<0 STATE DOCUMENTS COLLECTION APR 18 1982 MONTANA STATF: ' '5RARY 930 E lyncfeln Ave. Helena, Montan? 596B1 lr J* o :& 19 81 THE IMPACT OF HUNGRY HORSE DAM ON THE AQUATIC INVERTEBRATES OF THE FLATHEAD RIVER Research Conducted By: MONTANA DEPARTMENT OF FISH, WILDLIFE & PARKS Sponsored By: BUREAU OF RECLAMATION URT OCT 2 0 '8B Montana state library "•* *-' S 574.5263 F2ih c. 1 Perry The impact of Hungry Horse Dam on the aq OCT i o«f llilHIIIIlllIDIIllllllllHlllll 3 0864 00038607 1 THE IMPACT OF HUNGRY HORSE DAM ON THE AQUATIC INVERTEBRATES OF THE FLATHEAD RIVER by Sue Perry and Patrick J. Graham Montana Department of Fish, Wildlife and Parks Kali spell, MT 59901 September, 1981 Digitized by the Internet Archive in 2013 http://archive.org/details/impactofhungryho1981perr EXECUTIVE SUMMARY The aquatic invertebrate study was begun in June, 1979, as part of a fisheries study which was funded by the Bureau of Reclamation to assess the probable impacts of several proposed power alternatives on the aquatic biota in the areas of the Flathead River affected by discharges from Hungry Horse Dam. This report contains preliminary results of research completed since the last Annual Report (Graham et al. 1980). The benthic invertebrate study was undertaken to provide baseline information on density and biomass, community composition, species diversity and life history characteristics of macroinvertebrates in the South Fork of the Flathead River downstream from Hungry Horse Dam and in the main stem Flathead River above and below the confluence with the South Fork. The 1981 Annual Report presents data on the following: a continua- tion of the tabulation of monthly mean density data for each species collected in the benthic samples which were taken at monthly intervals at three sample sites over a two year period; a comparison of invertebrate densities and biomass in control and regulated areas of the Flathead River which were calculated from samples collected during the 1980 water year (October, 1979 to September, 1980); an assessment of differences in community composition in control and regulated areas based on species presence and abundance at the three sites and on data obtained using Shannon diversity indices. The Final Report will include data obtained in other portions of the study; the evaluation bf differences in community composition in regulated and free-flowing sections of the river using ordination techniques; the results of the seasonal study of the food habits of whitefish and trout in regulated and control areas; an assessment of the experimental study on the effects of different rates of increase in discharge and times of shutdown at Hungry Horse Dam on insect drift; and an evaluation of the effects of different discharge regimes on selected insect life histories. Management implications derived from another study (Perry, in progress) on the effects of river discharges on seston, periphyton, and Aufwuchs productivity will also be included in the Final Report. Biotic diversity is severely reduced and community composition is grossly altered in the regulated South Fork of the Flathead River. The mean of the Shannon diversity indices for the four months which were used to calculate seasonal values was 0.8 at the South Fork station and generally in the range of 3.1 to 3.3 at the main river sites. The fauna in the South Fork was dominated by the dipteran family Chironomidae, which represented 85 percent of invertebrates by mean annual density. The mayflies, stoneflies, and caddisflies represented only four percent of the invertebrate density in the South Fork as compared to 75 percent at the control site. The combined effects of flow fluctuations, the severe changes in the temperature regime (varying from only 3° to 7° C annually and thus providing much colder summer temperatures and warmer winter temperatures), and the consequent changes in the food base for invertebrates are responsible for the marked changes in zoobenthic composi- tion. 1 1 In contrast to the South Fork, both main river sites (above and below the confluence with the South Fork) had diverse insect faunas. No significant differences in overall diversity were shown between the control and partially regulated (downstream from the confluence with the South Fork) sites using Shannon diversity indices. The increase in biotic diversity which generally occurs with increasing distance down- stream from a dam, occurs abruptly in the Flathead River where the South Fork joins the unregulated North and Middle Forks. The main stem Flathead River is affected by the addition of waters from the regulated South Fork, but the adverse effects on the macroinvertebrates are greatly tempered due to dilution by the North and Middle Forks. This can be attributed to factors such as temperature modification, the flushing and redeposition of sediments which occurs during spring runoff, the import of particulate organic carbon and drifting insects from upstream areas, etc. Although no significant differences were shown in species diversity, there were compositional changes in the partially regulated portion of the river. Mayflies were far more abundant in the control area (54 percent versus 27 percent), while stoneflies and dipterans showed higher densities in the partially regulated area (Plecoptera - 21 percent versus' 15 percent; Diptera - 38 percent versus 24 percent). The composition of caddisflies was markedly different at the two sites, which is probably related to differences in periphyton and particulate organic carbon particle sizes of the seston. The timing of events in the life cycles of a number of species was different at the two main river sites; this can be correlated with seasonal temperature differences in the control and partially regulated areas of the river, which are due to discharges of hypolimnetic water from Hungry Horse Dam. Annual means of individual counts (no./m2) and biomass (cc/m2) data indicate that densities of zoobenthos are higher in the South Fork (10,472 ± 6,372) than at the control (6,666 ± 6,144) and partially regulated (6,412 ± 7,078) sites. Overall, biomass is not significantly different at the three sites (control - 12.1 ± 4.2; partially regulated - 14.4 ± 9.0; regulated - 12.3 ± 5.8). The ameliorative effects of the North and Middle Forks are limited when flows from natural areas are low. Major changes in the seasonal discharge regime from Hungry Horse Dam might substantially alter the composition of invertebrates in the main stem river and possibly affect the feeding habits and movement patterns of fish. Marked increases in discharge during certain seasons (e.g. sustained high winter flows) could cause species extinctions by increasing the winter heat load in the river and causing earlier emergences of certain species into lethal air temperatures. Preliminary data indicates that winter and early spring emerging species are abundant in the drift and provide a food source for trout. Also, high rates of discharge during dry summers could reduce or eliminate species which require higher summer temperatures for growth and emergence. Until more information is available on what environmental factors are important for the maintenance of a habitat suitable for important fish food species, caution should be exercised in altering discharge regimes. Recommendations and probable changes which may accompany particular operational options will be detailed in the Final Report. iii ACKNOWLEDGEMENTS Robert Schumacher, Regional Fisheries Manager, was instrumental in developing this study. Delano Hanzel , Montana Department of Fish, Wildlife and Parks, assisted in the hiring of personnel and with arrangements for computer analyses. Jack Stanford provided for the use of the University of Montana Biological Station facilities, equipment and stonefly reference col lection. We are indebted to William Perry, who has worked as a volunteer on the project for the past year, enumerating invertebrates, supervising personnel, and assisting with data calculations and graphics. Paul Leonard and Ken Frazer assisted with field work and graphics. We are indebted to employees of the CETA and YACC programs for their assistance in the collection and sorting of insects. Among the people who spent many tedious hours sorting insects were: Dave Arland, Dennis Barrow, John Bender, Nita Davis, Debbie De Gennaro, Laurie Dollan, Dave Donaldson, Buddy Drake, Sandy Entzel , Kirk Fallon, Mark Gaub, Emmie Ibison, Wanda Jamieson, Rick Johnson, Susan Kraft, Cathy Leddy, Robert Post, Chuck Richardson, Betty Schroder, Cathy Schloeder, Terry Seliger, Wendy Senger, Arlene Sinclair, John Squires, Jill Stanley, Ron Tate and Ande Wood. Dave Donaldson and Rick Johnson did the bulk of the volumetric measure- ments for biomass estimates. IV TABLE OF CONTENTS Page EXECUTIVE SUMMARY ii ACKNOWLEDGEMENTS iv LIST OF TABLES vi LIST OF FIGURES vi i INTRODUCTION .... 