HomeMy WebLinkAboutNC0003760_Wasteload Allocation_19900613NPDES DOCUMENT :SCANNING COVER SHEET
NPDES Permit:
NC0003760
DuPont Kinston facility
Document Type:
Permit Issuance
.'''
Wasteload Allocation
Authorization to Construct (AtC)
Permit Modification
Complete File - Historical
Engineering Alternatives (EAA)
Correspondence
Owner Name Change
Approval
Instream Assessment (67b)
Speculative Limits
Environmental Assessment (EA)
Document Date:
June 13, 1990
This document is printed on reuse paper - ignore any
content on the resrerse side
0o-re : 3 Lot -As
NPDES WAS I LOAD ALLOCATION
PERMIT NO.: NC0003760
PERMIFLEE NAME: E. I. Dupont de Nemours and Co. / Kinston
Facility Status: Existing
Permit Status: Renewal
Major Minor
Pipe No.: 001
Design Capacity: 3.6 MGD
Domestic (% of Flow): 4 %
Industrial (% of Flow): 96 %
Comments:
Effluent characteristics based on long term average flows totaling 2.475
MGD through plant (see attached calculations)
RECEIVING STREAM: the Neuse River
Class: C-NSW
Sub -Basin: 03-04-05
Reference USGS Quad: F 29 SW (please attach)
County: Lenoir
Regional Office: Washington Regional Office
Previous Exp. Date: 4/30/90 Treatment Plant Class: Class 2
Classification changes within three miles:
none
Requested by:
Prepared by:
Reviewed by:
w(GL
Rosanne Barona
Dg FT E r
Modeler
Date Rec.
#
.Torn
3-zd_ r'0
56so
Drainage Area (mi2 ) a55 o .3 Avg. Streamflow (cfs): l5 I LI-
7 Q10 (cfs)M, 1 Winter 7Q10 (cfs) I , (p 30Q2 (cfs)
Toxicity Limits: IWC ! . I % Acute hronic
Instream Monitoring:
Parameters 1ent-A DO. CUy1eUCHO ► 0,4 5 CS o
zyk
Upstream y Location C01-/-0
Location / et-n S 444-
L3 nu. dd1on571110.4'n-�
Downstream V
Effluent
Characteristics
—1
BOD5
`..' rl (EL)
NH 3-N `
b.3. (LW)
D.O. (mg/1)
—
TSS 'u
b3-3 (EL)
�, - _» , _ ',)
0 Cwo �
-
Covnp►;av�lc: CO t3
k2� , may i, Iatf
pH (SU)
\
TEE.,--ITTCH
D L13T
o .
L l m I T5 k)ir
aravli e -e0^s
re y u Ir.i-eo/
GCP3F
6Jb/ZL.r1 -
LinAt-1-5 are
.0 y 0/win/wilts
Comments:
r" r
FOR APPROPRIATE DISCHARGERS, LIST COMPLETE GUIDELINE LIMITATIONS BELOW
Effluent Characteristics
Monthly 0DailyC7
Averageaximum
M
Comments
rho 1i5
�
35`%
7/4
dointes1cafi 3o4 fP ysrmy/P
S
TS
6 3 3
l/ 9O
f (ocPsF440
_
4/4,4‘0)t (ocPsF
0 •
j- q
649
..d,a, ate°
Ize cadio ated,,,,,,,,f
.
ts--66„ eito,_ez-c-f-,4-.=&;..5-
/CPSF 55J4I Y/4V 9d
*),12,tv-tt't-"ui•-&-li
klete ,t_e‘j--(..6a64.&.
fet.e.44--gf_04.43
vi.i-E1 6;-. 0 -
'IA ifek ci.s$(.,
Type of Product Produced
Lbs/Day Produced
Effluent Guideline Reference
ro-Pirwt"- AlZe ciptoc:66,4to
arickncz,,IL
Request No.: 5650
WASTELOAD ALLOCATION APPROVAL FORM
Facility Name:
NPDES No.:
Type of Waste:
Status:
Receiving Stream:
Classification:
Subbasin:
County:
Regional Office:
Requestor:
Date of Request:
Quad:
E.I. Dupont de Nemours and
NC0003760 )Ipe 00k
4% Domestic/96% Industrial
Existing/Renewal
Neuse River
C NSW
030405
Lenoir
Washington
R. Barona
900329
F 29 SW
RECOMMENDED EFFLUENT
Wasteflow (mgd) :
BOD5 (#/day) :
NH3N (#/day) :
TSS (#/day) :
pH (su) :
Total Phosphorus (mg/1) :
EXISTING
Daily Avg
3.60
476
63.4
790
6-9
n/a
Other parameters as re-
gulated by OCPSF Subpart I:
Toxicity Requirement:
n/a
n/a
•
MONITORING
Co
NGTON OFFICE
REGULATED
Drainage area:
Summer 7Q10:
Winter 7Q10:
Average flow:
30Q2:
