ML19224C987

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Preconstruction Ecological Studies for Site, Suppl to May 1978 Final Rept
ML19224C987
Person / Time
Site: 05000514, 05000515
Issue date: 02/28/1979
From:
PORTLAND GENERAL ELECTRIC CO.
To:
Shared Package
ML19224C985 List:
References
NUDOCS 7907100414
Download: ML19224C987 (107)


Text

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j PRE-CONSTRUCTION ECOLOGICAL STlrS

! FOR THE PEBBLE SPRINGS SITE i

l SUPPLEMENT to May 1978 Final Report Prepared for PORTLAND GENERAL ELECTRIC COMPANY 121 S.W. Salmon Portland, Oregon 97201 By Beak Consultants Incorporated 317 S.W. Alder Portland, Oregon 97204 l

February 1979 i60716c w y 325 097 o

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! TABLE OF CONTENTS L

Page FOREWORD i ii

' ACKNOWLEDGMENTS iii i

SUMMARY

1 EFCTION 1. FlaHERIES 1

A. INTRODUCTION 1

B. LOCATION OF STUDY AREA AND SAMPLING STATIONS 4

C. METHODOLOGY

1. Hydroacoustic 4
a. Equipment and Calibration 4 Sampling 7 b.
c. Estimates of Fish Density 9 ri . Data Analysis 10
2. Gill Nets 10 11 D. RESULTS
1. Gillnetting 11
2. Hydroacoustic Studies 19 E. DISCUSSION 19 21 CONCLUSION SECTION II. LONG-BILLED CURLEWS 23 A. INTRODUCTION 23 24 B. METHODS RESULTS AND DISCUSSION 26 C.

34 SECTION III. RAPTORS l

34 A. INTRODUCTION 34 B. METHODS RESULTS AND DISCUSSION 35 C.

38 REFERENCES APPENDICES A, B, C, D, E, F, AND G

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FOREWORD During the 1976-77 water year the Pacific Northwest experienced its worst ,

drought in over 100 years. In response to this drought various agencies implemented l

laoNyramv:hichtransported2.8millionjuvenilesalmonidsfromthelowerSnake l

River to below Bonneville Dam.

Fortland General Electric felt that this action may have influenced the resu" ts of the hydroacoustic survey performed during this period at the Pebble Springs site (BEAK 1973).

In addition, the drought significantly af fected the vegetative growth at the plant site which nay, in turn, have affected the Long-b lied Curlew usage.

Therefore, in February 1978 PGE retained BEAK Consultants Incorporated to continue the monitoring program begun in 1977 on salmonid smnits, curlews and raptors. This document reports the results of those studies.

Data collection, analysis, and presentation were the responsibilities of the following personnel.

Project Staff Project Responsibility J. K. Dueker Project Manager E. L. Mulvihill Administration M. T. Hill Aquatic Field Supervisor T. W. Haislip Terrestrial Field Supervisor B. R. Eddy, D. E, Johnson Hydroacoustic Studies J. B. Glad, K. B. Kaster Vegetation Studies J. A. Roppe Avifaunal Studies Project Supervision WE Z-

// J. K. Dueker F 'i ce Presi dent ,. ,

Project Approval

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/ E. L. Mulvibill i ,

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l ACKNOWLEDG'iENTS l Beak Cor,sultants Incorporated expresses thanks to the staff of Portland General l

l Electric Company for its assistance on this study. Dr. S. C. Katkansky and

' Mr. R. Klein provided assistance in the review and preparation of this report.

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BEAK--- -- --- - ---

I

SUMMARY

I The results of the supplemental pre-construction ecological studies at the

, Pebble Springs site are summarized below.

I

> I. Fisheries A supplemental fish study was performed with hydroacoustic techniques con-current with gill net sampling from April,1978 through July,1978. The study location was approximately three miles up the Columbia River from Arlington, Oregon.

Data from the hydroacoustic and gill net studies indicate that very low numbers of salnonid smolts were present in the vicinity of the proposed Pebble Spring: in-take during the interval April 17 through July 25, 1978. These findings are con-sistent with the data obtained during 1977 (8EAK 1978).

II. Long-billed Curlews Data from the 1978 studies indicate that curlew populations and the number of territorial pairs were generally lower in 1978. Also, the distribution of observed curlews shifted from the previous studies.

The reduced population levels and number of territorial pairs observed on the Pebble Springs site in 1978 may be a result of the low reproductive success in 1977.

III. Raptors Common Raven, Ferruginous Hawk, and Swainson's Hawk were the most abundant raptor (or raptor-like) species in the study area during 1978. Four species, the Prairie Falcon, Rough-legged Hawk, Short-eared Owl, and Burrowing Owl, that were observed during 1977 were not recorded in 1978. A reduction in sampling intensity (i .e., one day site visit) during 1978 may have been a factor that contributed to the lower number of species observed.

111 325 10:

I. FISHERIES l A. INTRODUCTION This report presents supplemertary data on salmonid smoit densities in the

' vicinity of the proposed Pebble Springs cooling water intake. A previous study con-ducted by Beak Consultants Incorporated during the interval April, 1977 through March,1978 indicated that the intake site was not an area of high fish density (BEAK 1978). However, the data obtained during that study may not have been repre-sentative of normal conditions due to extremely low flow conditions in the Columbia River and large reductions in the normal smolt numbers due to the Army Corps of Engineers 1977 smolt transport program. To provide smolt density estinates for more representative conditions, PGE retained BEAK to continue the smcit sampling program for April 17, 1978 through July 25, 1978. Modifications were made in the hydroacoustic sampling technique to allow more precise estimation of relative smolt densities in the near-surface waters. This report contains a description of the sampling modifications (Section C) and results of the sampling program (Sections D, E, and Appendices A and B).

B. LOCATION OF STUDY AREA AND SAMPLING STATIONS The Pebble Springs aquatic study site is located along the Oregon shore of the Columbia River (River Mile 244 to 248) approximately three miles upriver from Arlington, Oregon (Figure 1). It is approximately 28 miles above John Day Dar end about 48 miles downriver from McNary Dam. The proposed Pebble Springs nuclear power plant site is about four miles inland, to the south-southeast. Sampling staticns for set gill nets, hydroacoustic transects, and inverted hydroacoustic transducer studies are depicted in Figure 2.

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i C. METHODOLOGY I

1. Hydroacoustic

!a Equipment and Calibration I

The hydroacoustic data acquisition system was basically a recording echo sound-er. Target information was stored in two ways, as echograms, and on magnetic tape.

Echograms were usable only as a gross indication cf fish density or depth. Analysis of the data recorded on magnetic tape yielded quantitative information on fish density, depth, and distribution.

The components of BEAK's hydroacoustic data acquisition syster are shown in Figure 3. The system consisted of a Ross 200A Fineline echo sounder with a fre-quency of 200 kHz and a pulse control switch for 0.1 of 016 msec transnitter pulse duration. The transceiver was tuned to 200 kHz and calibrat d to the echo sounder with a calibration oscillator switch. The transducer produced a circular beam pattern of approximately 22 full angle at 6 dB down es shown in Figure 4. The echo sounding data were converted from 200 kHz to 5 kHz by chopper and filter circuits in an interface amplifier and recorded by a standard stereophonic tape recorder.

The system was described in greater detail by Thorne et al . (1972).

Other components of the hydroacoustic system included a Philips PF 3212 0-25 mHz dual channel oscilloscope. The oscilloscope monitored the transmitted or re-ceived signal during a survey and allowed accurate field calibration of the hydro-acoustic system. Calibration of the transducer and measurement of the system's various power output, transmit, receiver sensitivity, and source level was perform-This laboratory j ed by the Applied Physics Laboratory, University of Washington.

calibration was sufficient unless field calibration indicated a trouble source.

