HomeMy WebLinkAboutNC0037001_speculative limits_19961120 (2)State of orth Carolina
Department of Environment,
Health and Natural Resources
Division of Water Quality
Jaynes B. Hunt, Jr., Governor
Jonathan B. Howes, Secretary
A. Preston Howard, Jr., P.E., Director
Mr. Bill Holcomb
Rockingham County Schools
511 Harrington Highway
Eden, North Carolina 27288
,a4m4,
Ar A
410
anal
SHNR
November 20, 1996
Subject: Speculative Limits: Monroeton School, NC0036994
Bethany School, NC0037001
Rockingham County
Dear Mr. Holcomb,
I am writing in response to the October 9, 1996 letter from Mr. W. Max Frazier, PE,
concerning a proposed expansion and relocation for the Monroeton and Bethany Schools'
waste water discharge. The proposal includes one site for the Monroeton School and two
sites for the Bethany School. I will outline each proposal separately.
The Monroeton School currently discharges to an unnamed tributary to Troublesome Creek
which has low flow statistics that require an alternatives analysis for the current discharge.
The proposed relocation for this discharge is to a swamp -like segment of the Haw River
which is classified as C - NSW. This segment of the Haw River generally offers little
assimilative capacity for oxygen -consuming wastes due to the low stream flows, low
reaeration rates, and high sediment oxygen demand. To protect the dissolved oxygen stream
standard of 5 mg/1 and allow for the allocation of the limited assimilative capacity in this
waterbody segment, limits no less stringent than 15 mg/1 of BOD5 and 4 mg/1 NH3-N are
recommended for new and expanding discharges to the Haw River and its tributaries upstream
of SR 2711.
In 1983, the need for watershed -wide nutrient management for the Jordan Reservior
prompted the development of a Nutrient Sensitive Water (NSW) strategy which requires
effluent total phosphorus limits of 2.0 mg/1 for all new or expanding discharges.
The following outlines our current recommendations for the Monroeton School,
NC0036994 expansion and relocation to the Haw River:
Flow (mgd):
BOD5 (mg/1):
NH3-N (mg/1):
Dissolved Oxygen (mg/1):
Total Suspended Solids (mg/1):
pH (SU):
Fecal Colifoim (#/100mL):
Total Residual Chlorine (g/l):
Total Phosphorus (mg/1):
Total Nitrogen (mg/1):
Summer
0.005
15
4
5
30
6-9
200
28
2
monitor
Winter
0.005
30
8
5
30
6-9
. 200
28
2
monitor
P.O. Box 29535, Raleigh, North Carolina 27626-0535
Telephone 919-733-7015 FAX 919-733-2496
An Equal Opportunity Affirmative Action Employer 50% recycled/ 10% post -consumer paper
Rockingham County Schools Speculative Limits
NC0036994 & NC0037001 Rockingham County
The Bethany School currently discharges to an unnamed tributary to Huffines Mill Creek
which has low flow statistics that require an alternatives analysis for the current discharge.
Two proposed sites for this discharge to relocate were requested. The first was to
Troublesome Creek which is classified as WS-III NSW CA. The proposed location, (at the
bridge for SR 2351) has a positive flow during low flow periods, therefore a modeling
analysis was performed and secondary treatment is predicted to protect the receiving waters
dissolved oxygen standard of 5.0 mg/1. As with the Haw River site, a 2.0 mg/1 total
phosphorus limit would be required.
The following outlines our current recommendations for the Bethany School, NC0037001
expansion and relocation to Troublesome Creek:
Flow (mgd):
BOD5 (mg/1):
NH3-N (mg/1):
Dissolved Oxygen (mg/1):
Total Suspended Solids (mg/1):
pH (SU).
Fecal Cohform (#/100mL):
Total Residual Chlorine (14/1):
Total Phosphorus (mg/1):
Total Nitrogen (mg/1):
Summer
0.010
30
monitor
monitor
30
6-9
200
28
2
monitor
Winter
0.010
30
monitor
monitor
30
6-9
200
28
2
monitor
The second site proposed for Bethany School was to Huffines Mill Creek which does not
have sufficient drainage to meet the minimum stream flow criterion for discharge. A change in
the proposed site to SR 2359, (downstream from the original request) has a drainage area
large enough to sustain positive flow during predicted low flow periods. This proposed
relocation has a positive flow during low flow periods, therefore a modeling analysis was
performed and advanced secondary treatment is predicted to protect the receiving waters
dissolved oxygen standard of 5.0 mg/l. Unhke the Haw River discharge, no nutrient limits
would be required at this discharge location as it is in the Roanoke River Basin which is not
showing signs of nutrient problems.
