The Sequence of Appearance at Dawn and Disappearance at Dusk of Some Coral Reef Fishes I

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

DOMINICA REEF FISH STATUS 2002: An Assessment of the Abundance and Species Composition of Dominican Reef Fishes. ITME Research Reports Number 13

Key words: community similarity; coral patch reef; Enewetak; reeffish; species diversity; Virgin Islands.

SPECIES RICHNESS IN THREE OCEANFLOOR HABITATS IN BERMUDA BAYS

Short-term Changes to the Coral Reef Fish Community Structure Following the Regional Coral Bleaching Event of René F.

Interspecific Competition of Stegastes fuscus. Luke Anderson. Mandy Stanford. Jessica Weems

Appendix 1 Figure A1.1.

and found that there exist a significant overlap between the billfish resources and the exploitation activities targeting tunas and mahi mahi.

Proceedings of the 6th International Coral Reef Symposium, Australia, 1988, Vol. 2 16E O' 166' 50' 167' 00'

Sea urchins, macroalgae and coral reef decline: a functional evaluation of an intact reef system, Ningaloo, Western Australia

FISHES OF THE YONGALA HISTORIC SHIPWRECK

Environmental influences on the diel timing of spawning in coral reef fishes

Vertical Composition of Coral Reef Fish at Recruitment Using a New Light Trap Method

Erin Collins and Kat Quintanilla

Key Words: Attraction, Color Cue, and Wavelength. Introduction

A Photographic Field Guide to Fish Species at Scott s Head and Champagne Reef

Reef Ecology and Fisheries Anal ysis in Diani Diani--Chale, southern Kenya: Chale, southern Kenya: A G IS GIS & RDBMS application

The Population Density of Diadema antillarum at Champagne Reef at Scott s Head Soufriere Marine Reserve

Chlorurus japanensis (Bloch, 1789) (Plate VIII, 57 and 58)

APPENDIX F DANGEROUS FISH AND MOLLUSKS

EXPERIMENTAL RESEARCH REGARDING NIGHT VISIBILITY IN ROAD TRAFFIC

Australian Acoustic Tracking and Monitoring System (AATAMS) Receiver Pool Application Final Report

Ecological Survey of Puhi Bay and Richardson s Ocean Center

Annual Measurement of Solar UVB at a Reef Site Using a Polyphenylene Oxide Dosimeter

AIS data analysis for vessel behavior during strong currents and during encounters in the Botlek area in the Port of Rotterdam

WATERWAYS AND HARBORS DIVISION Proceedings of the American Society of Civil Engineers. EQUILIBRIUM FLOW AREAS OF INLETS ON SANDY COASTS a

Chlorurus perspicillatus x C. sordidus, a hybrid parrotfish from the Hawaiian Islands

13. TIDES Tidal waters

OCN 201 Tides. Tsunamis, Tides and other long waves

Reef Channels as Spawning Sites for Fishes on the Shiraho Coral Reef, Ishigaki Island, Japan. Jack T. Moyer. (Received May 26, 1989) Results

Conditioned Alarm Behavior in Fathead Minnows (Pimephales promelas) and Test Their Ability

INDO-PACIFIC DISTRIBUTION OF MICRODESMID FISHES (GOBIOIDEA)*

JIMAR PFRP ANNUAL REPORT FOR FY 2006

Packwood Lake Intake Screen Velocity Test Report for Energy Northwest's Packwood Lake Hydroelectric Project FERC No Lewis County, Washington

GLMM standardisation of the commercial abalone CPUE for Zones A-D over the period

Examples of Carter Corrected DBDB-V Applied to Acoustic Propagation Modeling

Legendre et al Appendices and Supplements, p. 1

Remote Monitoring of Dolphins and Whales in the High Naval Activity Areas in Hawaiian Waters

SMOOTH HAMMERHEAD SHARK (HHS)

Recovery of Coral Populations at Helen Reef Atoll after a Major Bleaching Event

Diadema antillarum (Long-spined Black Urchin)

Community organization of reef fishes in the live coral sub-habitat of Kavaratti atoll, Lakshadweep, India

$ Course Price Includes: all materials, dive gear, instruction and 1 boat dive.

