AK SuckerCreek AOP Report Final.pdf
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- Attached to
- AK FWS KNA 74525(1) Swan Lake Road Project
- Solicitation number
- 69056723B000020
About this file
This document package includes technical specifications for an aquatic organism passage (AOP) culvert replacement project on Swan Lake Road near Sucker Creek in the Kenai National Wildlife Refuge in Alaska. The project involves replacing two existing 42-inch culverts with a larger structural plate pipe arch culvert to improve fish and aquatic organism passage. Specifications cover culvert design criteria including hydrologic analysis, hydraulic modeling, and streambed material gradations. Construction requirements include timing windows, dewatering, erosion control, and channel reconstruction. The package provides design drawings, calculations, and appendices specifying material types and gradations for the streambed, banks, and armoring. This project is in response to Solicitation Number 69056723B000020 issued by the Department of Transportation Federal Highway Administration for the AK FWS KNA 74525(1) Swan Lake Road Project.
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Memorandum
Western Federal Lands Highway Division 610 E. Fifth Street
Vancouver, WA 98661-3801
SWAN LAKE / SWANSON RIVER ROAD
SUCKER CREEK AOP HYDRAULICS REPORT
To: Stacy Bluhm, WFLHD Project Manager
From: James Neighorn, P.E. and Vernon Bevan, WFLHD Hydraulics Engineer
Date: June 20, 2023
Project: Swan Lake / Swanson River Road – AK FWS Kenai 74525(1)
Background
The Kenai National Wildlife Refuge (NWR) is rehabilitating Swan Lake Road and Swanson River Road to improve access to public recreation along the corridors, increase transportation safety, and to mitigate damage to wildlife and aquatic organism passage. As part of the project the NWR is replacing a culvert located on Swan Lake Road where it crosses Sucker Creek, Kenai National Wildlife Refuge, Kenai
Peninsula Borough, Alaska. Western Federal Lands Highway Division (WFLHD) is designing the replacement structure. The Kenai NWR will maintain the new structure. Recommendations for the proposed aquatic organism passage (AOP) structure design are presented.
AOP Design Criteria
The proposed AOP structure has been designed following the requirements Culvert Design Guidelines for
Ecological Function (U.S. Fish and Wildlife 2021) and per Stream Simulation: An Ecological Approach to
Providing Passage for Aquatic Organisms at Road-Stream Crossings (USDA-Forest Service 2008). These documents provide simplified design methodologies intended to mimic natural stream processes within the culvert. Sediment transport, debris conveyance and streambed morphology within the culvert should replicate these processes as they occur in the natural channel upstream and downstream of the culvert.
Determination of the high and low fish passage design flows, water velocity, and water depth is not required for this method since the stream hydraulic characteristics within the culvert are intended to replicate the stream conditions upstream and downstream of the crossing. AOP culvert design utilizes streambed materials and sizes which occur in the natural channel, providing similar channel complexity, flow depth, flow velocities, and resting areas.
USFW Alaska Fish Passage Program (USFW/AFPP) Guidelines
The AOP design for the Sucker Creek outfall crossing is consistent with the 2021 U.S. Fish and Wildlife
(USFW) Service design guidelines. The 2021 document generally follows the U.S. Forest Service stream simulation approach with certain modifications. The basis for AOP design is the geomorphic analog method. The underlying philosophy of the geomorphic analog method is similar to the stream simulation approach. However, many of the design criteria are based on the 100-year flood event as opposed to a specifically selected design flood. The following USFW/AFPP requirements have been incorporated into the AOP design:
Flood and Debris Conveyance: Culvert capacity is designed to accommodate the 100-year recurrence flood without interfering with the functioning of the floodplain while providing adequate clearance above the flood stage for expected debris. The headwater depth to opening depth ratio should be less than 0.8.
Crossing Location: Crossing structure is placed within the pre-development natural channel alignment
Memo to: Stacy Bluhm, WFLHD Project Manager
June 2023 wherever possible.
Culvert Width: Must accommodate the design channel bankfull width plus additional width for construction of stable bank rocks along both sides of the channel inside the culvert. All culverts will meet design requirements for a 6-foot minimum diameter.
Channel Vertical Clearance: Clearance from bed to ceiling must be at least 4-feet to allow for ease of construction, maintenance, and debris removal. Where possible, clearance will be 5-feet or greater.
Channel Slope: Reconstructed streambed within the culvert approximates the average slope of the stream reference reach. The slope should not deviate by more than 25% from the natural stream slope of the reference reach.
Embedment: Bottoms of round culverts should be buried below the streambed thalweg a minimum of
40% of the pipe diameter. Box or pipe arch culverts should be buried a minimum of 20% of the culvert’s rise.
Maximum Length of Road Crossing: Length should be less than 150-feet.
Fill Materials: Fill materials are generally comprised of sediment similar in size composition to natural bed materials that form the natural stream channel above and below the road crossing. Larger material is added to assist grade retention and provide resting areas for migrating fish. A dense, well-graded mixture is specified, with washing in of fines between constructed lifts, to encourage the stream to flow on the surface.
Fill/substrate material for culverts without an adequate sediment supply, such as those situated below a lake or wetland, should be designed to resist the predicted critical shear forces of the 100-year flood.
Water Depth and Velocity: Bankfull water depths and velocities in the culvert must closely resemble those existing reference reach as specified in the 2021 USFW Service guidance document.
Sucker Creek AOP Culvert
United States Fish and Wildlife Service (USFWS) has determined that the Sucker Creek crossing requires an AOP structure (60°43'29.43"N, 150°40'41.76"W NAD1983). Federal Lands Highway Division conducted field reconnaissance of the crossing in 2019 and 2021.
The crossing is located on Sucker Creek, roughly 800-feet downstream of Sucker Lake and approximately
1-mile upstream from the confluence of Swan Creek (Figure 1). Sucker Creek crosses Swan Lake Road through two 42-inch diameter CMPs. The crossing is located just downstream from a series of beaver dams, with the nearest beaver dam roughly 30-feet upstream of the crossing (Photos 4 and 5). The upstream reach is heavily influenced by the presence of beaver dams; therefore, observations and measurements within the upstream reach do not reflect channel forming processes downstream of the crossing. The upstream reach, which stretches from Swan Lake Road to Sucker Lake, reflects the influence of beaver activity and does not exhibit typical stream channel processes or morphology. The estimated stream width is roughly 50-feet
(Photo 5). The observed channel was relatively straight, wide, deep, and slow moving. Lots of small to moderate sized woody debris was observed within the reach, likely supplied from the lake and adjacent channel banks and amplified by beaver activity (Photos 4 and 5).
Downstream of the crossing, the channel slope is roughly 1.0% and riffle-pool is the dominant bed form.
