Data Report No~ 91. Juvenile Atlantic Salmon Densities, Miramichi River System, New Brunswick, J. L. Peppar and E. J.

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Juvenile Atlantic Salmon Densities, Miramichi River System, New Brunswick, 1969-77 J. L. Peppar and E. J. Schofield Freshwater and Anadromous Division Resource Branch Fisheries and Marine Service Department of Fish@ries and the Environment Halifax, Nova Scotia September 1978 Fisheries and Marine Service Data Report No~ 91

Fisheries and Marine Service Data Reports These reports provide a medium For filing and archiving data compilations where little or no analysis is included. Such compilations commonly will have been prepared in support of other journal publications or reports. The subject matter of Data Reports renects the broad interestsand policies of the Fisheries and Marine Service, namely, fisheries management, technology and development, ocean sciences and aquatic environments relevant to Canada. Numbers 1-25 in this series were issued as Fisheries and Marine Service Data Records by the Pacific Biological Station, Nanaimo, B.C. The series name was changed with report number 26. Data Reports are not intended For general distribution and the contents must not be referred to in other publications without prior written clearance From the issuing establishment. The correct citation appears above the abstract of each report. Service des peches et des sciences de la mer Rapports statistiques Ces rapports servent de base,\ la compilation des donnees de classement et d'archives pour lesquelles il y a peu ou point d'analyse. Cette compilation aura d'ordinaire ete preparee pour appuyer d'autres publications ou rapports. Les sujets des Rapports statistiques refletent la vaste gamme des interets et politiques du Service des peches et de la mer, notamment gestion des peches, techniques et developpement, sciences oceaniques et environnements aquatiques, au Canada. Les numeros 1-25 de cette serie ont ete publies,\ titre de Record.., statistiques, Service des peches et de la mer, par la Station biologique du Pacifique, Nanaimo (C.-B,). Le nom de la serie a ete modif'ie,\ partir du numero 26. Les Rapports statistiques ne sont pas prepares pour une vaste distribution et leur contenu ne doit pas etre mentionne dans une publication sans autorisation ecrite prealable de I'etablissement auteur. Le titre exact para'lt au haut du resume de chaque rapport..cover design by Christine Rusk

Fisheries and Marine Service Data Report No. 91 September 1978 JUVENILE ATLANTIC SALMON DENSITIES, MIRAMICHI RIVER SYSTEM, NEW BRUNSWICK, 1969-77 J.L. Peppar and E.J. Schofield Freshwater and Anadromous Division Resource Branch Fisheries and Marine Service Department of Fisheries and the Environment Halifax, Nova Scotia B3J 257

I Minister of Supply and Services Canada 1978 Cat. No. Fs 52-2/1978-0091 ISSN 0701-7634

iii CONTENTS LIST OF TABLES.............. v ABSTRACT/RESUME................vii INTRODUCTION......... 1 SCOPE OF OPERATIONS..... 1 METHODS AND PRESENTATION..... 1 RESULTS........ 1 APPENDIX A - ELECTROSEINING DATA (FORM)...... 15 APPENDIX B - ELECTROSEINING CALCULATIONS (FORM) 17 ACKNOWLEDGEMENTS......... 19

v TABLE 1. TABLE 2. LIST OF TABLES Streams and numbers of sites on the Miramichi River system where electroseining operations were conducted, 1969-77 ~. 3 Ca+culated qensiti~s of Atlantic salmqn fry, as determined by electroseining in the Mi~~michi River syste~, 1969-77~ samp+ing sit~s on Main Miramicpi streams... ~.'.. 4 TABLE 3. Calculated densities of Atlantic salmon fry, as determined by electroseining in the Miramichi River system, 1969-77~ sampling sites on Northwest Miramichistreams.. 5 TABLE 4. Calculated densities of Atlantic salmon fry, as determined by electroseining in the Miramichi River system, 19~9-77~ sampling sites on Southwest Miramichi streams... 6 TABLE 5. Calculated densities of Atlantic salmon small parr, as determined by electroseining in the Miramichi River system, 1969-77~ sampling sites on Main Miramichi streams. 7 TABLE 6. TABLE 7. TABLE 8. TABLE 9. TABLE 10. Calculated densities of Atlantic salmon small parr, as determined by electroseining in the Miramichi River system, 1969-77~ sampling sites on Northwest Miramichi streams. 8 Calculated densities of Atlantic salmon small parr, as determined by electroseining in the Miramichi River system, 1969-77; sampling sites on Southwest Miramichi streams. Calculated densities of Atlantic salmon large parr, as determined by electroseining in the Miramichi River system, 1969-77; sampling sites on Main Miramichi streams 10 Calculated densities of Atlantic salmon large parr, as determined by electroseining in the Miramiehi River system, 1969-77; sampling sites on Northwest Miramichi stream 11 Calculated Qensities of Atlantic s-lmon large parr, as d termined by electroseining in the Miramiehi River system, 196g e 77; sampling sites on Southwest Miramichi str ams. 9 12 TABLE 11. Calculated overall mean densities 0 Atlantie salmon juveniles per 83.6 m g (lao yd 2 ), a determined by eleetroseining in the Miramiehi River system, 1969-77; n number of estimate 13