The following outlines our current recommendations for the Bethany School, NC0037001
expansion and relocation to the Huffines Mill Creek:
Flow (mgd).
BOD5 (mg/1):
NH3-N (mg/1):
Dissolved Oxygen (mg/1):
Total Suspended Solids (mg/1):
pH (SU).
Fecal Cohform (#/100mL):
Total Residual Chlorine (µg/1):
Total Phosphorus (mg/1)
Total Nitrogen (mg/1):
Summer
0.010
30
14
monitor
30
6-9
200
28
monitor
monitor
Winter
0.010
30
monitor
monitor
30
6-9
200
28
monitor
monitor
Under current DWQ procedure, dechlorrnatron and chlorine limits are recommended for all
new or expanding dischargers proposing the use of chlorine for disinfection. An acceptable
level of residual chlorine in all of the proposed discharges is 28 µg/1 for protection against
acute toxicity. The process of chlorination / dechlorination or ultra violet radiation may allow
the facility to comply with the total residual chlorine limit.
Rockingham County Schools Speculative Limits
NC0036994 & NC0037001 Rockingham County
Please be advised that response to a speculative request does not guarantee that the Division
will issue an NPDES permit to discharge treated wastewater. In accordance with the North
Carolina General Statutes, the practicable waste treatment and disposal alternative with the
least adverse impact on the environment is required to be implemented. Nondischarge
alternatives, such as spray irrigation or connection to a regional treatment and disposal system,
are considered to be environmentally preferable to a discharge. Therefore, prior to submittal
of an NPDES application, a detailed alternatives analysis must be prepared to assure that the
environmentally sound alternative was selected from the reasonable cost effective options. In
order to receive final permit limits, a formal application indicating the proposed WWTP design
capacity and a justification for the facility will have to be submitted to the Division's Permits
and Engineering Unit.
The final NPDES effluent limitations will be determined after a formal permit application
has been submitted to the Division of Water Quality. If there are any additional questions
concerning this matter, please feel free to contact Farrell Keough at (919) 733-5083, extension
510 or me at extension 519.
Sincerely,
Donald L Safrit, P E
Assistant Chief for Technical Support
Water Quality Section
cc: Dave Goodrich, Permits and Engineering
Steve Mauney Winston-Salem Regional Office
Michelle Suverkrubbe, Planning
Bobby Blowe, Construction Grants
W. Max Frazier, PE, Tritech Civil Environmental, PC
Central Files
105
TRITECH
•
Tritech Civil WATER
& WASTEWATER ENGINEERS
(At
Post Office Box 4127 • Asheboro, North Carolina 27204 • (910) 672-5253
202 Commerce Place • Randleman, North Carolina 27317 • (910) 498-1060 • Fax: (910) 498-1070�
'
October 9, 1996
NC Department of Environment,
Health and Natural Resources
Division of Environmental Management
PO Box 29535
Raleigh, NC 27626-0535
Attention: Mr. Don Safrit
Dear Mr. Safrit:
Attached are maps that show discharge locations that are being considered for two wastewater dischargers
for whom Tritech Civil Environmental is providing engineering services. These dischargers are described
as follows:
Discharger Design Flow
1. Rockingham County Schools
Bethany School 10,000
2. Rockingham County Schools
Bethany School
10,000 gpd
3. Rockingham County Schools
Monroeton School 5,000
Discharge Point
Map Coordinates
Troublesome Creek ✓
921,600N
1,749,350E
Huffine Mill Creek ✓
93 7,900N
1,746,900E
Haw River
918,350N
1,783,850E
Please note that the proposed discharge point for Bethany School on Troublesome Creek is about 8 miles
upstream from the headwaters of the water supply reservoir for the City of Reidsville.
We request preliminary permit limits for these discharges at the points indicated.
Thank you for your assistance.
Very truly yours,
Tritech Civil Environmental, PC
W. Max Frazier, PE
lah/WMF
cc: Bill Holcomb, Rockingham County Schools
Steve Mauney, NCDEM - Winston-Salem Regional Office
•
P:96015-201sa.frit. doc
Oct-29-96 03-31
Tritech Civil Envy, PC 910 498 1070
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Number of pages including cover sheet 41
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For your review
Wu--5j.tesere d7! Ch.
