Osmoregulation | With Focus on Fluid and Solute Dynamics in Tardigrada
PhD Dissertation KENNETH A. HALBERG
© Kenneth A. Halberg FACULTY OF SCIENCE UNIVERSITY OF COPENHAGEN
Osmoregulation│With Focus on Fluid and Solute Dynamics in Tardigrada
PhD Dissertation Kenneth A. Halberg
UNIVERSITAS Dissertation submitted Monday the 14th of May 2012. HAFNIENSIS Supervisor: Associate Professor Nadja Møbjerg, PhD. 2012 Dissertation presented at University of Copenhagen to be publicly examined (provided acceptance in its current form) in Auditorium 1, August Krogh Building, Universitetsparken 13, Thursday, June 28, 2012 at 14:00 for the degree of Doctor of Philosophy. The examination will be conducted in English.
Abstract Halberg, K. A. 2012. Osmoregulation │With Focus on Fluid and Solute Dynamics in Tardigrada.
Osmoregulation is the regulated control of water and solute composition in body fluid compartments. On one hand, the internal composition must be kept within optimal conditions for metabolic processes in the face of external perturbation. On the other hand, the nature of the living state demands a continuous traffic of compounds in and out of the organism. These demands appear to be in fundamental contradiction however cells and animals achieve so-called “steady-state” by means of an array of transport proteins, which provide a stringent control on the exchange of water and solutes across body surfaces. The distinct mechanisms of solute transport have been studied in most animal groups, but there are still large gaps in our understanding of how animals cope with osmotic stress. In the present thesis, osmoregulatory phenomena were studied in vertebrate and invertebrate organism alike, with the main focus being on fluid and solute dynamics in Tardigrada. For example, the inorganic ion composition of several species was investigated, which revealed that tardigrades contain roughly similar relative contributions of inorganic ions to total osmotic concentration, when compared to closely related animal groups. Moreover, it was inferred that cryptobiotic tardigrades (species able to enter a state of latent life) contain a large fraction of organic osmolytes. The mechanisms of organic anion transport in a marine species of tardigrade was investigated pharmacologically, and compared to that of insects. These data showed that organic anion transport is localized to the midgut epithelium and that the transport is both active and transporter mediated with a pharmacological profile similar to that of insects. Tardigrades survive in a variety of osmotic environments (semi-terrestrial, limnic and marine habitats), why the ability to volume and osmoregulate was examined. These studies demonstrated an ability to regulate total body volume during both hypo- and hyperosmotic conditions, and that the ability to hyper-regulate could be a general theme among members of eutardigrades. Thus, the work presented herein, have contributed to establishing tardigrades as an important experimental group in which central physiological questions may be answered, including aspects of osmotic and ionic regulation.
Keywords: osmoregulation, volume regulation, organic anion transport, hyper-regulate, inorganic ions, organic osmolytes, tardigrade, insect,
Kenneth A. Halberg, The August Krogh Centre, Department of Biology, Universitetsparken 13, DK-2100 Copenhagen Ø, Denmark
© Kenneth A. Halberg 2012
“Beautiful is what we see,
More beautiful is what we perceive,
Most beautiful is what we do not understand”
- Niels Stensen List of Papers
This thesis is based on the following papers and manuscripts, which are referred to in the text by their Roman numerals.
I. Halberg, K. A., Larsen, K. W., Jørgensen, A., Ramløv, H. & Møbjerg, N. Cryptobiotic tardigrades contain large fraction of unidentified organic solutes: A comparative study on inorganic ion composition in Tardigrada. II. Halberg, K. A., & Møbjerg, N. (2012). First evidence of epithelial transport in tardigrades: A comparative investigation of organic anion transport. Journal of Experimental Biology, 215: 497-507. III. Møbjerg, N. M., Halberg, K. A., Jørgensen, A. Persson., D., Bjørn M, Ramløv H & Kristensen R. M. (2011). Survival in extreme environments – on current knowledge of adaptations in tardigrades. Acta Physiologica, 202: 409-420. IV. Haugen, B.M., Halberg, K.A., Jespersen, Å., Prehn, L.R. & Møbjerg, N. (2010). Functional characterization of the vertebrate primary ureter: Structure and ion transport mechanisms of the pronephric duct of axolotl larvae (Amphibia). BMC developmental Biology, 10: 56. V. Halberg, K. A., Persson, D., Ramløv, H., Westh, P., Kristensen, R. M. & Møbjerg, N. (2009). Cyclomorphosis in Tardigrada: Adaption to environmental constraints. Journal of Experimental Biology, 212: 2803-2811.
Additionally, the following papers and manuscripts were prepared during the course of my PhD studies, but are not included in the thesis:
VI. Halberg K. A., Jørgensen, A. and Møbjerg, N. (in prep.). Surviving without water: Tun formation in tardigrades is an active process mediated by the musculature VII. Halberg K. A., Persson, D., Jørgensen, A. Kristensen, R. M. and Møbjerg, N. (submitted). Population dynamics of a marine tardigrade: Temperature limits geographic distribution of Halobiotus crispae. Marine Biological Research VIII. Persson, D., Halberg K. A., Jørgensen A., Møbjerg N. & Kristensen R. M. (in review). Neuroanatomy of Halobiotus crispae (Eutardigrada: Hypsibiidae): Tardigrade brain structure suggests inclusion into Panarthropoda. Journal of Morphology. IX. Persson, D., Halberg K. A., Jørgensen A., Ricci C., Møbjerg N. & Kristensen R. M. (2010). Extreme stress tolerance in tardigrades: Surviving space conditions in low earth orbit. Journal of Zoological Systematics and Evolutionary Research, 49: 90-97. X. Halberg, K. A., Persson D., Møbjerg N., Wanninger A. & Kristensen R. M. (2009). Myoanatomy of the Marine Tardigrade Halobiotus crispae (Eutardigrada: Hypsibiidae). Journal of Morphology, 270: 996-1013.
Lastly, following paper provides important background knowledge for the work presented herein:
XI. Møbjerg, N., A. Jørgensen, J. Eibye-Jacobsen, K. A. Halberg, D. Persson & R. M. Kristensen (2007). New Records on cyclomorphosis in the marine eutardigrade Halobiotus crispae (Eutardigrada: Hypsibiidae). Journal of Limnology, 66 (suppl. 1): 132-140.
Reprint and publication is made with permission from the respective copyright holders.
Paper II, V © The Company of Biologists. Paper IV, is copyright of the authors. Paper III © Wiley-Blackwell
Statement of authorship
Paper I: KAH was deeply involved in study design. KAH participated in extracting animals and ion chromatography. KAH performed nanoliter osmometry. KAH performed the data analysis, prepared the figures, participated in discussions and interpretation of the data, and drafted the manuscript.
Paper II: KAH performed the major part of the experimental work and data analysis. He participated in planning of experiments, data interpretation, prepared the figures and drafted the manuscript.
Paper III: KAH performed cell counts and provided images of tardigrades. He helped draft parts of the manuscript.
Paper IV: KAH participated in immunostaining experiments, performed CLSM and prepared the 3D images. KAH participated in discussions and interpretation of the data.
Paper V: KAH participated in planning of experiments, sampling, staging, scanning electron microscopy, DSC experiments, experiments on cold hardiness and osmotic stress tolerance, volume measurements, hemolymph sample collections, and nanoliter osmometry. He furthermore participated in discussions and interpretation of data, prepared the figures and drafted the manuscript.
Front cover: Scanning elecron micrographs of the tardigrades Rictersius coronifer (top left), Halobiotus crispae (middle right), and Echiniscus testudo (middle bottom). Contents
Preface...... 9 Introduction ...... 11 Maintaining a stable internal environment ...... 11 Osmoregulators and osmoconformers ...... 12 Osmoregulatory organs...... 12 Filtration-Reabsorption systems...... 13 Secretion-Reabsorption systems...... 14 Phylum Tardigrada...... 17 General morphology ...... 18 Classification ...... 19 Ecology...... 21 Fluid and solute dynamics – an overview ...... 23 Inorganic ion composition ...... 23 Organic anion transport ...... 25 Volume and osmoregulation...... 26 Conclusions and future perspectives ...... 27 Dansk sammenfatning ...... 29 Acknowledgements ...... 30 References ...... 32
8 Preface
The primary aim of this thesis was to address several aspects of the fluid and solute dynamics in tardigrades, and hereby provide new insight into the general stress biology of these enigmatic creatures. This was done by adopting an integrative approach, i.e. applying advanced methods in biology, analytic biochemistry and physical chemistry, which offered functional data from different disciplines to be obtained. The experimental work was carried out mainly at The August Krogh Centre, University of Copenhagen; however, additional experimental work was performed at the Danish Natural History Museum, University of Copenhagen and at the Department of Nature, Systems and Models, Roskilde University. Overall this thesis has contributed to converting tardigrades, from an almost exclusive taxonomic phenomenon into an established and important experimental group, in which central physiological questions can be investigated. This PhD-thesis comprises a short introduction to osmotic and ionic regulation in Metazoa, accompanied by a brief review on the general morphology, classification and ecology of tardigrades. Moreover, an overview of the results presented as well as conclusions and future perspectives are presented. Five papers and manuscripts form the basis of this thesis, of which four are published in peer review journals (Papers II, III, IV and V), and one is prepared for submission (Paper I). I am the first author of three (Paper I, II and V) and second author on two (Papers III and IV) of these papers. Five additional papers and manuscripts were prepared during the course of my PhD studies, but are not included in the thesis. This work was funded by the 2008 Faculty of Science, University of Copenhagen Freja-Programme.