vii ABSTRACT Peppar, J.L. and E.J. Schofield. 1978. Juvenile Atlantic salmon densities, Miramichi River System, New Brunswick, 1969-77. Fish. Mar. Servo Data Rep. No. 91, 27 p. Electroseining operations were conducted throughout the freshwater reaches of the Miramichi River system, New Brunswick, over the period 1969-77, to determine population densities of juvenile Atlantic salmon. This report presents the calculated juvenile densities of all sites sampled. Key words: Atlantic salmon, juvenile salmon densities, electrofishing, Miramichi River system, sampling sites. RESUME Peppar, J.L. and E.J. Schofield. 1978. Juvenile Atlantic salmon densities, Miramichi River System, New Brunswick, 1969-77. Fish. Mar. Servo Data Rep. No. 91, 27 p. Durant les annees 1969 a 1977, on a effectue des operations d'echantillonnage a la p~che electrique couvrant toutes les sections d'eau douce du reseau de la riviere Miramichi au Nouveau-Brunswick. Le fut etait de determiner la densite de la population de jeunes saumons Atlantique. Ce rapport presente les densites calculees de jeunes saumons pour tous les sites echantillonnes. Mots-cles : Saumon Atlantique, densites de la population de jeunes saumons, peche electrique, reseau de la riviere Miramichi, sites echantillonnage.

INTRODUCTION Electroseining operations were conducted throughout the freshwater reaches of the Miramichi River system over the period 1969-77, to determine population densities of juvenile Atlantic salmon. These operations were conducted primarily to determine relative spawning success each year, in relation to increased or decreased escapements of adult salmon to the river system. With this objective in mind, operations each year concentrated on the repetition of sites sampled in previous years, so that consecutive-year comparisons could be drawn. This report summarizes data obtained from these juvenile salmon populationassessment investigations. Calculated juvenile densities (numbers/83.6 m 2 or 100 yd 2 ) are presented for all sites sampled by the electroseining operations. SCOPE OF OPERATIONS The electroseining operations were conducted on a number of selected streams throughout the Miramichi River system (Fig.). Most of the streams studied were inaccessible for much of their length; thus, sampling sites had to be selected in areas of reasonable access by standard vehicles. METHODS AND PRESENTATION OF DATA On each stream, sampling sites with similar physical characteristics were selected. Every attempt was made to select sites possessing all three basic kinds of habitat - pool, run and riffle. Barrier nets were employed to fence off areas in the order of 350 square metres. Each sampling site was fenced off with barriers at its upper and lower boundaries, and on one side as well, if the full width of stream could not be covered. of effort. Generally, five sweeps were made at each sampling site. All salmon taken in a sweep were measured (fork length) and sizes were recorded in a length-frequency table. Sizes recorded in this manner allowed the determination of the numbers of fry (underyearlings), small and large parr (postyearlings), on the basis of the mode distributions obtained. Numbers obtained were then applied to density/unit area calculations (Appendix B). The calculated juvenile densities obtained for all the individual sites over the nine years of sampling are summarized. RESULTS The streams and corresponding numbers of sites where electroseining operations were conducted are summarized (Table 1). The table indicates the location of each stream by specific area within the system (Main Miramichi - streams flowing into the Miramichi estuary or bay; Northwest Miramichi - streams flowing into the Northwest Miramichi River; and Southwest Miramichi - streams flowing into the Southwest Miramichi River), and presents the total area sampled and total number of juvenile salmon obtained each year. Calculated densities of fry, small parr and large parr for each stream and individual site sampled are presented (Tables 2-10). The overall mean densities for the Miramichi River system for each year of sampling are also presented (Table 11). All sites were diagrammed on data sheets (Appendix A) at the time of sampling, indicating their location and their habitat and substrate characteristics. All seining was performed with variable DC electrofishing generators. Two units were employed; a portable Dirigo 500 Electrofisher, and/or a larger unit produced by Nova Scotia Armature Works, Halifax. These units produced 350-750 volts, giving 0.6-2.0 amperes (usually held close to 1.0 ampere), stunning the fish but minimizing actual mortality or injury. In addition to the shocker, an apron seine and dip nets were employed. Estimates of the number of fish within a sample area were obtained by making several uniform coverages. Electroseining was done back and forth across the area while proceeding from the upper to the lower barrier. The elapsed time for the initial "sweep" (complete coverage of an area) was adhered to closely for succeeding sweeps, so that each would approximate a similar unit

_.. = r...,. o 10 20 30 40 Kilometres, I I I, 6 10 2'0 30 Miles N GLOUCESTER COUNTY NORTHUMBERLAND COUNTY LEGEND ~ Electroseining Stations VICTORIA COUNTY YORK COUNTY e...:::...-..."..., ',, Maine : I I I I,, FIG. Electroseining stations, Miramichi River system, New Brunswick.