The voltage return of an echo from a fish is measured as a decibel level and termed its " target strength." To determine the target strength of chinook and coho smolts, BEAK conducted a series of experiments in April- 1978 on contained ,

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! smolts prior to initiating the study. The target strength of smolts was found to range from about 40 to 46 decibels. Submerged ping pong balls were found to have a target strength of about 41 decibels and were used as a convenient means of cali-brating the hydroacoustic gear prior to each survey. This calibration technique j

allowed discrimination between fish of small sizes (like smolts) and larger fishes.

I Voltage returns from large fish saturated the magnetic tape and were excluded during tape analysis. It was felt that this method was more selective for smolts and provided reliable overall data even when considering fish aspect (the position of the fish when detected).

b. Sampling Two acoustical techniques were employed in this study: "downlooking" and "uplocking." The downlooking technique involved the use of a boat-mounted trans-ducer . hat echoed signals off the river bottom (BEAK 1978). The uplooking tech-nique employed a hydroacoustic transducer that was anchored to the river bottom with sound waves echoed off the surface (Fi gure 5). The uplooking technique is particularly sensitive to fish located near the water surface. Since downstream migrating smolts tend to swim near the surface, it was felt that the uplooking technique would be more effective.

Downlooking hydrc :oustic transects were run at essentially the sare locations as those described above. Transects were run at each sample site for 10 minutes parallel to shore (five minutes upstream and five minutes downstream) and 10 minutes perpendicular to shore (five minutes across channel and five minutes back)

(Figure 2).

Fixed location sampling with the uplooking technique was conducted at each sample site for one hour in 7 to 12 m of water (Figure 2). Hydroacoustic data were recorded on magnetic tape for five minutes every 15 minutes during the hour. The echogram ran continuously throughout the hour.

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i t Both hydroacoustic techniques were used in conjunction with gill net sampling.

l Gill net samples provided relative abundance data for interpretation of hydroacous-

! tic density estimates as well as an alternate estimate of smoit density. Hydro-l acoustic surveys were conducted simultaneously with gill net sampling both day and night at the proposed intake site and at the upstream and downstream control sites.

c. Estimates of Fish Density Two methods have been developed for the estimation of fish densities. The first equires the use of an oscillosccpe and a tape player (Nunnallee 1974), and the second includes the use of a Digital Data Analysis Unit (DDAU) computer. Fi sh density estimates by computer are designed for hydroacoustic data of high fish densities. The oscilloscope method is more applicable to low densities as en-countered on this survey and was used throughout the study.

The signal channel output of the player was connected to the oscilloscope vertical input connector and the synchronization pulse output was applied to the external synchronization input connector. In this manner, the echo train from each transmitted pulse could be displayed over the width of the oscilloscope screen.

To separate the echoes or noise inherent in the system, a threshold just above the largest of the small echoes was established. Individual fish exceeding the threshold in each transect were counted. Threshold level decreased in proportion to depth. Compensation for the effect of depth on echo strength was made according to the technique described by Thorne (1972).

Magnetic tapo recordings were analyzed 4 to 5 times until agreement was reached on the number of individual fish targets.

The number of fish detected hv each pulse was treated as an independent measure of fish density, and by extension, the average density of fish within a

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volume was found by dividing the total number of fish detections by the product of ,

the corresponding effective pulse volume and the transect length, fish /1,000 m = (1,000) (total detections)

(effective pulse volume) (length of transect) l The volume of water insonified was determined from the half angle (;) of the transdacer bean (see Figure 4) and water depth (f).

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The uplooking technique provided estimations of relative fish density at the three sampling stations. During each one-hour sampling interval, the number of targets recorded during four five-ninute cbservations were counted and reduced to the mean number of fish per five-minute observation.

d. Data Analysis Magnetic tape recordings of hydroacoustic data were analyzed by the echo count-ing method described by Nunnalee (1974) utilizing a Phillips PM 3212 0-25 mHz dual channel oscilloscope.
2. Gill Nets Experimental monofilament, variable mesh gill nets 3.66 m by 45.7 m were utilized in the study. The nets incorporated six panels of 1.27, 2.54, and 3.81 cm square-mesh netting. During the course of the downtooking hydroacoustic transects a gill net was placed at each location and left in position for 30 minutes (Figure 2). At the end of the 30 minutes, the net was pulled, fish identified, counted, weighed, and fork lengths determined.

During each fixed location or uplooking hydroacoustic set, a gill tet was placed immediately downstream of the inverted transducer (Figure 2) and left in

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i position for one hour. At the end of the hour the transducer was hauled up and the lgillnetwaspulled. The fish were identified, counted, weighed, and measured. i I

All nets were tended continuously at the request of the Oregon Department of Fish and Wildlife to reduce salmonid mortalities. Dead adult salmonids were clean-

' ed, iced, and turned over to the Oregon State Police.

D. RESULTS

1. Gillnetting The total gill net catch during the interval April 17,197E through July 25, 1978 was 289 individuals representing 'l species (Appendix A, Table 1). Sockeye and chit.cok salmon and rainbow trout-steelhead were the only salmonid species captured.

Gill n?t time during the downlooking hydroacoustic studies amounted to 24 hours2.777778e-4 days <br />0.00667 hours <br />3.968254e-5 weeks <br />9.132e-6 months <br /> with 58 fish captured. Gill net time during the uplooking studies arcunted to 48 hours5.555556e-4 days <br />0.0133 hours <br />7.936508e-5 weeks <br />1.8264e-5 months <br /> and 231 fish (80 percent of the total catch). Snolts made up 4.1 percent of the total catch and were approximately evenly distributed between day and night Figures 6-8 illustrate catch / effort values (number / hour) for sair onids anci nonsalmonids captured by set gill nets downstream (net 1), at the proposed intake site (net 2), and upstream (net 3). Data from gill net sets conducted with uplook-ing and downlooking hydroacoustics (Appendix A, Table c) were combined in these fi gures . The night catch / effort values were generall,y , eater than daj values. The largest catch occurred June 19 at night in net 2 (37 individuals, most of which were chiselmouth).

The lar;est smolt catch of the study (five chinook salmon / hour) occurred during the day on July 12 at 'Se downstream station (Figure 6). Other salmonid catches at the downstream station occurred on May 25 (one chinook salmon adult), June 19 (one sockeye smolt), July 12 (one steelhead) and July 25 (three sockeye smolts). The nonsalmonid species collected in the downstream net wereJ freqominantly /_ - ii im northern squawfish and chiselmouth. _3) _

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! Figure 7 illustrates the catch / effort values for net 2, which was located in the area of the proposed intake. Salmonid catches occurred on April 24 (two chinook smolts), May 25 (one chinook adult), June 19 (one chinook juvenile), and July 25 i'

(four sockeye smolts). Net 2 caught fewer salmonids than the downstream ret (net 1) 1 but slightly more than the upsteam net (net 3).

Catch / effort values for the upstream net are shown in Figure 8 Salmonid catches occurred on April 24 (two chinook smolts), June 19 (one chinook and one sockeye smolt) and July 23 (four sockeye smolts). The nonsalmonid species collected in the upstream net were predominantly northern squawfish and chiselnouth.

Length-frequency distributions of the fish caught in gill nets at each station were similar (Figures 9-ll and Appendix A, Tables 3 and 5). The majority of fish fell into the 20 to 30 cm size range. Most of these fish were young sucker, north-ern squawfish and chiselnouth. Most of the salmonid smolts were in the 10 to 20 cm size range. Fish in the 0 to 10 cm size range were primarily redside shiners.

