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1989

Palatability of Freshwater Surface to Potential Fish Predators (Lepomis macrochirus and Gambusia affinis)

Julie Heyward Mounts College of William & Mary - Arts & Sciences

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Recommended Citation Mounts, Julie Heyward, "Palatability of Freshwater Surface Hemiptera to Potential Fish Predators (Lepomis macrochirus and Gambusia affinis)" (1989). Dissertations, Theses, and Masters Projects. Paper 1539625502. https://dx.doi.org/doi:10.21220/s2-6msd-y891

This Thesis is brought to you for free and open access by the Theses, Dissertations, & Master Projects at W&M ScholarWorks. It has been accepted for inclusion in Dissertations, Theses, and Masters Projects by an authorized administrator of W&M ScholarWorks. For more information, please contact [email protected]. PALATABILITY OF FRESHWATER SURFACE HEMIPTERA TO POTENTIAL FISH PREDATORS (LEPOMIS MACROCHIRUS AND GAMBUSIA AFFINIS)

A Thesis

Presented to The Faculty of the Department of Biology

The College of William and Mary in Virginia

In Partial Fulfillment Of the Requirements for the Degree of

Master of Arts

by Julie Heyward Mounts

1989 ProQuest Number: 10628126

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ProQuest 10628126

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ProQuest LLC. 789 East Eisenhower Parkway P.O. Box 1346 Ann Arbor, Ml 48106 - 1346 APPROVAL SHEET

This thesis is submitted in partial fulfillment of

the requirements for the degree of

MASTER OF ARTS

'// A a ' Julie Heyward Mounts

Approved, October 1989

Grego^fr M/ Capelli, CMirman

Garnett R. Brooks

a ht'l ^Norman J . Rarshing

ii TABLE OF CONTENTS

Page

ACKNOWLE DGEMENTS i v LIST OF TABLES...... v

LIST OF FIGURES...... vii

ABSTRACT...... viii INTRODUCTION...... 2 GENERAL SURVEY AND IDENTIFICATION...... 7 MATERIALS AND METHODS...... 13 RESULTS...... 19 DISCUSSION...... 40 LITERATURE CITED...... 44

VITA...... 46

iii ACKNOWLEDGEMENTS

I wish to express my gratitude and appreciation to my committee chairman, Dr. Gregory M. Capelli, under whose direction this research was conducted, for his guidance and constructive criticism. I am also grateful to Drs. Garnett R. Brooks and Norman J. Fashing who served on my committee and critically reviewed this manuscript, providing valuable comments and support.

I thank Mrs. Jewel Thomas for helping to photograph the pictured in this manuscript and providing slides of

the insects and tables used in the oral presentation.

A special thank you is extended to my husband for his continual help and encouragement, and to my parents and brother for their support.

iv LIST OF TABLES

Table Page 1. Prey item information...... 8 2. Responses of Gambusia affinis to prey items... 21 3. Responses of juvenile Lepomis macrochirus to prey items 2 4 4. Responses of adult Lepomis macrochirus to prey items in 198 8 2 6 5. Mean number of Gambusia affinis attacks per prey item. Size classes of fish and replicate experiments from different years are combined. 2 7

6. Mean number of juvenile Lepomis macrochirus attacks per prey item. Size classes of fish and replicate experiments from different years are combined 2 8 7. Total number of prey items eaten by Gambusia affinis as a function of size class. Data from replicate experiments combined 3 0

8. Total number of prey items eaten by juvenile Lepomis macrochirus as a function of size class. Data from replicate experiments combined...... 31

9. Stomach analysis results for Gambusia affinis (8/15/88). Data expressed as percent of fish containing the item, for various times of day. 3 3

10. Stomach analysis results for Gambusia affinis (8/22/88). Data expressed as percent of fish containing the item, for various times of day. 3 4 11. Stomach analysis results for Gambusia affinis (9/25/88). Data expressed as percent of fish containing the item, for various times of day. 3 5

12. Stomach analysis results for juvenile Lepomis macrochirus in 1988. Data expressed as percent of fish containing the item...... 38

v 13. Stomach analysis results for adult Lepomis macrochirus in 1988. Data expressed as percent of fish containing the item...... 39

vi LIST OF FIGURES

Figure Page la. Trepobates inermis (adult-left, nymph-right) lb. Rheumatobates palosi...... 9 2a. Rheumatobates tenuipes

2b. Gerris marginatus...... 10 3a. Mesovelia mulsanti 3b. Microvelia americana...... 11

4. Microvelia pulchella...... 12 5. Experimental tank set-up...... 14 6a. Typical contents of a Gambusia affinis stomach including several Diptera larva. 6b. Gambusia affinis stomach containing nymphal Trepobates inermis...... 32

7. Typical contents of a juvenile Lepomis macrochirus stomach containing Diptera larva and several small Pelecypoda 3 7

vii ABSTRACT

Using laboratory experiments, I determined the palatability of eight of freshwater surface Hemiptera to potential fish predators (Lepomis macrochirus - bluegill, and Gambusia affinis - gambusia). Species tested included five from the family (Trepobates inermis, Rheumatobates palosi, Rheumatobates tenuipes. Gerris marginatus. and Gerris remiais), one from the family Mesoveliidae (Mesovelia mulsanti), and two from the family (Microvelia americana and Microvelia pulchella). Field collections of gambusia and bluegill were also made to determine by stomach analysis the importance of surface Hemiptera in their diet. The Gerridae tested were palatable to gambusia and bluegill but both Veliidae were unpalatable to both fish species. Results for Mesovelia mulsanti were mixed: gambusia rejected them while bluegill ate them. Stomach analyses indicated that surface Hemiptera are probably at most only an incidental and sporadic part of fish diets.

viii PALATABILITY OF FRESHWATER SURFACE HEMIPTERA TO POTENTIAL FISH PREDATORS (LEPOMIS MACROCHIRUS AND GAMBUSIA AFFINIS) INTRODUCTION

For many years ecologists have focused on predation as a major factor in the structure of communities, including aquatic ones. One aspect of predation, the unpalatability of the prey as a possible defensive mechanism in aquatic environments, has not received much attention until recently (Kerfoot 1982). Whirligig beetles (Gyrinidae) (Benfield 1972), predaceous diving beetles (Dytiscidae) (Schildknect et al. 1966), and aposematically colored water mites (Arachnoides) have been found unpalatable to fish (Kerfoot 1982). Two species of Hemiptera have also been found distasteful to fish in direct feeding experiments: pygmy backswimmers - Plea strida (Pleidae) (Kerfoot 1982) and caprai (Veliidae) (Bronmark et al. 1984). In addition, suspected multifunctional compounds (possible sexual attractants, alarm substances, defensive compounds) have been isolated and identified for eight species among the aquatic Hemiptera families Notonectidae, Corixidae,

Belastomatidae, Naucoridae, Pleidae, and Gelatotrichidae

(Scrimshaw and Kerfoot 1987).