3 TABLE 1. streams and numbers of sites on the Miramichi River system where electroseining orerations were conducted, 1969-77. Numbers of sites sampled Stream 1969 1970 1971 1972 1973 1974 1975 1976 1977 Hain Miramichi River Baie du Vin River 0 0 2 2 2 2 2 2 2 Black River 1 0 2 2 2 2 2 2 2 Napan River 0 0 2 2 2 2 2 2 2 Burnt Church River 0 0 2 2 2 2 2 2 2 Oyster River 0 3 3 3 3 2 2 2 2 Bartibog River 1 4 4 5 5 5 5 5 5 Northwest Miramichi River Northwest Miramichi River 0 0 0 0 0 12 11 10 11 Tomogonops River 0 0 1 0 1 1 0 0 0 [,ittle River 0 0 1 0 2 2 2 2 2 portage River 0 0 0 1 1 2 2 2 2 Little Sevog1e River 0 3 3 3 3 3 3 3 3 Little Southwest Miramichi River 4 0 4 4 4 4 4 4 4 Sutherland Brook 0 1 1 1 1 1 1 1 1 :~orthwest Millstream 0 3 3 3 3 3 0 0 0 Big Sevogle River 0 0 0 0 0 3 3 3 3 southwest Miramichi River Dungarvon River 0 0 0 0 0 3 3 2 3 Barnaby River 2 0 2 2 2 2 2 2 2 Renous River 0 5 5 4 7 6 6 5 5 Main Southwest Miramichi River 0 14 14 12 14 14 14 10 12 Bartholomew River 2 3 3 3 3 4 0 0 0 Morse Brook 0 2 2 2 2 2 2 2 1 Cains River 4 0 4 4 4 4 4 4 4 Big Hole Brook 0 3 3 3 3 3 3 3 3 Betts Mill Brook 0 2 2 2 2 2 2 2 2 Burntland Brook 0 0 2 2 2 2 2 1 2 Taxis River 0 0 0 3 3 3 3 3 3 MacBean Brook 0 2 2 2 2 2 2 2 2 Rocky Brook 0 3 4 3 3 3 3 2 4 Teague Brook 0 2 2 2 2 2 2 2 2 Totals 14 50 73 72 80 98 89 80 86 Total area sampled (m 2 ) 6,746 14,579 22,698 23,323 25,527 32,207 29,044 26,056 28,644 Total nurcijers of salrron captured 1,163 3,087 3,978 2,478 4,273 9,330 10,631 7,540 11,741

4 TA13t..E 2. Calculated densities of Atlantic salmon fry, as determined by electroseining in the Miramichi River system, 1969-77; sampling sites on Main Miramichi streams. Site Fry density per 100 yd 2 (83.6 m 2 ) Stream number 1969 1970 1971 1972 1973 1974 1975 1976 1977 Baie du Vin River 1 4.8 <1 10.9 6.1 <1 8.1 <1 2 2.0 <1 10.2 <1 13.7 <1 <1 Black River 1 <1 10.4 <1 10.5 7.1 4.1 4.8 5.5 2 <1 <1 <1 <1 <1 <1 1.7 :-Japan River 1 5.7 <1 2.0 <1 15.3 31. 3 <1 2 <1 <1 <1 <1 <1 <1 <1 3urnt Church River 1 <1 <1 <1 2 13.5 <1 1.5 <1 <1 <1 <1 3 3.0 <1 <1 <1 '-)yster River 1 <1 45.3 <1 <1 <1 <1 1.3 31. 2 2 <l 20.8 <1 <1 <1 <1 <1 <1 3 <l <1 <1 <1 3artibog River 1 4.0 3.4 16.4 <1 3.7 6.0 26.7 41. 7. 2.3 2 26.4 17.9 1.1 12.8 8.7 6.0 5.4 1.7 3 <l 16.6 <1 8.2 4.5 13.4 2.6 3.1 4 <l 5.4 <1 9.3 <1 <1 <1 2.9 6 <1 7.4 13.0 8.9 19.9 1.2 Overall mean 2.3 4.6 10.7 0.5 5.0 3.5 6.1 7.7 J.4 Total number of estimates 2 7 15 16 16 15 15 15 15

5 TABLE 3. Calculated densities of Atlantic salmon fry, as determined by e1ectroseining in the Miramichi River system, 1969-77 ; sampling sites on Northwest Miramichi streams. Site Fry density per 100 yd 2 (83.6 m 2 l Stream number 1969 1970 1971 1972 1973 1974 1975 1976 1977 I'omogonops River 10 <1 <1 6.8 11 Little River 3 7.2 7.5 2 65.5 15.9 <1 <1 10.1 12 10.7 <1 <1 12.6 Portage River 1 4.5 22.1 3.2 3.0 32.6 34.9 8 1.6 <1 <1 5.8 Little Sevogle River 1 13.9 13.5 2.4 19.6 <1 49.8 10.9 41.4 2 <1 8.4 <1 4.6 <1 24.7 2.7 17.6 3 <1 <1 <1 11.8 1.2 22.0 3.6 26.8 Little Southwest 1 <1 3.8 3.3 1.3 <1 28.9 11.0 14.2 Miramichi River 3 <1 <1 4.3 2.9 19.6 10.2 8.6 4.4 4 2.8 9.5 <1 30.5 <1 <1 1.7 90.5 6 <1 18.5 4.2 23.8 12.8 30.3 9.1 31.5 Sutherland Brook 1 7.7 <1 13.1 28.8 70.5 <1 <1 38.7 Northwest Millstream 1 <1 <1 <1 20.6 <1 2 <1 <1 <1 <1 <1 3 <1 <1 <1 <1 <1 Big Sevog1e River 1 29.7 42.0 14.5 39.1 2 37.6 30.9 6.5 44.3 3 25.9 36.2 35.3 21. 7 \ r Northwest Miramichi 2 15.2 47.0 20.7 River 3 3.2 4 10.6 <1 1.9 <1 5 4.7 <1 4.6 11.2 7 <1 <1 2.7 4.0 9A 6.8 38.2 6.2 1.7 9B <1 1.1 7.7 1.8 13 20.7 24.8 28.6 31.9 14 12.3 15 9.9 21.6 30.1 20.0 17 8.0 54.3 14.2 18 101.1 7.5 13.0 18.6 19 43.2 80.7 106.0 28.7 Overall mean 1.1 3.4 4.9 2.9 16.0 14.9 20.2 15.4 22.6 Total number of estimates 4 7 13 12 15 31 26 25 26