Copenhagen, the 14th of May 2012
Kenneth A. Halberg
9 10 Introduction
Maintaining a stable internal environment “Life is as a thing of macromolecular cohesion in salty water” (Gilles & Delpire, 1997). Albeit a crude statement, it frames the fact that the ability to control salt and water balance is a fundamental prerequisite for both cellular and animal life. Indeed, the internal environment must usually be kept within relatively narrow limits, as substantial deviations in cell composition are incompatible with the optimal function of macromolecules (lipids, proteins, RNA), and may ultimately modify the rate and extent of cellular reactions (Zhao, 2005). The overall mechanism by which animals conserve a proper osmotic balance between cells, extracellular fluid and the environment is termed osmoregulation. The basis for osmoregulation lies in the strict control of the ionic composition and the osmotic pressure of the intra- and extracellular compartments through the regulated accumulation and loss of inorganic ions and organic compounds (Dawson & Liu, 2009). This regulation is achieved through the coordinated activity of an array of transporter proteins (both energy-consuming and passive), which collectively maintain the steady-state condition of cells and animals (Essig, 1968). During steady-state conditions, compositions of the intra- and extracellular compartments are maintained in a non-equilibrium state (Dawson & Liu, 2009). This uneven distribution of solutes is important for keeping an optimal milieu for metabolic processes (Zhao, 2005). Accordingly, the extracellular fraction of the body fluids of animals are typically high in Na+ and Cl- , and relatively low in the other major ions (e.g. K+, Ca2+ and Mg2+), while the + + 3- intracellular environment of most organisms is low in Na but high in K , PO4 and proteins (e.g. Dawson & Lui, 2009; Paper I). As such, the plasma membrane of cells must maintain ionic, but not osmotic, differences, while specialized excretory organs – e.g. antennal glands of crustaceans, Malpighian tubules of insects and tardigrades, rectal glands of sharks and rays, gills and intestine of teleost fishes, salt glands of birds and reptiles, the kidneys of vertebrates etc. – often maintain both ionic and osmotic differences between animals and their environments (Riegel, 1970; Peaker, 1971; Paper IV, Beyenbach & Piermarini, 2011; Reilly et al., 2011; Whittamore, 2012). In general, mechanisms that allowed organisms to respond and adapt to an osmotic challenge over the course of
11 evolution, has been fundamental to the invasion of new osmotic hostile habitats, and such ecological divergence in turn is an important mechanism for the speciation process (Schluter, 2009). Accordingly, if the ability to osmoregulate had not evolved, life on the planet would look quiet different from how we know it.
Osmoregulators and osmoconformers Generally, animals are divided into two broad categories in terms of their responses to osmotic stress: osmoregulators, which maintain an internal osmolarity different from that of the external environment, and osmoconformers, which conform to the external medium in which they are immersed (Fig. 1). Most vertebrates are strict osmoregulators (e.g. Paper IV), as they maintain ionic and osmotic balance within narrow limits; although hagfish, a basal group of vertebrates, are a notable exception (Sardella et al., 2009). Conversely, marine invertebrates are typically categorized as osmoconformers, as many of them appear to be in osmotic balance with sea water over a range of salinities (Fig. 1). However, there are numerous obvious exceptions including the marine tardigrade Halobiotus crispae as well as several members of Crustacea (e.g. Sarver et al., 1994; Normant et al., 2005; Paper V). In fact, the terms ‘strict osmoregulator’ and ‘strict osmoconformer’ must be used with caution, as typical osmoregulators are forced to conform during the most extreme conditions (e.g. Dowd et al., 2010), whereas animals otherwise described as osmoconformers actually maintain slight differences between the internal and external environment (e.g. van Weel, 1957). Although achieved through different mechanisms, both osmoregulating and osmoconforming animals may tolerate wide ranges of external salinities, thus termed euryhaline species, while animals intolerant of large changes are called stenohaline species.
Osmoregulatory organs Osmoregulatory organs are specialized organs involved in maintaining ionic and osmotic homeostasis in the face of osmotic perturbation, as well as in excreting endobiotic and exobiotic waste products (Dawson & Lui, 2009; Papers II, IV). The specific organs mediating these processes may vary between different groups of animals (see above); however, the molecular basis and specific mechanism of solute and water transport often show a highly convergent/homologous pattern across different types of epithelia (e.g. Paper II). In general, two types of systems
12 Fig. 1 Examples of osmotic performance of representative species from various groups exposed to sea/brackish water, expressed as the relation between internal (extracellular) and external (habitat) osmolality. These data show that osmoconformaty (∆osm=0) is present in invertebrate and vertebrate species alike, albeit strong hypo-regulators and the ability to produce a hyperosmotic urine appears restricted to vertebrates. It should be emphasized that the selected species not necessarily represent the osmotic performance of the entire group, as large difference may exist between even closely related species. For original data see: Robertson, 1949a; van Weel, 1957e; Dice, 1968d; Liggins and Grigg, 1985j; Diehl, 1986b; Normant et al., 2005f; Sardella et al., 2009g; Paper Vc ;Reilly et al., 2011h; Whittamore, 2012i).
have evolved by which the initial process of urine formation takes place i) the filtration-reabsorption type and ii) the secretion-reabsorption type.
Filtration-Reabsorption systems The kidneys of vertebrates (fish, amphibians, reptiles, birds and mammals), and the functional analogs of crusteans and molluscs, maintain extracellular fluid homeostasis by producing urine through the filtration of plasma (ultrafiltration), which is subsequently modified by selective reabsorption and secretion of ions, organic molecules and water (Anderson, 1960; Schmidt-Nielsen, 1963; Riegel,
13 1970; Møbjerg et al., 2004; Paper IV; Whittamore et al., 2012). In vertebrates, three temporally and spatially different kidney generations, the pronephroi, mesonephroi and metanephroi, successively maintain fluid and electrolyte homeostasis during morphogenesis, with the pronephroi constituting the functional kidneys of fish and amphibian larvae (Paper IV). The functional unit of the vertebrate kidney is the nephron, which is composed of a filtration unit and a renal tubule (Anderson, 1960; Møbjerg et al., 2004; Paper IV). The filtration process that takes place in the filtration unit (the glomerulus and Bowman’s capsule) is ‘passive’ i.e. entirely driven by the hydrostatic pressure generated by the heart, whereas the reabsorption and secretion processes take place over specialized epithelia of the renal tubule (Schmidt-Nielsen, 1963). The primary membrane transporter for energizing vertebrate tissue is the Na/K-ATPase (e.g. Paper IV). Accordingly, vertebrate kidneys may produce both dilute, iso-osmotic and concentrated urine relative to the body fluids (Paper IV; Whittamore et al., 2012), which has been a dominant factor in allowing vertebrates to penetrate into all types of habitats on Earth. Filtration-reabsorption systems are capable of processing large volumes of fluids, but are energetically costly, as any substance (e.g. glucose) that has been filtered remains in the urine unless subsequently reabsorbed (Schmidt-Nielsen, 1963). The advantage of such a system; however, is that new potentially toxic compounds are eliminated without the need for developing distinct secretory pathways for each new compound, which may be necessary for the secretion-reabsorption type system (Paper II).
Secretion-Reabsorption systems The Malpighian tubules of insects, and possibly tardigrades (Møbjerg & Dahl, 1996; Papers II, III, V), are the functional analogs of the vertebrate kidney, but constitute a secretion-reabsorption system that produces urine in a fundamentally different way than the filtration-reabsorption-systems (Beyenbach & Piermarini, 2011). In the absence of blood vessels (i.e. a closed circulatory system), the hemolymph of insects is circulated at pressures insufficient for filtration, and the Malpighian tubules thus form the (primary) urine entirely by secretion (Beyenbach & Piermarini, 2011). The formation of the primary urine is generally initiated in the distal segments (blind-ended tip) of the Malpighian tubule, and is essentially iso-osmotic (consisting mainly of KCl and NaCl) to the hemolymph (Williams & Beyenbach, 1983). The subsequent reabsorption of water, ions and metabolites in proportions that maintain extracellular homeostasis (a process analogous to that of vertebrates) takes place in downstream structures i.e. proximal tubule, hindgut and rectum (O’Donnell & Maddrell, 1995; Coast, 2007). The final urine composition is
14 adjusted in the rectum (Coast, 2007) and may be either strongly hypo- or hyperosmotic depending on the species and its physiological status (Maddrell & Phillips, 1975; Reynolds & Bellward, 1989). In contrast to vertebrate epithelia, the V-type H+-ATPase is considered ubiquitous in energizing insect epithelia (Beyenbach & Piermarini, 2011); although the Na/K-ATPase is still expressed and functionally relevant for tubular function (Torrie et al., 2004; Paper II). In fact, energized by the H+-ATPase, some of the highest fluid secretion rates per unit area membrane from any tissue have been reported from hematophagous insects (e.g. Aedes aegypti, Rhodnius prolixus) after a blood meal (Williams & Beyenbach, 1983; Maddrell & Phillips, 1975). In addition to playing a key role in osmoregulation, new properties of the Malpighian tubules of insects have emerged in recent years, which suggest that Malpighian tubules are involved in such diverse functions as renal detoxification, metabolism of toxins and immune system responses (Dow & Davies, 2006; Paper II). As holds for insects, ultrastructural studies on the Malpighian tubules of tardigrades indicate that they function as secretion-reabsorption systems involved in fluid and solute transport (Weglarska, 1987; Møbjerg and Dahl, 1996; Peltzer et al., 2007). They are positioned at the transition zone between the midgut and rectum of eutardigrades (Fig. 2), and the positional conformity between insects and eutardigrades has been used as a strong argument for their homology (Greven, 1982; Møbjerg and Dahl, 1996). However, at present no functional data exist relating the Malpighian tubules of tardigrades to an osmoregulatory role. Accordingly, functional studies on the fluid and solute dynamics of tardigrades are greatly needed (Papers I, II, III, V), and due to the close affinity to the euarthropod complex (Aguinaldo et al., 1997), would be highly useful in understanding and reconstructing the evolution of osmoregulation in Insects and other arthropods.
