Departmenr of Zoology, Erindale College, University of Toronto, Mississauga, Ont., Canada L5L lc6 Received March 9, 1978

Similar documents
LIFE CYCLE AND COMMUNITY STRUCTURE OF CADDISFLIES (INSECTA:TRICHOPTERA) IN THE NAVASOTA RIVER, TEXAS.

The influence of current velocity and substrate on the distribution and drift of two species of mayflies (Ephemeroptera)

THE BIOLOGY OF THE PRAWN, PALAEMON

Brook Trout Life Cycle and Habitat

STUDIES OF EPHEMEROPTERA IN THE AUCKLAND AREA. by J. A. McLean * I: LIGHT TRAPPING IN CASCADE KAURI PARK INTRODUCTION

Job 1. Title: Estimate abundance of juvenile trout and salmon.

A New Species of Caenis Stephens (Ephemeroptera: Caenidae) from Taiwan

Positioning changes of mayfly nymphs due to behavioral regulation of oxygen consumption

STREAM DRIFT. Much variation among taxa: Fraction of benthos drifting: Distance drifted? at any moment? over 24 hr period?

FISHERIES BLUE MOUNTAINS ADAPTATION PARTNERSHIP

FEEDING HABITS OF THE PREDACEOUS NYMPHS OF DOLANIA AMERICANA IN NORTHWESTERN FLORIDA (EPHEMEROPTERA : BEHNINGIIDAE)

J. Great Lakes Res. 16(1): Internat. Assoc. Great Lakes Res., 1990

Discussion on the Selection of the Recommended Fish Passage Design Discharge

Relationships between size of stream insects and current velocity

Aquatic Macroinvertebrate ID

Comparison of the reproductive ability of varroa mites in worker and drone brood of Africanized Honey Bees

SEX RATIOS OF TWO SPECIES OF SPIDER CRABS, LIBINIA DUBIA H. MILNE EDWARDS, 1834 AND L. EMARGINATA LEACH, 1815, IN THE AREA OF GREAT BAY, NEW JERSEY

Jason Blackburn, Paul Hvenegaard, Dave Jackson, Tyler Johns, Chad Judd, Scott Seward and Juanna Thompson

Fraser River. FISH SURVEY AND MANAGEMENT INFORMATION Jon Ewert - Aquatic Biologist (Hot Sulphur Springs)

Contribution to the morphology of the third-instar larvae of Laccophilus poecilus KLUG (Coleoptera: Dytiscidae)

RIVER CONONISH INVERTEBRATE SURVEY Dr Kjersti Birkeland

SEA GRANT PROGRESS REPORT

Tweed Trout & Grayling Initiative. Invertebrate Guide

OBSERVATIONS ON SOME ASPECTS OF BIOLOGY OF JOHNIUS (JOHNIEOPS) VOGLERI (BLEEKER) AND PENNAHIA MACROPHTHALMUS (BLEEKER) IN THE KAKINADA REGION

Salmon age and size at maturity: Patterns and processes

2015 Winnebago System Walleye Report

Drunella karia n. sp. a second species of the genus Drunella (Ephemeroptera, Ephemerellidae), from Turkey

Alberta Conservation Association 2011/12 Project Summary Report. Project Name: Walleye Stock Assessment Program 2011/12 Moose and Fawcett Lakes

STUDY PERFORMANCE REPORT

Big Spring Creek Habitat Enhancement and Fishery Management Plans

Mayflies. Ecdyonurus dispar

THE STATUS THE OCEAN SHRIMP RESOURCE

An Annotated and Illustrated Key to Multistage Larvae of Ohio Salamanders

MORPHOMETRIC CHARACTERISTICS OF EUROPEAN GRAYLING ( YMALLUS THYMALLUS L.) IN TRANSCARPATHIAN RIVERS A. I. KUCHERUK 1 A. I. MRUK 1 V. O.

Stoneflies. Isoperla grammatica

Juvenile Steelhead and Stream Habitat Conditions Steelhead and Coho Salmon Life History Prepared by: DW ALLEY & Associates, Fishery Consultant

Fishery, biology and stock assessment of Cynoglossus macrostomus (Norman) off Malabar coast

Callinectes sapidus (blue crab) Guide

Check List 2006: 3(1) ISSN: X LISTS OF SPECIES

HADDOCK ON THE SOUTHERN SCOTIAN SHELF AND IN THE BAY OF FUNDY (DIV. 4X/5Y)

ACUTE TEMPERATURE TOLERANCE OF JUVENILE CHINOOK SALMON FROM THE MOKELUMNE RIVER

Cross-Vane Plan View FIN-UP Habitat Consultants, Inc. 220 Illinois Avenue Manitou Springs, CO (719) P.