t, TABLE 4. Calculated densities of Atlantic salmon fry, as determined by electroseining in the Miramichi River system, 1969-77; sampling sites on Southwest Miramichi streams. Site Fry density per 100 yd 2 (83.6 m 2 ) Stream number 1969 1970 1971 1972 1973 1974 1975 1976 1977 Dungarvon River 1 29.71 42.0 52.2 2 37.6 30.9 20.1 36.4 3 25.9 36.2 8.2 38.8 Barnaby River 1 1.6 2.7 <1 10.8 <1 3.4 <1 <1 2 6.9 7.5 <1 13.6 <1 1.7 <1 2.4 '<enous River 1 <1 7.8 2.2 2 2.9 2.9 2.5 2.0 22.0 3.2 16.4 15.7 3 6.3 11.7 15.9 6.8 40.7 4 <1 24.8 19.0 26.0 5 15.3 13.9 11. 0 13.2 65.0 65.5 92.3 82.8 6 4.0 9.2 11. 3 14.0 7 <1 3.2 64.7 30.0 4.6 32.5 8 19.5 29.4 25.7 23.1 30.2 Main Southwest 7 9.5 10.7 1.1 7.3 47.4 16.2 158.8 Miramichi River 4 6.6 2.5 1.9 14.8 15.0 32.9 52.0 10 3.3 1.3 <1 <1 <1 7.3 20.1 14 23.9 37.0 18.4 60.0 42.3 2.8 41.4 11 19.2 29.7 <1 18.0 34.7 20.2 21.3 37.8 6 13.9 13.0 9.4 32.1 43.1 49.5 12.2 5 15.0 14.5 1.6 1.9 1.1 38.2 21. 7 9.8 13 53.2 19.1 5.3 5.1 51.0 71.2 46.5 23.0 1 19.8 33.6 2.5 40.1 27.0 41.6 49.8 2 8.6 8.6 2.1 8.2 24.6 57.2 12.2 6.1 3 <1 19.3 4.6 19.9 50.0 70.4 9 20.1 7.6 8.3 30.1 50.7 27.6 <1 1.3 12 7.7 2.0 1.4 3.4 1.8 <1 34.9 64.1 8 4.9 6.8 2.0 22.0 19.7 34.2 24.0 33.3 Bartholomew River 1 <1 1.7 <1 <1 15.1 21.6 2 <1 1.1 1.9 <1 6.3 13.1 3 <1 4 <1 <1 14.2 <1 6 <1 ~'lorse Brook 1 <1 9.6 <1 27.0 <1 24.0 <1 <1 2 <1 <1 <1 <1 <1 <1 <1 Cains River 3 24.8 22.0 45.9 39.0 12.0 27.7 4 25.1 11. 6 7.7 4.8 42.9 37.2 23.2 56.0 6 7.9 6.1 7.3 10.2 16.3 243.1 81. 5 31. 9 7 1.5 52.0 8 19.8 10.5 3.9 26.9 32.7 43.0 20.3 69.6 Big Hole Brook 1 19.9 16.3 3.9 15.2 33.1 28.0 55.2 22.9 I" 2 <1 <1 <1 <1 <1 1.0 <1 <1 3 <1 4.4 <1 <1 <1 <1 <1 <1 Betts Mill Brook 1 52.0 33.3 14.5 89.5 12.2 14.0 11.3 45.7 2 <1 11.6 <1 <1 <1 6.1 2.9 8.7 Burntland Brook 1 32.0 5.7 8.8 85.4 94.2 41. 3 127.9 2 17.0 <1 7.8 5.3 6.9 32.3 Taxis River 1 <1 6.9 30.8 20.4 23.7 29.4 2 7.1 3.5 25.8 66.7 45.3 46.0 3 2.6 31. 9 67.1 34.1 47.3 68.9 MacBean Brook 1 9.9 25.1 2.4 12.7 23.1 10.2 32.3 83.4 2 3.4 71.0 <1 56.3 1.0 <1 1.4 95.6 Rocky Brook 1 3.4 25.6 20.0 3.2 34.7 49.5 39.7 2 129.8 43.1 47.0 49.5 65.5 92.5 51.1 69.4 3 <1 <1 38.5 4 45.6 50.8 66.6 25.5 55.1 138.5 49.6 Teague Brook 1 5.2 8.9 <1 7.6 10.2 50.0 19.5 45.2 2 7.1 2.0 <1 15.8 2.3 6.2 <1 31. 8 Overall mean 8.0 13.0 15.3 6.3 16.3 25.5 36.7 24.8 40.6 Total number of estimates 8 36 45 44 49 52 48 40 45

7 TABLE 5. Calculated densities of Atlantic salmon small parr, as determined by electroseining in the Miramichi River system, 1969-77; sampling sites on Main Miramichi streams. Si.te Small-parr density per 100 vd 2 (83.6 m 2 ) Stream number 1969 1970 1971 1972 1973 197-4 1975 1976 1977 Baie du Vin River 1 1.6 <1 <1 5.9 <1 <1 <1 2 1.2 2.0 <1 <1 <1 1.7 <1 Black River 1 2.1 <1 <1 <1 1.7 2.7 2.5 1.1 2 <1 <1 <1 <1 <1 <1 1.7 Napan River 1 <1 1.4 <1 <1 <1 <1 <1 2 <1 1.0 <1 <1 <1 <1 <1 Burnt Church River 1 <1 <1 <1 2 <1 1.3 <1 <1 <1 <1 <1 3 4.6 1.9 1.5 <1 Oyster River 1 <1 <1 3.1 <1 <1 <:1 <1 <1 2 <1 <1 3.4 <1 <1 <1 <1 <1 3 <1 <1 <1 <1 Bartibog River 1 16.4 6.7 9.6 4.7 <1 7.5 4.4 <1 16.8 2 <1 <1 <1 <1 <1 <1 16.2 6.4 3 4.8 2.9 2.4 <1 53.7 1.7 9.4 1.7 4 7.7 5.9 4.0 <1 <1 20.3 9.7 2.3 6 <1 <1 6.3 4.4 16.4 2.7 Overall mean 9.3 3.0 1.7 1.7 0.5 5.6 2.7 3.9 2.3 Total number of estimates 2 7 15 16 16 15 15 +5 15