Various semi-aquatic Hemiptera of the suborder

Heteroptera, infraorder occupy the surface

(neustonic) zone of fresh, brackish, and salt water. These

2 3 insects are often an abundant and very visible component of shallow, near-shore freshwater communities. Preliminary observations indicated that Lake Matoaka and other freshwater lakes and streams in the Williamsburg vicinity contained typical representatives, including the families

Gerridae (water striders), Veliidae (broad shouldered water striders), and Mesovellidae (water treaders). Two species of fish are common in the same general habitats: Gambusia affinis (gambusia) and juvenile Lepomis macrochirus (bluegill). Gambusia are generalists feeding on a wide variety of items including mosquito larvae and pupae, copepods, algae, and small fish (Carlander 1969, Flemer and Woolcott 1966). Juvenile bluegill feed on aquatic insects and smaller Crustacea while adults, which generally occur in somewhat deeper water, feed mainly on aquatic insects, small crayfish, and small fish (Carlander 1977).

In a review of prior studies Anderson (1982a) listed hunting spiders, damselflies, backswimmers, pelagic fish, frogs, and surface feeding birds as potential predators of surface Hemiptera, but presented no firm evidence. Many surface Hemiptera are known to be cannibalistic, feeding on vulnerable nymphs and smaller individuals (Anderson 1982a).

A review of the literature on gambusia and bluegill stomach analyses reveals sporadic and infrequent records of surface Hemiptera prey in their diet. In a saltmarsh habitat, combined data for 2,786 fish (including gambusia along with 9 other species) stomach samples yielded a total of 0.18% frequency of occurrence and 0.03% aggregate volume 4 for Veliidae (Harrington and Harrington 1961). Of 143 bluegill taken from 18 Kentucky farm ponds, one fish (in a

1.0-1.6" length range) contained one adult gerrid (Turner

1955). Only 3/273 bluegill from six collecting stations on

Tuckahoe Creek, Virginia contained gerrids, although gerrids were present in large numbers in all areas (Flemer and

Woolcott 19 66). Butler (1989) reported that in Dog Lake, Florida bluegill (60-125 mm in length) fed primarily on benthic invertebrate prey (95% by mass); surface Hemiptera were not found in any of the stomach samples. One of the most distinguishing organ systems of the Heteroptera is the metathoracic scent apparatus (Anderson

1982b). Although the role of the secretions for these glands is unknown, it has been suggested as a possible defensive chemical against predators in surface Hemiptera (Anderson 1982a). There is a statement with no documentation in Polhenus and Chapman (1979) suggesting that a metathoracic scent gland secretion would make Gerridae distasteful to predators.

A case where unpalatability apparently plays a defensive role involves the interaction of Velia caprai

(Heteroptera: Veliidae) with Salmo trutta ()

Bronmark et al. (198 4) found that trout refused to eat V. caprai in direct feeding experiments and suggested that the unpalatability of V. caprai is possibly enhanced by school formation which would promote learned avoidance behavior in the trout. Other defensive behavioral responses of the prey were also observed. These included thanatosis and expansion 5 skating (secretion of a fluid which decreases surface tension and shoots the across the water). Observations on rainbow trout (Salmo crairdneri) and gerrids (Gerris remicris) in stream pools indicated that the trout affect mircrodistribution of gerrids (Cooper 1984). Trout were added to previous troutless stream pools and removed from other pools. Undisturbed pools with and without trout served as controls. In stream pools lacking trout, gerrids occupied all parts of the pool. Conversely, it was observed that in pools containing trout, gerrids were restricted to the perimeter and apparently maintained there by trout harassment. Experimentally disabled gerrids were readily eaten by trout. However, gerrids were not found in any of eight trout stomachs collected in the research pools. Cooper (1984) was unable to determine any possible effect on gerrid fitness but noted that trout and gerrids share a similar food supply (terrestrial insects) so competition as well as potential predation may be occurring. Additionally, the increase in gerrid densities on the trout pool perimeter might cause increased intraspecific competition.

There is little other information on the nature of the predator-prey interaction involving surface Hemiptera, particularly in regard to palatability. The major purposes of this study, therefore, were to:

(1) Determine the palatability of various surface hemipteran prey to Gambusia affinis and Lepomis macrochirus in direct feeding experiments in the laboratory. Check by stomach analysis for any evidence that surface hemipterans are important in the natural diets of G. affinis and L. macrochirus. GENERAL SURVEY AND IDENTIFICATION

General surveys were conducted to determine species of surface Hemiptera present in Lake Matoaka and William & Mary Wildflower Refuge creek. Specimens were collected using a fine mesh net and preserved in 70% alcohol. The insects were keyed and identified to species using Bobb (1974),

Pennak (1978), and Usinger (1973). Final verification of species was made by comparison with preserved specimens in the Department of Entomology at the Smithsonian Institution in Washington D.C. A total of eight species was found as listed in Table 1 and pictured in Figures 1-4. Additional surveys in Waller Mill pond, Longhill Road marsh, Lake

Powell, and Crim Dell yielded no species other than the eight previously found. These were tested for palatibility as described in the following sections.

7 Table 1. Prey item information H G-H -H 4 O 44 rH Id 44 -H O G O T5 O G OPTS 0 0 0 4 0Pi 0 44 0 -H *H H -P «H E-« 4-1-H rH 44 - -P 0 -P O >i 0 ftft in u •rH •H rH ft 1—1 44 TS t f tft ft >\ g 0 0 > P p G G id 0 0 0 44 0 g > -H o -H o ft O C -H T3 t ft o g O ft ft ft ft 44 IPI PI g )pp p 0) 0) P p (U p in -P O 0 P P 0 0 4 44 g IPI PI 0) 0 P 0 g 0 0 0 0 G ft 0 0 1 G 0 1 0 0 0 i— i— o •*H •H 4 H -H *H +4 00 44 ft t f 0 44 g r G tr> P 0 G 0 d - -P -P id 0 0 £ G t f 0 p 0 p g 0 0 0 0 p O G O 0 0 0 G G 0 0 O 0 0 i • tr< i p rH rH 0 VO VO •H —1 r— ID 1 1— *H *H o +4 > -H 0 4> H +4 ip Pi J0 0 i 0 TJ a O 1 ft IS id g CD P in H G 0 — 0 P O' 0 0 P P P g tr 0 0 1 0 £ • • ) rH 1 in 0 0 ft ft 0 g g 0 ft P -rl -H i p i P•P -P CO CO -H o 1 -rH H r —1 c H r > g >4 44 44 O g —1 G G tr> did id UOP O G 0 G 0 0 O cd 0 > 0 O 0 0 g G P 0 0 0 0 0 O 0 3 • m +4 G G tJVH 4g a) +4 g CD DCD CD p 0 rd g > tr> CD •H H•H •H M C O C •H nO in 1— TS ft CM iH • 1 1 TS j p g 1 t f IS 1iH —1 (D 0 0 P id O —1 in P O > 0 O tr> 0 0 g 0 G 0 1 1 p 0 0 0 O G £ 0 0 • • • • 1 1 4 0 44 ft 0 P 0 PI 0 0 g g -H 1 CM 4-144 rH MO •rH 08 —1 ft 1 O ft g 1 1 44 XT' P 0 — CD —1 G —1 G O O P 0 0 ft G 0 O 0 0 O I l 0 1 G CD 44 P 0 *H tP p (D 0 44 G O 0 rd > 0 8 a. Trepobates inermis (adult-right, nymph-left) (Vertical bars denote millimeters in Figures 1-

b. Rheumatobates palosi 10

Figure 2. a . Rheumatobates tenuipes

b. Gerris marcrinatus Figure 3. a. Mesovelia mulsanti f f j 2i-T

b . Microvelia americana Figure 4.

a. Microvelia pulchella

3 MATERIALS & METHODS

Part I. Palatability tests.