15 Fig. 2 Structure and organization of the Malpighian tubules of the marine eutardigrade Halobiotus crispae. dm, dorsal Malpighian tubule; dp, distal part; is, initial segment; mg, midgut; mv, microvilli,; nu, nucleus; pp, proximal part; re, rectum; From: Møbjerg & Dahl, 1996.
16 Phylum Tardigrada
Tardigrades, also known as water bears, are among the smallest multi-cellular animals on the planet (0.1-1.2 mm). They were discovered in 1773 by the German pastor J. A. E. Goeze, who described them as “kleiner Wasserbär”, or little water bear, due to their strong resemblance to a tiny bear (Ramazzotti & Maucci 1982). Not long after the current name “Tardigrada” was given by the Italian naturalist Spallanzani in 1776 (Lat. tardus – slow, grado – walker). In response to unfavorable environmental conditions, many species of tardigrades have the ability to enter the ametabolic state of suspended animation, also known as cryptobiosis, in which the organism is neither dead nor alive (Møbjerg et al., 2011; Fig. 3). The animal can remain in this state for as much as 20 years (Jørgensen et al., 2007), yet once external conditions again become favorable, the tardigrade resumes activity unaffected. This incredible ability is shared with selected species of nematodes, rotifers and arthropods (Glasheen & Hand, 1988; Crowe & Maddin, 1974; Ricci et al., 2003). In 1962, Tardigrada was recognized as a phylum by Ramazzotti in Il Phylum Tardigrada. Presently, there are more than 1000 described species (Guidetti & Bertolani 2005; Degma & Guidetti, 2007; Degma et al., 2012); however, it has been estimated that several thousand species remain undescribed (Paper III). Tardigrada is included in the invertebrate superclade Ecdysozoa (Aguinaldo et al. 1997); however, their precise phylogenetic position is still being debated. Both molecular and morphological investigations produce conflicting conclusions, and it is currently unclear whether the group is more closely related to the nematodes and nematomorphs or to arthropods and onychophorans (Aguinaldo et al. 1997; Dunn et al. 2008; Zantke et al., 2008; Edgecombe 2010; Rota-Stabelli et al., 2010; Cambell et al., 2011). Regardless, this group is closely related to one of the two most species-rich and economically important groups Nematoda or Arthropoda, and thus maintains a central position in relation to the two major invertebrate model organisms, i.e. Caenorhabditis elegans Maupas, 1900 and Drosophila (Sophophora) melanogaster Meigen, 1830 (Gabriel et al. 2007; Goldstein and Blaxter 2002).
17 Fig. 3 Scanning electron micrographs showing the external morphology of Richtersius coronifer (Eutardigrada) A. lateral view of the active, hydrated state B. Dorsal view of the dehydrated, cryptobiotic state C. Ventral view of the dehydrated, cryptobiotic state. The pictures illustrate the morphological changes associated with entry into an ametabolic state (i.e. cryptobiosis), which include the retraction of head and limbs into the body cavity, and the formation of a compact shape – the tun. From: Paper VI.
General morphology Tardigrades are bilaterally symmetric micrometazoans with a body divided into five separate body segments, i.e. a cephalic segment, containing a mouth, eyespots
18 and sensory organs (papillae cephalica or cirri and clavae), and four trunk segments (Nelson, 2002; Fig. 3A). The first three trunk segments each bear a pair of lateroventrally directed legs, while the terminal trunk segment bears a pair of posterioventrally directed legs (Figs. 3, 4). The legs typically terminate in 4 to 13 claws or suction discs (Nelson, 2002). Tardigrades are ventrally flattened with a convex dorsal side, and are covered by a segmented cutinous cuticle, which is periodically shed during molting – formation of the new cuticle is maintained by a single layer of epidermal cells (Nelson, 2002). The digestive system consists of a foregut, midgut and a hindgut with a pair of stylets and stylet glands flanking the buccal tube. Three glands (the Malpighian tubules) are positioned at the transition zone between the midgut and hindgut in eutardigrades (Weglarska, 1987; Møbjerg and Dahl, 1996; Peltzer et al., 2007). Tardigrades posses a hemocoel-type of fluid- filled body cavity, i.e. an open circulatory system as seen in arthropods and nematodes, which likely functions in circulation and respiration. The somatic musculature is composed of structurally independent muscle fibers, which can be divided into a dorsal, ventral, dorsoventral, and a lateral musculature in addition to a distinct leg musculature (Schmidt-Rhaesa & Kulessa, 2007; Fig. 4). Moreover, the buccopharyngeal muscles, intestinal muscles and cloacal muscles comprise the animal’s visceral musculature. Whereas cross striation of the somatic musculature is especially pronounced in Arthrotardigrada, the somatic muscles of Eutardigrada are described as an intermediate between smooth and obliquely striated (Walz, 1974). The nervous system of tardigrades consists of an (at least) three lobed brain (Fig. 5) and a ventral nerve cord with four fused paired ganglia that shows a clear segmental organization.
Classification Originally based on morphological characters, tardigrades are divided into two main evolutionary lines, represented by the extant lineages Eutardigrada and Heterotardigrada. The validity of a third class, Mesotardigrada, is currently considered dubious (Ramazzotti and Maucci, 1983). Heterotardigrada consists of the orders Arthrotardigrada and Echiniscoidea with arthrotardigrades possessing the most plesiomorphic characters. Arthrotardigrada consists exclusively of marine species (Renaud-Mornant 1982; Jørgensen et al. 2010), and are morphologically the most diverse group. They are present in all oceans from intertidal zones to abyssal depths, and inhabit various types of sediment. In contrast, the Echiniscoidea comprises both limno-terrestrial, limnic as well as marine species with the majority of the described species belonging to the family Echiniscidae. Taxonomically, the main characters
19 Fig. 4 Tardigrade musculature as revealed by fluorescently coupled phalloidin in combination with confocal laser scanning microscopy three-dimensional reconstruction A. Lateral view of Halobiotus crispae (Eutardigrada), Paper VIII B. Ventral view of Echiniscoides sigismundi (Heterotardigrada), unpublished data. separating the two groups from Eutardigrada include a separate gonopore, a closed three-lobed anus as well as well-developed cephalic-, trunk-, and leg appendages (Guidetti and Bertolani, 2005). The eutardigrades are divided into the two orders; Apochela and Parachela. Both orders contain mainly limno-terrestrial species, albeit with a few exceptions –
20 Fig. 5 Conceptual drawing based on immunofluorescent and ultrastructural data, showing an interpretation of the brain structure of Halobiotus crispae. A. Lateral view B. Frontal view. clg, claw gland; co, connective; dc, dorsal commissure; ey, eye; g0, sub-pharyngeal ganglion; gI, first ventral trunk ganglion; ic, inner connective; il, inner lobe; lgg, leg ganglion; mg, median ganglion; mo, mouth opening; oc, outer connective; ol, outer lobe; pc, papilla cephalica; pb, pharyngeal bulb; st, stylet; t, temporalia; vll, ventrolateral lobe. From: Paper VIII.
most notably the marine genus Halobiotus (see Paper III). In general, eutardigrades are cylindrically shaped with a more or less distinct segmentation, and exhibit a relatively uniform morphology (Fig. 3A). The key characters of eutardigrades include a cloaca (combined gonopore and anus), the presence of Malpighian tubules and a strong reduction of cephalic sensory structures (Guidetti and Bertolani, 2005). Structures such as the bucco-pharyngeal apparatus and claw shape are important taxonomic characters within Eutardigrada.
Ecology Tardigrades occupy a range of moisture regimes and often constitute a major component of meiofaunal communities in terrestrial, limnic and marine ecosystems throughout the globe. However, they are distinctly aquatic organisms, requiring a film of water to be active. Tardigrades are predominantly egg-laying, with both sexual and parthenogenetic modes of reproduction described (Bertolani, 2001). Molting occurs continuously throughout their lifecycle, which may be between 3-30 months (Nelson, 2002). Populations of tardigrades have been studied in a variety of habitats; including mosses, lichens, leaf litter and soil, and
21 Fig. 6 Population dynamics of the marine tardigrade Halobiotus crispae showing a unimodal pattern of maximal frequency. Graphic representation of sampling data (2006-2012) comparing the temporal pattern in abundance of H. crispae to abiotic parameters (temperature, (─ ─); salinity, (- - -); pH, (- ─ -), and the seasonal appearance of the different cyclomorphic stages (shown on top), from the locality of Vellerup Vig, Isefjord, Denmark. Light grey area is the period in which exuvia containing eggs were found, and thus indicates the period of sexual reproduction. From: Paper VII. the life history and population dynamics have received some attention (Martinez, 1975; Morgan 1977; Guidetti et al. 1999; Uhía and Briones 2002; Jönson 2003; Suzuki 2003). Tardigrade population dynamics may show both unimodal and bimodal patterns of annual variation (Martinez, 1975; Morgan, 1977; Fig. 6), albeit the specific pattern appears to be both species and habitat specific. Factors such as temperature, moisture and food availability have been suggested to be correlated with population density (Hallas & Yeates, 1972; Morgan, 1977). However, other factors including competition, predation and parasitism may play a role in controlling population density and diversity (Nelson, 2002). Tardigrades possess an amazing reproductive capacity, as indicated by the large changes in animal density on short temporal scales (Morgan, 1977).
