yin}. 5,3, .l- .0 a u .‘ 1" twin..’$uf“\“a.! Bra. 1 u Hflfi: .....r.m...mv3.- _....,........f........r fawn} S. umwsrta. .21. him. 5...). 1...... ul. 1.9.! l.fl...¢....,hl éi.:c>7u-..Ml znflwwf " LIBRARY 2 008 Michigan State University This is to certify that the dissertation entitled CHARACTERIZATION OF AN ANCESTRAL GLUCOCORTICOID HORMONE AND ITS COGNATE RECEPTOR IN THE SEA LAMPREY presented by David A. Close has been accepted towards fulfillment . of the requirements for the . PhD. degree in Fisheries and Wildlife / M/W‘V Major Professor‘s Signature /0 ”66944” 20757 Date MSU is an afi‘innative-action, aqua/opportunity employer PLACE IN RETURN BOX to remove this checkout from your record. TO AVOID FINES return on or before date due. MAY BE RECALLED with earlier due date if requested. DAIEDUE DAIEDUE DAIEDUE 6/07 p:/ClRC/DaleDue.indd-p.1 CHARACTERIZATION OF AN AN CESTRAL GLUCOCORTICOID HORMONE AND ITS COGNATE RECEPTOR IN THE SEA LAMPREY By David A. Close A DISSERTATION Submitted to Michigan State University In partial fulfillment of the requirements For the degree of DOCTOR OF PHILOSOPHY Department of Fisheries and Wildlife 2007 ABSTRACT CHARACTERIZATION OF AN AN CESTRAL GLUCOCORTICOID HORMONE AND ITS COGNATE RECEPTOR IN THE SEA LAMPREY By David A. Close The goal of this research was to determine if one of the oldest extant vertebrates possesses a stress steroid hormone. Previous studies have been unsuccessful in determining if lampreys have a stress steroid. In order to confirm that a molecule is a hormone, the following criteria must be met: 1) definitive chemical identity, 2) a cognate receptor for that molecule, and 3) the molecule must mediate biological effects. Evidence is provided that 11-deoxycortisol is an ancestral stress steroid hormone in sea lampreys (Petromyzon marinas). The current study demonstrated the isolation and identification of two putative glucocorticoids from the blood of the lamprey, 11- deoxycortisol and ll-deoxycorticosterone. Both of these steroids were screened using radioimmunoassays and isolated by chromatography techniques. Positive identification of both steroids was by use of mass spectrometry. The study provided evidence that 11- Deoxycortisol has a receptor in the gill cytosol of the lamprey. The binding moiety for ll-deoxycortisol showed high specificity, affinity, and low capacity in the gill cytosol. Specific binding was highest in the intestine followed by gill, testis, liver, kidney, heart, and muscle. In addition, specific binding of the receptor complex to DNA was demonstrated by DNA-cellulose chromatography. The study showed that circulating levels of 1 l-deoxycortisol sharply increase after acute stress in spawning phase lampreys. The stress hormone responds to acute stress in parasitic stage lampreys also. Slow release ll-deoxycortisol implants increased circulating ll-deoxycortisol and decreased classic androgens and estrogens. In addition, the implants increased gill Na+, K+-ATPase activity in lamprey. The study demonstrated that mammalian corticotropin releasing hormone increased ll-deoxycortisol. Pituitary extracts also increased circulating 11- deoxycortisol in a dose-response manner. Overall, these results are the first to demonstrate that the ancestral vertebrate, the sea lamprey, has a stress steroid hormone. In conclusion, this study demonstrated evidence for the identification, receptor, and biological effects of l l-deoxycortisol. ACKNOWLEDGEMENTS A special thanks to my advisor Dr. Weiming Li and the members of my graduate committee, Dr. Tom Coon, Dr. Don Garling, and Dr. Ken Poff for their guidance and support. A warm thanks to Dr. Sang-Seon Yun for guidance and support. Support from Dr. Alexander Scott was appreciated. A special thanks to Dr. Brad Young for editing and support. I am grateful to the staff of the US. Geological Survey, Hammond Bay Biological Station for supplying laboratory space and sea lampreys. Bonneville Power Administration for providing finding and support for this research. I am grateful to Michigan State University and the National Institute of Health for fellowships. A warm thanks to the Confederated Tribes of the Umatilla Indian Reservation for support of this research. iv TABLE OF CONTENTS LIST OF FIGURES .......................................................................................................... vii INTRODUCTION ............................................................................................................... 1 Concept of stress ...................................................................................................... 1 Stress in fish ............................................................................................................. 4 Functions of corticosteroids ..................................................................................... 6 Lamprey as a model system ..................................................................................... 7 Introduction of dissertation ...................................................................................... 9 References .............................................................................................................. 11 CHAPTER 1 IDENTIFICATION OF PUTATIVE GLUCOCORTICOIDS IN THE SEA LAMPREY Petromyzon marinas .......................................................................................................... 15 Abstract .................................................................................................................. 16 Introduction ............................................................................................................ 17 Materials and methods ............................................................................... 21 Maintenance of animals and blood collection ........................................... 21 Plasma extraction ....................................................................................... 21 High performance liquid chromatography ................................................. 22 Radioimmunoassay (RIA) and protein binding assay (PBA) procedures .................................................................................................. 22 LH-20 column chromatography ................................................................. 23 Mass spectrometry analysis of plasma ....................................................... 23 Results .................................................................................................................... 25 Discussion .............................................................................................................. 32 Acknowledgements ................................................................................................ 36 References .............................................................................................................. 37 CHAPTER 2 CHARACTERIZATION OF A GLUCOCORTICOID RECEPTOR IN THE GILL OF THE SEA LAMPREY Petromyzon marinas ..................................................................... 39 Abstract .................................................................................................................. 40 Introduction ............................................................................................................ 41 Materials and methods ............................................................................... 43 Animals and holding facilities ................................................................... 43 Materials .................................................................................................... 43 Preparation of cytosolic fractions of tissues .............................................. 43 Saturation curve and scatchard analysis .................................................... 44 Association and dissociation kinetics ........................................................ 45 Steroid and tissue binding specificity ........................................................ 45 DNA-cellulose chromatography ................................................................ 46 Results .................................................................................................................... 48 Discussion .............................................................................................................. 55 Acknowledgements ................................................................................................ 60 References .............................................................................................................. 61 CHAPTER 3 BIOLOGICAL ROLES OF ll-DEOXYCORTISOL IN MEDIATING STRESS RESPONSES OF THE SEA LAMPREY Petromyzon marinas ....................................... 64 Abstract .................................................................................................................. 65 Introduction ............................................................................................................ 66 Materials and methods ............................................................................... 69 Source of animals ....................................................................................... 69 Handling and salinity stressors .................................................................. 69 Radioimmunoassay (RIA) procedure ........................................................ 7O Steroid implants ......................................................................................... 71 Gill Na+, K+-ATPase activity ..................................................................... 71 Corticotropin releasing hormone injections ............................................... 72 Pituitary extract injections ......................................................................... 72 Statistical analysis ...................................................................................... 73 Results .................................................................................................................... 74 Discussion .............................................................................................................. 86 Acknowledgements ................................................................................................ 90 References .............................................................................................................. 91 SUMMARY OF DISSERTATION ................................................................................... 96 vi LIST OF FIGURES Chapter 1 Figure 1-1. Screening of HPLC fractions of lamprey plasma for cortisol-like steroids using RIA and BPA. (A) Amount of immunoreactive cortisol found in 0.5 ml HPLC fractions from RIA of 20 pl of each fraction and back calculated fraction volume. (B) Amount of cortisol binding activity found in 0.5 m1 HPLC fractions from BPA of 20 ul of each fraction and back calculated to fraction volume. An arrow shows where cortisol and 11-deoxycortisol standard eluted. ir = immunoreactivity. .......................................... 27 Figure 1-2. Screening of HPLC fractions of lamprey plasma for corticosterone-like steroids using RIA. Amount of immunoreactive corticosterone found in 0.5 ml HPLC fractions from RIA of 20 ul of each fi‘action and back calculated to fraction volume. An arrow shows where corticosterone and 11-deoxycorticosterone elutes. ir = immunoreactivity. .............................................................................................................. 28 Figure 1-3. Screening of LH-20 fractions of lamprey plasma for immunoreactive 11- deoxycortisol and ll-deoxycorticosterone by RIA. Amount of immunoreactive 11- deoxycortisol and ll-deoxycorticosterone found in LH-2O fractions from 800 ml of sea lamprey plasma based on RIA of 20 pl of each fraction and back calculated to fraction volume. ir, immunoreactivity ............................................................................................. 29 Figure 1-4. Identification of 1 l-deoxycortisol in the plasma of sea lamprey. APCI MS/MS analysis (positive mode) of authentic 11-deoxycortisol steroid from a 10 ug ml'1 stock solution (A) and HPLC fraction corresponding to immunoreactive fraction for 11- deoxycortisol from 800 m1 lamprey plasma extract (B). ................................................... 30 Figure 1-5. Identification of l 1-deoxycorticosterone in the plasma of sea lamprey. APCI MS/MS analysis (positive mode) of authentic ll-deoxycorticosterone steroid from a 10 u g ml‘1 stock solution (A) and HPLC fraction corresponding to immunoreactive fraction for 11-deoxycorticosterone fi'om 800 ml lamprey plasma extract (B). ............................. 31 Chapter 2 Figure 2-1. Representative saturation curve (A) and hyperbolic regression plot (B) of 11- dexoycortisol binding to gill cytosol. The abbreviations are; total binding (B7), specific binding (B5), non-specific binding (BN5), maximum binding capacity of tissue (Bmax), fi'ee (i.e., unbound) [3 H] ll-deoxycortisol (F), and disintegrations per minute (DPM) are shown; 11 = 3 ....................................................................................................................... 50 vii Figure 2-2. Association and dissociation kinetics of a sea lamprey receptor in gill cytosol. For association kinetics (A), T1 /2 was 2.11 d: 0.32 min, 11 = 3. For dissociation kinetics (B), Tm was 26.44 :1: 8.41 min; n = 3. .................................................................. 51 Figure 2-3. Specificity of the lamprey gill cytosolic moiety for various steroids including ll-deoxycortisol (S), ll-deoxycorticosterone (DOC), cortisol (F), corticosterone (B), aldosterone (Aldo), Dexamethasone, (D), androstenedione (A), Estradiol (E2), 170(- hydroxyprogesterone (17OHP), and progesterone (P); n = 3. ........................................... 52 Figure 2-4. Specific binding of [3H] ll-deoxycortisol (5 nM) to cytosolic moiety from different tissues. Abbreviation; specific binding (B5). Vertical bars represent means :t SEM; n = 3. ........................................................................................................................ 53 Figure 2-5. Elution of 1 l-deoxycortisol-receptor complex from DNA-cellulose. Gill cytosol was preincubated with 20 nM [3 H] ll-deoxycortisol before binding to the column of DNA-cellulose. Abbreviations are; total binding (BT), specific binding (BS), nonspecific binding (BN3), and disintegrations per minute (DPM) are shown; 11 = 3 ........ 54 Chapter 3 Figure 3-1. Effect of handling and salt challenge stressors on plasma levels of 11— deoxycortisol for spawning (A) and parasitic (B) phase lamprey during recovery. Vertical bars represent means i SEM of 6-14 observations. *, P < 0.05; **, P < 0.01; ***, P < 0.001. ................................................................................................................... 78 Figure 3-2. Effect of 21 d ll-deoxycortisol implant treatment on plasma levels of 11- deoxycortisol (A) and 11-deoxycorticosterone (B). Vertical bars represent means 3: SEM of 1 1-12 observations. *, P < 0.05; **, P < 0.01; ***, P < 0.001. ................................... 79 Figure 3-3. Effect of 21 d ll-deoxycortisol implant treatment on plasma levels of Dehydroepiandrosterone-sulfate, DHEA-S (A) and Dehydroepiandrosterone, DHEA (B). Vertical bars represent means 1: SEM of 11-12 observations. *, P < 0.05 ; **, P < 0.01; ***, P < 0.001. ................................................................................................................... 80 Figure 34 Effect of 21 d 11-deoxycortisol implant treatment on plasma levels of androstenedione (A) and testosterone (B). Vertical bars represent means :1: SEM of 11-12 observations. *, P < 0.05; **, P < 0.01; ***, P < 0.001. .................................................. 81 Figure 3-5. Effect of 21 d ll-deoxycortisol implant treatment on plasma levels of estrone (A) and estradiol (B). Vertical bars represent means i SEM of 11-12 observations. *, P < 0.05; **, P < 0.01; ***, P < 0.001 .................................................................................. 82 Figure 3-6. Effect of 21 d ll-deoxycortisol implant treatment on gill Na+, K+-ATPase activity. Vertical bars represent means i: SEM of 11-12 observations. *, P < 0.05; **, P < 0.01; ***, P < 0.001. ...................................................................................................... 83 viii Figure 3-7. Changes in concentration of plasma ll-deoxycortisol following injections of mammalian CRH. Vertical bars represent means :1: SEM of 3-5 observations. *, P < 0.05; **,P<0.01; ***,P<0.001. .................................................................................... 84 Figure 38 Changes in concentration of plasma ll-deoxycortisol following injections of pituitary extract. Vertical bars represent means :1: SEM of 9-10 observations. *, P < 0.05; **,P<0.01; ***,P< 0.001. ............................................................................................. 