This series of experiments was conducted to determine palatability of surface Hemiptera to gambusia and bluegill.

Experiments were conducted between July - September 19 87 and

June - August 1988. All were conducted in a windowless room maintained at 65°F, with normal laboratory fluorescent lighting and a photoperiod continually adjusted to coincide with the natural one. All fish were collected from Lake Matoaka. Gambusia were collected with a dip net, juvenile bluegill with a baited minnow trap, and adult bluegill by hook and line. Dechlorinated tapwater was used to fill eight 10-gallon tanks to a level 6 cm from the top (Figure 5), and two 3 0- gallon tanks to a level 10 cm from the top. Bottoms of the tanks were covered with a mixture of sand and gravel. Four of the 10-gallon tanks contained 5 gambusia each. Four size classes (28-32 mm, 33-37 mm, 38-42 mm, and 43-47 mm) were established, with each tank containing only one size class. The other four 10-gallon tanks contained three juvenile bluegill each. Four size classes (43-50 mm, 51-58 mm, 59-66 mm, and 67-74 mm) were established with each containing only one size class. Two adult bluegill (148 mm and 175 mm) were

13 14

Figure 5. Experimental tank set-up. 15 maintained separately in the two 3 0-gallon tanks.

A control feeding regimen was established to maintain a standard level of hunger and to monitor the fishes' general willingness to eat. All fish were fed daily between 10 am and 1:30 pm. The eight 10-gallon tanks, containing gambusia or juvenile bluegill, received 10 wingless Drosophila melanogaster (2-3 mm in length) per tank. The total number eaten after three minutes was recorded. Tetramin was then added in slight excess to satiate the fish. The two adult bluegill each received two crickets daily. Fish quickly became accustomed to the presence of humans and generally fed readily. After each feeding, tanks were aerated and filtered for two hours.

To replace any experimental fish that occasionally died, extra fish were kept in 2 0-gallon tanks, with the same feeding regimen as the experimental fish.

Surface Hemiptera were collected the day of or the day prior to testing, using a fine mesh net. In the field they were temporarily stored in a bucket with a screen bottom to prevent injury or drowning. The insects were then transferred in the lab to 2 0-gallon holding tanks containing 3 cm of water.

Table 1, as described, lists the surface Hemiptera species tested for palatability and their size, as well as the location and general habitat where they were collected.

Some of the species from Lake Matoaka were tested in 1987, with replicate testing in 1988. Rheumatobates tenuipes was not discovered until 1988; this species and the two stream 16 species (Gerris remigis and Microvelia americana) were tested only in 1988. These three species were tested only in 1988. Male Rheumatobates tenuipes and Rheumatobates palosi can be distinguished from the other and from females; females, however, cannot be easily distinguished by species. For this reason, only males of these two species were tested. For all other species males and females were morphologically similar, therefore, test organisms were not distinguished by sex.

All testing was done immediately prior to the normal feeding regimen, with only one species tested per day. To begin a test, a prey item was dropped into the middle of a tank. The fate of the item was categorized as one of the following five possibilities; 1) Attacked & Eaten; 2)

Attacked, Ingested, Rejected, Eaten; 3) Attacked, Ingested, Rejected; 4) Attacked but not Ingested; 5) Not Attacked. If the prey item was eaten, a fresh one was added immediately.

If the prey item was not eaten, it was removed after 3 minutes and a fresh one added immediately. This procedure continued for 5 trials per tank = 2 0 each for both gambusia and bluegill = 40 trials total. The regular feeding and aeration regimen was followed immediately after the tests.

One rest day or more, with the control feeding regimen only, was allowed between each series of trials.

The two larger prey (Gerris marginatus and Gerris remigis^ were tested only with the large bluegill. To obtain a total of 20 trials for each prey species, five trials per tank were performed as above twice, with rest 17 days in between each set of five trials. Fish occasionally had to be replaced because of death; when this happened testing was stopped until feeding was again normal under the control regimen. For all Gerridae species, legs were removed from prey in some trials to help distinguish the palatability factor from simple leg interference or the ability to avoid the predator.

Part II. Stomach analysis A preliminary study was conducted to verify that ingested gerrids could be identified in stomach contents. Gerrids were fed to gambusia, which were then sacrificed at one hour intervals for four consecutive hours. Even after four hours when the gerrids had passed out of the stomach into the intestine, legs and characteristic gerrid markings were still readily visible.

All fish, including adult bluegill, were collected in

Lake Matoaka within 3 m of shore in the general vicinity of all surface Hemiptera tested above except Gerris marqinatus,

Gerris remigis, and Microvelia american. Gambusia were collected using a dip net. Collections of five gambusia were made nine times on three separate dates (8/15/88,

8/23/88, and 9/25/88), providing 135 fish for analysis.

Each day three five-fish collections were made one hour apart starting approximately one half hour following sunrise; other collections were made at 11 am and 1 pm; and the final three collections preceded sunset at one hour 18 intervals with the final collection at sunset. Juvenile and adult bluegill were collected in the evening of 8/23/88 and the morning of 9/25/88. A total of 16 juvenile bluegill (<

7 0 mm) were captured with a bread-baited minnow trap. A total of six adult bluegill (> 150 mm) were caught by hook and line. After capture gambusia and juvenile bluegill were treated using a method similar to that of Flemer and

Woolcott (1966). Specimens were rolled in cheese cloth for five minutes to induce partial suffocation and then placed in a bottle containing 10% formalin. For adult bluegill, stomachs were removed immediately and placed in 10% formalin.

Stomach contents were examined using a dissecting microscope. Data were recorded in terms of presence/absence of various food items. For invertebrates the categories were generally based on identification to the order or family level. Plant/algal material was lumped in a single category. RESULTS

Part I. Palatability tests Palatability results are summarized in Tables 2-8.