Adult chinook salmon ranged from 70 to 90 cm; the single steelhead captured fell into the 30 to 40 cm size range. No adult sockeye salmon were captured. It should be noted that larger size classes of fish were generally excluded fron the sanples due to the small mesh opening of gill net. Adult salmon occasionally becone en-tangled in small mesh gill nets even though they are . large to be gilled.

Mean wet weights of the species caught in the gill nets at each site are pre-sented in Appendix A, Table 4. Due to the low numbers of salmonids captured, no attempt was made to calculate biomass per unit effort from the weight data.

Total numbers and percentage composition of fishes caught in gill nets during downlooking studies and uplooking studies are compared in Appendix A, Table 6.

Salmonid smolts comprised 11.5 percent of the day catch and 8.7 percent of the night catch during downlooking studies, but only 2.3 percent -of, the day catch and Jdo '7'5 '

2.6 percent of the night catch during uplooking studies.

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  • Figure 10. Length-frequency distribution of salmonids and non-salmonids collected in experimental gili nets at Site 2 during day ano night sampling at the proposed intate site at the Pebble Springs study site on the Columbia River from April 17, 1978 through July 25,1978.

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! t Figure 11 Length-frequency distribusion of salmonids and non-salnonids collected in experimental gill nets at Site 3 during day and night sampling upstrecm of the proposed intake site at the Pebble Springs study site on the Columbia River fro- April 17, 1978 through July 25, 1978.

1

ew_ __ - . --__ -_- _-

l l

l 2. Hydroacoustic Studies The result of both the uplooking and downlooking hydroacoustic studies ndi- i l Cates that very few smolt-size fish were present at any of the sampling stations I

during the time intervals sampling v.<as conducted. Results of the uplooking hydro-acoustic samples are presented in Table 7. The largest number of smolt-size targets

! recorded during a five-minute uplooking observation (four targets) occurred at station 1 on April 17 and on July 25. One target per five-minute observation was the largest number of targets recorded at the proposed intake site (station 2).

The downstream station (station 1) had the largest total number of targets during the study. However, no significant station difference in relative fish density were detected.

Results of the downlooking transect surveys are shown in Table 8. Very few targets were recorded during either day or night surveye. No distribution patterns or station differences in fish density could be determined.

E. DISCUSSION Results of gill net and hydroacoustic studies conducted between April 17 and July 25,1978 indicate very low numbers of salmonid smolts in the vicinity of the proposed Pebble Springs intake. These results could be due to several factors.

First is the impact of the U.S. t.rmy Corps of Engineers (USACE) smolt transport program. Since 1977 the USACE has conducted a smolt trapping and hauling program at Lower Granite and Little Goose dans on the Snake River. In 1978 additional trapping and hauling was initiated at McNary Dam on the Columbia River. The cap-tured smolts were hauled to a release site below Bonneville Dam. In 1978, the USACE hauled 1.6 million chinook and 1.4 million steelhead from the Snake River Dans and 32,000 chinook, 21,000 steelhead, 22,000 coho and 7,000 sockeye fNm l

McNary Dam. This progrn may have resulted in reductions in the number of smolts passing the proposej intake site. The USACE plans to continue the trapping and 325 UO

c--- e e n - . .-- - -. ._ _ _ _ _ . _ _ _

I j hauling program in 1979. At the present time continuation of the program is deter-

' mined on a year-to-year basis by state and federal fisheries agencies (see letter

from E. M. Mains, Chief, Environmental Resources Branch USACE in Appendix B).

I Second, the migratory patterns of smolts in the study area are poorly under-stood. It is possible that the downstream migratory routes selected by the majority of smolts result in avoidance of the intake site. Although most of the available literature indicates that smolts tend to migrate along the shc. as of rivers (Mains and Smith 1964) there is relatively little information on their movement through impoundments. The sampling program was not designed to examine densities of fish in the midstream area or on the opposite shore. If this had been done, it is possible that migratory routes would have been identified, thereby, providing an alternate explanation for the low densities in the study area.

Third, it is possible that sampling techniques did not provide a representative estimate of the number of smolts ir the area. This is unlikely due to the variety of sampling methoas employed. Gill netting and hydroacoustic sanpling are techni-ques known to be effective in the estimation of fish density. Of the two hydroacous-tic methods employed, the uplooking technique probably provided the best estimate of smolt-size fish density. The downlooking technique is considered less efficient 3 due to potential problems associated with snolt avoidance of the noise created by the boat and the inefficiency of the gear in recording near-surfact fish. The fact that all three sampling techniques indicated low densities of smolts provides strong

, support for the conclusion that smoit densities were very low at the tire of samp-ling.

Finally, there is a possibility that the sampling frequency of two days per month was r.ot sufficient to detect representative smoit densities. Peak snolt migratory periofs in the Upper Columbia River are known to occur during the months that the study was conducted. However, it is also recognized that factors such as

,or < .I 3L] j c T)

__ e m _ _ _ _ _ . _ _ _ _ . _ _ . _ . _ _ _ _ _

! i water temperature, flow conditions and turbidity can infit.ence migratory rates l (Raymond 1968; USACE 1956). If one or more sampling dates happened to fall en a temporary period of slow migration, the measured densities may not have been repre-

! sentative of average daily densities preceding and following the sampling period.

Statistical analysis of the hydroacoustic data indicated no significant station differences in relative fish density. However, more targets were recorded at the downstre,o station (station 1) and gill net catches were generally higher at the oownstream station. Significantly higher fish densities were found at the down-stream station in 1977 (BEAK 1978). Differences in habitat characteristics might explain why more fish would be present at the downstrean site. Unlike the intake and upstream stations, the downstream station has back eddies and a shallow ledge that apparently make it a potential habitat for fishes, such as squawfish and chiselmouth. Gill net samples taken concurrently with the hydroacoustic sanple

in this study indicate that the relatively higher densities of targets that occur ed occasionally at downstream sites were probably caused by nonsalmonid fishes.

Fish densities from the downlooking hydroacoustics were considerably lower than those reported in the pebble Springs Final Report (BEAK 1978). This was probably due to calibration of the gear for smolt-size fish. In the previous study, no attempt was nade to discriminate between large and small fish.

CONCLUSION:

Data from the hydroacoustic and gill net studies indicate that very low nunbers of salmonid smolts were present in the vicinity of the proposed Pebble Springs in-take during the ird:rval April 17 through July 25, 1978. These findings are con-sistent with the data obtained during 1977 (BEAK 1978). The low number of smolts in this area may be, in part, a reflection of the effectiveness of the USACE smolt transport program. However, it is also possible that smolt migratory routes

-I n ase, the data through the John Day pool avoid the proposed intake area. D(3)pithgl I 2

BEAK - - - - - - - - - - -

indicate that the propased Pebble Springs intake would not pose a serious threat to downstream migratory salmonids.  !

i l

, r3 s')3


B E A K -

1 II. LONG-BILLED CURLEWS l A. INTRODUCTION One of the more conspicuous nesting birds in the Pebble Springs area is the Northern Long-billed Curlew (Numenius americanus parvus) (Rogers et al .1976).

{ This subspecies was formerly listed as " status undetermined" indicating that it "has been suggested as possibly threatened with extinction" (U.S. Department of Interior 1973), and is currently under consideration for endangered or threatened status by federal wildlife agencies. The major reason for this consideration is the extensive loss of curlew breeding habitat to agricultural development (David Marshall pers . comm. Aug.1977, U.S. Fish and Wild 1 Serv . ) .