LIMITS
MAY 2 1990
D. E. M.
2552.3
283.10
291.60
1514
sq mi
cfs
cfs
cfs
cfs
PROPOSED
3.60 Mo. Avg.
357 Mo. Avg. EL
63.4 Mo. Avg. WQ
633 Mo. Avg. EL
6-9 Min -Max EL
2 * Mo. Avg. WQ
* T P Compliance date:
May 1, 1993
Daily Max. as per a tacked list
Chronic Ceriod. Qrterly
Upstream (Y/N): Y Location: 200 yds upstream from outfall
Downstream (Y/N): Y Location: At Planks Landing (3 mi. downstream)
COMMENTS
The following instream parameters should be monitored: Temp, DO, cond,
pH, and BOD5 during the summer months only.
Prepared by:
Juan C. Mangles ./
Reviewed by
Instream Assessment:
Regional Supervisor:
Permits & Engineering:
RETURN TO TECHNICAL SUPPORT BY:
aMc.Ctnasv•--
M1Y26W O
Date:
Date:
Date:
Date:
L/ j 21/ 40
q/acylqd
List of Chemicals
A
B
C
D
1
2
Daily Max
Units
Criteria
3
Effluent Characteristics
4
5
Acenapthene
8469
ng/I
VvQ
6
Acrylonitrile
242
ug/I
EL
7
Benzene
1 3 6
ug/I
EL
8
Carbon Tetrachloride
38
ug/I
EL
9
Chlorobenzene
28
ug/I
EL
1 0
1,2,4-Trichlorobenzene
140
uq/I
EL
1 1
Hexachlorobenzene
0.2
ug/I /
W
1 2
1 ,2-Dichloroethane
211
ug/I
EL
1 3
1 ,1 ,1-Trichloroethane
54
ug/I
EL
1 4
Hexachloroethane
54
ug/I
EL
1 5
1,1-Dichloroethane
59
ug/I
EL
1 6
1,1,2-Trichloroethane
54
ug/I
EL
1 7
Chloroethane
268
ug/I
EL
1 8
Chloroform
46
ug/I
EL/'
1 9
2-Chlorophenol
27
ug/I
'v
2 0
1 ,2-Dichlorobenzene
1 63
ug/I
EL /
2 1
1 ,3-Dichlorobenzene
44
ug/I
EL
2 2
1 ,4-Dichlorobenzene
28
uq/l
EL
2 3
1,1-Dichloroethylene
25
ug/I
EL
2 4
1,2-trans-Dichloroethylene
54
ug/I
EL
2 5
2,4-Dichlorophenol
82
ug/I
WO
2 6
1,2-Dichloropropane
230
ug/I
EL
2 7
1,3-Dichloropropylene
44
ug/I
EL
2 8
2,4-Dimethylphenol
36
uq/I
EL
2 9
2,4-Dinitrotoluene
285
ug/I
EL
3 0
2,6-Dinitrotoluene
641
ug/I
EL
3 1
Ethylbenzene
1 0 8
ug/I
EL
3 2
Fluoranthene
68
ug/I
EL
3 3
Bis(2-Chloroisopropyl)ethe
757
ug/I
EL
3 4
Methylene Chloride
89
uq/I
EL
3 5
Methyl Chloride
190
ug/I
EL
3 6
Hexachlorobutadiene
49
ug/I
EL
3 7
Naphthalene
8469
ng/I
VbQ
3 8
Nitrobenzene
68
ug/I
EL
3 9
2-Nitrophenol
69
ug/I
EL
4 0
4-Nitrophenol
1 24
uq/I
EL
4 1
2,4-Dintrophenol
1 23
ug/I
EL
4 2
4,6-Dintro-o-cresol
277
ug/I
EL
4 3
Phenol
26
ug/I
EL
4 4
Bis(2-ethylhexyl)phthalate
279
ug/I
EL
4 5
Di-n-butyl phthalate
57
ug/I
EL
4 6
Diethyl phthalate
203
uq/I
EL
4 7
Dimethyl phthalate
47
ug/I
EL
4 8
Benzo(a)anthracene
8469
ng/I
VC
Page 1
List of Chemicals
A
B
C
D
4 9
Benzo(a)pyrene ,
8469
nq/l ,'
WC)
5 0
3,4-Benzofluoranthene ''
8469
ng/I J
Vfl
5 1
Benzo(k)fluoranthene ✓
8469
ng/I v
INQ
5 2
Chrysene v
8469
ng/I \/
VW)
5 3
Acenaphthylene
8469
ng/I \
VAQ
5 4
Anthracene ✓
8469
ng/I v
VbQ
5 5
Fluorene
8469
ng/I V
VbQ
5 6
Phenanthrene
8469
WIV
WJ
5 7
Pyrene v
8469
ng/I `/
i".