85 ix INTRODUCTION Concept of stress During the 19th century, physiologist Claude Bernard established the concept of a constant “milieu interieur” or internal environment in the body (Cannon 1929; Robin 1979). Bemard’s concept in 1878 was that an organism regulates a stable internal environment in an ever-changing external environment. Therefore, he is credited with laying the foundation for the concept of homeostasis which was articulated during the 19205 (Cannon 1929). Cannon (1924) demonstrated that adrenal secretions were of importance in maintaining homeostasis. Cannon (1929) actually coined the term homeostasis and related it to maintaining an internal stable state. He also suggested that there were two types of homeostasis involving supplies and processes to maintain a stable state of the internal fluid matrix. After Walter B. Cannon’s homeostasis concept came the idea of a General Adaptation Syndrome by Hans Selye (1936). Some of the most influential studies on stress response in animals were conducted by Hans Selye. Selye (1936) described animals responding to stress in stages of alarm, resistance and exhaustion. He called this phenomenon or theory the General Adaptation Syndrome (GAS). The syndrome included morphological changes such as an enlargement of the adrenal glands and atrophies of the thymus, spleen and lymphoid tissues. If animals were exposed to continued stressors, they would develop resistance. Eventually, the continuous stress would cause the animal to reach exhaustion and die. A few years later, Selye (1946; 1950; 1956; 1973) was able to fill in more details and provided evidence that non-specific stressors elicited the alarm stage which activated the pituitary-adrenal axis to release corticosteroids. Selye (1950) defined the syndrome as “the sum of all non-specific, systemic reactions of the body which ensue upon long continued exposure to stress.” In addition, he divided the idea of stress into stressors and stress response. Selye also reported that the adrenal glands were responsible for “adaptation diseases” although this was later refuted (Sayers 1950). While some of the details of Selye’s concept were proven incorrect through time (Munck et al. 1984), his overall principle of the GAS concept was generally accepted. During the 1980’s a different hypothesis was put forth regarding the role of the adrenal stress steroids. Munck et al. (1984) hypothesized that the physiological function of stress-induced increases in glucocorticoid levels is to protect not against the source of the stress itself, but against the possible over-reaction of normal defense mechanisms activated by stress. The glucocorticoids accomplish this function by inhibiting the defense reactions, thus preventing them from overshooting and themselves threatening homeostasis. Sapolsky et a1. (2000) provides a comprehensive review of glucocorticoid actions associated with stress. A relatively new concept of stress has emerged from the biomedical field called allostasis or allostatic load. Sterling and Eyer (1988) define allostasis as the process of adaptation to acute stress including the ability to increase or decrease vital functions to a new steady state on challenge. While this was a seemingly new terminology, others had already explored the concept under different names. Schreck (1981) explored the concept which he termed performance capacity in relation to stress compensation. Several years later the concept was broadened to include energetic load (Schreck and Li 1991). McEwen and Stellar (1993) and McEwen (2000), concerned with diseases in humans, coined the term allostatic load which was defined as, “The strain on the body produced by repeated upland downs of physiologic response, as well as by the elevated activity of physiologic systems under challenge, and the changes in metabolism and the impact of wear and tear on a number of organs and tissues, which can predispose the organ to disease.” The primary purpose of the concept was to explore the linkage between stress and disease at a finer scale to uncover the mechanistic causes. McEwen and Wingfield (2003) expanded the allostasis load concept to include Type 1 and Type 2 overload. The Type 1 overload means that energy demands exceed the energy income, and what can be mobilized from stores. Type 2 occurs if energy demands are not exceeded and the organism continues to take in or store as much or even more energy than it needs. Therefore, Type 1 and Type 2 overloads are in addition to normal allostatic load resulting from unpredictable events. The role of glucocorticoids in mediating the effects of allostatic loading has been reviewed by Landys et a1. (2006). After synthesis of the existing published data, they found 3 levels of allostasis. The first was a “low but critical basal level, the second an elevated seasonal baseline that varies in conjunction with predictable demands, and the third was a high stress-related level in response to unpredictable and life-threatening perturbations.” Fisheries biologists recognized the economic importance of the effects of stress in fish hatcheries (Pickering 1981). Hatchery fish were regularly exposed to acute stressors such as crowding, handling, and transporting. Sometimes the fish were exposed to chronic stressors also which would lead to increased mortality. Therefore, it became increasingly important for fisheries biologists to quantify stress. Stress in fish Most fish biologists developed their ideas about stress from Hans Selye’s GAS concept. Brett (1957) thought that Selye’s concept was too vague and fisheries professionals needed a better workable definition of stress. His definition is as follows: “stress is a state produced by any environmental or other factor which extends the adaptive responses of an animal beyond the normal range, or which disturbs the normal functioning to such an extent that, in either case, the chances of survival are significantly reduced.” He thought that this definition would provide a more quantitative approach by including estimates of chances of survival or by the measure of reduction in capacity of performance. The concept of stress in fish was firrther expanded to include performance capacity (Schreck 1981) and energetic load (Schreck and Li 1991) similar to the concepts described earlier regarding allostasis. Pickering (1981) reviewed the evolution of the stress concept as it relates to fish and provided accounts of fish biologists beginning to quantify the stress response. Instead of focusing on the concept of stress, fish physiologists focused efforts on measuring and quantifying the stress response (Pickering 1981; Wedemeyer et al. 1990). The new conceptual framework for stress in fish considered the stress response in terms of primary, secondary, and tertiary changes (Mazeaud et al. 1977; Donaldson 1981; Mazeaud and Mazeaud 1981; Wedemeyer and McLeay 1981). The primary response was an endocrine system response which included the hypothalamus-pituitary—interrenal axis (HPI). After a perceived stimulus by the central nervous system, catecholarnines and stress steroids are released into circulation. Catecholarnines (for example, epinephrine), which are the first to increase in the blood, are released from the chromaffin tissues located in various organs of different species (Mazeaud et al. 1977; Mazeaud and Mazeaud 1981). Their principal role is thought to be the stimulation of glucose release for immediate energy used in a fight or flight response. After the catecholamine response is initiated, the stress steroid response is activated by the central nervous system. The central nervous system stimulates Corticotropin Releasing Hormone (CRH) to be released from the hypothalamus which in turn stimulates Corticotrophin Hormone (ACTH) to be released from the pituitary. ACTH circulates and binds to receptors in the interrenal cells of fish (homologue to adrenal gland) to stimulate the release of cortisol or corticosterone (Donaldson 1981; Wendelaar Bonga 1997; Mommsen et al. 1999). The secondary response includes changes in blood and tissue chemistry in response to stress. Wedemeyer and McLeay (1981) and Wedemeyer et al. (1990) describe these as secondary alterations in blood chemistry such as; hyperglycemia, hyperlacticemia, hypochloremia, and reduced blood clotting time. In addition, they describe measuring changes in liver glycogen or even reductions in vitamin C from interrenal cells. The tertiary response includes changes to individuals and populations (Wedemeyer et al. 1990). Many of the tertiary responses were observed by hatchery workers in daily operations (Wedemeyer and McLeay 1981). Some examples of tertiary responses are reductions in growth rate, lowered resistance to disease, decreased reproductive success, oxygen consumption, swimming performance, altered feeding behavior or migratory behavior (Wedemeyer et al. 1990). Chronic stress may eventually lead to reduced performance by individuals and thus eventually impact the population. Functions of corticosteroids The corticosteroids are a group of steroids produced and secreted by the adrenal cortex cells in mammals or interrenal cells (in head kidney) in fish. In tetrapods, the adrenal cortex is divided into three zones that produce three different classes of steroids. The zones are the zona glomerulosa (minerlocorticoids), zona fasciculate (glucocorticoids), and zona reticularis (androgens) (Norman and Litwack 1997). Corticosteroids are divided into two subcategories: the glucocorticoids and minerocorticoids. They are both characterized by a hydroxyl group at the 21 carbon position. Further, glucocorticoids are characterized by the presence or absence of hydroxyls at carbon 11 and carbon 17 positions. The principal glucocorticoids in vertebrates are cortisol and corticosterone (Bern 1967; Idler and Truscott 1972; Sandor 1972; Jones et al. 1972) and are released in response to stressors. The only known exception is found in the elasmobranches, which produce 10: hydroxycorticosterone as their major glucocorticoid (Idler and Truscott 1967). The mineralocorticoids are characterized by a hydroxyl at the carbon 11 position, and the carbon 18 oxidized to an aldehyde (Norman and Litwack 1997). The principal mineralocorticoid is aldosterone in land vertebrates which is important in regulating ion exchange and water metabolism. In fish, there is no evidence that aldosterone exists. It was thought that cortisol had a dual role as stress steroid and mineralocorticoid in fish. However, a recent study has found that ll-deoxycorticosterone was an agonist for the mineralocorticoid receptor in rainbow trout (Sturm et al. 2005). Glucocorticoids are considered stress steroid hormones with many functions. Sapolsky et al. (2000) classified the roles of glucocorticoids in the stress response as permissive, suppressive, stimulatory, and preparative. The suppressive functions of glucocorticoids include regulation of reproduction, inflammation, and immune system, while permissive actions are important in adrenal gland insufficiencies or malfimctions (Sapolsky et al. 2000). Stimulatory functions of glucocorticoids include regulating metabolic processes like prolonged elevation of blood glucose by gluconeogenesis and inhibition of glucose utilization (Sapolsky et al. 2000). The sea lamprey as a model system The sea lamprey (Petromyzon marinus) offers a unique animal model for the studies of stress steroid hormone characterization due to its ancestral lineage. The lampreys are Agnathans, jawless fishes, which are one of the oldest extant vertebrates available for use in the characterization of stress steroid hormones. Characterizing the glucocorticoid in one of the earliest vertebrates helps us understand the evolution of stress hormones in the vertebrate lineage. While we know that most vertebrates utilize cortisol or corticosterone as their glucoccorticoid, it was not known whether these ancient j awless fish possess a stress steroid. Another benefit in using lamprey as a model is that the stress steroid hormone should be available at different life history stages of the lamprey. During the life cycle of the lamprey, they experience a freshwater and saltwater phase. These different phases include changing environments that may expose the lamprey to different stressors. The larvae go through a transformation called metamorphosis to prepare for the ocean or lake phase of their life cycle. After the parasitic phase, the sea lampreys reenter freshwater to spawn in tributaries where the eggs hatch in nests. The larvae leave the nests and then drift into soft substrate areas and reside as larvae for several years. The process of metamorphosis shares similar characteristics of smolting in salrnonids. It is well known that sahnonid smoltification is regulated by glucocorticoid cortisol. Therefore, lamprey may have a glucocorticoid hormone that acts similar to cortisol. The parasitic and spawning phases of the adult lampreys should also have a glucocorticoid stress response to help maintain allostasis. The sea lamprey also offers a good model to understand the glucocorticoid stress response for fisheries management purposes. Sea lampreys are an undesirable pest in the Laurentian Great Lakes. Since the 19505, substantial amounts of funding and effort to control the sea lamprey population have occurred. However, lamprey populations around the world are in decline due to habitat destruction. In the Pacific Northwest, the Pacific lampreys (Entosphenus tridentatus) are important subsistence foods for indigenous peoples. Identifying the glucocorticoid and being able to measure the stress steroid may assist in evaluating environmental stressors and various management activities for better conservation or control. Introduction to dissertation There is evidence that lampreys have the primary, secondary, and tertiary stress responses. For example, it has been shown that lamprey exhibit increases in catecholamines after an acute stressor, which is part of the primary stress response (Mazeaud and Mazeaud 1981). Plasma levels of epinephrine and norepinephrine were shown to increase in sea lamprey after various stressors (Mazeaud and Mazeaud 1981). The Hypothalamus-Pituitary-Adrenal (interrenal) Axis may exist in lamprey. While there is no evidence for CRH from the hypothalamus, there is evidence for ACTH in the lamprey pituitary. ACTH from the lamprey pituitary has been cloned and sequenced (Heinig et al. 1995; Takahashi et al. 1995A; Takahashi et a1. 1995B). The lamprey ACTH is 60 amino acids long, roughly 20 amino acids longer than other vertebrate ACTHs (Takahashi et al. 2006). However, lamprey ACTH levels have not been shown to increase after acute stress. In addition, there is no direct evidence for a stress steroid hormone or glucocorticoid in the j awless vertebrate, the sea lamprey. There is evidence that lampreys exhibit a secondary stress response. Different types of stressors such as dewatering and handling can induce hyperglycemia in lampreys (Larsen 1976; Morris and Islam 1969; Leibson and Plisetskaya 1969). Close et al. (2003) provided evidence that handling and tagging can change indicators of secondary and tertiary stress responses such as plasma glucose, ventilation rate, and swimming performance in lamprey. The goal of this research was to identify and characterize the stress steroid hormone in the ancient vertebrate, the sea lamprey. To accomplish this goal, the first prediction was that lampreys have a stress steroid circulating in the plasma (chapter 1). The second prediction was that any identified steroids have a receptor (chapter 2). The third prediction was that identified steroids that have a receptor will have classic glucocorticoid stress response and show biological effects (chapter 3). 10 REFERENCES Bern, HA. 1967. Hormones and endocrine glands of fishes. Science 158:455-462. Brett, J .R. 1958. Implications and assessments of environmental stress. In Investigations of Fish-Power Problems. Pages 69-83 in RA. Larkin, editor. H.R. MacMillan Lectures in Fisheries, University of British Columbia. Cannon, W.B., and Pereira J .R. 1924. Increase of adrenal secretion in fever. Proceedings of the National Academy of Sciences 10:247-248. Cannon, W.B. 1929. Organization for physiological homeostasis. Physiological Reviews 9(3):399-431. Close, D.A., Fitzpatrick, M.S., Lorion, C.M., Li, H.W., and Schreck, CB. 2003. Effects of intraperitoneally implanted radio transmitters on the swimming performance and physiology of Pacific Lamprey. North American Journal of Fisheries Management 23:1184-1192. Donaldson, EM. 1981. The pituitary-interrenal axis as an indicator of stress in fish. Pages 11-47 in AD. Pickering, editor. Stress and fish. Academic Press, London. Heinig, J .A., Keeley, F.W., Robson, P., Sower, S.A., and Youson, J .H. 1995. The appearance of pr00piomelanocortin early in vertebrate evolution: cloning and sequencing of POMC from a lamprey pituitary Cdna library. General and Comparative Endocrinology 99: 137-144. Idler, DR. and Truscott, B. 1967. 1a-Hydroxycorticosterone: synthesis in vitro and properties of an interrenal steroid in the blood of cartilaginous fish (Genus Raja). Steroids 9:457-477. Idler, DR. and Truscott, B. 1972. Corticosteroids in fish. Pages 126-252 in DR. Idler, editor. Steroids in nonmammalian vertebrates. Academic Press, New York. Jones, I.C., Bellamy, D., Chan, D.K.O., Follett, B.K., Henderson, I.W., Phillips, J .G., and Snart, RS. 1972. Biological actions of steroid hormones in nonmammalian vertebrates. Pages 414-480 in DR. Idler, editor. Steroids in nomnammalian vertebrates. Academic Press, New York. Landys, M.M., Ramenofsky, M., and Wingfield, J .C. 2006. Actions of glucocorticoids at a seasonal baseline as compared to stress-related levels in the regulation of periodic life processes. General and Comparative Endocrinology 148:132-149. 