Generally, all three smaller species of the family Gerridae (Trepobates inermis, Rheumatobates palosi, and Rheumatobates tenuipes) were palatable to both juvenile bluegill and gambusia. The larger Gerridae (Gerris marainatus and Gerris remigis^ were palatable to adult bluegill. However, all

Gerridae with legs were more difficult to capture and ingest than those with legs removed. Gambusia tended to reject the Mesoveliidae while juvenile bluegill ate them. Both gambusia and juvenile bluegill rejected both species of Veliidae.

A more detailed description of results follows below.

The statistical analysis reported involves pair wise comparisons of one insect species versus another with the

same fish predator, or of the response of one fish predator versus the other in regard to the same insect species. In all cases the test statistics are based on 2x2 contingency tables subjected. to X 2 analysis with ... critical values based on Yates' Correction for sample size and Sidak's multiplicative inequality for the total number of comparisons. Data used were for numbers eaten versus not

19 20 eaten, as described in the last two columns of Tables 2, 3, and 4, with totals combined for those experiments replicated in two different years.

As described, a control feeding regimen was used to make sure the fish were responding normally to addition of a prey item. Almost always, all ten control flies were eaten after experimental testing. However, on four occasions during the palatability testing the fish in a particular tank did not eat the controls normally. With Trepobates inermis (legs on) (Table 2 a, 1987) the gambusia in one tank ate only 1 of 10 control flies. With Trepobates inermis (legs removed) (Table 2 b, 1987) the gambusia in one tank ate only 4 of 10 control flies following testing. With Rheumatobates palosi (legs removed) (Table 2 d, 1987) the gambusia in one tank ate only 5 of 10 control flies. With

Rheumatobates palosi (legs on) (Table 3 c, 1987) the bluegill in one tank ate only 5 of 10 control flies. The data from each of those tanks for the respective tests has been discarded.

A. Gambusia Responses

Gambusia readily attacked members of the family Gerridae (Table 2 a-f) and readily ate gerrids with legs off but had difficulty capturing and ingesting individuals with legs on. Significantly fewer (P < .05) gerrids with legs on were eaten than gerrids with legs removed for all possible comparisons within and between gerrid species. For example in trials involving Trepobates inermis (Table 2 a), gambusia ate only 4/20 in 1987 and 5/20 in 1988 although many more in Table 2. Responses of Gambusia affinis to prey items. P rH E O id w w h

ft -V N "s ft si Wl I S t-3 w < M ft w P H a> <

H H •H 3 P T3 id O 1 P 01 d 0) id ) • a) P P •H H"rH •H IX IX) XI XI XI P-p -P p p i p s i oo o os O in H r O CM o o CO in 'c O' co O' HrH rH os o oo o o o o id rd a o o 01 C tP ' O tP CP CP tJ> tP Cr>CP c iP PI PI Pi -H Ert in rH CO as Ol rC p p p no'H* o in noOoi O O o O O in o O o in o c O <11 0) 01 0) 0) tft ft P a) )a a> a) d) 01 01 01 p e a) c *H HI—1 *H XI rH O rH J P< PIP «P

01 01 • • • . • "rH E 0O 0O OCO CO O' 00 O' 00 CO rn OS MCM CM OJ O o 0) g ai <11 h H•H •H -p XI XI -p 2 2 I PI PI HC O 0 - 0 O O rHrH rHCO iH ■vl< VOOS CO n o o rH o o o in o Sa os rH as OS r OO r rH O O O rH O o 9 o id E E id 10 uai 01 ai 01 IP G •rH I X 2 p p o CO O O O O o co rn CO r— CM P di id id ai 'O id id G G ai ai o P P G 01 ai >a 01 ai 01 01 a> 01 H > •H H O •H H 01 rH tn s i 1 • 01 rH • ai 01 o > d rH Id 1 01 01 ) "H 0) H*H -H i X O O OS VO CO s r o v rHrH CO ' r irH —i 00 rHO sa sas as as as MM* CM id E e P 101 01 id id G G G G -H 1—I S i—t oo no in o > id 0) a> o 0) 01 P

•H S -H 3 -H T3 X! > d a id *H HrH rH PI OJ o Or- r CO OCO CO H i—I rH CO O OJ O O O o MCM CM o > > 0) > 01 p id o 01 P id id e G ai 01 *rl •H — rH i—i x i rH s I PI PI O —i CM a p p 0 o id CPtP )Q) Q) 01 . "rH ■rH rH r—( X rH £ OS rH o O CO i—i CO as CM o 0) id H a ft id o ai P G 01

TJ p < w p -M ai O O Q) Q) id a) c J _p T T3 s ll

A/NI = Attacked but not Ingested NA = Not Attacked E = Eaten NE = Not Eaten 21 22 each case (9 & 15 respectively) were attacked. With the T. inermis legs removed (Table 2 b), gambusia captured and ingested 14/15 in 1987 and 20/20 in 1988. The same type of eating trend can be noted with both species of Rheumatobates

(Table 2 c-e). Gambusia had difficulty capturing

Rheumatobates palosi with legs on (Table 2 c) as evidenced by 4/20 eaten in 1987 and 1/20 in 1988. With legs off

(Table 2 d), 15/15 in 1987 and 20/20 in 1988 were captured and eaten. Gambusia captured and ate 11/2 0 Rheumatobates tenuipes with legs on and 20/20 with legs off (Table 2 e&f).

Gambusia readily attacked Mesovelia mulsanti (Table 2 g) , 19/20 in 1987 and 20/20 in 1988. However, only 3/20 in 1987 and 9/20 in 1988 were actually eaten. In addition, negative responses (rejection after ingestion) occurred: 7/20 in 1987 and 8/20 in 1988. Significantly fewer (P < .01 in all cases) M. mulsanti were eaten than any legless gerrid species.

Negative responses also occurred with both species of

Veliidae (Table 2 h&i). In 1988, 0/20 Microvelia americana were eaten, 8/2 0 were ingested and rejected, and 2/2 0 were not attacked at all (Table 2 h ) . In 1987, 6/20 Microvelia pulchella were attacked and eaten but 4/2 0 of these were ingested and rejected first, and 8/2 0 were not attacked

(Table 2 i). In 1988, only 1/20 M. pulchella was eaten and

9/2 0 were ingested and rejected (Table 2 i). Significantly fewer (P < .01 in all cases) M. americana and M. pulchella were eaten than any legless gerrid species. In most trials 23 thanatosis was a common behavior exhibited by both species of Veliidae which seemed to deter further attacks.