1 STUDY AREAS 7 METHODS 11 RESULTS AND DISCUSSION 13 Species Diversity 13 Abundance and Distribution 16 Density Estimates 16 Mayflies 21 Stoneflies 27 Caddisflies 27 Dipterans 27 Biomass Estimates 28 Life History 35 RECOMMENDATIONS 37 Selective Withdrawal System 37 CONCLUSIONS 39 LITERATURE CITED 41 APPENDIX A Al APPENDIX B Bl APPENDIX C CI LIST OF TABLES Table Page 1 Shanon Diversity Indices 14 2 Densities (x no./m2) (Kick + Circular Samples). Annual Mean of Monthly Means (October 1979 - September 1980) 17 3 Macroinvertebrates with higher densities in the free-flowing Flathead River (Bible Camp sampling site). Annual mean number/ m2 (October 1979 - September 1980)' 25 4 Macroinvertebrates with higher densities in the partially regulated Flathead River (Kokanee Bend sampling site). Annual mean number/m2 (October 1979 - September 1980) .... 26 5 Biomass (cc/m2) (Kick + Circular Samples). Annual Mean of Monthly Means (October 1979 - September 1980) 29 6 Percent of total number (no./m2) of invertebrates represented by insect order (Kick and Circular samples combined) 31 7 Percent of total biomass (cc/m2) of invertebrates represented by insect order (Kick and Circular samples combined) 33 LIST OF FIGURES Figure Page 1 Daily maximum and minimum temperatures recorded at USGS stations on the North (unregulated) and South (regulated) Forks of the Flathead River from October, 1979 through March, 1980 3 2 Daily maximum and minimum temperatures recorded at USGS stations on the Middle (unregulated) and South (regulated) Forks of the Flathead River from April through September, 1980 4 3 Mean daily temperatures recorded in the unregulated (North Fork) and partially regulated (Columbia Falls) areas of the Flathead River, October, 1979 through March, 1980 5 4 Mean daily temperatures recorded in the unregulated (North and Middle Forks) and partially regulated (Columbia Falls) areas of the Flathead River, April through September, 1980 6 5 Mean daily discharge recorded in the South Fork of the Flathead River during the 1980 water year 8 6 Mean daily discharge recorded in the partially regulated Flathead River (Columbia Falls) during the 1980 water year 9 7 Macroinvertebrate sampling sites in the main stem and South Fork Flathead Rivers, 1979-1980 10 8 Mean number of invertebrates per square meter; annual means of monthly means. Bars represent means, I represents standard deviations. E = Ephemeroptera ; P = Plecoptera; T = Trichoptera; Ch = Chironomidae; 0D = Other Diptera; 01 = Other Invertebrates. 18 9 Mean numbers of total invertebrate per square meter, October, 1979 through September, 1980 19 10 Mean number/m2 of the insect orders Ephemeroptera, Plecoptera, and Trichoptera at the South Fork (regulated) sampling site, October 1979 - September 1980. N.D. = no sample taken 20 11 Mean number/m2 of insect orders Ephemeroptera, Plecoptera and Trichoptera at the Kokanee Bend (partially regulated) sampling site, October 1979 - September 1980. N.D. = no sample taken . . 22 12 Mean number/m2 of insect orders Ephemeroptera, Plecoptera and Trichoptera at the Bible Camp (control) sampling site, October 1979 - September 1980. N.D. = no sample taken 23 13 Mean number/m2 of the insect order Ephemeroptera at the control (Bible Camp) and partially regulated (Kokanee Bend) sampling vn LIST OF FIGURES CONT. Figure Page site, October 1979 - September 1980. N.D. - no sample taken. . . 24 14 Biomass (cc/m2) of invertebrates; annual means of monthly means. Bars represents means; I represents standard deviations, means of total invertebrate biomass are represented by the large blocks. T = Trichoptera; P = Plecoptera; E = Ephemeroptera ; C = Chironomidae; 0 = Other Diptera and Other Invertebrates 30 15 Degree days (mean daily temperatures) summed by the month for control (North Fork), partially regulated (Columbia Falls), and regulated (South Fork) areas of the Flathead River for the 1980 water year 36 INTRODUCTION The benthic invertebrate study was begun in June 1979, as part of a larger fisheries study to assess the impacts of various proposed power alternatives and operating regimes on the aquatic biota in the Flathead River. Hungry Horse Dam, which is located 8 km upstream from the mouth of the South Fork of the Flathead River, was completed in 1953. It is operated for flood control and power production by the Bureau of Reclamation. The crest of the dam is 1087 m above sea level. Four penstocks are located 75 m below the crest. The present minimum flow from Hungry Horse Dam is 4.2 m3/sec (150 cfs) and peak discharge is approximately 323 m3/sec (11,417 cfs). The Bureau of Reclamation is assessing several alternatives which would increase peaking capacity and total annual power production. These include uprating the existing generators, a powerhouse addition, and the construction of a reregulating dam which would have an estimated storage capacity of 2.4 x 10^ m3. Maximum discharge from the existing dam could be increased to 390 m3/sec. The aquatic invertebrate study was undertaken to provide baseline information on community composition, species diversity, biomass, and life history characteristics of macroinvertebrates in the Flathead River above and below the confluence of the South Fork and in the South Fork of the Flathead River downstream from Hungry Horse Dam. The impact of operating regimes which have been proposed to enhance the fishery are being assessed with regard to their effect on the fish food organisms. Recommendations will be based on optimizing flows which 1) cause the least catastrophic invertebrate drift and stranding; 2) provide the most insect habitat; and 3) provide the best criteria for the growth and emergence of important fish food species. The objectives of the invertebrate study are: 1. To sample the benthos at monthly intervals over a two-year period in order to compare invertebrate densities and biomass in control and regulated areas of the Flathead River. 2. To assess differences in community composition in control and regulated areas with the use of diversity indices and ordinations techniques 3. To (seasonally) study the food habits of whitefish and trout in regulated and control areas of the river and to ascertain whether certain species are feeding selectively on the drift or on the bottom. 4. To determine experimentally whether different rates of increases in discharge and times of shutdown at Hungry Horse Dam differentially affect invertebrate drift. 5. To assess the effect of regulation and of different discharge regimes on the rates of growth and times of emergence of selected aquatic insect species. -!■ The construction of Hungry Horse Dam has resulted in a number of downstream modifications which are of significance to river zoobenthos. Dams can exert profound perturbative influences on the downstream riverine environment, and rapid, short-term fluctuations due to hydropower pro- duction have profoundly altered biological processes in the South Fork. Unpredictable and fluctuating flow conditions below dams with operational schedules based primarily on power needs have a detrimental effect on the benthos by inducing catastrophic drift, causing stranding, and altering the habitat. The manipulation of discharge affects the total lotic ecosystem. Certain changes in the discharge regime from dams can benefit invertebrate populations (high minimum flows, predictable flows, selective withdrawal systems, etc.). Water discharge is a factor of key importance to the benthos, especially due to its influence on temperature, current velocity, composition of the substrate, and the availability of food (Henricson and Muller 1979). Temperature is an important environmental factor affecting the benthos in the regulated areas of the Flathead River. The hypolimnial releases from Hungry Horse Dam have stabilized temperatures in the South Fork; the yearly thermal regime is severely altered, varying only from 3° C to 7° C. The marked reduction in thermal amplitude in the South Fork as compared to the unregulated North and Middle Forks for the 1980 water year is shown in Figures 1 and 2. The lack of appropriate thermal criteria for hatching, growth and emergence may be the major factor contributing to the absence of many species of insects in the South Fork (Stanford 1975). In general, environmental heterogeneity and biotic diversity will be reduced near an upstream impoundment, but will show a progressive recovery with increasing distance downstream (Ward and Stanford 1979). This recovery occurs abruptly in the Flathead River where the South Fork joins the unregulated North and Middle Forks. Because the ameliorative effect imposed by unregulated segments is much greater than in many regulated rivers, the main stem Flathead River will be referred to as partially regulated. The main stem Flathead River is affected by the addition of waters from the regulated South Fork, but the adverse effects on the macroinvertebrates are greatly tempered due to dilution by the North and Middle Forks. The partially regulated Flathead River also shows the late fall and winter elevation (Figure 3) and summer depression (Figure 4) in river temperatures, although to a lesser extent than the South Fork. In the partially regulated areas of the river, severe thermal fluctuations over short periods of time may occur as power releases peak and wane. In the summer during periods when there is no generation, river temperatures warm quickly, since most of the flow is from the North and Middle Forks. 