Relation between coral reef degradation and the Overexploitation of coral reef fishes in El-Tur region, Egyptian Red Sea Coast

Habitat selection during settlement of three Caribbean coral reef fishes: Indications for directed settlement to seagrass beds and mangroves

Two types of physical and biological standards are used to judge the performance of the Wheeler North Reef 1) Absolute standards are measured against

Technical and Financial Proposal

Citizen Science Based Survey GBR Far North Dive Trip 2016 April 18-26

DRIVING ON THE HARD SHOULDER A SAFETY ASSESSMENT ABSTRACT

The Ocean Geologic Features section introduced you

(679) Dive Line (679) FAX (679)

Pohnpei surf club. Pohnpei, FSM

Moku o Loe, Oahu. Benthic Habitat Data: 2 m

the eastern Pacific rocky intertidal from southern Alaska (Lamb and Edgell, 1986) to

THE SURVIVAL OF TRANSPLANTED CORAL ON PYRAMID-SHAPED FISH SHELTER ON THE COASTAL WATERS OF KELAPA AND HARAPAN ISLANDS, KEPULAUAN SERIBU, JAKARTA

Time Will Tell: Long-term Observations of the Response of Rocky-Habitat Fishes to Marine Reserves in Puget Sound

A REVIEW STRATEGY ON TROPICAL COAST MARINE FISHES FOR ITS REPRODUCTION

Environmental Correlates of the Distribution of Planktivorous Fishes in the One Tree Reef Lagoon

Tropical Pacific Wrasses, Part 1 REEF Fishinar March 14, 2018, Amy Lee - Instructor Questions? Feel free to contact

New power in production logging

Overview. What are Corals?

Volume and Shoreline Changes along Pinellas County Beaches during Tropical Storm Debby

Figure 1. AGRRA survey sites in Cahuita, Costa Rica (modified from Cortés, 1998).

FAO SPECIES IDENTIFICATION SHEETS KUHLIIDAE * Flagtails, daras

Life at its Peak of Exuberance: Coral Reefs and Tropical Rainforests

Technical Note. Determining the surface tension of liquids by measurements on pendant drops

There are many different kinds of beaches which are generally characterized by the dominance of waves, tides, rivers and currents, and in particular

Preliminary analysis of yellowfin tuna catch, effort, size and tagging data using an integrated age-structured model

Introduction (2 of 2) Systematic approach should be followed

92 ND MEETING DOCUMENT IATTC-92 INF-C

Diel, Lunar, and Seasonal Periodicity in the Reproductive Behavior of the Pomacanthid Fish, Centropyge potteri, and Some Other Reef Fishes in Hawaii!

Chapter 5: Methods and Philosophy of Statistical Process Control

Solunar Theory. One by one the factors were examined and rejected. Three of them, however, merited further examination. They were sun, moon and tides.

Data Set 7: Bioerosion by Parrotfish Background volume of bites The question:

SAVERS FAST FACTS

A SURVEY OF 1997 COLORADO ANGLERS AND THEIR WILLINGNESS TO PAY INCREASED LICENSE FEES

VARIABLE PATTERNS OF DEN HABITATION BY THE ORNATE ROCK LOBSTER, PANULIRUS ORNATUS, IN THE TORRES STRAIT. Jasper Trendall and Stewart Bell

Artificial Reef Program Biological Monitoring Update

Is what is there what you catch? 2008 update Baited Remote Underwater Video in the southern Great Barrier Reef

Analyzing spatial structure of recreational coastal reef fisheries in New Caledonia for management purposes

Instruction Guide for using Dive Tables (draft)

WHAT CAN WE LEARN FROM COMPETITION ANALYSIS AT THE 1999 PAN PACIFIC SWIMMING CHAMPIONSHIPS?

Palythoa Abundance and Coverage in Relation to Depth

Marine Ecosystems. Aquatic Ecosystems Section 2

I. Monitoring and Adaptive Management Approach. Potential Effects, Monitoring Studies & Mitigation

Traveling Waves vs. Standing Waves

National Weather Service

page - Laboratory Exercise #5 Shoreline Processes

-2- A. schlegeli and A. latus inhabit Hiroshima Bay. Although the former is abundant, the

Sea urchin density along a depth gradient at Rodney's Rock and Champagne Bay, Dominica

SCRIPPS BIRCH AQUARIUM WORKSHEET

INTERNATIONAL HYDROGRAPHIC REVIEW MAY 2015

While the fishing standing stock at Wheeler North Reef has been consistently below the 28 ton requirement, data from last summer s survey showed that

