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HomeMy WebLinkAboutSUS479I I I I I I I I I I I I I I I I I I I SUSITNA HYDROELECTRIC PROJECT MIDDLE SUSITNA RIVER SEDIMENTATION STUDY STREAM CHANNEL STABILITY ANALYSIS OF SELECTED SLOUGHS, SIDE CHANNELS AND MAIN CHANNEL LOCATIONS Report by Harza-Ebasco Susitna Joint Venture Prepared for Alaska Power Authority March 1985 •• 1 . .. . -. ::· ": • •J .·! . i I I I I I I I I I I I I I I I I I I I 'l'A.BLE OF CORTENTS SECTION/TITLE List of Tables List of Exhibits 1.0 SUMMARY 2.0 BACKGROUND 3.0 SCOPE OF STUDY 4.0 SETTING 5.0 STUDY SITES 5.1 Main Channel Near River Cross Section 4 5.2 Main Channel Between River Cross Sections 12 and 13 5.3 Main Channel Upstream From Lane Creek ,... 5.4 Mainste!m 2 Side Channel at River Cross Section 18.2 5.5 Slough 8A 5.6 Slough 9 5.7 Main Channel Upstream Fr~ 4th of July Creek 5.8 Side Channel 10 5.9 Lower Side Channel 11 5.10 Slough 11 5.11 Upper Side Channel 11 5.12 Main Channel Between River Cross Sections 46 and 48 5.13 Side Channel 21 5.14 Slough 21 6.0 DATA SOURCES -i- PAGE ;li ;., I 3 .1 s 7 , • , 8 ' ' ' ' ,. ,. ,. ,, " I I I I I I I I I I I I I I I I I I I - TABLE OF CONTENTS SECTION/TITLE 7.0 GENERAL APPROACH 7.1 Degradation 7.1.1 Competent Bottom Velocity 7.1.2 Tractive Force 7.1.3 Meyer-Peter, Muller Formula 7.1.4 Schoklitsch Formula 7.1.5 Shields Criteria 7.1.6 Depth of Degradation 7.2 Aggradation 8.0 HYDRAULIC DATA USED IN THE ANALYSIS 8.1 Dominant Discharge 8.2 Mean Velocities, Average Depths and Channel Widths 8.3 Channel Bed Slopes 8.4 Hanning's Roughness Coefficients 8.5 Bed Material Size Distribution 9.0 SEDIMENTATION PROCESS 9.1 9.2 Natural Conditions 9.1.1. River Morphology 9.1.2. Channel Stability 9.1.3. Intrusion of Fine With-Project Conditions River Morphology Channel Stability Sediments 9 .2.1 9.2.2 9.2.3 Intrusion of Fine Sediments ~tr~£tte/llt't.s TABLES EXHIBITS APPENDIX A -11- ,, 1.1 II ,, Jl u I I I I I I I I I I I I I I I I I I I Nuober 1 2 3 4 5 6 7 8 LIST OF TABLES Title Characteristics of Study Sites on Middle Susitna River Hydraulic Parameters for Mainstem Sites Hydraulic Parameters for Side Channels and Sloughs Representative Bed Material Size Distribution for Selected Sloughs, Side Channels and Main- stem Sites Transportable Bed Material Sizes in Selected Sloughs, Side Channels and Mainstem Sites Potential Degradation in Selected Sloughs, Side Channels and Mainstem Sites Natural and With-Project Average Weekly Flows of Susitna River at Gold Creek Maxhnuil Natural and With-Project Weekly Flows of Susitna Riv~r at Gold Creek -iii- I I I I I I I I I I I I I I I I I I I Number 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 LIST OF EXHIBITS Title Location Map Locations of Study Sites Main Channel near River Cross Section 4 Main Channel between River Cross Sections 12 and 13 Main Channel upstream from Lane Creek Hainstem 2 Side Channel Slough SA Slough 9 Main Channel upstream from 4th of July Creek Side Channel 10 Lower Side Channel 11 Slough 11 Upper Side Channel 11 Main Channel between River Cross Sections 46 and 48 Side Channel 21 Slough 21 Relatiouship between Particle Size and Bottom Velocity Relationship between Mean Diameter and Critical Tractive Force Relations hips between Slough/Side Channel l)ischarge and Discharge at Gold Creek Hydraulic Parameters for Slough 9 Hydraulic Parameters for Lower Channel 11 Size Distribution of Bed Material in Main Channel near Cross Section 4 Size Distribution of Bed Material in Main Channel between Cross Sections 12 and 13 Size Distribution of Bed Material in Main Channel upstream from Lane Creek -iv- I I I I I I I I I I I I I I I I I I I Number 25 26 27 2S 29 30 31 32 33 34 35 36 37 3S 39 40 41 42 LIST OF EXHIBITS Title Size Distribution of Bed Material in Mainsteam & Side Channels at Cross Section 18.2 Size Distribution of Bed Material in Slough SA Size Distribution of Bed Material in Slough 9 Size Distribution of Bed Material in Main Channel upstream from 4th of July Creek Size Distribution of Bed Material in Side Channel 10 Size Distribution of Bed Material in Lower Side Channel 11 Size Distribution of Bed Material in Slough 11 and Upper Side Channel 11 Size Distribution of Bed Material in Main Channel between Cross Sections 46 and 4S Size Distribution of Bed Material in Side Channel 21 and Slough 21 Transportable Bed Material Sizes in Hain Channel near Cross Section 4 Transportable Bed Material Sizes in Main Channel between Cross Sections 12 and 13 Transportable Bed Material Sizes in Main Channel upstream from Lane Creek Transportable Bed Uaterial Sizes in Mainstem 2 Side Channel Transportable Bed l-faterial Sizes in Slough SA Transportable Bed Material Sizes in Slough 9 Transportable Bed Material Sizes in Main Channel upstream from 4th of July Creek Transportable Bed Material Sizes in Side Channel 10 Transportable Bed Material Sizes in Lower Side Channel 11 -v- I I I I I I I I I I I I I I I I I I Number 43 · 44 45 46 47 48 49 50 51 52 53 54 55 56 57 sa 59 LIST OF EXHIBITS Title Transportable Bed Material Sizes in Slough 11 Transportable Bed Material Sizes in Upper Side Channel 11 Transportable Bed Material Sizes in Main Channel between Cross Sections 46 and 48 Transportable Bed Material Sizes in Side Channel 21 Transportable Bed Material Sizes in Slough 21 Estimated Depth of Degradation in Main Channel near Cross Section 4 Estimated Depth of Degradation in Main Channel between Cross Sections 12 and 13 Estimated Depth of Degradation in Main Channel upstream from Lane Creek Estimated Depth of Degradation in Mainstem 2 Side Channel Estimated Depth of Degradation in Slough 9 Esti~ted Depth of Degradation in Main Channel upstream from 4th of July Creek Estimated Depth of Degradation in Side Channel 10 Estimated Depth of Degradation in Lower Side Channel 11 Estimated Depth of Degradation in Upper Side Channel 11 Estimated Depth of Degradation in Main Channel between Cross Sections 46 and 48 Estimated Depth of Degradation in Side Channel 21 Estimated Depth of Degradation in Slough 21 -vi- I I I I I I I I I I I I I I I I I I I 1.0 SUMMARY This study was conducted to evaluate potential effects of the Susitna Hydro- electric Project on channel stability at selected sites in the mainstem and at selected sloughs and side channels. The sediment at ion process in the Susitna River under natural conditions also is discussed. The study reach includes the Susitna River between Devil Canyon and the confluence of the Susitna and Chulitna rivers. The selected sites (shown on Exhibit 2) are : 1. 2. 3. Mainstem Sites: near river Cross Section 4, river miles 99.0 to 100.0; between river cross sections 12 and 13, river miles 108.5 to 110.0; ups t ream from Lane Creek, river miles 113.6 to 114.2; upstream from 4th of July Creek, river miles 131.2 to 132.2 and between river cross sections 46 and 48, river miles 136.9 to 137.4. Side Channels: Mainstem 2 Side Channel, Side Channel 10, Lower and Upper Side Channels 11 and Side Channel 21. Sloughs: SA, 9, 11 and 21. For natural conditions, temporal deposition and/or scour was studied at the sites in qualitative terms. Under with-project conditions, a more quantitative estimate of potential degradation and/or aggradation was made for each study site. Intrusion of fine sediment into the gravel bed and its subsequent entrapment also were studied. The hydraulic and sediment data required for the study were derived from various reports prepared by the Alaska Department of Fish ani Game, Susitna Hydro Aquatic Studies Team; R&M Consultants, Incorporated; U.S. Geological Survey, Water Resources Division, Anchora·ge; and Harza-Ebasco Susitna Joint Venture during 1983 and 1984. The data were used to develop relationships 42188202 850404 1 I I I I I I I I I I I I I I I I I I I between the discharge rates at Gold Creek stream gaging station and corresponding flows at the mainstem sites and the flows entering the sloughs and side channels. These data also were used to estimate mean velocities, coverage depths and channel widths at each site. The bed material size distribution representative for the material at each site was derived from the analysis of the bed material samples collected by Harza-Ebasco. The sizes of transportable bed material corresponding to a selected range of discharges were estimated as the average of the five sizes computed using the methods of competent bottom velocity; tractive force; Meyer-Peter, Muller formula; Schoklitscb formula and Shields criteria. A comparison of median bed material size and the transportable size at each site indicated that under natural conditions, most of the selected sites are subject to temporal scour and/or deposition depending upon the magnitude and characteristics of the sediment load and high flows caused by floods or breaching of ice jams. About 56 percent of the suspended sediment load carried by the river, under natural conditions, is finer than 0.5 millimeter (medium to fine sand, silt and clay). This fine sediment has been observed to deposit in side channels and sloughs. However , many of these deposits are re-suspended and removed during high flows, probably because of disturbances of the surface bed material layer. Under with-project conditions, the flow regime of the Susitna River will be modified and the reservoirs will trap most sediment except the smaller particle sizes including fine silt and clay size material. The river will strive to adjust itself to a new equilibrium. The main channel will have the tendency to be more confined with a narrower channel. This may cause the main channel to recede from the beads of some sloughs and side channels. There also will be some streambed degradatic-n in the study reach. At the selected sites in the mainstem, the potential degradation would be in the range of about 1.0 to 1.5 feet corresponding to a dominant discharge of 4218821)2 850404 2 I I I I I I I I I I I I I I I I I I about 30,000 c fs. Flows of this magnitude would be expected in the early years of Watana and Devil Canyon operation; presently projected for 2002. An armor layer will develop as the degradation takes place and the riverbed will become more stable. In the sloughs and side channels, the degradation would be about 0 to 0.3 feet. The estimated degradations are based on the assuption that there will not be any deposition of sediments at the study sites. However, in the actual ,............_ situ~ ation, some of the bed material eroded from upstream reaches and .;.__..