8 TABLE 6. Calculated densities of Atlantic salmon small parr, as determined by electroseining in the Miramichi River system, 1969-77 ; sampling sites on Northwest Miramichi qiver. Site Small-parr density per 100 yd 2. (83.6 m 2 ) ;tream number 1969 1970 1971 1972 1973 1974 1975 1976 1977 ~omogonops River 10 <1 <1 <1 11 Little River 3 <1 <1 2 <1 19.1 8.3 24.8 5.7 12 4.7 19.2 3.5 17.9 'ortage River 1 <1 <1 2.6 <1 57.4 4.6 8 9.2 <1 4.3 10.0,ittle Sevog :;'e River 1 8.2 7.8 6.0 4.9 2.5 44.2 4.4 5.2 2 2.7 <1 1.7 <1 1.7 1.2 2.7 1.4 3 1.7 2.7 2.1 <1 5.6 2.2 2.9 5.0 ~ittle southwest 1 10.2 <1 <1 <1 <1 6.1 <1 1.1 Miramichi River 3 13.5 6.5 4.8 1.0 6.5 14.6 8.0 <1 4 42.2 <1 3.4 <1 28.0 1.2 3.4 2.6 6 1.0 1.7 <1 2.5 <1 <1 <1 <1 :utherland Brook 1 8.6 9.1 5.1 5.2 23.8 36.6 36.6 21.7 :' orthwest Millstream 1 14.0 5.4 1.1 2.7 17.6 2 <1 <1 <1 <1 9.7 3 <1 <1 <1 <1 <1 3ig Sevogle River 1 2.6 3.1 1.7 1.0 2 40.5 17.0 18.8 9.8 3 28.5 12.7 9.6 14.8 ';orthwest Miramichi 2 3.6 <1 <1 River 3 <1 4 <1 <1 7.6 <1 5 2.6 <1 <1 <1 7 <1 3.5 <1 25.1 9A 1.6 11.3 5.5 3.5 9B <1 4.3 8.4 2.0 13 14.8 15.1 20.6 24.3 14 15.8 15 24.5 23.1 42.0 37.3 17 25.7 18.0 36.3 18 26.4 16.2 3.6 18.9 19 42.9 30.1 50.7 49.1 1verall mean 16.7 5.2 2.8 2.2 1.4 11. 6 11. 3 12.7 11.5 Total number of estimates 4 7 13 12 15 31 26 25 26

TABLE 7. Calculated densities of Atlantic salmon small parr, as determined by electroseining in the Miram:(.chi River system, 1969-77; sampling sites on Southwest Miramichi streams. Site Small-parr density per 100 yd 2 (83.6 m 2 ) stream number 1969 1970 1971 1972 1973 1974 1975 1976 1977 Dungarvon River 1 6.8 8.8 6.3 2 1.1 3.9 <1 2.7 3 4.8 3.2 68.8 1.1 Barnaby River 1 1.3 <1 <1 <1 <1 <l <1 <1 2 <1 <1 6.1 <l <1 <l 2.0 <1 Renous River 1 <1 <1 <1 <1 2 1.8 6.1 2.3 3.1 1.3 15.5 6.9 8.1 3 1.8 <1 1.7 1.2 1.7 6.8 1.2 4.5 4 1.2 5 1.8 1.4 <1 1.8 7.7 6.0 2.1 2.9 6 1.4 1.5 7.2 7 2.7 <1 <1 1.0 1.1 3.6 8 4.1 5.1 13.9 9.7 10.4 :1ain Southwest 7 <1 <1 <l <1 <1 1l.8 14.1 Miramichi River 4 <1 <1 <1 <1 <1 2.6 16.5 10 <1 <1 <1 <1 <1 <1 4.5 14 2.8 6.3 <1 <1 2.3 <1 3.4 II <1 <1 <1 <1 <1 4.2 5.1 2.7 6 1.3 26.6 1.5 <1 3.4 15.1 1.1 5 5.9 3.4 <1 <1 <1 1.1 1.3 <1 13 4.0 3.2 6.8 <1 <1 1.3 6.8 11. 7 1 1.5 9.4 5.2 3.7 17.4 24.1 8.9 2 3.3 7.8 5.6 1.7 14.2 41.6 <l <1 3 <1 1.1 2.8 <l 2.4 217.5 9 1.2 3.5 9.4 2.0 13.9 11.1 <1 <1 12 <1 <1 <1 <1 <1 <l 2.8 <1 8 2.6 <1 1.1 2.9 7.4 6.4 1.1 <1 Bartholomew River 1 2.3 <1 <1 <1 <1 <1 2 1.4 <1 <1 <1 <1 <1 3 7.0 <1 <1 <1 4 <1 <1 <1 3.8 6 27.7 Morse Brook 1 <1 11.0 8.3 1.7 <1 7.1 7.5 <1 2 <1 <1 <1 <1 <1 <1 <1 Cains River 3 38.6 <1 10.9 2.0 24.8 9.2 4 17.3 <1 <1 <1 3.2 2.8 1.6 <1 6 14.5 1.2 <1 <1 3.9 6.4 3.8 1.1 7 14.7 3.2 8 17.5 1.9 4.8 1.2 7.5 9.9 14.6 4.2 Big Hole Brook 1 4.9 7.2 4.0 2.0 <1 6.7 5.2 3.9 2 <1 <1 <1 <1 <1 1.9 <1 <1 3 <1 <1 <1 <1 <1 <1 <1 <1 Betts Mill Brook 1 2.2 5.0 8.0 2.0 1.2 14.5 22.2 11.6 2 <1 <1 2.8 <1 3.0 6.8 6.8 1.1 Burntland Brook 1 6.4 6.0 <1 13.4 31. 6 22.7 11.1 2 10.4 8.9 1.8 24.0 26.3 23.8 Taxis River 1 6.1 3.2 4.4 10.0 13.0 13.2 2 11.7 5.7 3.0 27.0 22.3 19.5 3 9.1 3.8 25.7 28.7 28.2 20.5 MacBean Brook 1 1.4 5.9 9.0 1.4 6.2 24.1 10.9 17.9 2 1.9 12.5 16.4 2.2 24.6 8.8 18.8 23.1 Rocky Brook 1 10.8 45.0 23.9 5.7 30.1 60.9 42.2 2 7.8 36.8 14.0 22.4 30.3 31.9 22.6 39.8 3 <1 <1 1.7 4 37.4 5.5 8.5 7.3 25.6 22.7 21.4 Teague Brook 1 2.7 7.4 1.3 <l 21.1 17.4 7.2 9.9 2 <1 3.7 2.6 2.5 15.8 3.9 28.5 4.9 Overall mean 8.7 2.1 6.1 5.3 2.9 7.0 15.6 10.3 8.5 Total number of estimates 8 36 45 44 49 52 48 40 45