Factors Affecting the Reproduction of Bluegill Bream and Largemouth Black Bass in Ponds

Water Quality in the River Test at Leckford

.Conservation of the Fisheries of Lakes Victoria, Kyoga and Nabugabo

A COMPARATIVE ECOLOGICAL STUDY OF THREE STREAM FAUNAS IN THE AUCKLAND AREA. by J.A. McLean

Lewis River Bull Trout Habitat Restoration Project Identification Assessment

Size and spatial distribution of the blue shark, Prionace glauca, caught by Taiwanese large-scale. longline fishery in the North Pacific Ocean

Student Handout #2 Using Abiotic and Biotic Parameters to Monitor Water Quality: A Field Experiment

Life history and ecology of Megarcys signata (Plecoptera: Perlodidae), Mill Creek, Wasatch Mountains, Utah

Nest Substrates and Spawning Time of Etheostoma crossopterum in Southern Illinois

Notebooks or journals for drawing and taking notes

SCHOOLING BEHAVIOR OF HAEMULON SPP. IN BERMUDA REEFS AND SEAGRASS BEDS

STUDY PERFORMANCE REPORT

Blue-tipped Dancer. Summary. Protection Not listed in New York State, not listed federally.

Taxonomy. An Introduction to the Taxonomy and Ecology of EPT Families

Striped Bass and White Hybrid (x) Striped Bass Management and Fishing in Pennsylvania

AGE AND GROWTH OF THE WALLEYE, STIZOSTEDION VITREUM VITREUM, IN HOOVER RESERVOIR, OHIO 1-2

The fry patterns in the South American catfish genus Corydoras. Ian Fuller

SUMMARY OF MOVEMENT AND HABITAT USED BY TAGGED BROOK TROUT IN THE MAIN BRANCH AND NORTH BRANCH AU SABLE RIVER DURING SUMMER Data Submitted to:

Zooplankton community changes on the Canadian northwest Atlantic continental shelves during recent warm years

STREAM Girls field notebook

Wenatchee Spring Chinook Relative Reproductive Success Study. Andrew Murdoch (WDFW) Michael Ford (NOAA) Michael Hughes (WDFW)

The Life History of Triturus v. vittatus (Urodela) in Various Habitats

Manual of Fisheries Survey Methods II: with periodic updates. Chapter 22: Guidelines for Sampling Warmwater Rivers with Rotenone

Final Bull Trout Genetics Monitoring Plan for the Wallowa Falls Hydroelectric Project. (FERC No. P-308) June 2017

The Effects of Body Mass and Water Submersion on Decomposition Rates in Mice and Rats

Monitoring of Downstream Fish Passage at Cougar Dam in the South Fork McKenzie River, Oregon February 8, By Greg A.

Trout predation and the size composition of stream drift

DROPLETS FROM THE PLANKTON NET. XXI Title.

Evolution by Natural Selection 1

niche requirements, interspecific

Research Background: Name

Eastern Brook Trout Joint Venture Annual Report The Nature Conservancy 2013

CHAPTER 4. EPHEMEROPTERA (Mayflies)

NATIONAL BIORESOURCE DEVELOPMENT BOARD Dept. of Biotechnology Government of India, New Delhi

ELECTRO-FISHING REPORT 2016 UPPER TWEED

Caribou herd dynamics: impact of climate change on traditional and sport harvesting

2008 WMU 360 moose, white tailed deer and mule deer. Section Authors: Robb Stavne, Dave Stepnisky and Mark Heckbert

ADULT SALMONID SPAWNING MIGRATION

Hair Shedding Scores Relating to Maternal Traits and Productivity in Beef Cattle. An Undergraduate Honors Thesis in the. Animal Science Department

Preferential habitat and spatial distribution of 3. species of sicydiine gobies (Genus Sicydium) based. on substrate and flow rate within the

Monitoring of sea trout post-smolts, 2012

Life history patterns: many solutions to the same problem

This paper not to be cited without prior reference to the author. Relationships of Smolt Size and Age With Age at First Maturity in Atlantic Salmon

Chinook salmon (photo by Roger Tabor)

Fish monitoring requirements of new FERC licenses: are they adequate?