From:
Tritech Civil Environmental, PC
PO Box 4127
Asheboro, NC 27204
�Y�X FVazics-
Phone
(910)498-1060
Fax Phone (910)498-1070
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Notes for File
Monroeton School
NC0036994
Qw: 0.005 mgd
• Current discharge, (Qw: 0.00425 mgd) is to zero 7Q10 / 30Q2 u.t. to Troublesome Creek. Facility is
scheduled to cease current discharge by 9/97. 00 c/3 pccea-1,‘ AO16 R s wif 5 /7.- Ifs Mc ti,;,
Haw River 03-06-01
P 3 9 c is c-± re rvc-,0 ,,1
The proposed site for relocation is to a swamp -like segment of the Haw River classified as C - NSW.
The Basin Plan recommends an Alternative Analysis and/or 15 BOD5 / 4 NH3-N for this area of the
Haw River, (section 6.3.5). A 2 0 mg/1 Total Phosphorus limit is also required for all new or
expanding discharges to this area, (section 6 4 2)
No model will be run for proposed site for two reasons the high s7Q10 will result in less stringent
limits than those outlined by the Basm Plan and the proposed discharge is to a swamp system that will
not be well portrayed by the Level B model.
Bethany School
NC0037001
Qw: 0.010 mgd
• Cuiient discharge, (Qw: 0.00375 mgd) is to u.t. to Huffines Mill Creek [C waters] which has a zero
7Q10 / 30Q2. Facility is scheuled to meet Advanced Tertiary Limits by 1994. atu to LA — t 5
CO� L ��� 5 � ( S/z, �Aw (tic. 13
• Two proposed sites for relocation were requested; Huffines Mill Creek and Troublesome Cre„�
Huffines Mill Creek 03-02-03
The proposed site had a drainage area that was less than the minimum required for an HA 9
discharge. If the discharge was located further downstream at SR 2359 the flow statistics would
be positve. A model was run at this site to prevent the need for the consultant to re -request a
speculative on this waterbody. The flow statistics required a 14 mg/1 NH3-N, and the model
indicated that Advanced Secondary Limits would protect.
The Huffines Mill Creek site is located in the Roanoke River Basin and would not have the nutrient
or conventional parameters limits that the Cape Fear discharges would.
Troublesome Creek 03-06-01
The Toublesome Creek, [WS - III NSW CA] proposed site did have a positive flow and the
model was run. The model indicated Secondary Limits would protect.
The Troublesome Creek proposed site would have the same nutrient removal requirments that the
Haw River site above would have, (i.e. 2 0 mg/1 Total Phosphorus).
Facility:
NPDES#:
Receiving Stream.
Comment(s):
Low Flow Record Station Number:
Hydrologic Area Number:
Drainage Area Low Flow Record Station:
Mean Annual Runoff:
Qave Low Flow Record Station:
s7Q1 0 Low Flow Record Station:
w7Q10 Low Flow Record Station:
30Q2 Low Flow Record Station:
Drainage Area New Site:
MAR New Site:
Qave per Report Equation:
s7Q1 0 per Report Equation:
w7Q10 per Report Equation:
30Q2 per Report Equation:
Drainage Area Ratio:
[ new DA/Da at gage]
Weighted Ratio:
Over -ride Inappropriate Site. (y ):
Monroeton School
NC0036994
Haw River
Open Report site upstream at US 220
02.0932.6000
HA9
20 60 miles squared
1.00 miles squared
20.60 cfs
0.90 cfs
4.00 cfs
4.40 cfs
must be < 400 sq. miles
62.10 sq. miles
1.0 cfs/miles squared
62.10 cfs
1.75 cfs
7.05 cfs
9.73 cfs
Continue
3.01 . 1
Continue
0.33 : 1
Drainage Area New Site:
MAR New Site:
Weighted Qave per Report Equation:
Weighted s7Q10 per Report Equation:
Weighted w7Q10 per Report Equation:
Weighted 30Q2 per Report Equation:
62.10 miles squared
1.0 cfs/miles squared
62.10 cfs
2.07 cfs
8.69 cfs
10.89 cfs
Bethany School
Segment
/
Reach
S1
R1
S1
R2
S1
R3
S1
R4
S1
R5
Length
1.8
1.0
0.3
1.5
-
Qw
0090
-
-
-
-
CBOD
45
-
_
-
_
NBOD
90
-
-
-
_
DO
-
_
-
-
_
:.::.••:::.:.:::
:.............::...:..........:.>:.;:•::•:•::.::::::<.::•:;::<•:<....::<::::...