The Long-billed Curlew commonly bred throughout the prairie regions of the United States and southern Canada prior to the 1900's (Bent 1929) but the extensive conversion of open prairie and rangelands to cultivated farmland has greatly reduced the present occurrence of breeding curlews to scattered populations in the western U.S. (U.S. Department of Interior 1973). This is especially true of the Gilliam, Morrow, and Umatilla Counties where thousands of acres of potential breeding habitat (shrub-steppe) have been converted to irrigated agricultural circles in the bst few years (Melland undated, John Kurtz pers. comm. April 1977, Umatilla Natl .

Wildl. Defuge).

Current information on curlew breeding behavior and the status of their population levels is limited. BEAK, therefore, developed a program to provide information on these factors which would assist in determining the effect of con-struction and operation of the Pebble Springs nuclear power plant and ancillary facilities on curlews. This report reviews information collected during 1978 to supplement data gathered during 1977 and provide additional information _on the curl ew populations of the Pebble Springs study area.

j

,, m B. hETF")DS  !

I l

Field studies were conducted during 1978 to collect information on the Long-  ;

billed Curlew popuiotions in the Pebble Springs study area. Road surveys were l i

' undertaken to determine the distribution, seasonal occurrence, habitat usage, and i

l nesting actif ties of the curlews in the area. The sampling methods were similar

, to those used in 1977 (BEAK 1978a)t iith slight modifications. The data generated each yea. are comparable within the constraint of these modifications.  ;

Four road survey transects (A, B, C, D) were established to survey Long-billed Curlews in the Pebble Springs study area with an observation corridor of 0.5 km on either side of the route (Figure 12). They very slightly from those used in 1977 (BEAK 1978a). Road transects were systematically run weekly in April, twice a month ir. May and June, and monthly in July and August in 1978. In 1977 the same schedule of site visits occurred but surveys were conducted on two consecutive cays for each site visit. Therefore, the sampling intensity in 1978 was about one half os great as the 1977 investigations. Leng hs of the transects and extent of major hab: tat type occurring in each transect corridor are presented in Appendix C. The routes were designed to provide a broad and representative inventory of the Pebble

.igs study area. During each site visit the road transects were driven by two observers in a 4-wheel drive ve 'icle. These observers plotted the number and location of all curlews observed w. thin the observation corrider on a field data map. A separate data map was used to record curlew observations for each site

' visit.

Long-billed Curlew habitat usage information was also collected during the )

t road surveys. Curlews that were " sing an area (e.g., perched, feeding, or nesting) when first detected were included in the analysis of habitat usage. Birds that were observed over an area but were not actually utilizing tbn habitat (i .e. , fly-ing, " mobbing") were omitted from the analysis. ,,, ,

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- - - - - - Future impounament boundary o- ,,.c u  : m e .

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l No systematic nest searches were undertaken but incidental surveys were con-  !

ducted if behavior of birds indicated a potential nesting location. In addition, i

a composite map of curlew observation was developed to assist in determining loca-l tion of territorial pairs. Repeated observations of one or two birds exhibiting feigning or defense behavior in the same area during two or more visits were assum-ed to designate a territorial pair.

C. RESULTS AND DISCUSSION Long-billed Curlews were observed fron 7 April when studies were initiated to 25 July 1978 (Figure 13, Appendix D). In contrast,16 June was the latest observa-tion of curlews on the Pebble Springs study area in 1977.

The observations of Long-billed Curlews fluctuated greatly along the individ-ual road transects during the survey period (Figure 13, Appendix D) in 1978. The high number of curlews observed on Transect A in July was probably a late occurring flock of migrants passing through the area or a concentration of local curlews engaged in premigratory staging. A segment of this flock (minimum of 20 birds) were females which typically have left on migration by the first week of July (Mel-land undated, BEAK 1978b). This implies that at least a portion of this flock were northern birds moving through the area. Tremaine (1975) reported that sporadic flocks from farther north passed through her study area after the breeding birds had departed. Transect B values were consistently high during most of the study period and the transect appeared to support the highest number of ootentially breeding curlews in the study area. The increase in curlew numbers near the end of the study (June and July) probably reflected a combination of premigratory stagirg and reproductive recruitment. Transect C supported a high number of cur-lews in mid April but the number 01 observat'ons declined greatly by the end of the month. Values for Transect D were generally low throughout the study period.

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l The number of curlews observed per site visit was generally lower during 1978 '

l '

! than 1977 (Figure 14). Patterns of abundance were generally similar for the two years. During the early part of the studies (April and May) the variations in observed numbers were of low magnitude and probably reflected a relatively stable breeding population. Only the observation of the large flock of late occurring i

curlews in 1978 departed from the pattern of abundance for 1977. The occurrence of these migratory flocks is probably sporadic and their observation may have been a chanc? occurrence due to the limited number of site visits during the fall migratory period.

Curlew observations were distributed throughout the study area but areas of concentration were noted (Figura 15). These concentration areas shifted in 1973 from those observed in 1977 (BEAK 1978a). The most notable difference occurred in the central portion of the reservoir where no large groups were observed as were seen in 1977.

Along the survey routes curlew observations were located exclusively in the rabbitbrush/cheatgrass (Chrysothamnus nauseosus/Bronus tectorum) comnunity (Appen-dix E). However, the rabbitbrush/cheatgrass comunity occupied almost the entire survey area with only small amount of other habitats (i.e., sagebrush, bitterbrush, cultivated) available. Therefore, curlew observations appeared to be roughly in proportion to those amounts of habitat available. Although information on habitat preferences was inconclusive the lack of curlew observations in sagebrush or culti-vated areas does appear to agree with studies by ;iacCallum et al . (1977), Grimes

' et al . (undated), Bent (1929), BEAK (1978b), Melland (undated), and Tremaine (1975).

Information from these studies indicate that rabbitbrush/cheatgrass community ap-parently provides a sparse, short-statured vegetation that curlew prefer during the breeding season for nesting and feeding.

Observer biases due to varying ability to locate birds in the habitat types f 4ID

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may have influenced the results. Birds in the low, sparse vegetation of the  !

O rabbitbrush/cheatgrass habitat may have been easier to locate than birds in the dense, tall stands of sagebrush and bitterbrush. While this may be an important factor, it does not appear t account for the observed difference in usage between 8 habitat types. In addition, breeding activities (i.e., calls, courtship and defen-

sive flights) of the curlews were generally quite conspicuous and would have been

. easily observed in the sagebrush /bitterbrush habitats. Findings reported by BEAK 9 (197Eb) appeared to verify this assumption.

A minimum of four territorial or nesting pairs of Long-billed Curlews were judged to be using the study area based on composite mapping of bird observations O

(Figure 16) but these estimates are highly speculative due to the limited number of site visits. No nests or juveniles were located during 1978, although, incidental searches were made on several occasions when behavior of the birds indicat< a O

potential nesting site. The number of territorial pairs using the study area in 1978 was lower than in 1977, and only two of the territorial pairs observed in 1978 occurred in locations similar to those reported in 1977 (BEAK 19783).

Atypical weather conditions (i .e., drought, late frost) reported during 1976 and 1977 were presumed to hav disrupted curlew breeding activities. Data collect-

  1. ed during 1978 was to be used to determine what might occur during more nomal climatic conditions. However, data for 1978 indicate that curlew populations and the number of territorial pairs were generally lower in 1978 (BEAK 1978). In 8 addition, the distribution of the observations of curlews also snif ted. Fa c tors

, that may have contributed to this decline are unknown .aut Tremaine (1975) indicated that following a year of low reproductit e success, 30r of the nesting territories 8 could be vacant the next year. During 1977 no fledged juveniles were observed at Pebble Springs or Boardman (BEAK 1978a,b). Similarly Melland (undated) indicated that no young curlews were observed in 1977 in Heppner-Hardm3n 23 1x apea, so

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III. RAPTORS A. INTRODUCTION A substantial raptor (i.e., birds of prey) population has been recorded for Pebble Springs study area (Rogers et al . 1975, 1976). Considerable public interest 1

i and concern has developed in recent years due to the aesthetic and emotional appeal of raptors, their relative rarity, and their economic and environmental importance.