22 Fluid and solute dynamics – an overview
Inorganic ion composition Knowledge of the composition as well as concentrations of dissolved particles in internal fluids of an organism, and how these change during various exposures, is fundamental to the understanding of its basic physiology. However, practically nothing is known about these aspects in tardigrades, which has been a major obstacle to the study of the fluid and solute dynamics in these animals. In Paper I, the inorganic ion content of five different species (Echiniscus testudo, Milnesium tardigradum, Richtersius coronifer, Macrobiotus cf. hufelandi and Halobiotus crispae) covering both a large phylogenetic and habitat spectrum was analyzed (Fig. 7A). These data demonstrated that Na+ and Cl- are the principle inorganic + + 2+ ions in tardigrade fluids, albeit substantial concentrations of K , NH4 , Ca , 2+ - 2- 3- Mg , F , SO4 and PO4 were also detected. Moreover, tardigrades appear to contain roughly similar relative contributions of the respective inorganic ions to total osmotic concentration, when compared to selected species of arthropods, nematodes and onychophorans (Hobson et al., 1952; Sutcliffe, 1962; Campiglia, 1975; Wilder et al., 1998; Normant et al., 2005), albeit a large relative contribution of calcium appears characteristic of tardigrade fluids. Inorganic ions destabilize macromolecules and affect the rate and extent of metabolic reactions at high concentrations, which invariably leads to impairment of cellular function (Zhao, 2005; Yancey, 2005). However, apparently R. coronifer does not exclude inorganic ions during dehydration (Fig. 7B), which suggests a concomitant accumulation of organic solutes. Moreover, as evidenced by the differences between the calculated osmotic concentrations of the known ions and the measured total osmolarity in the different species (Fig. 7A), it was inferred that cryptobiotic tardigrades (in steady-state) contain a large fraction of unidentified organic osmolytes. Organic osmolytes can be divided into a few major categories (sugars, polyols, amino acids and various derivatives), and several of these groups possess known protective functions in relation to osmotic stress (Hincha and Hagemann, 2004; Yancey, 2005). Accordingly, the future detection and analysis of such compounds are likely to provide new insight into the biochemistry and physiology of superior tardigrade adaptations.
23 Fig. 7 Ionic contributions to total osmotic concentration A. Concentrations (mM) of the respective cations and anions measured in each investigated species, as well as the corresponding total osmotic concentration (mOsm/kg). The blank area represents the osmotic deficit (OD). B. Concentrations (mg/l) of the respective cations and anions measured in hydrated, active specimens compared to dehydrated cryptobiotic animals of Richtersius coronifer. Data are expressed as mean ± s.d. From: Paper I.
24 Organic anion transport The ability to excrete endogenous waste products as well as environ- mental toxins is an essential step to avoid these compounds reach toxic levels and to keep metabolic reactions within optimal conditions. One of the better known systems involved in such an excretion is the organic anion transport system, the function of which has been studied in several vertebrate (fish, amphibians, reptiles, birds and mammals) and invertebrate (nematodes and insects) model organisms (George et al., 1999; Dantzler, 2002; Dow and Davies, 2006). In Paper II, these data were expanded as the sites, characteristics Fig. 8 Tentative cellular model for the and pharmacological profile of the transepithelial transport of organic anions in transepithelial transport of chloro- tardigrades. From: Paper II. phenol red (CPR), a prototypical substrate of the classic organic anion secretion pathway, was investigated in the tardigrade Halobiotus crispae Kristensen, 1982 and compared to corresponding data from the desert locust Schistocerca gregaria Forskål, 1775. This was done by introducing a new method for quantifying non-fluorescent dyes. Our study revealed i) that tardigrades posses an organic anion transport system, ii) that it was localized to the midgut epithelium, and iii) that organic anion secretion was both active and transporter mediated, with possible members of the SLC21/SLCO transport families mediating the basolateral entry step in tardigrade midgut cells. Transport by insect Malpighian tubules showed a similar pharmacological profile, but higher concentrations of CPR were achieved. Based on the observed transport characteristics in the presence and absence of transport inhibitors, a tentative cellular model for the transepithelial transport of CPR in tardigrades was suggested (Fig. 8). Specifically, a large lumen positive potential generated by the H+-ATPase could provide the driving force for accumulation of anions in the lumen, although the exact coupling between electrochemical gradients generated by the pumps and transport of ions is unknown. This study was the first to provide evidence for epithelial transport in tardigrades.
25 Volume and osmoregulation Tardigrades survive in a variety of osmotic environments and must protect the internal tissues from the vagaries and extremes of the external environment. The secondary marine species Halobiotus crispae colonizes habitats characterized by especially large fluctuations in external salinity, why the ability to respond to an osmotic challenge was investigated in this species (Paper V). Animals were exposed to both hypo- and hyperosmotic media and the subsequent changes in total body volume and internal osmotic pressure were recorded. These data revealed that H. crispae is able to regulate total body volume back to control values when immersed in hypotonic solutions, yet was unable to do so in concentrated media. Instead a new steady-state was achieved significantly below control conditions. Animal activity was only markedly affected in very dilute media, suggesting a possible effect on neuro-muscular function at low salt concentrations. Conversely, when analyzing the concomitant changes in hemolymph concentrations, it appeared that H. crispae is a euryhaline osmoconformer, in which the hemolymph osmotic pressure is largely governed by the external environment. However, expressing the hemolymph osmolality measured during exposure to dilute as well as concentrated media as a function of external salinity revealed that H. crispae is in fact a strong hyper-regulator (Fig. 9A). Expanding these studies to include the limno-terrestrial species Richtersius coronifer Richters, 1903 (Paper III) showed that this is could be a general feature of all eutardigrades (Fig. 9B), which was further supported by data presented in Paper I. The ability to hyper-regulate indicates the excretion of dilute urine. The three glands positioned at the transition zone between the midgut and rectum of eutardigrades, are generally considered to have an excretory function. This assumption is based on the probable homology of the Malpighian tubules of eutardigrades and insects (Greven, 1982; Møbjerg and Dahl, 1996), and on several ultrastructural studies that shows that the epithelium is likely involved in fluid and solute transport (Weglarska, 1987; Møbjerg and Dahl, 1996; Peltzer et al., 2007). However, data in support of an osmoregulatory function of both the rectum (Dewel and Dewel, 1979) and midgut (Paper II) also exists, which emphasizes the need for functional studies on these organs at both the molecular and cellular level.
26 Fig. 9 Osmotic performance of A. Halobiotus crispae and B. Richtersius coronifer during exposure to media of varying osmotic strength. From: Paper III.
27 Conclusions and future perspectives
This dissertation has provided new insight into the fluid and solute dynamics of metazoans, particularly relating to one of the most enigmatic groups on the planet – the tardigrades. Using a multi-disciplinary approach, crucial information was provided on both organs and systems of several species, representing vertebrates, arthropods and tardigrades, and general patterns in especially tardigrade physiology have emerged (e.g. Paper III). By comparing our data on tardigrades to several evolutionary related groups, including nematodes, onychophorans and arthropods, basic physiological principles have been discovered (e.g. Paper II), which emphasizes the importance of comparative physiology. In this respect, future work on tardigrade physiology could encompass an extension of the work presented herein. Additional species from different habitats and evolutionary lineages should be investigated, in order to further explore the diversity as well as common trends in tardigrade biology. In particular, studies on marine cryptobionts (e.g. Echiniscoides sigismundi) and additional non- cryptobiotic species would help clarify whether the osmotic deficits observed in cryptobiotic animals (Fig. 5; Paper I) in fact are related to cryptobiotic ability or alternatively to habitat preference. Regardless, large scale analyses and characterization of the organic solutes of cryptobiotic tardigrades should be performed, which surely would provide an enhanced resolution of several aspects relating to tardigrade stress responses. Other studies could include a characterization of the volume and osmoregulatory capacity of heterotardigrade species. Our results on eutardigrades show a capacity to hyper-regulate over a broad range of external salinities (Fig. 7); however, do heterotardigrades without Malpighian tubules posses the same ability? True limnic species (e.g. Bertolanius nebulosus) should also be investigated. In addition to the suggested whole animal experiments, studies on the molecular and cellular level are needed to fully understand how fluid and electrolyte homeostasis is achieved in these animals. For example, electrophysiological investigations using single cell glass microelectrode impalements on dissected native tissue would help characterize the cellular transporters involved in e.g. urine formation. Collectively, these studies would be important to elucidate how tardigrades functionally have solved colonizing every major type of habitat on the planet, and perhaps be useful in reconstructing how osmoregulation has evolved in metazoans.