- ~ .:.. injected by the tributaries or bank erosion would be deposited at these sites. Therefore, the actual degradation will likely be less than those estimated. It is not possible to accurately estimate the actual degradation since there are many unquantifiable parameters. These include bed material transport from tributaries and bank erosion, the degree of armoring by the present bed and the actual streamflows and floods which will occur for the first few years of Devil Canyon operation. However , based on many samples of bed material and visual inspection it is believed that degradation in the main channel will not exceed approximately one foot, on the average. The amount of this degradation may be greatest near the Devil Canyon Dam face and decrease with distance downstream. When the system energy demand increases (as in 2010), and less flow is discharged in July and August, the armoring layer developed earlier will be stable, more so than under natural conditions. Infrequent flood events will not be controlled to as great an extent as smaller floods, and will still have the ability to remove the armor layer and cause bed degradation. Reservoir operation studies indicate that floods up to the 50-year event will be controlled for projected energy demands in 2002 . Control of infrequent flood events will be improved as energy demand increases, and the potential for bed degradation will therefore be reduced. 42188202 850404 3 I I I I I I I I I I I I I I I I I I I Because of the inability to predict degradation of these small amounts it will be necessary to monitor water levels. This will allow modification of habitat areas if and when degradation occurs. Because of degradation in the mainstem, the discharges higher than those under natural conditions would be required to overtop the berms at the heads of the sloughs and side channels. Assuming that the river bed at the entrances would be lowered by about one foot due to the degradation, the with-project discharges that would overtop the sloughs and side channels were estimated to be between 4000 and 12000 cfs higher than those under natural conditions with an average value of approximately 8000 cfs. The analysis indicated that if the sloughs or side channels were overtopped, the velocities would be sufficiently high to carry our the fine sediment of sizes .004 millimeter and less. However, any coarse silt and fine sand picked up from the river bed would have the tendency to settle out in pools ansd backwater areas. With project flows will still be sufficient to overtop these slough berms and therefore, some deposition of such material can be expected. Mechanical devices such as "gravel gerties" have been developed to flush these materials from sloughs. Alternately project discharges can be raised to overtop the slough berms and flush the sands from the sloughs. Spiking discharges in this manner may tend to destabilize the main channel streambed and result in additional degradation. 2. 0 BACI.CROUIID This is a th i rd report by Harza-Ebasco Susitna Joint Venture on the evalu- ation of potential effects of the proposed Susitna Hydroelectric project on 42188202 850404 4 I I I I I I I I I I I I I I I I I I I sediment transport in the Susitna River. The first report entitled "Reser- voir and River Sedimentation·· (H-E, April 1984)!/ addressed the sediment acc11mulation in the Watana and Devil Canyon reservoirs and poten tial aggra- dation and degradation in the river reach between Devil Canyon and the Sun- shine stream gaging station. That study provided esticates of degradation and/or aggradation within the study reach in a general s~nse without any specific reference to side sloughs or side channels. The transportable sizes under natural and with-project conditions were computed based on dominant discharges taken to be the mean annual floods in both· cases . Th e bed material size distributions at various locations in the reach was based on limited number of samples taken from surface layer material . The second report entitled "Lower Susitna River Sedimentation Study, Project Effects ou Suspended Sediment Concentration" (H-E, November 1984) provided a compari son of monthly suspended sediment concentrations at Gold Creek and Sunshine stream gaging stations for natural and with-project conditions. The present report provides channel stability analysis for specific sites in the cainstem of the Susitna River and in the selected sloughs and side ~h a n­ nels between Devil Can yon and the confluence of the Susitna and Chulitna Rivers. The analysis are based on bed material samples taken from surface and subsurface material at or near the selected sites. 3.0 SCOPE OF STUDY This study is made to provide input to the instream flow relationship stud- ies which will provide quantitative assessment of potent i al effects on fis h habitat because of with-project changes in streamflow, stream teoperature, 1/ Indicated reference at the end of text. -4- I I I I I I I I I I I I I I I I I I I suspended sediments, channel degradation or aggradation and water quality. A number of side sloughs, side channels and main channel sites were identi- fied in the study reach where potential project impacts on the fish habitat would likely be significant. The scope of this study includes the analysis of sedimentation process to evaluate stream channel stability under natural and with-project conditions for the study sites in the mainstem and in selected sloughs and side chan- nels. For these analysis, a stable channel means that its shape, slope and bed material size distribution do not change significantly with time. The taajor tasks ar~: 1. 2. 3. 4. to evaluate sedimentation process under natural conditions; to estimate pG~ential degradation or aggradation under with- project conditions; to determine discharge rates at which the mainstem flows are like- ly to overtop the entrances of the sloughs and side channels under natural and with-project conditions; and to estimate discharge rates for the sloughs and side channels at which their beds will be unstable and also the rates to flush out fine sediment deposits. 4.0 SETTING The Susitna River drains an area of about 19,600 square miles (mi2) in the south central region of Alaska. The major tributaries include the Chulitna, Talkeetna and Yentna rivers with drainage areas of about 2,650, 2,040 and 6,200 mi2, respectively. The Susitna River originates in the West Fork, Susitna, East Fork and Maclaren glaciers of the Alaska Range (Exhibit 1) and travels a distance of about 320 miles to its mouth at the Cook Inlet. The Chulitna River origi- nates in the glaciers on the south slopes of Mount Mckinley and joins the -5- I I I I I I I I I I I I I I I I I I I Susitna River from the west near Talkeetna at river mile 9~ (RM, river miles referenced from the Cook Inlet). The Talkeetna River originates in the Talkeetna Mountains and joins the Susitna River from the east near Talkeetna at RM 97. The Yentna River originates in the Alaska Range and enters the Susitna Riv~r from the west at RM 28. The Susitna River gradients average about 14 feet per mile (ft/mi) in a 54-mile reach immediately upstream of Watana, about 10.4 ft/mi from Watana to the entrance of Devil Canyon and about 31 ft/mi in a 12-mile reach between the entrance and the mout h of Devil Canyon (ACRES, 1982). The river gradients between mouth of Devil Canyon and the confluence of the Chulitna and Susitna Rivers, and between the confluence and Susitna Station (Exhibit 1) average about 10 and 4 ft/mi, respectively, as estimated from the United States Geological Survey (USGS) topographic maps of 1:63,360 scale. The Susitna River is a typical natural glacial river with high turbid summer flow and low, clear winter flow. The river generally starts rising in early May, sustains high flow during July through September and starts falling rapidly in Novewber or December as the freeze-up occurs. The mean annual flow of the Susitna River at Cantwell, Gold Creek and Susitna Station (See Exhibit 1 for locations) are about 6,400 (13 years, 1962-72, 81-82), 9,720 (33 years, 1950-82) and 50,700 (8 years, 1974-82) cubic feet per second (cfs), re.spectively. rbe river carries a significant amount of suspended sediments during flood season. Bedload movement also occurs and fairly large scale aggradation or degradation have been observed (H-E, April 1984). The bed load and sus- pended sediment discharges during the water year 1982, were estimated to be about 423,000 and 13,330,000 tons, respectively for the Susitna River at Sunshine (H.E. April 1984). -6- I I I I I I I I I I I I I I I I I I The Susitna Hydroelectric Project will include two dams, Watana and Devil Canyon, located at RM 184 and RM 152, respectively. The drainage areas at the two sites are about 5,180 and 5,810 mi2, respectively. S.O STUDY SITES The channel stability analysis was limited to the Middle Susitna River, from mouth of Devil Canyon to just upstream from the confluence of the Susitna and Chulitna Rivers. The specific sites for which the analysis was made include; 1. 2. 3. Mainstem Locations: Near river cross section 4, RH 99.0-100.0 Between river cross sections 12 and 13, RH 108.5-110.0 Upstream from Lane Creek, ~I 113.6-114.2 Upstream from 4th of July Creek, ~~ 131.2-132.2 Between river cross sections 46 and 48, rn1 136.9-137.4 Side Channels Side Mainstem 2 Side Channels at river cross section 18.2, RH 114.4;115.5 Side Channel 10, RH 134.2 Lower Side Channel 11, RM 135.0 Upper Side Channel 11, RH 136.2 Side Channel 21, RM 140.6 Slough Slough 8A Slough 9 Slough 11 Slough 21 The above locations, are shown on Exhibit 2. A brief description of each site is given below. -7- I I I I I I I I I I I I I I I I I I I 5.1 MAIN CHANNEL NEAR RIVER CROSS SECTION 4 Exhibit 3 shows a sketch of channel pattern at this location. The study reach is about one mile long (RM 99.0 to 100.0). A number of small islands (gravel bars with or without vegetation) are present in the reach. Most of these islands are submerged during medium to high flows. 5.2 MAIN CHANNEL BETWEEN RIVER CROSS SECTIONS 12 and 13 Exhibit 4 shows the channel configuration at this site. The study reach is about 1.5 miles long (RM 108.5 to 110.0). A few gravel bars with or without vegetation exist in the reach. Some of these are submerged during medium to high flows. 5.3 MAIN CHANNEL UPSTREAM FROM LANE CREEK Exhibit 5 shows the channel configuration at this site. The study reach is about 0.6 mile, between ~~ 113.6 and 114.2. The Lane Creek Slough is on left bank of the river (left bank looking downstream). A number of small gravel bars are visible during low flow. 5.4 MAINSTEH 2 SIDE CHANNELS AT RIVER CROSS SECTION 18.2 Exhibit 6 shows the configuration of the main and side channels, and island .or gravel bars near river cross section 18.2. A side channel is located on the left bank of the river. At the upstream end, the channel is divided into sub-channels. Measured along the main channel and the northwest sub- channel, the study site is about one mile long (between RH 114.4 and 115.4). The northeast sub-channel is about 0.4 mile in length (between RM 115.2 and 115.6). -8- I I I I I I I I I I I I I I I I I I I 5.5 SLOUGH 8A The slough is located on the left bank of the river approximately at river mile 126.2 (Exhibit 7). It is about 2 miles in length and is se,arated from the main river by a large vegetated island. The main slough channel branches into two sub-channels approximately 2,500 feet upstream of the mouth of the slough. Two beaver dams, one downstream of the confluence of two sub-channels and one in t~e northeast sub-channel, exist in the slough. 