Bankfull width measurements in the downstream reach, were between 16 and 17-feet (Photo 8). Bankfull depths were measured between 1.0 to 2.3 feet. Bed material is mostly sand and cobble with some gravel and boulders (Photos 7 and 9). A streambed pebble count was performed at the channel riffle downstream of the crossing. The data was processed using FHWA Hydraulic Toolbox, version 4.2, to compute the resulting gradation: D100 10-inches, D85 3.5-inches, D50 1.6-inches, and D15 0.12-inches (Figure 3). The stream appears stable with riffle crest vertical controls, a low accessible floodplain, and well vegetated banks (Photo 8). The channel is unconfined, with a flood-prone width estimated at roughly 50-feet. Based on observed field conditions, the stream can likely carry a moderate amount of small sized woody debris.
Stream flow may be low when fish passage is needed.
The existing crossing is served by two 42-inch CMPs which are in fair condition (Photos 1 and 6). One of the existing pipes appears to be slightly elevated and is likely activated during higher flows (Photo 3 and
6). The other pipe is situated within the main channel and active during low and high flows (Photos 2 and
6). The roadway elevation provides adequate cover over the existing culvert. Excessive scour at the culvert outfall was not observed and both culverts appeared free of woody debris. The existing culverts are situated perpendicular to the roadway and well aligned with the stream thalweg.
Recommendations:
A larger pipe will be necessary to provide space for bankfull width, a natural channel bottom, and stable banks. The upstream complex of beaver dams will impact the amount and type of sediment supplied to the culvert. The designed streambed sediment will need to account for limited sediment supply by augmenting the streambed gradation with larger cobbles and boulders.
• Install a 72-foot long, structural plate pipe arch with a 19.5-foot span and a 12.5-foot rise.
• Place the culvert at a 0.84% slope to match channel slopes at the crossing by setting the inverts at elevation 178.5-feet upstream and at elevation 177.9-feet downstream (project datum).
• Embed the culvert a minimum of 3.75 feet and backfill the culvert interior with streambed material conserved during excavation of the culvert. If the conserved streambed material quantity is insufficient for backfilling the culvert, use material similar to the natural streambed material.
Streambed material will be augmented with Class D gradation cobbles specified in the attached
Special Contract Requirements (SCR) and Gradation Stability Calculations to provide a dynamically stable substrate.
• Allow clearance for debris passage and maintenance access by providing 8.75 feet of clearance from the crown of the culvert and the installed bed material and providing a headwater to depth of opening ratio (HW/D) of less than 0.8.
• Construct a channel with a bankfull width of 16 feet and a bankfull depth of 2 feet including a low flow channel and streambanks inside the culvert to provide resting opportunities for fish.
• Install 4 rock weirs spaced at 16-foot intervals to help maintain banks and channel shape.
• Install 4 round boulders, approximately 24-inches in diameter for inducing channel migration and providing low velocity fish resting areas.
• Install concrete collars to mitigate the influence of frost heaving at pipe ends.
• Install Class 3 riprap (FHWA FP-14), minimum 3 feet thick, at the inlet and outlet for controlling erosion near the culvert.
Construction
The Alaska Department of Fish and Wildlife instream work period is May 15 to July 15. Temporary flow deflectors placed for isolating the work area and diverting the stream flow must have a minimum height of
3-feet above the stream bottom and be stable assuming 5-feet per second parallel flow. Use plastic-lined channels or pipes for temporally conveying stream flow through the construction area. Protect the outfalls from erosion. Ensure fish can pass smoothly through the diversion. Temporary stream diversions in place must provide an equivalent capacity to a 3-foot diameter pipe or demonstrate a minimum flow capacity equal to the 2-year discharge (169-cfs). Before installing the flow deflectors, remove fish from the work area to the level and methods meeting the 2009 ADF&G and FHWA Fish Habitat MOU requirements.
Full construction area dewatering is expected up to the groundwater level for excavation and installing the culvert, streambed material, backfill, and riprap. Water pumped from work area must be discharged at an upland treatment area near the site.
Temporary access route adjacent to the road embankment is needed for installing flow barriers, removing the channel debris, and completing culvert inlet, interior, and outlet work.
Stream Impacts
The proposed fish passage culvert is expected to dramatically improve stream flow conveyance, sediment transport, and woody debris transport to a level comparable to reaches upstream and downstream of the culvert. A moderate amount of turbidity and sediment is expected to be released when the flow barriers are removed, and stream flow is introduced into the newly constructed culvert. The amount of turbidity and sediment will be reduced by removing the flow barriers gradually introducing the stream flow over an extended two to three-hour time.
Operation and Maintenance
Scour or aggradation of the streambed is also expected to occur to some extent, as would be expected for the natural stream. Monitoring at regular intervals, and ideally during flood events, will be especially important during the first few years to ensure that excessive debris accumulation, scour, or aggradation does not impair passage through the culvert. Increase the frequency of culvert inspections and debris removal for the first three years. Fish boulders placed within the culvert and stream channel should be inspected annually and after each extreme flood event to ensure effective backwater and bed retention.
Replace or reposition dislodged rock or boulders. Additional rock may need to be installed to correct erosion or channel degradation. Riprap placed at the culvert inlet and outlet should be inspected annually and after each extreme flood event. Replace or reposition dislodged stone.
Floodplain and Flood-rise Impacts
Flood limits and elevations have not been mapped by the National Flood Insurance Program for the site.
The proposed culverts will improve hydraulic conveyance and is not expected to negatively impact flooding at the site.
Hydrology
The USGS StreamStats (version 4) web-based application was used for delineating the watershed and calculating drainage area (15.5 sq. miles) and mean annual precipitation (17-inches). Since delineations made by StreamStats can include inaccuracies for smaller watersheds and flat areas, the delineated watershed was verified by comparing it to both USGS TOPO maps and Digital Terrain Maps produced by the Alaska Division of Geological and Geophysical Surveys. No significant deviations that would impact flow estimates were found.
Peak discharges were estimated with StreamStats using USGS regression equations from Magnitude and
Frequency at Gaged and Ungaged Sites on Streams in Alaska and Conterminous Basins in Canada (USGS
WRIR 2016-5024). The watershed is mostly comprised of forested land and surface water (Figure 2).
Dozens of lakes are located within the basin and their presence can influence the amount of runoff generated by the basin. Lakes can increase runoff by increasing the amount of impervious surface area, or conversely, lakes can act to attenuate flows. Hydraulic modeling of the channel and the existing culverts indicate that the flows derived from the USGS regression equations are likely reasonable estimates of the basin’s hydrology. A summary of peak discharges and their corresponding water depths at the culvert inlet are presented in Table 1.
Dominant flooding is from snow melt. Larger floods typically occur in April and May. Rain-on-snow flood events can occur in October through December. Lower flows typically occur from January to February and
July through September.
Culvert Hydraulics
Water surface profiles and culvert capacities were estimated using the FHWA Culvert Hydraulics Analysis
Program, HY-8, version 7.7 (results attached). Floods larger than the 2-year were analyzed assuming culvert slope of 0.83 percent and Manning’s Roughness coefficient of 0.035 for the channel bottom and 0.034 for the culvert sides and top.
The computed outlet tailwater depth of 2.0 feet for the 2-year discharge was compared with the bankfull channel design depth of 2.0 and found to be within the measured range of the 1.0 to 2.3 feet in the natural channel.
Hydraulic results are included in the attachments with headwater depths and ratios shown in Table 2.