28 Dansk sammenfatning
Osmoregulering er kontrollen af kropsvæskernes sammensætning af vand og opløste stoffer. Foruden at opfylde de optimale betingelser for metaboliske processer under indflydelse af eksterne påvirkninger, skal denne sammensætning samtidig imødekomme den kontinuerlige transport af stoffer ind og ud af den levende organisme. Disse krav forekommer umiddelbart fundamentalt uforenelige, men celler og dyr opnår et såkaldt ”steady-state” ved hjælp af et spektrum af transportproteiner, der udøver streng kontrol over udvekslingen af vand og opløste stoffer over forskellige kropsoverflader. De forskellige transportmekanismer ansvarlige for denne kontrol er blevet undersøgt i de fleste dyregrupper, men vores viden om hvorledes dyr håndterer osmotisk stress, er stadig ufuldstændig. I dette arbejde er osmoregulatoriske fænomener blevet undersøgt i såvel vertebrater som invertebrater, omend der hovedsageligt er blevet fokuseret på dynamikkerne af vand og opløste stoffer i Tardigrada. Eksempelvis blev sammensætningen af uorganiske ioner undersøgt i flere forskellige arter af bjørnedyr, hvilket afslørede, at de relative bidrag af uorganiske ioner til den totale osmotiske koncentration overordnet set er ens i bjørnedyr og nært beslægtede dyregrupper. Desuden blev det udledt, at kryptobiotiske bjørnedyr (arter, der er i stand til indtræde i et stadie af latent liv) indeholder en stor andel af organiske osmolytter. Mekanismerne for aniontransport blev undersøgt farmakologisk i en marin art af bjørnedyr, og sammenlignet med de tilsvarende mekanismer i insekter. I bjørnedyret blev den organiske aniontransport lokaliseret til epitelet i midttarmen, og viste sig at være en aktiv transport, med en farmakologisk profil svarende til den i insekter. Bjørnedyr kan overleve et bredt spektrum af osmotiske miljøer (semiterrestrisk, limnisk og marine habitater), hvorfor evnen til at volumen- og osmoregulere blev undersøgt. Disse studier demonstrerede at bjørnedyr kan regulere den samlede kropsvolumen under såvel hypo- som hyperosmotiske forhold, samt indikerede at hyperregulering kan være en gennemgående tendens hos eutardigrader. Indeværende arbejder har altså bidraget til at fastslå bjørnedyr som en vigtig eksperimentel gruppe, hvori centrale fysiologiske spørgsmål kan besvares, heriblandt aspekter af ionregulering og osmoregulering.
29 Acknowledgements
During the course of my PhD studies I was fortunate to have the generous help of many great people, which has made this work possible. First and foremost, I thank my supervisor Nadja Møbjerg for being an unwavering source of support, encouragement and guidance during past years, but also for constantly challenging me to develop intellectually as well as a researcher. I truly appreciate all you have done for me, and hope to be able to continue our collaboration in the future. I also greatly appreciate the support of Reinhardt Møbjerg Kristensen (close to being my second supervisor) who initially introduced me to strange world of tardigrades, and who took me under his wing, offering me guidance and support (and equally important coffee). You have had enormous impact on my education as a young researcher, and I have sincerely enjoyed working with you. I have had the great fortune of working with many wonderful colleagues at University of Copenhagen, both at The August Krogh Center and the Natural History Museum who all are warmly thanked. Thanks to you it has been a pleasure coming to work every day. I am especially grateful to Erik Hviid Larsen with whom I shared many interesting discussions, and who was an endless source of inspiration. Aslak Jørgensen is thanked for great collaborations and discussions over the years as well as for critical review of my thesis. Dennis Krogh Persson is thanked for being a good colleague, but more importantly, a good friend. Since we started this journey in research together, I have come to depend on our collaborations and camaraderie, which has been an invaluable help along the way (by the way, it is your turn to buy cake). I thank Jette Lyby Michelsen for technical assistance over the years. During my visits to Roskilde University I was fortunate to collaborate with several great people. I especially thank Hans Ramløv for allowing me to come work in his laboratory (on several occasions), which scientifically turned out to be quite fruitful. I have particularly enjoyed our conversations and discussions, and I thank you for both your encouragement and support. I also thank Kristine Wulff Larsen for unparalleled project teamwork as well as our many conversations on everything and anything. It was an absolute pleasure,
30 which I hope to repeat some time in the future. Peter Westh is thanked for allowing me to work in his laboratory and for his enormous expertise and help. Perhaps most importantly I thank the help and support of family and friends. I especially thank my parents and parent in-laws for their invaluable support during difficult times, and for helping me and my family in more ways than I care to mention. You’re the best! Lastly I thank my girlfriend Iben Rønn Veland for helping me, supporting me, tolerating me and loving me, but mostly for taking care of our son when I was working – none of this was possible without your help! I also thank my little son Hannibal for tolerating that I had to work sometimes, and couldn’t be home when you wanted me to. I am looking forward to making up for lost time. I love you both more than you know. Thank you. This work was funded by the 2008 Faculty of Science, University of Copenhagen Freja-Programme.
31 References
Anderson, E. (1960). The ultramicroscopic structure of the reptilian kidney. J Morph 106:205- 240. Aguinaldo, A.M.A., Turbeville, J.M., Linford, L.S., Rivera, M.C., Garey, J.R., Raff, R.A. & Lake, J.A. (1997). Evidence for a clade of nematodes, arthropods and other moulting animals. Nature 387 (6632):489-493. Beyenbach, K. W. & Piermarini P. M. (2011). Transcellular and paracellular pathways of transepithelial fluid secretion in Malpighian (renal) tubules of the yellow fever mosquito Aedes aegypti. Acta Physiol 202:387-407. Bertolani, R (2001). Evolution of the reproductive mechanisms in tardigrades – a review. Zool Anz 240:247-252. Campbell, L.I., Rota-stabelli, O., Edgecombe, G.D., Marchioro, T., Longhorn, S.J., Telford, M.J., Philippe, H., Rebecchi, L., Peterson, K.J. & Pisani, D. (2011). MicroRNAs and phylogenomics resolve the relationships of Tardigrada and suggest that velvet worms are the sister group of Arthropoda. PNAS 108:15920-15924. Campiglia, S. (1976). The blood of Peripatus acacioi Marcus & Marcus (Onychophora) – III. The ionic composition of the hemolymph. Comp Biochem Physiol 54(A):129-133. Coast, G. (2007). The endocrine control of salt balance in insects. Gen Comp Endocrinol 152:332-338. Crowe, J. H. & Madin, K. A. (1974). Anhydrobiosis in tardigrades and nematodes. Trans Am Microsc Soc 93:513-524. Dantzler, W. H. (2002). Renal organic anion transport: a comparative and cellular perspective. Biochim Biophys Acta 1566:169-181. Dawson, D. C. & Liu, Xuehong (2009). Osmoregulation: some principles of water and solute transport. In: David H. Evans (ed) Osmotic and ionic regulation: cells and animals. CRS Press, Florida, USA. Degma, P., Bertolani, R. & Guidetti, R. 2009-2012. Actual checklist of Tardigrada species. Ver. 20: 17-01-2012. http://www.tardigrada.modena.unimo.it/miscellanea/Actual checklist of Tardigrada.pdf Degma, P. & Guidetti, R. (2007). Notes to the current checklist of Tardigrada. Zootaxa, 1579:41-53. Dewel, R. A. & Dewel, W. C. (1979). Studies on the tardigrades. J Morphol 161:79-110. Diehl, W. J. (1986). Osmoregulation in echinoderms. Comp Biochem Physiol A 84:199-205. Dow, J. A. T. & Davies, S. A. (2006). The Malpighian tubule: Rapid insights from post- genomic biology. J Insect Physiol 52:365-378. Dowd, W. W., Harris, B. N. Chech Jr, J. J. & Kültz, D (2010). Proteomic and physiological responses of leopard sharks (Triakis semifasciata) to salinity change. J Exp Biol 213:210- 224.
32 Dunn, C.W., Hejnol, A., Matus, D.Q., Pang, K., Browne, W.E., Smith, S.A., Seaver, E., Rouse, G.W. Obst, M., Edgecombe, G.D., Sørensen, M.V., Haddock, S.H.D., Schmidt-Rhaesa, A., Okusu, A., Kristensen, R.M. & Wheeler, W.C. (2008). Broad phylogenomic sampling improves resolution of the animal tree of life. Nature 452:745- 750. Edgecombe, G. D. (2010). Arthropod phylogeny: An overview from the perspective of morphology, molecular data and the fossil record. Arthropod Struct Dev 39:74-87. Essig, A. (1968). The “pump-leak“ model and exchange diffusion. Biophys J 8(1):53-63. Gabriel, W. N. & Goldstein, B. (2007). Segmental expression of Pax3/7 and Engrailed homologs in tardigrade development. Dev Genes Evol 217:421-433. George, R. L., Wu, X., Huang, W., Fei, Y. J., Leibach, F. H. & Ganapathy, V. (1999). Molecular cloning and functional characterization of a polyspecific organic anion transporter from Caenorhabditis elegans. J Pharmacol Exp Ther 291:596-603. Gilles, R. & Delpire, E. (1997). Variations in salinity, osmolarity and water availability. In: Dantzler, W. H. (ed.). Handbook of comparative physiology. New York: Oxford University Press, USA. Glasheen, J. S. & Hand, S. C. (1988). Anhydrobiosis in embryos of the brine shrimp Artemia: characterization of metabolic arrest during reductions in cell associated water. J Exp Biol 135:363-380. Goldstein, B. & Blaxter, M. (2002). Tardigrades. Curr Biol 12:R475. Guidetti, R. & Bertolani, R. (2005). Tardigrade taxonomy: an updated check list of the taxa and a list of characters for their identification. Zootaxa 845:1-46. Guidetti, R., Bertolani, R. & Nelson, D. R. (1999). Ecological and faunistic studies on tardigrades in leaf litter of beech forest. Zool Anz 238:215-223. Hallas T, Yeates G (1972) Tardigrades of the soil and litter of a Danish beech forest. Pedobiologia 12:287-304. Hincha, D. K. & Hagemann, M. (2004). Stabilization of model membranes during drying by compatible solutes involved in the stress tolerance of plants and microorganisms. Biochem J 383:277-283. Hobsen, A. D., Stephenson, W. & Eden A. (1952). Studies on the physiology of Ascaris lumbricoides: II. The inorganic composition of the body fluid in relation to that of the environment. J Exp Biol 29:22-29. Jönson, K. I. (2003). Population density and species composition of moss-living tardigrades in a boreo-nemoral forest. Ecography 26:356-364. Jørgensen, A., Faurby, S., Hansen, J. G., Møbjerg, N. & Kristensen, R. M. (2010). Molecular phylogeny of Arthrotardigrada (Tardigrada). Mol Phylogenet Evol 54:1006- 1015. Jørgensen, A., Møbjerg, N. & Kristensen, R. M. (2007). A molecular study of the tardigrade Echiniscus testudo (Echiniscidae) reveals low DNA sequence diversity over a large geographical area. Proceedings of the Tenth Internationl Symposium on Tardigrada. J limnol 66:77-83. Liggins, G. W. & Grigg, G. C. (1985). Osmoregulation of the cane toad Bufo marinus, in salt water. Comp Biochem Physiol A 82:613-619. Macallum, A. B. (1910). The inorganic composition of the blood in vertebrates and invertebrates, and its origin. Proc R. Soc Lond B 82(559):602-624.
