HomeMy WebLinkAbout2017-07-06 Draft_WQMPP Hoh River
DRAFT
Water Quality Monitoring Plan (WQMP)
Upper Hoh River Road Bank Stabilization
and Culvert Replacement
Prepared by
David Evans and Associates, Inc.
14432 SE Eastgate Way, Suite 400
Bellevue, WA 98007
July 6, 2017
Water Quality Monitoring Plan Page | 1
Upper Hoh River Bank Stabilization
PURPOSE
The Water Quality Monitoring Plan (WQMP) will be used to track the performance of Best
Management Practices (BMPs) used during in-water work within the project limits of the Upper
Hoh River Road Bank Stabilization and Culvert Replacement project (Project).
This WQMP includes a monitoring schedule (Table 1) that identifies the appropriate parameters
to be monitored, locations, monitoring and sampling procedures, and frequency. Attachment A
is a Sample Monitoring Results Recording Form.
OBJECTIVES
This WQMP will:
Through water quality monitoring and sampling, document the performance of BMPs used
within waters of the state, including wetlands, in which the project requires work.
Determine if Water Quality Standards are being met at the edge of the point of compliance.
Any changes to monitoring must be approved by Ecology prior to making the changes.
IN-WATER/OVER WATER ACTIVITY DESCRIPTION
The Project will construct bank stabilization measures in the form of engineered log jams with
dolosse (ELJ/dolosse) at three locations needing bank stabilization. It will also replace three
tributary crossings: the culvert at MP 4.38, the Tower Creek Bridge with a new bridge, and the
Canyon Creek culvert with a bridge.
The following activities will occur below the Ordinary High Water Mark (OHWM) of the Hoh
River or of nearby wetlands:
Installation of temporary stream diversions at replaced stream crossings;
Installation of flow deflection at locations along the Hoh River near bank stabilization
sites;
Excavation and fill activities related to culvert demolition and ELJ/dolosse installation;
Installation of a new 16- by 16-foot concrete box culvert at MP 4.38; and
Restoration of disturbed stream banks following culvert removal and bridge construction
at Canyon Creek.
The Project also includes roadway realignment and regrading at the tributary crossings to
accommodate the new structures. Roadway stormwater ditches will be improved in some areas.
Water quality monitoring includes stormwater monitoring at the discharge points of these ditches
as shown on the monitoring locations map in Attachment B.
Water Quality Monitoring Plan Page | 2
Upper Hoh River Bank Stabilization
BEST MANAGEMENT PRACTICES (BMPS)
BMPs will be in place at the monitoring locations shown on maps in Attachment B. Silt fence
will be used to contain turbid runoff from disturbed areas along the roadway, particularly around
the bridge and culvert replacement work. Check dams will be installed within roadway ditches to
reduce flow and retain sediment.
The ELJ/dolosse structures will be installed along the edge of water in the Hoh River. Typical
BMPs are not practical in these locations but measures will be taken to contain disturbance and
minimize impacts. Environmental commitments for this project are provided in Appendix C.
WATER QUALITY STANDARDS FOR SURFACE WATERS
This project is located in Water Resource Inventory Area (WRIA) 20, and involves work in the
Upper Hoh River, Tower Creek, Canyon Creek, and an unnamed tributary to the Hoh River.
Turbidity is the main concern during construction of this project and is the focus of this
monitoring plan. The Water Quality Standard for turbidity on all project reaches is:
5 nephelometric turbidity unit (NTU) over background when the background is 50 NTU
or less; or
A 10 percent increase in turbidity when the background turbidity is more than 50 NTU.
MONITORING PLAN
Monitoring Contacts
Steve Morrow with Federal Highway Administration’s Western Federal Lands Highway
Division will be responsible for providing Ecology with the necessary notifications and results of
the water quality monitoring according to the frequency specified in the Section 401 Water
Quality Certification (401).
Monitoring personnel who will conduct the 401 water quality monitoring will be determined by
the contractor.
Name: TBD
Office Phone: TBD
Cell Phone: TBD
Monitoring Schedule
Table 1 outlines the monitoring parameters and schedule for all in-water work activities.
