. 6o•. RFDI, e/c.} 04 SIC CODE
I
05 CITY 06 STATE 07 ZlPCODE 05 CITY 1°6 STATE 07 ZIP CODE
01NAME 02 0+8 NUMBER 01NAME 02D+BNUMBER
I 03 STREET ADDRESS (P.O. Bai. RFD~, •tr;./ I 04 S_IC CODE 03 STREET ADDRESS /P.O. Boi. RFDt1, •1,;,J 04SICCODE
I
05CITY 06STATE 07 ZIP CODE 05 CITY 1°6STATE 07 ZIPCOOE
.
V. SOURCES OF INFORMATION /CW.1PKll1t;r•f•••,,,m. "-II 1f•t• lh1 ... mol• .,,-,y$l1. "'P<lf/lJ
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EPA FOAM 2070•13 (7•81)
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POTENTIAL HAZARDOUS WASTE SITE I. IDENTIFICATION &EPA SITE INSPECTION REPORT 01 STATE102 SITE NUMBER
PART 10 -PAST RESPONSE ACTIVITIES r-.Tr' D O:"i-----:i I 11. PAST RESPONSE ACTIVITIES
01 0 A. WATER SUPPLY CLOSED 02 DATE 03AGENCY 04 DESCRIPTION I
01 D B. TEMPORARY WATER SUPPLY PROVIDED 02 DATE 03AGENCY 04 DESCRIPTION I 01 0 C. PERMANENT WATER SUPPLY PROVIDED 02 DATE 03 AGENCY 04 DESCRIPTION
01 0 0. SPILLED MATERIAL REMOVED 02 DATE 03AGENCY I
04 DESCRIPTION
01 ~ E. CONT AMINA TED SOJL REMOVED 02 DATE 03AGENCY I 04 DESCRIPTION .
Aoril and Mav 1980; November 1980; July 1986
01 □ F. WASTE REPACKAGED ' 02 DATE 03AGENCY 04 DESCRIPTION I
01 D G. WASTE DISPOSED ELSEWHERE 02 DATE 03 AGENCY 04 DESCRIPTION I
01 0 H. ON SITE BURIAL 02 DATE 03AGENCY 04 DESCRIPTION I
01 0 I. IN SITU CHEMICAL TREATMENT 02 DATE 03AGENCY 04 DESCRIPTION I
01 0 J. IN SITU BIOLOGICAL TREATMENT 02 DATE 03 AGENCY 04 DESCRIPTION
I 01 0 K. IN SITU PHYSICAL TREATMENT 02 DATE 03AGENCY 04 DESCRIPTION
01 0 L. ENCAPSULATION 02 DATE 03AGENCY I 04 DESCRIPTION
01 0 M. EMERGENCY WAf>TE TREATMENT 02 DATE 03AGENCY 04 DESCRIPTION . I
01 0 N. CUTOFF WALLS 02 DATE 03AGENCY 04 DESCRIPTION I
01 0 0. EMERGENCY DIKING/SURFACE WATER DIVERSION 02 DATE 03AGENCY 04 DESCRIPTION I
01 0 P. CUTOFF TRENCHES/SUMP 02 DATE 03AGENCY 04 DESCRIPTION I
01 0 0. SUBSURFACE CUTOFF WALL 02 DATE 03AGENCY 04 DESCRIPTION I EPA FORM 2070•13 /7•81 J
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I POTENTIAL HAZARDOUS WASTE SITE I. IDENTIFICATION &EPA SITE INSPECTION REPORT . 01 STATE! 02 SITE NUMBER
PART 10 • PAST RESPONSE ACTIVITIES Nr D 003200383
II PAST RESPONSE ACTIVITIES (conr1n1Je<11
I 01 0 A. BARRIER WALLS CONSTRUCTED 02 DATE 03AGENCY
04 DESCRIPTION '
I 01 0 S. CAPPING/COVERING 02 DATE 03AGENCY
04 DESCRIPTION
01 0 T. BULK TANKAGE REPAIRED ' 02 DATE 03AGENCY
I 04 DESCRIPTION '
01 0 U.GROUTCURTAtNCONSTRUCTED 02 DATE OJ AGENCY 04 DESCRIPTION I 01 0 V. BOTTOM SEALED 02 DATE 03AGENCY
04 DESCRIPTION
I 01 0 W. GAS CONTROL 02 DATE 03AGENCY .