NATIONAL BIORESOURCE DEVELOPMENT BOARD Dept. of Biotechnology Government of India, New Delhi

Hester-Dendy Sampling Method Leaf Bag Sampling Method D-Net Sampling Method

Understanding the Impacts of Culvert Performance on Stream Health

Relative Size Selectivity of Trap Nets for Eight Species of Fish'

Fish Conservation and Management

NATIONAL BIORESOURCE DEVELOPMENT BOARD Dept. of Biotechnology Government of India, New Delhi

Notes on the Biology of Three Trematodes (Digenea: Cryptogonimidae)

Ecology of stream-rearing salmon and trout Part II

SECTION 3: THE FISHES OF THE TWEED AND THE EYE

SALMON FACTS. Chinook Salmon. Oncorhynchus tshawytscha

Stoneflies. Yet another group of aquatic life disappearing from rivers. John Woodling Colorado Mesa U Environmental Sciences Department

Invasive Fish in the Cariboo Region. Russell Bobrowski Fisheries Biologist, BC Gov Cariboo Region Dec 19, 2017

Yale Reservoir Kokanee (Oncorhynchus nerka) Escapement Report 2016

Transcription:

The nymphal development of Paraleptophlebia adoptiva (McDunnough) and Paraleptophlebia mollis (Eaton) (Ephemeroptera: Leptophlebiidae) and the possible influence of temperature LYNDA D. CORKUM' Departmenr of Zoology, Erindale College, University of Toronto, Mississauga, Ont., Canada L5L lc6 Received March 9, 1978 CORKUM, L. D. 1978. The nymphal development of Paraleptophlebia adoptiva (McDunnough) and Paraleptophlebia mollis (Eaton) (Ephemeroptera: Leptophlebiidae) and the possible influence of temperature. Can. J. Zool. 56: 1842-1846. Nymphal development of Paraleptophlebia adoptiva (McDunnough) and Paraleprophlebia mollis (Eaton) was studied in the West and East branches of the Credit River, Peel County, Ontario. Nymphs of P. adoptiva were found only in the cooler water of the West branch; they continued to grow during winter months and had a short emergence period in mid-may. Paraleprophlebia mollis nymphs occurred in both branches, nymphs in the West branch being significantly smaller than those of the East. No growth was observed for P. mollis nymphs in winter and a protracted emergence period for this species throughout June was evident. Both mayfly species are univoltine. CORKUM, L. D. 1978. The nymphal development of Paraleprophlebia adoptiva (McDunnough) and Paraleptophlebia mollis (Eaton) (Ephemeroptera: Leptophlebiidae) and the possible influence of temperature. Can. J. Zool. 56: 1842-1846. Le developpement larvaire de Paraleptophlebia adoptiva (McDunnough) et de Paraleptophlebia mollis (Eaton) a ete etudik dans les branches ouest et est de lariviere Credit, comte de Peel, en Ontario. Les larves de P. adoptiva n'habitent que les eaux plus fraiches de la branche ouest; elles continuent leur croissance durant les mois d'hiver et ont une courte periode d'emergence au milieu de mai. Les larves de P. mollis habitent les deux branches de la riviere et celles de la branche ouest sont de taille significativement moindre que celles de la branche est. I1 ne semble pas y avoir de croissance chez les larves de P. mollis en hiver; la periode d'emergence de I'espece se prolonge durant tout le mois de juin. Les deux espkces sont univoltines. [Traduit par le journal] Introduction Paraleptophlebia adoptiva (McDunnough) and Paraleptophlebia mollis (Eaton) are distributed throughout eastern Canada and northeastern, southeastern, and central United States (Edmunds et al. 1976). Although Traver (1937) collected both species in South Carolina, Berner (1975) considers them rare in the southeastern United States. Despite the similarity in geographical distribution, water temperature requirements have been shown to segregate these species within a single stream (Ide 1935). This study examines the seasonal development of Paraleptophlebia adoptiva and P. mollis at one location in the West and East branches of the Credit River, Peel County, Ontario. Materials and Methods The Credit River, which flows through farmland and mixed deciduous forests, is generally a fast-flowing stream (up to 1 m per second) at the study area near the Forks of the Credit River, Peel County, Ontario (43"4Uf N; 79'59' W). The West and East branches of the Credit meet near the village of Belfountain. 'Present address: Department of Zoology, University of Alberta, Edmonton, Alta., Canada T6G 2E9. Samples were taken from the West branch immediately upstream from the confluence and from the East, 200m upstream from the confluence. The stream bed at both sites iscomposedof boulders, cobbles, gravel, scattered logs, and the occasional fallen tree. Stream widths varied between 14 and 16 m and water depth was variable with a maximum of 0.5 m. Both sites were sampled forp. adoptiva and P. mollis nymphs from April 1974 to June 1975. Weekly visits were made from April to October; but between November and March, when nymphal growth slowed, samples were taken biweekly. Nymphs were hand picked from all substrate types and immediately preserved in 70% ethanol. Nymphs were also collected using a modified Hess sampler (Waters and Knapp 1961) (mesh size: 0.432mm). Water temperatures were taken at the time of collection with a pocket thermometer at the two sites within 15 min of each other. Paraleptophlebia adoptiva and P. mollis nymphs were distinguished according to the followingcriteria: (1) Since P. adoptiva nymphs are larger than those of P. mollis, representatives, which are collected at the same time and place, can be readily distinguished by size. (2) Paraleprophlebia adoptiva nymphs have a pair of pale strokes (paramedial) at the anterior border of the 10th abdominal tergum. This character is lacking in P. mollis (Ide, personal communication). (3) Both sexes of P. udoptiva nymphs are pigmented over the entire abdominal tergum. Female P. mollis nymphs possess dark-pigmented areas near the gill origin and along the lateral edges of the abdominal terga only. Male P. mollis nymphs lack these abdominal pigmented areas. Representative nymphs were reared to imagos for positive identification.