Water Quality Monitoring Plan Page | 3
Upper Hoh River Bank Stabilization
Table 1
Monitoring Parameters and Standard Schedule
In-water Activities
Monitoring Point
Location Frequency Parameters
Water
Quality
Standard
- Hoh River ELJ/dolosse Installation
- MP 4.38 culvert replacement
- Tower Creek bridge replacement
- Canyon Creek culvert removal/bridge
installation
See Attachment B Once per
week Turbidity
See
Turbidity
Standard
Above
Monitoring Duration
Grab samples and visual observations will be collected for the duration of the construction
activity that has triggered monitoring.
Visual monitoring will be performed continuously for (1) all work below the OHWM, but not
within the wetted perimeter, and (2) for all over water work activities.
Contingency Sampling
If sample results confirm that water quality is out of compliance with water quality standards, the
contractor will modify or stop the activity causing the problem and commence the contingency
sampling requirements (Table 2) until standards are met for two consecutive sample periods.
Table 2
Contingency Sampling Requirements
Parameter Contingency Sampling
Location
Contingency
Frequency Water Quality Standard
Turbidity Point of Non
Compliance Hourly
5 NTU over background when background is 50
NTU, or a 10% increase in turbidity when
background is >50NTU. See section below on
Sampling Protocol for a discussion of background
turbidity.
Once compliance with water quality standards is achieved, the project shall return to its standard
sampling schedule.
Non Compliance
If either visual or physical monitoring indicates that water quality standards have been exceeded,
the required reporting, as discussed below, will be initiated.
Water Quality Monitoring Plan Page | 4
Upper Hoh River Bank Stabilization
SAMPLING PROTOCOL
Sampling Locations
Monitoring locations are provided on the attached maps, in Attachment B, for activities below
the OHWM and for locations where stormwater may leave the site. In general, in the Hoh River,
turbidity will be measured at a point of compliance 300 feet downstream of each bank
stabilization site. Turbidity will also be measured 50 to 100 feet upstream of each bank
stabilization site to obtain background turbidity levels for comparison. At the structure crossings,
turbidity will be measured up to 200 feet downstream of the construction area where possible. At
some locations, the confluence with the Hoh River is less than 200 feet from the construction
area. In these cases, monitoring will occur just upstream from the confluence with the Hoh River.
Turbidity will also be measured roughly 50 feet upstream of the structure crossing construction
to establish background turbidity levels.
The sampling locations are labeled as follows:
POC# – Point of Compliance; for river locations downstream of construction (7 sample
sites)
B# – Background; for upstream background sample site (7 sample sites)
D# – Discharge; for roadside ditch discharge points (13 sample sites)
Sampling Procedures
A background sample must be taken outside the area of influence and immediately prior to the
downstream or radius samples.
Water samples will be collected and analyzed for the appropriate parameters, per the Monitoring
Schedule above, following the equipment and sampling guidelines below:
Turbidity will be monitored using a Hach 2100P turbidimeter, or similar equipment;
The first compliance sample for turbidity will be taken approximately 1 hour after the in-
water activity starts, unless there is a visual plume at the point of compliance prior to 1
hour;
A portable turbidity meter will be used in the field. A representative sample should
accurately reflect the true condition of the water source from which the sample was
taken. The following protocol will be used to ensure a representative sample is analyzed:
Use a clean container to obtain a grab sample from the source;
Collect sample with care to avoid disturbance of sediments and collecting surface
contaminants;
Gently but thoroughly mix the sample before pouring it into the small vial used to
read the sample in the turbidimeter; and
Without allowing the sample to settle, take turbidity reading according to turbidimeter
manufacturer’s instructions.
Water Quality Monitoring Plan Page | 5
Upper Hoh River Bank Stabilization
A calibration check of the turbidimeter using secondary standards will be carried out
regularly (at least once per week). The instrument will be recalibrated using primary
standards at least once every 3 months, or more when a calibration check indicates there
is a problem. The manufacturer’s calibration procedures will be followed.
REPORTING
All water quality monitoring results (visual and physical) will be recorded on the monitoring
form attached (Attachment A).
All sample results will be submitted to the Ecology Federal Permit Manager/Coordinator at the
frequency specified in the 401.
If sample results or visual monitoring indicate a exceedance of water quality standards,
notification shall be made within 24 hours to Ecology’s Federal Permit Manager/Coordinator.