5.6 SLOUGH 9 Exhibit 8 shows the location of Slough 9 with respect to main river and side channels. The slough is about 1.2 miles in length and is separated from the main river by a large vegetated island. Two small tributaries, designated as A and B (Exhibit 8) enter the slough from left bank at respectively about 500 and 3,000 feet upstream from the mouth of the slough. 5.7 MAIN CHANNEL UPSTREAM FROM 4TH OF JULY CREEK Exhibit 9 shows the general configuration of the main river, side channels and the mouth of 4th of July Creek. The main river channel considered in this study is about one mile in length (between RM 131.2 and 132.2, river cross sections 36 and 37). A number of small and large-size islands or gravel bars exist in the reach which separate the side channels from the !D&in river. 5.8 SIDE CHANNEL 10 The general configuration of the main river, Side Channel 10 and Slough 10 is shown on Exhibit 10. The side channel is about 0.5 mile in length (between RM 133.8 and 134.2). It confluences with Slough 10 before rejoining the main river. A large gravel bar separates the channel from the main river. -9- l I I I I I I I I I I I I I I 5.9 LOWER SIDE CHANNEL 11 The side channel is located on the left bank of the river approximately between RM 134.6 and 135.3 and is separated from the main river by a well vegetated island (Exhibit 11). At the upstream end, the channel has two forks which join at the confluence with Slough 11. 5.10 SLOUGH 11 The slough is located on the left bank of the river approximately between RM 135.4 and 136.4 (about 1.0 mile in length) and is separated from the main river by a large vegetated island (Exhibit 12). The downstream end conflu- ences with the Lower Side Channel 11. The upstrame end joins with the Upper Side Channel 11 . The slough runs almost parallel to the main river. 5.11 UPPER SIDE CHANNEL 11 The channel is located on the left bank approximately at RM 136.2 and is about 0.4 mile in length (Exhibit 13). The Slough 11 Rtarts from the chan- nel approximately 800 feet downstream of the head of the channel. The chan- nel is separated from the main river by a vegetated island. 5.12 MAIN CHANNEL BETWEEN RIVER CROSS SECTIONS 46 AND 48 Exhibit 14 shows a sketch of the main channel. The selected reach for study is between RM 136.9 and 137.4. A large gravel bar divides the river into two channels at this location (Exhibit 14). 5.13 SIDE CHANNEL 21 Exhibit 15 shows the location of Side Channel 21. The channel is located approximately at RM 140.6 on the left bank of the river and is separated from the main river by a series of well vegetated islands and gravel bars. -10- I I I I I I I I I I I I I I I I I I I ·-The length of the channel is about 1.0 mile. Slough 21 joins the channel at about 800 feet downstream of the head of the channel. 5.14 SLOUGH 21 A general sketch of Slough 21 is shown on Exhibit 16. The slough is located on the left bank of the river, approximately at RM 141.8. It is about 0.5 mile long (between ~~ 141.8 and 142.3) and is separated from the main river by a large vegetated island. At about 1500 feet upstream from the mouth, the slough is divided into two sub-channels. 6.0 DATA SOURCES The basic data used in this study were taken from various reports prepared for Alaska Power Authority by the Alaska Department of Fish and Games, Susitna Hydro Aquatic Studies Team (ADF&G}, R and M Consultant, Incorporated (R&M} and Harza-Ebasco Susitna Joint Venture (H-E). Discharge aod sediment data also were taken from the publications of U.S. Geological Survey, Water Resources Division (USGS) prepared in co-operation with Alaska Power Authority. Hydraulic parameters such as stage-discharge relationships, channel widths, average channel depths, measured velocities and bed slopes of selected side channels and sloughs, were taken from various reports of R&M (R&M, February 1982 and December 1982) and ADF&G (ADF&G, 1983 and 1984). The hydraulic parameters for the main channel reaches were derived fr~ the data given in H-E, January 1984 Report. Some unpublished data were obtained from USGS, R&M and ADF&G through correspondences. The Manning's roughness coefficients for various main channel reaches, side channels and sloughs were estimated based on field reconnaissances made in 1983 and 1984 and also based on the analysis presented in the H-E, January 1984 report. -11- I I I I I I I Bed caterial samples were collected by USGS and Harza-Ebasco personnel for this study. The results of these samples are given in the H-E, April 1984 and Knott-Lipscomb, 1983 reports. Data for samples collected by USGS in 1984 were obtained from the USGS office, Anchorage. 7. 0 GENERAL APPROACH As discussed under Section 3.0, "Scope of the Study", the purpose of the present analyses is to evaluate sedimentation process under natural and with-project conditions in the Susitna River at the study sites (Table 1 and Exhibit 2). Of major concern are potential aggradation or degradation in the sloughs and side channels and at their entrances, and at the sites in the main channel. Also of concern are intrusion of fine sediment into gravel bed and its subsequent entrapments. In case of fine sediment deposi- tion on the gravel bed, appropriate measures will have to be taken to flush out the sediments so that the bed can be kept clean. To provide some background for analyzing the specific problems under study, brief description of sediment transport in a river is given below. Some of the terminologies used are defined in Appendix A. Sediment particles are transported by the flow as bedload and suspended load. The suspended load consists of wash load and bed-material load. In large rivers, the amount of bedload generally varies between about 3 to 25 percent of the suspended load. Although the amount of bedload is generally small compared to the suspended load, it is important because it shapes the bed and affects the channel stability. The amount of material transported or deposited in a stream under a given set of conditions depends upon the interaction between variables represent- ing the characteristics of the sediment being transported and the capacity of the stream to transport the sediment. A list of these variables is given below (Simons, Li and Associates, 1982). -12- I I I I I I I I I I I I Sediment Characteristics : Quality: Size, settling velocity, specific gravity, shape, re- sistance to wear, state of dispersion and cohesiveness. Quantity : Geology and topography of watershed, magnitude, inten- sity, duration, distribution and season of rainfall, soil condition, vegetal cover, cultivation and grazing, surface erosion and bank cutting. Capacity of Stream: Geometric shape: Depth, width, form and alignment. Hydraulic Properties: Slope, roughness, hydraulic radius, dis- charge, velocity, velocity distribution, turbulence, tractive force, fluid proper- ties and uniformity of discharge. The above variables are not independent and in some cases the effect of a variable is not definitely known. However, the response of channel pattern and longitudinal gradient to variation in the variables have been studied by various investigators, Lane (1955), Leopold and Haddock (1953), Schul'ilm (1971) and Santos and Simmons (~972). The studies by these investigators support the following general relationships (Simons and Senturk, 1977): (i) depth of flow is directly proportional to water discharge; (ii) channel width is directly proportional to both water discharge and sediment discharge; (iii) channel shape expressed as width to depth ratio is directly relat- ed to sediment discharge; (iv) channel slope is inversely proportional to water discharge and directly proportional to both sediment discharge and grain size; (v) sinuosity is directly proportional to valley s:'.ope and inversely proportional to sediment discharge, and (vi) transport of bed material is directly related to streampower (defined as product of bed shear and cross-sectional average velocity), and concentration of fine material and inversely related to bed material sizes. -13- I I I I I I I I I I I I I I I I I I I Because of the complexity of interaction between variot:.s variables, the river response to natural or man-made changes is gener~lly studied by (i) qualitative analysis, involving morphological concepts, (ii) quantitative analysis involving application of morphological concepts and various empiri- cal or experimental relationships, and (iii) quantitative analysis using mathematical models. The insights to the problems obtained through qualita- tive approach, provides understanding of the methods required to quantify the changes in the system. Mathematical modeling can help to study many fctors simultaneously. Recent work by Simons and Li (1978) and others indi- cates that physical process computer modeling provides a reliable methodolo- gy for analysing the impacts and developing solutions to complex problems of aggradation, degradation and river response to engineering activities. For river channels of non-cohesive sediment, qualitative prediction of river response have been made using Lane's relationship (Lane, 1955): QS -Gsd s in which Q stream discharge S • longitudinal slope of stream channel bed material discharge particle size of bed material, generally represented by d 50 (median diameter). The use of above relationship to predict potential responses of the Susitna River under the natural and wi tb-project conditions, is discussed under Section 9. 0. Predict ion of quantitative changes in a river system requires geomorphic and hydraulic data or information which are generally not readily available. Considerable efforts, time and money are required to collect such informa- tion. The data of primary needs includes hydrologic and topographic maps and charts, large scale aerial and other photos of the river and surrounding -14- I I I I I I I I I I I I I I I I I I • terrain, existing river conditions (roughness coefficient, aggradation, degradation, local scour near structures), discharge and stage data (under natural and with-project conditions), existing channel geometry (main chan- nel, side channels, islands); sediment data (suspended load and bed-load, size distribution of bank and bed material and suspended sediment), and size and operation of anticipated reservoir(s) on the river system. Because of the available data and time did not permit a meaningful mathema- tical modeling using computer techniques, the morphological concepts and empirical relationships were used to predict potential aggradation or degradation at the study sites. 