CORKUM A S 0 N D J F M A M J J MONTH FIG. 1. Seasonal changes in water temperature for the West (--; WCR) and East (-; ECR) branches of the Credit River. Male nymphs of both species were recognized by the presence of 'double' compound eyes. Using abdominal pigmentation, nymphs of P. mollis could be sexed at an earlier developmental stage than is possible with eye formation. All nymphs were measured under a dissecting microscope at 40 x with the aid of an ocular micrometer. Initially, three growth parameters were measured for each specimen: wing-pad length, ratio of wing-pad length to the length of the seventh abdominal tergite, and head capsule width (HCW). Coefficientsof variation were calculated to determine the parameter with the least variability over a sampling period of 2 months. For both species, HCW measurements were least variable and they alone were subsequently used to determine size distributions. Results and Discussion The 37 samples collected during 1974-1975 yielded 489 nymphs of P. adoptiva and 33 15 of P. mollis. These numbers do not reflect the relative abundance of each species in the river. Paraleptophlebia adoptiva nymphs were found only in the West branch of the Credit, whereas P. mollis nymphs were found in both branches. This still appears to be the case after 3 years of sampling in the area. Both species are univol!ine. From field observations, it was assumed that food sources were not limiting in either branch. Wilcoxon's signed-ranks test for two groups arranged as paired observations (Sokal and Rohlf 1969) was used to determine if differences in water temperature existed between the two sample areas. The water temperatures were significantly higher (p < 0.001) in the East branch than in the West (Fig. 1). Paraleptophlebia adoptiva nymphs, most of which possessed gills, were first collected in September. Since early instars of mayfly nymphs lack gills, this species must have been overlooked in earlier collections at the site. These earlier instars may have occupied interstitial spaces within the stream bed (Coleman and Hynes 1970a; Bishop 1973; Williams and Hynes 1974). Based on HCW measurements, immature P. adopriva nymphs grow rapidly from September until December at which time water temperatures vary between 2.5 and 1 C (Fig. 2). The nymphs continue to grow throughout the winter months, but at a slower rate. Once temperatures increase, rapid growth resumes with the nymphs emerging by the 2nd week of May. Paraleptophlebia adoptiva emergence in the West Credit River is confined to a short period in mid-may when the maximum water temperatures reach about 15 C. This species is one of the first mayflies to emerge in the spring (Gordon 1933; Leonard and Leonard 1962). Leonard and Leonard (1962) note that the peak emergence of P. adoptiva is during the first 3 weeks of May in Michigan, yet imagos continue to appear until July 8. Gordon (1933) collected subimagos and imagos in flight on May 5 in a New York stream and by June 17, no more were found. Paraleptophlebia mollis nymphs collected in early August lacked gills, indicating that they were