ATTACHMENTS
Attachment A - Sample Monitor Results Reporting Form
Attachment B - Monitoring Location Maps
Attachment C – Environmental Commitments
Water Quality Monitoring Plan
Upper Hoh River Bank Stabilization
ATTACHMENT A
SAMPLE MONITOR RESULTS REPORTING FORM
TURBIDITY
WQ MONITORING FORM
Monitoring and Reporting Form for the
Upper Hoh River Bank Stabilization and Culvert Replacement Project
WQ Tester:
Date of last calibration for Turbidity Meter________
Monitoring Point
Sample
Location
Date &
Time Turbidity
Notes (include weather , waterbody flow in cfs, other
observations of waterbody, etc)
Water Quality Monitoring Plan
Upper Hoh River Bank Stabilization
ATTACHMENT B
MONITORING LOCATIONS MAPS
24524
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CP
14101
CP
14102
BEGIN PROJECT
El= 266.89
E= 814,443.431
N= 318,075.887
9+62.52
UPPER HOH RIVER ROAD
WA JEFF 91420(1)
El= 259.98
E= 815,019.639
N= 318,061.255
15+39.03
UPPER HOH RIVER ROAD
WA JEFF 91420(1)
SUSPEND PROJECT
UP
T
T
T
UP
CP
14105
RESUME PROJECT
El= 269.92
E= 816,549.507
N= 318,249.233
30+93.41
UPPER HOH RIVER ROAD
WA JEFF 91420(1)
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CONTROL PLAN
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LEGEND
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HOH RIVER
HOH RIVER
Roadway Obliteration
Inlet Protection
Filter Rock Check Dam
Silt Fence
Flow Arrow
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POC1 - Sample 300' d/s
of construction within flow
along the right bank.
B1 - Sample 50-100' u/s
of construction within flow
along the right bank.
POC2 - Sample 300' d/s
of construction within flow
along the right bank.
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UP
UP
UP
T T
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CP
TT
T
CP
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Clearing limits
Clearing limits
SUSPEND PROJECT
El= 263.11
E= 818,510.379
N= 317,242.985
53+48.89
WA JEFF 91420(1)
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37+00 TO 54+00
CONTROL PLAN
EROSION/SEDIMENT
LEGEND
HOH RIVER
HOH RIVER
Check dam (Filter rock)
47+81 to 49+31 Lt
Check dam (Filter rock)
49+70 to 50+80 Lt
Silt fence
47+81 to 50+79 RT
Silt fence
49+22 to 49+39 LT
Silt fence
49+71 to 49+84 LT
Roadway Obliteration
Inlet Protection
Filter Rock Check Dam
Silt Fence
Flow Arrow
70
%
PL
A
N
IN
HA
N
D
04
-
1
8
-
2
0
1
7
B2 - Sample 50-100' u/s
of construction within flow
along the right bank.
D2 - Sample at ditch
discharge point
POC5 - Sample d/s of
construction and u/s of
Hoh River confluence.
B5 - Sample 50'
u/s of construction Un
n
a
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discharge point
7
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350
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365
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32
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32
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320
3
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325
3
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325
3
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32
5
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25
32
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325
325
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2
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330
33
0
3
3
0
330
3
3
0
33
0
330
3
3
0
330
330
3
3
0
3
30
3
3
0
330
3
3
0
330
3
3
0
33
5
3
3
5
3
3
5
335
33
5
335
335
3
3
5
3
3
5
335
3
3
5
3
3
5
3
3
5
335
335
34
0
3
4
0
3
4
0
340
340
340
3
4
0
3
4
0
3
4
0
34
0
340
340
34
0
340
340
34
0
340
34
5
3
4
5
3
4
5
345
345
34
5
3
4
5
3
4
5
345
34
5
3
4
5
350
3
5
0
3
5
0
350
3
5
0
3
5
0
35
0
3
5
0
350
350
350 3
5
0
3
5
0
3
5
0
3
5
0
3
5
0
35
0
35
0
35
0
3
55
3
5
5
355
355
3
5
5
3
5
5
355
3
5
5
3
5
5
3
5
5
355
355
3
5
5 355
3
5
5
3 5 5
36
0
36
0
360
360
3
6
0
3
6
0
360
3 6 0
360
3
6
0
3 60
365
3
6
5
365
36
5
365
3
6
5
3
6
5
3
6
5
3
6
5
370
370
3
7
0
370
37
0
370
370
37
0
370
370
375
375
375
375
375
375
37
5
3
7
5
375
375
3
8
0
38
0
380
3 8 0
380
380
3
8
0
380
3
8
5
38
5
3 85
385
38
5
385
3
9
0
3
9
0
390
3 90
39
0
3
9
5
3
9
5
395
395
3 95
4
0
0
4
0
0
40
0
4 00
400
4
0
5
4
0
5
4 05
405
405
4
1
0
4
1
0
410
410
41
5
4
1
5
41
5
415
4
2
0
42
0
4
2
0
4 20
42
0
4
2
5
425
425
4
3
0
430
430
4
3
5 435
43
5
4
4
0
440
4 4
0
4
4
5
44
5
4
4
5
4
5
0
4 50
4
5
5
45
5
4
60
460
4
65
4
6
5
470
4 70
47
0
N
Clearing limit
Clearing limit
Clearing limit
Clearing limit
HOH RIVER
Silt fence
71+00 to 76+99 Rt.