B. Bluegill responses

As with gambusia, juvenile bluegill readily attacked members of the family Gerridae (Table 3 a-f) and ate gerrids with legs removed but had difficultly capturing and ingesting gerrids with legs on. Significantly fewer (P <

.01) gerrids with legs on were eaten than gerrids with legs removed for all possible comparisons within and between gerrid species. In trials involving Trepobates inermis with legs on (Table 3 a), 10/20 in 1987 and 5/20 in 1988 were eaten. With legs off (Table 3 b), 19/20 in 1987 and 20/20 in 1988 were eaten. The same trend is evident with both species of Rheumatobates (Table 3 c-f). In trials involving Rheumatobates palosi with legs on (Table 3 c), 3/20 in 1987 and 7/20 in 1988 were eaten. With legs off (Table 3 d), bluegill ate 20/20 in 1987 and 20/20 in 1988. In 1988, only

4/2 0 Rheumatobates tenuipes with legs on (Table 3 e) were eaten but 20/20 with legs off (Table 3 f) were eaten.

Juvenile bluegill ate more Mesovelia mulsanti (Table

3 g) than gambusia (P < .01). Bluegill ate 19/20 in 1987 and 17/20 in 1988 while gambusia ate 3/20 in 1987 and 9/20 in 1988. The bluegill response to M. mulsanti is not significantly different from their response to T. inermis with legs off (Table 3 b&g). As with gambusia, the majority of both species of Veliidae (Table 3 h&i), were not eaten as compared to species of Gerridae (P < .01) and negative responses occurred. In 1988 (Table 3 h ) , 1/20 Microvelia Table 3. Responses of juvenile Lepomis macrochirus to prey items. P l E H r E (0 ai wi O h

Oi p >\ dl \ < w M s H >H < Cl rd WI p l C 0) 10

-H E -H X) O d) P P a oi

-H A A A A r •rH•rH 4-> id p W W w w w w w w w W W Hr r H iH rH rH rH rH O H O O O O O O O O O O O o o o o o o CN O o o rH O CN O O O O O O O O o CO O' CO O' 00 O' Hr H rH rH rH rH CO O d) d< drd rd

•H E - - 4-1 4-* 4-> ldl p dl Q O o CO dl (/) )ci d) EJ m n o h J 1 o M1 O O n OJ O H A E •rH 4 4 <44<44 <44<44 P P <44<44 P P ON O ON o O rH 0 00 CO 00 00 00 o o CN H r O ON O rH dl C/lC/1 G £ W > d> d> CP CP CP CP CP CP CP m h • in •H *«H E id) di O di a> G e m h ■*5 •rH 4-1 A 4-1 rH o CO O' o o o O' CO G o o £ rH rH rH rH rH rH o o CN rH o in rH rH O drd rd N NO O N NO ON ON ON ON ON ON ON ON m ON OJ fd i •rH E p ww ^ ^4—1 W 4^ W 4^ w w w w <44<44 dl o o o o o o CN CN CN £ co co 00 O' CN CN O rd O 00 CO OJ CN OJ o o o o rd C/l di rd / C/l C/l ) >d d ) )d) d) a) d) dl d> d) CP CP CP CP CP CP CP . . • A *H A 4J 4-1 rH dl G £ rd rd O dl c/l rd A P *H E E -Pi dl<44 ldl G dl G o o £ drd rd CN CN CN CN CN co co CN CN o o rH ■*J* O o VO rd O O ldi dl C/l G G ld) dl G a n in in G <44 G E S *H P p P <44 O OJ £ OJ rd in G a

< O * -H rH rH P> E > CP E O dl •O i • di in 0 E > l 01 dl rd dl -rH •rH rH rH P / l/l 1/1 O CN O NO O O' ON o © rH O rH rH rH CO rH O O O ' 00 ' CO O' O O 00 rH rH o 00 O' O O O' ON £ £ rd o oco co oo / )01 P G 0) C/1 rd rd G CP CP CP c/i G G G •H * rd dl G G in •rH • rH T3 *H T3 d O rd i • di h E •H •H rH rH in > > > H H CN rH O ON rH CN O O rH CN )dl d) ON rd rd £ O rd rd G CP / w (/I •H •rH •H E —1i— t i— 1 Hr— t rH E rH rH u O O O P p O O O CO rH O rH ON VO (—i H rH rH co co CN CN O rH o N ON ON rn ro ro rn drd rd G P G O O ldl dl drd rd ) 0) d) CP CP CP G G . •rH •H E E i— i i— I a O dl a in < < \ * * H W 4-> -p c c c XS *3 0) 4-1 w c w ii ii rd a 0) d) d) 4-1 C tocn T3 s s? w •n TJ H XI 4-1 4-1 E w m d> a) 0) O ai (0 0) c

A/I/R = Attacked, Ingested, Rejected A/NI = Attacked but not Ingested NA = Not Attacked E E = Eaten NE = Not Eaten 24 25 americana was eaten, 11/2 0 were ingested and rejected and 5/20 were not attacked. In 1987 (Table 3 i), 1/20

Microvelia pulchella was eaten but rejected first, 6/2 0 were ingested and rejected, and 13/2 0 were not attacked. In 19 8 8 (Table 3 i), no M. pulchella were eaten, 9/20 were ingested and rejected, and 3/2 0 were not attacked. As with gambusia, in most trials thanatosis was a common behavior exhibited by both species of Veliidae which seemed to deter further attacks. Adult bluegill had great difficulty capturing both

Gerris marginatus and Gerris remigis with legs on (Table 4) because the gerrids were continually able to run away from the fish. Only 1/20 G. marginatus (Table 4 a) and 0/20 G. remigis (Table 4 b) were eaten although most were attacked. With legs removed, bluegill ate 20/20 G. marginatus (Table 4 a) and 19/20 G. remigis (Table 4 b). Significantly fewer (P < .01) gerrids with legs on were eaten than gerrids with legs removed for all possible comparisons within and between both gerrid species.

C. Average number of attacks per prey item

An analysis of the average number of attacks per prey item is summarized by prey species in Table 5 (gambusia) and

Table 6 (bluegill). There is a trend involving palatable verses unpalatable prey items. Gambusia (Table 5) made 5.97 attacks on T. inermis with legs on but only 2.65 on M. americana and 2.2 on M. pulchella. Bluegill (Table 6) made

3.6 attacks on T. inermis with legs on but only .5 attacks on M. americana and 1.05 on M. pulchella. Overall, bluegill Table 4. Responses of adult Lepomis macrochirus to prey items in 1988. -p I E —I o w Si rd h HI I H H H si <\ s 1 < H P-i 1 0 H H l d o p a)

H•H •H •H i-P +i o o o o o o o o in OO O o ^ VO o r ocr> o o I — i o o H S lo Cl o u p p tJ G (0 G 01 rd (11 o g <0 P 01 ■ . •rH N I-H ON H cn iH o N C p p O' G rd G 01 10 01 01 01 g rd p -H •H •rH a\ 43 i T C H i O O H S 01 P P P p p o CD ai g rH *H •rH *H rH H r 01 P o di ai g P P P-P -P -P -P -P -P -P -P 2 2 242 42 42 42 TJ T* T3 TJ G H t r] rtj rt] rtj eg c dt tn tn rd d) O o O d) dr rd rd rd II II II II P P -P -P -P -ro*ro -P -P -P T T J TJ -p 73 TJ H H P H H

a) -P 43 tn G O G O rd II

-P P P -P -P -P -P 42 s < HS H S < dl rd O O III II H S H dO rd dl G -P H rd dl G II