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Inorganic sediments settle out in the reservoir, reducing turbidity and sediment scour in the South Fork and main stem Flathead River, thus allowing increased periphyton growth. Seston from the reservoir is not abundant in the South Fork, since water is withdrawn only from the unproductive hypolimnion of the reservoir. Organic carbon is more abundant in the partially regulated areas of the Flathead River due to input from the unregulated forks and recruitment of debris from shoreline areas during generation (Perry, in progress). Regulation also affects the composition of streambed materials and thus reduces habitat diversity. Natural areas of the Flathead River are characterized by loosely compacted flood plain materials composed of large cobble interspersed with smaller gravels and sand. In the South Fork, the smaller materials have been removed from the surface layer of rocks by the clearwater discharges from Hungry Horse Dam. The reservoir acts as a settling basin for inorganic materials, so there is no redeposition of the finer gravels and sand in the tailwater area. Substrate particle size has been shown to have an important effect on community structure (Cummins 1966; de March 1976; Minshall and Minshall 1977; Williams 1980). STUDY AREAS The Flathead River drains 21,876 km2 of southeast British Columbia and northwest Montana. It is the northeastern most drainage in the Columbia River Basin. Three forks of approximately equal size drain the west slope of the Continental Divide. The South Fork flows out of the Bob Marshall Wilderness area to Hungry Horse Reservoir, a deep- storage impoundment approximately 66 km long with a storage capacity of 4,268 x 106 m3. Discharge from Hungry Horse Dam varies from a minimum flow of 4.2 m3/sec to a peak discharge of 323 m3/sec, and vertical water level fluctuations in the South Fork downstream from the dam can vary as much as 2.5 m daily. The South Fork is grossly altered for its entire course (8 km) before it joins with the North and Middle Forks of the Flathead River. The hydrograph of the main stem Flathead River below the confluence with the South Fork is determined by the sum of the dis- charge from the three forks. Peak flows in the main stem normally occur in May and June, coinciding with peak runoff in the North and Middle Fork drainages. Except for peak runoff periods, the hydrograph of the main stem parallels that of the South Fork (Figures 5 and 6). The macroinvertebrate work has been concentrated in riffle areas at three study sites: 1) South Fork of the Flathead River - 7.4 km from Hungry Horse Dam near the mouth of the South Fork; 2) Glacier Bible Camp (Control Site) - 1.2 km north of the mouth of the South Fork; and 3) Kokanee Bend Fishing Access Site - 12 km south of the mouth of the South Fork in the partially regulated main stem Flathead River (Figure 7). -7- r O O (f) m Hi SL o X > DC o z X (0 s- , 5- 1J +J TO 2 o co CTi cu -t-> CD c S- 3 T3 S- CD > rD CU -£Z 4-> 03 0J JSZ +-> <4- o ^*: i. o o +J c T3 OJ -a 5- o o cu S- cu en S- ro u t/1 >> -a < O _Q E O o Q < < UJ . I ■* I- => -j O u. O C/5 5- > -I Ql T3 ra O) _e +-> ra 1 o CO o CM o o ~T~ O (0001 X sjo) 39HVH0Sia NV3IAI -a +j ro 0.1 4-> S- ra Q. O) x: c '11 ■o s- o u CD S- OJ • ais- s- ra ro CD -s= >, o 00 S- •r- a> -D+J ro >><: •r-O raCO i— I cz ro O) OJ-C S- =s CTj -9- Bl BLE CAMP BENTHIC SAMPLING SITE COLUMBIA FALLS DRIFT SAMPLING SITE KALISPELL 0 KILOMETERS KALISPELL DRIFT SAMPLING SITE Fiqure 7. Macroinvertebrate sampling sites in the main stem and South Fork Flathead Rivers, 1979-1980. 10- METHODS Monthly sampling of benthic invertebrates at the three established sites was begun in July, 1979. Eight to ten samples were taken at each site each month through September, 1980, by a combination of systematic sampling (the transect method) and stratified random sampling (selection of habitat types). Starting in October, 1980, the sample number was reduced to three samples per month at each of the three sites until sampling was terminated in April, 1981. All samples were taken at conditions of minimum discharge from Hungry Horse Dam (4.2 m3/sec in all months but January and February, 1980, when minimum flows were 12.7 m3/sec). The maximum depth which was generally sampled was about 25 cm, which excluded animals living deeper in the substrate. Mean current velocity (taken with a Price AA current meter at the 0.6 depth) and water depths were taken just upstream from each benthic sample. Two different samplers were used in an effort to reduce biases associated with any one sampling device. Sampling in the Flathead River was difficult due to the large substrate sizes, so conventional samplers had to be modified. Both samplers enclose a sample area of one-third m2 and have a small mesh size (150 urn) for retaining small instars of insects. The modified kick net consisted of an outer rectangle 97 cm wide and 89 cm high made of Nitex with a 355 urn mesh and bordered with canvas. A bag (72 cm long, 150 urn mesh) with an opening 44 cm by 42 cm extended from the rectangular portion of the net. The net was held downstream from the sampling area which was delineated by a square made of one- quarter inch strap iron and encompassed one-third m2. The net was curved around the square with the bottom taut during sampling. Rocks in the sample area were individually lifted inside the bag and brushed clean by hand. After all of the larger rocks were removed, the collection area was disturbed by kicking for 15 seconds. Organisms were retained in a clear acrylic bucket (with a drain made of Nitex with a 150 urn mesh) at the cod end of the net. The other sampler employed in this study was a circular depletion sampler described by Carle (1976). It functioned more efficiently at faster current velocities. The height of our sampler was 54 cm and the inside circumference and diameter were 205 and 65 cm, respectively. The collecting net was made of Nitex with 150 urn mesh. Our sampler was made of aluminum, which was flexible and allowed the sampler to be wedged in around large rocks. Heavy rubber was riveted to the bottom of the sampler to provide a seal. An exact sample site was chosen by attempting to find a location where large rocks did not intersect the sampler edge. The sampler was then rapidly thrust down and turned into the substrate. If the sampler could not be stabilized and sealed within a few seconds by moving rocks, the site was abandoned. The procedure -11- was the same as with the kick net, brushing all the larqe rocks and removing them and then kicking the substrate within the sampler for 15 seconds. Organisms were preserved in 10 percent formalin to which Rose Bengal stain had been added. Macroinvertebrates were handpicked from the algae, detritus, and inorganic material, sorted to order and placed in vials containing 75 percent alcohol. The larger insects were removed (greater than 2 mm in length) and then a one-quarter or one-eight subsample was taken. The subsample was completely picked with the aid of a micro- scope. All insects were identified to the lowest taxonomic level possible and enumerated using a laboratory counter. A number of workers were employed to sort samples, so quality control procedures were adopted to insure consistency. All samples were checked by a supervisor and subsampling methods were standardized. Biomass was measured by volume displacement, with any volume less than 0.1 ml assigned a trace value of 0.05. Volumetric measurements were made with the use of a 50 milliliter burette and a graduated centrifuge tube. Three drift nets were constructed of heavy materials to accommodate changes in discharge and large enough to adequately sample when drift rates were low. These nets had a rectangular opening measuring 45.7 by 30.5 cm and a Nitex bag with 355 urn opening which was 1.5 meters long. The frame was made of angle iron with holes for steel rods which were driven into the substrate. Rubber flanges projecting backward from the edge of the net prevented large insects from walking out of the net. Adult insects were collected by hand, with sweep nets, in pit traps (buried cans containing formalin covered with a thin film of diesel fuel), and with light traps (containing uv fluorescent lights used with a battery which was operated by a photocell or used with 110 volt A.C.). Six pit traps were in position at the three sites from March to August, 1980. Light traps were operated nightly from June to October, 1980, at the control and partially regulated sites. Water samples were collected on a monthly basis from November, 1979, to November, 1980. Chemical parameters measured on water samples from the South Fork included total suspended solids (gravimetric), particu- late and dissolved organic carbon (International Oceanography Total Organic Carbon Analyzer), Na+, K+, Ca++, Mg++, NO3-, SO4 = (ion exchange chromatography Dionex Corporation), and total P (Standard Methods). The analyses were conducted by the Analytical Services Group of the Freshwater Research Laboratory at the University of Montana Biological Station. Flow data and continuous recording thermograph data which are collected by the U.S. Geological Survey were obtained for the South Fork, North Fork, and main stem Flathead River at Columbia Falls. -12- Species