Attachments: Table 1 - Peak Discharge Estimates
Table 2 – Headwater Depths and Ratios
Figures 1, 2, and 3
Photographs
HY-8 Calculations
USGS StreamStats Report
Drawings
Special Contract Requirements and Gradation Stability Calculations
Tables
| Table | 1. | Peak | Discharges | Estimates |
| Peak | Annual | Floods | Discharge | (ft3/2) |
| 2‐Year | 169 |
| 5‐Year | 292 |
| 10‐Year | 389 |
| 25‐Year | 522 |
| 50‐Year | 626 |
| 100‐Year | 738 |
| 200‐Year | 854 |
| 500‐Year | 1020 |
Table 2. Peak Discharges and Water Depths
| Peak | Annual | Floods | Discharge | (ft3/2) | Headwater | Depth | (ft) |
| 2‐Year | 169 2.23 | ||||||
| 50‐Year | 626 5.37 | ||||||
| 100‐Year | 738 6.03 |
Image date: 4/17/2011
Project AOP Culvert Site Location
Project Area Location
USGS Topographic Maps on Google Earth
N
FIGURE 1
SUCKER CREEK
AOP CULVERT
SITE LOCATION
AOP
1000 feet0
Sucker
Map printed from Google Earth, Image date 4/17/2011.
N
DA = 15.5 sq. mi.
FIGURE 2
SUCKER CREEK
AOP CULVERT
DRAINAGE AREA
0 8000 feet
Photos
PHOTO 1
PHOTO 2
PHOTO 3
6/5/2019
Sucker Creek AOP
Existing 42" culvert inlet. Perched with no flow.
Existing 42" culvert inlet.
Right culvert inlet, looking downstream.
Culvert inlets.
Looking downstream at double 42" diameter culverts on Sucker Creek. Left culvert is flowing roughly 1/4 full, right culvert is perched with no flow.
Left culvert inlet, looking downstream.
PHOTO 4
PHOTO 5
PHOTO 6
6/5/2019
Sucker Creek AOP
Looking upstream at double 42" diameter culverts on Sucker Creek.
Right culvert is flowing roughly 1/4 full, left culvert is perched with no flow.
Beaver Dam upstream of crossing.
Beaver dam located immediately upstream of crossing. The beaver dam is roughly 3-feet tall. Some water flows over the beaver dam directly into the inlet. Most of the channel flows around the beaver dam, on the right side looking downstream.
Channel upstream of crossing.
A series of multiple beaver dams can be found upstream. The water is relatively deep (~4'), wide (~50'), and slow moving due to the beaver dams. In the distance is Sucker Lake, ~800' upstream of the crossing.
Culvert outlets.
PHOTO 7
PHOTO 8
PHOTO 9
6/5/2019
Sucker Creek AOP
Exposed gravel bar
Roughly 50' downstream of crossing the channel flows over and around large boulders within the channel.
Channel alluvium material visible on exposed bar. Measuring tape is open to 3-feet.
Channel downstream of crossing.
Roughly 100' downstream of the crossing the channel settles into a meandering riffle/pool structure with a sand gravel bed. Bankfull widths measured around 16' to 17' wide.
Channel immediately downstream of crossing.
HY-8 Culvert Analysis Report - Proposed AOP Crossing Discharge Data Discharge Selection Method: Specify Minimum, Design, and Maximum Flow
Minimum Flow: 169.00 cfs
Design Flow: 626.00 cfs
Maximum Flow: 738.00 cfs
Table 1 - Summary of Culvert Flows at Crossing: Sucker Creek Headwater Elevation (ft)
Total Discharge (cfs)
Sucker Creek Discharge (cfs)
Roadway Discharge (cfs)
Iterations
184.50 169.00 169.00 0.00 1
185.09 225.90 225.90 0.00 1
185.50 282.80 282.80 0.00 1
185.89 339.70 339.70 0.00 1
186.25 396.60 396.60 0.00 1
186.61 453.50 453.50 0.00 1
186.95 510.40 510.40 0.00 1
187.29 567.30 567.30 0.00 1
187.63 626.00 626.00 0.00 1
187.96 681.10 681.10 0.00 1
188.29 738.00 738.00 0.00 1
193.30 1607.78 1607.78 0.00 Overtopping
Rating Curve Plot for Crossing: Sucker Creek
Culvert Data: Sucker Creek
Table 1 - Culvert Summary Table: Sucker Creek Total Discharge (cfs)
Culvert Discharge (cfs)
Headwater Elevation (ft)
Inlet Control Depth (ft)
Outlet Control Depth (ft)
Flow Type
Normal Depth (ft)
Critical Depth (ft)
Outlet Depth (ft)
Tailwater Depth (ft)
Outlet Velocity (ft/s)
Tailwater Velocity (ft/s)
169.00 cfs 169.00 cfs 184.50 2.14 2.248 3- M1t
1.75 1.33 1.95 1.95 4.53 5.79
225.90 cfs 225.90 cfs 185.09 2.61 2.840 3- M1t
2.12 1.62 2.69 2.69 4.43 4.31
282.80 cfs 282.80 cfs 185.50 3.04 3.254 3- M1t
2.47 1.88 2.92 2.92 5.14 4.37
339.70 cfs 339.70 cfs 185.89 3.44 3.637 3- M1t
2.80 2.12 3.10 3.10 5.84 4.47
396.60 cfs 396.60 cfs 186.25 3.82 4.004 3- M1t
3.13 2.36 3.25 3.25 6.52 4.57
453.50 cfs 453.50 cfs 186.61 4.19 4.357 3- M2t
3.44 2.57 3.37 3.37 7.20 4.71
510.40 cfs 510.40 cfs 186.95 4.53 4.700 3- M2t
3.76 2.78 3.46 3.46 7.91 4.93
567.30 cfs 567.30 cfs 187.29 4.86 5.039 3- M2t
4.07 2.99 3.54 3.54 8.59 5.14
626.00 cfs 626.00 cfs 187.63 5.19 5.385 3- M2t
4.40 3.19 3.63 3.63 9.28 5.35
681.10 cfs 681.10 cfs 187.96 5.50 5.707 3- M2t
4.72 3.38 3.70 3.70 9.90 5.53
738.00 cfs 738.00 cfs 188.29 5.83 6.037 3- M2t
5.05 3.56 3.78 3.78 10.53 5.70
Culvert Barrel Data Culvert Barrel Type Straight Culvert
Inlet Elevation (invert): 182.25 ft, Outlet Elevation (invert): 181.65 ft
Culvert Length: 72.00 ft, Culvert Slope: 0.0083
Culvert Performance Curve Plot: Sucker Creek
Site Data - Sucker Creek Site Data Option: Culvert Invert Data