26 Table 5. Mean number of Gambusia affinis attacks per prey item. Size classes of fish and replicate experiments from different years are combined. -P P - H O rH -Q "H h rd Eh -P O p 0 rd (0 > a> CD P O rd n t a) ) 4-> Q)

u c M ai p \ > ai n Cl

H - E J T £ D C d p P rd P P 0) 0) -H -H H - -P XI I P i P o o O C O C n i n i a> - o n i o\ Cl l/l a o 0) rd e p s ) a) a) n t G G a) m m n i G h • • CM o o co co o o CM Cr> -H X - h p P O ai l/l p l/l ia i a ai ai o rd ci H - n P-P -P — i—i i—l X -p 2 2 s i P i P i P I P o o o o 3 CO04 04 0 4 0 O C n i -3* o o oin o n i vo co 3 i1^ 04 ^ i—1 ^3* dr rd G e rd rd dr rd o rd rd / / l/l i/l ai l/l P P rd l/l l/l / l/l l/l ) )c a> ci a) a) > U n t G O . . H - X X -P G O dCD rd m DCD £ Cl d a) rd CDrH -rH •H p - i I P O "d* o — O Ovo VO > rd £ in G m G ci 01 G G n t . . i H - H - H r £ TJ > d H - H - rd 01 o o -rH -rH 1—1 i p O o 4 0 O n i 04 P G rd oi o > Cl p rd rd Cl g U rd -H rH ,C rH 1—1 l £ I P O o — 04 04 rd G o ai rd l/l G Cl ' O o > ai p P • 1 27 Table 6. Mean number of juvenile Lepomis macrochirus attacks per prey item. Size classes of fish and replicate experiments from different years are combined. 4-1 Xi P - -P -P i—I o E • O g -P OJ 0 o -P -P o h p -rH rd

&4 P > P 0 > p a) Pi Gl •H o 0 P rd 0 -H vo co o o o o PI PI o o Pi Pi G P g 0 0 0 C G 0 • p 0 0 CP •H £* -P E H r 4-1 H 4 p rd rd 0 O 0 0 c 0 p g 0 h •

-p n -P o o M C O O vo o 3 M C M C -3* O C o in I P Pi PI PI Pi o o 0 G g rd o rd 0 0 i P i P 0 G 0 • 0 0 s S 0 0 0 O > d 0 rd i—I 0 -H -H I—I p-p H i nO in PI H4 O o o rd G g 0 G rd rd 0 tp G 0 G . . .

•H -H i-H TS > 0 d h *h rd 0 S o •H •H i—I o in PI o 4 H M C p O > 0 rd rd g 0 p O rd G rd 0 C 0 p

-H •rH l—l Xi S' I—I i in o PI O o u p o > 0 —i rd i P G O 0 rd 0 C 0 G p 28 29 made fewer attacks per prey item than gambusia. Gambusia were more persistent in attacks than bluegill. For example, gambusia (Table 5) made 5.97 attacks per T. inermis with legs on while bluegill (Table 6) made only 3.6 attacks. D. Number of prey items eaten as a function of fish size class. There were no strong apparent trends regarding the number of prey items eaten as a function of fish size class (Tables 7 & 8). In some cases one fish size class ate more prey items than another. For example, the largest size class of gambusia (43-47) ate 6/10 M. pulchella while the smaller size classes (28-32, 33-37, and 38-42) ate 1/10, 0/10, and 0/10 respectively. However, sample sizes are too small within size groups to do any meaningful comparisons.

Part II. Stomach Analysis

The gambusia stomach analysis (Figure 6 a) results for the 3 collection dates (8/15/88, Table 9; 9/22/88, Table 10;

& 9/25/88, Table 11 respectively) can be summarized as follows. Both Diptera larvae and pupae were a common part of the diet, with larvae found in 50%, 3 0%, and 2 5% of the fish and pupae found in 3 0%, 5%, and 27.5%. A variety of unidentified, apparently insect parts were also common and were contained in 25%, 37.5%, and 22.5% of the fish. Plant material was found in 40%, 32.5%, and 32.5% of the fish.

Other identifiable Insecta, Crustacea, Arachnidae, and

Mollusca were all less common with occurrence ranging up to

15%. Table 7. Total number of prey items eaten by Gambusia affinis as a function of size class. Data from replicate experiments combined. H CO -H p c i—i U Ui eg E rd co i o 01 CO N 1 O 'st* ' - r co GP CO CM CO CM CO CO P 0 l 1 1 -H J EH TJ O 0 P P p P cd ) )a) a) a) -rH -rH•H W W -P i P n i—i in w w rH rH ■—i i—i i in rH w w o o O CM o o o o H rH rH o o cry in o o in rH i i—1 iH O O tp ) o )0 0 0 a) i o *H EH -p Si O 1 - r iH CL o CL 3 0 01 -H o — a) ■—i S TJ > a) 0 in > Cd "H O 0 -rH \ -rH 1 in \ \ I—1 in o o in o in — O p dCL cd cd > > 0 o P o ai G E G cd cd tp 01 1 -rH -H \ \ rH rH O vo s \ i—1 Si \ o o rH rH o o O rH o pi rH rH o P O cd 0 0 O 0 0 c tp 0 cd ) ) 30 Table 8. Total number of prey items eaten by juvenile Lepomis macrochirus as a function a a function of size class. Data from replicate experiments combined. Cd O' vo cy\ in CO lo vo vo o in o in H m )Pin P P d) >1 i 1 1 I ■H J E TJ 0 n n n n t n t tn tn tn tr> tn d> tp tr> G a> H < G in h •rH \ \ A 1—1 o rH O i—1 0) 0) Ej - \ J02 & N \ P P P P N ■P O O in i—1 O i—1 OJ i—I *— -p O CO a G 0 h H■H •H £ \ nin in cd -P -P \ \ in in rH 1—1 in CVJ - nin in IPJ PI 0) G p. in rd * H O -H — d)i—i 2 J O > TJ Dd) h O £ d) ) rH 0) d d) rd in •rH “H N t—i rH i—i cn O rH o a\ rH -p o i—i PI O 00 in in G rd a) dP £ G rd G -H -rH i—1 J £ TJ > ) o d) rd *H H-H -H *H \ \ o \ tn in i—i in — i—1 r—1 o in o Pi O P d) > > in G G g drd rd rd )d) d) O G drd rd d) rd -rH \ \ \ \ £ o o i—1 i—1 O o rH rH 1—1 i—1 ,G O o o i—1 rH PI O o p in a o d) O d> G 31 32

Figure 6. a. Typical contents of a Gambusia affinis stomach including several Diptera larva.