04 DESCRIPTION
I 01 0 X. FIRE CONTROL 02 DATE OJ AGENCY
04 DESCRIPTION
I 01 0 Y. LEACHATE TREATMENT 02 DATE OJ AGENCY
04 DESCRIPTION
I 01 0 Z. AREA EVACUATED 02 DATE 03 AGENCY
04 DESCRIPTION
01 0 1 . ACCESS TO SITE RESTRICTED 02 DATE 03AGENCY
I 04 DESCRIPTION
01 0 2. POPULATION RELOCATE,0
04 DESCAIPTJON
02 DATE 03 AGENCY
I '
01 0 3. OTHER REMEDIAL ACTIVITIES 02 DATE 03AGENCY
04 DESCRIPTION
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Ill. SOURCES OF INFORMATION /Cit• Si.>•cif/c r•t•r•nc•s. • g • 51•!• f~as. J41T1111• 1nalysls. r•parn}
References 2,5
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EPA.FORM 2070•13{7 81)
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POTENTIAL HAZARDOUS WASTE SITE I. IDENTIFICATION oEPA SITE INSPECTION REPORT 01 STATE I 02 SITE NUMBER NC D 003200383 PART 11 • ENFORCEMENT INFORMATION
II. ENFORCEMENT INFOAMA TION
01 PAST REGULATORY/ENFORCEMENT ACTION O YES )Ii NO
02 DESCAIPTK)N OF FEDERAL STATE. LOCAL REGULATORY/ENFORCEMENT ACTION
'
Ill. SOURCES OF INFORMATION {C,t• spec1to:rel11reru;u, "·!1-, st•t11 f~es. Hmplean.alys,s. ••POrls/
EPA FORM 2070-13{7-81)
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SITE SAFETY PLAN
A. GENERAL INFORMATION
Site Name Koppers Inc.
Location Morrisville, NC
Purpose of Visit __ ___;PA X ---SI
Site Number NC D003200383
Date 12/15/86
Other ---
Proposed Date of Inspection 12/17/86 ----'-.C..:....:....:. ________ _
Date of Briefing 12/15/86 --~~--------
Priority Ranking ---
Site Investigation Team
Personnel
Pat DeRosa
Mark Durway
Low X Medium ---High ---
Responsibilities
Sampling
Sampling
B. SITE/WASTE CHARACTERISTICS
X Liquid Solid --X Sludge Gas ---Waste Type(s)
Characteristics Ignitable Radioactive Corrosive -----;--;v-o· 1a tile --~-_x __ Toxic Reactive __ Other
List Known or Suspected Hazards (physical,chemical biological or radioactive)
on Site and their toxicological effects. Also, if known, list chemical amotmts
HAZARD
Pentachlorophenol
Isopropylether
EFFECT(S)
0.5 mg/m -TLV skin, light brown solid with
a pungent odor when hot
250 ppm -TLV
colorless liquid with ether odor
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Facility Description: Size 20-25 acres Buildings 6 buildings
Disposal Methods Being Investigated land farming of wastes
Unusual Features on Site (dike integrity, power lines, terrain etc.):
3 acre pond on site
History of the Site: This site has been in use since 1961. Waste materials
from pentachlorophenol treatment were land farmed and disposed of in on-site
pits from 1968-1975. A cleanup involving removal of 220 tons of contaminated
soil was done in 1980. PCP has been identified in pond sediment and wells
on site (6.4 mg/kg in pond).
C. HAZARD EVALUATION
Sampling at this time is to consist of off-site private drinking water wells.
This sampling can be done in Level D protection. Polyethylene gloves and
goggles should be worn ·while pipetting acid for the water samples.