1844 CAN. J. ZOOL. VOL- 56, 1978 WCR ECR 0 WCR a = sexes combined o n o = females A = males A S 0 N D J F M A M J J MONTH FIG. 2. Seasonal changes in mean head capsule width (HCW) for nymphs of P. adoptiva (a, 0) (WCR) and for P. mollis in the East (A, A; ECR) and West. (,0) branches of the Credit. in the West Credit River in very early instars. Hatching, therefore, occurred about this time. Populations in both branches exhibited growth in the autumn and showed no growth during the winter months (December-March). Once water temperatures increased in the spring (at about 5"C), growth resumed until June (Fig. 2). This pattern of P. mollis development agrees with the study by Coleman and Hynes (1970b) in the Speed River, Ontario. From a life history study on the Pigeon River, Michigan, Kovalak (1978) reported that P. mollis nymphs grew slowly between August and March, but rapidly between April and July. Water temperatures may significantly influence the relative size of P. mollis nymphs in the two branches. Two-way ANOVA paired comparison tests (Sokal and Rohlf 1969) were used to test for differences in mean male and female HCW between sample sites. Although growth patterns were similar (increased growth in the autumn and spring with no growth in the winter), the mean HCW of both males and females was greater in the warmer East branch than the West (p < 0.001). The frequency distribution of HCW of P. mollis with time is illustrated in more detail in Fig. 3 for the East branch. Samples differ between years for May (1975) and June (1974), but after testing overlapping sample populations (Student's t-test), no significant difference (p > 0.05) in HCW was found. Some P. mollis individuals overwintered as 'large' nymphs, i.e. the lengths of the mesothoracic wing pads were greater than the distance between them. During April, however, many nymphs could be still classed as immatures with lengths of the mesothoracic wing pads less than the distance between them (note the large range of HCWs in April, Fig. 3). This might be a consequence of delayed hatching as well as a precursor to an expanded emergence. Throughout June, the HCW of P. mollis nymphs changed little. Mature P. mollis nymphs with black wing pads were first observed on May 28. Other nymphs continued to grow and were found until the end of June. These individuals, however, did not attain the ultimate size of the larger overwintering nymphs. High water temperatures in late June (20 C) probably forced the emergence of the smallest nymphs. Cole-

CORKUM MALE a FEMALE SEX I?) g 41 5Z 51 49 - MAY JUNE E E 1975 1974 1.4 il I 14 2$ 11 25' 11 25 1 8 15 22 2b JANUARY FEBRUARY MARCH APRIL 1975 0.8 I 0.4 8142028'5 18 13 17 2'71 SEPTEMBER OCTOBER NOVEMBER DECEMBER 1974 FIG. 3. Frequency distribution of head capsule widths for P. mollis nymphs in the East branch of the Credit River. Number of nymphs collected is associated with each histogram. man and Hynes (1970b) also showed that nymphal water temperatures at that time were 20 C. This size at maturity appeared to decrease as the temperature appears to be the upper threshold for emergence season progressed. In the West branch, emergence within this species. P. mollis nymphs were found up until July 8 when The emergence period of P. mollis in southern