•...::. • • •..:.....•......
:>:::::::
s 7Q10
0
0
0
0
-
w7Q10
0013
0.013
0013
0013
-
Qave
0.96
0.96
0.96
0.96
-
Iiiiiii
a.::::::::......:••.....•:..
•::.......•.�.....•...........•....:.::::•:::.;>;
•:::•;>•:•;<:::i::>
:::::•:
;>:::;:;
::
s 7Q10
-
-
0.39
0.33
-
w 7Q 10
-
-
0.74
0.58
-
Qave
-
-
3.58
2.63
-
Slope
7.7
10.5
10.5
5.7
02.0933.2525 HA9 MAR 1.1
Bethany School DA: 13.6
NC0037001 s7Q10: 0.78
Qw: 0.010 mgd w7Q10: 2.12
Qave: 14.96
30Q2: 2.76
Troublesome Creek
Runoff
s7Q10: (1.09 - 0.33 - 0.39 - 0.78 ) / 4.6 = (-0.089 cfs) zero will be used
w7Q10: (3.5-0.58-0.74-2.12)/4.6 = 0.013cfs
Qave: (25.6 - 2.63 3.58 - 14.96) / 4.6 = 0.96 cfs
02.0933.2552
DA: 3.58
s7Q10: 0.39
w7Q10: 0.74
Qave: 3.58
30Q2: 0.91
HA9 MAR 1.1
02.0933.2800 HA9 MAR 1.1
DA: 25.6
s7Q10: 1.09
w7Q10: 3.50
Qave: 25.6
30Q2: 4.66
S1 R1
SR 2351
S1 R2
S1 R3
S1 R4
02.0933.2750 HA9 MAR 1.1
DA: 2.63
s7Q10: 0.33
w7Q10: 0.58
Qave: 2.63
SR 1001
Discharger
Receiving Stream
The End D.O. is
The End CBOD is
The End NBOD is
Segment 1
Reach 1
Reach 2
Reach 3
MODEL RESULTS
: BETHANY SCHOOL
: HUFFINES MILL CREEK
7.95 mg/l.
1.99 mg/l.
1.31 mg/l.
DO Min
(mg/1) Milepoint Reach #
6.87 0.00
1
SUMMER
PROPOSED SITE CHANGED DWNSTREM
30 MG/L BOD 14 MG/L NH3-N
WLA
CBOD
(mg/1)
45.00
0.00
0.00
WLA
NBOD
(mg/1)
63.00
0.00
0.00
WLA
DO Waste Flo
(mg/1) (mgd)
0.00
0.00
0.00
0.01000
0.00000
0.00000
I Seg #
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
Seg #
1
Reach
1
1
1
1
1
1
1
1
1
2
2
2
2
2
2
3
3
3
3
Reach
Seg Mi I
0.00
0.20
0.40
0.60
0.80
1.00
1.20
1.40
1.60
1.60
1.80
2 00
2.20
2.40
2.60
2.60
2.70
2.80
2.90
# I Seg Mi
D.O.
6.87
7.60
7.76
7.81
7.84
7.86
7.88
7.90
7.91
7.91
8.02
8.03
8.03
8.04
8.04
8.04
7.99
7.96
7.95
D.O.
1
I CBOD
4.51
4.22
3.96
3.71
3.49
3.28
3.09
2 91
2 75
2.75
2.61
2 48
2 36
2 25
2.14
2.14
2.09
2.04
1.99
CBOD
SUMMER
PROPOSED SITE CHANGED DWNSTREM
30 MG/L BOD 14 MG/L NH3 N
NBOD I Flow I
4.62 0.27
4.18 0 27
3.79 0.28
3.44 0.29
3.12 0.30
2 84 0.31
2.59 0.31
2 36 0.32
2.15 0.33
2.15 0.33
2 00 0.34
1.85 0.35
1.72 0.35
1.60 0.36
1.49 0.37
1.49 0.37
1.43 0.37
1.37 0.38
1.31 0.38
I NBOD I Flow I
*** MODEL SUMMARY DATA ***
Discharger .
Receiving Stream .