11 Larsen, L0. 1976. Blood glucose levels in intact and hypophysectomized lampreys (Lampetrafluviatilis L.) treated with insulin, “stress,” or glucose, before and during the period of sexual maturation. General Comparative Endocrinology 29:1-13. Leibson, LG, and Plisetskaya, EM. 1969. Hormonal control of blood sugar level in cyclostomes. General Comparative Endocrinology 2:528-534. Mazeaud, M.M., Mazeaud, F., and Donaldson, EM. 1977. Primary and secondary effects of stress in fish: some new data with a general review. Transactions of the American Fisheries Society 106:201-212. Mazeaud, M.M., and Mazeaud, F. 1981. Adrenergic responses to stress in fish. Pages 49- 75 in AD. Pickering, editor. Stress and fish. Academic Press, London. McEwen, BS. 2000. Allostasis and allostatic load: Implications for neuropsychopharrnacology. Neuropsychopharmacology 22: 108-124. McEwen, BS, and Stellar, E. 1993. Stress and the individual. Archives of Internal Medicine 153:2093-2101. McEwen, BS, and Wingfield, J.C. 2003. The concept of allostasis in biology and biomedicine. Hormones and Behavior 43:2-15. Mommsen, T.P., Vijayan, M.M., and Moon, T.W. 1999. Cortisol in teleosts: dynamics, mechanisms of action, and metabolic regulation. Reviews in Fish Biology and Fisheries 92211-268. Morris, R., and Islam, D.S. 1969. The effect of hormones and hormone inhibitors on blood sugar regulation and the follicles of Langerhans in ammocoete larvae. General Comparative Endocrinology 12:8 1-90. Munck, A., Guyre, P.M., and Holbrook, NJ. 1984. Physiological fimctions of glucocorticoids in stress and their relations to pharmacological actions. Endocrine Reviews 5:25-44. Norman, A.W. and Litwack, G. 1997. Hormones. 2nd edition. Academic Press, San Diego. . Pickering, AD. 1981. Introduction: the concept of biological stress. Pages 1-9 in AD. Pickering, editor. Stress and fish. Academic Press, London. Robin, ED. 1979. Claude Bernard and the internal environment. A memorial symposium. Marcel Dekker, New York. 12 Sapolsky, R.M., Romero, L.M., and Munck, A.U. 2000. How do glucocorticoids influence stress responses? Integrating permissive, suppressive, stimulatory, and preparative actions. Endocrine Reviews 21 :55-89. Sandor, T. 1972. Corticosteroids in amphibia, reptilia, and aves. Pages 253-327 in DR. Idler, editor. Steroids in nonmammalian vertebrates. Academic Press, New York. Sayers, G. 1950. The adrenal cortex and homeostasis. Physiological Reviews 30:241-320. Schreck, CB. 1981. Stress and compensation in teleostean fishes: response to social and physical factors. Pages 295-321 in AD. Pickering, editor. Stress and fish. Academic Press, London. Schreck, CB, and Li, H.W. 1991. Performance capacity of fish: stress and water quality. In D.E. Brune and J .R. Tomasso, editors. Aquaculture and water quality. World Aquaculture Society, Baton Rouge, LA. Advances in World Aquaculture 3:21-29. Sterling, P. and Eyer, J. 1988. Allostasis: a new paradigm to explain arousal pathology. Pages 629-649 in S. Fisher and J. Reason, editors. Handbook of life stress, cognition and health. John Wiley & Sons, New York. Selye, H. 1936. A syndrome produced by diverse nocuous agents. Nature 138:32. Selye, H. 1946. The general adaptation syndrome and the diseases of adaptation. The Journal of Clinical Endocrinology 62117-230. Selye, H. 1950. Stress and the general adaptation syndrome. British Medical Journal 121383-1392. Selye, H. 1956. The stress of life. McGraw-Hill, New York. Selye, H. 1973. The evolution of the stress concept. American Scientist 61 :692-699. Sturm, A., Bury, N., Dengreville, L., F agart, J ., Flouriot, G., Rafestin-Oblin, ME, and Prunet, P. 2005. 11-Deoxycorticosterone is a potent agonist of the rainbow trout (Oncorhynchus mykiss) mineralocorticoid receptor. Endocrinology 146:47-55. Takahashi, A., Amemiya, Y., Sarashi, M., Sower, S.A., and Kawauchi, H. 1995. Melanotropin and corticotropin are encoded on two distinct genes in the lamprey, the earliest evolved extant vertebrate. Biochemical and Biophysical Research Communications 2 13:490-498. Takahashi, A., Amemiya, Y., Nozaki, M., Sower, S.A., Joss, J ., Gorbman, A., and Kawauchi, H. (1995). Isolation and characterization of melanotropins from lamprey pituitary glands. International Journal of Peptide & Protein Research 46: 197-204. 13 Takahashi, A., Yasuda, A., Sower, S.A., Kawauchi, H. 2006. Posttranslational processing of pr00piomelanocortin family molecules in sea lamprey based on mass spectrometric and chemical analysis. General and Comparative Endocrinology 148:79-84. Wedemeyer, G.A., and McLeay, DJ. 1981. Methods for determining the tolerance of fishes to environmental stressors. Pages 247-275 in AD. Pickering, editor. Stress and Fish. Academic Press, London. Wedemeyer, G.A., Barton, B.A., and McLeay, DJ. 1990. Stress and acclimation. Pages 451-489 in CB. Schreck and PB. Moyle, editors. Methods for fish biology. American Fisheries Society, Bethesda, Maryland. Wendelaar Bonga, SE. 1997. The stress response in fish. Physiological Reviews 77:591- 625. 14 CHAPTER 1 IDENTIFICATION OF PUTATIVE GLUCOCORTICOIDS IN THE SEA LAMPREY Petromyzon marinas 15 ABSTRACT This study was undertaken to identify putative glucocorticoids in the blood of the sea lamprey Petromyzon marinas. Most glucocorticoid chemical structures are known throughout the vertebrate lineages. However, previous studies have failed to provide definitive evidence that the lamprey, one of the most ancient vertebrates, possess a stress steroid hormone. We hypothesized that lampreys do have a stress steroid hormone in their blood. High Performance Liquid Chromatography (HPLC) was used to fractionate extracted lamprey plasma for screening. Radioimmunoassays and protein binding assays were used to screen fractionated lamprey plasma for cortisol-like and corticosterone-like steroids. Radioimmunoassays were also used to monitor steroids in conjunction with LH-20 partition chromatography followed by HPLC to fractionate 800 ml of extracted lamprey plasma. Corresponding immunoreactive peaks were collected and subjected to mass spectrometry. The blood of the lamprey contained possible stress steroid hormones. Definitive identification was made by mass spectrometry analysis of 1 1-deoxycortisol and 1 1-deoxycorticosterone circulating in the blood of lamprey. This study provided evidence that one of these steroids is a putative glucocorticoid in the ancient vertebrate, the sea lamprey. 16 INTRODUCTION Corticosteroids are steroid hormones produced by the adrenal cortex in mammals and the interrenal tissue located in the anterior portion of the kidney in teleosts (Bern 1967; Frazer 1992). Corticosteroids are divided into two groups, the glucocorticoids (GC) and mineralocorticoids (MC) based on fimction. GCs are considered stress steroid hormones with many functions. Sapolsky et al. (2000) classified the roles of GCs in the stress response as permissive, suppressive, stimulatory, and preparative. The suppressive functions of glucocorticoids include regulation of reproduction, inflammation, and immune system, while permissive actions are important in adrenal gland insufficiencies or malfimctions (Sapolsky et al. 2000). Stimulatory functions of glucocorticoids include the regulation of metabolic processes like prolonged elevation of blood glucose by gluconeogenesis and inhibition of glucose utilization (Sapolsky et al. 2000). The principal stress steroids (GCs) in vertebrates are cortisol or corticosterone (Bern 1967; Idler and Truscott 1972; Sandor 1972; Jones et al. 1972). Mammals secrete cortisol; while rats and mice secrete corticosterone. Reptiles and birds also produce and circulate corticosterone as their primary glucocorticoid (Nelson 2000). In bony fish, the active GC is cortisol (Idler and Truscott 1972) while in elasmobranchs like sharks and rays the active GC is 101- hydroxycorticosterone (Idler and Truscott 1967). In teleosts, cortisol may act as both a GC and MC which provides homeostasis in salt and water balance. The principal MC in land vertebrates is aldosterone, which fimctions to regulate 17 sodium and potassium transport and controls water reabsorption in the kidney (Norman and Litwack 1997). There is no evidence that fish have aldosterone. The current thinking is that the steroid/receptor complex evolved in the vertebrate lineage (Escriva et al. 1997; Baker 1997). The question of whether stress steroids exist and fimction in ancient j awless fishes had not been answered. Identifying the possible stress steroids in lamprey would be an important step toward understanding vertebrate steroid/receptor evolution. Previous studies have provided some evidence that a stress steroid may exist in the jawless vertebrates. The first line of evidence was from in vitro experiments using presumptive adrenal tissue incubations (PAT) with tritiated steroid precursors to examine possible corticosteroids in sea lamprey, Petromyzon marinus. Weisbart and Youson (1975) incubated PAT from larval and parasitic adult sea lamprey with [4-14C] progesterone and identified the products using thin layer chromatography and recrystallization. The identified steroids were ll-deoxycortisol, 17oz- hydroxyprogesterone, and androstenedione. From incubations with testes, the authors also identified 11-deoxycorticosterone. The PAT incubations failed to form cortisol, cortisone, corticosterone, or ll-deoxycorticosterone. Weisbart et al. (1978) conducted another PAT incubation experiment with [1, 2- 3 H] cholesterol, which failed to produce any known putative corticosteroids in spawning phase adult sea lamprey. Efforts to find possible corticosteroids in lamprey also included in vivo studies. The second line of evidence was from in vivo experiments designed to examine possible corticosteroids in the blood of lamprey. Using double-isotope derivative methods, it was determined that either lampreys had no corticosteroids or levels were too 18 low to be biologically active (Weisbart and Idler 1970). Weisbart and Idler (1970) measured plasma cortisol levels at < 5 ng/ 100 m1 , while cortisone and corticosterone levels were at 2 ng/100 ml in sea lamprey. Another study using the same methods found serum levels of cortisol, ll-deoxycortisol, corticosterone, at < 3 ng/ 100 ml and cortisone < 5 ng/ 100 ml in lamprey (Buus and Larsen 1975). Weisbart and Youson (1977) used chromatography and recrystallization to identify ll-deoxycorticosterone after [3 H] progesterone injections into parasitic adult sea lampreys. Weisbart et al. (1980) identified cortisol, corticosterone, 1 1-deoxycortisol, l 1-dehydrocorticosterone by double-isotope derivative assay in sea lamprey after injecting porcine adrenocorticotropin releasing hormone (ACTH). The study failed to identify cortisone or ll-deoxycorticosterone in lamprey. The third line of evidence was from recent receptor research in lamprey. Thornton (2001) identified DNA sequences which were homologues to estrogen, progesterone, and corticosteroid receptor in the lamprey. The analysis predicted that estrogen receptor evolved first, followed by the progesterone receptor, then the corticosteroid receptor. Recently, Bridgham et al. (2006) synthesized the ligand binding domain of the ancestral corticoid receptor for use in a transactivation assay. The assay showed that aldosterone and ll-deoxycorticosterone had the highest activation levels of the luciferase reporter. In addition, Bridgham et al. (2006) provided phylogenetic evidence that the ancestral corticoid receptor was a mineralocorticoid receptor which then gave rise to the glucocorticoid receptor in teleosts and tetrapods. The three lines of evidence mentioned, give reason to postulate that lampreys possess a stress steroid hormone. l9 The aim of the study was to establish chemical identification of possible stress steroids present in the plasma of sea lamprey. Our first objective was to use radioimmunoassays to screen lamprey plasma for cortisol-like and corticosterone-like steroids. Our second objective was to extract the steroids from a large pool of plasma, then to isolate them using chromatography methods. Our third objective was to determine the chemical identification of the putative stress steroids by mass spectrometry analysis. 20 MATERIALS AND METHODS Maintenance of animals and blood collection Sea lamprey Petromyzon marinas were collected in landlocked streams by the US. Fish and Wildlife Service employees, and transported to Michigan State University (East Lansing, MI) or USGS Hammond Bay Biological Station (Millersburg, MI) for experiments and collecting plasma where they were held at 10-13 °C. Blood was obtained by cardiac puncture using vacutainers containing EDTA (Becton Dickinson, Franklin Lakes, NJ), placed on ice for 15 min, and then centrifuged at 1000 x g at 4 ° C for 15 min. The plasma was removed and stored at -80 °C. All experiments were approved by the Michigan State University Institutional Animal Care and Use Committee (AUF # 05/04—077-00). Plasma Extraction Pooled plasma (20 ml) from male and female lampreys was diluted 1:1 with 0.9% saline, passed through a 0.45 p.M filter (Millipore, Billerica, MA), and loaded onto an activated Sep-Pak (Waters, Milford, MA). The Sep-Pak was washed with 5 ml deionized water and eluted with 5 ml methanol. The methanol elute was evaporated under reduced pressure using a CentriVap Concentrator (Labconco, Kansas City, MO). 21 High performance liquid chromatography Samples were dissolved in 1 ml actonitrile/water/trifluoroacetic acid (TFA) (28/72/0.01, v/v/v) and loaded onto a C18 reverse-phase HPLC column (Nova-Pak, 3.9 mm x 300 mm, Waters) fitted with a guard module. Two solvents were used to deliver a gradient to the column. Solvent A was 0.01% TF A in deionized water and solvent B was 70% acetonitrile and 0.01% TFA in deionized water. The pattern of development was as follows: 0 —. 10 min, 28% B; 10 -> 60 min, 28 -> 100% B; 60 -’ 80 min, 100% B. The eluate was monitored for UV absorption with a photodiode array detector (Waters). Fractions were collected every 1 min between 11 and 70 min into 1.5 ml tubes. Radioimmunoassay (RIA) and protein binding assay (PBA) procedures RIAs and PBA were conducted in glass culture tubes (10 mm X 75mm, Fisher Scientific, Pittsburgh, PA). Briefly, the assay buffer consisted of 50 mM sodium phosphate, pH 7.4, 0.2% BSA, 137 mM NaCl, 0.40 mM EDTA, and 0.77 mM sodium azide. Nine standards were made up in duplicate over the range 1.95-500 pg/ 100 til/tube. The tubes containing samples also had a volume of 100 pl of RIA buffer. Binding reagent was made by adding radiolabel (American Radiolabled Chemicals, St. Louis, MO) and antiserum (Chemicon, Temecula, CA., 1:100) or rabbit sera (Sigma-Aldrich, St. Louis, MO, 1:40) for PBA to 20 ml of assay buffer in amounts such that, when 100 ul was dispensed to all tubes, each tube contained 5000 dpm and, in the absence of any standard, 50% of the radiolabel was bound to the antiserum or cortisol binding protein. 22 Blank tubes, to which no antibody was added, and tubes necessary to determine the total and maximum dpm counts were also included in the assay. All tubes were incubated overnight at 4 °C. After overnight incubation, 500 pl of ice-cold charcoal solution at 0 °C (50 mM sodium phosphate, Pb 7.4, 0.1% gelatin, 1.0% dextran-coated charcoal) was added to each tube. The tubes were kept on ice for 20 min, and then centrifuged in an Allegra 6R (Beckrnan Coulter, Fullerton, CA) at 1000 x g for 12 min. The supernatants were poured into 8 ml scintillation vials, mixed with 6 ml scintillation fluid and DPM were counted with an LS-6500 (Beckrnan Coulter, Fullerton, CA) scintillation counter. LH-20 column chromatography Sample was dissolved in 2 ml 98% dichloromethane and 2% methanol and loaded onto a glass column (450 mm x 15 mm) packed with 20.0 g of Sephadex LH-20 (Amersham, Piscataway, NJ). Two solvents were used to deliver sample through the column. A solution containing 98% dichloromethane and 2% methanol was pumped through the column at 4 ml/min. Fractions were collected every 1 min between 1 and 60 min into 16 x 100 mm glass culture tubes. Elute was dried down and resuspended with 0.5 ml methanol per tube. Mass spectrometry analysis of plasma LH-20 fractions corresponding to immunoreactivity of 11-deoxycortisol and 11- deoxycorticosterone were collected and each group combined and dried down under 23 reduced pressure. Samples were then fractionated by HPLC and assayed to identify immunoreactive peaks in fractions. Immunoreactive fractions were combined, dried down under reduced pressure and then subjected to Atmospheric Pressure Chemical Ionization Mass Spectrometry (APCI-MS) analysis. Mass spectra were obtained using a LCQ-Deca ion trap (Thenno Scientific, Waltham, MA). The vaporizer temperature was 300 °C and the capillary temperature was 250 °C. Samples were compared against authentic ll-Deoxycortisol and ll-Deoxycorticosterone standards (Si grna-Aldrich). Mass spectrometry analysis was performed at the Mass Spectrometry Facility, Research Technology Support Facility at Michigan State University. 