7.1 DEGRADATION Generally, river bed degradation occurs downstream of newly constructed diversion and storage structures. The rate of degradation is rapid at the beginning, but is checked because of the development of a stable channel slope or formation 9f an ~rmor layer if sufficient coarse sediment particles are available in the bed. The important variables affecting the degradation process are: 1. Characteristics of the flow released from the reservoir, 2. Sediment concentration of the flow released from the reservoir, 3. Characteristics of the bed material, 4. Irregularies in the river bed, 5. Geometric and hydraulic characteristics of river channel; 6. Existence and location of controls in the downstream channel. The assumptions used in the present analysis include: 1. Bedload is comvletely trapped by the reservoir but suspended sedi- ment particles of about .004 mm and less will remain in suspension and pass through the reservoir (PND, 1982). The sediment passing -15- I I I I I I • • • • • • • • • • • • • 2. 3. 4. s. 6. 7. through the reservoir would be about 18 percent of sediment inflow (Harza-Ebasco, November 1984); Irregularities in the river and channels configurations remain unchanged; Sed ment supply due to bank erosion is negligible. Sediment eroded from the river bed is carried downstream as bed- load. Sediment injections by tributaries is carried downstream without significant deposition; Size distribution of bed material is constant througho ut the depth at each study site; and Sufficient coarse material exists in the river bed to form an armoring layer which prevents further degradation • The size of transportable bed material was estimated using (i) competent bottom velocity concept of Mavis and Laushey (1948) given in Design of Small Dams (1974), (ii) Tractive force versus transportable size relationship derived by Lane (1953) {iii) Me y er-Peter, Muller formula (Design of Small Dams, 1974), (iv ) Schoklitsch formula (Design of Small Dams, 1974) and (v) Shields criteria (Simon and Li, 1982). Each of these methods is discussed below • 7.1.1 Competent Bottom Velocity The velocity at which a sediment particle starts to move is defined as the competent bottom velocity (Mavis and Laushey, 1948). This velocity has been found to be approximately 0.7 times the mean channel velocity. Exhibit 17 shows a relationship between the competent bottom velocity and transport~ble sediment size (Figure H-13, Design of Small Dams) which was used in the study • -16- I I I I I I I I I ·I I I I 7.1 .2 Tractive Force The tractive force is defined as the drag or shear acting on the wetted area of the channel bed for a given discharge rate (Design of Small Dams) and can be exp~essed as: Tractive force • y d S (pounds/square feet, lbs/ft2) in which: y • unit weight of water (62.4 lbs/ft3) d • average water depth, ft S • stream slope, ft/ft Exhibit 18 shows empirical relationships between tractive force and trans- portable size (Lane 1953 and , Figure H-14, Design of Small Dams). The average relationship also shown in the exhibit• was used in the study. 7.1 .3 Meyer-Peter, Muller Formula The Meyer -Peter, Muller formula for bedload transport can be written in the following form (Design of Small Dams): Q G • 1.606B (3.306 (QB) ( in which : G • bedload, tons/day B • stream width, feet D 1/6 90 >3 '2 d s-0.627 Dm)312 n s Qa • water discharge quantity directly over the area of bedload 1 transport, cubic feet per second (c f s). I I I I I Q • total water discharge, cfs D90 • particle size in millimeters (mm) at which 90 percent of bed material is finer, ns • Manning's 'n' value for the bed of the stream, -17- - - - - ·- Dm • effective size of bed material in mm usually determine as nm -r pi dsi, pi is fraction by weight of that fraction of the bed sediment with mean size dsi d • mean water depth, feet S • hydraulic gradient For no bed load transport and assuming Q • Qs, the transportable size is given by : 7.1.4 Schoklitsch Formula The Schoklitsch formula for initiation of transport can be expressed as (Design of Small Dams): -_;_• 0.:...0.:...0:...::2:...::1..,.D~i=--­q -i s4/3 in which: qi • unit discharge in cfs/foot width to initiate motion of size D1 in mm; S • hydraulic gradient ft/ft If B is width of stream in feet and Q is total discharge then D • 4762 s 413 Q B 7.1.5 Shields Criteria According to the Shields criteria, the beginning of motion of bed material can be expressed as (Simon and Li 1982): T F* • ~----~c~~-- ( Ys -y) D -18- I I I I I I I I I I I I I I I I I I I in which: F* • dimensionless number, referred to as the shields parameter; Tc • critical boundary shear stress, lbs/ft2 Ys • specific weight of sediment particles lbs/ft3 y • specific weight of wa ter (62.4 lbs/ft3) D • diameter of sediment particle, ft Shields determined a graphical relationship between F* and shear velocity Reynolds number R* to define initiation of motion. In the region where R* is between 70 and 500, the boundary is completely rough, the F* is considered independent of R*. The value of F* in this region range from 0.047 to 0 .060. A value of F* equal to 0.047 was assumed for this study. Using a specific weight of about 165 lbs/ft3 for the bed material and shear stress equal to "y d S", the transportable size is given by the following relationship: T D • -:-_ ___:;c~~-:- ( Ys -y) F* T (ft) c (165 -62.4) (0.047 ) X 12 X 25.4 • 0.207 (12 X 25 .4) T c -3944 d s in which D • transportable size, mm d • mean water depth, ft S • hydraulic gradient, ft/ft -19- (mm) r • I I I I I I I I I I I I I I 7.1.6 Depth of Degradation The depth of degradation or the depth from original streambed to top of armoring layer was computed by the following relationship given in Design of Small Dams: y -d y a 1 (--1) Ap in which Yd • depth of degradation, ft Ya • thickness of armoring layer, assumed as 3 times transportable size or 0.5 ft whichever is smaller, ~ • decimal percentage of material larger than the transportable size The transportable size for a given discharge was the average of the five sizes estimated by using the five methods discussed above. 7.2 AGGRADATION Potential aggradation at the entrances of sloughs and side channels were estimated by comparing the transportable size of the flow in the mainstem before diversion into the slough or side channel and the transportable size of the remaining flow in the main channel after diversion into side channel or slough. If the two sizes were significantly different, it was concluded that some of the bedload being transported would be deposited near the entrance. 8.0 JIJDUDLIC DA'I'A USED Ill TB1 AJIALYSBS Based on the procedures, described in the previous section, the hydraulic data required to estimate depths of degradation at the study sites in- clude: -20- I I I I I I I I I I I I I I I I I I I 1. Dominant discharges based on which transportable sizes are c~­ puted; 2. 3. Mean velocities, average depths, and channel widths corresponding to various discharge rates; Channel bed slopes; 4. Manning's roughness coefficients ('n' values); and 5. Bed caterial size distributions. These data were derived from various reports prepared by ADF&G, R~~ and H-E, as dicussed below. 8.1 DOMINANT DISCHARGE Generally, the estimation of depths of degradation is based on dominant discharge. The dominant discharge is defined as the discharge which, if allowed to flow constantly, would have the same overall channel shaping effect as the natural fluctuating discharges would. The dominant discharge for an uncontrolled stream is usually considered to be either the bank-full discharge or the peak discharge having a recurrence interval of about 2 years (Desib~ of Small Dams). With regulation of streamflow by an upstream reservoir, the definition of dominant discharge would depend on the degree of regulation and the magni- tude of flow from the area intervening between the dam site and the point of interest. If the reservoir releases follow a certain pattern without much deviation due to floods and flood flows from the intervening area are not significant, the higher discharge in the release pattern probably can be used as the dominant discharge. If the reservoir releases are subject to considerable fluctuations due to power demands or due to floods, the peak discharge having a 2-year recurrence interval would be a better representa- tive of the dominant discharge. For the Middle Susitna River under study, ~ the dominant discharge was derived based on .seekly reservoir operation -21- I I I I I I I I I I • • • • • • • • • studies for the 1996, 2001, 2002 and 2020 energy demands and is discussed under Section 9.2.2. The dominant discharges for side channels and sloughs will depend upon the frequency of overtopping the side channels and sloughs and on the magnitude and duration of the overtopped flows. The side channels and sloughs under study are overtopped currently at different mainstem discharges as shown in Table 1. Under with-project conditions, the high flows at Gold Creek will be greatly reduced unless the spiking release (being considered for flushing out fine sediments) is made from the reservoirs. Therefore, assuming that the entrances to the sloughs and side channel remain unchanged, the frequen- cy of overtopping will be greatly reduced as also discussed under Section 9.2.2. The relationships were developed between dominant discharge and transport- able size and between dominant discharge and depth of degradation. The computation were made by using data of the individual locations but the discharges at a given location are reference~ to the corresponding dis- charges at the Gold Creek stream gaging station. The computations cover a range of discharge between 5,000 and 50,000 cfs at Gold Creek • 8.2 MEAN VELOCITIES, AVERAGE DEPTHS AND CHANNEL WIDTHS For the sites on the main channel, the mean velocities, average depths and channel widths corresponding to various discharges were derived from the H-E January 1984 report. The data representative for the study sites are given in Table 2 • The discharges entering the sloughs and side channels at various discharges at Gold Creek were estimated using data available in ADF&G and RMt reports, data received with R&M letter no. 452403 dated December 6, 1984 and ADF&G letter no. 02-84-13.06 dated Deceaber 13, 1984, and additional discharge, depth, velocity and width data, observed by ADF&G at various transects in -22- I I I I I I I I I I I I I I I I I I I Sloughs SA, 9, 11 and 21, and Side Channels 10, 11 and 21. The same data were also used in determining the relationships between the slough or side channel discharges and average channel width, depths and velocities. Generally, flows enter the sloughs or side channels during medium to high river stages dependin g upon the elevations of channel inverts at the heads of the sloughs or side channels. For stages lower than these, the flows in the sloughs and side channels are either from