b. Gambusia affinis stomach containing nymphal Trepobates inermis. 33

Table 9. Stomach analysis results for Gambusia affinis (8/15/88). Data expressed as percent of fish containing the item, for variousi times of day

%Stomachs with item n=15 n=10 n=15 Total Item Morn Mid Eve n=4 0 Insecta Coleoptera 0.0 0.0 13 . 3 5.0 Diptera (larva) 60.0 60. 0 33 . 3 50.0 Diptera (pupa) 60.0 10. 0 13 . 3 30.0 Ephemeroptera 0.0 0.0 6.7 2.5 Unidentified 26.7 50. 0 20.0 30.0 insect parts Arachnida Araneida 0 . 0 20.0 0.0 5.0 Hydracarnia 0.0 0.0 6.7 2 . 5 Crustacea Cladocera 6.7 10. 0 13 . 3 10. 0 Ostracoda 0.0 10.0 33.3 15. 0 Mollusca Gastropoda 0 . 0 0.0 6.7 2 . 5 Plant Material 20.0 40 . 0 60. 0 40 . 0 34

Table 10. Stomach analysis results for Gambusia affinis (8/22/88). Data expressed as percent of fish containing the item, for various times of day.

%Stomachs with item n=15 n=10 n=15 Tota Item Morn Mid Eve n=4 0 Insecta Diptera (1arva) 40.0 30.0 20.0 30.0 Diptera (pupa) 13 . 3 0.0 0 . 0 5.0 Ephemeroptera 0.0 10. 0 0 . 0 2 . 5 Hemiptera Gerridae 80.0 30.0 0 . 0 37.5 Megaloptera 0.0 0.0 6.7 2 . 5 Odonata 0.0 0.0 13 . 3 5.0 Unidentified 40.0 40.0 33 . 3 37.5 insect parts Arachnida Araneida 0.0 0.0 13 . 3 5.0 Crustacea Cladocera 6.7 10.0 0.0 5.0 Ostracoda 0 . 0 10. 0 0 . 0 2 . 5 Unidentified 0.0 0.0 6.7 2 . 5 Plant Material 33 . 3 40.0 26.7 32 . 5 35

Table 11. Stomach analysis results for Gambusia affinis (9/25/88). Data expressed as percent of fish containing the item, for various times of day.

iStomachs with item n=15 n=10 n=15 Tota! Item Morn Mid Eve n=4 0

Insecta Diptera (larva) 46.7 10.0 13 . 3 25.0 Diptera (pupa) 33 . 3 40.0 13 . 3 27.5 Ephemeroptera 6.7 0.0 0.0 2.5 Hymenoptera 6.7 0.0 6.7 5.0 Unidentified 20.0 30.0 26.7 25.0 insect parts Crustacea Cladocera 6.7 20.0 6.7 10.0 Ostracoda 6.7 20.0 6.7 10.0 Mollusca Pelecypoda 0.0 10. 0 6.7 5.0 Plant Material 6.7 20.0 66.0 32 . 5 36

The main focus of the stomach analysis collections was to determine the importance of surface Hemiptera in the diet of fish. Out of the total 13 5 gambusia stomachs examined only 15 (11.1%) contained surface hemipterans; all were from the same day. Specifically, on the second collection date (Table 10) nymphal Trepobates inermis (Figure 6 b) were found in 12/15 (80%) of the morning collection stomachs and in 15/40 (37.5%) of the stomachs for that day. The percent occurance for bluegill in each of the two categories (juvenile and adult) are combined for dates of collection. The most common contents (Figure 7) of juvenile bluegill (Table 12) included Diptera larva (75%), unidentified insect parts (37.5%), ostracods (75%), and plant material (25%). All the large bluegill collected contained Diptera larva and plant material (Table 13). There was no indication of surface hemipterans in any bluegill stomach samples examined. 37

Figure 7. Typical stomach contents of a juvenile bluegill stomach containing Diptera larva and several small Pelecypoda 38

Table 12. Stomach analysis results for juvenile Leoomis macrochirus in 1988. Data expressed as percent of fish containing the item.

%Stomachs with item 8/23 9/25 n=10 n=6 Total Item Morn Eve n=16

Insecta Diptera (larva) 90.0 50.0 75. 0 Odonata 10.0 0.0 6.2 Unidentified 30.0 0.0 18 . 8 insect parts Crustacea Amphipoda 10.0 0.0 6.2 Cladocera 50.0 50.0 50.0 Ostracoda 90.0 50. 0 75. 0

Mollusca Pelecypoda 10.0 0.0 6.2

Rotifera 20.0 0.0 12.5

Plant Material 20.0 33 . 3 25.0 39

Table 13. Stomach analysis results for adult Lepomis macrochirus in 1988. Data expressed as percent of fish containing the item.

%Stomachs with item 8/23 9/25 n=2 n=4 Total Item Eve Morn n=6 Insecta Coleoptera 0.0 25. 0 16.0 Diptera (larva) 100. 0 100. 0 100. 0 Hymenoptera 0.0 25. 0 16. 0 Unidentified 0.0 25.0 16. 0 insect parts

Crustacea Amphipoda 0.0 25.0 16.0 Isopoda 50.0 0.0 16. 0

Rotifera 0.0 25.0 16. 0 Plant Material 100.0 100. 0 100 . 0 DISCUSSION

It has been suggested that the secretion of the metathoracic scent glands serves as a defensive chemical in surface Hemiptera (Anderson 1982a). However, none of the five species of the family Gerridae tested were found to be inherently unpalatable to gambusia or bluegill. Although a tank is an extremely artificial situation which greatly hinders the escape of the insect prey, many gerrids did escape within the three minute time interval. Mere speed and agility are apparently the main defensive agents of the Gerridae.

The two species tested from the family Veliidae, Microvelia americana and Microvelia pulchella. were unpalatable to both gambusia and bluegill. Similarly, a member of the same family, Velia caprai, was unpalatable to brown trout (Bronmark et al. 1984). Veliidae are smaller in size and slower in movement than gerrids, and in the laboratory were caught more readily than intact gerrids with legs on. Consequently, the chemicals produced by the veliid metathoracic scent gland might be subject to selective pressures directed more towards distastefulness, as a better defensive strategy. Thanatosis seems to deter additional attacks. Another possibility for the rejection of the

40 41

Veliidae is from an energy stand point for the fish. Perhaps the organisms were too small to provide an energetically efficient amount of food. The control organisms were the same size as the smallest test organisms

(Veliidae), therefore, size alone might not be an adequate explanation for the reluctance of the fish to eat these prey items. It is difficult to speculate why bluegill readily ate and gambusia rejected Mesovelia mulsanti. Perhaps the degree of distastefulness has something to do with size of the predator in proportion to the prey, as the bluegill were generally larger than the gambusia. There was no apparent trend in the number of prey items eaten as a function of fish size class. For both gambusia and bluegill, responses differed to palatable and unpalatable prey items. Palatable prey items were attacked more (even with legs on) than unpalatable prey items.