1846 CAN. J. ZOOL. VOL- 56, 1970 Ontario closely resembles that reported by Gordon (1933) in New York State. She indicates that the earliest collection of a subimago in the field occurred on May 30. Although the emergence period extended through June, the peak occurred early in the month. Leonard and Leonard (1962) agree with this time of peak emergence for P. mollis, but indicate that emergence extends until August 23. A long emergence period of from mid-may until mid-august was reported by Coleman and Hynes (1970b). Examples of expanded emergence in other species of mayflies are also known: Ameletus inopinatus (Gledhill 1959), Baetisca rogersi (Pescador and Peters 1974), Epeorus pleuralis (Ide 1935; Minshall 1967), and Leptophlebia cupida (Clifford 1970). Ide (1940) demonstrated that P. mollis emerging from Costello Creek, Algonquin Park, Ontario, came from two overlapping, segregated populations. Based on egg counts of female subimagos, he separated P. mollis A, emerging from the 1 st to the 3rd week of June, from P. mollis B, emerging from the 3rd week of June to the end of the 1st week of July. Ide (personnal communication) now considers these to be distinct species. I visited Costello Creek on June 6 and again on June 28, 1977, and sampled a 200-m stretch of riffle at the outflow of Costello Lake. Paraleptophlebia mollis nymphs were present on the earlier sampling date (water temperature: 18 C); however, on the second visit, I found only two nymphs after an hour's search (water temperature: 25 C). The exceptionally warm temperatures that month must have forced an earlier emergence. Despite the wide range of nymphal size at any one time in the Credit River, there was no clear evidence of bimodality. Egg counts, however, were not made. This problem of heterogeneity within a species could be examined using electrophoresis on samples of nymphs or imagos throughout the expanded emergence period. The above evidence suggests that water temperature may be an important factor in maintaining microdistributional differences between congeneric species. The distinguishing features of P. adoptiva development (occurrence in cooler water, continued growth, earlier and shorter emergence period) suggest that this species would extend into more northerly latitudes, higher elevations, or farther upstream than P. mollis. Ide (1935) reported that in one Ontario river supporting both P. adoptiva and P. mollis, P. adoptiva extends farther upstream towards the source where lower water temperatures prevail. Continuously low water temperatures, i.e. those below the emergence level of P. mollis, would eliminate this species from a river. Acknowledgments This research was conducted under the supervision of Dr. P. J. Pointing and was carried out at Erindale College with the aid of internal grants to Dr. Pointing and myself. I thank Dr. F. P. Idefor his frequent and enjoyable discussions on a variety of entomological topics, but especially for his help with Paraleptophlebia adoptiva and P. mollis. Mr. J. J. H. Ciborowski and Drs. H. F. Clifford, F. P. Ide, and P. J. Pointing improved the reading of the manuscript. I also thank my parents for a memorable trip to Algonquin Park. BERNER, L. 1975. The mayfly family Leptophlebiidae in the southeastern United States. Fla. Entomol. 58: 137-156. BISHOP, J. E. 1973. Observations on the vertical distribution of the benthos in a Malaysian stream. Freshwater Biol. 3: 147-156. CLIFFORD, H. F. 1970. Variability of linear measurements throughout the life cycle of the mayfly Leptophlebia cupida (Say) (Ephemeroptera: Leptophlebiidae). Pan-Pac. Entomol. 46: 98-106. COLEMAN, M. J., and H. B. N. HYNES. 1970a. The vertical distribution of the invertebrate fauna in the bed of a stream. Limnol. Oceanogr. 15: 31-40. 19706. The life histories of some Plecoptera and Ephemeroptera in a southern Ontario stream. Can. J. Zool. 48: 1333-1339. EDMUNDS, G. F., JR., S. L. JENSEN, and L. BERNER. 1976. The mayflies of North and Central America. University of Minnesota Press, Minneapolis. GLEDHILL, T. 1959. The life history of Ameletus inopinatus (Siphlonuridae, Ephemeroptera). Hydrobiologia, 14,85-89. GORDON, E. L. 1933. Notes on the Ephemerid genus Leptophlebia. Bull. Brooklyn Entomol. Soc. 28: 116134. IDE, F. P. 1935. The effect of temperature on the distribution of the mayfly fauna of a stream. Publ. Ont. Fish. Res. Lab. 50: 1-76. 1940. Quantitative determination of the insect fauna of rapid water. Publ. Ont. Fish. Res. Lab. 59: 1-24. KOVALAK, W. P. 1978. Relationships between size of stream insects and current velocity. Can. J. Zool. 56: 178-186. LEONARD, J. W., and F. A. LEONARD. 1962. Mayflies of Michigan trout streams. Cranbrook Institute of Science, Bloomfield Hills. MINSHALL, J. D. 1967. Life history and ecology of Epeorus pleuralis (Banks) (Ephemeroptera: Heptageniidae). Am. Midl. Nat. 78: 369-388. PESCADOR, M. L., and W. L. PETERS. 1974. The life history and ecology of Baetisca rogersi Berner (Ephemeroptera: Baetiscidae). Bull. Fla. State Mus., Biol. Sci. Ser. 17: 151-209. SOKAL, R. R., and F. J. ROHLF. 1969. Biometry. W. G. Freeman and Co., San Francisco. TRAVER, J. R. 1937. Notes on mayflies of the southeastern states (Ephemeroptera). J. Elisha Mitchell Sci. Soc. 53: 27-86. WATERS, T. F., and R. J. KNAPP. 1961. An improved stream bottom fauna sampler. Trans. Am. Fish. Soc. 90: 225-226. WILLIAMS, D. D., and H. B. N. HYNES. 1974. The occurrence of benthos deep in the substratum of a stream. Freshwater Biol. 4: 233-255.