Inlet Station: 0.00 ft
Inlet Elevation: 178.50 ft
Outlet Station: 72.00 ft
Outlet Elevation: 177.90 ft
Number of Barrels: 1
Culvert Data Summary - Sucker Creek Barrel Shape: Pipe Arch
Barrel Span: 232.22 in
Barrel Rise: 150.30 in
Barrel Material: Steel Structural Plate
Embedment: 45.00 in
Barrel Manning's n: 0.0340 (top and sides)
Manning's n: 0.0350 (bottom)
Culvert Type: Straight
Inlet Configuration: Beveled Edge (Ke=0.2)
Inlet Depression: None
Tailwater Data for Crossing: Sucker Creek
Table 2 - Downstream Channel Rating Curve (Crossing: Sucker Creek) Flow (cfs) Water
Surface Elev (ft)
Velocity (ft/s)
Depth (ft) Shear (psf) Froude Number
169.00 183.60 1.95 5.79 1.22 0.75
225.90 184.34 2.69 4.31 1.68 0.73
282.80 184.57 2.92 4.37 1.82 0.74
339.70 184.75 3.10 4.47 1.93 0.74
396.60 184.90 3.25 4.57 2.03 0.75
453.50 185.02 3.37 4.71 2.10 0.76
510.40 185.11 3.46 4.93 2.16 0.77
567.30 185.19 3.54 5.14 2.21 0.78
626.00 185.28 3.63 5.35 2.26 0.79
681.10 185.35 3.70 5.53 2.31 0.79
738.00 185.43 3.78 5.70 2.36 0.80
Tailwater Channel Data - Sucker Creek Tailwater Channel Option: Irregular Channel
Channel Slope: Irregular Channel
User Defined Channel Cross-Section Coord No. Station (ft) Elevation (ft) Manning's n 1 0.00 189.00 0.0550 2 10.00 185.00 0.0350 3 42.00 183.65 0.0350 4 43.00 181.65 0.0350 5 57.00 181.65 0.0350 6 58.00 183.65 0.0350 7 90.00 185.00 0.0550 8 100.00 189.00 0.0000
Roadway Data for Crossing: Sucker Creek Roadway Profile Shape: Constant Roadway Elevation
Crest Length: 200.00 ft
Crest Elevation: 193.30 ft
Roadway Surface: Gravel
Roadway Top Width: 28.00 ft
HY-8 Culvert Analysis Report - Existing Conditions
Crossing Discharge Data
Discharge Selection Method: Specify Minimum, Design, and Maximum Flow
Minimum Flow: 169.00 cfs
Design Flow: 626.00 cfs
Maximum Flow: 738.00 cfs
Table 1 - Summary of Culvert Flows at Crossing: Sucker Creek Existing Conditions
Headwater Elevation (ft)
Total Discharge (cfs)
Sucker Creek Discharge (cfs)
Floodplain Overflow Discharge (cfs)
Roadway Discharge (cfs)
Iterations
189.08 169.00 91.66 77.35 0.00 8
192.04 225.90 118.25 105.30 2.25 7
192.35 282.80 120.45 107.68 54.34 6
192.54 339.70 121.75 109.17 108.43 5
192.71 396.60 122.83 110.40 163.20 5
192.85 453.50 123.75 111.45 217.79 4
192.98 510.40 124.60 112.42 272.96 4
193.10 567.30 125.39 113.31 328.38 4
193.22 626.00 126.15 114.16 385.58 4
193.32 681.10 126.81 114.91 438.87 3
193.43 738.00 127.47 115.64 494.59 3
192.00 222.81 117.86 104.96 0.00 Overtopping
Rating Curve Plot for Crossing: Sucker Creek Existing Conditions
Culvert Data: Sucker Creek
Table 1 - Culvert Summary Table: Sucker Creek
Total Discharge (cfs)
Culvert Discharge (cfs)
Headwater Elevation (ft)
Inlet Contro l Depth (ft)
Outlet Contr ol Depth (ft)
Flow Type
Normal Depth (ft)
Critical Depth (ft)
Outlet Depth (ft)
Tailwater Depth (ft)
Outlet Velocity (ft/s)
Tailwater Velocity (ft/s)
169.00 cfs 91.66 cfs 189.08 7.09 7.496 7-M2c 3.50 2.97 2.97 1.81 10.54 5.26
225.90 cfs 118.25 cfs 192.04 10.44 10.461 7-M2c 3.50 3.24 3.24 2.15 12.73 4.67
282.80 cfs 120.45 cfs 192.35 10.77 10.734 7-M2c 3.50 3.25 3.25 2.30 12.92 3.72
339.70 cfs 121.75 cfs 192.54 10.96 10.898 7-M2c 3.50 3.26 3.26 2.42 13.04 3.49
396.60 cfs 122.83 cfs 192.71 11.13 11.033 7-M2c 3.50 3.27 3.27 2.52 13.14 3.42
453.50 cfs 123.75 cfs 192.85 11.27 11.156 7-M2c 3.50 3.27 3.27 2.61 13.22 3.42
510.40 cfs 124.60 cfs 192.98 11.40 11.260 7-M2c 3.50 3.28 3.28 2.69 13.30 3.45
567.30 cfs 125.39 cfs 193.10 11.52 11.367 7-M2c 3.50 3.28 3.28 2.77 13.38 3.50
626.00 cfs 126.15 cfs 193.22 11.64 11.461 7-M2c 3.50 3.29 3.29 2.85 13.45 3.55
681.10 cfs 126.81 cfs 193.32 11.74 11.552 7-M2c 3.50 3.29 3.29 2.92 13.51 3.61
738.00 cfs 127.47 cfs 193.43 11.85 11.634 7-M2c 3.50 3.30 3.30 2.99 13.57 3.67
Inlet Elevation (invert): 181.58 ft, Outlet Elevation (invert): 181.56 ft
Culvert Length: 56.04 ft, Culvert Slope: 0.0003
Culvert Performance Curve Plot: Sucker Creek
Water Surface Profile Plot for Culvert: Sucker Creek
Site Data - Sucker Creek
Inlet Station: 0.00 ft
Inlet Elevation: 181.58 ft
Outlet Station: 56.04 ft
Outlet Elevation: 181.56 ft
Number of Barrels: 1
Culvert Data Summary - Sucker Creek
Barrel Shape: Circular
Barrel Diameter: 3.50 ft
Barrel Material: Corrugated Steel
Embedment: 0.00 in
Barrel Manning's n: 0.0240
Culvert Type: Straight
Inlet Configuration: Thin Edge Projecting (Ke=0.9)
Culvert Data: Floodplain Overflow
Table 2 - Culvert Summary Table: Floodplain Overflow
Total Discharge (cfs)
Culvert Discharge (cfs)
Headwater Elevation (ft)
Inlet Control Depth (ft)
Outlet Control Depth (ft)
Flow Type
Normal Depth (ft)
Critical Depth (ft)
Outlet Depth (ft)
Tailwater Depth (ft)
Outlet Velocity (ft/s)
Tailwater Velocity (ft/s)
169.00 cfs 77.35 cfs 189.08 5.70 5.624 7-M2c 3.50 2.75 2.75 1.81 9.54 5.26
225.90 cfs 105.30 cfs 192.04 8.66 8.488 7-M2c 3.50 3.13 3.13 2.15 11.61 4.67