diversity was compared at six sites on the Flathead River using Shannon and Brillouin diversity indices. They were calculated using data collected during the months of October and December, 1979 and March and July, 1980, at the South Fork, Kokanee Bend and Bible Camp sample sites. Data collected for the fish food habits study (three kick samples per site per month taken at Columbia Falls and Kalispell during March, July and October, 1980) as well as six kick samples collected in October, 1980 at Spotted Bear (above Hungry Horse Reservoir) were also used to calculate diversity indices (Table 1). Samples were pooled by sampler type at each sample location and date. Values obtained by using the two indices were almost identical , so only the Shannon Index will be discussed. s Ni_ Ni The formula used for the Shannon function was H' = s:(N )log2(N ) i where s = number of taxa in sample, N. = number of individuals in taxon i, s and N = z:N . . A value of zero is obtained when all individuals belong to l the same species. The maximum value of H' depends on the number of individuals counted and is obtained when all individuals belong to different species. H1 usually varies between three and four in natural stream areas and is usually less than one in polluted or stressed stream areas. Evenness (Ev), as measured by Margalef (1957) is a ratio of the observed H' to a maximum theoretical diversity (H'max) computed with all individuals equally distributed among the species. Maximum diversity (H'max) was computed as log2s; therefore evenness = \V_ . Evenness generally log^s ranges between 0 and 1. Perturbation reduces Ev below 0.5 and generally to a range of 0.0 to 0.3. RESULTS AND DISCUSSION To date, 369 quantitative benthic samples have been picked and analyzed numerically and volumetrical ly. An additional 63 benthic samples from the second year of the study have been collected and picked. Species Diversity The benthic invertebrate composition was grossly different in the Scuth Fork than at the main stem stations. Species diversity was low in the South Fork. Reductions in species diversity in the tailwater areas downstream from hypolimnial release reservoirs have been found by a number of researchers (e.g. Pearson et al . 1968; Hilsenhoff 1971; Hoffman and Ki Iambi 1971; Spence and Hynes 1971; Fisher and Lavoy 1972- Lehmkuhl 1972; Ward 1974, 1976; Young et al . 1976). The fauna in the South Fork was dominated by the dipteran family Chironomidae (Appendix C). Reproducing populations of turbel larians , nematodes, ol igochaetes, and water mites were also present. A few other insect species probably -13- co CU ■a c +-> ■i — in S- O) > o co ai 03 •o ^-»CM CO r- 1 ^00 un o CO o CO o CO o 00 o o o o o o o o o o IX CO CO <-* CO CO CO Ln CO CO cr> r—i Ln in r~- o o co o CO o CO o CO o CO o 5- =3 U 1.15 0.26 3.64 0.72 3.4 0.65 >^ o 3 J cr> r-^ 1^ CO . — i CO co 1^. r-~ co r-H CM Ln r^. C\J >vl- ^t CO ■L. i-H o CO o CO o CO o CO o O CM co Ln co «3- 00 .-I O CO 1^ CM CT> CM CM O Ln r^ co in co o en cr> en Ln co o CT> CO CO l^~- en Ln CM O CTi CO r-- Ln o o cm Ln CM o o o CO r— I o o 1^ CO r-l O o o CM CO CM O CM O CM CO CO CO CM O CO i— I CM CO CO O 00 CM i— I CO CO o «— i Ln co o Ln o~> o i-n cm o cm o co cr> i— i Ln co o t— i r-» oo Ln cm o co "^J- r~- r^- con co co o Ln cm Ln o o co o co o co o CO o CO o - > - > - > - > - > - zm uj nz to re LlJ 3= ■a c: UJ DC LiJ re UJ Z3Z (0 .^ U_ a> Q. CU s- CO r— E oo o CT3 i — fO U-. -Q CU 0) CU a. o .zz fc c CO CU +-> +-> =3 ro • 1 — ( — +-> Z3 i — J*. ^~- -O o o O O fO •1— Q_ CO O ^ •^ CQ CO -14- complete their life cycles under the constant temperture conditions that exist in the South Fork, although their populations were very small. These included the stoneflies, lapada columbiana, lapada cinctipc^, Caprua 6pp., Utacapn-ia 6pp., Tanvu-Onma pacZfa-icuin , Swztt6a t>p., and VajuJuol knowttovU, the mayflies BaeXu> &vLcauda£ii6 , BantLb b icaudcutuA , RkJXhAogzna Jiobtuta., CZnygmuZa 6p. and Ep2.0K.n6 gtiancLU, the caddisfly RhijacophJJLa veAAula, and the dipteran SimoHum cutcuticum. To date, a total of 45 species of insects have been collected in the South Fork. Because only one or a few individuals of many of these species were collected, it is unlikely that they have reproducing populations in the South Fork. Many of these probably drifted downstream from Fawn Creek, a tributary of the South Fork. Some of the species collected in the South Fork were characteristic of smaller streams like Fawn Creek and have not generally been reported in rivers as large as the Flathead River. Many of these species may exist in the South Fork because they are adapted to the colder, more constant temperatures found in headwater streams. In contrast to the South Fork, both the control and partially regulated stations on the main stem Flathead River had diverse insect faunas. To date, 71 species have been identified at the control site and 70 species at the partially regulated site. The species list at each site will be much higher after adult collections have been identified (many insects cannot be identified to species in their immature stages). Species lists for the control and partially regulated sites were similar, but there were a number of differences in the abundance of species at the two sites. Species diversity was compared at six sites on the Flathead River using the Shannon diversity index. The mean of the diversity indices for the four seasons for which they were calculated was 0.8 at the South Fork station and generally 3.1 to 3.3 at the main river sites (Table 1). Thus no significant differences in overall diversity were shown between the control and partially regulated sites. Differences in composi- tion were found between the main river sites, but diversity indices do not take into account the species involved. Although diversity has been considered an intrinsic property of communities, the more recent view is that it is too vague (Hurlbert 1971) and that the two components (species richness and equitabil i ty) often vary independently (Moore 1975). Ordination and clustering methods may be more informative methods for reducing biological data and arraying it spatially. Ordination techniques will be applied to the data using two computer programs from the Cornell Ecology Program series - DECORANA, a Fortran program for detrended correspondence analysis and reciprocal averaging (Hill 1979) and ORDIFLEX, a flexible computer program for four ordination techniques: weighted averages, polar ordination, principal components analysis, and reciprocal averaging (Gauch 1977). -15- Abundance and Distribution The 1980 water year (October 1979 to September 1980) was used for detailed comparisons of numbers (no./m2) and biomass (cc/m2) at the three sample stations. Accurate quantification of numbers and biomass was difficult in a large, regulated river. With our sampling gear, it was possible to sample only at minimum flows near the shore in riffle areas. The highest densities were found near waters edge where current speeds were slower than those near the middle of the river. The Flathead River had an extensive hyporheic zone which could not be sampled. The channel and adjacent substrata were composed of loosely compacted flood plain gravels. Water circulated deep within the substrate and laterally from the river channel. This subterranean habitat was colonized by certain species of macrobenthos, in particular, a few species of stoneflies (Stanford and Gaufin 1974), which were collected only when they were near emergence. The Bible Camp site was frozen during the winter and could not be sampled during January and February. Densities were low at the Kokanee Bend site during the winter months, suggesting that some species may have moved deeper into the substrate. It was also difficult to sample during the runoff period, although reasonably good samples were obtained at waters edge during June after the shoreline areas were recolonized. It was not possible to sample during May when the runoff began, because insects had not colonized recently wetted areas. Mean numbers per square meter were calculated for each insect order at each site by month (Appendix A - Figures 16-27). The Chironomidae were treated separately due to the large numbers represented by this family of dipterans in regulated areas. The monthly means were averaged to give an annual mean (Table 2, Figure 8). The chironomids and oligochaetes dominated in the South Fork and the mayflies, stoneflies, and caddisflies were much reduced. The annual mean for the mayflies was much higher at the control site, but the annual mean numbers of the other orders were larger at the partially regulated site. The annual mean number/m2 of total macroinvertebrates was highest in the South Fork (10,472), but not significantly different at the Bible Camp (6,666) and Kokanee Bend (6,412) sites. The total number of inverte- brates was most affected by the numerically dominant groups - the midges, blackflies, certain mayflies and large numbers of small instars of any of the common species. During most months the total number of invertebrates per square meter was highest in the South Fork (Figure 9). Differences between the Bible Camp and Kokanee Bend sites were due to compositional shifts and differences in the timing of life cycles at the two sites. Density Estimates The mean monthly densities of the three insect orders more sensitive to perturbation were graphed for the South Fork (Figure 10), Kokanee -16- Table 2. Densities (x no./m2) (Kick + Circular Samples) Annual Mean of Monthly Means (October 1979 - September 1980) Bible Camp Kokanee Bend South Fork n=9 n = 9 n=ll x(s.d.) x(s.d.) x(s.d.) Ephemeroptera 3,608(1,789) 1,738(899) 330(193) Plecoptera 990(1,201) 1,335(1,753) 76( 37) Trichoptera 374(332) 522(483) 8( 7) Chironomidae 1,427(534) 1,739(992) 8,931(3,078) Other Diptera 194(359) 708(1,465) 148(313) Other Invertebrates 74( 56) 370(269) 979(344) TOTAL 6,666(3,072) 6,412(3,539) 10,472(3,186) Percent Composi tion % % % Ephemeroptera 54.1 27.1 3.2 Plecoptera 14.9 20.8 0.7 Trichoptera 5.6 8.1 0.08 Chironomidae 21.4 27.1 85.3 Other Diptera 2.9 11.0 1.4 Other Invertebrates 1.1 5.8 9.3 17- 3ui / oN x -18- cc O u. I 3 o CO UJ 0. CD 5 < UJ (J 111 z Ui < _i m o OQ * - CO 3 -< -2 — ~3 - z - o o CO S- o. ai LO -C CT Z3 O S- cn en OJ -Q O +-' u o a; +-> 01 E CD S- ro =5 CT 1/1 <~ 1' Cl OJ +-' rd i- J3 0) > O +-> .o c (O T T n\Vr o oo -r T to t T co M I 0001 x) 7w /-on X CT. S- Z5 cr, -19- - CO I- < o in CD 4J rO rO 5- OJ 4-> CL o < UJ (- a O oc UJ 2 UJ X 0. UJ < a: UJ h- a o o < UJ (- a. 