Silt fence
77+80 to 85+00 Rt.
rolled erosion control product
Filter rock check dams with
72+85 to 75+50 Lt.
Silt fence
77+61 Lt./Rt.
77+34 Lt./Rt.
Filter rock check dams
78+55 to 80+75 Lt.
F.5
STATE PROJECT
NUMBER
SHEET
]
U
S
_
S
u
r
_
f
t
2
D
[
c
:
\
m
y
f
i
l
e
s
\
p
w
_
p
r
o
d
u
c
t
i
o
n
\
d
0
2
0
3
2
2
7
\
w
a
-
a
2
0
1
3
0
2
0
_
d
d
.
d
g
n
WA JEFF 91420(1)
1
2
:
4
2
P
M
1
3
A
p
r
il
2
0
1
7
C
.
C
o
n
r
a
d
-
-
/
-
-
-
-
0
1
/
2
0
1
7
C
h
e
c
k
e
d
b
y
:
D
e
s
i
g
n
e
d
b
y
:
71+00 to 79+00
CONTROL PLAN
EROSION/SEDIMENT
LEGEND
Roadway Obliteration
Inlet Protection
Filter Rock Check Dam
Silt Fence
Flow Arrow
7
0
%
P
L
A
N
I
N
H
A
N
D
0
4
-
1
8
-
2
0
1
7
B6 - Sample 50'
u/s of construction
POC6 - Sample 200'
d/s of construction
or just u/s of Hoh
River confluence.
D3 - This is a
temporary flow line
along the silt fence.
Sample at end of
fence.
D4 - Sample at ditch
discharge point
D5 - Sample at ditch
discharge point
315
3
1
5
3 15
315
3
1
5
3
1
5
3
1
5
3
1
5
31
5
3
1
5
315
3
1
5
315
315
315
315
3
1
5
31
5
3
1
5
31
5
315
315
315
315
315
315
3
1
5
315315
3
1
5
3
1
5
31
5
3
1
5
315
3
1
5
315
315
315
315
315
320
320
320
325
325
325
330
3
3
0
33
0
33
5
335
335
340
3
4
0
340
3
4
0
340
340
345
345
345
345
3
5
0
350
350
3
5
5
3 55
355
355
3
6
0
360
360
3
6
0
360
3
6
5
365
3
6
5
365
365
365
3
7
0
370
3
7
0
370
3
7
5
3 7 5
3
8
0
380
38
5
3
8
5
385
390 390400410
420
330
335
3
3
5
340
345350
355
355
35
5360
360
3
1
0
310
310
3
1
0
3
1
0
3
1
0
310
310
31
0
310
310
3
1
0
3
1
0
3
1
0
3
1
0
3
1
0
310
3
1
0
31
0
3
1
0
31
0
3
1
0
3
1
0
3
1
0
310
3
1
0
310
3
10
3
1
0
3
1
0
3
1
0
3
1
0
3
1
0
3
1
0
31
0
3
1
0
3
1
0
3
1
0
3
1
0
3
1
0
310
3
1
0
31
5
3
1
5
3
1
5
315
315
315
315
315
31
5
3
1
5
3 2 0
320
320
320
320
320
320
320
325
325
3
2
5
325
325
325
3
3
0
330
330
330
330
3
3
0
3
3
0
3
3
0
335
33
5
335
335
335
335
3
3
5
340
3
4
0
3
4
0
340
340
340
3
4
0
3
4
0
3
4
0
3
4
5
345
3
4
5
3
4
5
345
345345
345
3
4
5
35
0
350
350
3
5
0
350
3
5
0
3
5
0
3
5
5
355 355
355
355
3
5
5
360
360
360
3
6
0
36
0
3
6
5
3
6
5
36
5
365
365
365
365
3
6
5
365
3
7
0
370
3
7
0
370
370
3
7
0
370
370
370
3
7
0
3
7
5
375
375
375
3
7
5
375
375
3