24 RESULTS To identify possible stress steroids in sea lamprey, plasma was screened for immunoreactive cortisol and corticosterone. In addition, the plasma was also screened for binding activity with cortisol binding protein. Plasma immunoreactive cortisol levels peaked in HPLC fraction 44 at 1561 pg ml'l (Fig. 1A). The peak in fraction 44 corresponds to the retention time of 1 1-deoxycortisol standard. A small immunoreactive peak occurred at fiactions 32/33, where the cortisol standard eluted from the column. However, the peak was only slightly higher than background levels in other fractions. Background immunoreactive cortisol levels appeared to gradually rise throughout the HPLC run. The cortisol binding protein assay showed results similar to the cortisol radioimmunoassay (Fig. 1B). The cortisol level markedly increased to 2231 pg ml'1 in HPLC fiaction 44. The ll-deoxycortisol standard eluted from the HPLC column at the same fraction. Cortisol was not detected in HPLC fractions 32/33. Cortisol binding activity, unlike immunoreactivity to cortisol antibody, showed much lower background levels in other fractions. Irnmunoreactive corticosterone peaked in fraction 50 at 608 pg ml'l (Fig 2). Plasma levels of corticosterone also peaked in fractions 31, 56/57, and 63. However, no corticosterone was detected in fi'actions 41/42 where corticosterone standard eluted from the HPLC column. The major peak at fraction 50 corresponded with 11- deoxycorticosterone standard. 25 To collect a sufficient amount of steroids needed for identification, 800 ml plasma was extracted with Sep-Pak and the sample was subjected to gel filtration on a Sephadex LH-20 column to separate the immunoreactive steroids. Eluted LH-20 fractions were screened with ll-deoxycortisol and 11-deoxycorticosterone RIAs (Fig. 3). Irnmunoreactive ll-deoxycortisol levels were elevated in fractions 19-28 with a peak of 25 ng ml". Irnmunoreactive ll-deoxycorticosterone levels were elevated in fractions 10- 12 with a peak of 23 ng ml". Each set of fractions was combined, dried down, and run on HPLC separately. HPLC fractions were screened using 11-deoxycortisol and 11- deoxycorticosterone RIAs. Irnmunoreactive HPLC fractions corresponding with 11- deoxycortisol (44) and 1 1-deoxycorticosterone (50) were collected, dried down, and subjected to mass spectrometry analysis. HPLC fractions corresponding to immunoreactive ll-deoxycortisol and 11- deoxycorticosterone were analyzed by APCI-MS in positive mode to observe parent ions. To confirm the identity of the compounds, the parent ions were subj ected to tandem mass spectrometry (MS/MS) and compared to authentic ll-deoxycortisol and 11- deoxycorticosterone fi'agmentation patterns of daughter ions. The MS/MS spectrum of authentic ll-deoxycortisol [M+H]+ ion at m/z 347, obtained by direct infusion of a 10 pg ml'1 ll-deoxycortisol standard solution, are shown in figure (4A). The standard fragmented at m/z 269, 293, 311, and 329, which matched the fragmented daughter ions of the plasma sample (Fig. 4B). The MS/MS spectrum of authentic ll-deoxycorticosterone [M+H]+ ion at m/z 331, fragmented at m/z 295 and 313 (Fig. 5A). The two most abundant ions obtained by fragmenting the plasma sample [M+H]+ ion, are also at m/z 295 and 313 (Fig. 5B). 26 2000- A Cortisol y-Deoxycortlsol ’5 1500 . 0 E g 1000 - 0 L- : g ‘ 500' 0 V U U V U V I I I 1 0 20 30 4O 50 60 70 3000 ' Cortisol 11-Deoxycortisol l l Cortisol-like binding (pg/fraction) 1O 20 30 40 50 60 70 Retention Time (min) Figure 1-1. Screening of HPLC fractions of lamprey plasma for cortisol-like steroids using RIA and BPA. (A) Amount of immunoreactive cortisol found in 0.5 ml I-IPLC fractions fi'om RIA of 20 pl of each fraction and back calculated fraction volume. (B) Amount of cortisol binding activity found in 0.5 ml HPLC fi'actions from PBA of 20 p1 of each fraction and back calculated to fraction volume. Arrows, show where cortisol and ll-deoxycortisol standard elute. ir = immunoreactivity. 27 1000' 800 4 Corticosterone 1 1 -Deoxycorticosterone 600' ir Corticosterone (pg/fraction) 10 20 3O 4O 50 60 70 Retention Time (min) Figure 1-2. Screening of HPLC fractions of lamprey plasma for corticosterone-like steroids using RIA. Amount of immunoreactive corticosterone found in 0.5 ml HPLC fractions from RIA of 20 pl of each fraction and back calculated to fraction volume. Arrows, show where corticosterone and ll-deoxycorticosterone elute. Ir = immunoreactivity. 28 30 - —O— 1 1 -Deoxycorticosterone . + 1 1 -Deoxycortisol -¥ N N 0| O 01 o teroids (nglfraction) 8 0| "'8 O v I V I v ' 0 10 20 3O 40 Retention time (min) Figure 1-3. Screening of LH-20 fractions of lamprey plasma for immunoreactive 11- deoxycortisol and ll-deoxycorticosterone by RIA. Amount of immunoreactive 11- deoxycortisol and ll-deoxycorticosterone found in LH-20 fractions from a Sep-Pak extract of 800 ml of sea lamprey plasma based on RIA of 20 p1 of each fraction and back calculated to fraction volume. Ir = immunoreactivity. 29 1 00 . 311,0 329.0 A Authentic 1 1 -Deoxycortisol 50 r 8 ‘ 293.0 347.1 5 . 26 .o 'D 1 g 4 .a . < o v '. r '1 . . v . . In.“ I - Jr 1 I - ' g 100 150 200 250 300 350 3.3 100 . 329.0 7, i B Plasma sample a l i 311.1 3 3417.0 503 1 269.1 293-1 0 ‘ r v t . ' n 'i .1; :J...u lili.J: Ii.v 100 150 200 250 300 350 m/z Figure 1-4. Identification of 1 l-deoxycortisol by APCI MS/MS analysis. Fragmentation patterns generated from both the synthetic ll-deoxycortisol (A) and a compound in HPLC fraction 44 (B), positively identifying the unknown compound in fraction 44 as 1 l-deoxycortisol. 30 100 - 313.1 ‘ A Authentic 11-Deoxycorticosterone - 912°” 295.1 1 C=O 1 331.1 50 1 1 O 4’ 1 U . C . a 1 .2 o J v j v ' I 4 NJ. .l.lv 1 - I 3 100 150 200 250 300 350 j 100 . 313.1 E - B Plasma sample 16 ‘ 331.1 7’ l I! 1 so 1 l 4 295.2 0 I v v 4’ I’L v 1 r Iv —'-I-q 100 150 200 250 300 350 m/z Figure 1-5. Identification of 1 l-deoxycorticosterone by APCI MS/MS analysis. Fragmentation patterns generated from both the synthetic ll-deoxycorticosterone (A) and a compound in HPLC fraction 50 (B), positively identifying the unknown compound in fraction 50 as 11-deoxycorticosterone. 31 DISCUSSION Biological and chemical analysis provided strong evidence for the identification of l l-deoxycortisol and ll-deoxycorticosterone. There were three lines of evidence to identify these putative stress steroids in the plasma of the sea lamprey. First, the results showed co-elution of immunoreactive cortisol, cortisol binding protein activity, and immunoreactive corticosterone peaks with ll-deoxycortisol and 11-deoxycorticosterone standards in I-IPLC fractions. Second, the results showed the use of immunoreactive ll- deoxycortisol and ll-deoxycorticosterone to monitor LH-20 and HPLC fractionation with imunoreactive peaks corresponding to elution times of 1 l-deoxycortisol and 11- deoxycorticoserone standards. Third, the study confirmed the identity of the parent ions of 11-deoxycortisol [M+H]+ ion at m/z 347 and ll-deoxycorticosterone [M+H]+ ion at m/z 331 from plasma of sea lamprey. To confirm the identity, the parent ions were subjected to MS/MS analysis to observe the fragmentation patterns. The fragmentation patterns of the daughter ions of authentic ll-deoxycortisol and ll-deoxycorticosterone standards matched the fragmentation patterns from the plasma steroid samples. In earlier studies, steroid identification was problematic due to limitations of the extant techniques and methods. Sandor and Idler (1972) developed the following criteria for identification of steroids; positive, presumptive, tentative, and suggestive based on the level of rigor in methodology. Idler and Truscott (197 2) used the criteria to examine earlier reported corticosteroid identifications. They reported that Weisbart and Idler (1970) had used; thin layer chromatography (TLC), derivative methods (Der), recrystallization (Cry), and double-isotope derivative assay (DIDA) to identify cortisol 32 with plasma levels at 50 pg/ml in sea lamprey. In contrast, they reduced the number techniques to TLC, Der, and DIDA to identify plasma cortisone and corticosterone 20 pg/ml in the sea lamprey (Weisbart and Idler 1970). Thus based on Idler and Truscott’s identification criteria, Weisbart and Idler’s (1970) identification of cortisol was a presumptive identification, while cortisone and corticosterone were suggestive identifications. In later studies through the 19705, in vivo and in vitro studies continued using the same techniques mentioned above to confirm whether lampreys possessed corticosteroids (Buus and Larsen 1975; Weisbart and Youson 1975; Weisbart and Youson 1977; Weisbart et al. 1978; Weisbart et al. 1980). These studies could not take the identification criteria beyond presumptive. In the most recent study, Weisbart et a1. (1980) identified cortisol (130 pg/ml), 11-deoxycortisol (570 pg/ml), and corticosterone (210 pg/ml) in the serum of adrenocorticotropin releasing hormone (ACTH) injected sea lampreys. Although the study reported identifying ll-deoxycortisol, their study also reported cortisol and corticosterone which is in contrast with our study. In our study, unlike earlier studies, cortisol and corticosterone were absent in the circulation of sea lamprey. After fractionating the lamprey plasma by HPLC, only background levels of immunoreactive cortisol in fractions 32/33 were observed. In addition, the cortisol binding protein activity showed no binding activity in the fiactions 32/33 where cortisol standard eluted. Irnmunoreactive corticosterone was not observed in fractions where corticosterone standard eluted in HPLC fractions. Even though previous studies (Weisbart and Idler 1970; Buus and Larsen 1975; and Weisbart et al. 1980) presumptively identified low levels of cortisol and corticosterone in the circulation of 33 lamprey, their methods may have been limited by their levels of detection and possibly background noise. In the current study, in vitro PAT incubation experiments were conducted to reproduce the earlier findings by Weisbart and Youson (1975). Incubation experiments with [3 H] pregnenolone and [3 H] progesterone with parasitic and spawning phase sea lamprey presumptive adrenal tissue (data not shown). A major radioactive peak was observed to co-elute with ll-deoxycortisol standard in the HPLC fractions. The isolated radioactive peak was subjected to TLC. The radioactive peak co-migrated with 11- deoxycortisol standard on TLC. However, changing the solvent system caused the unknown radioactive peak and 11-deoxycortisol to clearly separate. Therefore, the conclusion was that presumptive adrenal tissue was not the source of 11-deoxycortisol. These results are in contrast with the previous report that ll-deoyxcortisol was produced in the sea lamprey PAT (Weisbart and Youson 1975). In our study, results from RIA, HPLC, LH-20 chromatography, and mass spectrometry analysis demonstrate strong evidence that ll-deoxycortisol and 11- deoxycorticosterone are putative glucocorticoids in sea lamprey. In addition, the results show that cortisol and corticosterone are absent in the plasma of the ancient vertebrate. Weisbart and Youson (197 5) suggested that the 1 16-hydroxylase may not be present in lamprey. Our study provides evidence that llfi-hydroxylase did not evolve in the steroid biosynthetic pathway in early vertebrates, but evolved later in the elasmobranch lineage, since they produce la—hydroxycorticosterone (Idler and Truscott 1967). In conclusion, this study provided definitive identification of two putative glucocorticoid hormones in sea lamprey. Although the results provide identification of 34 ll-deoxycortisol and ll-deoxycorticosterone in the blood, there is no evidence that these steroids have receptors or biological functions. The positive identification of these two steroids will allow further testing to determine whether or not each has associated receptors. In order to classify these steroids as hormones, they must circulate in the blood, have cognate receptors, and have biological effects. Therefore future research efforts will focus on testing the ability of 1 1-dexoycortisol and ll-deoxycorticosterone binding affinity to receptor in lamprey. 35 ACKNOWLEDGEMENTS A special thanks to the staff of the US. Geological Survey, Hammond Bay Biological Station for supplying laboratory space and sea lampreys. A special thanks to Lijun Chen for her assistance with mass spectrometry and the MSU mass spectrometry facility. This research was supported and funded by the Bonneville Power Administration. A warm thanks for the support from the Confederated Tribes of the Umatilla Indian Reservation. 36 REFERENCES Baker, ME. 1997. Steroid receptor phylogeny and vertebrate origins. Molecular and Cellular Endocrinology 135: 101 -107. Bern, HA. 1967. Hormones and endocrine glands of fishes. Science 158:455-462. Bridgham, J .T., Carroll, S.M., and Thornton, J.W. 2006. Evolution of hormone-receptor complexity by molecular exploitation. Science 312:97-101. Buus, O., and Larsen, L0. 1975. Absence of known corticosteroids in blood of river lampreys (Lampetrafluviatilis) after treatment with mammalian corticotropin. General and Comparative Endocrinology 26:96-99. Escriva, H., Safi, R., Hanni, C., Langlois, M-C., Saurnitou-Laprade, P., Stehelin, D., Capron, A., Pierce, R., and Laudet, V. 1997. Ligand binding was acquired during evolution of nuclear receptors. Proceedings of the National Academy of Sciences 94:6803-6808. Fraser, R. 1992. Biosynthesis of adrenal steroids. Pages 117-130 in V.H.T. James, editor. The adrenal gland, second edition. Raven Press, New York. Idler, DR. and Truscott, B. 1967. la-Hydroxycorticosterone: synthesis in vitro and properties of an interrenal steroid in the blood of cartilaginous fish (Genus Raja). Steroids 92457-477. Idler, DR. and Truscott, B. 1972. Corticosteroids in fish. Pages 126-252 in DR. Idler, editor. Steroids in nonmammalian vertebrates. Academic Press, New York. Jones, CL, Bellamy, D., Chan, D.K.O., Follett, B.K., Henderson, I.W., Philips, J .G., and Snart, RS. 1972. Biological actions of steroid hormones in nonmammalian vertebrates. Academic Press, New York. Nelson, R.J. 2000. An introduction to behavioral endocrinology. Sinauer Associates, Sunderland, Massachusetts. Norman, A.W., and Litwack, G. 1997. Hormones. Academic Press, San Diego, CA. Sandor, T. 1972. Corticosteroids in amphibia, reptilia, and aves. Pages 253-327 in DR. Idler, editor. Steroids in nonmammalian vertebrates. Academic Press, New York. Sandor, T. and Idler, DR. 1972. Steroid methodology. Pages 126-252 in DR. Idler, editor. Steroids in nonmammalian vertebrates. Academic Press, New York. 37 Sapolsky, R.M., Romero, L.M., and Munck, A.U. 2000. How do glucocorticoids influence stress responses? Integrating permissive, suppressive, stimulatory, and preparative actions. Endocrine Reviews 21:55-89. Thornton, J .W. 2001. Evolution of vertebrate steroid receptors from an ancestral estrogen receptor by ligand exploitation and serial genome expansions. Proceedings of the National Academy of Sciences 98:5671-5676. Weisbart, M., and Idler, DR. 1970. Re-exarnination of the presence of corticosteroids in two cyclostomes, the Atlantic hagfish (Myxine glutinosa L.) and the sea lamprey (Petromyzon marinas L.). Journal of Endocrinology. 46:29-43. Weisbart, M., and Youson, J .H. 1975. Steroid formation in the larval and parasitic adult sea lamprey, Petromyzon marinas L. General and Comparative Endocrinology 27:5 1 7-526. Weisbart, M., and Youson, J .H. 1977. In vivo formation of steroids from [1,2,6,7-3H] progesterone by the sea lamprey, Petromyzon marinas L. J 01mm] of Steroid Biochemistry 8: 1249-1252. Weisbart, M., Youson, J .H., and Weibe, J .P. 1978. Biochemical, histochemical, and ultrastructural analyses of presumed steroid-producing tissues in the sexually mature sea lamprey, Petromyzon marinus L. General and Comparative Endocrinology 34:26- 37. Weisbart, M., Dickhoff, W.W., Gorbman, A., and Idler, D. 1980. The presence of steroids in the sera of the Pacific hagfish, Eptatretus stouti, and the sea lamprey, Petromyzon marinas. General and Comparative Endocrinology 41 :506-519. 