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CLQ E . ra ^ CJ cd . r, i — 0 _Q CO • r- cx> CQ 1 — 1 — ■* S- i — CD O JD 5- E +J CD C +-> o Cl u CD U~) ■v JZ 1 +-> en 4-> r-» ra en 1 — 1 ra 5- s_ a> a) +j .a Cl 0 O +-> t- 0 UJ • 1— CO S^ V CJ) -a c: S- •( — o 1 — CL +J E u 03 CD 00 t/1 c - — . ■1— X5 c OJ O) jc CQ 4-> O) ^- CD O c ra CVI -^ E 0 ^ S- CD jQ -0 E CD Z5 4-> c ra • 1 — c c zs ai rrj cn-^: a> CD ra 2: U. -M 00 5- .24- Table 3. Macroinvertebrates with higher densities in the free-flowing Flathead River (Bible Camp sampling site). Annual mean number/m2 (October 1979 - September 1980). Bible Camp Kokanee Bend x(s.d. ) x(s.d.) EPHEMEROPTERA Baetis hageni 247(277) Rhithrogena hageni 1,079(910) Epeorus sp. 116 ( 78) Ephemerella doddsi 59( 58) Ephemerella inermis 198(188) Paraleptophlebia heteronea 36 ( 36) TRICHOPTERA Symphitopsyche oslari 130(183) Symphitopsyche cockerel li 35 ( 40) Hydropsyche occidental is 33( 42) DIPTERA Hexatoma sp. 7( 9) 3( 3) 43 ( 75) 258(179) 37( 85) 28 ( 30) 111(138) 3( 4) 20 ( 36) IK 15) 4( 6) -25- Table 4. Macroinvertebrates with higher densities in the partially regulated Flathead River (Kokanee Bend sampling site). Annual mean number/m2 (October 1979 - September 1980). Bible Camp Kokanee Bend x(s.d. ) x(s.d. ) EPHEMEROPTERA Ephemerella tibialis 80 ( 96) 204(253) PLECOPTERA Pteronarcella badia 27 ( 56) 63( 61) Capniidae 174(144) 341(264) Chloroperlidae 38 ( 34) 104 ( 84) TRICHOPTERA Arctopsyche grandis 21 ( 31) 190(248) Glossosoma sp. 43(120) 234(385) DIPTERA Atherix variegata 3( 5) 7( 9) Simulium arcticum 196(449) 706(1,447) ■26- this category and are the only mayfly species which were found in greater numbers at the Kokanee Bend site. Stonefl ies A number of stonefly species do not show significantly different densities at the two main river sites. The families Capniidae and Chloroperl idae were found in larger numbers at the Kokanee Bend site. PtesionaAcoLta bacUa also occurred in consistently larger densities at the Kokanee Bend site. It is a shredder which is often found in depositional areas. Wood and large particulate matter were collected much. more fre- quently in our sample nets at Kokanee Bend and there are indications that course particulate organic matter was more abundant in the substrate in the regulated areas. This may be related to the fact that fluctuating flows can collect more debris from shoreline areas. After the spring runoff the river channel is removed from shoreline vegetation in un- regulated areas. Caddisflies Caddisfliesnoften show compositional changes in regulated areas (Henricson and Muller 1979). In the Flathead River, AtLctop&yche. QfiandU was much more abundant at the regulated site and the other hydropsychid species {S>ymphJXopi>yokp. showed a marked increase in density at the regulated site. It is an algal scraper and is probably more abundant due to increased periphytic growth in the regulated areas (Perry, in progress). The saddle cases it constructs and firmly affixes to rock surfaces would also make it more resistant to displacement or desiccation due to flow changes. Dipterans Most dipterans were collected in greater numbers at the Kokanee Bend site (e.g. Blephariceridae , Deuterophlebi idae, Antocka i>p. , Athnnlx va/iZdgcuta, Pn.otanydp., Smatimn ah.cXA.cum, and the Chironomidae) . The first two families have suckers which would enable them to hold on during velocity changes; they also are algal scrapers and periphyton was more abundant in regulated areas. AthnnXx, Pxotanydizn.a6 and many Chironomidae are burrowers which would not be as subject to catastrophic drift during the quick velocity changes due to regulation. S-unullam aA.ctic.um abundances may be related to larger amounts of the smaller size fractions of particulate organic matter in the seston at Kokanee Bend. ■27- Biomass Estimates The annual mean of mean monthly estimates of biomass (cc/m2) indicated that the total biomass of macroinvertebrates was not significantly different at the three sites. Kokanee Bend data showed slightly higher values on an annual basis (13.9) than the Bible Camp (11.9) and South Fork (11.9) data (Table 5, Figure 14). The Chironomidae and oligochaetes still dominated the fauna in the South Fork, but not by the overwhelming proportion that was characteristic of the data showing numbers per square meter. The biomass data from the Bible Camp and Kokanee Bend showed the same general trend on an annual basis as the numerical data. Biomass of mayflies was higher at the Bible Camp, biomass of stoneflies and caddisflies was higher at Kokanee Bend, and the Chironomidae and Other Invertebrate categories were not significantly different. Volumes of Other Invertebrates include other dipterans as well as non-insect inverte- brates. Numerical and volumetric data can be compared at the three sites by converting the actual mean monthly values to percent composition (Tables 6 and 7). In the South Fork, percent composition was much higher on a biomass than on a numerical basis for the Ephemeroptera , Plecoptera, Trichoptera, and Other Invertebrates. In comparisons of the other two sites (Appendices A & B), the mayflies showed both higher numbers and biomass at the control sites in every month. Both numbers and biomass of stoneflies were generally higher at Kokanee Bend (with the exception of December, June and September when numbers were higher at the Bible Camp). Numbers and biomass of caddisflies were also generally higher at Kokanee Bend (with the exception of the months of June and July when numbers and biomass were higher at the Bible Camp, and the months of August and September when volumes were higher at the Bible Camp). The Chironomidae showed higher numbers and volumes at Kokanee Bend in the months of October, November, April, June and August and at the Bible Camp in December, March, July and September. Ephemeroptera were the numerically dominant order at the Bible Camp in all months (Appendix A, Figures 16-27). Plecoptera were dominant numerically at the Kokanee Bend in October and November, then the Diptera dominated in December through June, and Ephemeroptera were dominant July through September. When biomass was considered, the dominant order in any month could change (Appendix B, Figures 28-38). To some extent, dominance volumetrical ly was a matter of chance, because if more large stoneflies or caddisflies were captured in the samples for a particular month, the balance was shifted. At the Bible Camp, mayflies were dominant volumetrically in all months but October when stoneflies were dominant, and November and September when caddisflies were dominant. The stoneflies were dominant volumetrically at Kokanee Bend, except in November, January and April when caddisflies were dominant, and June when large numbers of blackflies changed the dominant category to Other. ■28- Table 5. Biomass (cc/m2) (Kick + Circular Samples) Annual Mean of Monthly Means (October 1979 September 1980) Bible Camp n=9 x(s.d.) Kokanee Bend n=9 x(s.d.) South Fork _n=ll x(s.d.) Ephemeroptera Plecoptera Trichoptera Chironomidae Other Invertebrates TOTAL Percent Composition 3.9(1.2) 2.9(0.7) 1.9(0.8) 2.6(1.2) 4.8(1.5) 0.7(0.4) 2.5(1.0) 3.2(2.4) 0.2(0.2) 1.4(0.4) 1.3(0.2) 5.9(1.7) 1.7(0.6) 2.2(2.5) 3.6(1.3) 12.1(2.1) % 14.4(4.5) % 12.3(2.9) % Ephemeroptera 32.2 Plecoptera 21.5 Trichoptera 20.7 Chironomidae 11.6 Other Invertebrates 14.0 20.1 33.3 22.2 9.0 15.3 15.4 5.7 1.6 48.0 29.3 -29- tr UJ > 1 o 00 1 en QL 0) rr O) Q T— rr UJ 00 2 < < 09 5 UJ o h- X 1- O 0. UJ h- o f/> < -J u_ o «H h o H 3 "ii UJ Hi T i i >) • * JX CD co ro rz -o -a a. ro 1) •i— 5 X> 4-' t r: C o < +-> CD 00 o O C CD X UJ S*. •1 — CO CL-C UJ CD CD CX> _i Q. II m CD X 1) C_3 »* 03 OQ (/) S_ LO ro ro CO S- CQ ro £ O rjj 4^ CL O CO X3 i_ c cu ro 0J E CD -l-> CU fc ro S- CI >>-C UJ r^ CD -C +J n +-> S- C ru LU x. o F > .» oc •i— ro O 4- O , cu Li. ro 4-> CO 4J Q. 