Perhaps avoidance was learned quickly after exposure to the unpalatable prey item. There did seem to be a difference in the average number of attacks per prey item between bluegill and gambusia. Gambusia were more persistent in attacking than bluegill.

Of the 12 0 gambusia examined, a total of 15 fish contained gerrids. Since the majority of fish containing gerrids were taken during one morning time interval, the importance of gerrids in the gambusia diet seems to be sporadic at best. It is also interesting to note that no adult gerrids were found in stomachs. One can only 42 speculate about the reason for the abundance of nymphal T. inermis found at this particular time period. Maybe some type of material such as an algal bloom or pollen on Lake

Matoaka (personal observation) was interfering with the surface tension of the water and inhibiting normal locomotion by the gerrids. The lack of M. mulsanti. M. americana. and M. pulchella in any of the gambusia or bluegill suggests that the same defensive mechanism(s) that deterred predation in the lab may be working in the field. In addition, Veliidae and Mesoveliidae are also found often on or near vegetation in very shallow water, perhaps decreasing the chance of predator interactions. The stomach analysis results suggest that gerrids may only be an incidental and sporadic part of the gambusia diet. However, this does not mean that there is no interaction in the field. Gambusia commonly occupy the surface layer of very shallow water close to shore around submerged vegetation (personal observation). Juvenile bluegill and other sunfish occupy the more vegetated habitats somewhat deeper and more distant from shore and thereby segregate themselves from the large piscivourous fish (Mittelbach 1988, Werner et al. 1977). Frequent casual observations on the field distribution of gerrids suggests that in the presence of gambusia there is a definite avoidance of the shallow water near shore. Gambusia may be maintaining the gerrids in separate territory just as trout forced gerrids to the perimeters of pools (Cooper 1984).

One may also look at the relative lack of surface 43

Hemiptera from gambusia and bluegill stomachs and their segregated distribution in the field from a competition standpoint (see Krebs & McCleary 1984 for a general review).

Even if fish generally can't capture gerrids, gerrids may be maintaining distance to conserve energy in this case just as gerrids may have segregated themselves from trout (Cooper

1984). This is especially true when gerrids and fish may be competing for a similar resource — insects trapped in the surface layer of water (Cooper 1984). LITERATURE CITED

Anderson, N. Moller. 1982a. Adaptations & Ecological Diversifications. Pages 263-351 in The semiaquatic bugs (Hemiptera, Gerromorpha). Scandinavian Science Press Ltd. Klampenborg, Denmark. Anderson, N. Moller. 19 82b. Phylogeny of the Gerromorpha. Pages 22-61 in The semiaquatic bugs (Hemiptera, Gerromorpha). Scandinavian Science Press Ltd. Klampenborg, Denmark. Benfield, E.F. 1972. A defensive secretion of Dineutes discolor (Coleoptera: Gyrinidae). Annals of the Entomological Society of America 65(6):1324-1327. Bobb, Marvin L. 1974. The aquatic and semi-aquatic Hemiptera of Virginia. Virginia Polytechnic Institute and State University. Blacksburg, Virginia. Bronmark, C., B. Malmqvist, and C. Otto. 1984. Anti­ predator adaptations in a neustonic insect (Velia caprai). Oecologia 7:75-89.

Butler, Mark J. 1989. Community Respones to variable predation: Field studies with sunfish and freshwater macroinvertebrates. Ecological Monographs: 59(3):311- 328.

Carlander, Kenneth D. 1969. Mosquitofish-Gambusia affinis. Page 5 68 in Handbook of freshwater fishery biology. Volume One. The Iowa State University Press, Ames, Iowa.

Carlander, Kenneth D. 1977. Bluegill-Lepomis macrochirus. Pages 73-118 in Handbook of Freshwater Fishery Biology, Volume Two. The Iowa State University Press, Ames, Iowa.

Cooper, Scott D. 1984. The effects of trout on waterstriders in stream pools. Oecologia 63:376-379.

Flemer, David A., and William S. Woolcott. 1966. Food Habits and distribution of the fishes of Tuckahoe Creek, Virginia, with special emphasis on the bluegill, Lepomis m. macrochirus Rafinesque. Chesapeake Science 7:75-89.

44 45

Harrington, Rober W. Jr. and Eleanor S. Harrington. 1961. Food selection among fishes invading a high subtropical salt marsh: From onset of flooding through the progress of a mosquito brood. Ecology 42(4):646-666.

Kerfoot, W. Charles. 1982. A question of taste: Crypsis and warning coloration in freshwater zooplankton communities. Ecology 63(2):538-554

Krebs, John R. and Robin H. McCleery. 1984. Optimization in behavioural ecology. Pages 91-121 in John R. Krebs and N.B. Davis, editors. Behavioural Ecology. Sinauer Associates Inc, Sunderland, Massachussets. Mittelbach, Gary G. 1988. Competition amoung refuging sunfishes and effects of fish density on littoral zone invertebrates. Ecology 69(3):614-623. Pennak, Robert W. 1978. Hemiptera (Bug). Pages 567-585 in Freshwater invertebrates of the United States, Second edition. John Wiley & Sons. New York. Polhemus, John T. and Harold C. Chapman. 197 9. Family Gerridae, Pages 58-69 in Arnod Menke editor. The semiaquatic and aquatic Hemiptera of California (Heteroptera: Hemiptera). University of California Press, Berkeley California. Schildknecht, H., R. Siewerdt, and U. Maschwitz. 1966. A vertebrate hormone as defensive substance of the water beetle (Dvtiscus maroinalis). Angewante Chemie, International Edition in English 5(4):421-422. Scrimshaw, Steve and W. Charles Kerfoot. 1987. Chemical defenses of freshwater organisms: beetles and bugs. Pages 240-262 in Predation: Direct and indirect impacts on aquatic communities. University Press of New England. Hanover, New Hampshire.

Turner, William R. 1955. Food habits of the bluegill Lepomis macrochirus (Rafinesque), in eighteen Kentucky farm ponds during April and May. Transactions of the Kentucky Acadamy of Science 16(4):98-101.

Usinger, Robert L. 1973. Aquatic Hemiptera. Pages 182-228 in Aquatic insects of California. University of California Press, Berkeley.

Werner, Earl. E. Donald J. Hall, Dennis R. Laughlin, Donald J. Wagner, Leni A. Wilsmann, and Frederick C. Funke. 1977. Habitat partitioning in a freshwater community. Journal of Fisheries Reserve Board Canada 34:3 60-370. VITA

Julie Heyward Mounts

Born in Park Ridge, Illinois October 13, 1964.

Graduated from Adlai E. Stevenson High School, Prairie View Illinois, June 1982. Received a B.A. degree in Biological

Sciences from DePauw University, Greencastle, Indiana in May 1986. Entered graduate school at the College of William and

Mary in August 1986. Currently a candidate for the degree of Master of Arts in Biology.

46