D • WORK PLAN INSfRUCTION ·
Map or Sketch Attached? in file
Perimeter Identified? yes Command Post Identified? no Zones of Contamination Identified? yes
Personal Protective Equipment
Level of Protection A B C X D ---
Modifications goggles and gloves need to be worn when pipetting acid.
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Hospital (Address and·Phone Number)
Rex Hos ital
Blue Ridge Road, Raleigh, NC
Emergency Transportation Systems (Phone Numbers)
Fire use 911
Ambulance use 911
Rescue Squad use 911 ---------------
Emergency Route to Hospital Take Hwy. 54 to 1-40, take 1-40 towards Durham.
Get off on Wade Avenue exit. Get off on Blue Ridge Road exit. Take a left at
top of exit ramp, hospital will be on the right in 1-2 miles.
PREVAILING WEATHER CONDITIONS AND FORECAST partly cloudy with a high in
the u er 50's .
EQUIPMENT CHECKLIST
Air ,purifying respirator
Cartridges for respirator
3M 8710 Respirator
X First Aid Kit
X 3 gal. Distilled H20
X Personal Protective _:..;,___ 02 Indicator Clothing
---Detector Tube & Pump
Eye Wash Unit
---H Nu
Boots or Boot Covers
----Coveralls (tyvek)
X Eye Protection ----Hard Hat ___ pH Meter
Explosimeter
---Radioactive Monitor X Decontamination
ASHEVILLE
704-255-4490
CHARLOTTE
704-379-5827
DURHAM
1-800-6 72-1697
GREENSBORO
919-379-4105
1-800-722-2222
Materials.
Poison Control Center -State Coordinator
Duke University Medical Center
Telephone: .l-800-672-1697
Box 3024
Durham, NC 27710
Western NC Poison HENDERSONVILLE
Control Center 704-693-6522
Memorial Mission Hosp. Ext. 555, 556
509 Biltmore Ave. 28801
Mercy Hospital HICKORY
2001 Vail Ave, 28207 704-322-6649
Duke Univ Medical Center JACKSONVILLE
Box 3007, 27710 919-577-2555
Moses Cone Hospital WILMINGTON
1200 N. Elm St, 27420 919-343-7046
Margaret R. Pardee
Memorial Hospital
Fleming St., 28739
Catawba Mem. Hosp.
Fairgrove Chur. Rd 28601
Onslow Mem. Hospital
Western Blvd. 28540
New Hanover Mem. Hospital
2131 S. 17th St, 28401
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Surveillance Equipment:
H Nu ----Explosimeter ---TLD
Detector Tubes and Pumps
02 Meter
(Radiation Monitor)
Decontamination Procedures
Level A
Level B ---
Level C ---
Segregated equipment drop, boot cover and glove wash, boot
cover and glove rinse, tape removal, suit and hard hat
removal, SCBA backpack removal, inner glove wash, inner
glove removal, inner clothing removal, field wash, redress
Segregated equipment drop, boot cover and glove wash,boot
cover and glove rinse, tape removal. boot cover removal
outer glove removal, suit/safety removal, SCBA backpack
removal, inner glove wash, inner glove rinse, facepiece
removal, inner glove removal, inner clothing removal, field
wash, redress.
Segregated equipment drop, boot cover and glove wash, boot
cover and glove rinse, tape removal, boot cover removal,
outer glove removal,suit/safety boot wash, suit/safety boot
rinse lCanister or Mask Change), safety boot removal, splash
suit removal, inner glove wash, inner glove rinse, facepiece
removal, inner glove removal, inner clothing removal. field
wash redress.
X Level D Segregated equipment drop. boot and glove wash, boot and
glove rinse. ---
Modifications ---------------------------
Work Schedule/ Limitations __ s_am_p~l_1_·n~g~o_f_r_e_s_id_e_n_t_i_a_l_w_e_l_ls ________ _
I EMERGENCY PRECAITTIONS
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Acute Exposure Symptoms
skin
eyes
inhalation
ingestion
First Aid
soap and water wash immediately
flush immediately
fresh air and artificial resp.
medical attention
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''".'.'·. I' "'
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EPA CHEMICAL PROFILE·,:·,
INTERIM· ,, ....