I 10 TABLE 8. Calculated densities of Atlantic salmon large parr, as determined by electroseining in the Miramichi River system, 1969-77; sampling sites on Main Miramichi streams. Site Large-parr density per 100 yd 2 (83.6 m 2 ) Stream number 1969 1970 1971 1972 1973 1974 1975 1976 1977 Baie du Vin River 1 <1 1.2 <1 2.2 <1 <1 5.1 2 1.1 2.3 <1 1.9 <1 5.7 <1 Black River 1 6.2 1.3 <1 <1 1.5 2.5 5.2 1.6 2 <1 <1 <1 <1 <1 <1 <1 '~apan River 1 <1 <1 <1 <1 <1 4.2 10.9 2 <1 <1 <1 <1 <1 4.2 5.8 Burnt Church River 1 <1 <1 <1 2 3.9 5.0 <1 6.2 :.:;1 1.1 <1 3 <1 <1 1.9 <1 Oyster River 1 <1 <1 1.5 2.1 <1 <1 <1 1.4 2 <1 <1 <1 <1 <1 <1 <1 <1 3 <1 <1 <1 <1 Bartibog River 1 1.4 6.7 2.1 <1 <1 <1 1.9 3.4 <:1 2 <1 <1 1.6 <1 <1 <:1 3.2 1.4 3 <1 <1 <1 <1 <1 <1 <1 <1 4 2.3 2.8 1.5 1.9 5.2 3.7 2.3 1.4 6 <1 <1 <1 1.5 2.1 <1 Overall mean 3.8 1.6 1.1 1.1 0.7 1.5 1.0 2.3 1.9 Total number of estimates 2 7 15 16 16 15 15 15 15

11 I'ABLE 9. Calculated densities of Atlantic salmon large parr, as determined by electroseining in the Miramichi River system, 1969~77i sampling sites on Northwest Miramichi streams. Site Large-parr density per 100 yd 2 (83.6 m 2 ) Stream number 1969 1970 1971 1972 1973 1974 1975 1976 1977 Tomogonops River 10 <1 <1 <1 11 Little River 3 1.8 1.5 2 1.2 <1 <1 3.6 4.7 12 <1 <1 2.5 6.2 ])ortage River 1 <1 <1 <1 <1 1.2 <1 8 1.8 <1 <1 1.2 Little Sevogle River 1 7.4 1.9 1.1 3.0 <1 1.9 <1 3.1 2 5.0 1.6 <1 <1 <1 <1 <1 1.3 3 4.1 2.1 1.2 <1 1.4 1.2 1.3 1.4 Little Southwest 1 <1 <1 <1 <1 <1 <1 <1 <1 Miramichi River 3 1.3 <1 4.7 <1 <1 1.7 1.1 <1 4 1.1 4.1 3.5 <1 <1 10.3 1.4 6 <1 <1 <1 <1 <1 <1 <1 3.0 <1 Sutherland Brook 1 14.3 4.2 3.5 2.1 2.4 25.5 20.1 15.7 Northwest Millstream 1 3.8 8.3 1.4 1.7 <1 2 <1 <1 <1 <1 <1 3 <1 <1 <1 <1 <1 Big Sevogle River 1 <1 <1 <1 <1 2 5.0 6.3 6.6 6.9 3 9.6 7.2 8.1 1.8 Northwest Miramichi 2 <1 <1 <1 River 3 <1 4 <1 <1 <1 <1 5 <1 <1 <1 <1 7 <1 <1 <1 <1 9A <1 1.3 1.1 <1 9B <1 <1 7.0 <1 13 <1 2.3 3.1 4.2 14 3.6 15 <1 10.3 7.2 18.7 17 <1 13.3 14.0 18 <1 6.5 <1 1.4 19 2.4 8.1 8.9 7.9 Overall mean <1 5.1 2.0 1.5 1.0 1.2 3.6 3.1 3.7 Total number of estimates 4 7 13 12 15 31 26 25 26