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E E O CU CU +-> > U U O i 3 +-> rO> CU CU s_ cu cu >> s- -Q CU cu -Q -Q S_ ra -»-> E c -Q F H rO 3 -£= 1 — oo cu ra o O) 1) 3 i- O •1 — CD >, 3 -l-J -^ +-> > U cn s. S_ >i c i — cn cl o o o CU rO CD r--Lr>oLnoc\jLr)Ovjoocx5 QJ O roc\io|fi^HO|ou5n<^o 03 s- ai +-> a_ o .c u c\joo«3-ooocNjooc\jcr> o o o •— l i— l i— I CO i— ioowo 03 S- QJ 4-> Q_ O o ai l~~- c o o QJ I— o o oo QJ O +J u o IO 3Ti — 3 S- O -i- CH !. i. >, ro tu ia a id QJ i- oj -O -t-> E >> =3 -t-> i— CD Q. a» tlls:<2:to, Symphitoptychz oilan.1, SymphJjtop&yzhz zozkoAzllZ, Bn.achyczntnw*> &p. , and kthznix vanZzgcUa) . This was apparently due to the fact that the heat accumulation was greater during the summer and early fall months in unregulated areas of the river. Elliott (1972) found that the time between oviposition and hatching and the length of the hatching period may be greatly extended by low summer temperatures. The reverse situation appears to have occurred in species which were growing later in the fall when temperatures were warmer in the partially regulated areas. Small capniid and chloroperlid stoneflies reached their maximum abundance one month later at the Bible Camp. These observations need to be further substantiated by emergence data and head capsule measurements. Sweeney and Vannote (1978) found that small adult aquatic insects with reduced fecundity resulted when temperatures were either warmed or cooled with respect to more optimal thermal conditions. Temperature apparently affected adult size by altering the larval growth rate and the timing and rate of adult tissue development. Monitoring adult size and fecundity of aquatic insects was suggested as a tool for assessing the impact of sublethal alteration of natural temperature patterns. Warming the seasonal cycles of a river by 2° to 3° C might eliminate species by affecting body size and fecundity. This should be considered when planning prolonged winter discharges from Hungry Horse Dam. It is possible that sustained winter discharges ■35- 400 - 300- us a. z> *- < a. UJ a. UJ t- < a NORTH FORK AT CANYON CREEK FLATHEAD RIVER AT COLUMBIA FALLS SOUTH FORK AT HUNGRY HORSE |x 200 w «/) Q UJ UJ DC (D UJ G 100- i N i D T* F T M M i A Figure 15. Degree days (mean daily temperatures) summed by the month for control (North Fork), partially regulated (Columbia Falls), and regulated (South Fork) areas of the Flathead River for the 1980 water year. ■36- from Hungry Horse Dam could increase the winter head load in the river enough to eliminate certain species of stoneflies. During the winter of 1981, a number of species emerged earlier in the partially regulated areas of the river (starting in January). This was probably due to the combined effects of sustained winter discharge and warmer weather conditions. In a colder winter, higher winter water temperatures may induce emergence into lethal ly cold air or during periods when mating was impossible. The raising of river temperatures may disrupt mating behavior in some species by widening any time lag between emergence of males and females (Nebeker 1971a). Coutant (1967) has shown that a slight temperature increase (1° C) will cause hydropsychid caddisflies to emerge two weeks earlier down- stream from the Hanford (Washington) reactors than in upstream areas. In experimental situations, it has been demonstrated that exposure of aquatic insect larvae to artificially high temperatures and stable flow conditions can cause advances in the onset of adult emergence of up to five months in some species (Nebeker 1971b). Stoneflies have been almost eliminated from the Kootenai River (Montana) since impoundment (Huston et al. 1980). This may be due in part to warmer winter temperatures. However, in the Kootenai River, winter discharges are generally continuous (no weekend shutdown) for a period of several months, which allows a greater heat accumulation. It is probable that night and weekend shutdowns at Hungry Horse Dam will prevent deleteriously high heat accumulations, although higher daily maximum temperatures than in control areas may eliminate certain species. Preliminary data indicates that stoneflies are a food source for cutthroat trout during the winter in the partially regulated area of the Flathead River. The impact of discharge changes on what appears to be an important food resource should be considered in management decisions. RECOMMENDATIONS Selective Withdrawal System There is no question that a selective withdrawal system would increase species diversity and benefit invertebrate populations in the South Fork. However, due to the fact that the totally regulated section in the Flathead River is so short (8 km) and that the construction of a reregulatory dam would inundate an additional five km of the South Fork, considerations of a selective withdrawal system should be made with regard to the partially regulated area of the river rather than the South Fork. Presently, the partially regulated area of the Flathead River supports a diverse fauna due to the ameliorative effects of waters from the free- flowing North and Middle Forks. Differences in invertebrate composition between the Bible Camp (control) and Kokanee Bend (partially regulated) sampling sites may be due as much to changes in the food regime as to ■37- changes in temperature per se. A selective withdrawal system would introduce more plankton from the reservoir. Carbon and ATP profiles from the forebay of Hungry Horse Reservoir indicate that there are greater amounts of seston in the epilimnion than in the hypolimnion (personal communication, Jack Stanford, Director, University of Montana Biological Station). Warmer summer temperatures may further increase the growth of periphyton during the summer or early fall in the partially regulated area. The flushing effects due to changing discharges, which remove the finer organic carbon particles from the substrate and introduce coarse particulate organic matter from shoreline areas, would not be changed. Changes in the invertebrate composition could be expected. Most mayfly species, which are unable to tolerate flow fluctuations and the loss of the fine detritus in the substrate, would not come back. Other mayfly species such as Epkm&ioJULa. iyiojimi^ and BaztA,t> PU.caadcutiii> which can tolerate the flow fluctuations and feed on the increased periphyton growths would be expected to increase. These species are present in very large numbers downstream from Libby Dam, which is equipped with a selective withdrawal system. Caddisfly composition may change. Glo6&o6oma i>p., which is already greatly increased in the partially regulated areas, would be expected to increase further due to increased growths of periphyton. The species of hydropsychids, which are currently more abundant in control areas, may increase due to the increased export of seston from the reservoir. It is not known how they would compete with Asictoptyckd, which is presently the dominant species of hydropsychid at Kokanee Bend. AticXop&ychz is not present in the Kootenai River, although it is present in the Fisher River (a tributary of the Kootenai), which has a very similar total annual heat budget. The winter stoneflies, which are the unique resource characteristic of the partially regulated Flathead River, may be adversely affected due to increased periphyton growths and altered temperatures. The factors which affect their distri- bution in the Flathead and Kootenai Rivers are not completely understood. They are more abundant in the partially regulated area than at the control site in the Flathead River, while they have almost been eliminated from the Kootenai River. Their elimination in the Kootenai is probably related to the fall decrease in percent saturation of oxygen, due to heavy utili- zation by both living and scenescent plankton in the reservoir discharges and by periphyton on the river substrate, and to the higher winter temperatures due to sustained discharges. The Flathead River is not as productive as the Kootenai (Perry, in progress), so the effects on the stoneflies may not be as marked in the Flathead. It is not fully understood how much the heavy periphyton growths in the Kootenai River are related to the warmer fall temperatures imposed by the selective withdrawal system as opposed to the generally higher nutrient load in the Kootenai system. Periphyton in the partially regulated Flathead River would still be scoured during spring runoff and light penetration would be reduced during periods when turbidity is high in the North and Middle Forks. However, marked increased in the growth of periphyton in the partially regulated Flathead River would be expected to alter insect •38- composition and possibly interfere with the flow of water to the hyporheic zone. The changes which would be expected from the installation of a selective withdrawal system on Hungry Horse Dam cannot be fully predicted from the existing data base. Experimental tests which would refine our ability to make predictions and management decisions have not been done. These tests would involve rearing selected species under different temperature and food regimes in experimental streams and environmental chambers to determine their environmental