, , --•',. \ ~ :i'' 7 ' I ' -' • -~ .""~--~;.' __ , ~,:: · · · Date: Octob~·r; 31'; 1985
Revision:
CHEMICAL IDENTITY. c:-PENTACHLOROPHENOL
·. "'·' ·_}(,·:_: .... .-::;;.,::~~---
CAS Registry Number: 87-86-5
Synonyms: 2, 3, 4 ,5, 6-Pentachlorophenol; Chem-Tel; Chlorophen; Dowii::ide 7;
Durotox; EP 30; Fungifen; Grundier Arbezol; Lauxtol; Lauxtol A; Liroprem;
NCI-C54933; PCP; Penchlorol; Penta; Penta-Kil; Pentachlorophenate; Pentacon;
J Pentasol; Penwar; Peratox; Permacide; Permagard; Permasan; Permatox DP-2;
Permite; Santophen; Santophen 20; Sinituho; Term-I-Trol; Thompson's Wood Fix;
Weedone; Phenol, Pentachloro-
Chemical Formula: c6ttc1 5o
Molecular Weight: 266. 35
SECTION I --HAZARDOUS INGREDIENTS/IDENTITY INFORMATION
OSHA PEL: TWA 500 µg/m' (NIOSH/OSHA 1978, p. 148)
ACGIH TLV: TWA 0.5 mg/m'; STEL 1.5 mg/m' (skin) (*ACGIH 1982) -.:•.
IDLH: 150 mg/;., (NIOSH/OSHA 1978, p. 148)
Other Limits Recommended: Not Found
SECTION II --PHYSICAL/CHEMICAL CHARACTERISTICS
Boiling Point: 588°F, 309°C (*Merck 1976)
Specific Gravi~ (H20=l): ;1.978 at 2tC/4°C (*Merck 1976)
Vapor Pressure (mmHg): 0.0002 at 20°C (NI0SH/OSHA 1978, p. 148)
Melting Point: 374°F, 190°C (*Merck 1976)
Vapor Density (AIR=l): 9.20 (*Verschueren 1983)
Evaporation Rate (Butyl acetate=l): Not Found
Solubility in Water: 0.002 g/100 ml at 30°C (*Spencer 1982)
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CAS Registry Number: 87-86-5
Page 2 of 4
PENTACHLOROPHENOL
SECTION 11 --PHYSICAL/CHEMICAL CHARACTERISTICS (Continued)
Appearance and Odor: Needle-like crystals (*Merck 1983). Colorless crystals (pure); dark greyish powder o"r flakes (crude product) (''Spencer
1982). Phenolic odor ("'Spencer 1982) and also a very pungent odor when hot (*Merck 1976).
SECTION 111 --FIRE AND EXPLOSION HAZARD DATA
Flash Point (Method Used): Not Found
Flammable Limits: This material may burn but may not ignite readily (*DOT 1984). Under normal conditions it is not flammable c-:,cHil.IS 1978). LEL: Not Found
UEL: Not Found
Extingu.ishing Methods: Water spray may be used to extinguish fire. Dry chemicals, foam, or carbon dioxide can also be used. Use water to keep fire-exposed containers cool ("'NFPA 1978).
Special Fire Fighting Procedures: Full protective clothing:
self-contained breathing apparatus, rubber gloves, boots, and bands around legs, arms, and waist. No skin surface should be exposed (*~'FPA 1978). If protective clothing becomes soaked it must be replaced immediately (*Clayton and Clayton 1982).
Unusual Fire and Explosion Hazards: Liquid must be moderately heated before ignition will occur (*NFPA 1978).
SECTION IV --REACTIVITY DATA
Stability: Unstable:
Stable: Yes (*NFPA 1978)
Conditions to Avoid: Prolonged heating above 200°C produces trace amounts of octachlorodibenzo-para-dioxin (*IARC 1972-1985).