This increased concern coupled with the drastic decline of raptor populations in North America has resulted in federal and state legislation and regulations to protect many of these species (e.g. , Bald Eagle and Golden Eagle Protection Act, Endangered Species Act as amended 1973). In addition, raptors are consuners at the top of the food web and have been shown to exhibit population changes which could be associated with environmental stresses such as chemical variations in prey population and modifications of habitat (e.g. , Cooke 1973, Craighead and Craighead 1969, White 1974, Snyder and Snyder 1975, and Verner 1975). Thus changes in the raptor populations nay serve as an indirect measure of habitat quality for a wide variety of wildlife species. Therefore, raptors were studies to deterrine their distribution, abundance, and nestir.g status on the Pebble Springs study area ,

Raptor (i .e. , birds of prey) studies on the Pebble Springs study area included hawks, owls, eagles, and falcons; however, two additional kinds of birds , the Connon Raven and Loggerhead Shrike, were also included in the program. Although taxonom-ically and morphologically these species are not viewed as "true" raptor species, they compete with various raptorial species for prey and nesting sites and ecologi-cally function as raptors or birds of prey (Craighead and Craighead 1969).

B. METHODS Four road su"vey transects were established to collect information on th?

distribution and abundance of raptors (i .e. , birds of prey) population or, the Pebble Springs study area from 7 April to 8 August,1978. Raptor surveys were conducted 3 ') G 1~~

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i concurrent with Long-billed Curlew surveys and followed similar data collection procedure . A 0.5 kilometer strip on each side of the route (Figure 12) formed the l

approximate observation corridor for the road survey transects. Lengths of the survey routes are presented in Appendix C.

1 iC. RESULTS AND DISCUSSION Eight species of raptors were observed on the Pebble Springs study area during 1978 ( Appendices F and G). These species are typically associated with the shrub-steppe community of the Pacific Nortnwest (Rotenberry and Wiens 1978). In 1977,12 species were recorded during general bird transects and incidental observations (BEAK 1978a). Four species, the Prairie Falcon, Rough-legged Hawk, Short-eared Owl, and Burrowing Owl, that were observed during 1977 were not recorded in 1978. A reduction in sampling intensity (i.e., one day site visit) during 1978 may have been a factor that contributed to the lower number of species observed.

Common Raven, Ferruginous Hawk, and Swainson's Hawk were the most abundant raptor species in the Pebble Springs study area in 1976 (Appendices F and G).

The Common Raven was most abundant on Transect A where it was also the only species observed. Ravens along this transect were frequently observed feeding on carrion (i.e., sheep carcasses). The high number of Swainson's Hawks on Transect B and C and Ferruginous Hawks on Transect D were attributed to survey routes adjacent to active nest locations. Likewise, the high number of Common Ravens on Transect B were probably due to the suitable nesting sites (i .e., cliffs) adjacent to the route. The greatest number of raptor species in the Pebble Springs area occurred along Transect C, specifically the Eight Mile Canyon area. Obstruction currents (i.e., updraf ts) and riparian habitat of the canyon apparently created suitable conditions for soaring and foraging for a variety of raptors.

The Swainson's and Ferruginous Hawks and Common Ravens were observed repeatedly during 1978 and presumed to be breeding in the study area (Appendix G). Breeding

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i activities of the Ferruginous and Swainson's Hawks were verified by the location of

' nests (Figure 17). The frequent observations of Common Ravens along the cliff areas of Transect B indicated the presence of a potential nest location. Observations of the Red-tailed Hawk, Golden Eagle, and Marsh Hawk were limited and sporadic i

! indicating that these species were probably not breeding in the study area. Logger-i

! head Shrike and American Kestrel may have been nesting in the study area but no nest sites or territorial pairs were recorded.

An egg-laying / incubating Ferruginous Hawk was observed on a nest in a juniper on 27 April (Figure 17). Adult birds were recorded repeatedly on subsequent field visits and two downy young were observed on 21 June witn both adults in attendance.

However, on 25 July the nest was found demolished with one young hanging dead in the tree and an adult bird was nearby. Although the fate of the second nestling is unknown, an immature Ferruginous Hawk was observed in adjacent Eight Mile Canyon on 8 August.

A Swainson's Hawk was observed on a nest in a juniper on 5 May (Figure 17).

This same nest was also occupied by a Swainson's Hawk in 1977. Three young nest-lings and one egg were observed in the nest on 21 June 1978 with a dark phase Swainson's Hawk soaring nearby. On 25 July one nestling was observed in the nest and the remains of a down-covered juvenile were discovered under the nest. The nest was found deserted on 8 August and the remaining young bird had presunably fl edged .

Although no productivity studies were conducted at Pebble Springs, it appears that both nests observed during 1978 were successful (i.e., fledged young). In 1977 the only nest site located was a single Swainson's Hawk and it was also presumed to be successful .

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REFERENCES Beak Consultants Incorporated. 1978a. Pre-construction ecological studies for Pebble Springs site, Final Report. Prepared for Portland General Electric, Portland, Oregon. 86 pp.

l Beak Consultants Incorporated. 1978b. Boardman terrestrial monitoring program April 1977 through September 1978. Prepared for Portland General Electric ,

Portland, Oregon. 196 pp. + appendices.

Bent, A. C. 1929. Long-billed Curlew. pp 97-109 h A. C. Bent. Life histories of North American shorebirds. Government Printing Office, Washington, D.C.

Cooke, A. S. 1973. Shell thinning in avian eggs by environmental pollutants.

Environ. Pollut. 4(2):85-152. ,

i C'aighead, J. J., and F. C. Craighead, Jr. 1969. Hawks , owls and wildli fe. Dover Publications, Inc., New York. 443 pp.

Grimes, J. , L. Fujii, Chase, C. Zeigler, and P. Blom. undated. Long-billed Curlew density and habitat study. Snake River Regional Studies Center, College of Idaho, Caldwell, Idaho. Unpublished. 13 pp.

MacCullum, D. A., W. D. Graul, and R. Zaccagnini. 1977. The breeding status of the Long-billed Curlew in Colorado. Auk 94(3)S59-601.

Mains, Edward M., and John M. Smith. 1964 The distribution, size, time, and current preferences of seaward migrant chinook salmon in the Columbia and Snake i Rivers. Wash. Dept. Fish. , Fish. Res . Papers. 2(3):5-43.

Melland, J. Undated. Long-billed Curlew study (Numenius americanus) in Morrow and Umatilla Counties during 1976 and 1977. Oregon Fish and Wildlife Departnent Nongame Wildlife Report. Portland, Oregon. Unpublished. 5 pp.

Nunnallee, E. P. 1974 A hydroacoustic data acquisition and digital data analysis system for the assessment of fish stock abundance. WSG 74-2 Div. of Marine Res.

University of Washington.

Raymond, Howard L. 1968. Migration rates of yearling chinook salmon in relation to flows and impoundment in the Columbia and Snake Rivers. Trans. Am. Fish Soc. i 97(4):356-359.

Rogers , L. , D. Uresk, J. Hedlund and W. Rickard. 1976. Terrestrial ecology base-1 line study of the Pebble Springs Site, Gilliam County, Oregon, Final Report.

Prepared for Portland General Electric Portland, Oregon 59 pp.