ground water seepage or local runoff. Based on detailed field investigations, ADF&G determined the dis charges at Gold Creek at which various sloughs and side channels are over- topped (Table 1). It also determined that the discharge entering a sloughs or side channel can be expressed as a function of the discharge at Gold Creek in the following form: Q lOA (Q )B slough or side channel • Gold Creek The relationship was derived based on the data collected in 1982 through 1984. These data correspond to discharges at Gold Creek of 12,000 to 32,000 cfs. The relationships provided reasonably good comparison between the observed and computed discharges in the sloughs and side channels for the observed range of the data. However, it was found to provide unrealistical- ly high slough and side channel discharges for flows higher than 32,000 cfs at Gold Creek. Therefore, new relationships were developed by visually fitting curves to observed data. Typical relationships for Slough 9 and Side Channel 10 are shown Exhibit 19. The extension of these relationships for higher discharges is somewhat arbitrary but they represent the best relationships that can be established before additional observations are made for such discharges. After the estimation of slough and side channel discharges for a given flow at Gold Creek, the next step was to derive the corresponding channel width, average depth and mean velocity data at the sloughs and side channels. For -23- I I I I I I • • • • • • • • • • • • • the cases where depth and velocities data for a given discharge were availa- ble at a number of transects in a slough or side channel, the average of these data over the transects were used to represent the slough or side channel. ADF&G also has developed stage discharge relationships for sloughs and side channels at selected locations. These locations are shown on Exhibits 6, 7 , 8, 10, 11,_12, 13, 15 and 16. Additional cross sections also have been observed on soue sloughs and side channels • The hydraulic parameters generally change along the channel length because of changes in the cross sec tional shape and also because of presence of riffles and pools (changes in stream bed slope). Attempts were made to use the additional channel cross sections to derive representative width, aver- age depth and mean velocity corresponding to a given discharge in a slough or side channel. However, in most cases, the discharge measuring station was assumed to represent the study reach because of lack of additional data for a detailed analysis. Therefore, the stage-discharge relationships developed for the stream gaging stations and the channel cross sectional at the same locations were used to determine the representative width, average depth and mean velocity data. Typical depth-discharge and velocity-dis- charge relationships are shown on Exhibits 20 and 21 • 8.3 CHANNEL BED SLOPES The bed slopes of the reaches of the main channel were determined from the river thalweg profiles given in the H-E January 1984 report • ADF&G developed thalweg profiles for sloughs and side channels from field survey data (ADF&G, 1984). Alternate riffles and pools exist in nearly all sloughs and side channels. The bed slope changes significantly from one sub-reach to the other along the length of the sloughs and side channels. For the purpose of the present analysis, the overall slopes were used • -24- I I I I I I I I I I I I I I I I I I I Table 1 shows the overall slopes for the sloughs and side channels along with the slopes of the adjacent mainstem. These data were derived from various reports of ADF&G . The bed slopes of Side Channel 10, Upper Side Channel 11 and Slough 2 1 are steeper than those of other sites. This, probably, is the reason for the higher velocities as shown in Table 3. 8.4 MANNING'S ROUGHNESS COEFFICIENTS The Manning's roughness coefficients ("n" values) for the sloughs and side channels were estimated based on field reconnaissance. The "n" values for the sites on the mainstem were based on the data and analysis presented in the Harza-Ebasco report on water surface profiles (H-E, January 1984). The estimated "n" values are given in Table 1. 8.5 BED MATERIAL SIZE DISTRIBUTION Bed materials of the Susitna River consist mostly of gravel and cobbles with some percentage of sand. The substrate in the sloughs and side chan- nels vary significantly along the channel length. Moderate to heavy deposits of silt and sand over gravel and cobbles are visible in the pool areas. The substrates at riffles are generally of clean gravel, cobbles or so~etimes boulders. Near the head of the sloughs, the substrates are clean with little deposition of fine ~aterial. In backwater areas near the mouths, some deposition of silt and sand occurs over gravel and boulders. The size distribution of bed material greatly affect the evaluation of sedimentation process. Therefore, representative bed material size distri- bution data was considered essential for the study. Harza-Ebasco took about 36 sediment samples (see footnotes on Table 4) at the selected locations in the mainstem, sloughs and side channels. The samples were taken both from surface and sub-surface layers. -25- I I I I I I I I I I I I I I I I I I I In the mainstem of the Susitna River, the surface material is generally coarser compared to the sub-surface material. The bed material saQples collected in the sloughs and side channels, however, did not show any dis- tinct difference between the surface and sub-surface materials. The surface and sub-surface samples at a given site were combined to determine the size distribution. The adopted size distributions are given in Table 4 and shown on Exhibits 22 to 33. These are considered only indicative of the bed material at the specific sites because many additional samples will be required to determine a representative size distribution for the whole length of the study reach. 9.0 SEDIMENTATION PROCESS 9.1 NATURAL CONDITIONS 9.1.1 River Morphology The Susitna River between Devil Canyon and above the confluence of the Susitna and Chulitna Rivers, has a single channel or a split channel con- figuration. A number of barren gravel bars or moderately to heavily vegetated islands exist in the river. The mid-channel gravel bars appear to be mobile during moderate to high floods (R&M, January 1982). A number of tributaries including Portage Creek, Indian River, 4th of July Creek and Lane Creek join the main river in this reach. Almost each tributary has built an alluvial fan into the river valley. Due to relatively steep gradi- ents of some of these tributaries, the deposited material is somewhat coarser than that normally carried by the Susitna River. Vegetated islands generally separate the main channel from side channels and sloughs. These sloughs and side channels exist on one bank of the river at locations where the main river channel is confined towards the opposite bank. The flows enter into these sloughs and side channels depending upon -26- I I I I I I I I I I I I I I I I I I I the elevations of the berms at their heads. relative to the mainstem river stages (see Table 1). Coarser bed materials are generally found at the heads of sloughs and side channels. This is because the flow enters these sloughs and side channels is from the upper layer of the flow in the main channel and does not carry coarse material. This relatively sediment free flow picks up finer bed material at the heads. thereby. leaving coarser material. A preliminary report was prepared by Arctic Environmental Information and Data Center (AEIDC) on morphological changes in the Susitna River (AEIDC. Hay 1984). The changes are evaluated based on photographs taken during 1949 through 1951 and 1977 through 1980. Results of the evaluation indicate that some sloughs have come into existence since 1949-51. some have changed character and/or type significantly. and others have not yet changed enough to be noticeable. Many sloughs have evolved from side channels to side sloughs or from side sloughs to upland sloughs. Thus. they are now higher in elevation relative to the water surface in the mainstem at a given dis- charge. The perching of the sloughs and increased exposure of gravel bars above the water surface are indicative of river degradation over the 35-year period. However. the photographs presented in the report also show signifi- cant increase in the number and/or size of barren gravel bars which indi- cates that depositions also have occurred. Therefore. both aggradation and degradation can be expected to occur in the Susitna River under natural conditions depending upon the flows and sediment loads. 9.1.2 Channel Stability The channel stability at each of the study sites was evaluated by comparing the median diameter of bed material (Table 4) with the transportable sizes under various discharges. These sizes were estimated using the procedures discussed in Section 7.0J"General Approach". and are listed in Table 5. Exhibits 34 through 47 show the relationships between discharges at Gold Creek and transportable sizes at the study sites. -27- I I I I I I I I I I I I I I I I I I I A comparison of median diameters listed in Table 4 and transportable sizes listed in Table 5 shows that: 1. 2. 3. For all the study sites in the main channel, the transportable sizes for a flow of about 15,000 cfs or greater at Gold Creek are considerably larger than the median sizes (d5o) of the bed materi- al. Therefore, for a discharge of this magnitude or greater, active exchange of particles occurs between the channel bed and the bedloads carried by the flow. This undoubtly has cuased temporal deposition and scour in the past and likely exhibits similar behavoirs at present . The extent of the deposition or scour can not be predicted with any degree of certainty because it depends on so cany factors such as the flow, sediment loads and ice james all of which are highly unpredictable. In North-east and North-west Forks of Mainstero 2 Channel, the transportable sizes corresponding to a flow of about 55,000 cfs at Gold Creek are smaller than the median size of the bed material. Therefore, these sub-channels are stable under the present condi- tions . However, the channel downstream from the confluence of these sub-channels, indicates the transportable sizes larger than the median size for flows of about 35,000 and above at Gold Creek. Thus, this channel likely exhibits temporal deposition and scour for flows larger than about 35,000 cfs at Gold Creek or equivalent river flow caused by breaching of an ice jam. For Sloughs 8A and 11 and Side Channel 21, the transportable sizes correspondins to flows upto about 55,000 cfs at Gol~ Creek, are smaller than the median size of bed material at these sites. Therefore, appreciable changes in the channel cross-sections are not expected at these sites upto a flow of about 55,000 cfs at Gold Creek. However, much larger floods or higher river flows -28- I I I I I I I I I I I I I I I I I I I 4. 