OVERVIEW OF METHODOLOGY

Zooplankton Migration Patterns at Scotton Landing: Behavioral Adaptations written by Lauren Zodl, University of Delaware

Reef Watch Fish Survey Manual

Intraspecific and interspecific relationships between host size and the abundance of parasitic larval gnathiid isopods on coral reef fishes

Ocean Series Coral Reefs

Relationship between roving behaviour and the diet and client composition of the cleaner fish Labroides bicolor

A Baseline Study on Coral Reef Fishes in the Marine Protected Areas in Southern Cebu, Philippines

Transcription:

Pacific Science (1973), Vol. 27, No.2, p. 12-135 Printed in Great Britain The Sequence of Appearance at Dawn and Disappearance at Dusk of Some Coral Reef Fishes I S. B. DOMM AND A. J. DOMM2 ABSTRACT: Coral reef fishes were observed from the Hook Island Underwater Observatory and the light intensity and time at which each species appeared at dawn and disappeared at dusk were measured. For the species considered there was a definite sequence of disappearance at dusk (showing family groupings) that more or less reversed itself in the appearance at dawn. Light is probably a factor governing this behavior but whether it is light intensity, rate of change of light intensity, or a change in light quality (wavelength) is not known. It is postulated that the sequential appearance at dawn and disappearance at dusk of the fishes may have evolved to reduce confusion and hence the likelihood of predation at this time. COLLETTE AND TALBOT (in press) have obtained detailed information on the diurnal-nocturnal changeover pattern of many coral reef fishes in the Virgin Islands, but these authors did not report a sequential pattern in the diurnalnocturnal changeover. This study was conceived to investigate the possibility ofa sequence in the disappearance of diurnal fishes at dusk and a corresponding sequence in the appearance of these fishes at dawn. The observations were made at the Hook Island Underwater Observatory. Hook Island (lat 20 07' S, long 14 55' E) is considered to be a part of the Great Barrier Reef of Australia. It is 12 miles from shore and near the central Queensland town of Proserpine. Hook Island like the other islands of the Whitsunday Group is a high island, surrounded bya well-developed fringing coral reef. The reefs in this area support many species of tropical coral reef fishes. The Hook Island Underwater Observatory consists of a large rectangular viewing chamber 4 meters wide by 6 meters long by 2t meters high and contains 36 windows. A platform 2 meters wide surrounds the viewing chamber and supports the living corals that make up the viewing area. The depth of the platform varies from 2t meters at low tide to 6 meters at high I Manuscript received 16 October 1972. 2 The Australian Museum, 6- College Street, Sydney, New South Wales, Australia. tide. A large number of fishes frequented the viewing area (51 species identified), and there were no enclosures to prevent their movement. Their behavior seemed undisturbed by the observers' presence. The owners of the Observatory, however, did encourage the larger carnivores by occasional feeding. From the Observatory we were able to make close-range observations on fish behavior without the disadvantages of continual diving and the disturbance caused by diver presence. 12 METHODS Before observations commenced, the fishes frequenting the Observatory were identified. In fishes without distinct color patterns and in fishes that are known to change their coloration with age (e.g., some Labridae), the identifications can only be taken as tentative. Although this is a disadvantage, it should not impair the value of this study. Identifications were made visually using the following reference texts: Schultz et al. (1960 and 1966), Smith (1949), Smith and Smith(1963), Marshall (1964), Munro (1967), Gosline and Brock (1960), and Choat (1969). From 16 August 1970 to 5 September 1970 repeated visits were made to the Observatory during the times of dusk and dawn. Observations on the presence and relative abundance of the most common species (Table 1) and the