Incompatibility (Materials to Avoid): Contact with strong oxidizers may cause.fires or explosions (*NIOSH/0SHA 1981).
Hazardous Decomposition or Byproducts:
it emits highly toxic fumes of chlorides
chlorinated phenols, and carbon monoxide
decomoosition (*NIOSH/OSHA 1981). . .
When heated to decomposition,
('''Sax 1975). Hydrogen chloride,
may be released upon
.a::: .. , ......... . 1··········· ,;_;-;;;,;-;;-:-
·.·::·:·:·-·.·
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CAS Registry Number: 87-86-5
Page 3 of 4
PENTACHLOROPHENOL
SECTION IV --REACTIVITY DATA (Continued)
Hazardous Polymerization: May Occur: Not Found
May Not Occur: Not Found
Conditions to Avoid: Not Found
I SECTION V --HEAL TH HAZARD DATA
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Routes of Entry: Inhalation:
Skin: Yes
Ingestion:
Yes (*Clayton and Clayton 1982)
(*Clayton and Clayton 1982)
Yes (*Clayton and Clayton 19.82)
Health Hazards· (Acute, Delayed, and Chronic): Poisonous if swallowed or inhaled (*DOT 1984). Very toxic: probable oral lethal dose (human) 50-500 mg/kg (1 teaspoon to l ounce) for 70 kg person (150 lbs.) ("'Gosselin 1976). Lethal oral doses in humans have been reported at 29 mg/kg (*NI0SH 1985). Causes lung, liver, and kidney damage, and contact dermatitis (*Herek 1976). Inhalation results in acute poisoning centering in circulatory system with accompanying heart failure. Also, visual damage, scotoma, inflammation of conjuctiva, cornea opacity, co~nea numbness and slight pupil dilation are experienced C''ACGIH 1980). Repeated exposure to commer.cial material preceded aplastic anemia, pure red cell aplasia, Hodgkins disease and acute leukemia (*Roberts 1983).
Signs and Symptoms of Exposure: Ingestion causes increased then decreased respiration, blood pressure, and urinary output; fever; increased bowel action; motor weakness; collapse with convulsions; and death (*Herek 1976). Inhalation of dust and mist cause violent sneezing and coughing (*USEPA, AWQC 1980). Liquid or solid dermal contact causes smarting of skin and first-degree burns on short exposure; may cause secondary burns on long exposure (*CHRIS 1978).
Medical Conditions Generally Aggravated by Exposure: Kidney and liver diseases (*Cfayton and Clayton .1982") .
. Emergency and First Aid Procedures: Hove victim to fresh air. Remove and isolate contaminated clothing and shoes at the site. In case of contact with material; immediately flush skin or eyes with running water for at least 15 minutes (*DOT 1984). Bathe and shampoo contaminated skin and hair promptly with soap and water. Flush eyes ,dth copious amount of clean water. Systemic poisoning: reduce elevated body temperature by physical means. (Do not administer aspirin.) Adrninis ter sponge baths and cover with low-temperature blankets (*~organ 1982).
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CAS Registry Number: 87-86-5 Page 4 of 4
PENTACHLOROP.HENOL
SECTION VI --USE INFORMATION
Wood preservative; soil fumigant for termites, herbicide, fungicide, · slimicide, algicide, antibacterial agent in disinfectants and cleaners ('~SRI) .
SECTION VI I --PRECAUTIONS FOR SAFE HANDLING AND USE (Steps to be Taken in Case Material is Released or Spilled)
Avoid inhalation. Wear proper respiratory protection and protective clothing (see Section V above). Avoid contact with solid and dust. Keep unnecessary people away (*CHRIS 1978) .. · Ventilate area of spilL Collect spilled material in most convenient and safe manner and deposit in sealed containers for reclamation or disposal in secure sani1:ary landfill. Liquid should be absorbed in vermiculite, dry sand, earth, or similar material (*NIOSH/OSHA 1981).
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:is oxides of
•· pin.sties '
'1iou]d stay
l ,te ill'C.'.l.