5. caused by breaching of ice jams can cause deposition and/or scour. For Slough 9, the transportable size corresponding to a flow of about 45,000 cfs at Gold Creek, is larger than the median bed material size. Therefore, active exchange of sediment particles is expected between the channel bed and bed load being carried, causing temporal scour and deposition. fl Similar phenomen•n (active exchange of sediment particles between the channel bed and bed load) causing temporal scour and/or deposition, exists in Side Channel 10, Upper and Lower Side Channels 11 and Slough 21 for flows corresponding to flows larger than about 30,000, 35,000, 25,000 and 45,000 cfs respectively, at Gold Cre~k. Based on the above observations, it can be concluded that most of the selected sites are subject to temporal scour and/or deposition under natural conditions depending upon high flows (caused by flood or breaching of ice jams) and characteristics of sediment load being transported. 9.1.3 Intrusion of Fine Sediments The fine sediments consisting of medium to fine sand, and silt (particle sizes between 0.50 to .004 me) have been observed deposited on gravel bars and banks of the mainstem channel and side channels during low flows. In sloughs, the deposits have been observed in backwater areas and in pools. Field reconnaissances during 1983 and 1984 indicated that much of these deposits (except those in the pools of the sloughs) were removed during high flows. This was because of disturbances of surface bed material layer under high flows, which caused the fine sediment to be re-suspended. -29- I I I I I I I I I I I I I I I .I I I I The analysis of suspended sediment data collected at Gold Creek (H.E., November 1984) indicates that, on the average, about 56 percent of suspended load is finer than 0.5 mm. Thus, there is a high probability of fine sedi- ments depositing on channel bed. A number of laboratory studies are available to understand the process of the intrusion of fine sediments in a gravel bed (Carling, 1984; Einstein, 1968, Beschta and Jackson, 1979 and Cooper, 1965). These studies indicates that at low velocities, deposition occur on the surface of substrates wh i le at high velocities the surface is flushed clean. 9.2 WITH-PROJECT CONDITIONS 9.2.1 River Morphology The construction of the Susitna Hydroelectric Project will change the streamflow pattern and also will trap sediments. The essentially sediment-free flows from the reservoirs will have the tendency to pick-up bed material and cause degration. The modified discharges downstream from the dams, however, will have reduced compentence to transport sediment especially that brought by the tributaries. These two factors tend to com- pensate with each other, resulting in the overall effects discussed below. The Lane's relationship discussed under Section 7.0, "General Approach", is ~ased on equilibrium concept, that is, if any change occurs in one or two parameters of the water and sediment discharge relationships, the river will strive to compensate the other parameters so that a new equilibrium is attained. In the case of the Susitna River, both water discharge and bed load discharge will he modified by the reservoirs. Therefore, adjustments will occur in the river channel and particle sizes of the bed material. A number of studies (Hey, et al 1982) have indicated that the new median diameter under with-project conditions may correspond to the D9o or D95 of the original bed material. -30- I I I I I I I I I I I I I I I I I I I The potential morphological changes of the Susitna River also were addressed qualitatively by R&M (January 1982). It was argued that the Susitna River between Devil Canyon and the confluence of the Susitna and Chulitna Rivers would tend to become more defined with a narrower channel. The main channel river pattern will strive for a tighter, better defined meander pattern within the existing banks. A trend of channel width reduction by encroach- ment of vegetation and sediment deposition near the banks would be expect- ed. 9.2.2 Channel Stability Potential degradation at the selected sites were estimated for various dis- charges using the procedure discussed under "General Approach". The rela- tionships between the index discharge at Gold Creek and estimated degrada- tion at various sites are shown on Exhibits 48 through 59. The potential degradation at each site estimated from these relationships is listed in Table 6. These estimates are based on the assumption that there would not be significant supply of coarse sediments by the tributaries and also there would not be redeposition of bed material eroded from upstream channel. Table 7 shows average weekly flows at Gold Creek for four project operation scenarios and for natural conditions. These data were obtained from recent H-E studies (under preparation). These data indicate about 50 percent re- duction in flows during May through SepteMber period and about 3 to 4 times increase in flows during October through April period. Table 8 shows annual maximum weekly flow at Gold Creek for natural and witl~project conditions. Under with-project conditions, the maximum weekly flows occurs under 2002 load conditions. Using the average of these annual maximum weekly flows as the dominant discharge (about 30,000 cfs), the potential degradation at the main channel sites would be in the range of about 1.0 to 1.5 feet. In the sloughs and side channels, the degradation would be about Qi to 0.3 feet. These estimates, however, are based on the assumptions that there will not be significant inject i on of bedload by the tributarites and there would not -31- I I I I I I I I I I I I I I I I I I I be redeposition of sediment eroded froo upstream channel. In actual situa- tions, there ~ill be sediments carried down by the tributaries and some of which will be deposited in the main river. Redeposition of some sediment eroded from upstream channel will occur. Therefore, actual degradation at the main channel sites would be less than those estimated. Table 3 shows that bifurcation of flow at the heads of the sloughs and side channels will not significantly reduce the discharge rates in the main chan- nel. Therefore, the competence of flow to transport bed material will not be affected due to bifurcation of flow and little aggradation should be expected in the main channel near the entrances ·to the sloughs and side channels. As discussed above, the main channel will have the tendency to degrade and to be more confined with a narrower channel. This may cause the main chan- nel to recede from the heads of sloughs and side channels. Therefore, the berms at the heads of the sloughs and side channels would be overtopped at higher discharges than those under natural conditions. Assuming that the river bed at the entrances would be lowered by about one foot due to the degradation, larger mainstem discharges would be required to overtop the sloughs and side channels. Thus, the overtopping of the sloughs and side channel will be less frequent, and the estimated 0 to 0.3 feet degradation for the sloughs and side channels would be smaller. This could cause some of sloughs and side channels to become less effective, but some new sloughs Qr side channels will likely be created by the new flow regime in the Susitna River. 9.2.3 Intrusion of Fine Sediments As discussed under "General Approach", the reservoir will trap all sediment except particles sizes of .004 mm and less, which constitute about 18 per- cent of the suspended load. The velocities at the study sites (Table 2 and 3) would be sufficiently high to carry these fine particles in suspension, -32- I I I I I I I I I I I I I I I I I I I and the substrates would generally be cleaner. However. some coarse silt and fine sand might be picked up from the river bed which would have the tendency to settle out in pools and backwater areas. Therefore. some depo- sition of such silt and sand in the sloughs and side channel is possible. and it may be desirable to operate the pr oject such that the sloughs and side channels are overtopped at least for a few days each year. unless other means such as "Gravel Gertiea" ar~ employed to flush out the fine sediment deposition. -33- - • • • • • • • • • • • • • • • • • • REFERENCES Acres American Incorporated, 1982: Susitna Hydroelectric Project, Feasibility Report, Volume 1, Basin Description, Final Draft, prepared for Alaska Power Authority • Arctic Environmental Information and Data Center, University of Alaska, May 1984: Geocorphic change in the Devil Canyon to Talkeetna Reach of the Susitna River since 1949, submitted to Harza-Ebasco Susitna Joint Venture for Alaska Power Authority. Alaska Department of Fish and Game, Susitna Hydro Aquatic Studies Team, 1983: Phase II Basic Data Report, Volume 4: Aquatic Habitat and Instream Flow Studies 1982, Appendices F to J, prepared for Alaska Power Author! ty • Alaska Department of Fish and Game, Susitna Hydro Aquatic Studies Team, 1983: Phase II Hasic Data Report, Voluce 4: Aquatic Habitat and Instream Flow Studies 1982, Part II, prepared for Alaska Power Authority • Alaska Department of Fish and Game, Susitna Hydro Aquatic Studies Team, 1983: Phase II Basic Data Report, Volume 4: Aquatic Habitat and Instream Flow Studies, 1982, Part I, prepared for Alaska Power Authority • Alaska Department of Fish and Game, Susitna Hydro Aquatic Studies Team, 1983: Phase II Basic Data Report, Volume 4: Aquatic Habitat and Instream Flow Studies 1982, Appendices B and D-E, prepared for Alaska Power Authority • Alaska Department of Fish and Game, Susitna Hydro Aquatic Studies Team, May 1984: Aquatic Habitat and Instream Flow Investigations (May-October -34- • • • • • • • • • •• • • • • • • • • • 1983), Report No. 3, Part I, Chapter 1, Chapter 1 Appendices, and Chapter 2, prepared for Alaska Power Authority • AlasRa Department of Fish and Game, Susitna Hydro Aquatic Studies Team, 1984: Aquatic Habitat and Instream Flow Investigations (May-October 1983), Report No. 3, Part II, Chapter 7, prepared for Alaska Power Authority • Beschta, R.L., and W.L. Jackson, 1979: The Intrusion of Fine Sediments into Stable Gravel Bed, J. Fish. Res . Board, Cun. 36: 204-210 • Carling, P.A., 1984 : Deposition of Fine and Coarse Sand in an Openwork Gravel Bed, Can. J. Fish. Aquat. Sci. 41: 263-270 • Cooper, A.C., 1965: The Effect of Transposed Stream Sediments on the Survival of Sockeye and Pink Salmon Eggs and Alevin, Bulletin XVII, International Pacific Salmon Fisheries Commission, Canada • Einstein, H.A., 1968: Deposition of Suspended Particles in a Gravel Bed, J. of Hydraulic Division, Proceedings of ASCE, Vol. 94, No. HY5, pp • 1197-1205 • Harza-Ebasco Susitna Joint Venture, Susitna Hydroelectric Project, April 1984: Reservoir and River Sedimentation, Final Report, Document No • 475, prepared