5 8
Tetrachloroethylene
56
ug/I
EL
5 9
Toluene
80
ug/I
EL
6 0
Trichloroethylene
54
ug/I
EL
6 1
Vinyl Chloride
268
ug/I
EL
6 2
Total Chromium)
2587
ug/I ✓
WC)
6 3
Total Copper
362
u q/ I '
VVQ
6 4
Total Cyanide `-'^j ^1=1-,
259
uq/I ,i
VbQ
6 5
Total Lead
690
u g/ I
EL
6 6
Total Nickel
3980
ug/I
EL
6 7
Total Zinc _
2587
ug/I '
\AO
Page 2
10/89
Facility Name
Permit# OC_00 0 3-76C�
O%A 001
CHRONIC TOXICITY TESTING REQUIREMENT (QRTRLY)
The effluent discharge shall at no time exhibit chronic toxicity in any two consecutive toxicity tests,
using test procedures outlined in:
1.) The North Carolina Ceriodaphnia chronic effluent bioassay procedure (North Carolina Chronic
Bioassay Procedure - Revised *September 1989) or subsequent versions.
The effluent concentratioaat which there may be no observable inhibition of reproduction or
significant mortality is 1 • % (defined as treatment two in the North Carolina procedure
document). The permit holder shall perform quarter1v monitoring using this procedure to establish
compliance with the permit condition. The first test will be perfonved after thirty days from
issuance of this permit during the months of TC n 1` J v l O 0 tK . Effluent
sampling for this testing shall be performed at the NPtDE ermittedfinal effluent discharge below
all treatment processes. p g
All toxicity testing results required as part of this permit condition will be entered on the Effluent
Discharge Monitoring Form (MR-1) for the month in which it was performed, using the parameter
code TGP3B. Additionally, DEM Form AT-1 (original) is to be sent to the following address:
Attention: Environmental Sciences Branch
North Carolina Division of
Environmental Management
P.O. Box 27687
Raleigh, N.C. 27611
Test data shall be complete and accurate and include all supporting chemicaVphysical measurements
performed in association with the toxicity tests, as well as all dose/response data. Total residual
chlorine of the effluent toxicity sample must be measured and reported if chlorine is employed for
disinfection of the waste stream.
Should any single quarterly monitoring indicate a failure to meet specified limits, then monthly
monitoring will begin immediately until such time that a single test is passed. Upon passing, this
monthly test requirement will revert to quarterly in the months specified above.
Should any test data from this monitoring requirement or tests performed by the North Carolina
Division of Environmental Management indicate potential impacts to the receiving stream, this
permit may be re -opened and modified to include alternate monitoring requirements or limits.
NOTE: Failure to achieve test conditions as specified in the cited document, such as minimum
control organism survival and appropriate environmental controls, shall constitute an invalid test
and will require immediate retesting(within 30 days of initial monitoring event). Failure to submit
suitable test results will constitute noncompliance with monitoring requirements.