Rogers, l.. E. , J. M. Gurtisen, W. H. Rickard, and P,. E. Fitzner. 1975. Ecological characterizations of the Boardman Site and environs, Morrow County, Oregon, Final Report. Prepared for Fortland General Electric Company, Portland, Oregon. 86 pp

+ appendices.

Rotenberry, J. T., and J. A. Wiens. 1978. Nongame bird communities in northwest-ern rangelands. pp. 32-46 in Richard M. DeGraa f (Coor.) . Proceeding of the i workshoo on ncngame bird habitat management in the coniferous forests of the western U.S. USDA For. Serv. Gen. Tech. Rept. PNW-64. 100 pp.

I

i Sr.yder, N. F. R. , and H. A. Snyde r. 1975. Raptors in range habitat. pp. 190-209 in D. R. Smith (Coor.). Symposium on management of forest and range hacitats l for nongame birds. USDA For. Serv. Gen. Tech. Rept. WO-1, 343 pp.

  • Thorne, R. E. 1971. Hydroacoustic assessment of limnetic-feeding fishes. pp 317-i 322 in J. F. Franklin, L. S. Dempster and R. H. Waring (ed.) . Proc-Research on coniferous forest ecosystems. A sytposium. USDA For. Ser . Pn-;iand , Ore.

Thorne , R. E . , E . P. Nunnalle , and J . H . Green . 1972. A portable hydroacoustic data acquisition system for fish stock assessment. WSG72-4 Di v . of Ma r. Res.

Univ. of Washington. 14 pp.

Tremaine, M. M. 1975. Letter dated January 28, 1975 to L. Napier, Wildlife Biologist, Malheur National Wildlife Refuge. 6 pp.

U.S. Army Corps of Engineers , North Paci fic Division. 1956. " Progress Report on Fisheries-Engineering Research Program" pp 14-26, Contributed by E. M. Mains and J. M. Smith, Washington State Dept. of Fisheries. " Determination or the normal stream distribution, size, time and current preferenccs of downstream migrating salmon and steelhead trout in the Columbia o sd Snake Rivers."

U.S. Department of Interior, Fish and Wildlife Service. 1973. Threatened wild-li fe of the United States . Resource Publication Ne 14 Washington, D. C.

289 pp.

Verner, J. 1975. Avian behavior and habitat management. pp.39-58 in D. R. Smith (Coor.) Symposium on Management of forest and range habitats for Nongame birds. USDA, For. Serv. Gen. Tech. Rep . WO-1, 343 pp.

White, C. M. 1974 Cur-ent problems and iechniques in raptor management and con-servation. Trans . N. Amer. Wild 1. Conf. 39:310-312.

2) 140

_._ggag . _ _ _ _ _._ _ -

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l APPENDIX A Tables 1-8 325 14:

r__ o c u ..__. _ _ _ _ _ _ . _ _ _ _ . _

Table 1. Common and scientific names of fishes collected in the Columbia River at the Pebble Springs study site during the period April 17, 1978 through July 25, 1978,

! Common Name Scientific Name Salmonidae i

Sockeye salmon Oncorhynchus nerka (Walbaum)

Chinook salmon Oncorhynchus tshawytscha (Walbaum)

Rainbow trout (steelhead) Salmo gaardneri (Richardson)

Catostomidae Bridgelip sucker Catostonus columbianus (Eigenmann and Eigen-ann)

Largescale sucker Catostomus macrocheilus (Girard)

Cyprinidae Carp Cyprinus carpio (Linnaeus)

Peamouth Mylocheilus caurinus (Richardson)

Northern squawfish Ptychocheilus oregonensis Redside shiner Richardsonius balteatus (Richardson)

Chiselmouth Achrocheilus alutaceus (Agassiz and Pickering)

Percopsidae Sand roller Columbia transmontana (Eigere. ann and Eigenmann) 325 142

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BEAK --

I 1

l l

' Table 5. Length-frequency distribution of salmonids and nonsalmonids collected  !

in experimental gill nets during day and night uplooking hydroacoustics at the Pebble Springs study site on the Columbia River from April 17, 1978 through July 25, 1978. I DAY NIGHT FORK LENGTH RANGE j SAL N-S Al. SAL N-SAL i 0-9 NET 1 0 0 0 0 1 2 2 4 10-19 0 10 0 35 20-29 0 0 0 1 30-39 0 0 0 0 40-49 0 0 0 1 50-59 0 0 0 0 60-69 1 0 0 0 70-  :

NET 2 0 0 0 3 0-9 0 5 0 13 10-19 0 9 0 53 20-29 0 0 1 6 30-39 0 0 0 1 40-49 0 0 0 0 50-59 0 0 0 0 60-69 0 0 1 0 70-NET 3 0 0 0 4 0-9 0 7 3 10 10-19 0 7 0 47 20-29 0 1 0 2 30-39 0 0 0 1 40-49 0 0 0 0 50-59 0 0 0 0 60-69 0 0 0 0 70-i

e r A

BEAK

{

l t

Table 5. Length-frequency distribution of salmonids and nonsalmonids collected in experimental gill nets during day and night downlocking hydro-acoustics at the Pebble Springr study site on the Columbia River from April 17, 1978 through July 25, 1978.

DAY NIGHT FORK LENGTH RANGE l

SAL N-SAL _ SAL N-SAL l i NET 1 0 0 0 0 0-9

! 2 0 1 6 10-19 0 1 0 6 20-19 0 0 1 1 30-39 0 0 0 0 40-49 0 0 0 0 50-59 0 0 0 0 60-69 0 0 0 0 70-NET 2 0 0 0 0 0-9 2 1 1 5 10-19 0 8 0 2 20-29 0 1 0 0 30-39 0 0 0 0 40 49 0 0 0 0 50-59 0 0 0 0 60-69 0 0 0 0 70-NET 3 0 0 0 0 0-9 0 3 0 0 10-19 17 0 0 2,-29 0

0 0 0 0 30-39 0 0 0 0 40-49 0 0 0 0 50-59 0 0 0 0 60-69 0 0 0 0 70-i kb-

}'[!}

ecu _ _

i Table 5. Length-frequency distribution of salmonids and nonsalmonids collected in i experimental gill ;,ets during day and night, uplooking and downlooking j hydroacoustics at the Pebble Springs study site on the Columbia River from April 17, 1978 through July 25, 1978.  ;

i CAY NIGHT FORK LENGTH RANGE

SAL N-SAL SAL N-SAL I

NET 1 0 0 0 0 0-9 3 2 3 10 10-19 0 11 0 41 20-29 0 0 1 2 30-39 0 0 0 0 40-49 0 0 0 1 50-59 0 0 0 0 60-69  !

1 0 0 0 70-  !

l NET 2 0 0 0 3 0-9 2 6 1 18 10-19 0 17 0 55 20-29 0 1 1 6 30-39 0 0 0 1 40-49 0 0 0 0 50-59 0 0 0 0 60-69 0 0 0 0 70-79 0 0 1 0 80-89 NET 3 0 0 0 4 0-9 0 10 3 10 10-19 0 24 0 47 20-29 0 1 0 2 30-39 0 0 0 1 40-49 0 0 0 0 50-59 0 0 0 0 t3-69 0 0 0 0 70-i I .)

i

ggag i

l Table 6. Total number and pucentage of fishes captured day and night in experi-

! mental gill nets at the Pebbie Springs study site on the Columbia River from April 17, 1978 through July 25, 1978.