Summer 7Q10 .•
Design Temperature:
BETHANY SCHOOL
HUFFINES MILL CREEK
0 25
26.0
Subbasin : 0302
Stream Class: C
Winter 7Q10 : 0.4
ILENGTHI SLOPE' VELOCITY 1 DEPTH' Kd I Kd I Ka I Ka I KN I KN I KNR 1 KNR I SOD I SOD
mile I ft/mil fps I ft Idesignl @20 'design) @20 Idesignl @20 'design) @20 'design' @20
Segment 1
Reach 1
1 1 1
1.601 64.901 0.126 0.40 0.52 0.39 116.82 14.761 0.79 0.50 0.79 0.00 0.00 0.00
1 I 1 1
Segment 1
Reach 2
I I i
1.001116.701 0.153 1 0.39 1 0.57 1 0.44 136.66 1 32.181 0.79 1 0.50 1 0.79 1 0.00 1 0.00 1 0.00
I I 1 1 I 1 I 1 1 1
Segment 1
Reach 3
I 1 1 1 I 1 I 1 I 1 1
0.301 50.001 0.121 1 0.45 0.47 1 0.36 112.45 1 10.931 0.79 0.50 1 0.79 0.00 1 0.00 0.00
I I 1 1 I 1 1 1 1 I 1
Flow I
cfs
Segment 1 Reach 1
Waste I 0.015 I
Headwaters) 0.250
Tributary ( 0.000
* Runoff 1 0.040
Segment 1
Waste
Tributary
* Runoff
each 2
0.000
0.000
0.040
Segment 1 Reach 3
Waste
Tributary
* Runoff
CBOD I NBOD I D.O. I
mg/1 1 mg/1 I mg/1 I
45.000 1 63.000 I
2.000 1 1.000
2.000 1 1.000
2.000 1 1.000
0.000
7.300
7.300
7.300
0.000 1 0.000 I 0.000
2.000 1 1.000 7.300
2.000 1 1.000 7.300
0.000 1 0.000
0.000 I 2.000
0.040 1 2.000
* Runoff flow is in cfs/mile
0.000 I 0.000
1.000 I 7.300
1.000 I 7.300
Bethany School
Segment
/
Reach
S1
R1
S1
R2
S1
R3
S1
R4
S1
R5
Length
1.6
1.0
0.3
-
_
Qw
9 •
t,.t4_ •
_
_
-
-
CBOD
10
_
-
or
_
NBOD
63
_
_
-
_
DO
-
-
_
-
:::::::::•
.........:...............::::::.............................•:•:.
• ..........
.....................:•:;••:::.:;:.........
s 7Q10
0.04
0.04
0.04
-
-
w 7Q 10
0.09
0.09
0.09
-
-
Qave
0.56
0.56
0.56
-
-
:
.::
r`:::::: »:
»
«
<:
<
:
::libsita. :<:>:::
?<::
:::>::>::::";
s 7Q10
-
_
_
_
_
w7Q10
-
_
-
_
_
Qave
-
_
-
_
-
Slope
64.9
116.7
50
Bethany School
NC0037001
Qw: 0.010 mgd
Huffines Mill Creek
HA9 MAR 1.1
DA 1.63
s7Q10: 0.25
w7Q10: 0.40
Qave: 1.79
30Q2: 0.47
Runoff
s7Q10: ( 0.36 - 0.25 ) / 2.95 = 0.04
w7Q10: (0.66 - 0.40 ) / 2.95 = 0.09
Qave: (3.43 - 1.79 ) / 2.95 = 0.56
02.0709.1625 HA9 MAR 1.1
DA: 3.12
s7Q10: 0.36
w7Q10: 0.66
Qave: 3.43
30Q2: 0.81
DA 0.7
originally proposed site
Unuseable Drainage Area
considered zero 7Q10 / 30Q2
SR 235
S1 R1
S1 R2 S1 R3
Jacobs Creek
MODEL RESULTS
Discharger : BETHANY SCHOOL
Receiving Stream : TROUBLESOME CREEK
The End D.O. is
The End CBOD is
The End NBOD is
Segment 1
Reach 1
Reach 2
Reach 3
Reach 4
7.43 mg/l.
1.24 mg/l.
0.55 mg/l.