7
5
3
8
0
3
8
0
380
380
3
8
0
380
380
3
8
5
3
8
5
385
385
385
385
385
3
9
0
390
390
390
390
390
3
9
0
3
9
0
3
9
5
395
395
395
39
5
3
9
5
40
0
400
400
400
4
0
5
405
405
410
410
410
415
420
4
2
5
4
3
0
N
N
8
0
500
8
5 9
6
9
8
F.6
STATE PROJECT
NUMBER
SHEET
]
U
S
_
S
u
r
_
f
t
2
D
[
c
:
\
m
y
f
i
l
e
s
\
p
w
_
p
r
o
d
u
c
t
i
o
n
\
d
0
2
0
3
2
2
7
\
w
a
-
a
2
0
1
3
0
2
0
_
d
e
.
d
g
n
WA JEFF 91420(1)
1
2
:
4
1
P
M
1
3
A
p
r
il
2
0
1
7
C
.
C
o
n
r
a
d
-
-
/
-
-
-
-
0
1
/
2
0
1
7
C
h
e
c
k
e
d
b
y
:
D
e
s
i
g
n
e
d
b
y
:
79+00 to 85+00
CONTROL PLAN
EROSION/SEDIMENT
96+00 to 98+60
CONTROL PLAN
EROSION/SEDIMENT
LEGEND
LEGEND
Clearing limit
Clearing limit
Clearing limit
HOH RIVER HOH RIVER
Silt fence
77+80 to 85+00 Rt.
Filter rock checkdams
78+55 to 80+75 Lt.
Roadway Obliteration
Inlet Protection
Filter Rock Check Dam
Silt Fence
Flow Arrow
Roadway Obliteration
Inlet Protection
Filter Rock Check Dam
Silt Fence
Flow Arrow
70
%
PL
A
N
IN
HA
N
D
04
-
1
8
-
2
0
1
7
POC3 - Sample 300' d/s
of construction within flow
along the right bank.
POC4 - Sample 300' d/s
of construction within flow
along the right bank.
B3 - Sample 50-100' u/s
of construction within flow
along the right bank.
B4 - Sample 50-100' u/s
of construction within flow
along the right bank.
D6 - Sample at ditch
discharge point
380
380
3
8
0
3
8
0
38
0
3
8
0
385
38
5
3
8
5
3
8
5
385
385
385
3
9
0
390
390
390
3
9
0
390
390
39
0
395
395
3953
9
5
395
395
395
4
0
0
400
400
4
0
0
4
0
0400
4
0
0
400
4
0
0
40
0
4
0
0
400
40
5
4
0
5
4
0
5
405
4
0
5
4
0
5
405405
405
405
4
0
5
4
0
5
4
0
5
4
0
5
4
0
5
4
0
5
4
0
5
4
05
410
4
1
0
410
410
410
410
410
4
1
0
4
10
4
1
0
4
1
0
4
1
0
4
1
0
4
1
0
4
1
0
4
1
0
4
1
0
415
4
1
5
4 1 5
415
415
415
41
5
41
5
415
4
1
5
4
1
5
4
1
5
4
1
5
4
1
5
4
1
5
4
1
5
415
420
42
0
4
2
0420
420
4
2
0
420
4
2
0
4
2
0
420
4
2
0
42
0
4
20
4
2
0
4
2
0
4
2
0
420
4
2
0
4
2
0
4
2
0
420
4
2
0
4 2 0
4
2
0
4
2
0
4
2
0
420
4
2
5
425
425
425
425
4
2
5
425
425
425
42
5
4
2
5
4
2
5
4
2
5
425
425
425
4
3
0
430
430
430
4
3
0
43
0
4
30
43
0
4
3
0
4
3
0
4
3
0
4
3
0
430
4
3
0
4
30
4
3
0
4
3
0
43
0
4
3
0
4
3
0
43
0
435
435
435
435
435
435
435
4
3
5
4
3
5
4
3