33 Maddrell, S. H. P. & Phillips, J. E. (1975). Secretion of hypo-osmotic fluid by the lower Malpighian tubules of Rhodnius prolixus. J Exp Biol 62:671-683. Martinez, E. A. (1975). Marine meiofauna of a New York City beach, with particular reference to Tardigrada. Est Coast Mar Sci 3:337-348. Morgan, C. I. (1977). Population dynamics of two species of Tardigrada, Macrobiotus hufelandii (Schultze) and Echiniscus (Echiniscus) testudo (Doyère), in roof moss from Swansea. J Anim Ecol 46:263-279. Møbjerg, N & Dahl, C. (1996). Studies on the morphology and ultrastructure of the Malpighian tubules of Halobiotus crispae Kristensen, 1982 (Eutardigrada). Zool J Linn Soc 116:85-99. Møbjerg, N., Jespersen, Å & Wilkinson, M. (2004). Morphology of the kidney in the West African caecilian, Geotrypetes seraphini (Amphibia, Gymnophiona, Caeciliidae). J Morph 262(2):583-607. Nelson, D. R. (2002). Current status of Tardigrada: evolution and ecology. Integr Comp Biol 42(3):652-659. Normant, M., Kubicka, M., Lapucki, T., Czarnowski, W. & Michalowska M. (2005). Osmotic and ionic haemolymph concentration in the Baltic Sea amphipod Gammarus oceanicus in relation to water salinity. Comp Biochem Physiol A 141:94-99. O’Donnell, M. J. & Maddrell, S. H. P. (1995). Fluid reabsorption and ion transport by the lower Malpighian tubules of adult female Drosophila. J Exp Biol 198:1647-1653. Peaker, M (1971). Avian salt glands. Philos Trans R Soc Lond B 262:289-300. Pelzer, B., Dastych, H. & Greven, H. (2007). The osmoregulatory/excretory organs of the glacier-dwelling eutardigrade Hypsibius klebelsbergi Mihelcic, 1959 (Tardigrada). Mitt. hamb. Zool Mus Inst 104:61-72. Ramazzotti, G. & Maucci W. (1983). Il Phylum Tardigrada. Terza edizione riveduta e corretta. Mem Insti Ital Idro Dott Marco De Marchi 41:1-1012. Reilly, D., Cramp, R. L., Wilson, J. M., Campbell, H. A. & Franklin, C. E. (2011). Branchial osmoregulation in the euryhaline bull shark, Charcharhinus leucas: a molecular analysis of ion transporters. J Exp Biol 214:2883-2895. Renaud-Mornant, J. (1982). Species diversity in marine Tardigrada. In: Nelson (Ed.) Proceedings of the 3rd international symposium on Tardigrada. East Tennessee State University Press, pp. 149-178. Reynolds, S. E. & Bellward, K. (1989). Water balance in Manduca sexta caterpillars: water recycling from the rectum. J Exp Bio 141:33-45. Ricci, C., Melone, G. Santo, N. & Caprioli, M. (2003). Morphological response of a Bdelloid Rotifer to dessication. J Morphol 257:246-253. Riegel, J. A. (1970). A new model of transepithelial fluid movement with detailed application to fluid movement in the crayfish antennal gland. Comp Biochem Physiol 36:403-410. Robertson, J. D. (1949). Ionic regulation in some marine invertebrates. J Exp Biol 26:182- 200. Rota-Stabelli O, Kayal E, Gleeson D, Daub J, Boore J, Telford M, Pisani D, Blaxter M, Lavrov D. (2010). Ecdysozoan mitogenomics: evidence for a common origin of the legged invertebrates, the Panarthropoda. Genome Biol Evol 2:425-440. Sardella, B. A., Baker, D. W. & Brauner, C. J. (2009). The effects of variable water salinity and ionic composition on the plasma status of the Pacific Hagfish (Eptatretus stoutii). J Comp Physiol B 179:721-728.
34 Sarver, R. G., Flynn, M. A. & Holliday, C. W. (1994). Renal Na, K-ATPase and osmoregulation in the crayfish Procambarus clarkii. Comp Biochem Physiol (A) 107:349- 356. Schluter, D. (2009). Evidence for ecological speciation and its alternative. Science 323:737- 741. Schmidt-Nielsen, K. (1963). Osmotic regulation in higher vertebrates. Harvey lect 58:53-93. Schmidt-Rhaesa A, Kulessa J. (2007). Muscular architecture of Milnesium tardigradum and Hypsibius sp. (Eutardigrada, Tardigrada) with some data on Ramazzottius oberhaeuseri. Zoomorphol 126:265-281. Sutcliffe, D. W. (1962). The composition of haemolymph in aquatic insects. J Exp Biol 39:325-343. Suzuki, A. C. (2003). Life history of Milnesium tardigradum Doyère (Tardigrada) under a rearing environment. Zool Sci 20:49-57. Torrie, L. S., Radford, J. C., Southall, T. D., Kean, L., Dinsmore, A. J., Davies, S. A. & Dow, J. A. T. (2004). Resolution of the insect ouabain paradox. PNAS 101: 13689-13693. Uhía, E. & Briones, M. J. I. (2002) Population dynamics and vertical distribution of enchytraeids and tardigrades in response to deforestation. Acta Oecolog 23:349-359. Van Weel, P. B. (1957). Observations on the osmoregulation in Aplysia juliana Pease (Aplysiidae, Mollusca). Z vergl Physiol 39:492-506. Walz, B. (1974). The Fine Structure of Somatic Muscles of Tardigrada. Cell Tiss Res 149:81- 89. Weglarska, B. (1987). Studies on the excretory system of Isohypsibius granulifer Thulin (Eutardigrada). In: Biology of tardigrades. Selected symposia and monographs (1) (ed. Bertolani, R.), pp. 15-24. Modena: U.Z.I. Mucchi. Whittamore, J. M. (2012). Osmoregulation and epithelial water transport: lessons from the intestine of marine teleost fish. J Comp Physiol B 182:1-39. Wilder, M. N., Ikuta, K., Atmomarsono M., Hatta, T. & Komuro, K. (1998). Changes in osmotic and ionic concentrations in the hemolymph of Macrobrachium rosenbergii exposed to varying salinities and correlation to ionic and crystalline composition of the cuticle. Comp Biochem Physiol A 119:941-950. Williams, J. C. & Beyenbach, K. W. (1983). Differential effects of secretagogues on Na and K secretion in the Malpighian tubules of Aedes aegypti. J Comp Physiol B 149:511-517. Yancey, P. H. (2005). Organic osmolytes as compatible, metabolic and counteracting cytoprotectants in high osmolarity and other stresses. J Exp Biol 208:2819-2830. Zantke, J., Wolff, C. & Scholtz, G. (2008). Three-dimensional reconstruction of the central nervous system of Macrobiotus hufelandi (Eutardigrada, Parachela): implications for the phylogenetic position of Tardigrada. Zoomorphol 127:21–36. Zhao, H. (2005). Effect of ions and other compatible solutes on enzyme activity, and its implication for biocatalysis using ionic liquids. J Mol Catal B: Enzymat 37:16-25.
35
UNIVERSITAS HAFNIENSIS 2012
36 Paper I
Inorganic ion composition in Tardigrada: cryptobionts contain large fraction of unidentified organic solutes
1,* 2 3 2 Kenneth Agerlin Halberg , Kristine Wulff Larsen , Aslak Jørgensen , Hans Ramløv and Nadja Møbjerg1
1 Department of Biology, the August Krogh Centre, University of Copenhagen, Universitetsparken 13, DK- 2100 Copenhagen Ø, Denmark, 2 Department of Nature, Systems and Models, University of Roskilde, Universitetsvej 1, DK-4000 Roskilde, Denmark and 3 Laboratory of Molecular Systematics, Natural History Museum of Denmark, University of Copenhagen, Sølvgade 83, DK-1307 Copenhagen K, Denmark *Author for correspondence ([email protected])
Submitted June 2012
SUMMARY Tardigrades are a group of micrometazoans known to tolerate extreme environmental stress. Significant efforts have been devoted to the field, however; mechanisms explaining the extreme adaptations found among tardigrades is still lacking. Here we present data on the inorganic ion composition and total osmotic concentration of five different species of tardigrades (E. testudo, M. tardigradum, R. coronifer, M. cf. hufelandi and H. crispae) using high-performance anion-exchange chromatography and nanoliter osmometry. Quantification of the ionic content indicates that Na+ and Cl- are the principle inorganic ions + + 2+ 2+ - 2- 3- in tardigrade fluids, albeit substantial concentrations of K , NH4 , Ca , Mg , F , SO4 and PO4 also were detected. In limno-terrestrial tardigrades, the respective ions are concentrated by a large factor compared to that of the external medium (Na+, ×70-800; K+, ×20-90; Ca2+ and Mg2+, ×30-200; Cl-, ×20-50; 2- + - 2- SO4 , ×30-150), whereas in the marine species H. crispae Na , Cl and SO4 are almost in ionic equilibrium with (brackish) salt water, while K+, Ca2+ and Mg2+ are slightly concentrated (×2-10). However, there is an anion deficit of ~120 mEq/l in M. tardigradum and H. crispae, indicating that there are ionic components that remain unidentified in these species. Body fluid osmolality ranged from 361±49 in R. coronifer to 961±43 mOsm/kg in H. crispae. Concentrations of most inorganic ions are largely identical between active and dehydrated groups of R. coronifer, suggesting that this tardigrade does not exclude large amounts of ions during dehydration. The large osmotic and ionic gradients maintained by both limno-terrestrial and marine species are indicative of a powerful ion-retentive mechanism in Tardigrada. Moreover, our data indicates that cryptobiotic tardigrades contain a large fraction of unidentified organic osmolytes, the identification of which is expected to provide increased insight into the phenomenon of cryptobiosis.