12 TABLE 10. Calculated densities of Atlantic salmon large parr, as determined by electroseining in the Miramichi River system, 1969-77 ; sampling sites on Southwest Miramichi streams. Site Large-parr density per 100 yd 2 (83.6 m 2 ) Stream number 1969 1970 1971 1972 1973 1974 1975 1976 1977 Dungarvon River 1 <1 2.6 3.1 2 <1 <1 <1 <1 3 <1 <1 <1 <1 Barnaby River 1 <1 <1 2.2 <1 3.9 <1 <1 <1 2 <1 <1 3.4 <1 9.9 3.4 2.4 3.1 Renous River 1 4.0 <1 <1 2 6.6 2.6 1.5 <1 <1 1.9 <1 <1 3 1.2 <1 <1 <1 <1 <1 <1 <1 4 3.8 5 1.1 <1 <1 <1 <1 <1 <1 1.6 6 <1 <1 <1 <1 7 <1 <1 <1 <1 <1 1.4 8 1.5 <1 1.5 1.2 5.5 Main Southwest 7 1.0 <1 <1 <1 <1 <1 2.6 5.0 Miramichi River 4 3.2 <1 <1 1.7 10.5 1.0 2.0 10 <1 <1 <1 <1 <1 <1 <1 14 1.9 <1 <1 <1 <1 <1 <1 11 <1 <1 <1 <1 <1 <1 <1 <1 6 2.8 <1 <1 <1 <1 2.5 <1 5 3.4 4.0 <1 <1 <1 <1 <1 <1 13 8.2 3.5 6.6 <1 <1 <1 1.5 <1 1 1.5 <1 1.9 <1 <1 7.6 1.3 2 8.9 2.4 2.0 <1 1.7 7.4 <1 <1 3 <1 <1 <1 <1 <1 2.0 9 2.3 1.9 1.6 <1 <1 3.2 <1 <1 12 <1 <1 <1 <1 <1 <1 <1 <1 8 2.3 <1 1.7 1.1 <1 <1 <1 <1 Bartholomew River 1 5.1 <1 <1 <1 <1 <1 2 2.5 <1 <1 <1 <1 2.7 3 2.5 4 <1 <1 <1 <1 6 <1 Morse Brook 1 15.3 1.8 2.0 2.6 8.9 3.8 6.7 8.6 2 <1 <1 <1 <1 <1 <1 <1 Cains River 3 16.2 <1 <1 <1 <1 <1 4 1.2 <1 <1 <1 <1 1.1 <1 <1 I. 6 5.3 <1 1.4 <1 <1 7.6 <1 <1 [ 7 4.8 <1 I 8 <1 3.9 <1 6.4 1.6 7.6 3.5 Big Hole Brook 1 7.6 5.8 <1 <1 2.1 8.2 2.0 3.7 2 5.1 <1 <1 <1 <1 <1 <1 <1 3 <1 <1 <1 <1 <1 1.9 2.2 <1 Betts Mill Brook 1 10.2 1.3 1.1 3.3 21.0 1.1 3.4 1.4 2 <1 <1 3.3 <1 1.8 1.2 1.6 1.8 Burntland Brook 1 4.2 4.3 <1 8.1 5.6 18.1 14.6 2 6.7 5.0 <1 3.2 8.1 2.4 Taxis River 1 1.1 4.2 1.2 2.1 6.5 3.9 2 3.7 37.2 <1 2.6 9.9 5.1 3 <1 4.7 1.1 7.7 8.9 6.5 MacBean Brook 1 12.0 6.8 <1 4.0 3.2 8.7 5.7 14.7 2 16.3 5.9 1.3 4.4 <1 10.5 13.9 9.2 Rocky Brook 1 12.8 12.7 13.2 1.9 6.8 30.6 28.7 2 2.3 2.5 7.2 8.7 1.0 <1 5.3 14.1 3 <1 <1 <1 4 1.7 <1 <1 <1 6.6 2.2 6.6 Teague Brook 1 7.6 <1 <1 <1 3.7 7.4 3.8 3.1 2 2.4 <1 2.2 2.4 9.7 9.2 4.0 11.4 Overall mean 2.8 4.2 1.8 2.2 2.0 2.2 3.5 2.9 3.7

13 TABLE 11. Calculated overall mean densities of Atlantic salmon juveniles per 83.6 m 2 (100 jd 2), as determined by electroseining in the Miramichi River system, 1969-77; n = number of estimates. Fry Small parr Large parr {ear n range mean n range mean n range mean 1969 14 <1-25.1 5.2 14 <1-42.2 11.6 13 <1-6.2 2.4 1.970 50 <1-129.8 10.5 50 <1-14.0 2.7 50 <1-16.3 4.0 ~971 73 <1-71.0 12.5 73 <1-45.0 4.6 73 <1-12.5 1.7 L97 2 72 <1-50.8 4.4 72 <1-38.6 4.0 72 <1-16.2 1.9 1973 80 <1-89.5 14.0 80 <1-22.4 1.6 80 <1-37.2 1.5 1974 98 <1-101.1 18.8 98 <1-53.7 8.3 98 <1-21.0 1.9 1975 89 <1-243.1 26.4 89 <1-217.5 12.2 89 <1-30.6 3.2 1976 80 <1-138.5 18.6 80 <1-68.8 9.8 80 <1-20.1 2.8 1977 86 <1-158.5 28.7 86 <1-49.1 8.3 86 <1-28.7 3.4 Jveral1 642 <1-243.1 15.4 642 <1-217.5 7.0 641 <1-37.2 2.5