5
43
5
435
4354
3
5
435
4
3
5
43
5
4
3
5
435
4
3
5
43
5
4
3
5
440
4
4
0
440
4
4
0
4
4
0
4
4
0
4
4
0
4
4
0
4
4
0
4
4
0
44
0
4
4
0
44
0
445
445
445
4
4
5
4 4 5
44
5
4
4
5
4
4
5
44
5
4
4
5
4
4
5
44
5
45
0
45
0
4
5
0
4
5
0
4
5
0
4
5
0
4
5
0
4
5
0
4
5
0
4
50
4
5
0
450
4
5
0
4
5
0
4
50
45
0
45
0
45
0
4 5 0
4
50
45
0
450
4 5 5
4
5
5
45
5 455
4
55
455
455
455
460
4
6
0
460
460
460
465
4
6
5
465
46
5
470
4 70
470
4
7
5
4
7
5
475
48
0
4
8
0
4
8
0
480
4
8
0
480
485
4
8
5
4
8
5
4
8
5
48
5
485
48
5
485
48
5
485
485
485
4
8
5
485
4
8
5
485
4
8
5
4
9
0
4
9
0
4
9
0
49
0
490
4
9
0
3
9
0
395
4
0
0
4
0
0
4
0
5
4
0
5
405
405
4
1
0
4
1
0
41
0
4
1
5
4
1
5
415
4
2
0
4
2
0
420
4
2
5
425
4
2
5
4
2
5
4
2
5
430
430
4
3
0
4
3
0
4
3
0
4
3
5
4
3
5
4
3
5
43
5
4
35
440
440
440
445
445
445
445
450
450
455
455
455
460
460
460
465
465
465
465
4
6
5
470
470
470
4
7
0
475
475
475
480
480
480
485
485
485
N
k
e
e
r
C
n
o
y
n
a
C
rolled erosion control product
Filter rock checkdams with
103+00 to 107+52 Lt.
Filter rock check dams
110+42 to 112+40
Clearing limit
Silt fence
103+00 to 108+68 Rt.
Silt fence
109+30 Lt./Rt.
108+51 Lt/Rt.
Silt fence
107+47 to 108+49 Lt.
Silt fence
109+29 to 110+43 Lt.
Silt fence
109+11 to 110+22 Rt.
rolled erosion control product
Filter rock checkdams with
701+19 to 702+17 Lt.
rolled erosion control product
Filter rock checkdams with
700+46 to 701+20 Rt.
control product
checkdams with rolled erosion
700+22 to 700+45 Lt. Filter rock
1
0
5
70
0
1
1
0
F.7
STATE PROJECT
NUMBER
SHEET
]
U
S
_
S
u
r
_
f
t
2
D
[
c
:
\
m
y
f
i
l
e
s
\
p
w
_
p
r
o
d
u
c
t
i
o
n
\
d
0
2
0
3
2
2
7
\
w
a
-
a
2
0
1
3
0
2
0
_
d
f
.
d
g
n
WA JEFF 91420(1)
1
2
:
4
0
P
M
1
3
A
p
r
il
2
0
1
7
C
.
C
o
n
r
a
d
-
-
/
-
-
-
-
0
1
/
2
0
1
7
C
h
e
c
k
e
d
b
y
:
D
e
s
i
g
n
e
d
b
y
:
103+00 to 112+00
CONTROL PLAN
EROSION/SEDIMENT
LEGEND
rolled erosion control product
Filter rock check dams with
701+60 to 702+17 Rt.
Roadway Obliteration
Inlet Protection
Filter Rock Check Dam
Silt Fence
Flow Arrow
7
0
%
P
L
A
N
I
N
H
A
N
D
0
4
-
1
8
-
2
0
1
7
B7 - Sample 50'
u/s of construction
POC7 - Sample 200'
d/s of construction
or just u/s of Hoh
River confluence.