7Q10 2$ 3 . i cfs
Permited Flow 3 ( MGD Recommended by:
IWC% k • q
Basin & Sub -basin Q 30 `I 0
Receiving Str am QU. `
County " o"
Date 2oia�
**Chronic Toxicity (Ceriodaphnia) P/F att.%, n , Psi"' r , See Part , Condition
PERMIT NO.: NCO() 0 3 7o ('
FACILITY NAME- e L D1 t6/ dw
Facility Status:
(circle one)
Permit Status: /RENEWAL } MODWICA11oN UNPERWITED NEW
(circle one)
Major b` Minor.
Pipe No• 0 O
Design Capacity (MGD):
Domestic (% of Flow) -
Industrial (X of Flow):
Continents:
RECEIVING STREAM: an IAA 'canna/ 'Fr`'h� y '�o
Class-
.
C-JV51/L) k1-
euse ,ve,
Sub -Basin• o —OS
Reference USGS Quad: f
County: . �.0 D r
Regional Office: As Fa Mo
(circle ens)
Requested By: k• 8a.r0 rtfi-
Prepared By:
Reviewed By:
kotov = N/A
(please attach)
Wi WS
Date:
Date:
Date -
/3
5o
lNPDES WASTE LOAD�l C
a,
Modeler
h.
Date Rec.
TG Pvt
3.29-7o
56
5 /
I
Drainage Area (mi2 )C (9• O Avg. Streamflow (cfs)-
7Q10 (cfs) Winter 7Q10 (cfs) 30Q2 (cfs)
Toxicity Limits: IWC U % (circle one) Acute / Chronic
Instream Monitoring:
;
Parameters ;_
Upstream
Location
Lo ation
CoI Cu)
S* AY
Effluent
Characteristics
Summer
Winter
BODE (mg/I)
NHa N (mg/1)
D.O. (mg/I)
TSS (mg/1)
F. Col. (/100m1)
pH (SU)
6 _ q
--1v\rzk cakit W tu)
S t7
—F o c.)
3 2_
,
A O Cr, .w
Y\ Cu ajcn t 4
4,<c),),x11),a-
cuni\In-t:1
ATTACHMENT #2
SUBJECT: BIOCIDE SHEETS, REVISED ACTIVITY DESCRIPTIONS
FOR MINOR OUTFALLS 002 AND 003
BIOCIDE SHEETS C/x4k C-Vuta-ci'
Biocide - Betz Slimicide C-68 Worksheet Form 101 attached. This additive
was submitted and approved for use in October 1987, Ref. letter
R. Paul Wilms to J. D. Henderson dtd. 10/2/87.
Biocide - Betz C-77, C-78-BCDMH additive. Form 101 attached - Ref. letter
R. Paul Wilms to J D. Henderson 10/2/87 expressed concern for
carryover of residual chlorine from this additive. Recommended
testing was conducted. Following two months testing (results
attached) meeting was held with DEM, at which time DEM
indicated further testing was not necessary due to low chlorine
carryover and the additive was approved for use. Ref. letter dtd.
6/23/88, R.P. Wilms to K. J. Kozelski.
All cooling water is treated in the wastewater treatment system
prior to discharge.
RECEIVED
WASHINGTON OFFICE
MAY 21990
Request No.:
D. E. M.
WASTELOAD ALLOCATION APPROVAL FORM
Facility Name:
NPDES No.:
Type of Waste:
Status:
Receiving Stream:
Classification:
Subbasin:
County:
Regional Office:
Requestor:
Date of Request:
Quad:
5651
E.I. Dupont de Nemours and Co./Kinston
NC0003760 P't�C p0a.
Industrial
Existing/Renewal
UT to Neuse River
C-NSW
030405
Lenoir
Washington
R. Barona
032790
F 29 SW
RECOMMENDED EFFLUENT LIMITS
EXISTING PROPOSED
Wasteflow (mgd) :
pH (su) : 6-9
Turbidity (NTU) :
Temperature:
Metals (ug/1) :
6-9
50
32° C (MAX)
Quarterly metal
scans
3ti& 141 , Clew M,ONITOCR0NG p deJ e
Upstream (Y/N): N
Downstream (Y/N): N
Location:
Location:
ehr
COMMENTS
* The discharge shall not cause the receiving water's temperature to exceeA
2.8°C above background and in no case cause it to exceed 32°C.