DO Min
(mg/1) Milepoint Reach #
6.80 1.00
1
SUMMER
SECONDARY LIMITS W/
2.0 MG/L TOTAL PHOSPHORUS
WLA
CBOD
(mg/1)
45.00
0.00
0.00
0.00
WLA
NBOD
(mg/1)
90.00
0.00
0.00
0.00
WLA
DO Waste Flo
(mg/1) (mgd)
0.00
0.00
0.00
0.00
0.01000
0.00000
0.00000
0.00000
Seg #
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
Seg #
1
1
SUMMER
SECONDARY LIMITS W/
2 0 MG/L TOTAL PHOSPHORUS
Reach # 1 Seg Mi 1 D.O. 1 CBOD 1 NBOD 1 Flow 1
1 0.00 7.16 2.84 2.73 0.80
1 0.20 7.01 2 70 2.52 0.80
1 0.40 6.91 2.58 2.33 0.80
1 0.60 6.84 2.45 2.14 0.80
1 0.80 6.81 2 34 1.98 0.80
1 1.00 6.80 2.23 1.82 0.80
1 1 20 6.80 2.12 1.68 0.80
1 1.40 6.82 2 02 1.55 0.80
1 1.60 6.85 1.93 1.43 0.80
1 1.80 6.89 1.83 1.32 0.80
2 1.80 6.89 1.83 1.32 0.80
2 2 00 7.01 1.75 1.22 0.80
2 2.20 7.12 1.67 1.13 0.80
2 2 40 7.21 1.59 1.05 0.80
2 2 60 7.28 1.52 0.97 0.80
2 2.80 7.35 1.45 0.90 0.80
3 2.80 7.34 1.63 0.93 1.19
3 2.90 7.38 1.60 0.91 1.19
3 3.00 7.41 1.57 0.88 1.19
3 3.10 7.45 1.54 0.85 1.19
4 3.10 7.41 1.64 0.88 1.52
4 3.60 7.39 1.49 0.75 1.52
4 4.10 7.40 1.36 0.64 1.52
4 4.60 7.43 1.24 0.55 1.52
Reach # 1 Seg Mi 1 D.O. 1 CBOD 1 NBOD 1 Flow 1
*** MODEL SUMMARY DATA ***
Discharger .•
Receiving Stream .
Summer 7Q10 .•
Design Temperature:
BETHANY SCHOOL
TROUBLESOME CREEK
0.78
26.0
Subbasin : 0306
Stream Class: WS I
Winter 7Q10 : 2.12
!LENGTH' SLOPEI VELOCITY 1 DEPTH' Kd I Kd I Ka 1 Ka I KN I KN I KNR I KNR I SOD 1 SOD
► mile I ft/mil fps 1 ft (design! @20 'design I @20 !design! @20 !design! @20 'design l @20
I I I
Segment 1 1 1.801 7.701 0.072 ► 0.86 1 0.29 1 0.22 1 1.13 1 1,001 0.48 ► 0.30 1 0.48 1 0.00 1 0.00 1 0.00
Reach 1 1 I I 1 1 1 1 1 ► ► i i
I I I
Segment 1 1 1.001 10.501 0.076 1 0.83 1 0.29 1 0.22 1 1.64 1 1.441 0.48 1 0.30 1 0.48 1 0.00 1 0.00 1 0.00
Reach 2 I I I
Segment 1
Reach 3
I I I
0.301 10.501 0.095 ( 0.91 1 0.30 1 0.22 1 2.05 1 1.801•0.48 1 0.30 1 0.48 1 0.00 1 0.00 1 0.00
I I 1 1 1 I I ► i 1
Segment 1
Reach 4
I I
1.501 5.701 0.091 1 1.05 0.28 0.21 1 1.07 1 0.931 0.48 1 0.30 10.48 1 0.00 1 0.00 1 0.00
I I I I 1 I I I 1 I 1
Flow
cfs
Segment 1 Reach 1
Waste
Headwaters
Tributary
* Runoff
Segment 1
Waste
Tributary
* Runoff
0.015
0.780
0.000
0.000
CBOD
mg/1
45.000
2.000
2.000
2.000
NBOD
mg/1
90.000
1.000
1.000
1.000
D.O. I
mg/1 I
0.000
7.300
7.300
7.300
each 2
0.000 1 0.000 1 0.000 1 0.000
0.000 1 2.000 1 1.000 1 7.300
0.000 1 2.000 1 1.000 1 7.300
Segment 1 Reach 3
Waste 1 0.000
Tributary 1 0.390
* Runoff 1 0.000
Segment 1 Reach 4
Waste I 0.000
Tributary I 0.330
* Runoff I 0.000
0.000
2.000
2.000
0.000
2.000
2.000
0.000
1.000
1.000
0.000
1.000
1.000
0.000
7.300
7.300
0.000
7.300
7.300