1 1 cvapo-
Sttch as a •1cd in a
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1·0.nmon name: Isopropyl ether
,·,,nnula: ((Cl-l"),Cl·I),O
ISOPROPYL ETHER / 505
Synonyms: Diisopropyl ether; 2-isopropoxypropanc
CAS No.: 108-20-3
Carcinogen: N / A
II.REGULATORY INFORMATION
!lawrdous substance: No
Haznrrlous waste: No
DOT Hazard Class: Flammable liquid
111. PHYSICAL CHARACTERISTICS
Boiling point: G8.9 C (156 F)
Specific gravity: 0.7
Vapor density: At boiling point, 3.5
Melting point: -85 C (-121 F)
Vapor pressure: At 20 C, 119 mm Hg
Solubility in water: At 20 C, 0.2 g/l00g water
Evaporation rate: 8
Appearance and odor: Colorless liquid with a sharp, sweet, ether-•
like odor · ·
IV. PHYSICAL HAZARDS
Flash point: -27.8 C (-18 F)
Autoignition temperature: 443 C (830 F)
Flammable limits in air(% by vol.): Lower: 1.4; Upper: 7.9
Extinguishants: Dry chemical, alcohol foam, or carbon dioxide
V. HEAL TH HAZARDS
Stong vapor concentrations can cause irritation of the· eyes and
nose. Animal experiments have . indicated the possibility of
drowsiness, dizziness, and unconsciousness. Long-term exposure
may cause dryness and irritation of the skin.
VI. EMERGENCY FIRST AID
Eyes: Wash with large amounts of water, lifting the lids occasional-
ly. Get medical attention as soon as possible. Do not wear
contacts when working with the substance.
Skin: Wash with soap or mild detergent. Remove contaminated
clothing. If there is skin irritation, get medical attention.
Breathing: M.ove patient to fresh air. Perform artificial respiration
if needed. Keep patient warm and at rest. Get medical attention
as soon as possible.
. ·-·--~ -·---· •' ·•:1•,:,..,
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506 / CHEMICAL SAFETY DA TA
Swallowing: Get medical attention immediately. Give large ~uard:• ties of water, and then induce vomiting.
VII. PERMISSIBLE EXPOSURE LIMIT OSHA TWA: 500 ppm ACGIH TLV: 250 ppm ACGIH: 310 ppm IDLH: 10,000 ppm
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TO:·
FROM:
RE:
3U December 1~86
File
Mary Giguere l\R<':
Koppers Inc, NC D003200383
Site Safety Plan
On January 7, 1987 Pat DeRosa and Mark Durway are planning to tour
the Koppers Inc. Morrisville site. Samples are not going to be taken during
the visit. Level D protection will be adequate for the visit. Rubber boots
are to be worn when touring the site.
MG/tb/024lb
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2 February 1987
TO: File
FROM: Mary Giguere f'<'V
RE: Koppers Inc. Morrisville site
NC D003200383
All samples collected during a site investigation will be preserved by
storing them on ice. Water samples for metal and volatile organics analyses
should also be preserved with acid unless they contain visible sediment.
The metals samples should be preserved with nitric acid to a pH of less than
2 but greater than 1. To do this start by adding 3 ml. of nitric acid to the
sampling container. After collecting the sample, check the pH, if more acid
is needed add it and note how much was added. Put a check mark on the cap of
the metal samples that have been preserved. If more than 3 mls. of acid have
been added indicate the total amount of acid added on the sample container cap.
For the VOA samples 4 drops of HCl should be added before the sample
is collected. Collect the sample as usual.
Goggles and gloves will be worn while measuring acids and collecting
samples. Pasteur pipets will be used for measuring the hydrochloric acid.
Graduated pipets will be used for nitric acid. Pipets will be rinsed and then
disposed of.
Samples are to be taken for phenol analysis. These samples shall be
collected in a 1-liter amber glass container with a Teflon lined closure.
Sulfuric acid will be added to adjust the pH to less than two.
!,1;/tb/0354b
3/87
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