Coral Reef Fishes-DoMM AND DOMM 129 TABLE 1 FISHES OF THE HOOK ISLAND UNDERWATER OBSERVATORY FROM WHICH DATA WERE OBTAINED CENTROPOMIDAE Psammoperca melanopus HOLOCENTRIDAE Holocentrus sp. SERRANIDAE Plectropomus maculatus Cephalopholis miniatus Epinephelus fasciatus An.yperodon leucogrammicus Epinephelus merra Epinephelus tauuina Epinephelusfuscoguttatus Epinephelus lanceolatus Cephalopholis pachycentron Cephalopholis ~yanostigma Diploprion bifasciatum Cromiliptes altive/is APOGONIDAE No species differentiated LUTJANIDAE Caesio chrysozonus CHAETODONTIDAE Chaetodon aureofasciatus Chaetodon rainfordi Chelmon rostratus Chaetodontiplus personifer POMACENTRIDAE Abudefdufpalmeri Abudefdufmelas Abudefduf bankieri Pomacentrus sutflavus Chromis dimidiatus LABRIDAE Lienardella fasciatus Hemigymnus melapterus Labroides dimidiatus Thalassoma lunare Epibulus insidiator Choerodon albigena Choerodon venustus SCARIDAE Scarusfasciatus Scarus ghobban Scarus venosus Scarus f/avipectoralis Scarus microrhinos Scarus spp. ACANTHURIDAE Acanthurus xanthopterus SIGANIDAE Siganus doliatus light intensity were taken at approximately 5 minute intervals. Eight separate observations were made at dawn and eight at dusk, making a total of 16 observations over days. Light intensities were measured with a Gossen "Lunasix 3" photographic light meter. This instrument did not read in footcandles, but the appropriate conversion was made. Although this is a sensitive light meter for photographic purposes, its sensitivity to different wavelengths is probably not identical to that of the fish eye. To arrive at a particular light intensity and time for the appearance of a given species of fish at dawn we decided to take the time and light intensity at which the first fish of that species was seen. At dusk the time and light intensity were taken when the last fish of a given species disappeared. These gave cutoff points that were easy to determine. In fact most 9 species offishes appeared or disappeared within a short interval of time: about 5 minutes for most fishes, although scarids took up to 15 minutes. Certain species of fishes were seen taking shelter at dusk in the many nooks and crannies of coral surrounding the Observatory (Chaetodontidae, Pomacentridae, Scaridae, Apogonidae, and Lutjanidae). With these fishes it was possible to obtain exact information on their disappearance at dusk and appearance at dawn. Other species (e.g., Siganidae) did not seek shelter but merely became motionless and ceased active swimming. The most difficult group consisted ofthose that disappeared over the edge of the Observatory platform (e.g., Labridae and Acanthuridae). Because these fishes disappeared within fairly narrow time limits and in a consistent pattern, we have assumed they were taking cover for the night. H PS 27

130 PACIFIC SCIENCE, Volume 27, April 1973 TABLE 2 THE TIME AND LIGHT INTENSITY AT WHICH THE LABRIDAE DISAPPEARED AT DUSK STANDARD STANDARD MEAN LIGHT DEVIATION SAMPLE DEVIATION (FOOT- (FOOT- SIZE FISH MEAN TIME (MINUTES) CANDLES) CANDLES) (N) Lienarde/la fascia/tis 1730 16. 76.0 3.0 7 Hemigymnus melaptems 1745 12.2 40.0 1.0 Labroides dimidiattls 1751 4.4 26.4 9.3 Thalassoma lunare 1752 3. 23.7.6 Epibulus insidia/or 1754 4. 22.0 9.4 Average time of sunset 1754 NOTE: Choerodon albigena was not present at the Observatory during the late afternoon and dusk. FOOT CANDLES 12 15-30- 20-10- 10 9 55 1745 1750 7 6 11 5 i4 3 t 2 1 1755 100 105 110 115 FIG. 1. Thetime of disappearance of fishes at dusk in relation to light intensity is shown. The vertical lines with each number represent the standard deviation (footcandles) for that species. 1, Abudefduf palmeri; 2, Scaridae; 3, Sigamls doliatlls; 4, Acanthums xanthoptertls; 5, Apogonidae; 6, Caesio chrysozonus; 7, Chaetodontidae;, Abudefdtif bankieri; 9, PomacClltms stllflavus; 10, Chromis dimidiatlls; 11, Chaetodontiplus personifer; 12, Thalassoma lllnare. TIME When the results from the first set ofobservations were analyzed, the data for the disappearance of the labrids at dusk, with the exception of those for Thalassoma lunare, did not give a clear picture. A shorter, more detailed study was conducted, therefore, on the disappearance of labrids. This study dated from 26 September 1970 to October 1970. As conditions and time of year differ slightly, these results cannot be compared directly with the first set of data and are included in Table 2. RESULTS The results indicate that the appearance and disappearance ofthe fish species relative to each other are not random but follow a certain sequence at dusk that approximately reverses it-