i' l

APPENDIX A. (810-15 ) C RESOURCE DEVELOPMENT - BRANCH ) ( A- ) (SYSTE~ SWEEP#: 8 TIME SPECIES ( ELEC ATA ) )etion 15 ) (RECORDER ) (DATE ) I I 21 31 41 51 61 MIN. MIN, MIN MIN MIN MIN TOTALj I I I SPECIES -r- I I C T()T - SI'l:.CIES T('TALC _._- 1-. ';IJLCIES I I I I I I I I 1- L- [--.- -.. r---'- L---...._... -..[~~ ' --_:~~~. I I ~jl'~ \...ll5 TriTf.L I' SPl:.CIE:.S 4 1 _-- -- -~-- i.j..._ I I.l_.~~..... L ~._-_.. _[~' - rc,tf L _L_ 1-..,ITl::iFS ~--..[-- 1. --_._[--. L r-' - ".- -- --.. " _11'~f'I..L.. [------ J_. c-..._-- r. I I ---- I --.. I.- ')'I.t.IL J I I TOTAL r- '..'- I 1'-' I I \'-' r--- THIS SHU.:T TO BE USED ONLY WHEN CATCH/EFFORT 0ALCULATIONS WISH TO' BE MADE - NOT SUITABLE FOR SCHNABEL METHOD. CALCULATIONS FOUND ('IN BIO -- 11i-- I

(BI0-15 ) C RESOURCE DEVELOPMENT BRANCH ) (_s- l LENGTHS WIDTHS RATEofFLCM DEPTHS lin INCHES) LEFT HANK LR. BARRIER I UPPER BARRIER -l-. -!-' 0 I 2 f------. -...- f--. 3 0 i: 4 0 : f- RIGHT RANK UP. BARRIER AVERAGE X AVERAGE LOWER BARRIER MAXIMUM DEPTH IN. l- i- 0 0 =1= ~~ n ( lil IN) *' TO~AL i SKETCH ond/or NOTES pools I % ri Hie I bottom type, cover. bonks. CREW 1-- _----------------1 ~..._.. PROAE ---._._--_._-- [)IP...---..-----1 AIR H 2 0 TEMPERATURE TEMPERATURE.----_..._-----+---_._---1 ph 1---- ------+--------1 SPECIFIC CONDo...----.--- ~...-----i--------- WEATHER f---.------1---------1 ~ARRIERS USED 2 4 MACHINE VOLTS LOAD AMPS 5 I--~--...-f-- ----- 6 [ REMARKS ~)

17 l\.ppendix B ( B10-16 ) ( RESOURCE DEVELOPMENT BRANCH ) (A-) (ELECTRO C LCULATIONS ) (STREA~ ) (STATION ) (DATE ) SPECIES SPE~ES n U :iu= X UX n o o 0 W WI- W <l: > ~~ ~~~gs~ <l:~ <l: <l: W ::e <l: :a a: Zu ~ ~U= U X UX 2 3 4 4 5 5 6 (n) ~u, ~U ~X 6 XI 2 1_(::;: i :?:U 2 i :ix 2 I i ~UX _1_::eL.Q;X J A = n:eux - ~U~X B = n ~X2 - ( :i X)2 'k' = -AlB I I < C.-----J (~ C ) A ESTIMATE DENSITY I A kn = (:EU + k ~X) ACTUAL CATCH I n POPULATION ESTIMATE = ~U SQ. YD. ( ( c ) ) ) F-6450

C810-16 ) CRESOURCE DEVELOPMENT BRANCH) CB- ) SPECIES SPECIES ~ n 0 U./~ 0 <1 W :>':J: W wll:> 11:<.:> l<: <1:.) 11: 0 0 II: ~<1 <1. <1 ~ ZU ~ II: => :tu= n U X U 2 X 2 UX I 2...._-- "'- _..._---- 3 f-. -_. --1------ 4 ~.._- 5 _. - --- - -..._-- t----. 6 t----t---- -1-- ----- :z 0 0 o w ~~ w~li:~ CI:<.:> :>O:II:O::!E <1=> 1I:<t W 2«~ cr 2u => :;;EU= n U )( U 2 X 2 UX I 2,3 4 5 6 - -- --t-----.. _.. _._- -- --- --r-- n) ~U ~x :ieu 2 ~X2 ~UX (0) ~U ~X ~U2 ~X2 :EUX eu,' I,,,,' I~u~x ] l~u,' [(>X)' I~~, J ---- A = n:eux ~u~x B 2.. n~x - (~X)2 'i( = -AlB A ~N :: (:EU + It~X ) In A ( ) 'N' :: ~/k' ( ) POPULATION ESTIMATE ( ) ACTUAL CATCH :; :leu ( ) ( ) ESTIMATE DENSlTY I SQ. YD. C ) 1 HIS SHEET CAN 8E USED ONLY WHEN CATCH -EFFORT CALCULATIONS WISH TO BE Mt.Dl - NOT SUI TABLE CALCULATOR FOR SCHNABEL METHOD_ BASIC DATA IS FROM B10-15 ) NOTES

19 ACKNOWLEDGEMENTS The authors are pleased to express their gratitude to P.R. Pickard, Biological Technician, who was responsible for the supervision of field staff and the collection and compilation of data during several years of these investigations.

,.!