for Alaska Power Authority • Harza-Ebasco Susitna Joint Venture, Susitna Hydroelectric Project, November 1984: Lower Susitna River Sedimentation Study, Project Effects on Suspended Sediment Concentration, Draft Report, prepared for Alaska Power Authority • -35- Harza-Ebasco Susitna Joint Venture, Susitna Hydroelectric Project, January 1984: Middle and Lower Susitna River, Water Surface Profiles and Discharge Rating Curves, Volumes I and II Draft Report, Document No. 481, prepared for Alaska Power Authority. Hey, R.D., J.C. Bathurst and C.R. Thorne, editors, 1982: Gravel-Bed Rivers Fluvial Processes, Engineering and Managecent, John Wiley and Sons, New York. Knott, J.M., and Stephen w. Lipscomb, 1983: Sediment Discharge Data for Selected Sites in the Susitna River Basin, Alaska, 1981-82, U.S. Geological Survey Open-file Report 83-870, prepared in cooperation with the Alaska Power Authority. Lane, E.W., 1955: The Importance of Fluvial Morphology in Hydraulic Engineering ; Proc., ASCE, Vol. 21, no. 745, 17 p. Leopold, L.B., and T. Maddock, 1953: The Hydraulic Geometry of Stream Channels and Some Physiographic Implications, USGS Prof. Paper 252, 57 P• Lane, E.w., and E.J. Carlson, 1953: Some Fact ors Affecting the Stability of Canals Constructed in Coarse Granular Mat e rials, Proceedings of the Minnesota International Hydraulics Convention , Joint Meeting of ~IR and ~ydraulics Divisio n, ASCE. Mavis, F.T., and L.M. Laushey, June 1948: A Reappraisal of the Beginning of Bed-Movement Competent Velocity, International Association for Hydraulic Research, Second Meeting, Stockholm. Peratrovich, Nottingham and Drage, Inc.; November 1982: Susitna Reservoir Sedimentation and Water Clarity Study, prepared for Acres American Inc. -36- I I I I I I I I I I I • • • • • • • • R and M Consultants, Incorporated, December 1982: Susitna Hydroelectric Project, Field Data, Collection and Processing. Supplement 1, prepared for Acres American Incorporated for Alaska Power Authority. R and M Consultant, Incorporated, February 1982: Susitna Hydroelectric Project, Field Data, Collection and Processing. Volume 3, prepared for Acres American Incorporated for Alaska Power Authority. R and M Consultants, Incorporated, January 1982: Susitna Hydroelectric Project, River Morphology, prepared for Acres American Incorporated for Alaska Power Authority. Simons, Li & Associates, 1982: Engineering Analysis of Fluvial Systems, Fort Collins, Colorado. Santos-Cayudo, J. and D.B. Simons, 1972: River Response, Environmental Impact on Rivers, H.W. Shen, Editor, Chapter 1, Water Resources Publications, Fort Collins, Colorado. Simons, D.B., and Fuat Senturk, 1977: Sediment Transport Technology, Water Resources Publications, Fort Collins, Colorado • Simons, D.B. and R.M. Li, 1978: Degradation Below the Emergency Spillway Chute of the Site 8C, T or C Williamsburg Watershed, New Hexico, Report for USDA, Soil Conservation Service, Albuquerque, New Mexico • Simons, D.B. and R. H. Li, 1978: Erosion and Sedimentation Analysis of San Juan Creek, New Conrock Gravel Pit, Orange County, California, Technical Report for Dames and Moore, Denver, Colorado • Schumm, S.A., 1971: Fluvial Geomorphology. The Historical Perspective, River Mechanics, H.W. Shen, editor, Vol. I., Chapter 4, Water Resources Publications, Fort Collins, Colorado • -37- I I I I I I I I I I I I I I I I I I I United States Department of the Interior, Bureau of Reclamation, 1974: Design of Small Dams, A Water Resources Technical Publication, Second Edition, Revised Reprint. -38- • T Cohesive Sediments: Sediments whose resistance to initial movement or erosion is affected mostly by cohesive bonds between particles. Colloids: Finely divided suspended solids which do not settle in a liquid. Concentration of Sediment (by weight): The ratio of the weight of dry sediment in a water-sediment mixture to the weight of the mixture. This concentration, determined as parts per million (ppm) can be converted to grams per cubic meter or milligram per litre. Contact Load: Sediment particles that roll or slide along in almost continuous contact with the streambed. Degradation: The process by which stream beds, flood plains and the bottoms of other water bodies are lowered in elevation by the removal of material from the boundary. Density of Water-Sediment Mixture: Bulk density which is mass pe r unit volume including both water and sediments. Deposition: The mechanical or chemical processes through which sediments accumulate in a resting place. Discharge-weighted Concentration: Dry weight of sediment in a unit volume of stream discharge, or the ratio of discharge of dry weight of sediment to discharge by weight of water-sediment mixture. Erosion: The wearing away of the land surface (including river beds, etc.) by detachment and movement of soil and rock fragments through the action of moving water and/or other geological agents. I I I I I I I I I I I I I I I I I I I ; . ....._ .. .:. Fine Material: Particles of size finer than the particles present in appreciable quantities in the bed material; normally silt and clay particles (particles finer than 0.062 mm). Scale of particle sizes for sediment is given below: Class Name Boulders Cobbles Gravel Very coarse sand Coarse sand Medi\111 sand Fine sand Very fine sand Coarse silt Medi\111 silt Fine silt Very fine silt Coarse clay Mediun clay Fine clay Very fine clay Colloids Millimeters >256 256 -64 64 -2 2.0 -1.0 1.0 -0.50 0.50 -0.25 0.25 -0.125 0.125-0.062 0 .062 -0.031 0.031 -0.016 0.016 -0.008 0.008 -0.004 Micrometers (microns) 2,000 -1,000 1,000 500 500 250 250 125 125 62 62 31 31 16 16 8 8 4 4 2 2 1 1 0.5 0.5 0.24 (0.24 Fine Material Load (or wash load): That part of the total sediment load that is composed of particle sizes finer than those represented in the bed. Normally the fine-sediment load is finer than 0.062 mm for a sand-bed channel. Silts , clays and sand could be considered as wash load in coarse gravel and cobble bed channels. A-3 I I I I I I I I I I I I I I I I I I 1 Load (or sediment load): Sediments that is being moved by a stream. Measured Sediment Discharge: The quantity of sediment passing a cross sec- tion of a stream in a unit of time that is computed with information derived from sampling. Sampling with suspended-sediment samplers makes the measured sediment discharge the same as the measured suspended-sediment. this is generally computed as the product of: (1) the discharge weighted concentra- tion from the suspended-sediment samples, (2) the total water discharge through the cross section, and (3) an appropriate units conversion constant. Thus, measured suspended-sediment discharge for the cross section includes all of the suspended-sediment moving in the sampled zone, but only part of the suspended sediment moving in the unsampled zone. This is because the water discharge in the unsampled zone was included with sediment concentra- tion which is generally less than that in the unsampled zone (a concentra- tion gradient exists). Median Diameter: The size of sediment such that one-half of the mass of the material is composed of particles larger than the median diameter, and the other half is composed of particles smaller than the median diameter. Noncohesive Sediments: Sediments consisting of discrete particles; for given erosive forces, the movement of such particles depends only on the properties of shape, size, and density and on the position of the particles with respect to surrounding particles. Particle-Size Distribution: The frequency distribution of the relative amounts of particles in a sample that are within specified size ranges or a cumulative frequency distribution of the relative amounts of particles coarser or finer than specified sizes. Relative amounts are usually ex- pressed as percentages by weight (mass). I I I I I I I I I I I I I I I I I I I Sediment (or fluvial sediment): Fragmental material that originates from weathering of rocks and is transported by, suspended in, or deposited by water. Sedimentation: A broad term that pertains to the five fundamental processes responsible for the formation of sedimentary rocks: (1) weathering, (2) detachment, (3) transportation, (4) deposition, and diagenosis, also means the gravitational settling of suspended-sediment particles that are heavier than water. Sediment Delivery Ratio: The ratio of sediment yield to gross erosion ex- pressed in percent. Sediment Discharge (or sediment load): Quantity of sediment that is carried past any cross section of a stream in a unit time. Discharge may be limited to certain sizes of sediment or to discharge through a specific part of the cross section. Sediment Yield: Total sediment outflow from a watershed or a drainage area at a point of reference and in a specified time period. !his is equal to the sediment discharge from the drainage area. Spatial Concentration: Dry weight of sediment per unit volume of water- sediment mixture in place or the ratio of dry weight of sediment to total weight of water-sediment mixture in a sample taken from a place, or unit volume of the mixture at a place. Suspended Load (or suspended sediment): Sediment that is supported by upward components of turbulent currents and stays in suspension for an appreciable length of time. Also quantity of suspended sediment passing through a stream cross section above the bed layer in a unit of time . A-5 I I I I I I I I I I I I I I I I I I I Total Sediment Load (or total sediment discharge or total load): Total sediment load (or discharge) of a stream, it is sum of suspended load (or discharge) and bedload (or bedload discharge) or the sum of bed-material load (or bed-material discharge) and wash load (or wash load discharge). Velocity-Weighted Sediment Concentration: Dry weight of sediment discharged through a cross section during unit time. Wash-load Discharge (wash load): That part of total sediment discharge that is composed of particle sizes finer than those represented in the bed and is determined by available bank and upslope supply rate. i I Table 2 I HYDRAULIC PARAMETERS FOR MAINSTEM SITES Loution Gold Creek Diacharae (cfs) I 3,000 5,000 7,000 9,700 l3 ,400 17,000 23,400 34,500 52,000 Near River Crose Section 4 Diacharge , cfa 3,090 5,150 7,210 9,990 13,800 17,500 24,100 35,500 53,600 I Width, ft 650 750 860 1,010 1,200 1,380 1,640 2,060 2,680 Depth, ft 2.9 3.4 3.9 4.6 5.5 6.3 7.3 8.9 10.6 Velocity, ft/aec 2.7 3.4 3.8 4.4 4.4 4.3 4.2 4.6 4.9 6~._.. I ~ River Crou Section• 12 and 13 Diacharge, cfs 3,090 5,150 7,210 9,990 13 ,800 17 ,500 24,100 35,500 53,600 Width, ft 380 410 425 445 460 473 495 518 545 I Depth, ft 5.6 6.6 7.6 8.0 9 .2 9.9 ll.2 13.1 16.0 Velocity, ft/aec 2.3 3.0 3.4 4.2 4.7 5.3 6.1 7.0 7.7 Upatream from Lane creek I Diacharge, cfs 3,090 5,150 7,210 9,990 13,800 17,500 24,100 35,500 53,600 Width, ft 850 960 1,020 1 ,llO 1,350 1,680 1,790 1,860 1,900 Depth, ft 5.9 6.8 7.4 8.2 8.5 9.3 10.0 ll.O 12.9 Velocity, ft/aec 1.7 2.2 2.6 3.1 4.1 4.3 5.2 6.7 7.5 I Upatream from 4th of July Creek Discharge, cfa 3,000 5,000 7,000 9, 700 13,400 17 ,ooo 23,400 34,500 52,000 I Width, ft 250 340 430 580 800 970 1,150 1,250 1,380 Depth, ft 6.3 7.2 7.7 8.3 9.0 9.3 10.1 10.6 11.6 Velocity, ft/aec 2.1 2.7 3.3 4 .0 4.9 5.8 6.2 7.4 8.8 I Jletween River Croaa Section a 46 and 48 Diacharge, c fa 3,000 5,000 7,000 9,700 13,400 17,000 23,400 34,500 52,000 Width, ft 305 385 465 545 600 650 710 800 920 I Depth, ft 5.1 6.2 6.9 8.1 9.0 9.7 10.6 12.0 14.1 Velocity, ft/aec 3.6 4.1 4.6 4.9 5.7 6.4 6.8 8.2 9.4 I I I ·I I I I I I '!able 3 HYDRAULIC PARAMETERS FOR SIDE CHANNELS I AND SLOUGHS Slough/ Side I Gold Creek Channel Slouah/Side Channel Location Dhcharae Dhcharae Width (Pt Velocit~ (ch) (ftf t (ft/uc (1) (2) (3) (4) (5) (6) I Hainste11 2 Side Channel Northwest Channel 17,000 150 112 1.0 1.39 I 23,400 940 117 1.9 2.78 34,500 2,940 228 2 .5 5.20 52,000 6,700 264 2.9 8.75 I Northeast Channel 34,500 650 111 3.4 1.71 52,000 2,900 124 3.8 6.09 Main Channel Below I Confluence 17,000 150 128 0.5 2.31 23,400 940 250 1.4 3.78 34,500 3,590 341 2.7 3.89 52,000 9,600 366 4.4 6.00 I Slough 8A Northwest Channel 30 ,000 19 45 0.7 0.62 I 35,000 47 45 0.9 1.18 40,000 98 45 1.0 2.21 45,000 183 45 1 .1 3. 