D7 - Sample at ditch
discharge point
D8 - Sample at ditch
discharge point
D9 - Sample at ditch
discharge point
D10 - Sample at
ditch discharge point D11 - Sample at
ditch discharge point
380
3
8
0
3
8
0
380
380
3
8
5
38
5
38
5
390
39
0
390
395 39
5
39
5
395
4
0
0
40
0
40
0
40
0
400
4
0
0
4
0
0
4
0
0
4
0
5 405
405
40
5
4
0
5
4
0
5
4
1
0
410
410
410
415
4
15
41
5
4
1
5
420
4
2
0
42
0
42
0
4
2
5
42
5
42
5
425
425
4
2
5
4
2
5
4
2
5
430
430
4
3
0
4
3
0
430
4
3
0
430
430
4
3
0
4
3
0
4
3
0
4
3
0
4
3
0
4
3
0
4
3
0
4
3
0
4
3
0
4
3
0
4
3
5
4
3
5
435
435
4
3
5
4
3
5
435
4
3
5
4
3
54
3
5
435
4
3
5
4
3
5
4
3
5
4
3
5
4
3
5
4
3
5
4
3
5
4
3
5
4
3
5
4
3
5
4
3
5
4
3
5
4
3
5
435
4
3
5
435
4
3
5
4
3
5
4
3
5
4
3
5
4
3
5
4
3
5
4
3
5
4
3
5
4
3
5
4
3
5
4
3
5
4
3
5
440
440
4
4
0
4 4 0
4
4
0
440
4
4
0
4
4
0
4
4
0
4
4
0
4
4
0
4
4
0
4
4
0
4
4
0
4
4
0
4
4
0
4
4
0
4
4
0
4
4
0
44
5
44
5
4
4
5
445
445
4
4
5
4
4
5
4
4
5
4
4
5
4
4
5
4
4
5
445
4
4
5
4
4
5
4
4
5
4
4
5
4
5
0
450
4
5
0
450
45
0
455
455
460
4
3
0
4
3
0
435
4
3
5
4
3
5
435
4
3
5
435
4
4
0
4
4
0
4
4
5
445
N
1
1
5
Clearing limit
Clearing limit
rolled erosion control product
Filter rock checkdam with
111+40 to 112+63 Rt.
F.8
STATE PROJECT
NUMBER
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WA JEFF 91420(1)
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112+00 to 117+03.39
CONTROL PLAN
EROSION/SEDIMENT
LEGEND
Filter rock check dams
112+71 to 117+02 Lt.
Filter rock check dams
112+63 to 117+02 Rt.
Roadway Obliteration
Inlet Protection
Filter Rock Check Dam
Silt Fence
Flow Arrow
70
%
PL
A
N
IN
HA
N
D
04
-
1
8
-
2
0
1
7
D12 - Sample at
ditch discharge point
D13 - Sample at
ditch discharge point
Water Quality Monitoring Plan
Upper Hoh River Bank Stabilization
ATTACHMENT C
ENVIRONMENTAL COMMITMENTS
(as identified in the project Final EA)
Water Quality Monitoring Plan Page | 1
Upper Hoh River Bank Stabilization Attachment C
Upper Hoh River Road Bank Stabilization and Culvert Replacement Project
Environmental Commitments
WFLHD, in partnership with Jefferson County, will construct two complementing mitigation
projects designed to improve long-term aquatic habitat conditions in the project area along the
mainstem Hoh River. In addition to these two mitigation projects discussed in more detail in the
Final EA, the following mitigation commitments will also be implemented as components of the
proposed project:
Conduct construction activities outside of critical nesting times for sensitive species,
where feasible, including critical nesting seasons for marbled murrelet (April 1 to
September 23) and Northern spotted owl (March 1 to September 30);
Conduct construction activities outside of critical spawning times for Chinook and
steelhead salmon, where feasible;
Utilize stream flow diversion, bypass, and fish exclusion methods at Tower Creek and
Canyon Creek to minimize downstream sedimentation impacts;
Implement all reasonable and prudent resource protection measures identified during
Endangered Species Act (ESA) consultation, and as prescribed by USFWS in the
Biological Opinion;
Adhere to all conditions in issued permits and approvals (e.g., Hydraulic Project
Approval, Clean Water Act [CWA] Section 404 Permit, CWA Section 401 Water Quality
Certification, CWA Section 402 Construction Stormwater General Permit, Shoreline
Substantial Development Permit); and
Justly compensate property owners for temporary construction easements or permanent
property acquisitions, according to the Uniform Relocation Assistance and Real Property
Acquisition Policies for Federal and Federally Assisted Programs (42 USC Chapter 61).