38 CHAPTERZ CHARACTERIZATION OF A GLUCOCORTICOID RECEPTOR IN THE GILL OF THE SEA LAMPREY Petromyzon marinas 39 ABSTRACT This study was conducted to determine if 11-deoxycortisol or 11- deoxycorticosterone identified in chapter 1 had a receptor in the gill tissue of the sea lamprey Petromyzon marinas. Previous research has provided evidence that a corticosteroid receptor may exist in an ancient vertebrate. This prompted the hypothesis that one of the two possible corticosteroids; ll-deoxycortisol and ll-deoxycorticosterone identified must have a cognate receptor in the gill cytosol of sea lamprey. This study identified and characterized high affinity (Kd = 2.66 i 0.47 nM, mean :t SEM, n = 3), low capacity (Bmax = 58.10 i 3.33 fmollmg protein, n = 3) glucocorticoid receptors in the sea lamprey gill cytosol. The receptor appears to be highly specific for 1 1-deoxycortisol. Competitive binding assays showed that only 11-deoxycortisol displaced [3H] 11- deoxycortisol compared to nine other steroids. The glucocorticoid receptor had the highest specific 11-deoxycortisol binding activity in the intestine followed by gill, testis, liver, kidney, heart, and muscle. The specific ll-deoxycortisol-receptor complex binds to DNA-cellulose. These results are consistent with characteristics of glucocorticoid receptors in fish. 40 INTRODUCTION The nuclear receptor (NR) superfamily arose very early in the evolutionary history of animals (Laudet 1997; Escriva et al. 1997). Recent phylogenetic studies suggest that NRs evolved sometime between the Metazoan and Bilateria divergence (Thornton 2003a; Bertrand et al. 2004). The superfamily receptor groups have the characteristic of binding to small molecules such as steroids, thyroid hormones, fatty acids, and retinoic acids (Robinson-Rechavi et al. 2003). The NR superfamily consists of 1i gand-dependant transcription factors that provide the bridge between hydrophobic signaling hormones and target gene expression (Bertrand et al. 2004). The steroid receptor subgroup was thought to be restricted to vertebrates (Escriva et al. 1997; Baker 1997); however, recent research has shown that steroid receptors similar to vertebrate estrogen receptors exist in mollusks (Thornton et al. 2003b; Keay et al. 2006). While chordate estrogen receptors have ligands that are signaling hormones, protostome estrogen receptors were also found, yet it is unclear if they are functional or not (Keay et al. 2006). It is possible that the mollusks have the estrogen-like receptor but do not have the enzymes capable of producing estrogens. The sea lamprey Petromyzon marinas is an agnathan, one of the oldest extant vertebrates which emerged over 500 million years ago (Kumar and Hedges 1998; Shu et al. 1999). Thornton (2001), using PCR techniques, amplified DNA segments from sea lamprey that were homologues to parts of estrogen, progestin, and corticoid receptor genes in higher vertebrates. Phylogenetic analysis using the DNA sequences showed progestin and corticoid receptors evolved from the estrogen receptor. Recently, 41 Bridgham et al. (2006) using maximum likelihood phylogeny and existing ligand binding domain sequences, inferred the amino acid sequence of the ligand binding domain of the presumed ancestral corticoid receptor. They also synthesized the sequence of the corticosteroid ligand binding domain for use in a transactivation assay. The assay showed that aldosterone and ll-deoxycorticosterone had the highest activation levels of the luciferase reporter. In addition, Bridgham et al. (2006) provided phylogenetic evidence that the ancestral corticoid receptor was a mineralocorticoid receptor which then gave rise to the glucocoricoid receptor in teleosts and tetrapods. There have been several efforts to characterize steroid receptors from lamprey. Ho et al. (1987) characterized an estrogen binding moiety in the testes of the sea lamprey. The putative receptor shared similar binding characteristics to higher vertebrate estrogen receptor. It was thought that androgen receptor did not exist in lamprey (Thornton 2001). However, Bryan et al. (2007) provided evidence of an androgen receptor in the sea lamprey testes. The study suggested that androstenedione was the ligand; however, the study was unable to convincingly prove that the moiety was not a binding protein typically found in the gonads. There have been no studies characterizing the corticosteroid receptor in lamprey. The aim of this study was to determine if the two definitively identified steroids 11- deoxycortisol and ll-deoxycorticosterone in chapter 1 are hormones in lamprey. In order to classify identified steroids as hormones, 1) they must be in circulation in the blood; 2) they must have a receptor, and 3) they must mediate relevant biological effects. This chapter will focus on whether or not lampreys possess a receptor for either of the identified steroids from chapter 1, l 1-deoxycortisol or ll-deoxycorticosterone. 42 MATERIALS AND METHODS Animals and holding facilities Sea lamprey Petromyzon marinas were collected in streams by the US. Fish and Wildlife Service employees, and transported to Michigan State University (East Lansing, MI) or USGS Hammond Bay Biological Station (Millersburg, M1) for tissue collection. Lampreys were held at 10-13 °C in flow through tanks. Tissues collected from fish were frozen in liquid nitrogen and held at -80 °C until processed for cytosolic fractions. All experiments were approved by the Michigan State University Institutional Animal Care and Use Committee (AUF # 05/04-077-00). Materials Radiolabled steroids were obtained from American Radiolabled Chemicals (St. Louis, MO). Synthetic steroids were obtained from Steraloids (Newport, RI) and Sigma (St. Louis, MO). All other reagents were obtained from Sigma unless otherwise noted. Preparation of cytosolic fractions of tissues The decision to use gill cytosol was based on previous research to characterize glucocorticoid receptors in fish. It is well known that gill tissues mainly have glucocorticoid receptors and the receptors are expressed at higher levels than other tissues 43 in teleosts. Preparation of cytosolic fractions of tissues was adapted from Patino and Thomas (1990). Frozen tissue was ground in liquid nitrogen with a mortar and pestle. Frozen tissue was mixed 1:5 (weight: volume) in HEPES buffer (25 mM HEPES, 10 mM NaCl, 1 mM monothioglycerol, pH 7.4) and kept on ice while being homogenized. The homogenate was centrifirged at 1000 x g for 15 min at 4 °C. The supernatant containing the cytosolic fi'action was collected and the pellet discarded. The supernatant was centrifuged at 40,000 x g for l h at 4 °C. The supernatant was removed and glycerol (10% v/v) was added. Cytosolic fiactions were immediately used in subsequent assays. Saturation curve and scatchard analysis Radiolabled 1 1-deoxycortisol (0.2-20 nM) in ethanol was added to each assay tube with or without 1 pg cold 1 1-deoxycortisol (to determine non-specific binding). The ethanol was evaporated under nitrogen at 40 °C. Then, 200 pl of gill cytosol were added to the assay tubes and incubated at 0 °C for 2 h. After incubation, 500 pl of ice cold dextran coated charcoal (DCC) solution were added to assay tubes and incubated on ice for 5 min. The samples were then centrifuged at 1000 x g for 5 min at 4 °C, and the supematants were poured into scintillation vials. Six ml of scintillation cocktail were added to each vial and disintegrations per minute (DPM) were counted by a scintillation counter. The concentration of binding sites (Bmax) and the dissociation constant (KD) were determined by hyperbolic regression using Sigrnaplot v9.0 (SYSTAT, San Jose, CA, USA). Protein concentrations were determined by DC Protein Assay Kit for microplates (Bio-Rad, Hercules, CA, USA) using bovine serum albumin as a standard. 44 Association and dissociation kinetics The rate of association was determined by incubating gill cytosol (200 pl) with 3.3 nM of [3 H] ll-deoxycortisol with or without 1 pg of 1 l-deoxycortisol at 0 °C for 0-4 hr. To determine the dissociation rate, gill cytosol (200 pl) was incubated with 3.3 nM of [3 H] ll-deoxycortisol in the presence or absence of 1pg of l l-deoxycortisol at 0 °C for 2 hr and then the dissociation was initiated by adding 1 pg of 11-deoxycortisol to all assay tubes for another 0-2 hr at 0 °C. Bound and free steroid were separated by addition of DCC. The tubes were kept on ice for 5 min, and then centrifuged at 1000 x g for 5 min. The supematants were poured into 8 ml scintillation vials, mixed with 6 ml scintillation fluid and DPM were counted using a scintillation counter. Steroid and tissue binding specificity To determine steroid specificity of the binding moiety, cold steroids were used for their ability to compete with [3 H] ll-deoxycortisol binding. Gill cytosol preparations (200 p1) were incubated at 0 °C for 2 hr with 3.3 nM [3H] 11-deoxycortisol in the presence of different amounts of cold steroid (0.1-1000 nM). Specificity was examined for ll-deoxycortisol (S), ll-deoxycorticosterone (DOC), cortisol (F), corticosterone (B), aldosterone (Aldo), dexamethasone (D), androstenedione (Ad), 176-estradiol (E2), 1701- hydroxyprogesterone (17a-P), and progesterone (P). 45 Relative binding was measured in the gill, intestine, testis, liver, kidney, heart, and muscle by binding assays. Radiolabled S (5 nM) in ethanol was added to each tube in the presence or absence of 1pg of cold S and dried down. Each tube received an aliquot of gill cytosol (200 pl) and was incubated for 2 hr at 0 oC. The reaction was stopped by the addition of DCC. The tubes were kept on ice for 5 min, and then centrifuged at 1000 x g for 5 min. The supematants were poured into 8 ml scintillation vials, mixed with 6 ml scintillation fluid and DPM were counted using a scintillation counter. DNA-cellulose chromatography DNA-cellulose chromatography procedures were modified from Knoebl et al. (1996). Hepes buffer with 0.2 mg/ml BSA consisted of three different concentrations of NaCl, 0.05 M (column buffer), 0.4 M (elution buffer), and 2.0 M (wash buffer). Gill cytosol (1.0 ml) was incubated for 2 hr at 0 °C with 20 nM [3H] S with or without 2 pg cold S. Samples were placed on a lab table for 30 min at 25 °C and then cooled back down with ice for 5 min. The samples were then diluted in 3 ml of column buffer (total volume 4 ml) and added to a 20-ml column (Bio-Rad, Hercules, CA) containing 5 ml DNA-cellulose (Amersham, Piscataway, NJ) in column buffer. The sample was allowed to flow into the DNA-cellulose, and then the flow was stopped to allow absorption for 20 min. The column was then washed with 20 ml of column buffer to remove free radiolabled steroid. To elute the bound receptor complex from the DNA, 7 ml of 0.4 M 46 NaCl elution buffer followed by 7 ml of wash buffer (2.0 M NaCl) was used. One ml fractions were collected and DPM were counted using a scintillation counter. 47 RESULTS Saturation curve and determination of K, and B...“ Saturation binding assays showed specific and saturable binding moiety for S in the cytosolic fiaction of the gill homogenate (Fig. 1A). Hyperbolic regression analysis (Fig. 1B) revealed the cytosol binding moiety had a high affinity (Kd = 2.66 3c 0.47 nM, mean i SEM, n = 3) and low capacity (Bmax = 58.10 i 3.33 finol/mg protein, 11 = 3) for S. Association and dissociation kinetics Kinetic studies of the S binding moiety showed the association rate (Tl/2) was 2.11 i 0.32 min (11 = 3) and the specific binding remained constant during the experiment (Fig. 2A). The specific binding was reversible with a dissociation rate (Tl/2) of 26.44 :t 8.41 min (n = 3) during the 2-hr experiment (Fig. 2B). Steroid and tissue specificity S had the highest affinity to the cytosolic binding moiety, among the 9 steroids tested (Fig. 3). The other steroids failed to displace 50% of 3.3 nM of [3H] S up to 1000 nM concentration. At 1000 nM concentration, DOC almost displaced 50 % of [3H] S specific binding. The remaining steroids did not compete for the S binding moiety. 48 Specific binding of S to the binding moiety was found in all tissue tested (Fig. 4). The highest levels of specific binding were found in cytosolic preparations from gill, intestine, and testis. Relatively low specific binding was found in the liver, kidney, heart, and muscle tissues. DNA-cellulose chromatography The [3 H] 1 1-deoxycortisol receptor complex showed specific (BS) DNA binding in the DNA-cellulose chromatography assays (Fig. 5). The specific and non-specific (BN3) binding were both eluted with 0.40 M NaCl buffer. The 2.0 M NaCl wash buffer did not elute any additional specific or non-specific binding. 49 200001 15000- ' 3N8 Bound [3H] 11-Deoxycortisol (rnawn 1oooo- . ° sooo« . o ' . . . . o 5 1o 15 20 [3H] 11-Deoxycortisol (nM) B so- __________________________________ g 50 . Bmax 3 O 2 40 Q E 30- 3 E 20 m” 10- 0 . . . . . o 5 1o 15 20 F(nM) Figure 2-1. Representative saturation curve (A) and hyperbolic regression plot (B) of 11- dexoycortisol binding to gill cytosol. The abbreviations are; total binding (BT), specific binding (B3), non-specific binding (BN5), maximum binding capacity of tissue (Bmax), free (i.e., unbound) [3 H] l 1-deoxycortisol (F), and disintegrations per minute (DPM) are shown; n = 3. 50 100 ' . o 0 60 120 1 80 240 100 4' 80- 60' Specific [3H] 11-Deoxycortisol binding (%) 40‘ 20‘ 0 . . . . . . 0 20 40 60 80 100 120 Time (min) Figure 2-2. Association and dissociation kinetics of a sea lamprey receptor in gill cytosol. For association kinetics (A), Tm was 2.11 d: 0.32 min, 11 = 3. For dissociation kinetics (B), Tm was 26.44 i 8.41 min; 11 = 3. 51 #r——--"'— --------- v ________ v 0:100 _::-::—:~-—*~—~;_ ._- - iii-'13 : A...” ~~~~~~ """“"' ............... O§§T+ ——————— a 'g 80 . —._ s i ....................... ‘ ._ ........ O ........ DOC .D ——+—- F .2 so - _.._A._.._ 3 2‘5 ——--— Aldo .. —'—U—'— D O 8. 40 ' —+— A U) —<>— E2 °\° 20 d ........ ‘ ........ 17OHP ——-v—-- P O . 0.1 1 10 100 1000 Log Competitor Concentration (nM) Figure 2-3. Specificity of the lamprey gill cytosolic moiety for various steroids including ll-deoxycortisol (S), 11-deoxycorticosterone (DOC), cortisol (F), corticosterone (B), aldosterone (Aldo), Dexamethasone, (D), androstenedione (A), Estradiol (E2), 1701- hydroxyprogesterone (17 OHP), and progesterone (P); n = 3. 52 701 75 60- '5 '5 5°' 1L '- —I— O. E 40- : 30 - o g 20- (D m 10 ' If] 0 " . [“1“] WW— Gill Intestine Testis Liver Kidney Heart Muscle Tissue Figure 2-4. Specific binding of [3 H] ll-deoxycortisol (5 nM) to cytosolic moiety fiom different tissues. Abbreviation; specific binding (BS). Vertical bars represent means i SEM; n = 3. 53 ’2‘ n. 9, 2000 0.05 M NaCl , 0.40 M NaCl . 2.0 M NaCl 3 1 ' ' .22 ' ' ‘l: 1500 I ' 3 . ' g i —e— B... I I C? . '*‘ 3,, | g I .— 500 1 I m:I: H ‘ 0"°.0--o.--O"‘O"'¢"“O""O g o ITTTTTFCJZ-virrr"" o m 0 5 10 15 20 Fraction Figure 2- 5. Elution of 1 l-deoxycortisol-receptor complex from DNA-cellulose. Gill cytosol was preincubated with 20 nM [3H] ll-deoxycortisol before binding to the column of DNA-cellulose. Abbreviations are; total binding (137), specific binding (BS), nonspecific binding (BN5), and disintegrations per minute (DPM) are shown; 11 = 3. 54 DISCUSSION This study has provided several lines of evidence to support the hypothesis that ll-deoxycortisol is a stress steroid and has a glucocorticoid receptor in the gill of an ancestral vertebrate, the sea lamprey. Our study demonstrated the presence of a glucocorticoid receptor in the gills of the sea lamprey. The binding moiety was characterized by high affinity, low capacity glucocorticoid binding sites specific to 11- deoxycortisol within gill cytosolic extracts. The dissociation constant (Kd) in our study falls within the range reported for glucocorticoid receptors using [3 H] cortisol in the gill, liver, intestine, muscle, leukocytes, erythrocytes and brain of sahnonids (Chakraborti et al. 1987; Chakraborti and Weisbart 1987; Pottinger 1990; Maule and Schreck 1991; Knoebl et al. 1996; and Pottinger and Brierley 1997). The concentration of binding sites (Bmax) in our study was lower than concentrations (224 fmol/mg protein) found in salmonid gill tissue (Chakraborti et a1. 