282.80 cfs 107.68 cfs 192.35 8.97 8.758 7-M2c 3.50 3.15 3.15 2.30 11.81 3.72
339.70 cfs 109.17 cfs 192.54 9.16 8.930 7-M2c 3.50 3.16 3.16 2.42 11.94 3.49
396.60 cfs 110.40 cfs 192.71 9.33 9.065 7-M2c 3.50 3.17 3.17 2.52 12.04 3.42
453.50 cfs 111.45 cfs 192.85 9.47 9.190 7-M2c 3.50 3.18 3.18 2.61 12.13 3.42
510.40 cfs 112.42 cfs 192.98 9.60 9.311 7-M2c 3.50 3.19 3.19 2.69 12.21 3.45
567.30 cfs 113.31 cfs 193.10 9.72 9.417 7-M2c 3.50 3.20 3.20 2.77 12.29 3.50
626.00 cfs 114.16 cfs 193.22 9.84 9.513 7-M2c 3.50 3.21 3.21 2.85 12.37 3.55
681.10 cfs 114.91 cfs 193.32 9.94 9.609 7-M2c 3.50 3.21 3.21 2.92 12.43 3.61
738.00 cfs 115.64 cfs 193.43 10.05 9.692 7-M2c 3.50 3.22 3.22 2.99 12.50 3.67
Inlet Elevation (invert): 183.38 ft, Outlet Elevation (invert): 182.86 ft
Culvert Length: 57.25 ft, Culvert Slope: 0.0090
Culvert Performance Curve Plot: Floodplain Overflow
Water Surface Profile Plot for Culvert: Floodplain Overflow
Site Data - Floodplain Overflow
Inlet Station: 0.00 ft
Inlet Elevation: 183.38 ft
Outlet Station: 57.25 ft
Outlet Elevation: 182.86 ft
Number of Barrels: 1
Culvert Data Summary - Floodplain Overflow
Barrel Shape: Circular
Barrel Diameter: 3.50 ft
Barrel Material: Corrugated Steel
Embedment: 0.00 in
Barrel Manning's n: 0.0240
Culvert Type: Straight
Inlet Configuration: Thin Edge Projecting (Ke=0.9)
Tailwater Data for Crossing: Sucker Creek Existing Conditions
Table 2 - Downstream Channel Rating Curve (Crossing: Sucker Creek Existing Conditions)
Flow (cfs) Water Surface Elev (ft)
Velocity (ft/s) Depth (ft) Shear (psf) Froude Number
169.00 183.38 1.81 5.26 0.95 0.72
225.90 183.71 2.15 4.67 1.12 1.59
282.80 183.86 2.30 3.72 1.20 1.01
339.70 183.98 2.42 3.49 1.27 0.84
396.60 184.08 2.52 3.42 1.32 0.75
453.50 184.18 2.61 3.42 1.37 0.71
510.40 184.26 2.69 3.45 1.41 0.67
567.30 184.34 2.77 3.50 1.45 0.65
626.00 184.42 2.85 3.55 1.49 0.64
681.10 184.48 2.92 3.61 1.53 0.63
738.00 184.55 2.99 3.67 1.57 0.62
Tailwater Channel Data - Sucker Creek Existing Conditions
Tailwater Channel Option: Irregular Channel
Channel Slope: Irregular Channel
User Defined Channel Cross-Section
Coord No. Station (ft) Elevation (ft) Manning's n
1 0.00 189.00 0.0550
2 10.00 183.65 0.0550
3 90.00 183.65 0.0550
4 92.00 181.56 0.0350
5 108.00 181.56 0.0350
6 110.00 183.65 0.0550
7 190.00 183.65 0.0550
8 200.00 189.00 0.0000
Roadway Data for Crossing: Sucker Creek Existing Conditions
Roadway Profile Shape: Constant Roadway Elevation
Crest Length: 100.00 ft
Crest Elevation: 192.00 ft
Roadway Surface: Gravel
Roadway Top Width: 28.00 ft
Sucker Creek
Basin Characteristics
Parameter Code Parameter Description Value Unit
DRNAREA Area that drains to a point on a stream 15.5 square miles
PRECPRIS00 Basin average mean annual precipitation for 1971 to 2000 from PRISM
17 inches
Region ID: AK Workspace ID: AK20191001192926753000 Clicked Point (Latitude, Longitude): 60.72490, -150.68129 Time: 2019-10-01 12:29:43 -0700
Page 2 of 4StreamStats
10/1/2019https://streamstats.usgs.gov/ss/
Peak-Flow Statistics Parameters[Peak Areas less than 1000 sqmi SIR 2016 5024]
Parameter Code Parameter Name Value Units
Min Limit
Max Limit
DRNAREA Drainage Area 15.5 square miles
0.4 1000
PRECPRIS00 Mean Annual Precip PRISM 1971 2000
17 inches 8 280
Peak-Flow Statistics Flow Report[Peak Areas less than 1000 sqmi SIR 2016 5024]
PIl : Prediction Interval-Lower, PIu: Prediction Interval-Upper, SEp: Standard Error of Prediction, SE: Standard Error (other -- see report)
Statistic Value Unit PIl PIu SEp
2 Year Peak Flood 169 ft^3/s 59.1 485 70.8
5 Year Peak Flood 292 ft^3/s 104 821 69.1
10 Year Peak Flood 389 ft^3/s 138 1090 69.2
25 Year Peak Flood 522 ft^3/s 182 1500 71.2
50 Year Peak Flood 626 ft^3/s 214 1840 72.8
100 Year Peak Flood 738 ft^3/s 247 2210 74.6
200 Year Peak Flood 854 ft^3/s 276 2640 77.4
500 Year Peak Flood 1020 ft^3/s 312 3300 81.9
Peak-Flow Statistics Citations
Curran, J.H., Barth, N.A., Veilleux, A.G., and Ourso, R.T.,2016, Estimating Flood Magnitude and Frequency at Gaged and Ungaged Sites on Streams in Alaska and Conterminous Basins in Canada, Based on Data through Water Year 2012: U.S.
Geological Survey Scientific Investigations Report 2016-5024, 47 p.
(http://dx.doi.org/10.3133/sir20165024http://dx.doi.org/10.3133/sir20165024)
USGS Data Disclaimer: Unless otherwise stated, all data, metadata and related materials are considered to satisfy the quality standards relative to the purpose for which the data were collected. Although these data and associated metadata have been reviewed for accuracy and completeness and approved for release by the U.S.
Geological Survey (USGS), no warranty expressed or implied is made regarding the display or utility of the data for other purposes, nor on all computer systems, nor shall the act of distribution constitute any such warranty.