requirements and is beyond the scope of the present project. Until the factors which control the distributions of invertebrates in the Flathead River have been more completely delineated, the construction of a selective withdrawal system is not presently recommended. CONCLUSIONS Annual means of numbers (no/m2) and biomass (cc/m2) data indicate that densities of zoobenthos are higher in the South Fork than at the control and partially regulated sites, but the overall biomass is not significantly different at the three sites. Species diversity is much reduced in the South Fork, but Shannon indices showed no significant differences between the control and partially regulated sites. The faunal composition was markedly changed (consisting primarily of midges and ol igochaetes) and the number of species was decreased in the South Fork, mainly due to the extreme modification of the tempera- ture regime. Due to the addition of water from the North and Middle Forks of the Flathead River, the changes were much less marked in the partially regulated areas of the river. This can be attributed to factors such as temperature modification, the flushing and redeposition of sediments which occurs during spring runoff, the import of particulate organic carbon and drifting insects from upstream areas, etc. However, there were compositional changes in the partially regulated portion of the river. Mayflies were far more abundant in the control area, while stoneflies and dipterans showed increased abundances in the partially regulated area. The composition of caddisflies was markedly different at the two sites due to differences in periphyton growth and particulate organic carbon particle sizes. The timing of events in the life cycle of a number of species was different at the two sites due to seasonal temperature differences. The ameliorative effects of the North and Middle Forks are limited during seasons of lower flows from natural areas. Major changes in the discharge regime from Hungry Horse Dam during certain times of the year could substantially alter the composition of invertebrates in the main stem river. Marked increases in discharge during certain seasons (e.g. during the winter) could cause species extinctions. The partially regulated section of the Flathead River is a rather unique area, which under the current discharge regime, seems to combine advantages of both ■39- free flowing rivers and regulation. This area currently supports a diverse fauna despite perturbations, but is not resistant to species deletion (see Pimm 1979). Until more information is available on what environmental factors are important for the maintenance of a habitat suitable for specific groups of species, caution should be exercised in altering discharge regimes. -40- LITERATURE CITED Coutant, C.C. 1967. Effect of temperature on the development rate of bottom organisms, p. 11-12 j_n: Biological effects of thermal discharges, U.S.A. E.C. (Atomic Energy Comm.) Pac. N.W. Labs, Div. Biol. Med. Ann. Rep. Cummins, K.W. 1966. A review of stream ecology with special emphasis on organism-substrate relationships. Spec. Publ. Pymaturing Lab. Field Biol. 4:2-51. de March, Brigitte, G.E. 1976. Spatial and temporal patterns in macro- benthic stream diversity. J. Fish. Res. Bd. Can. 33:1261-1270. Elliott, J.M. 1972. Effect of temperature on time of hatching in BaeXci nhodcivu. (Ephemeroptera: Baetidae) Oecologia 9:47-51. Fisher, S.G. and A. LaVoy. 1972. Differences in littoral fauna due to fluctuating water levels below a hydroelectric dam. J. Fish. Res. Bd. Can. 29:1472-1476. Gauch, H.G. , Jr. 1977. ORDIFLEX a flexible computer program for four ordination techniques: weighted averages, polar ordination, principal components analysis, and recriprocal averaging. Release B. Cornell Ecology Programs Series. Cornell Univ. Ithaca, NY 180 pp. Hauer, F.R. 1980. Ecological studies of Trichoptera in the Flathead River, Montana. PhD. Dissertation, N. Texas State Univ., Denton, Texas. Henricson, J. and K. MUller. 1979. Stream regulation in Sweden with some examples from central Europe, pp. 183-199 j_n: Ward, J.V. and J. A. Stanford (eds.). The Ecology of Regulated Streams. Plenum Press, NY. Hill, M.O. 1979. DECORANA - A FORTRAN program for detrended correspondence analysis and reciprocal averaging. Cornell Ecology Programs Series. Cornell Univ., Ithaca, NY. 52 pp. Hilsenhoff, W.L. 1971. Changes in the downstream insect and amphipod fauna caused by an impoundment with a hypolimnial drain. Ann. Entomol . Soc. Amer. 64:743-746. Hoffman, E.C. and R.V. Ki Iambi. 1971. Environmental changes produced by cold water outlets from three Arkansas reservoirs. Water Resource Research Center Publ. No. 5, Univ. Arkansas, Fayetteville, Ark. Hulbert, S.H. 1971. The nonconcept of species diversity: a critique and alternative parameters. Ecology 52:577-586. Lehmkuhl , D.M. 1972. Change in thermal regime as a cause of reduction of benthic fauna downstream of a reservoir. J. Fish. Res. Bd. Can. 29:1329-1332. ■41- Lehmkuhl , D.M. 1979. Environmental disturbance and life histories: principles and examples. J. Fish. Res. Bd. Can. 36:329-334. Margalef, D.R. 1957. Information theory in ecology. Gen. Syst. 3:36-71. May, F. , S. Appert and J. Huston. 1980. Annual Progress Report, Kootenai River Investigations. Mt. Dept. of Fish, Wildl. Parks. 26 pp. Minshall, G. Wayne and J.N. Minshall. 1977. Macrodistribution of benthic invertebrates in a Rocky Mountain (U.S.A.) stream. Hydrobiologia 55:231-249. Moore, P.D. 1975. Changes in species diversity. Nature 254:104-105. Nebeker, A.V. 1971a. Effects of temperature at different altitudes on the emergence of aquatic insects from a single stream. J. Kansas Entomol. Soc. 44(l):26-35. Nebeker, A.V. 1971b. Effect of high winter water temperatures on adult emergence of aquatic insects. Water Res. 5:777-783. Pearson, Wm. D. , R.H. Kramer and the late D.R. Franklin. 1968. Macro- invertebrates in the Green River below Flaming Gorge Dam, 1964-65 and 1967. Proc. Utah Acad. Sci . , Arts Lett. 45(1) : 148-167. Perry, S.A. (In progress). Comparative ecology of benthic communities in free-flowing and regulated areas of the Flathead and Kootenai River, Montana. PhD Dissertation. North Texas State Univ., Denton, Texas.. Pimm, S.L. 1979. Complexity and stability: another look at MacArthur's original hypothesis. Oi kos 33:351-357. Spence, J. A. and H.B.N. Hynes. 1971. Differences in benthos upstream and downstream of an impoundment. J. Fish. Res. Bd. Can. 28:35-43. Stanford, J. A. 1975. Ecological studies of Plecoptera in the Upper Flathead Rivers, Montana. PhD. Dissertation, Univ. of Utah. Salt Lake City, 241 pp. Stanford, J. A. and A.R. Gaufin. 1974. Hyporheic communities of two Montana Rivers. Science 185:700-702. Sweeney, B.W. and R.L. Vannote. 1978. Size variation and the distributions of hemimetabolous aquatic insects: two thermal equilibrium hypotheses. Science 200:444-446. Ward, James V. 1974. A temperature stressed stream ecosystem below a hypolimnial release mountain reservoir. Arch. Hydrobiol. 74:247-275. Ward, James V. 1976. Effects of thermal constancy and seasonal temperature displacement on community structure of stream macroinvertebrates. In: Thermal Ecology II, G.W. Esch and R.W. McFarlane (eds.), ERDA Symp. Series (C0NF-750425) , pp. 302-307. -42- Ward, J.V. and J. A. Stanford (eds.). 1979. The Ecology of Regulated Streams. Plenum Press. NY 398 pp. Williams, D.D. 1980. Some relationships between stream benthos and substrate heterogeneity. Limnol. Oceonogr. 25(1) : 166-172. Young, W.D., D.H. Kent and B.G. Whiteside. 1976. The influence of a deep storage reservoir on the species diversity of benthic macroinvertebrate communities of the Guadalupe River, Texas. Tex. J. Scie. 27:213-224. -43- APPENDIX A Figures 16 - 27 Mean number of invertebrates per square meter, October, 1979 through September, 1980. E = Ephemeroptera P = Plecoptera T = Trichoptera Ch = Chironomidae 0D = Other Diptera 01 = Other Invertebrates Bars represent monthly means (kick and circular samples combined); I represents standard deviations. O 3 o 01 0> o o O \ o o o o o o w o o o r^rr o o o O o o CM uj / on o o x2 a a o z i m O UJ UJ Z »- < o UJ Q O < o UJ _i CO UJ UD en ■1- E o CM CO CO o o Q .a E a> > o iY H DC o I- I a. O C/) yj ^ H M o o s o o o CO o o o CM o o I HI X. CD « LU LU Z ■" < o a. * tSJ < O LU _J CD QQ UJ .lu / ON X o o o 1) 5- -2- 11 O o UJ Q a O z: UJ I CQ o UJ z 1- < o 00 a. XL QJ S- UJ Q O X -2= o < o UJ _l QQ CQ m Ci -3- r~ CO O) If) CO II II IX Q CO I" o CO 0) c a o X Q a. UJ D Z UJ s 1 UJ 1 1 Z < 1 1 1 o I 1 1 1 i ■a m a. E nj CO O O O co w I o o o ° * cc I o U. X I- o CO UJ CT) 1) < u UJ _i CD CQ 2uj / on x -4- HI I Q O o CO CD 03 -Q o o o w o o o t 1 r ui / "ON X X o uu O I o in UJ a z UJ CD UJ UJ Z < o o O-J < o -o 0) UJ Q. _l E GQ CD (/» m «^ o z a o o -5- > CO *• (O o> *Z. m C UJ m O O o °h UJ H 4 H o O Lur 0) DC LU DQ LU > O z u H 41 yj Q- < o _i CQ m cc o LL X I- o CX> C\J CD en LU Q Z LU m LU LU z < O ID CM o CM ,LU / 0 0 o ssvwoia i in -2- |2 4 "H a. < o in O) m 00 LU UJ O UJ Q «H DC o J- = o o °° CO cu cr. H °ll o HI H CD LU UJ 2 < o 04 o CM m o gUJ / oo | SSVIAI0I8 -3- o 00 0J a < z < -3 ssvwoia •4- o 00 O) a. < o _j m DO < a: m ID -H o O LJJ J O u_ X H o a I 4 Q O Z Hi GO o Ull- i LU UJ Z * i_ I o CM I o cs I 1 O 1 I jUi/ oo i ssvwoia CVI CO OJ 5- -5- o o 00 o 4 Hi H ■H < O UJ m m i o ac < | ^uj/oo ) ssvwoia -6- UJ O 00 0) °H •H Q. < O UJ -J m m a. < u to o UJ H i ■I DC O I I- O en s- =5 CO o iUU H Q z m UJ UJ z < o in CM o CN u-) | 7LU / 00 ) O ssvwoia T m -7- o to o ili\ ■H a. < O LU _l QQ CD O CD m HI «8 o HI •H DC O Li. X Z> o CO LT) CD O LU D Z Ui OQ Ui UJ z < o CM I O CM | zui / 00 o m ssvinois -8- A3 O o CD "H ■H < o OQ OQ to *■< o (J H w H o LL X O 1X3 I) 5- rs to o UJ 4 a z LU CD UJ LU Z < o O 1^ cm | 3iu/ 00 o ssvwoia -9- 'II to o "H { 41 o 00 0) O < O oh U UJl •H a < o uj _j m m 3 ( 'II Q Z UJ 00 CO o »H UJ UJ a J z * ^ -h H O ■ 1 IO CM 1 o CM ■ 1 IO 1 O i 10 O 3 o CO s- zm/ oo ) SSVWOIfl -10- (X) o O CD UJ yj »- a. 