These specific measures would be implemented as part of construction:
Stabilize cleared ground as necessary to prevent erosion, particularly on slopes adjacent
to the Hoh River or its tributaries;
Employ standard best management practices (BMPs) at all project sites during
construction as required by the project Construction Stormwater General Permit. BMPs
would minimize the release of turbid water from the construction site, in order to protect
water quality, and would follow current permit requirements for erosion and sediment
control;
BMPs related to stormwater and erosion control will be implemented prior to
construction and maintained throughout construction and until vegetation is established:
Develop a Hazardous Material Spill Plan prior to construction; in the event of a
hazardous material spill, ensure that the contractor responds in compliance with the spill
plan;
Water Quality Monitoring Plan Page | 2
Upper Hoh River Bank Stabilization Attachment C
Implement dust control measures (e.g., apply water) as needed during construction;
Coordinate with utility owners to minimize service interruptions and provide advance
notice of service interruptions to affected parties;
To the extent possible, avoid direct impacts to power and telephone lines, poles, and
related structures during construction;
If avoidance of utilities is not feasible, work with utility providers to temporarily relocate
utility infrastructure;
Ensure outages will not last more than four hours;
Apply black cottonwood bark-like concrete form-liner texture to dolosse, instead of
smooth finish, to help the structures better blend into the environment;
Place signage in advance of and during construction to inform the public in advance;
Ensure all equipment has muffled exhaust and has sound control devices no less effective
than those provided on the original equipment;
Ensure all equipment complies with pertinent Environmental Protection Agency noise
standards and the Jefferson County Code;
Shut off idling equipment whenever possible;
If a specific noise complaint is anticipated due to noisy construction, notify nearby
residents in advance of such work or install temporary acoustic barriers around stationary
noise sources, if possible;
Coordinate temporary traffic control devices to provide the least impact to motorized
users;
Position equipment to maintain access to local properties along the construction corridor;
Use flaggers and temporary battery- or solar-powered traffic signals to maintain access
during long-term road closures;
Provide pilot cars to guide residents or parks visitors through construction zones, as
appropriate during lane closures;
Coordinate with Olympic National Park so that notice of the Upper Hoh River Road
(UHRR) closure is posted on ONP’s website;
Limit removal of mature trees greater than 21 inches dbh to those whose removal is
necessary for construction;
For the ELJ/dolosse units, source logs from outside the project area;
Maintain fire and emergency services access during construction;
Develop specific emergency procedures prior to the potential winter road closure and
implement them if emergency vehicle passage is required during road closure;
Coordinate with residents to the extent practical to ease access during construction; and
Water Quality Monitoring Plan Page | 3
Upper Hoh River Bank Stabilization Attachment C
Coordinate with the local school district to ensure students are served during the winter
road closure.
The contractor will implement the following measures after construction and during re-
vegetation:
After ELJ/dolosse unit placement, restore disturbed areas, including stream buffers, at a
1:1 impact-to-mitigation ratio; restoration would include re-planting (1) vegetation
salvaged from the site, and (2) supplemental plantings from native nursery stock;
Monitor restored planting sites for at least five years to ensure successful re-vegetation;
Use at least 5-gallon size trees when planting the riparian zone to speed up establishment;
Revegetate all streambanks and riparian areas temporarily disturbed by bank stabilization
activities with native coniferous and deciduous trees;
Use an FHWA-approved native seed mixture;
Place only certified weed-free mulch and straw bales;
Ensure all equipment used in the project area is free of weed seed;
Take precautions to prevent introduction and spread of weeds caused by moving weed-
infested material;
Notify and or coordinate vegetation management activities with land owners within or
adjacent to the transportation right-of-way (ROW) that is proposed for treatment;
Design cut-slopes to take advantage of natural rock and soil material characteristics as
they are encountered;
Design cut-slopes in soil or granular materials to be as flat as practicable to minimize
ravel, surface erosion, and slope instability, and to promote re-vegetation while
maintaining an acceptable level of slope stability;
Conserve and stockpile topsoil for later use to enhance revegetation success;
Use locally native plants to improve the revegetation rate; and
Stake straw wattles where appropriate.