Page 3 of 4StreamStats
10/1/2019https://streamstats.usgs.gov/ss/
SCALE IN FEET
10 0 10 20 30 40
OUTLETINLETPIPEHYDRAULIC INFORMATION
0 20 40 60 8020406080
LENGTH: 72 ft
PIPE SLOPE: 0.0084 ft/ft
HEADWALL: Conc./Riprap
FLOWLINE SLOPE: 0.0084 ft/ft
100 120100120140
Q : 169 CFS
Q : 626 CFS
BANKFULL CHANNEL WIDTH: 16 ft
TYPE: Struct. Plt. Pipe Arch SPAN: 19.5 ft RISE: 12.5 ft
LOWER BEVEL HEIGHT: 3.73 LOWER BEVEL HEIGHT: 3.73
BEVEL: 1.5h : 1v
HEADWALL: Conc./Riprap
BEVEL: 1.5h : 1v
Q : 738 CFS
INV N/E/EL: 2457424.08/1518985.46/178.50 /1518966.31/177.90'INV N/E/EL: 2457493.63
WALL THICKNESS: NA
:1
Existing ground
Flow
Flow
Remove two exisiting 42" CMP's
HW : 188.29 ft
S ucker C reek
N
LC
OHW : 184.50 ft
Slope 0.84%
Line to be constructed
BURIAL DEPTH: 3.75 ft BURIAL DEPTH: 3.75 ft
1:1
New culvert centerline
19'-6" span x 12'-6" rise.
Structural plate pipe arch culvert
104+99.37
105+03.85, 32.83 LT
104+94.10, 38.64 RT
PLAN AND PROFILE
SUCKER CREEK CULVERT
[1]method B, class 3
Placed riprap
[1]method B, class 3
Placed riprap
[1]method B, class 3
Placed riprap [1]method B, class 3
Placed riprap detail Sheet G.13
Backfill with streambed material per
FOOTNOTE:
See Sheet G.11 for riprap details.[1]
G.2
STATE PROJECT
NUMBER
SHEET
AK FWS KNA 74525(1)
J N e ig h o r n
/2
/2
C h e c k e d b y
D e s ig n e d b y
In t_ ft
D c p w w o r k \d
\a k r k e n a i1 h .d g n
Road centerline
Channel elev. 181.65
Channel elev. 182.25
Channel flowline
Road grade
:1
A
M
J u ly
Concrete collar
Concrete collar (typ.)
98° per detail sheet G.14
Install rock weirs at 16' spacing
End channel grading
Concrete collar
Begin channel grading
Concrete collar
Begin channel grading
Concrete collar
Cut and fill limits (typ.)
End channel grading
1:1 1.5
TYPICAL SECTION
CHANNEL GRADING
4" depth and seed
Place topsoil, .7
16' bankfull width
16'
NOTE:
FOOTNOTE:
DETAILS
RIPRAP HEADWALL
Sl op e
PIPE BEVEL DETAIL
Sl op e
SKEW ANGLE DIAGRAM
c e n te r li n e
R o a d w a y
Cu lv er t ce nt er lin e
BOP
EOP
(DIAMETER OR SPAN GREATER OR EQUAL TO 48-INCHES)
(DIAMETER OR SPAN LESS THAN 48-INCHES)
.2
D o r R
.2
D o r R o r R is e
R
D ia m e te r
D o r R is e
R
D ia m e te r
D
W
Sl op e
FRONT VIEW SIDE VIEW
[2
24" shown in the plans
Streambed material where shown in the plans
Streambed material where
V a ri a b le R is e
W2
Variable W2
V a ri a b le R is e
Placed riprap, class 3
Placed riprap, class 3
[3
" m in geotextile, class 1, type C
Separation and stabilization
Manufacturer's standards
0.25 D or R or per the
Optional
Skew
N e ig h o r n
/2
/2
C h e c k e d b y
D e s ig n e d b y
G.11
STATE PROJECT
NUMBER
SHEET
In t_ ft m y f il e s \p w p r o d u c ti o n
\d
\m t-a e z .d g n
AK FWS KNA 74525(1)
:5
A u g u s t beneath and at all sides of placed riprap.
Place earthwork geotextile between riprap and existing ground, Earthwork geotextile, type II-C is subsidiary to 251.
Contractor to field verify all invert elevations, prior to installation.
3.
2.
1.
shown on site specific details, whichever is greater.
Construct riprap end treatment to a thickness of 36-inches or as[3]
Riprap end treatment slope to match roadway embankment slope.[2]
Bevel to match roadway embankment.[1]
RIPRAP END TREATMENT
[1]
[1]
V
B e v a
N e ig h o
/2
/2
C h e c k e d b y
D e s ig n e d b y
G.12
STATE PROJECT
NUMBER
SHEET
In t_ ft m y f il e s \p w p r o d u c ti o n
\d
\m t-a e z .d g n
AK FWS KNA 74525(1)
:5
A u g u s t
SECTION VIEW
ANCHOR BOLT DETAIL
1.5
3'-0"
TYPICAL SECTION
THRU COLLAR
CONCRETE COLLAR
ISOMETRIC VIEW
3'-0"
3'
Sp an
3'
LC
Culvert crown
2' min. lap splice
#4 Reinf (6 total)
Culvert invert galvanized " Dia.4 bolt design - 4" hook
Acceptable anchorStructural plate pipe
18" o.c. See detail " Anchor bolt @4
#4
#4 stirrups m in
2' min. lap splice
#4 Reinf (6 total)
6" min.
To bedrock or 3' max.
To bedrock or 3' max.
COLLAR DETAILS
REINFORCED CONCRETE
LARGE CULVERT
SECTION A-A
PLAN
NOTE:
FOOTNOTE:
3.
2.
1.
Pipe arch culvert
W
Streambed sediment
Streambed cobble
Pipe arch culvert wall
Box culvert wall
Stagger in-channel fish passage boulders within the culvert span.
streambed cobble, and bank stone gradations.
See special contract requirements for streambed sediment, Mix streambed cobbles evenly throughout streambed sediment.
Channel flowline
Streambed sedimentRound pipe culvert wall Streambed top
Round culvert
Culvert wall
LC
Flow
BB
A where specified on plan
Sediment retention sill on plan where specified
Rock weir culvert boulder within
Fish passage where specified on plan
Sediment retention sill culvert boulder within
Fish passage
NO SCALE
Streambed Material.
Infill informational quantities are incidental to ITEM 64704-1000 [4] dimension.
smallest 4 3 Embed fish passage boulders within active channel [3] sediment where listed in the infill quantities table.
Construct well defined banks with bank stone and streambed[2] parabolic shape.
Slope streambed aggregate towards flowline to ensure[1]
[1]Channel flowline
[2]Bank stone
[2]Bank stone
TREATMENT
STREAM CULVERT
SIMULATED
A Flow
SECTION B-B
36" min.
Streambed cobble
Culvert outlet where specified on plan
Sediment retention sill
[3]within culvert
Fish passage boulder
Streambed sediment plan sheet or Length on
LC
specified on plan
Rock weir where outlet
Culvert
LOCATION
(FT)
X
(CUYD)
COBBLE
STREAMBED
(CUYD)
SEDIMENT
STREAMBED
(CUYD)
STONE
BANK
GRADATION
COBBLE
STREAMBED
(FT)
W
MITIGATION
FISH PASSAGE BOULDER
(IN)
DIA. NO.