Coral Reef Fishes-DoMM AND DOMM 131 FOOT CANDLES 17 1 25-20- 15-10 - 14 15 1. 5- I 0550 10 6} 7ft 9 11 13 12 1 I ~ ~ 4~" 0555 0600 0605 0610 5R 0615 0620 TI ME FIG. 2. The time ofappearance offishes at dawn in relation to light intensity is shown. The vertical lines with each number represent the standard deviation (footcandles) for that species. 1, Abudefdufpalmeri; 2, Caesio chrysozonus; 3, Scaridae; 4, Chaetodontidae; 5, Acanthurus xanthopterus; 6, Abudefdufmelas; 7, Apogonidae;, Pomacentrus sufllavus; 9, Choerodon albigena; 10, Epibulus insidiator; 11, Lienardella fasciatus; 12, Chromis dimidiatus; 13, Abudefdufbankieri; 14, Siganus doliatus; 15, Thalassoma lunare; 16, Chaetodontiplus personifer; 17, Labroides dimidiatus; 1, Hemigymnus melupterus. self at dawn. Each species has a characteristic position in the sequence (see Fig. 1 and 2). Only the most abundant fishes have been treated in this study. With the exception of the Apogonidae, all are diurnal. There were very few nocturnal fishes present at the Observatory. Of these, only two species were present in any number: Holocentrus sp. (Holocentridae) and Psammoperca melanopus (Centropomidae). Both of these fishes commenced activity at dusk after all the diurnal fishes had disappeared and either became inactive (Psammoperca) or disappeared (Holocentrus) at dawn before the diurnal fishes emerged. The only common diurnal fishes not considered were the Serranidaewhich, although abundant by day, were rarely present during the dawn and dusk observations. DISCUSSION It is apparent particularly at dusk that fishes of the same family tend to disappear together within relatively narrow time limits (Tables 3 and 4). For example, all the labrids disappear first (Table 2). These are followed by the three species of small schooling pomacentrids. The chaetodontids retire next, followed by the acanthurids and siganids. The scarids all disappear together. The large solitary pomacentrids are more variable in their behavior and tend to disappear last of all. At dawn the family groupings are not so clearly seen. The division of coral reef fishes into diurnal and nocturnal guilds has been suggested by other workers: Schroeder and Starck (1964), Starck and Davis (1966), and Hobson (1965). Hobson separates most of the fishes studied into diurnal, nocturnal, and crepuscular groups and 9-2

132 PACIFIC SCIENCE, Volume 27, April 1973 TABLE 3 THE TIME OF DISAPPEARANCE OF FISHES AT DUSK STANDARD DEVIATION IN SAMPLE FISH MEAN TIME MINUTES SIZE (N) Thalassoma lunare 174 7.2 Chromis dimidiatus 1755 4.6 Chaetodontiplus personifer 1755 7.6 5 Pomacentrus sutjlavus 1756 4.9 Abudefduf bankieri 1757 4.6 Chaetodontidae 1759 6.9 Caesio chrysozonus 100 5.6 Apogonidae 100 4.6 7 Acanthurus xanthopterus 104 5.6 Siganus doliatus 106 6.3 7 Scaridae 10 5.3 Abudefdufpalmeri 114 4.9 4* * Abudefduf palmeri remained active on four of the eight observations after nightfall which prevented our recording the time of its disappearance. TABLE 4 THE TIME OF ApPEARANCE OF FISHES AT DAWN FISH MEAN TIME STANDARD DEVIATION IN MINUTES SAMPLE SIZE (N) Abudefdufpalmeri Caesio chrysozonus Scaridae Acanthurus xanthopterus Chaetodontidae Abudefdufme/as Apogonidae Pomacentrus suff/avus Choerodon albigena Epibulu.r insidiator Lienardella fasciatus Chromis dimidiatus Abudefduf bankieri Siganus doliatus Thalassoma lunare Chaetodontiplus personifer Labroides dimidiatus Hemigymnus melapterus 0553 0557 055 0602 0602 0605 060 060 0609 0609 0610 0612 0612 0612 0615 0617 0620 0621 6.1 5.9 7.1 4.3 6.6 6. 5.0 7.0 5.0 6.4.7 6.5 6.6 12.1 6.5 4.5 5.3 6.7 5 7 7 5 7 7 notes that"the time of major activity tends to be consistent within most of the families of fishes." Our data suggest that within most families of fishes there is also a consistent time of appearance at dawn and disappearance at dusk. This may break down when the family is large and diverse as in the Pomacentridae, where the small schooling species are separated in time from the large solitary species. As mentioned under "Methods," fishes belonging to some families simply disappeared over the platform of the Observatory at dusk, and we had to assume that they were retiring for the night at that time. The same problem in interpretation occurred at dawn. Randall (1961), discussing the night behavior of the acanthurid Acanthurus triostegus sandvicensis, mentioned that this species commonly rests on the bottom in