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O cc s- E •«- E -r- -a co HI 3 0)r- 3 fl >,t- zz.\— so— izrcD. -4- JANUARY (1-15-80) EPHEMEROPTERA Baetidae Baetis tricaudatus Baetis haqeni Heptageni idae Rhithrogena hageni Rhithrogena robusta Epeorus sp. Cinygmula sp. small Heptageni idae Ephemerel lidae Ephemerel la doddsi Ephemerel la inermis Ephemerel la spinifera Leptophlebiidae Paraleptophlebia heteronea PLECOPTERA Pteronarcidae Pteronarcys californica Pteronarcel la badia Taeniopterygidae Taenionema pacificum Nemouridae Zaoada cinctipes Zapada columbiana Prostoia besametsa Capni idae Utacapnia sp. Capnia sp. Capnia sp. A small Capni idae Perl idae Classenia sabulosa Hesperaperla pacifica small Perl idae Perlodidae Isogenoides colubrinus Megarcys watertoni Diura knowltoni Kogotus modestus Isoperla fulva Isoperla patricia small Perlodidae Kokanee Bend Kick n=8 x (s.d.) 202 ( 254) 6( 11) 377 ( 401) 0.9( 2) 3( 8) 135 ( 166) 7( 11) 63( 97) 0.3( 1) 4( 10) 10( 25) 38 ( 43) 110( 89) 4( 5) 1( 1) 21( 16) 30 ( 37) 2( 4) 59( 121) 5( 5) 1( 2) 3( 4) 0.9( 2) 2( 4) 35 ( 41) 5( 13) 0.9( 2) South Fork Kick n=8 x (s.d.) 378(392) 0.3(0.9) 13( 19) 7( 7) 5( 9) 4( 4) 30 ( 33' 27 ( 28) 0.3(0.9) ■5- JANUARY (continued) Kokanee Bend South Fork Kick Kick n=8 n=8 x (s.d.) x (s.d.) Chi proper! idae Sweltsa coloradensis 4( 5) K 2) Trisnaka sp. 34 ( 41) small Chloroperlidae 57( 78) TRICHOPTERA Hydropsychidae Arctopsyche grandis 151(219) Symphitopsyche oslari 3( 6) Symphitopsyche cockerel li K 2) Hydropsyche occidental is 3( 6) small Hydropsychidae 23( 52) Rhyacophi 1 idae Rhyacophila angel ita 2( 4) Rhyacophi la bifila 2 2 0.3( 1) Rhyacophila coloradensis Glossosomatidae Glossosoma sp. 242(324) ._ _ Brachycentridae Brachycentrus sp. 3( 6) COLEOPTERA Elmidae Optioservus quadrimaculatus 2( 4) DIPTERA Blephariceridae 0.3( 1) Tipul idae Hexatoma sp. 4( 5) Antocha sp. 0.3( 1) Simul i idae Simul ium sp. 13( 24) Chironomidae Chironomidae larvae 895(983) 10,397(9,253) Chironomidae pupae 0.3( 1) Chironomidae adults 4( 5) Tanyderidae Protanyderus sp. 0.3( 1) Athericidae Atherix variegata 7( 10) OTHER INVERTEBRATES Turbel laria 3( 8) 330(206) Nematoda 2( 4) 12( 13) 01 igochaeta Lumbriculidae 6( 10) 446(382) Naididae 26 ( 50) 59( 69) Hydracarina 14 ( 38) 183(264) -6- FEBRUARY (2-11-80) Kokanee Bend South Fork Kick Circular n=4 n=4 x(s.d. ) x(s.d. ) Kick Circular n=4 n=4 x(s.d. ) x(s .d . ) COLL EM BO LA EPHEMEROPTERA Siphlonuridae Ameletus sparsatus small Siphlonuridae Baetidae Baetis tricaudatus Baetis hageni Heptageni idae Rhithrogena hageni Epeorus sp. Cinygmula sp. Ephemerel 1 idae Ephemerella doddsi Ephemerel la inermis Ephemerella sp. Leptophlebi idae Paraleptophlebia heteronea PLECOPTERA Pteronarcidae Pteronarcys californica 6( 12) 76( 63) 0.9( 2) 175(150) 176(291) 2( 2) 23( 25) Pteronarcel la badia 6( 7) Taeniopterygidae Taenionema pacificum 275(183) Nemouridae Zapada cinctipes 8( 11) Zapada columbiana Prostoia besametsa 6( 7) small Nemouridae 6( 12) Capni idae Utacapnia sp. 110( 81) Capni a sp. small Capni idae 461(138) Perl idae Classenia sabulosa 0.9( 2) Hesperaperla pacifica Doroneuria theodora Perlodidae Skwala parallela Diura knowltoni 2( 2) Isoperla fulva 3( 2) 6 12) 24 ; 20) 248 ,228) 383 ;378) 479 [555) 7 ; 8) 54 ; 44) 2 [ 3) 2 3) 68 ; 84) 96 ; 68) 2 I 2) 13 I 16) 6 ' 12) 19 ; 25) 259 [243) 17 ' 31) 14 ! 26) 0.9 I 2) 0.91 2) 351 ' 50) 362(101) 191( 32) 33( 62) 1( 2) K 2) 17( 35) 22 ( 26) 10( 16) 2( 5) 56( 70) 6( 12) K 2) 9(" 8) 2( 2) K 2) 2( 2) 6( 5) 9( 18) 9( ID •7- FEBRUARY (continued) Kokanee Bend South Fork Kick Circular Kick Circular n=4 h=4 n=4 n=4 x(s.d.) x(s.d.) x(s.d.) x(s.d.) Chloroperlidae Sweltsa coloradensis 2( 3) 7(10) Trisnaka sp. 0.9( 2) 53( 65) small Chloroperlidae 41( 44) 110( 56) 7( 12) TRICHOPTERA Hydropsychidae Arctopsyche grandis 4( 3) 147(212) Symphitopsyche oslari 4( 8) Symphitopsyche cockerelli 2( 5) Hydropsyche occidentals 2( 2) small Hydropsychidae 12( 24) Rhyacophilidae Rhyacophila coloradensis 1( 2) Rhyacophila verrula 9( 16) 1( 2) small Rhyacophila sp. 2( 3) 13( 15) Glossosomatidae Glossosoma sp. 70( 63) 236(188) Hydroptil idae Ochrotrichia sp. 0.9( 2) Brachycentridae Brachycentrus sp. 0.9( 2) DIPTERA Simuliidae Simul ium sp. 29( 21) 24( 48) 68(137) K 2) Chironomidae Chironomidae larvae 1,220(764) 1,417(1,273) 10,081(8,250) 7,541(2,671) Chironomidae pupae 2( 5) Chironomidae adults 0.9( 2) Athericidae Atherix varietaga 2( 3) 2( 2) Empididae Hemerodromia sp. 6( 12) OTHER INVERTEBRATES Turbel laria 5( 7) 402 ( 30) 72( 17) Nematoda 19( 38) 6( 12) 01 igochaeta Lumbriculidae 3( 4) 3( 4) 258(121) 131(131) Naididae 15( 14) 38 ( 57) 102(204) 36( 31) Hydracarina 36( 31) 354(342) 36 ( 72) Hirudinea Piscicola 2( 3) -8- o CO I co cr: 5_ 03 1 — • =3 =5 O oo -u: TJ U IX -* -o r- II CO ^ e -— IX 03 -— " « =3 «d" "O U II i- c w I X -^ -o o ro • •r- II co v: e -— IX CVI 3781 co LD cn II 1 1 1 1 II — - 1 1 1 1 i i c\j i i i i i i «3- iiit I tO C\J CVI 1 CO 1 1 — 1 1 CO 1 1 <^- 1 m CVI LT> to cvi co 1 LO 1 | | 1 1 I— 1 ^J- 1 1 — cn 1 CVI CO 1 i i loin ♦ CO CVI o cn to » i LO to CO to CVI CO CO I CO CVI I I r-H I ■ r-^ co to ^d- i to i — i h-. «* «* CVI 1 — 1 CO o co • i i LO r-H 1 I— 1 1 .— 1 , — [III 1 1 1 — -- i v 1 ^-^ ^— ^ ^-^ 1 1 1 <3- ' r—> 1 ■* CTi 1 o Cn CO ' 1 ' <* to 1 — 1 CVI o CO 1 — 1 CVI ■—1 CO CVI LO O i — i < 1 LO co cn i — I i — I to CVI i— t CTi CO Cn ^t- <* CO CVI ' • 1 CVI i i i N — •"* ^ > »«. <" to 1 *» — -* s — .*> — ' 1 1 1 cn to <— i LO r-H <* CTv 1 1— 1 r— 1 LD 1 1 1 CO CO to co to .— I i to i-^ CO 1 1 » CVI CVI i— 1 r . — I r^ I — 1 C J to *- S^^^^ N *—^*^^ LD »* *• S * — w — ■. 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' I 1 CO CO oo r-^ co ■=d- ■=3- o> cxi OO 0O O CO d <— « CXJ lo ^r co LO CTIUO ro CXJ CXI I CO CXJ I <3- CXJ oo CXJ CTv CTi O ai 03 T3 03 03 E X QJ •i- 03 s- -a aj >i- -c -a 4-> -r- 03 QJ a: UJ 03 i — 4-> =3 CD S- d) U UJ 03 03 03 t- "O i— "O -*= t- t- >— o o oi -a a cu 4J o e •>— re £103 013(0 1. s- e -r- _i s: -a =s a» i— >> I— ^: o =c 16- MAY (5-12-80) South Fork Kick n=4 x(s.d.) EPHEMEROPTERA Siphlonuridae small Siphlonuridae Baetidae Baetis tricaudatus Baetis bicaudatus Heptageniidae Cinygmula sp. Rhithrogena robusta Epeorus grandis Ephemerell idae Ephemerella doddsi Ephemerella flavilinea Ephemerella heterocaudata Ephemerella tibialis PLECOPTERA Perlodidae Diura knowltoni Chloroperl idae Sweltsa coloradensis Pteronarcella badia small Chloroperl idae Nemouridae Zapada columbiana Capni idae Capnia sp. Isocapnia sp. TRICHOPTERA Rhyacophi lidae Rhyacophila bifila Rhyacophi la verrula Rhyacophila vagrita small Rhyacophila DIPTERA Chironomidae Chironomidae Chironomidae Chironomidae Simul lidae sp. larvae pupae adults 12( 14) 288( 98) 326 ( 174) 114( 133) 0.9( 2) 0.9( 2) 38( 47) 0.9( 2) 0.9( 2) 6( 12) 41 5 13 6 59 6 0.9 0.9 6 0.9 6 1,611 252 35 43) 4) 13) 12) 41) 12) 2) 2) 4) 2) 12) 3,341) 224) 39) Simul i urn 494(409) •17- MAY (continued) South Fork Kick n=4 x(s.d.) OTHER INVERTEBRATES Turbellaria 302(353) Lumbriculidae 417(371) Naididae 132(233) Hydracarina 186(248) -18- 5- o -M 3 o OO a s- u n ■o c: CD CQ CD CD c 03 o o «* • •i- II 00 IX 03 '— O II s~ c: oo CJ i oo i 03 C_> O) JO CQ •r- II 00 v: c: -— i x S- 03 --- 3 "=j- -a U II <*- £Z 00 I > ^ -o ■r- II 00 I X CVI O 1 = — 1 1 1 en 111*3- Cvl 1 CM CM 1 evi 1 r— 1 1 II 1 t | i oo n i i CM i i i — - 1 1 1 o LO ■ — I 1 1 i — i . — I 1 1 II 1 ID 1 II I CsJ LO CO Cn ft r& CO O.J "5* 1 OO . — 1 1 1 1 1 1 1 — - — 1 1 1 1 1 1 1 — 1 CXI 1 I 1 1 1 cn < cm n oo con cm lo cm cm cm cn cn i o n oo i *3- lo i m^t ro ix> I < — I i—l It — I I LO i — I CO LO I i— i o cn I >3- CO i lo n cc i— i ■— i oo O *X> uO N LO WrOrH ^- ■—I CM «3- i — IN i—l LO CO IX) LT) CM OT rn Lfi CTl r-- c\j OO ,— I CM (X) OO OO N oo >3- iX) en cm oo CO CM 00 <3" cm i— i cn LO r-l CM rororoN o n ■—I oo OO IX) OO CTl CM CM 0O CTl CM CO LO OO «=*■ O CO IX) LO IX) CM LO LO 00 I "vt" I I CT. 03 03 T3 CD n3 00 ro 00 •i- +-> 13 T3 3 00 C 00 +-> t- 4-> =3 CD =5 rO S_ ro +-> CDX3 00 13 -a TD Q- 03 O S- C 3 "O ■.- 00 x: S_ 03 o r0 3 c =C a> Q-r— o ro ai c: a> ro fO q; fo oo x: •r— U CT) O 03 C C UJ "O O. s- •r— 03 CD "O CD CD l— -r- 00 -r- +-> JQ x: ■ — •.- cr cr> D_ S- 3 OO a •<- o o O =3 +J O) 00 00 oo o c: S- S- CC £Z ai i— fO • i — •r— •t- XJ CD x: x: UJ O 1 — 1 — -a +J ■M +j 3 cr +-> -M si <— CD n3 •r- CU ai CD CD rt3 •1 '1 UJ jC E E 4-» n3 rO (C 00 +-> x: .c n= o. >=C 00 CU CQ CO CQ Q_ Q. a: ai D_ -r- ro CD uj oo CQ nz CX. 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