1987), but was higher than salmonid brain, intestine, and leukocytes (Chakraborti et al. 1987; Maule and Schreck 1991; Knoebl et al. 1996) In our study, the glucocorticoid binding moiety shared similar binding characteristics to glucocorticoid receptors in salmonids (Chakraborti and Weisbart 1987; Chakraborti et al. 1987). Although, the association and dissociation rates of the lamprey glucocorticoid receptor were similar to salmonid glucocorticoid receptor, the rates (Tl/2) were faster. For example, Knoebl et al. (1996) using brain cytosolic extracts estimated 55 the dissociation rate Tm = 64.3 min, compared to T1 /2 = 26.44 min using gill cytosol in our study. The sea lamprey corticoid binding moiety is highly specific to 11-deoxycortisol. The specificity of the corticosteroid binding moiety in the gill was different than those reported for other glucocorticoid receptors found in fish (Chakraborti et al. 1987; Chakraborti and Weisbart 1987; Pottinger 1990; Maule and Schreck 1991; Knoebl et al. 1996; and Pottinger and Brierley 1997). In this study, the synthetic steroids dexarnethasone and triamcinolone acetonide (data not shown), along with natural corticosteroids, were ineffective at displacing ll-deoxycortisol from the binding moiety. Chakraborti et al. (1987) found ll-deoxycortisol had the highest affinity of the natural corticosteroids tested with brook trout (Salvelinusfontinalis) gill receptors followed by cortisol and corticosterone. Recently, Bridgeham et al. (2006) using existing corticoid ligand binding domain sequences, inferred the amino acid sequence of the ligand binding domain of the presumed ancestral corticoid receptor. They synthesized the ligand binding domain of the corticoid receptor in lamprey and developed a transactivation assay. Their assay showed the ligand binding domain to be activated by aldosterone, 11- deoxycorticosterone, ll-deoxycortisol, corticosterone, and cortisol. The current study used native receptor complex and found highly specific binding only for 1 1-deoxycortisol with limited displacement binding at high concentrations of 1 l-deoxycorticosterone. The steroid specificity assay and plasma screening for cortisol and corticosterone (chapter 1) provides strong evidence that the ancestral vertebrate does not produce cortisol or corticosterone and thus lacks the 11 fl-hydroxylase enzyme. This could 56 explain why in our study, the native receptor does not recognize cortisol or corticosterone. The findings using the native receptor contrast the results of Bridgeham et al. (2006). However, they used an inferred amino acid sequence and only included the ligand binding domain of the receptor. This may have changed the protein conformation creating a nonspecific sequence allowing other corticosteroids to bind. Our study detected an ll-deoxycortisol binding moiety in tissues that have been characterized for glucocorticoid receptor in salmonids (Chakraborti et al. 1987; Chakraborti and Weisbart 1987; Pottinger 1990). In addition, specific ll-deoxycortisol binding moiety was observed in all tissues tested, however, much higher capacity was found in gill, intestine, testis and much lower in liver, kidney, heart and muscle. Our study has shown that the sea lamprey ll-deoxycortisol receptor complex binds to DNA-cellulose, indicating that it is a nuclear steroid receptor. Similar to earlier glucocorticoid receptor studies, heat activation was important for increasing the levels of specific binding during DNA-cellulose chromatography (Eisen and Glinsmann 1978; Knoebl et al. 1996). This study showed glucocorticoid receptor complex eluting from the DNA-cellulose with 0.4 M NaCl column buffer, which was similar to the findings of Knoebl et al. (1996). No further specific binding or nonspecific binding peaks were found after elution with the 2.0 M NaCl wash buffer, indicating that activated receptor complex binds to DNA-cellulose. Functional corticosteroid binding globulin (CBG) has not been found in lower vertebrates (Breuner and Orchinik 2002). Breuner and Orchinick (2002) report that a cDNA sequence of a CBG homologue was found in zebrafish, however, the authors doubted that it fiinctioned as a CBG. There is no other evidence supporting CBG in 57 lower vertebrates. Therefore, it is unlikely that the binding moiety is a CPG in our study. The results demonstrated that the ll-deoxycortisol receptor complex binds to DNA. Recent studies have focused on steroid receptors and their role in increasing regulatory and developmental complexity in vertebrates (Baker 1997; Baker 2001; Baker 2004; Whitfield et al. 1999). There is evidence that teleostean fish experienced an additional whole-genome duplication event that led to increased speciation and biodiversity (Hoegg et al. 2004; Volff 2005). Thornton (2001) provided evidence that the ancient corticoid receptor gene may have experienced a gene duplication event, which led to the development of glucocorticoid and mineralocorticoid receptors in later vertebrates. A previous study found ll-deoxycorticosterone circulating in the ancestral vertebrate (chapter 1) and that the steroid had a higher relative affinity to the receptor compared to other corticosteroids tested. Recently, Sturrn et al. (2005) using transactivation assays provided evidence that 11-deoxycorticosterone might be the ancestral hormone associated with the mineralocorticoid receptor in rainbow trout Oncorhynchus mykiss. Gillrnour (2005) suggested that in order to establish that 11- deoxycorticosterone as a mineralocorticoid receptor ligand, it must increase in circulation with a physiological stressor. In addition, it should not only increase, but it must also be used in characterization of the receptor and show biological effects. The recent findings suggest that 1 1-deoxycorticosterone might be the putative hormone for the ancestral mineralocorticoid receptor which arose after agnathans, but before chondrichthyes diverged (Bury and Sturm 2007). Our study provided the first characterization of a glucocorticoid receptor in one of the earliest extant vertebrates, the sea lamprey. The results provide evidence that 11- 58 deoxycortisol is highly specific for the glucocorticoid receptor. The next step in confirming that ll-deoxycortisol is the actual hormone is to provide evidence of biological effects. 59 ACKNOWLEDGEMENTS We thank the staff of the US. Geological Survey, Hammond Bay Biological Station for supplying sea lampreys. I would like to thank the Bonneville Power Administration for providing funding and support for this research. I would also like to thank the Confederated Tribes of the Umatilla Indian Reservation for support. 60 REFERENCES Baker, ME. 1997. Steroid receptor phylogeny and vertebrate origins. Molecular and Cellular Endocrinology 135:101-107. Baker, ME. 2001. Adrenal and sex steroid receptor evolution: environmental implications. Journal of Molecular Endocrinology 26:119-125. Baker, ME. 2004. Co-evolution of steroidogenic and steroid-inactivating enzymes and adrenal and sex steroid receptors. Molecular and Cellular Endocrinology 215:55-62. Bertrand, S., Brunet, F .G., Escriva, H., Parmentier, G., Laudet, V., and Robinson- Rechavi, M. 2004. Evolutionary genomics of nuclear receptors: from twenty-five ancestral genes to derived endocrine systems. Molecular Biology and Evolution 21:1923-1937. Breuner, C.W., and Orchinik, M. 2002. Plasma binding proteins as mediators of corticosteroid action in vertebrates. Journal of Endocrinology 175:99-112. Bridgham, J .T., Carroll, S.M., and Thornton, J .W. 2006. Evolution of hormone-receptor complexity by molecular exploitation. Science 312297-101. Bury, NR, and Sturm A. 2007. Evolution of the corticosteroid receptor signaling pathway in fish. General and Comparative Endocrinology 153247-56. Chakraborti, PK, and Weisbart, M. 1986. High-affinity cortisol receptor activity in the liver of the brook trout, Salvelinusfontinalis (Mitchill). Canadian Journal of Zoology 65:2498-2503. Chakraborti, P.K., Weisbart, M., and Chakraborti, A. 1987. The presence of corticosteroid receptor activity in the gills of the brook trout, salvelinusfontinalis. General and Comparative Endocrinology 66:323-332. Eisen, H.J., and Glinsmann, W.H. 1978. Maximizing the purification of the activated glucocorticoid receptor by DNA-cellulose chromatography. Biochemical Journal 171:177-183. Escriva, H., Safi, R., Hanni, C., Langlois, M-C., Saumitou-Laprade, P., Stehelin, D., Capron, A., Pierce, R., and Laudet, V. 1997. Ligand binding was acquired during evolution of nuclear receptors. Proceedings of the National Academy of Sciences 94:6803-6808. 61 Gillmour, KM. 2005. Mineralocorticoid receptors and hormones: fishing for answers. Endocrinology 146:44-46. Ho, S-M., Press, D., Liang, L-C., and Sower, S. 1987. Identification of an estrogen receptor in the testis of the sea lamprey, Petromyzon marinas. General and Comparative Endocrinology 67:119-125. Keay, J ., Bridgham, J .T., and Thornton, J .W. 2007. The octopus vulgaris estrogen receptor is a constitutive transcriptional activator: evolutionary and functional implications. Endocrinology 147 :3861-3869. Knoebl, I., Fitzpatrick, MS, and Schreck, CB. 1996. Characterization of a glucocorticoid receptor in the brains of Chinook sahnon, oncorhynchus tshawytscha. General and Comparative Endocrinology 101:195-204. Kumar, S., and Hedges, SB. 1998. A molecular timescale for vertebrate evolution. Nature 392:917-920. Laudet, V. 1997. Evolution of the nuclear receptor superfamily: early diversification from an ancestral orphan receptor. Journal of Molecular Endocrinology 19:207-226. Maule, A.G., and Schreck, CB. 1991. Stress and cortisol treatment changed affinity and number of glucocorticoid receptors in leukocytes and gill of coho salmon. General and Comparative Endocrinology 84:83-93. Patino, R., and Thomas, P. 1990. Characterization of membrane receptor activity for 17 a, 203, 21-trihydroxy-4-pregnen-3-one in ovaries of spotted seatrout (Cynoscion nebulosus). General and Comparative Endocrinology 78:204-217. Pottinger, TC. 1990. The effect of stress and exogenous cortisol on receptor-like binding of cortisol in the liver of rainbow trout, Oncorhynchus mykiss. General and Comparative Endocrinology 78: 194-203. Pottinger, T.G., and Brierley, I. 1997 . A putative cortisol receptor in the rainbow trout erythrocyte: stress prevents starvation-induced increases in specific binding of cortisol. The Journal of Experimental Biology 200:2035-2043. Robinson-Rechavi, M., Garcia, HE, and Laudet, V. 2003. The nuclear receptor superfamily. Journal of Cell Science 116:585-586. Shu, D-G., Luo, H-L., Monis, S.C., Zhang, X-L., Hu, S-X., Chen, L., Han, J., Zhu, M., Li, Y., and Chen, L-Z. 1999. Lower Cambrian vertebrates from south China. Nature 402242-46. 62 Sturm, A., Bury, N., Dengreville, L., Fagart, J ., Flouriot, G., Rafestin-Oblin, ME, and Prunet, P. 2005. ll-Deoxycorticosterone is a potent agonist of the rainbow trout (Oncorhynchus mykiss) mineralocorticoid receptor. Endocrinology 146:47-55. Thornton, J .W. 2001. Evolution of vertebrate steroid receptors from an ancestral estrogen receptor by ligand exploitation and serial genome expansions. Proceedings of the National Academy of Sciences 98:5671-5676. Thornton, J .W. 2003a. Nonmammalian nuclear receptors: evolution and endocrine disruption. Pure Appl. Chem. 75: 1827-1839. Thornton, J .W., Need, E., and Crews, D. 2003. Resurrecting the ancestral steroid receptor: ancient origin of estrogen signaling. Science 301 :1714-1717. Volff, J -N. 2005. Genome evolution and biodiversity in teleost fish. Heredity 94:280-294. Whitfield, G.K., Jurutka, P.W., Haussler, CA., and Haussler, MR. 1999. Steroid hormone receptors: evolution, ligands, and molecular basis of biologic firnction. Journal of Cellular Biochemistry Supplements 32/33:110-122. 63 CHAPTER 3 BIOLOGICAL ROLES OF ll-DEOXYCORTISOL IN MEDIATING STRESS RESPONSES OF THE SEA LAMPREY Petromyzon marinus 64 ABSTRACT This study was conducted to assess whether ll-deoxycortisol serves as a glucocorticoid in the ancient vertebrate, the sea lamprey Petromyzon marinas. Earlier research has shown that 1 1-deoxycortisol circulates in the blood and has a specific receptor in the gills of the sea lamprey. In this study, the hypothesis was that 11- deoxycortisol would exhibit a classical stress response and have biological effects. After acute stress, an increase in ll-deoxycortisol levels occurred by 1 h and remained elevated for at least 8 h, recovering to basal level by 24 h. 1 1-deoxycortisol implants elevated circulating levels of 1 1-deoxycortisol and reduced levels of classic androgens and estrogens in the plasma. The implants also increased gill Na+, K+-ATPase activity in lamprey. Mammalian corticotropin releasing hormone injections sharply increased plasma levels of 1 l-deoxycortisol. In addition, lamprey pituitary extract injections increased plasma concentrations of 1 l-deoxycortisol in a dose response manner. This study provided strong evidence that 11-deoxycortisol is an ancient glucocorticoid in the lamprey. 65 INTRODUCTION The stress response is vital to vertebrates and is well conserved among the jawed vertebrates. In tetrapods, an important component of the stress steroid response system is the hypothalamic-pituitary—adrenal (HPA) axis (Chrousos 1998). Teleosts have the same system, except they secrete corticosteroids from interrenal cells located in the anterior portion of the kidneys (N andi and Bern 1960; Wendelaar Bonga 1997; Barton 2002). The secretion of the corticosteroids is mainly under the control of the neuropeptides corticotropin-releasing hormone (CRH) and adrenocorticotropic hormone (ACTH) (W endelaar Bonga 1997; Maj zoub 2006). The hypothalamus is stimulated to release CRH, which in turn mediates the release of ACTH from the pituitary in jawed vertebrates. ACTH then binds to receptors in the adrenal or interrenal cells to release corticosteroids into circulation. While the physiological stress steroid response is well conserved in vertebrates, the chemical structures of the corticosteroids are different. There are two types of corticosteroids in vertebrates, the glucorticoids and mineralocorticoids. Glucocorticoids regulate metabolism and are released in response to a stressor (Sapolsky et al. 2000). Cortisol and corticosterone, which differ only by the absence a 17-01 hydroxyl, are the two principal glucocorticoids in animals. Mammals secrete cortisol; while rats and mice secrete corticosterone. Reptiles and birds also produce and circulate corticosterone as their primary glucocorticoid (Nelson 2000). Fish, 66 on the other hand, secrete cortisol as their glucocorticoid (Idler and Truscott 1972; Mommsen et al. 1999; Wendelaar Bonga 1997; Barton 2002), with the exception of elasmobranchs which synthesize la—hydroxycorticosterone (Idler and Truscott 1967; Nunez and Trant 1999). It was previously thought that glucocorticoids in fish also functioned as mineralocorticoids (Wendelaar Bonga 1997). Aldosterone is the principal mineralocorticoid in terrestrial vertebrates (Nelson 2000). Aldosterone is important in regulation of mineral and ion balance in vertebrates (Norman and Litwack 1997). Evidence to support aldosterone circulating in fish seems to be absent (Gilmour 2005; Bury and Sturm 2007). However, Sturm et al. (2005) has shown that ll-deoxycorticosterone is specific for a cloned portion of the mineralocorticoid receptor in rainbow trout. Their study suggests that 11- deoxycorticosterone may be a putative mineralocorticoid in fish (Sturm et al. 2005). Bridgham et al. (2006) found a mineralocorticoid receptor homologue in the skate, Raja erz’nacea but not in lamprey. It was unclear if one of the earliest vertebrates, the lamprey, contains a stress steroid. The lamprey is an agnathan, one of the oldest extant vertebrates which emerged over 500 million years ago (Kumar and Hedges 1998; Shu et al. 1999). To discover the actual stress hormone would be an important step in understanding the evolution of steroid receptor systems in the vertebrates. Two putative glucocorticoids were identified, ll-deoxycortisol and 11- deoxycorticosterone, circulating in the lamprey plasma (Chapter 1). Further, the results from chapter 2 have shown that ll-deoxycortisol has a specific glucocorticoid receptor in the gill of lamprey. The last lines of evidence needed to support the claim that 11- 67 deoxycortisol is an ancestral glucocorticoid was to show classic glucocorticoid response to stress and to show biological effects. The specific questions for this study are: 1) Does ll-deoxycortisol show a classical stress steroid response, sharply rising and returning to basal levels? 2) Will ll-deoxycortisol implants reduce classical androgens and estrogens in circulation and increase gill Na+, K+-ATPase activity? 3) Will mammalian CRH increase circulating levels of 1 l-deoxycortisol? 4) Will lamprey pituitary extract increase circulating levels of 11-deoxycortisol? 68 MATERIALS AND METHODS Source of Animals Sea lamprey, Petromyzon marinus, were collected in streams by US. Fish and Wildlife Service employees, and transported to Michigan State University (East Lansing, M1) or Hammond Bay Biological Station (Millersburg, MI) for collecting tissues where they were held at 10-13 °C. Tissues collected from fish were frozen in liquid nitrogen and held at -80 °C until processed. All experiments were approved by the Michigan State University Institutional Animal Care and Use Committee (AUF # 05/04-077-00). Handling and Salinity Stressors Adult lampreys were acclimated in flow through tanks (254 L) at least 2 weeks before stress tests were conducted. Tanks were isolated to keep people from disturbing the lampreys during acclimation. In the first stress experiment (1-48 h recovery), 140 lampreys were distributed in tanks at a density of 7 lampreys/tank with replicate tanks for each treatment at each time. No lampreys were sampled more than once. In the second stress experiment (1-24 h recovery), 80 parasitic lampreys were distributed in tanks at a density of 5 lampreys/tank with replicate tanks for each treatment at each time. No 69 lampreys were sampled more than once. Lampreys were netted out of tanks and placed in a dry bucket for 5 min then transferred to 3 % salt water for 10 min. Handling and salinity tests are routine methods to elicit a stress steroid response in teleosts (Wedemeyer et al. 1990). To obtain plasma, lampreys were netted out of tanks and immersed in anesthetic dose of 400 mg/L of tricaine methanesulfonate (MS-222) buffered with sodium bicarbonate. Blood samples were collected at 1, 4, 8, 24, and 48 h after stressors to measure steroid levels. For parasitic lampreys, blood was sampled at 1 and 24 h after stressors. Lampreys were then euthanized with a lethal dose of MS-222. Blood was centrifuged at 1000 x g at 4°C for 15 min and plasma removed. Plasma was stored at -80 °C until analysis. Radioimmunoassay (RIA) procedure RIAs were conducted in glass culture tubes (10 mm X 75mm, Fisher Scientific, Pittsburgh, PA). Briefly, the assay buffer consisted of 50 mM sodium phosphate, pH 7.4, 0.2% BSA, 137 mM NaCl, 0.40 mM EDTA, and 0.77 mM sodium azide. Nine standards were made up in duplicate over the range 500-1.95 pg/ 100 pl/tube. The tubes containing unknowns also had a volume of 100 ul. Binding reagent was made by adding radiolabel and antiserum to 20 ml of assay buffer in amounts such that, when 100 ul was dispensed to all tubes, each tube contained 5000 dpm and in the absence of any standard, 50% of the radiolabel was bound to the antiserum. Blank tubes, to which no antibody was added, and tubes necessary to determine the total and maximum dpm counts, were also included in the assay. All tubes were incubated overnight at 4 °C. After overnight incubation, 500 70 pl of ice-cold charcoal solution (50 mM sodium phosphate, Pb 7.4, 0.1% gelatin, 1.0% dextran-coated charcoal) was added to each tube. The tubes were kept on ice for 20 min, and then centrifuged at 1000 x g for 12 min. The supematants were poured into 8 ml scintillation vials, mixed with 6 ml scintillation fluid and DPM were counted using a scintillation counter. Steroid implants 11-Deoxycortisol (Sigma-Aldrich, St. Louis, MO) time release pellets were made by Innovative Research of America (Sarasota, F1). The 21-day slow release steroid implants (5 mg/pellet) were injected between the muscle and the skin near the front dorsal fin of the sea lamprey. A total of 48 lampreys were distributed in flow through tanks (254 L) at a density of 6 lampreys/tank with replicate tanks for each treatment. On the 21St day, blood samples and gill tissues were collected. Plasma was analyzed by RIAs for ll-deoxycortisol (S), 1 1-deoxycorticosterone (DOC), dehydroepiandrosterone-sulfate (DHEA-S), dehydroepiandrosterone (DHEA), androstenedione (AD), testosterone (T), estrone (E1), and estradiol (E2). Gill Na+, K+-ATPase Activity A gill pouch was removed and placed in ice-cold SEI buffer (150 mM sucrose, 10 mM EDTA, 50 mM imidazole, pH 7.3) and frozen immediately at -80 °C. Na+, K'- ATPase activity was determined with a kinetic assay run in 96-well microplates at 25 °C 71 and read at a wavelength of 340 nm for 10 min as described in McCormick (1993). Gill tissue was homogenized in 500 111 SEID (SEI buffer and 0.1% deoxycholic acid) and centrifuged at 5000 x g for 30 5. Ten pl samples were run in two sets of duplicates; one set containing the assay mixture and the other assay mixture and 0.5 mM ouabain. The resulting ouabain-sensitive ATPase activity is expressed as pmoles ADP/mg protein/h. Protein concentrations were determined using BCA (bicinchoninic acid) Protein Assay (Pierce, Rockford, 11). Both assays were run on a THERMOmax microplate reader using SOFTmax software (Molecular Devices, Menlo Park, CA). Corticotropin Releasing Hormone Injections Mammalian corticotropin releasing hormone (CRH) (Si gma-Aldrich) was dissolved in 0.9% saline and injected intraperitoneally with a dose of 100 pg/Kg. Saline solution was used as a control. Blood samples were collected 1 hr after injections by cardiac puncture using vacutainers (Becton Dickinson, Franklin Lakes, NJ ,). Blood samples were centrifuged at 1000 x g for 15 min; plasma was collected and stored at -80 °C until analyzed by RIA for S. Pituitary extract injections To obtain pituitary extract, sea lamprey pituitary glands from 400 adults were collected in June 2000, at Hammond Bay Biological Station (Millersburg, MI, USA). The frozen pituitary glands were homogenized in 20 ml of 20-mM Tris buffer, pH 7, 72 containing protease inhibitor cocktails (Roche, Nutley, NJ, USA). This mixture was centrifuged at 1000g for 20 min allowing recovery of the supernatant. The protein concentration was determined using DCA protein analysis kit (Pierce, Rockford, IL). The protein concentration for the extract was 6.7 mg/ml. One milliliter of the extract was equivalent to 201amprey pituitary glands. Lampreys were given a single intraperitoneal injection of equivalent to 1, 5, or 10 pituitaries or a 0.9% saline as a control (4 treatments total, 10 lampreys per treatment). Blood was sampled at 0, 6, 12, 24, and 48 h after the injection. Blood samples were centrifuged at 1000 x g for 15 min; plasma was collected and stored at -80 °C until analyzed by RIA for S. Statistical analysis Statistical analysis of the acute stress experiments was done using Analysis of Variance (AN OVA) in which time was an independent variable. Comparisons among time intervals were compared using Bonferroni’s multiple comparison tests. Analysis of the implant experiments was done using an Unpaired t test with Welch’s correction. Males and females were analyzed separately. The corticotropin releasing hormone injection experiment was also analyzed by an unpaired t test. Analysis of the pituitary extract experiment was done with repeated measures two-way ANOVA in which pituitary equivalent dosage and time were factors. 73 RESULTS Acute Stress Response Spawning phase adult lampreys subjected to a 5-min dewatering and 3% salt water bath (10 min) exhibited a sharp increase in S levels within 1 hr (Fig 1A). Plasma S levels in control lampreys were 1.09 i 0.06 ng ml”, while stressed lampreys elevated levels to 2.38 :t 0.14 pg ml'1 (P < 0.001) at l h. Concentrations of plasma S remained elevated at least for 8 h, returning to control levels by 24 h. Parasitic male and female lampreys subjected to a 5-min dewatering and 3% salt water bath (10 min) exhibited a sharp increase in S levels within 1 hr (Fig. 1B). Plasma S levels in stressed male lampreys was 1.08 :l: 0.09 ng ml", compared to control levels 0.45 i 0.04 ng ml'l (P < 0.001) at 1 h. Plasma S levels in stressed female lampreys was 1.46 :l: 0.19 ng ml”, compared to the control levels 0.39 :l: 0.01 ng ml'1 (P < 0.001) at 1 h. Plasma levels of S in male and female parasitic phase lampreys returned to control levels by 24 h. We found basal levels of S nearly doubled from the parasitic stage to the spawning phase in lampreys. Effects of steroid implants The S implants caused an increase in plasma levels of S and DOC in male and female lampreys (Fig. 2). S implanted male lampreys had a mean S level of 18.9 :1: 2.0 ng ml”, compared to 1.1 i .06 ng ml'1 (P < 0.0001) in control implanted lampreys (Fig. 2A). 74 Implanted female lampreys had a mean S level of 20.5 d: 3.0 ng ml’l , compared to 1.2 :l: 0.09 ng ml'1 (P < 0.0001) in control lampreys. The S implants also increased circulating DOC in males from 0.84 i 0.02 ng ml" to 2.55 :h 0.14 ng ml" (P < 0.0001) (Fig. 2B). The S implants increased circulating DOC levels from 0.54 :l: 0.02 ng ml" to 1.95 :l: 0.17 ng ml'1 (P < 0.0001) in female lampreys. The S implants caused a decrease in plasma levels of DHEA-S and DHEA in male and female lampreys (Fig. 3). Implanted male and female lampreys decreased mean plasma DHEA-S levels from 2.66 a: 0.15 ng ml" and 1.61 i 0.07 ng ml" to 2.16 i 0.11 ng ml'1 and 1.30 :I: 0.07 ng ml" (P = 0.01) respectively (Fig. 3A). Implanted male and female lampreys decreased mean plasma DHEA levels from 0.32 i 0.01 ng ml'1 and 0.28 a: 0.008 ng ml" to 0.29 i: 0.008 mg ml" (P = 0.04) and 0.21 :t 0.02 ng ml" (P = 0.02) respectively (Fig. 3B). The mean plasma levels of AD in male and female lampreys implanted with S were not significantly different (Fig. 4A). However, plasma levels of T decreased in male and female lampreys implanted with S (Fig. 4B). Implanted male and female T levels decreased from 0.31 :1: 0.005 ng ml'1 and 0.23 i 0.01 ng ml" to 0.27 i 0.01 ng ml'1 (P = 0.002) and 0.17 1. 0.01 ng ml" (P = 0.005) respectively. Implants caused a decrease in mean plasma level of E1 in male lampreys, but not in female lampreys (Fig. 5A). Mean plasma E1 levels in males implanted with S was 1.76 i 0.15 ng ml", while plasma levels in control lampreys were 2.46 i 0.18 ng ml'1 (P = 0.009). lrnplants decreased plasma levels of E2 in male and female lampreys (Fig. 5B). The mean plasma level of E2 in control males and females was 3.50 i 0.28 ng ml'1 and 75 2.03 :1: 0.13 ng ml", with levels decreasing to 2.44 :l: 0.21 ng ml" (P = 0.008) and 1.12 i 0.12 ng ml'1 (P = 0.0001) respectively. Na+, K+-ATPase Activity The S implants nearly doubled gill Na+, K+-ATPase activity in both male and female lamprey after 21 days (Fig. 6). The gill Na+, K+-ATPase activity was 2.9 d: 0.23 pmol ADP/mg protein/h and 2.8 :t 0.22 pmol ADP/mg protein/h, in control male and female lamprey, with levels increasing to 5.7 :l: 0.53 pmol ADP/mg protein/h (P < 0.0001) and 4.1 i 0.30 pmol ADP/mg protein/h (P = 0.002). Corticotropin Releasing Hormone Injections Mammalian CRH injections markedly increased plasma S levels in male and female lampreys 1 hr after injection (Fig. 7). Mean plasma S level in saline injected male lampreys was 0.99 i 0.13 ng ml" and increased to 2.08 i: 0.39 ng ml" (P = 0.02). Mean plasma S level in saline injected female lampreys was 0.72 :l: 0.12 ng ml'1 and increased to 2.84 i 0.28 ng ml" (P = 0.001). Pituitary Extract Injections Pituitary extract injections increased plasma S levels in a dose dependent manner (Fig. 8). The 1, 5, and 10 pituitary equivalent treatments significantly increased plasma S 76 levels to 2.11 d: 0.51 (P = 0.002), 3.16 i: 0.55 ng ml'1 (P < 0.0001), and 3.31 :t 0.52 ng ml' 1 (P < 0.0001) from a control level of 1.35 :l: 0.40 ng ml'1 at 6 h. By 12 h, all treatment groups except for the 10 pituitary equivalent group returned to control levels. At 48 h, the l pituitary equivalent group was slightly reduced compared to control levels. 77 2'5 i I 1: Control ** ** I: Stress 2.0 - i I} E 1.5 - a . 5 1.0- g . E 0.5 8 0 0 ' >1 3 1 4 8 24 48 w n a. 2 o . B Time (h) ‘— To ' ** :1 1h Control E 1.5 . _ 1h Stress to m 24h Control 2 ** 1:! 24 h Stress n. 1.0 - 0.5 - 0.0 , Male Female Figure 3-1. Effect of handling and salt challenge stressors on plasma levels of 11- deoxycortisol for spawning (A) and parasitic (B) phase lamprey during recovery. Vertical bars represent means i SEM of 6-14 observations. *, P < 0.05; **, P < 0.01; ***, P < 0.001. *** 31’ > 1+. 1: Control I: S implant .3 UI (nglml) 10: Plasma 11-Deoxycortisol 3.0 - B m 2.5 -' "Ii 2.0 -' 3f 1.5 - 1.0 - .° 01 0.0 - i H- ' Male Female Plasma 11-Deoxycorticosterone (nglml) Figure 3-2. Effect of 21 d ll-deoxycortisol implant treatment on plasma levels of 11- deoxycortisol (A) and ll-deoxycorticosterone (B). Vertical bars represent means :1: SEM of 1 1-12 observations. *, P < 0.05; **, P < 0.01; ***, P < 0.001. 79 9" o :1 Control S implant lilil> 1+. 1+1 _L O Plasma DHEA-S (nglml) 99 #0 0.3- {-2 {E- . * 0.1 1 Plasma DHEA (nglml) O N I-H 0.0 . " . ‘ Mal Female Figure 3-3. Effect of 21 d ll-deoxycortisol implant treatment on plasma levels of Dehydroepiandrosterone-sulfate, DHEA-S (A) and Dehydroepiandrosterone, DHEA (B). Vertical bars represent means i SEM of 11-12 observations. *, P < 0.05; **, P < 0.01; ***, P < 0.001. 80 d) g . A 1:3 Control :5 [:1 S implant o 0.3 - E, 2 *2 s .5 g 0.2 - c I < E 0.1 - 1n .9 1 m 0.0 . 0.4 - a) . c g 0.3- T" ** 1;; c 1* *3 E 02 .2 .3.“ g . m 0.1 ~ 2 Q- 0.0 Male Female Figure 3-4. Effect of 21 d 1 1-deoxycortisol implant treatment on plasma levels of androstenedione (A) and testosterone (B). Vertical bars represent means i SEM of 11-12 observations. *, P < 0.05; **, P < 0.01; ***, P < 0.001. 81 3.0 - 2.5 - 1.5 - 1.0 . 0.5 ' Plasma Estrone (nglml) 0.0 [:1 Control CI] 3 implant 4.0 - 3.0 - 2.0 - 1.0 - Plasma Estradiol (nglml) *** v - unmuu 0.0 Male Female Figure 3-5. Effect of 21 d 11-deoxycortisol implant treatment on plasma levels of estrone (A) and estradiol (B). Vertical bars represent means i SEM of 11-12 observations. *, P < 0.05; **, P < 0.01; ***, P < 0.001. 82 *** :13 Nw-hOION Na"'-K"'-ATPase Activity (pmol ADP/mg protein/h) lulu“ llllll :1 Control I: S implant ** {— 0 Female Figure 3-6. Effect of 21 d ll-deoxycortisol implant treatment on gill Na: K+-ATPase activity. Vertical bars represent means :1: SEM of 11-12 observations. *, P < 0.05; **, P < 0.01; ***, P < 0.001. 83 g 35 . 1:1 Saline injected 2) :1 CRH injected ** : 3.0 - _E_ o .2 2.5- * E o 2.0 - 2 o 1.5 - 8 ‘; 1.0 - ‘_ «1 0.5 - E g 0.0 . - 0- Male Female Figure 3-7. Changes in concentration of plasma 1 1-deoxycortisol following injections of mammalian CRH. Vertical bars represent means i SEM of 3-5 observations. *, P < 0.05; **, P < 0.01; ***, P < 0.001. 84 E l:|Saline(n=9) El 4000' i i I:I1x(n=10) E'- * -5x(n=9) 3 -10x(n=10) 53 3000- * E * * 0 5‘ 2000- j 3 l l * , 1 ~ 1 11 l l S 1000- to E 8 0J__-_ _.lh. Li. —-H L..— E 0 6 12 24 48 Time (h) Figure 3-8. Changes in concentration of plasma ll-deoxycortisol following injections of pituitary extract. Vertical bars represent means i SEM of 9-10 observations. *, P < 0.05; **, P < 0.01; ***, P < 0.001. 85 DISCUSSION Our study has provided several lines of evidence to support the hypothesis that S is an ancestral glucocorticoid hormone. The results demonstrated that circulating S responds to acute stress in the ancient vertebrate, the sea lamprey. In lamprey, S exhibits similar characteristics to the classical cortisol responses in teleosts. In this study, S levels increased significantly within 1 hour of an acute stressor, remained elevated for at least 8 h, and returned to basal levels by 24 h. In most teleosts, cortisol levels generally increase rapidly, peaking within 1-2 h after exposure to an acute stressor, remain elevated, followed by recovery (Pickering et al. 1987 ; Barton 2002; Milston et al. 2006). Plasma S levels doubled after acute stress in lamprey, however, the levels were found to be lower than cortisol levels measured in most fishes (Barton and Iwama 1991; Barton 2002). This study showed that S response to acute stress in lamprey was most similar to cortisol levels in stressed Pallid sturgeon Scaphirhynchus albus (Barton 2002). Parasitic phase lamprey had lower basal plasma S levels compared to spawning phase lamprey. The pattern of increasing cortisol levels during spawning phase salmonids is well documented (Carruth et al. 2000). Our study demonstrated that S has classic glucocorticoid effects such as decreasing androgens, estrogens, and increasing gill Na+, K+-ATPase activity in the ancient vertebrate. This study found that S implants decreased classical androgens in the plasma of lamprey. The S implants also significantly reduced plasma levels of androgens DHEA-S, DHEA and T. The synthetic glucocorticoid dexamethasone has been shown to decrease DHEA-S, DHEA, AD, and T in humans (Abraham 1974; Kalimi et al. 1994). 86 Acute and chronic stressors have been shown to elevate plasma glucocorticoid, while decreasing T in fish (Pickering et al. 1987; Pankhurst and Dedual 1994), amphibians (Moore and Zoeller 1985), and reptiles (Lance and Elsey 1986). Cortisol implants were also shown to be effective at reducing plasma levels of T in fish (Carragher et al. 1989; F00 and Lam 1993A,B). Interestingly, S implants did not reduce circulating AD in lamprey, even though Bryan et al. (2007) provided evidence that AD was an androgen in the sea lamprey. One possibility is that AD is not the principal androgen and that the ancestral vertebrate utilizes the 5-ene pathway to T. It is well known that the biosynthetic pathway can go from DHEA to androstenediol then to T (Grower 1995). Our study demonstrated that plasma levels of E2 in both sexes and E1 in males significantly decrease after S implants in lamprey. Similar to the current findings, acute stress and cortisol implants were shown to decrease plasma levels of E2 in teleosts (Pankhurst and Dedual 1994; F00 and Lam 1993A). E2 has been well studied in lamprey and established as a sex hormone in lamprey. Ho et al. (1987) provided evidence for an E2 receptor in the testis of the sea lamprey. Plasma levels of E2 were shown to increase during the reproductive stage in lamprey (Bolduc and Sower 1992) and increased with injections of lamprey GnRH I, and III (Deragon and Sower 1994; Gazourian et al. 1997). In addition, E2 was shown to stimulate vitellogenesis in female and male lampreys (Mewes et a1. 2002). The S implants increased gill Na+, K+-ATPase activity in adult lamprey. Our results show that S implants significantly increased ion regulating proteins in the gills of male and female lampreys. In juvenile sahnonids, cortisol and growth hormone have been shown to increase gill Na+, K+-ATPase activity (McCormick 1996). Cortisol 87 administration by itself has also been shown to increase gill Na+, K+-ATPase activity (Madsen 1990; McCormick et al. 1991; McCormick 1996; Seidelin et al. 1999; Quinn et al. 2003) and intestinal Na+, K+-ATPase activity (Veillette and Young 2005) in juvenile salmonids. Our results have demonstrated that S is regulated by the hypothalamus-pituitary axis in the ancient vertebrate. The mammalian CRH injections increased plasma levels of S in male and female sea lampreys. CRH elicits a pronounced increase in plasma S compared to the saline injected lampreys. In teleosts, the regulation of cortisol release is under the hypothalamus-pituitary-interrenal axis (Mommsen et al. 1999). CRH neuropeptide controls the release of ACTH from the anterior pituitary which circulates in the blood and binds to receptors in the interrenal cells, which in turn, stimulates release of cortisol (Wendelaar Bonga 1997). In goldfish, injections of CRH, urotensin I, and sauvagine elicited significant increases in plasma cortisol and stimulated release of ACTH from interrenals (Fryer et al. 1983). Pepels et al. (2004) showed significant increases of plasma levels of CRH and cortisol by 5 min in tilapia. The CRH peptide sequences in the vertebrates are highly conserved (Lovejoy and Balrnent 1999). Lovejoy and J ahan (2006) suggest the CRH system based on CRH homologues found in insects and chordates may have evolved in a metazoan ancestor. Pituitary extract injections increased plasma levels of S in a dose-response manner. The increases in plasma S from control levels were substantially elevated at 6 h for all treatment groups. All treatment groups recovered to control levels by 24 h. ACTH secreted from the pituitary is the principal hormone that controls cortisol secretion in teleosts (Wendelaar Bonga 1997). Pickering et al. (1987) have shown increased levels 88 of plasma ACTH in brown trout after acute stress. In lamprey, ACTH has been cloned and sequenced from the pituitary (Heinig et al. 1995; Takahashi et al. 1995A; Takahashi et al. 1995B). The lamprey ACTH is 60 amino acids long, roughly 20 amino acids longer than other vertebrate ACTHs (Takahashi et a1. 