Key words: tardigrades, inorganic ions, ion chromatography, nanoliter osmometry, organic osmolytes, cryptobiosis
INTRODUCTION intensive research efforts have been devoted to the Tardigrades are a group of minute multi-cellular field, as the translational output associated with a animals that are known to tolerate extreme detailed understanding of their complex stress environmental stress (Guidetti et al., 2010; biology is expected to include new methods for Møbjerg et al., 2011). This capacity derives preserving and stabilizing biological materials mainly from their ability to enter a state latent of (Wełnicz et al., 2010). Several advances have been life, i.e. cryptobiosis, in which their resistances to made in our understanding of tardigrade stress adverse environmental conditions are greatly responses, especially regarding i) the role of increased (Møbjerg et al., 2011). In recent years, selective carbohydrates (trehalose), ii) the K. A. Halberg and others differential expression of stress proteins (heat 1834 and Milnesium tardigradum Doyère, 1840 shock proteins and late embryogenesis abundant were extracted from moss collected at Öland, proteins), and iii) the identification of anti- Sweden, while Echiniscus testudo Doyère, 1840 oxidant defenses and DNA repair mechanisms was found in moss collected at Nivå, Denmark. (see reviews by Guidetti et al., 2010; Wełnicz et These species were extracted by washing the al., 2010; Møbjerg et al., 2011). However, a respective moss samples with tap water through general mechanism explaining the extreme six different sieves of progressively smaller mesh adaptations found among tardigrades is still size, so as to concentrate the tardigrades and to lacking. Consequently, new approaches that may remove large debris. Specimens of Halobiotus provide increased insight into the superior stress crispae Kristensen, 1982 were isolated from adaptations of tardigrades are greatly needed. marine algae and sediment collected from Knowledge of the composition as well as Vellerup Vig, Denmark according to the method concentrations of dissolved particles in internal of Halberg and Møbjerg (2012). The total number fluids is fundamental to the understanding of of animals used in all experiments was 2220 R. basic physiological processes, such as fluid and coronifer, 326 M. tardigradum, 630 M. cf. electrolyte homeostasis, signal transduction and hufelandi, 426 E. testudo and 268 H. crispae. solute transport. Accordingly, such data have been provided for most major groups of animals Inorganic cation and anion analysis (cnidarians, echinoderms, annelids, molluscs, The dominant cations and anions present in the crustaceans, insects, chelicerates, tunicates, fish, different tardigrade species were determined by amphibians and mammals) more than half a HPAEC using a Metrohm chromatography system century ago (Macallum, 1910; Robertson, 1949, (830 IC interface, 818 IC pump, 819 IC 1954; Sutcliffe, 1962; Hronoski & Armstrong, conductivity detector, columns C4 - 150/4.0 1977). However, practically nothing is known (cations) and A supp 5 150/4.0 (anions); Metrohm, about the chemical composition of tardigrades, Herisau, Switzerland). The eluents (mobile which has been a major obstacle to the phases) were made according to manufacturer’ understanding of the fluid and solute dynamics in instructions: For cations, the eluent consisted of these animals (Halberg et al., 2009b; Møbjerg et 0.7 mM C7H5NO4 + 1.7 mM (65%) HNO3. For al., 2011; Halberg & Møbjerg, 2012). Questions anions, it consisted of 3.2 mM Na2CO3 + 1.0 mM relating to this area of research are especially NaHCO3. The eluents were filtered (mesh size: 45 important to address, if we wish to unravel the µm) prior to use. The analysis settings employed biological mechanisms mediating the unique were a flow-rate of 0.9 ml/min (cations) and 0.7 tolerance to extreme desiccation (anhydrobiosis) ml/min (anions) with a pressure of ~6.4 MPa. – the most widespread form of cryptobiosis in Cation analyses were performed non-suppressed, Tardigrada. whereas anion detection was conducted using In the present study, we use a combination of chemical suppression. Fluka multi-element cation high-performance anion-exchange chromato- and anion standards (Sigma-Aldrich, St. Louis, graphy (HPAEC) and nanoliter osmometry, to MO, USA) were used to construct calibration identify and quantify inorganic cations and anions curves for the respective ions bracketing the present in tardigrade homogenates, and to concentration range of interest. Based on these measure the total osmotic concentrations of five calibration curves, the ion chromatography (IC) different species of tardigrades, covering both a software (IC Net 2.3, Metrohm, Herisau, broad phylogenetic and habitat spectrum. Our Switzerland) calculated the ion concentrations of study indicates that tardigrades possess powerful all subsequent samples (mg/l), which were ion-retentive and osmoregulatory capacities, and recalculated to a different unit of concentration that (only) cryptobiotic species contain a large (mM) and adjusted according to the appropriate fraction of organic solutes. dilution factor (see below). Representative chromatograms of both the cationic and anionic MATERIALS AND METHODS fractions are shown for all investigated species Tardigrade sampling (Figs. 1, 2). The empirically determined elution Specimens of Richtersius coronifer Richters, order and retention times of the investigated ions + + 1908, Macrobiotus cf. hufelandi C.A.S. Schultze, were Na (tR = 5.37 min), NH4 (tR = 6.03 min), Inorganic ion composition in Tardigrada
Fig. 1. Representational chromatograms revealing the principal inorganic cations present in each investigated species: 1, sodium; 2, ammonium; 3, potassium; 4, calcium; 5, magnesium; nOAp, negative organic acid peak. Stitched square indicates an unidentified compound (tR = 10.36 min) that increases app. two-fold in absolute concentration in dehydrated animals of Richtersius coronifer (data not shown). Column, Metrohm C4-150/4.0; mobile phase, 0.7 mM dipicolinic acid + 1.7 mM (65%) nitric acid; flow-rate, 0.9 ml/min; Conductivity detector without suppression. Injection volume, 60 µl.
+ 2+ 2+ K (tR = 7.73 min), Ca (tR = 18.12 min), Mg performed as fast and uniform as possible. A total - - (tR = 23.17 min), F (tR = 4.05 min), Cl (tR = 6.01 of 40-225 animals were transferred to each test 3- 2- min), PO4 (tR = 14.74 min) and SO4 (tR = 16.58 tube and the sample was subsequently min). homogenized using a sterile plastic pestle; great care was taken to ensure complete homogenization Sample preparation (visually confirmed at 50× magnification), and the Following extraction, specimens were washed pestle was subsequently rinsed with a small repeatedly with ddH2O (Halobiotus crispae was volume of cation eluent to ensure total transfer of washed in filtered salt water; SW, 20 ‰), and ions to the test tube. The number of animals per subsequently transferred, using an Irwin loop, to sample (N) varied according to species size and sample tubes containing cation eluent (75-100 availability (Tables 1, 2). The entire sample was µl); samples dissolved in cation eluent allows for then centrifuged (10 min at 5600 rpm) to remove a more precise quantification of cations due to solid particles (e.g. cuticle fragments), and the increased signal to noise ratio (pers. comm.; supernatant was filtered (mesh size: 0.20 µm) Metrohm Nordic, Denmark). Prior to transfer, using a single use syringe filter (Sartorius AG, surface water was removed by blotting the Göttingen, Germany). The samples were animals with tissue paper in an attempt to avoid subsequently frozen at -20 ºC, if not quantified unwanted dilution of the samples. Pilot immediately. A total of five to seven samples were experiments revealed that this process was critical prepared for each species (Table 2). to acquire reproducible data, and was accordingly K. A. Halberg and others
Fig. 2. Representational chromatograms revealing the principal inorganic anions present in each investigated species: 6, fluoride; 7, chloride; 8, phosphate; 9, sulfate; W, negative water peak. Stitched square indicates an unidentified compound (tR = 7.24 min) that increases app. two-fold in absolute concentration in dehydrated animals of Richtersius coronifer (data not shown). Column, Metrohm A supp 5 150/4.0; mobile phase, 3.2 mM sodium carbonate + 1.0 mM sodium hydrogen carbonate; flow-rate, 0.7 ml/min; Conductivity detector with chemical suppression. Injection volume, 60 µl.