Coral Reef Fishes-DoMM AND DOMM TABLE 5 COMPARISON OF RESULTS FROM COLLETTE AND DOMM COLLETTL DOMM DAWN Pomacentridae (large solitary) Scaridae Chaetodontidae and Acanthuridae Pomacentridae (smail schooling) and some Labridae Labridae Pomacentridae Acanthuridae Scaridae Labridae DUSK Labridae Pomacentridae (smail schooling) Chaetodontidae Acanthuridae Scaridae Pomacentridae (large solitary) Labridae Chaetodontidae Acanthuridae Pomacentridae NOTE: The families above are listed in order of appearance at dawn and disappearance at dusk. Only families common to both studies are listed. One or more species were not considered representative of a family unless separated from the next species by a reasonable interval of time. what appears to be sleep during the hours of darkness. Starck and Davis (1966) and Hobson (1965) reported that many labrids seek shelter for the night in cracks and crevices, whereas others bury themselves in the sand. The sequence of disappearance of fishes at dusk more or less reverses itself in their appearance at dawn (Fig. 1 and 2 and Table 5). The fishes in this study constitute only a small number of the species found on the Great Barrier Reef, and more data are needed before all family groupings become clear. The sequential appearance and disappearance of fishes may vary from one locality to another; however the principle remains the same. The results of Collette and Talbot (in press) tend to be in agreement with the present study. Comparing the same families of fishes used in this study to those observed by Collette and Talbot (Table 5), we find that both show a reversal of dawn and dusk sequence and a tendency for species of the same family to be grouped together. From observation to observation the time of appearance at dawn and disappearance at dusk is fairly consistent for each species. Most standard deviations for time are relatively 133 small, approximately 5 to 6 minutes (see Tables 3 and 4), suggesting a rather narrow threshold of response. It seems that, whatever the stimulus is that triggers the seeking of shelter and leaving it, the response is consistent with respect to time. However, this could occur because time was more accurately measured than light. Initially it was thought that it was light intensity that provided the stimulus inducing fishes to retire for the night and appear at dawn. The reversal of sequence tends to suggest this. If light intensity were the critical stimulus one might expect small standard deviations for light intensity; however, our results indicate that these are generally large. But this may be because conditions of water depth and clarity and of cloud cover vary from observation to observation; factors that cannot readily be corrected for. Interpretation is also complicated by the fact that, as light intensity increases in footcandles, the standard deviation also increases. In the human eye (and probably in the eyes of most other vertebrates as well) sensitivity varies inversely with intensity (Steinhardt, 1936). Therefore, it cannot be assumed that a large standard deviation implies a less critical threshold, it may reflect merely a limitation in the sensitivity of the fish eye. Most fishes tend to appear at dawn at a lower light intensity than that at which they disappear at dusk, so that two light intensities may be involved. However, this may be because at dusk the fish eye is adapting from light to dark, whereas at dawn it is dark-adapted and so should be more lightsensitive. During dusk and dawn the wavelengths of light penetrating seawater are changing very rapidly. The fishes could be responding to a change of light quality, that is, wavelength composition. There is also the possibility that the fishes are not responding to a particular level of light intensity so much as they are to the rate of change of light intensity. The present data do not differentiate between these various possibilities. It seems likely that the fishes are responding to an endogenous circadian clock or rhythm, the phase of which is set by light quantity, quality, or a combination of these. Activity patterns of this type have been described for a number of fishes (Woodhead, 1966).