DOWNLOOKING PERCENT TABLES DAY NIGHT TOTAL

! Sockeye Salmon (S) 1 2.9% 0 0.0% 1 1.75

! Chinook Salmon 0 0.0% 0 0.0% 0 0.09

' Chinook Salmon (S) 3 8.6% 2 8.7% 5 8.65 Chinook Salmon (J) 0 0.0% 0 0.0% 0 0.0%

Rainbow Trout 0 0.0% 1 4.35 1 1.7%

Bridgelip Sucker 1 2.9% 2 8.7% 3 5.25 Largescale Sucker 2 5.7% 0 0.01 2 3.45 Carp 0 0.0% 0 0.05 0 0.05 ,

Peamouth 5 14.3% 7 30.45 12 20.7" Northern Squawfish 7 20.0% 5 21.7% 12 20.79 ,

Redside Shiner 0 0.05 0 0.05 0 0.01 45.7% 26.1% 22 37.9; Chiselmouth 16 6 Sand Roller 0 0.0% 0 0.0% 0 0.05 UPLOOKING PERCENT TABLE _S DAY NIGHT TOTAL Sockeye Salmon (S) 0 0.05 4 2.1% 4 1.7%

Chinook Salmon 1 2.3% 1 .5" 2 .95 Chinook Salmon (S) 1 2.3" l .5# 2 . 9?;

- Chinook Salmon (J) 0 0.09 1 .5% 1 .45 Rainbow Trout 0 0.05 0 0.05 0 0.0" Bridgelip Sucker 0 0.09 1 .55 1 4E Largescale Sucker 1 2.34 1 .55 2 .95 Carp 0 0.05 2 1.1% 2 .9' Peamouth 8 18.65 17 9.0^' 25 10.8E Northern Squawfish 5 11.6% 22 ll.7N 27 11.7%

Redside Shiner 0 0.0 ' 3 1.65 3 1.3t Chiselmouth 27 62.8% 124 66.01' 151 65.4=

Sand Roller 0 0.0% 11 5.95 11 4.8E OVERALL PERCENT TABLES DAY NIGHT TOTAL Sockeye Salmon (S) 1 1.3% 4 1.9% 5 1.7" Chincok Salnon 1 1.3% 1 .5" 2 .75 Chirook Salmon (S) 4 5.1 % 3 1.4% 7 2.45' Chinook Salmon (J) 0 0.0% 1 .55 1 .3%

0 0.0% 1 .5% 1 . 3 *:

l Rainbow Trout l Bridgelip Sucker 1 1.3% 3 1.4% 4 1.4%

Largescale Sucker 3 3.8% 1 .5% 4 1. 4 'l

! Carp 0 0.0% 2 .9% 2 . 7 c/

l Peamouth 13 16.7% 24 11.4% 37 12.85 Northern Squawfish 12 15.4% 27 12.8% 39 1 3 . 551 Redside Shiner 0 0.0% 3 1.4% 3 1.05 Chiselmouth 43 5 5 .1 ", 130 61.6% 173 59.99 Sand Roller 0 0.0% 11 5.2% 11 3.8%

(S) Smol ts (J) Jack

B C A 8C l

l Table 7. Mean and total number of smolt-size targets observed per 5-minute sampling

' interval at each station for day and night uplooking hydroacoustic l I samples April 17 through July 25, 1978. l l

i FISH OBSERVED IN MEAN NUMBEP TIME EACH 5 MINUTE OF FISH PER STANDARD l STATION INTERVAL 5 MINUTE INTERVAL DEVIATION DATE DAY / NIGHT ,

4-17-78 N 1 0,0,0,0 0 -

l N 2 0 ,1,1,0 0.50 0.58 l N 3 0,0,0,0 0 -

D 1 4,0,0,0 1.00 2.00 D 2 0,0,0,0 0 -

D 3 0,0,0,0 0 -

4-24-78 N 1 0,0,0,0 0 -

i N 2 0,0,0,0 0 -

N 3 0 ,1.0 .0 0.25 0.50 D 1 0,0,0,0 0 -

D 2 0,0,0.0 0 -

D 3 0,0,1,0 0.25 0.50 5-15-78 N 1 No Data * - -

N 2 No Data * - -

i N 3 No Data * - -

D 1 0,0,0,0 0 -

D 2 0,0,0,0 0 -

D 3 0,0,0,0 0 -

5-25-78 N 1 0,0,1,0 0.25 0.50 8 "

N 2 0,0,0,1 0.25 0.50 1

N 3 No Data ** - -

t D 1 3,0,3,0 1.50 1.70 D 2 0,0,0,0 0 -

D 3 0,0,0,0 0 -

6-19-78 N 1 + 0,C,0,0 0 -

N 2 0,0,0,0 0 -

N 3 0,0,0,0 0 -

0 - i D 1 0,0,0,0 D 2 0,0,0,0 0 -

D 3 0,0,0,0 0 -

t 6-27-78 N 1 0,0,0,0 0 -

t N 2 0,0,1,0 0.25 0.50 N 3 0,1,0,0 0.25 0.50 D 1 0,0,0,0 0 -

I D 2 0,0,0,0 0 -

D 3 0,0,0,0 0 -

l 1 No Data ** - - ,

l7-12-78 "

N No Data ** - - l N 2 l  !

N 3 No Data ** - -

D 1 0,0,0,0 0 -

D 2 0,0,0,0 0 -

f "

D 3 1,0,0,0 0.25 0.50 7-25-78 N 1 2,4,0,0 1.50 1.90 N 2 1,0,0,0 0.25 0.50 N 3 0,0,0,0 0 D 1 0 ,1,0 ,0 0.25 0.50

.l -

D 2 0,0,0,0 0 ,

! I D 3 2,0,0,0 0.5d 2 b } b / 1.00

  • Sampling cancelled due to weather l
    • Sampling not completed di to equipment failure 1

i

BEAK-f 3

Ta bl e 8. Density (number of targets /1,000 m ) of smolt-size targets recorded along ,

downlooking hydroacoustic transects at each station for day and night j surveys, April 17 through July 25, 1978.

DAY NIGHT DATE STATION 1 STATION 2 STATION 3 STATION 1 STATION 2 STATION 3 4/17 0.000 0.000 0.000 0.000 0.000 0.000 4/24 0.000 0.000 0.000 0.000 0.000 0.000 j 4/15 0.000 0.000 0.000 5/25 0.000 0.000 0.000 0.000 0.000 0.000 )

6/19 0.000 0.000 0.000 0.000 0.000 0.000 j 6/27 0.000 0.000 0.000 0.000 0.000 0.000 7/12 0.000 0.000 0.005 7/25 0.035 0.004 0.000 0.000 0.000 0.000

  • Sampling cancelbd due to weather
    • Sampling not sompleted due to equipment failure i

1 __ _ _ _.

y ' DEPARTMENT OF THE ARMY

- X. s* NORTH PACIFIC DIVislON. CORPS or ENGINEERS d P.O. BOX 2870 PORTLAND, OREGON 97208 k

20 September 1978 NPDPL-ER Mr. Mark T. Hill Fishing Biologist Beak Consultants Inc.

8th Floor, Loyalty Bldg.

317 S.W. Alder St.

Portland, Oregon 97200

Dear Mark:

In response to your 14 September 1978 letter regarding stolt transporta-tion objectives, the following information is provided.

At present our objective is to trap and haul all the smolts we can from Lower Granite, Little Goose, and McNary Dams to a release point below Bonneville Dam.

In 1777 and 1978 we hauled everything we could trap and haul from Lower Grtnite and Little Goose, but we did not have all units at these projects :ully s:reened.

In 1979 we will have all six units at each of these projects fully screened and should nave the capability of trapping and hauling 70% to 80% of the Snake RiverThey migra-tion. The one possible constraint is the fisheries agencies.

have made a determination on a year-to-year basis as to what percent of the fish we should haul. So far we have heard nothing about 1979, but are planning to haul everything we can trap.