TRC should be monitored at the eff. if CL2 is added to cooling water
Prepared by:
Juan C. Mangles
Reviewed by
Instream Assessment:
/ Date: V72 9 OD
Regional Supervisor:
Permits & Engineering:
RETURN TO TECHNICAL SUPPORT BY:
Date: 4/�616
Date:
Date:
MAY 2 6 1990
PERMIT NO.: NCOO 037 (p 0
DRAfTsTR
FACILITY NAME- € • r• j
Facility Status:
(circle on.)
Permit Status:
(circle one)
Major N1noz,
Pipe No: DD
MOOFICATION UNPFSI,QI'IED NEW
Design Capacity (MGD):
Domestic (% of Flow):
Industrial (X of Flow):
Comments:
CO
RECEIVING STREAM:
Class:: e
Sub -Basin: 0 3 (-/: 6) `5. .
Reference USGS Quad: Pr?
County: Let' 0 -
Regional Office: As Fa Mo . Ra
lclrcl..ns)
Requested By:
f aro
ea tiera'am i5re nch
(please attach)
Date:
Prepared By: �• • �r•�:f ��-•++� Date:
Reviewed By:
cDv I-14
ate-
Wi WS
3/; 7/c.o
(Geci
QUE&T
Dr —A u
Modeler
5 52_
JC M
Drainage Area (m1 )
Date Rec.
3-27- 96
Avg. Streamflow (cfs).
7Q10 (cfs) r Winter 7(210 (cfs)
30Q2 (cfs)
Toxicity Limits: IWC X (circle on.) Acute / Chronic
Instream Monitoring:
NArA"-Z-k-titr4- ch—k-kA(a•Z SAL4
Parameters
Upstream
Location
AA- 1JC 11
Downstream
L---.. A(L �L
o a
At. Vt„,z_
sr.xca.r9d V
lC&)JJ+-1? :...ntAitosa
Effluent
Characteristics
Summer
Winter
BOD5 (mg/I)
NH5 N (mg/1)
D.O. (mg/I)
TSS (mg/l)
.
F. Col. (/l00mi)
pH (Su)
4 -- Q
via
,,AA
— -4 W,Ae.f,,
A2AQ,-
'cot,c`�,
, sue d AY •
C v ( i , Pb, i
v) + a ,\ a) ,
-rtc S�0AA4�
_g
oM„ �"rcl
eX,aceed ,-,,
Coa�to•"�q tau"
Comments:
MC4i.0 \hq
0. Off- 6& C Odd
ex U& ! 3 2° c .
i�e C Sc� °A ce s r�i ti c c 2
, S ,e w►e Qna.f.
owe, A o. A k\ 0 co.a1Z -%o C a
D
WASH NGTONLOFFICE
MAY 2 1990
D. E. Request No.: 5652
WASTELOAD ALLOCATION APPROVAL FORM
Facility Name: E.I. Dupont de Nemours and Co./Kinston
NPDES No.: NC0003760 P(Pe 003
Type of Waste: Industrial
Status: Existing/Renewal
Receiving Stream: Beaverdam Branch
Classification: C-NSW
Subbasin: 030405
County: Lenoir
Regional Office: Washington
Requestor: R. Barona
Date of Request: 032790
Quad: F 29 SW
RECOMMENDED EFFLUENT LIMITS
EXISTING PROPOSED
Wasteflow (mgd) :
pH (su) : 6-9 6-9
Turbidity (NTU) : **
Temperature:
Metals(ug/1): Quarterly metal
then? 51141 (' 1Y6114;°1I)L Z'`MONITOR 6td e( � `%l'P e
Upstream (Y/N): Y
Downstream (Y/N): Y
Location: At NC 11
Location: At railroad track
scans
PFRViITS r-,.�,.
COMMENTS
The following instream parameters should be monitored: temperature and
turbidity.
** The discharge shall not cause the turbidity of the receiving waters
to exceed 50 NTU. If turbidity exeeds these levels due to natural backgrouC--
conditions, the discharge level can not cause any increase in turbidity
in the receiving waters.
* The discharge shall not cause the receiving water's temperature to exceed
2.8°C above background and in no case cause it to exceed 32°C.
TRC should be monitored at the eff. if CL2 is added to cooling water
Prepared by:
Juan C. Mangles
\A,c0--civC
I
Reviewed by
Instream Assessment: Art
Regional Supervisor:
Permits & Engineering:
RETURN TO TECHNICAL SUPPORT BY:
Date:
Date:
Date:
Date:
MAY 26 1990
V2-3/9°
(//d-60/1