[4]STREAMBED MATERIAL
TOTAL
.B e v
N e ig h o
/2
/2
C h e c k e d b y
D e s ig n e d b y
G.13
STATE PROJECT
NUMBER
SHEET
In t_ ft m y f il e s \p w p r o d u c ti o n
\d
\m t-a e w
.d g n
AK FWS KNA 74525(1)
:4
A u g u s t
SUCKER CREEK NA 16 24 4
UNNAMED TRIBUTARY NA 3 24 7
RAINBOW LAKE NA 6 18 5
C
D
B
(FT)
BD
1.5
3% (typ.)
Slope
295 295 39
B D
W
X (typ.)
B u ri a l d e p thd e p th
B u ri a l
X (typ.)
match rock weir spacing
Stagger fish boulders each side and
B
/3
Flow
F lo wA
A
(in)
DIAMETER
FOOTER ROCK
TOP ROCK AND
(no.)
QUANTITY
ROCK WEIR
MITIGATION
ROCK WEIR
(ft)
B
(ft)
[5] Z
(ft)
W
LOCATION
ELEVATION
PLAN
SECTION A-A
DETAIL
ROCK WEIR
NO SCALE
FOOTNOTE:
[4] [3]Footer rock
Z
D o w n s tr e a m f r o m c o n tr o l)
Top rock
Bottom of channel
Bottom of channel
[4] [3]Footer rock high water level
Ordinary normal low flow
Edge of water
Control point
6[3] [2]Top rock streambed material elevation or top of
Original streambed
[4] [3]Footer rock
[3]Top rock water level
Ordinary high
BWB
B W3
W 3
W3
B
W3
B e v
N e ig h o
/2
/2
C h e c k e d b y
D e s ig n e d b y
G.14
STATE PROJECT
NUMBER
SHEET
In t_ ft m y f il e s \p w p r o d u c ti o n \d
\m t-a e y .d g n
AK FWS KNA 74525(1)
:5
A u g u s t
SUCKER CREEK 16 1.75 6 4
UNNAMED TRIBUTARY 3 3 1.5 7
RAINBOW LAKE 6 1.5 3 5
Align footer rocks flush against bed retention sills inside culvert. [5] and stable foundation for the top rocks.
Place footer rocks close together to create a tightly packed[4] streambed material.
Fill voids in top rock and footer rock with specified[3]
Space top rocks in center 1/3 only.[2]
Orient top rocks to deflect water towards center of stream.[1]
[2] [1] [2] [1]
[2]
[2]
[2] [2] [2]
[2]
VAP
Existing ground
Roadway centerline
2000 50 100 15050100150200250
Sucker Creek
250 300
Section 703. — AGGREGATE
703.18 Furnished Streambed Material. (Added Subsection).
Streambed material consists of streambed sediment and streambed cobbles (class A, B, C, or D as specified on the plans) with volumes of each specified on the plans. Provide a uniform mixture.
Furnish material consisting of hard, durable, free from seams, cracks, and other defects conforming to the following:
(a) Durability index, AASHTO T 210
(1) Coarse aggregate 35 min.
(2) Fine aggregate 35 min.
(b) Apparent specific gravity, AASHTO T 85 2.55 min.
(c) Los Angles abrasion, AASHTO T 96 50% max.
(d) Gradation, Streambed Sediment. Furnish material meeting the gradation requirements of Table 703-13. Conserve round or sub-round material from the culvert and roadway excavation meeting the requirements of Table 703-13 to use as streambed sediment.
Table 703-13 Streambed Sediment Gradation
Sieve Size
Percent by Weight Passing Designated Sieve
(AASHTO T 27 and T 11)
6 inch 100
4 inch 75 – 85
3 inch 65 – 75
1 ½ inch 50 – 60
3/4 inch 35 – 45
No. 4(1) 15 – 25
No. 10 15 min.
(1) No more than 0.2 percent woody debris retained.
(e) Gradation, Streambed Cobbles. Furnish material meeting the requirements of Table 703-14. Conserve round or sub-round material from the roadway excavation meeting the requirements of Table 703-14 to use as streambed cobbles.
Table 703-14 Streambed Cobbles Gradation(1)
Nominal Size
Percent less than the nominal size Class
A B C D 28" 100 20” 65-75 14" 100 35-45 12" 100 85-95 30-40 8" 65-75 45-55 10-20 6" 45-55 30-40 4" 100 35-45 20-30 0-10 3" 30-40 15-25 2"
1 ½" 35-45 0-10 0-10 ¾" 10-15
(1) Grading of the cobbles will be by visual inspection of material before it is placed, and if directed by the CO, by placing material on a flat surface and sorting and measuring a sampling of the cobbles.
Note: Approximate size can be determined by taking the average dimension of the three axes of the rock; length, width, and thickness by use of the following calculation:
𝐿𝐿𝐿𝐿𝐿𝐿𝐿𝐿𝐿𝐿ℎ + 𝑊𝑊𝑊𝑊𝑊𝑊𝐿𝐿ℎ + 𝑇𝑇ℎ𝑊𝑊𝑖𝑖𝑖𝑖𝐿𝐿𝐿𝐿𝑖𝑖𝑖𝑖
= 𝐴𝐴𝐴𝐴𝐴𝐴𝐴𝐴𝐴𝐴𝐴𝐴𝑊𝑊𝐴𝐴𝐴𝐴𝐿𝐿𝐿𝐿 𝑆𝑆𝑊𝑊𝑆𝑆𝐿𝐿
Project:
Location/Stream:
New Stream Channel Design (Culvert, Rock Ramp)
FINE 50%
Using Corps of Engineers Equations - FHWA Circular on Development in the River System - Page 6.25. COARSE 50% FHWA NHI 01-004; River Engineering for Highway Encroachments, 2001 http://www.fhwa.dot.gov/engineering/hydraulics/library_arc.cfm?pub_number=8&id=20
YELLOW ARE INPUTS
Safety Factor 1.5 Stability Coefficient for Incipient Failure 0.36 (0.36 round rock, 0.3 angular rock) Vertical Velocity Distribution Coeff 1.00 (1.0 for straight channels) Blanket Thickness Coeff 1 (1xD100 or 1.5 or D50 max, whichever is greater) Local depth of flow 3.78 ft for 100 year event Unit Weight of water 62.4 lb/ft^3 assumed Unit weight of rock 165 lb/ft^3 assumed Local depth-average velocity 10.53 ft/s from 100-year event avg. velocity in pipe Side Slope correction factor 1 Gravitational Acceleration 32.2 ft/s^2 D85/D15 1.7 (1.7-5.2) D50/D30 1 Note: This method is based on the minimum D30 size Riprap Design Method - Selecting Proper Gradation, Page 131.
Design Hydrology and Sedimentology for Small Catchments, Haan, Barfield and Hayes, 1981.
D15 0.5 ft 7.0 inches D30 1.0 ft 12.0 inches D50 1.2 ft 14.0 inches D85 2.0 ft 24.0 inches
D100 2.3 ft 28.0 inches
Using D50 size, used FHWA circular for Rip Rap design to spec out D100, D85 and D15.