134 The conclusions drawn from this study are that the sequential disappearance at dusk and appearance at dawn ofthe fishes observed seem to be consistent with respect to time for each species, and that light is probably involved in triggering this response; but the mechanism is not yet understood. In order to accommodate the large numbers of diurnal species seeking shelter at dusk, natural selection possibly may have favored the development of a sequential pattern whereby most diurnal reef fishes seek shelter for the night at slightly different times. This sequential pattern would be a mechanism enabling many species offish to obtain shelter for the night in a relatively short time, reducing the confusion which would favor predation. It would also reduce the interspecific aggression that might develop between more than one species competing for the same shelter at the same time. SUMMARY 1. The time and light intensity at which certain species of coral reef fishes appeared at dawn and disappeared at dusk were recorded. Observations were made from the Hook Island Underwater Observatory. 2. The fishes emerged at dawn in a definite sequence that more or less reversed itself in their disappearance at dusk. There was a tendency for species of the same family to disappear close together at dusk, but this was less apparent at dawn. 3. The possibility that light is a controlling stimulus is discussed. Whether light intensity, rate of change of light intensity, or a change in wavelength is responsible, cannot be resolved. It is suggested that the fishes may be responding to an endogenous rhythm, the phase of which is set by light. 4. It is postulated that the sequential disappearance offishes at dusk mayreduce confusion and, hence, the possibility of predation by pisciverous carnivores which are active at this time. It may also reduce interspecific aggression resulting from competition for sheltering places. PACIFIC SCIENCE, Volume 27, April 1973 ACKNOWLEDGMENTS We would like to thank the owners of the Hook Island Underwater Observatory for giving us the opportunity to live on Hook Island and work in the Observatory. Many thanks go to J. Randall and P. M. J. Woodhead for their very helpful comments on the manuscript and to F. Talbot for his helpful comments and for making available to the authors his unpublished manuscript. LITERATURE CITED CHOAT, J. H. 1969. Studies on the biology of labroid fishes (Labridae and Scaridae) at Heron Island, Great Barrier Reef. Part 1. Ph.D. thesis, Univ. Qd. COLLETTE, B. B., and F. H. TALBOT. In press. Activity patterns of coral reef fishes with emphasis on nocturnal-diurnal changeover. Sci. Bull. Los Angeles County Mus. Nat. Hist. GOSLINE, W. A, and V. E. BROCK. 1960. Handbook ofhawaiian fishes. Univ. Hawaii Press, Honolulu. 372 p. HOBSON, E. S. 1965. Diurnal-nocturnal activity of some inshore fishes in the Gulf of California. Copeia 3: 291-302. MARSHALL, T. C. 1964. Fishes of the Great Barrier Reef and adjacent waters of Queensland. Angus and Robertson, Sydney. 566 p. MUNRO, I. S. R. 1967. The fishes of New Guinea. Dep. Agric. Stock Fish., Pt. Moresby, New Guinea. 650 p. RANDALL, J. E. 1961. A contribution to the biology of the convict surgeonfish of the Hawaiian Islands, Acanthurus triostegus sandvicensis. Pacif. Sci. 15(2): 215-272. SCHROEDER, ROBERT E., and WALTER A. STARCK II. 1964. Diving at night on a coral reef. Nat. Geogr. Mag. 125(1): 12-154. SCHULZT, L. P., ET AL. 1960. Fishes of the Marshall and Marianas islands. Vol. 2. Bull. U.S. Nat. Mus. 202(2): 1-43. ---. 1966. Fishes of the Marshall and Marianas islands. Vol. 3. Bull. U.S. Nat. Mus. 202(3): 1-76. SMITH, J. L. B. 1949. The sea fishes ofsouthern Africa. Central News Agency Ltd., S. Afr. 550 p.

Coral Reef Fishes-DoMM AND DOMM SMITH, ]. L. B., and M. M. SMITH. 1963. The fishes of Seychelles. Rhodes Univ., Grahamstown, S.Afr. 215 p. STARCK, WALTER A. II, and WILLIAM P. DAVIS. 1966. Night habits of fishes off Alligator Reef, Florida. Ichthyologica, Aquar. ]., Jersey City, N.]. 3(4): 313-356. 135 STEINHARDT, J. 1936. Intensity discrimination in the human eye. J. Gen. PhysioI. 20: 15 209. WOODHEAD, P. M. ]. 1966. The behaviour of fish in relation to light in the sea. Oceanogr. Mar. BioI. Ann. Rev. 4: 337-403.