75 52 ,000 383 46 1.3 6.58 I Northeast Channel 30,000 17 70 1.0 .42 35,000 26 71 1.1 .51 40,000 37 73 1.2 .59 I 45,000 51 75 1.4 .67 52,000 74 78 1.6 .77 Main Channel Below I Confluence 30,000 36 62 0.8 .72 35,000 73 66 1.0 1.14 40,000 135 70 1.1 1.74 45,000 234 72 1.2 2.68 I 52,000 457 78 1.5 3.96 Slough 9 23,400 80 73 1.3 0.82 34,500 580 151 2.2 2.34 I 45,000 1,600 156 3.0 4.03 52,000 2,650 160 3.2 5.30 I I I ~ I I Table 3 (cont' d) HYDRAULIC PARAMETERS FOR SIDE CHANNELS I AND SLOUGHS Slough/ Side I Gold Creek Channel Sloush/Side Channel Location Dhcharse Dhcharse Width Depth Velocitl (ch) (ft) (ft) (ft/uc) (1) (2) (3) (4) (5) (6) I Side Channel 10 21,000 30 38 0.8 1.00 25,000 150 83 1.5 1 .25 30,000 430 102 2.1 2.05 I 34,500 860 108 2.6 3.07 45,000 2,800 119 3.7 6.36 52,000 4,900 127 4.4 8 .75 I Lower Side Channel 1 7,000 520 275 0.9 1.75 9,700 862 280 1.3 2.27 13,400 1,420 285 1.8 2.96 17,000 2,053 290 2.3 3.60 I 23,400 3,365 295 3.2 4.64 34,500 6,133 300 4.8 6.46 45,000 9,248 300 6.3 7.87 52,000 11,565 300 7.5 8.90 I Upper Side Channel 11 17,000 38 101 0.5 .75 23,400 170 117 1.0 l. 52 34,500 1,060 146 2.2 3.30 I 45,000 3,900 155 4.0 6. 70 52,000 7,800 170 5.2 8.80 Slough 11 44,000 21 24 0.5 1.65 I 46,000 33 30 0.6 1.80 48,000 94 49 0.9 2.25 50,000 176 64 1.1 2.60 52 ,000 332 84 1.3 3.00 I Side Channel 21 12,000 67 77 1.0 0.87 16,000 205 105 1.4 1.40 20,000 420 130 1.7 1.90 I 25,000 810 162 2.0 2.50 30,000 1,350 189 2.3 3.10 40,000 2,900 260 2.7 4.15 52,000 5,600 298 3.3 5 .70 I Slough 21 25,000 13 5~ 0.5 0.50 30,000 39 72 0.9 0.60 35,000 105 94 1.4 0.80 I 40,000 235 98 2.0 1.20 45,000 500 99 2.8 1.80 50,000 970 99 3.9 2.52 I I I I I I I I I I I I I I I I I I I I 1 I I 1ll ble 4 REPRESENTATIVE BED MATERIAL SIZE DISTRIBUTION FOR SELECTED SLOUGHS, SIDE CHANNEL AND MAINSTEM SITES Particle Size, .a .062 .125 .250 .500 1 .00 2.00 4.00 8.06 --Percent Finer Than 16 .o Main Channel near Crou Section 4.1 1 Main Channel between Crou Sections 12 and lll1 Main Channel upatream from ane Creekl' Hainatem 2 Side Channels at Cross Section 18.2.!1 Slough W 1 Slough 9~1 Main Channel upatream from 4th of July Creekl1 S1 de Channel lnl-1 Lower Side Channel ll, down- stream from Sloug h ttl' Sl. oug h 11..1.9.' Upperside Channel 11, up- atreaa from Slough 1~1 Main Channel between Cross Section 46 and 4&.! ... l' Side Channel 21 , downatream from Slough 2Lll 1 2 3 2 2 3 3 5 3 2 2 4 3 2 2 2 2 0 0 0 0 7 10 13 16 3 5 8 12 5 7 9 10 7 10 13 17 6 10 12 13 7 15 18 20 6 8 11 14 6 12 17 20 5 7 10 14 5 8 12 15 5 8 12 15 3 7 10 13 4 6 8 4 6 8 ~1 Baaed on 6 aamples taken at three locationa near croaa aection 4. l.1 Baaed on 2 aarplea taken near river ailea 109.3. 22 18 14 22 15 23 20 25 19 20 20 17 12 12 ~1 Baaed on 2 aa.ples taken in aain channel upatre .. froe ane Creek. !!.1 !llaed on 4 samples taken in the Kainatea 2 aide channel, at four locationa. 1 1 Baaed on 6 a.-plea taken near the alou&h in the aain channel at RM 125.6 • .§.I a. .. d on 5 samples taken near the alou&h in the uin channel at RM 128.7. L 1 Ba1ed on 3 a.-plea taken in the aain and aide channel• near .11 \i~eSfoiu2y .~;f~i taken in Slouah 10. 1 1 Baaed on 2 1amplea taken in Side Channel 11, downatre .. from Slough 11 • .!..2.1 Baaed on one aample taken in Slough 11. l.J.I !111ed on 2 aup1ea taken between croaa aectiona 46 and 48. 1.!1 !111ed on one 1aaple taken near the upetre .. end of aide channel. 29 42 24 32 21 32 29 37 18 28 30 41 27 36 34 44 30 41 27 35 27 35 24 33 17 23 17 23 32.0 70 50 48 53 47 63 55 62 58 50 50 53 40 40 Bed Material 64 .o Stzu (aa) For Given Percentage D!6 Dso Dgo 89 1. 7 20 65 77 3.0 34 78 77 5.0 35 84 73 l. 7 30 110 83 4.3 35 70 93 0.5 22 58 78 2.5 28 85 82 0.8 20 80 84 2.6 25 72 68 2. 2 32 100 68 2.2 32 100 72 3.3 30 100 62 7.5 46 96 62 7.5 46 96 ~ble 5 7RANSPORTABLE BED HATERI.\1. SIZES IN SELECTED SLOUGHS, SIDE CHANNELS AND MAINSTEM SITES Loc:ation Diac:harae at Cold Creek (c:fa) 5,000 7,000 10,000 l5 ,000 20,000 25,000 30,000 35,000 11/),000 45,000 55 ,O'lO Trana2ortable Bed Material Size Hain Channel near 18 21 24 29 33 36 38 c-> 41 43 44 48 Cro .. Sec:tion 4 Main Channel between Croaa Sec:tiona 12 & 13 21 25 28 37 44 48 53 57 60 65 76 Main Channel upatreaa 25 28 32 37 44 48 52 56 60 64 72 fr011 Lane Creek Mainate. 2 Side Channel at Croaa Sec:tion 18.2 Main Channel 6 11 18 25 31 37 43 56 North-eut Fork 5 9 13 16 18 21 24 29 North-we at Fork 5 9 13 16 17 19 21 24 Slough 8A 4 6 8 9 12 Slough 9 9 13 17 20 24 31 Main Channel upatreaa 27 31 35 40 45 50 54 57 61 64 7l from 4th of July Creek Side Channel 10 5 13 22 29 37 45 60 Lover Side Channel ll 5 9 16 22 28 34 39 45 50 61 Slough 11 5 17 Uppe r Side Channel ll 7 13 20 30 44 57 84 Main Channel between 30 35 41 49 56 62 68 73 79 84 94 Croaa Sec:tiona 46 and 48 Side Channel 21 6 10 15 18 22 25 28 31 37 Sl ough 21 3 5 9 14 21 30 58 T I '!able 6 POTENTIAL DEGRADATION AT SELECTED SLOUGHS, SIDE CRANNELS AND KAINSTEM SITES • Location Diacharse at Cold Creek (cfa) 5,000 7,000 10,000 iS ,000 20 ,000 25 ,000 30 ,000 3S ,000 (() ,000 45,000 55,ooo Eatiaated Desradation1 ft • Main Channel near 0.1 0.2 0.3 0.6 0.8 1.1 1.3 1.5 1.7 1.9 2.4 Croaa Section 4 Main Channel between • Croaa Sectiona 12 & 13 0 .1 0.2 0.3 0.4 0.6 0.8 1.1 1.3 1.8 2.4 3.7 Main Channel upatreaa 0.2 0.2 0.3 0.4 0.6 0 .8 1.0 1.2 1.5 1.8 2.5 fr0111 Lane Creek • Hainatea 2 Side Channel at Croaa Section 18.2 Main Channel 0 0 0 0 0 0.1 0 .2 0.3 0.5 0.7 1.2 • Nor th-ea at Fo r k 0 0 0 0 0 0 0 0.1 0.1 0.2 0.2 North-eat Fo r k 0 0 0 0 0 0 0 0.1 0.1 0.2 0.2 Slough 8A 0 0 0 0 0 0 0 0 0 0 0 -Slough 9 0 0 0 0 0 0 0 0.1 0.2 0.3 0.5 Main Channel upstream 0.3 0.3 0.4 0.6 0.8 1.1 1.3 1.5 1.7 2.0 2 .5 from 4th of July Creek -Side Channel 10 0 0 0 0 0 0.1 0.2 0.4 0.6 1.0 2.0 Lover Side Channel 11 0 0 0 0.1 0.2 0.3 0.5 0.7 1.0 1.3 2. 1 -Slough 11 0 0 0 0 0 0 0 0 0 0 0. 1 Upper Side Channel 11 0 0 0 0 0 0.1 0.2 0.3 0.6 0.9 1.8 -Main Channel between 0.3 0.4 0.6 0.9 1.2 1.4 1.7 1.9 2.1 2.4 2.8 Croaa Sections 46 and 48 • Side Channel 21 0 0 0 0 0 0 0.1 0.1 0.2 0.2 0 .3 Slough 21 0 0 0 0 0 0 0 0 0.1 0.2 0.5 • • - - - - I ' 'nable 7 I NATURAL AND WIT!t-PROJECT AV!RAC! WElKLY FLCJlS OF SUSITNA RIVER AT COLD CREEK (:t: 9 50-1983) I With-Project Flonl1 1996 2001 2002 2020 Natural Load !Dad !Dad !Dad "' ~ ""' I Week..!' Flov Con cUtiona.!' Conditional' Conditiona.!!.1 Condit••"' (T) (2) (3) (4) (5) "(6)- 1 1607 9552 9695 7027 10323 I 2 1554 9540 9679 6997 10300 3 1512 9526 9655 6965 10285 4 1494 9537 9666 6936 10201 5 1427 9518 9 639 6897 10225 6 1354 9561 9789 6903 10262 I 7 1300 9603 9775 6851 10141 8 1258 9 502 9669 68 02 10082 9 1204 9 357 9521 67 09 9957 10 1152 8711 8971 6376 9448 I 11 1149 8338 8486 6167 9117 12 1157 7953 809 3 59 59 8781 13 1167 7715 78 52 58 40 85 81 14 1216 7593 7682 5832 8500 I 15 1240 7260 7303 5670 8245 16 1408 7 028 702 8 5543 8000 17 1667 6765 6765 5534 7644 18 3654 6912 6875 5481 7532 I 19 7914 7449 7559 5910 7932 20 13466 8886 9001 6780 9067 21 18715 10440 10521 7434 9896 22 23556 11910 11953 8115 10782 I 23 27284 11367 11438 9014 10252 24 29369 11679 11741 8960 10452 25 27860 ll415 11539 10227 10322 26 26313 10974 11142 11773 10112 27 23987 10006 10161 13951 9317 I 28 24491 10124 10254 16950 9383 29 24708 10153 10275 19797 9460 30 24031 10013 10204 20915 9355 31 25294 ll002 11103 22285 9613 I 32 23320 10470 10629 21810 9415 33 22387 ll770 11072 21224 10756 34 20411 12367 12177 20478 11875 35 18377 12280 11929 18366 11281 I 36 15621 12685 12088 15756 11772 37 14039 ll783 11100 14030 10998 38 12871 11269 10790 12790 10211 39 10663 10304 10033 10750 9649 I 40 8102 8990 8726 8297 8812 41 6782 8384 8266 7258 8695 42 5348 8543 8374 6443 8557 43 43 03 8636 8456 6531 8514 44 3332 8440 834 5 6620 8461 I 45 2861 879 2 8 69 1 6824 8908 46 2562 9215 9 165 7032 9554 47 235 8 9 727 9698 7255 10122 48 2204 10196 10195 7476 10603 I 49 1978 10892 11 025 7775 11108 50 1886 111 62 11 312 7918 11474 51 1785 10796 109 15 76 7 5 11162 52 1739 1 0080 10 142 7263 10590 I 1/ F1 rat veelt 1a the firat vee It o f aonth of J anuary. I 2/ Baaed on environ.ental c ona t rainta, E-6 . J/ Watana Ope r ation. !t Wltana -Devil Canyon operatio n. I I 'Dl ble 8 I MAXIMUM NATURAL AND WITH-PROJECT WEEKLY FLOWS OF SUSITNA RIVER AT GOLD CREEK I . 1996 2001 2002 2020 Natural Load Load Load Load I Year Flow Conditions Conditions Conditions Conditions 1950 26171 10092 11534 21157 10327 I 51 30057 15024 11374 30057 11856 52 38114 14216 14216 37243 12721 53 35114 14356 15779 25643 11771 I 54 31143 13975 13975 31143 12664 55 37243 22402 19671 35236 18572 56 43543 25394 22429 32000 26000 57 37443 20071 19275 25943 13414 I 58 38686 12426 12426 37485 11817 59 44171 28700 16498 41415 14829 60 32043 13342 13914 28943 12203 I 61 38714 15622 15622 26000 13787 62 58743 26057 26057 35557 23571 63 40257 19900 19543 38549 22106 I 64 75029 18410 18410 29834 14941 65 33643 21913 21913 28514 19812 66 47686 17098 17098 28014 14719 67 54871 41459 29071 41589 30600 I 68 37343 14439 15125 29429 12551 69 18114 9861 8000 8000 10228 70 26429 9211 9409 8126 10226 I 71 47186 22857 22857 37427 22857 72 44243 18029 19488 33149 18029 73 36443 11756 11756 23171 10293 I 74 31357 11846 11846 16614 10828 75 36400 19886 18629 29900 19886 76 29843 11965 11965 25844 11530 77 46300 15438 15438 25514 14420 I 78 22786 11800 11921 20214 11685 79 32457 12955 13558 32457 12927 80 33557 13106 13264 33557 13304 I 81 46729 37029 37029 39966 37029 82 28857 12141 12145 27500 11895 83 27343 12683 13481 26586 12875 I I I I I I I I I I I I I I I I I I I I I I I ' ......... ·., J -IIIF •" -J . c ~ _a.. ____ -""'ri 1... - / I : .... 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