D100 = 2.0D50
Fuller-Thompson Estimating for Maximum Density: D100 (inches) 28.0 Method Adapted from US Forest Service Stream Simulation Guidelines D30 12.0 Stability (D30):
D30 Req'd 12.0
YELLOW ARE INPUTS COARSE FINES
Custom Fine Aggreg. Combined %F-T EQN Check Coarse Material Design -D30 Required p RELATIVE % = 0.50 0.50 1.0000 Riprap D30 Riprap Req 12.0
Size (inches) Sieve Size % Passing % Passing % Passing % Passing % Passing D30 Size = 12.0 48 48 in 1.00 1.00 100% 131% 100% No OK 44 44 in 1.00 1.00 100% 125% 100% No 42 42 in 1.00 1.00 100% 122% 100% No 36 36 in 1.00 1.00 100% 113% 100% No 28 28 in 1.00 1.00 100% 100% 100% No 20 20 in 0.70 1.00 85% 85% 70% No 14 14 in 0.40 1.00 70% 71% 40% No 12 12 in 0.30 1.00 65% 65% 30% 12.00 8 8 in 0.10 1.00 55% 53% 10% 8.00 6 6 in 0.00 1.00 50% 46% 0% 6.00 4 4 in 0.00 0.80 40% 38% 0% 4.00 3 3 in 0.00 0.70 35% 33% 0% 3.00
1.5 1.5 in 0.00 0.55 28% 23% 0% 1.50
0.75 0.75 in 0.00 0.40 20% 16% 0% 0.75
0.187 #4 0.00 0.20 10% 8% 0% 0.19
0.0787 #10 Sand 0.00 0.15 8% 5% 0% 0.08
Gradation values should be within +/-5% of this gradation (Rice) AND we need to have at least 5% sand size (#10) or smaller (Forest Service) in the combined gradation
DATA for Graph & Fuller-Thomson Eqn Size (in) Combined % pa F-T equation
48.000 100% 131%
44.000 100% 125%
42.000 100% 122%
36.000 100% 113%
28.000 100% 100%
20.000 85% 85%
14.000 70% 71%
12.000 65% 65%
8.000 55% 53%
6.000 50% 46%
4.000 40% 38%
3.000 35% 33%
1.500 28% 23%
0.750 20% 16%
0.187 10% 8%
0.079 8% 5%
OK
MATERIAL PROPORTIONS
AK FWS Kenai 74525(1) - Swan Lake / Swanson Rive
Sucker Creek Culvert
0%
10%
20%
30%
40%
50%
60%
70%
80%
90%
100%
0.010 0.100 1.000 10.000 100.000
P as si n g
Particle Size
Design
Fuller‐Thomson
YELLOW ARE INPUTS
Desired tolerance (+/-): 5%
SIEVE % PASSING
12 in 1.00 8 in 1.00 6 in 1.00 4 in 0.75 to 0.85 3 in 0.65 to 0.75
1.5 in 0.5 to 0.6
0.75 in 0.35 to 0.45
#4 0.15 to 0.25 #10 Sand 0.15 min
Desired tolerance (+/-): 5%
SIZE % PASSING
48 in 1.00 44 in 1.00 42 in 1.00 36 in 1.00 28 in 1.00 20 in 0.65 to 0.75 14 in 0.35 to 0.45 12 in 0.3 to 0.4 8 in 0.1 to 0.2 6 in 0 to 0.1 4 in 0 to 0.1
3 in 0 to 0.1
TABLE 1
FINE MATERIAL
TABLE 2
COARSE MATERIAL
| 1-AK SuckerCreek AOP Report Final |
| 2-Sucker Creek Tables |
| 3-SuckerCreek AOPreport_figures1-3 |
| 3-SuckerCreek AOPreport_figures1-3 |
| Fig 1 |
| Fig 2 |
Sucker Creek Semi-log Gradation Plot
| 5-AOP Report Photos SuckerCreek |
| Sheet1 |
| 6-HY8 Swan Lake AOP Design - Sucker Creek |
| Crossing Discharge Data |
| Table 1 - Summary of Culvert Flows at Crossing: Sucker Creek |
| Rating Curve Plot for Crossing: Sucker Creek |
| Culvert Data: Sucker Creek |
| Table 1 - Culvert Summary Table: Sucker Creek |
| Culvert Barrel Data |
| Culvert Performance Curve Plot: Sucker Creek |
| Site Data - Sucker Creek |
| Culvert Data Summary - Sucker Creek |
| Tailwater Data for Crossing: Sucker Creek |
| Table 2 - Downstream Channel Rating Curve (Crossing: Sucker Creek) |
| Tailwater Channel Data - Sucker Creek |
| User Defined Channel Cross-Section |
Roadway Data for Crossing: Sucker Creek
| 7-HY8Report_Sucker Creek-Existing |
| 8-GISnd more |
| 8-GISnd more |
| SuckerCreek___streamstats.usgs |
| Sucker G-Sheets Revised 6-14-23 |
| 8-GISnd more.pdf |
| ak-r-kenai7452501_HY01-Long Profiles |
| SCR 703 Furnish Streambed Material - Swan Lake |
| Section 703. — Aggregate |
| 703.18 Furnished Streambed Material. |
Streambed Material Sizing Analyzer_Sucker Creek
| AK SuckerCreek.pdf |
| AK SuckerCreek AOP Report |
| 1-AK SuckerCreek AOP Report Final |
| 2-Sucker Creek Tables |
| 3-SuckerCreek AOPreport_figures1-3 |
| Fig 1 |
| Fig 2 |
| Sucker Creek Semi-log Gradation Plot |
| AK SuckerCreek AOP Report |
| 5-AOP Report Photos SuckerCreek |
| Sheet1 |
| 6-HY8 Swan Lake AOP Design - Sucker Creek |
| Crossing Discharge Data |
| Table 1 - Summary of Culvert Flows at Crossing: Sucker Creek |
| Rating Curve Plot for Crossing: Sucker Creek |
| Culvert Data: Sucker Creek |
| Table 1 - Culvert Summary Table: Sucker Creek |
| Culvert Barrel Data |
| Culvert Performance Curve Plot: Sucker Creek |
| Site Data - Sucker Creek |
| Culvert Data Summary - Sucker Creek |
| AK SuckerCreek AOP Report |
| 6-HY8 Swan Lake AOP Design - Sucker Creek |
| Culvert Data: Sucker Creek |
| Tailwater Data for Crossing: Sucker Creek |
| Table 2 - Downstream Channel Rating Curve (Crossing: Sucker Creek) |
| Tailwater Channel Data - Sucker Creek |
| User Defined Channel Cross-Section |
Roadway Data for Crossing: Sucker Creek
7-HY8Report_Sucker Creek
| HY8Report_Sucker Creek |
| AK SuckerCreek AOP Report |
| 8-GISnd more |
| SuckerCreek___streamstats.usgs |
| Sucker G-Sheets Revised 6-14-23 |
| ak-r-kenai7452501_HY01-Long Profiles |
| SCR 703 Furnish Streambed Material - Swan Lake |
| Section 703. — Aggregate |
| 703.18 Furnished Streambed Material. |
Streambed Material Sizing Analyzer_Sucker Creek
File details come from the government source that posted it. Updated .