2006). However, plasma ACTH levels have not been shown to increase in lamprey and direct stimulation of 11- deoxycortisol by lamprey ACTH has not been shown. In teleosts, there is evidence of other pituitary hormones producing corticotrOpic activity (Wendelaar Bonga 1997; Mommen et al. 1999). Schreck et a1. (1989) demonstrated that gonadotropin hormone stimulated higher levels of cortisol release than ACTH in coho sahnon Oncorhynchus kisutch interrenals. Recently, Sower et al. (2006) cloned and sequenced a gonadotropin like protein from the pituitary of sea lamprey. Therefore the stimulatory effect from the pituitary injection might not be lamprey ACTH, but instead another factor or peptide hormone causing the increase in plasma S levels. In conclusion, this study has demonstrated that S functions as a glucocorticoid and has biological effects in the ancestral vertebrate, the lamprey. The results have shown that S, like cortisol in higher vertebrates, exhibits a classical stress steroid response in lamprey. In addition, the glucocorticoid hormone S reduced circulating levels of classic androgens and estrogens in the plasma of lamprey. The glucocorticoid hormone S, like cortisol in teleosts, up regulates ion regulating proteins in the gills of sea lamprey. Lastly, we provide evidence that the lamprey glucocorticoid hormone S is controlled by the hypothalamus-pituitary axis in these ancient vertebrates. 89 ACKNOWLEDGEMENTS We thank the staff of the US. Geological Survey, Hammond Bay Biological Station for supplying sea lampreys. I would like to thank the Bonneville Power Administration for providing funding and support for this research. I would also like to thank the Confederated Tribes of the Umatilla Indian Reservation for support. 90 REFERENCES Abraham, GE. 1974. Ovarian and adrenal contribution to peripheral androgens during the menstrual cycle. Journal of Clinical Endocrinology and Metabolism 39:340-346. Barton, BA. 2002. Stress in Fishes: A diversity of responses with particular reference to changes in circulating corticosteroids. Integrative and Comparative Biology 42:517- 525. Barton, B.A., and Iwama, GK. 1991. Physiological changes in fish from stress in aquaculture with emphasis on the response and effects of corticosteroids. Annual Review of Fish Diseases 1:3-26. Bolduc, T.G., and Sower, SA. 1992. Changes in brain gonadotropin-releasing hormone, plasma estradiol 17-0, and progesterone during the final reproductive cycle of the female sea lamprey, Petromyzon marinas. The Journal of Experimental Zoology 264255-63. Bridgham, J .T., Carroll, S.M., and Thornton, J .W. 2006. Evolution of hormone-receptor complexity by molecular exploitation. Science 312:97-101. Bryan, M.B., Scott, AP, and Li, W. 2007. The sea lamprey (Petromyzon marinus) has a receptor for androstenedione. Biology of Reproduction 77:688-696. Bury, NR, and Sturm, A. 2007. Evolution of the corticosteroid receptor signaling pathway in fish. General and Comparative Endocrinology 153247-56. Carragher, J .F ., Sumpter, J .P., Pottinger, T.G., and Pickering, AD. 1989. The deleterious effects of cortisol implantation on reproductive firnction in two species of trout, Salmo trutta L. and Salmo gairdneri Richardson. General and Comparative Endocrinology 76:310-321 . Carruth, L.L., Dores, R.M., Maldonado, T.A., Norris, D.O., Ruth, T., and Jones, RE. 2000. Elevation of plasma cortisol during the spawning migration of landlocked kokanee sahnon (Oncorhynchus nerka kennerlyi). Comparative Biochemistry and Physiology Part C 127:123-131. Chrousos, GP. 1998. Stressors, stress, and neuroendocrine integration of the adaptive response. Annals New York Academy of Sciences 851 :31 1-335. Deragon, KL, and Sower, SA. 1994. Effects of lamprey gonadotropin-releasing horrnone-III on steroidogenesis and sperrniation in male sea lampreys. General and Comparative Endocrinology 95:363-367. 91 F 00, J .T.W., and Lam, T.J. 1993. Retardation of ovarian growth and depression of serum steroid levels in the tilapia, Oreochromis mossambicus, by cortisol implantation. Aquaculture 115:133-143. Foo, J .T.W., and Lam, T.J. 1993. Serum cortisol response to handling stress and the effect of cortisol implantation on testosterone level in the tilapia, Oreochromis mossambz‘cus. Aquaculture 1 15: 145-1 58. Fryer, J ., Lederis, K., and Rivier, J. 1983. Urotensin I, a CRF-like neuropeptide, stimulates ACTH release from the teleost pituitary. Endocrinology 113:2308-2310. Gazourian, L., Deragon, K.L., Chase, C.F., Pati, D., Habibi, HR, and Sower, SA. 1997. Characteristics of GnRH binding in the gonads of effects of lamprey GnRH-I and —III on reproduction in the adult sea lamprey. General and Comparative Endocrinology 108:327-339. Gilrnour, KM. 2005. Mineralocorticoid receptors and hormones: Fishing for answers. Endocrinology 146:44-46. Grower, DB. 1995. Extraction, purification and estimation of the androgens and their derivatives. Pages 268-368 in H.L.J. Makin, D.B. Grower and D.N. Kirk, editors. Steroid Analysis. Chapman & Hall, London. Ho, S-M., Press, D., Liang, L-C., and Sower, S. 1987. Identification of an estrogen receptor in the testis of the sea lamprey, Petromyzon marinus. General and Comparative Endocrinology 67:119-125. Heinig, J .A., Keeley, F.W., Robson, P., Sower, S.A., and Youson, J .H. 1995. The appearance of pr00piomelanocortin early in vertebrate evolution: cloning and sequencing of POMC from a lamprey pituitary Cdna library. General and Comparative Endocrinology 99:137-144. Idler, DR, and Truscott, B. 1967. la-Hydroxycorticosterone: synthesis in vitro and properties of an interrenal steroid in the blood of cartilaginous fish (Genus Raja). Steroids 9:457-477. Idler, DR, and Truscott, B. 1972. Corticosteroids in fish. Pages 126-252 in DR. Idler, editor. Steroids in nonmammalian vertebrates. Academic Press, New York. Kalimi, M., Shafagoj, Y., Loria, R., Padgett, D., and Regelson, W. 1994. Anti- glucocorticoid effects of dehydroepiandrosterone (DHEA). Molecular and Cellular Biochemistry 131:99-104. Kumar, S., and Hedges, SB. 1998. A molecular timescale for vertebrate evolution. Nature 392:917—920. 92 Lance, V.A., and Elsey, RM. 1986. Stress-induced suppression of testosterone secretion in male alligators. The Journal of Experimental Zoology 239:241-246. Lovejoy, D.A., and Balrnent, R.J. 1999. Evolution and physiology of the corticotropin- releasing factor (CRF) family of neuropeptides in vertebrates. General and Comparative Endocrinology 115: 1-22. Lovejoy, D.A., and J ahan, S. 2006. Phylogeny of the corticotropin-releasing factor family of peptides in the metazoa. General and Comparative Endocrinology 146: 1-8. Madsen, SS. 1990. The role of cortisol and growth hormone in seawater adaptation and development of hypoosmoregulatory mechanisms in sea trout parr (Salmo trutta trutta). General and Comparative Endocrinology 79: 1-1 1. Majzoub, IA. 2006. Corticotropin-releasing hormone physiology. European Journal of Endocrinology 155:S71-S76. McCormick, SD. 1996. Effects of growth hormone and insulin-like growth factor I on salinity tolerance and gill Na+, K+, -ATPase in atlantic salmon (Salmo salar): Interaction with cortisol. General and Comparative Endocrinology 101:3-11. McCormick, S.D., Dickhoff, W.W., Duston, J ., Nishioka, R.S., and Bern, HA. 1991. Developmental differences in the responsiveness of gill Na+, K”, -ATPase to cortisol in salmonids. General and Comparative Endocrinology 84:308-317. Mewes, K.R., Latz, M., Golla, H., and Fischer, A. 2002. Vitellogenin from female and estradiol-stimulated male river lampreys (Lampetrafluviatilis L.). Journal of Experimental Zoology 292:52-72. Milston, R.H., Davis, M.W., Parker, S.J., Olla, B.L., Clements, S., and Schreck, CB. 2006. Characterization of the physiological stress response in lingcod. Transactions of the American Fisheries Society 135:1165-1174. Mommsen, T.P., Vijayan, M.M., and Moon, T.W. 1999. Cortisol in teleosts: dynamics, mechanisms of action, and metabolic regulation. Reviews in Fish Biology and Fisheries 9:211-268. Moore, FL, and Zoeller, RT. 1985. Stress-induced inhibition of reproduction: Evidence of suppressed secretion of LH-RH in an amphibian. General and Comparative Endocrinology 60:252-258. Nandi, J. and Bern, HA. 1960. Corticosteroid production by interrenal tissue of teleost fishes. Endocrinology 66:295-303. Nelson, R.J. 2000. An introduction to behavioral endocrinology. Sinauer Associates, Sunderland, Massachusetts. 93 Norman, A.W., and Litwack, G. 1997. Hormones. Academic Press, San Diego, CA. Nunez, S., and Trant, J .M. 1999. Regulation of interrenal gland steroidogenesis in the Atlantic stingray (Dasyatis sabina). Journal of Experimental Zoology 284:517-525. Pankhurst, N.W., and Dedual, M. 1994. Effects of capture and recovery on plasma levels of cortisol, lactate gonadal steroids in a natural population of rainbow trout. Journal ofFish Biology 45:1013-1025. Pepels, P.P.L.M., van Helvoort, H., Wendelaar Bonga, SE, and Balm, P.H.M. 2004. Corticotropin-releasing hormone in the teleost stress response: rapid appearance of the peptide in plasma of tilapia (Oreochromis mossambicus). Journal of Endocrinology 180:425-438. Pickering, A.D., Pottinger, T.G., Carragher, J ., and Sumpter, JP. 1987. The effects of acute and chronic stress on the levels of reproductive hormones in the plasma of mature male brown trout, Salmo trutta L. General and Comparative Endocrinology 68:249-259. Quinn, M.C.J., Veillette, P.A., and Young, G. 2003. Pseudobranch and gill Na+, K+, - ATPase activity in juvenile chinook sahnon, Oncorhynchus tshawytscha: developmental changes and effects of growth hormone, cortisol and seawater transfer. Comparative Biochemistry and Physiology Part A 135:249-262. Sapolsky, R.M., Romero, L.M., and Munck, A.U. 2000. How do glucocorticoids influence stress responses? Integrating permissive, suppressive, stimulatory, and preparative actions. Endocrine Reviews 21:55-89. Schreck, C.B., Bradford, C.S., Fitzpatrick, MS, and Patino, R. 1989. Regulation of the interrenal of fishes: non-classical control mechanisms. Fish Physiology and Biochemistry 7:259-265. Seidelin, M., Madsen, S.S., Byrialsen, A., and Kristiansen, K. 1999. Effects of insulin- like growth factor-1 and cortisol on Na+ , K+ , -ATPase expression in osmoregulatory tissues of brown trout (Salmo trutta). General and Comparative Endocrinology 113:331-342. Shu, D-G., Luo, H-L., Morris, S.C., Zhang, X-L., Hu, S-X., Chen, L., Han, J ., Zhu, M., Li, Y., and Chen, L-Z. 1999. Lower Cambrian vertebrates from south China. Nature 402:42-46. Sower, S.A., Moriyarna, S., Kasahara, M., Takahashi, A., Nozaki, M., Uchida, K., Dahlstrom, J .M., and Kawauchi, H. 2006. Identification of sea lamprey GTHfi-like cDNA and its evolutionary implications. General and Comparative Endocrinology 148:22-32. 94 Sturm, A., Bury, N., Dengreville, L., Fagart, J ., Flouriot, G., Rafestin—Oblin, M.B., and Prunet, P. 2005. ll-Deoxycorticosterone is a potent agonist of the rainbow trout (Oncorhynchus mykiss) mineralocorticoid receptor. Endocrinology 146:47-55. Takahashi, A., Amemiya, Y., Sarashi, M., Sower, S.A., and Kawauchi, H. 1995. Melanotropin and corticotropin are encoded on two distinct genes in the lamprey, the earliest evolved extant vertebrate. Biochemical and Biophysical Research Communications 2 1 3 2490-498. Takahashi, A., Amemiya, Y., Nozaki, M., Sower, S.A., Joss, J ., Gorbman, A., and Kawauchi, H. 1995. Isolation and characterization of melanotropins from lamprey pituitary glands. International Journal of Peptide & Protein Research 46:197-204. Takahashi, A., Yasuda, A., Sower, S.A., Kawauchi, H. 2006. Posttranslational processing of pr00piomelanocortin family molecules in sea lamprey based on mass spectrometric and chemical analysis. General and Comparative Endocrinology 148:79-84. Veillette, P.A., and Young, G. 2005. Tissue culture of sockeye salmon intestine: functional response of Na+, K“, -ATPase to cortisol. American Journal of Physiology- Regulatory, Integrative and Comparative Physiology 288:R1598-Rl605. Wendelaar Bonga, SE. 1997. The stress response in fish. Physiological Reviews 77:591- 625. 95 SUMMARY OF DISSERTATION At the beginning of this research it was unknown if the ancient vertebrate, the sea lamprey, had a stress steroid hormone. However, there were some indications that it might exist. Research in the 1990s showed that lamprey ACTH might be an active hormone in circulation by cloning and sequencing an ACTH homologue. Recent evidence confirmed that lamprey ACTH 1-60 is produced in the pituitary. However, evidence is lacking that it increases in circulation or that is stimulates the release of a stress steroid. Another piece of evidence supporting the notion that lamprey might have a stress steroid was cloning of a corticoid receptor homologue. Recent research has shown that lamprey possess a corticoid receptor homologue. Researcher’s using PCR techniques amplified DNA segments from sea lamprey, which were homologues to parts of the corticoid receptor genes in higher vertebrates. However, the receptor had not been proven to be functional or characterized in the lamprey. In chapter 1, the first prediction was that lampreys have a stress steroid circulating in the plasma. In the laboratory, various chromatography and mass spectrometry methods were used to address this hypothesis. A large a quantity of blood was extracted to increase the abundance of steroids for identifications. Radioimmunoassays were used to screen the plasma for cortisol or corticosterone like steroids. These two steroids were chosen due to their prevalence as stress steroids (glucocorticoids) in almost all vertebrates. Once immunoreactive peaks were identified, a large quantity of the steroid was purified for definitive identification. LH-20 chromatography and HPLC were used in conjunction with RIA to clean up the extract matrix before mass spectrometry. These 96 steps enabled the definitive identification of two possible glucocorticoids in the sea lamprey. In chapter 2, the second prediction was that one of the two definitively identified steroids from chapter 1 have a receptor. An important criterion to classify a hormone is that it must have a cognate receptor. Both radioligands were used for testing of tissue cytosol. ll-deoxycortisol, but not ll-deoxycorticosterone, bound to gill cytosol containing glucocorticoid receptor. Our study showed that the receptor in lamprey gill tissue had similar characteristics to glucocorticoid receptors in fish. The receptor was found by competitive assay to be highly specific for ll-deoxycortisol. However, 11- deoxycorticosterone was the only steroid that nearly displaced 50 percent of 11- deoxycortisol but only at 1000 nM. Finally, this study showed that ll-deoxycortisol- receptor complex bound to DNA-cellulose, an important step in characterization of a receptor. In chapter 3, the last prediction was that ll-deoxycortisol will have classic glucocorticoid stress response and show biological effects. This study demonstrated that adult lampreys exposed to acute stress responded with a classic glucocorticoid response. Steroid levels were elevated and remained elevated for hours, but returned to basal levels by 24 h. The ll-deoxycortisol implants decreased circulating androgens and estrogens in the sea lamprey, a typical glucocorticoid effect. In addition, the implants stimulated gill Na+, K+-ATPase activity which is mainly controlled by cortisol (glucocorticoid) in teleosts. Evidence was shown that the hypothalamus-pituitary axis controls 11- deoxycortisol just like cortisol in higher vertebrates. Mammalian CRH injections sharply 97 increase plasma ll-deoxycortisol. In addition, pituitary extract injections also increased plasma ll-deoxycortisol in a dose-response manner. The results from our research confirm that one of the earliest vertebrates, the sea lamprey, contains a stress steroid hormone (glucocorticoid). These findings are an important step in understanding the evolution of steroid biosynthesis in the vertebrate lineges. It is clear that ll-B hydroxylase is absent in the early vertebrates, which is an important enzyme to in the biosynthetic pathway to make cortisol and corticosterone which are glucocorticoids in higher vertebrates. The 11 position hydroxyl is converted to a ketone which inactivates the steroid. Thus cortisol is converted to cortisone and corticosterone is converted to ll-dehydrocorticosterone. An important question is; how do the ancient vertebrates control excess stress steroid? Now research can proceed to better understand the roles of the glucorticoid in the early vertebrates. In addition, these results may have an impact on the management activity to control or conserve lamprey. In the Great Lakes, management agencies have been trying to control sea lamprey for many years. On the Pacific coast, fisheries management agencies are concerned about negative impacts to Pacific lampreys. 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