Our effort at Mc Nary is still largely experimental with two of fourteen units to be screened by spring, 1979. We do plan to haul most of the fish that are taken at McNary, subject to fisheries agencies concur-rence. Some fish will be released at McNary as control fish.

As far as numbers are concerned, N.M.F.S. usually estimates 8 to 10 We million salmon and steelhead stolts leaving the Snake River system.

haven't seen any numbers like that. In 1977 we hauled 1.7 million chinook and 1.1 million steelhead from Little Goose and Lower Granite to below Bonneville. In 1978 we hauled 1.6 million chinook and 1.4 million steel-1oa 60e 2rJ

September 1978 S20PL-ER Mr. Mark T. Hill head. In 1978, our first year's effort at McNary, 32,097 chinook, 20,799 steelhead, 22,458 coho and 6,857 sockeye were transported.

I hope this information is useful to you. Please let me know if I can be of further assistance.

Sincerely yo, ,

s'

(

f ED'n'bO M. MAINS Chief, Environmental Resource Branch 2

}2)I )I

9 ocu I

i Appendix C. Area (W , of major habitat types along the road survey transects at Pebble Springs Study Area in 1978. Values are based on a 0.5 9 km strip on either side of the transects.

1 TRANSECT A B C D l

' Length of Transect (km) 2.0 4.1 4.4 3.0

! HABITAT TYPES i  !

Rabbitbrush/Cheatgrass 6.0 (95?;) 8.5 (100?:) 10.0 (97?;) 6.4 (90!;)

Sagebrush /Bitterbrush 0.0 (0%) 0.0 (0!!) 0. 3 (3 % ) 0.0 (OT:)

' Disturbed /Agricultur e 0.3 (5") 0.0 (05;) 0.0 (01) 0.7 (10!;)

Total 6.3 (100!. 8.5 (100!') 10.3 (100';) 7.1 (100i:)

9 O

l e

e  !

9 I

I i I

i i

I

,e r- ,4 3i (/ 4 O

l t _

Appendix D. Number of Long-billed Curlews observed per site visit on road survey transects at the Pebble Springs

  • study area during 1978.

TRANSECT ALL TRANSECTS A B C D 1978 19771 No./ No./ No./ No./ No./ No./ No./ No./ Average No./

Sample Period Survey 10 km Survey 10 km Survey 10 km Survel 10 km Total No. 10 km Total No.

0.0 0.0 9.0 10.6 2.0 1.9 1.0 1.4 12.0 3.5 15.0 4/7 0.0 0.0 6.0 7.1 8.0 7.8 0.0 0.0 14.0 3.7 20.0 4/12 0.0 0.0 2.0 2.4 6.0 5.8 1.0 1.4 9.0 2.4 16.0 4/18 1.0 1.5 2.0 2.4 2.0 1.9 1.0 1.4 6.0 1.8 20.0 4/27 0.0 0.0 5.0 5.9 1.0 1.0 4.0 5.6 10.0 3.1 17.0 5/10 3.0 4.6 6.0 7.1 0.0 0.0 0.0 0.0 9.0 2.9 19.0 5/22 2.0 3.0 11.0 13.0 0.0 0.0 1.0 1.4 14.0 6.3 43.0 6/6 2.0 3.0 0.0 0.0 1.0 1., 0 0.0 0.0 3.0 1.0 3.0 6/21 196.0 297.0 0.0 0.0 0.0 0.0 0.0 0.0 196.0 74.3 0.0 7/25 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 8/8 204.0 309.1 41.0 48.5 20.0 19.4 8.0 11.2 278.0 99.0 153.0 I Total Average number of curlews observed during 2-day site visits on comparable dates in 1977.

N

~1 I

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u s l

. s h a t8 a s r a7 r u u

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t a p b s t -

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O ecax - --

___ _l Appendix F. Average number of raptors observed per 10 km of road survey transects on the Pebble Spring study area from 7 April to 8 August 1978.

e TRANSECTS A C D Total B.

l '

' 0.2 0.9 0 1.1 Red-tailed Hawk C GP i  !

0 1.2 1.6 1.0 3.8 Swainson's Hawk i 0 1.1 3.0 4.1 Fe.ruginous Hawk 0 Buteo spp. 0 0.4 0.4 0 0.8 l 0 0.2 0 0.4 Golde- Eagle 0 0.2 0 0 0.2 0 0.2  !

Marsh Hawk  :

American Kestrel 0 0 0.7 1.0 1.7 l 8 1.3 24.6  !

Common Raven 20.0 2.2 1.1 0 0.4 0 0.3 0.7 l Loggerhead Shrike l

Total 20.0 4.6 6.2 6.6 i ED O

e t 9

O r r j ("i p" i

)[) i / '

cp l .

+

w --

Appendix G. Number of raptors observed per 10 km of road survey transect on the Pebble Spring study area from 7 April to 8 August 1978.  ;

l SURVEY PERIODS April 7 April 12 April 18 April 27 May 10 SPECIES TRANSECTS A B C D A B C D A B C D A B C D A B C D 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Red-tailed Hawk 0 0 2.3 0

,Swainson's Hawk 0 2.5 0 0 0 0 2.3 0 0 0 4.6 0 0 0 2.3 3.3 0 0 4.6 3.3 Ferruginous Hawk 0 0 2.3 3.3 0 0 0 0 0 0 0 3.3 0 0 0 3.3 0 0 2.3 3.3 0 0 0 3.3 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Buteo spp.

2.3 0 0 0 0 0 0 0 0 0 0 0 0 0 Golden Eagle 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 American Kestrel 0 0 0 0 0 0 0 0 2.3 6.6 0 0 2.3 0 lMarshHawk Common Raven 0

0 0

10.0 0 0 3.3 0 0 0 0

0 0 9.9 4.9 0 2.3 0 24.5 2.5 0 3.3 4.9 7.5 4.6 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Loggerhead Shrike 0 0 2.3 0 0 0 Total 0 12.5 6.9 9.9 0 0 4.6 9.9 4.9 0 6.9 3.3 24.5 2.5 4.6 16.5 4.9 7.5 13.8 6.6 SURVEY PERIODS J May 22 June 6 June 21 Ju T 25 August 8

( SPECIES TRANSECTS C D A B C D A B C D A B C D

~A B C D A B 0 n 0 0 0 4.6 0 0 0 2.3 0 0 2.5 0 0 Red t iled Hawk 0 0 0 0 0 0

Swainson's Hawk 0 2.5 0 0 0 2. .3 0 0 2.5 2.3 3.3 0 2.5 0 0 0 0 0 Ferruginous Hawk 0 0 0 3.3 0 0 -.3 3.3 0 0 2.3 5.6 0 0 0 3.3 0 0 2.3 0 0 0 0 0 0 0 2.5 4.6 0 0 0 0 0 0 0 0 0 lButeo spp. 0 2.5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Golden Eagle 0 2.5 0 0 0 0 0 0

0 0 0 0 0 0 0 0 0 Marsh Hawk 0 0 2.3 0 0 0 0 0 0 C 0 0 0 0 0 0 0 0 0 0 0 0 0 0

'American Kestrel 0 0 '3

. 0 0 0 2.5 2.3 0 0 0 0 0 0 0 Common Raven 14.7 0 .3 0 0 0 2.3 0 0 0 C 0 0 0 0 0 0 0 2.5 0 0 0 0 0 3.3 Loggerhead Shrike 0 0 0 0 0 0 14.7 7.5 6.9 3.3 0 2.5 6.9 3.3 0 7.5 16.1 9.9 0 5.0 23 3.3 0 2.5 2.3 3.3

Total 1

- --]