The ionic concentration and composition of dehydration, tissue paper saturated with ddH2O the external media from the different habitats i.e. was used to rinse the surface of the animals, and a moss water (MW) and SW, were additionally dry tissue paper was used to remove excess determined. Moss samples were rehydrated in moisture. This was done in order to remove ddH2O for several hours, and MW samples were potential solutes extruded on the surface of the subsequently collected from between the leaf- animals – the surface of some animals was covered stems. SW samples were prepared by inaccessible due to animal clumping, and therefore diluting SW (1:200) collected at the locality. could not be rinsed. A volume of 90 µl of cation Samples were quantified in triplets using both eluent was added, and the animals were vapor pressure osmometry (Vapro 5520, Wescor immediately homogenized. The samples were then inc., UT, USA) and HPAEC (Table 3). prepared as described above with six samples In order to document whether changes in prepared in total (Table 2). Data (mg/l) from this inorganic ion content occur during dehydration experiment was directly compared to that of from an active to a cryptobiotic state, samples of hydrated animals (Table 4; Fig. 3B), as both sets dehydrated Richtersius coronifer were of samples contained near identical number of additionally prepared. Groups of 75 animals were animals per unit volume (i.e. 0.81 and 0.83 transferred to each sample tube, and excess water animals/µl eluent respectively), which was removed by blotting the animals with tissue circumvented the need for recalculations (see paper. The animals were subsequently allowed to below). In order to test whether R. coronifer dehydrate over the ensuing 24 h at ambient actually produced viable tuns during the temperature and humidity. Following complete abovementioned conditions, post-cryptobiotic Inorganic ion composition in Tardigrada survival was assessed. Using four groups of 50 tardigrade, r is the radius and h the length of the specimens, a survival rate of 94 ± 4% (mean ± trunk and hind legs respectively, while W (0.72 i.e. s.d.) was observed, which is comparable to the mean fractional water content of R. coronifer and maximally reported survival rate of R. coronifer H. crispae) is the gravimetrically measured dehydrated on Whatman filters (Persson et al., fractional water content. Using these data (Table 2010). 1), the total tardigrade test volume was calculated by multiplying the volume of an individual with Calculation of ion concentrations the number of animals included in the sample The IC software expressed the integration of according to equation (2). peaks as a concentration (mg/l), which was recalculated using the respective molecular (Eq 2) Vtotal = Vindividual × N weights of each compound to a different concentration (mM) prior to adjusting for the Vtotal is the total tardigrade test volume, and N the dilution factors. number of animals included in the sample. Lastly, The volume of each investigated species was the concentrations of the dominant cations and calculated according to an adjusted method of anions in the investigated species of tardigrades Halberg et al. (2009b). In brief, micrographs were were calculated by multiplying the measured ion taken of N = 20 animals of each species, using a concentrations with the dilution factor, which was digital camera (C-5050, Olympus, Japan) calculated according to equation (3). mounted on an Olympus BX 51microscope (Olympus, Japan), and median length (h) and (Eq 3) D = F / Vtotal width (2r) of the trunk and legs were measured. Approximating the geometric shape of the trunk Where D is the dilution factor and F is the final and legs as a cylinder, and adjusting the volume volume (i.e. volume of cation eluent the of liquid according to the gravimetrically tardigrades were transferred to + Vtotal). Sample measured water content (based on Westh and information for the respective species is listed in Kristensen, 1992; Halberg et al., 2009b), the fluid Table 2. volume of an individual tardigrade of each species was calculated using equation (1). Nanoliter osmometry The total osmotic concentration of tardigrades 2 2 (Eq 1) Vindividual = π(r trunkhtrunk + 8r leghleg) × W from each investigated species was estimated using nanoliter osmometry. This was done in order Where Vindividual is the volume of an individual to determine the fraction that the identified
Table 1. Volume estimations. Mean values of length (h) and width (2r) of the trunk and legs (N = 20 animals), as well as the calculated volume (Eq 1), of each investigated species. W is the average of the gravimetrically determined water content (72%) of Richtersius coronifer (Westh and Kristensen, 1992) and Halobiotus crispae (Halberg et al., 2009). Data are expressed as mean ± s.d. K. A. Halberg and others inorganic ions constitute of the total osmotic respect to the external medium; hyper-regulation concentration in each species, and to provide an has previously been suggested to be a general independent verification of our HPAEC data, i.e. theme among members of Eutardigrada (Halberg total osmotic concentration should be higher than et al., 2009b; Møbjerg et al., 2011). Comparing the accumulated concentration of the respective the measured total osmotic concentrations with the inorganic ions (Table 3). Using the same calculated total ionic concentrations reveals that procedure for removing excess water as described there is a large ‘osmotic deficit’, especially in the above, individual specimens were transferred into limno-terrestrial cryptobiotic species E. testudo, sample oil wells (loading oil type B; cST=1250 ± M. tardigradum, R. coronifer and M. cf. hufelandi 10%; Cargille laboratories, Cedar grove, NJ (Fig. 3A; Table 3). Furthermore, in most species 07009, USA) of a calibrated nanoliter osmometer the measured positive and negative charges do not (Clifton Technical Physics, Hartford, NY, USA), entirely maintain electro-neutrality (Table 3). This and the osmolality (mOsm/kg) was determined by charge deficit indicates that there are ionic freezing point depression (FPD = 1.858 components that remain unidentified, especially in °C/Osmol). Six to ten animals of each species M. tardigradum and H. crispae, and that these were used in this experiment (Table 3). unidentified ions contribute to the observed osmotic deficits. Bicarbonate for example, is Statistics important for pH-regulation of the extracellular Significant changes in the individual inorganic fluid of most animals, and could contribute ion concentrations between active and significantly to the unidentified anionic fraction. cryptobiotic animals of Richtersius coronifer The charge deficit appears to account for the entire were tested using an unpaired, two-sample t-test osmotic deficit in H. crispae (Table 3), however; with significance levels of P>0.05 (not even when accounting for the charge deficits, a significant, NS), P<0.05 (significant, *) and large fraction of unidentified osmolytes remain P<0.01 (very significant, **). unaccounted for in the limno-terrestrial, cryptobiotic species (Fig. 3A). In fact, this RESULTS difference is likely even greater than indicated in Ionic composition and total osmotic Figure 3A, as our ionic data was not corrected concentration in tardigrades according to osmotic coefficients. Total osmotic concentration range 361±49 in R. Na+ and Cl- are the principal inorganic ions of coronifer to 961±43 mOsm/kg in H. crispae from tardigrade fluids, accounting for 11-56% of the (Table 3), indicating that both limno-terrestrial total osmotic concentration in all investigated and marine species are hyper-osmotic with species; with Macrobiotus cf. hufelandi and
Table 2. Sample data. Number of samples (n), number of animals per sample (N), total number of animals used (n × N), total tardigrade test volume (Vtotal, Eq 2), final volume (F), as well as the resulting dilution factor (D, Eq 3) is listed. Dehydrated animals of R. coronifer have no measurable water content, why Vtotal, F and D cannot be listed. Inorganic ion composition in Tardigrada
Figure 3. Graphical representation of the respective ionic contributions to total osmotic concentration. A. Concentrations (mM) of the respective cations and anions measured in each investigated species, as well as the corresponding total osmotic concentration (mOsm/kg), as measured by nanoliter osmometry (see also Table 3). The blank area represents the osmotic deficit (OD), i.e. other solutes. The phylogenetic position and habitat preference of each species is listed. The light micrographs of the animals are shown to scale (see Table 1 for average species size). B. Concentrations (mg/l) of the respective cations and anions measured in hydrated, active specimens compared to dehydrated cryptobiotic animals of Richtersius coronifer (see also Table 4). Data are expressed as mean ± s.d. K. A. Halberg and others
Halobiotus crispae containing the lowest and bone of vertebrates and exoskeletons of highest concentrations respectively (Fig. 3A; invertebrates, and is for example found in Table 3). There are notable differences in the Na+/ extremely high levels in the cuticle of marine Cl- ratio between the animals, i.e., the ratio is less crustaceans (Adelung et al., 1987; Sands et al., than unity in the limno-terrestrial herbivores E. 1998). In contrast, the [F-] in blood/hemolymph testudo (0.61), R. coronifer (0.60) and M. cf. and soft tissue is negligible (Adelung et al., 1987; hufelandi (0.33), higher than unity in the limno- Sands et al., 1998). Therefore, the [F-] of our terrestrial predator M. tardigradum (1.19) and samples could reflect ions bound to cuticular close to unity in the marine herbivore H. crispae structures that do not contribute to the dissolved (0.92). anionic fraction. Indeed, high levels of dissolved Compared with Na+ and Cl-, generally, the F- are deleterious to enzymatic function (Eagers, [K+] is relatively low in all species, ranging from 1969). In line with this suggestion, the observed 19-73 mM (Tab. 3). Thus, the Na+/ K+ ratio is differences in [F-] could relate to differences in higher than unity in E. testudo (2.39), M. cuticle composition, with a lower F- content in tardigradum (2.05), R. coronifer (1.32) and H. members of Macrobiotiidae (R. coronifer and M. crispae (6.12), however; lower than unity in M. cf. hufelandi) compared to other species (Table 3). 3- 2- cf. hufelandi (0.77). Interestingly, the relative Conversely, the detected [PO4 ] and [SO4 ] both contribution of K+ to total osmotic concentration contribute to the anionic fraction in all tardigrade is low constituting <10 % in all investigated species, accounting for approximately 1-6% and species (Table 3), regardless of dietary and 1-4% of the total osmotic concentration, habitat preferences – an observation that is respectively, with the highest concentrations paralleled by insects, in which K+ usually detected in the marine H. crispae (Fig. 3A; Table contributes 2-10% of total hemolymph 3). concentration (Sutcliffe, 1963). The highest absolute [K+] is found in the predator M. Changes in ionic composition during tardigradum, and is app. 2-3 times the dehydration concentration of the herbivorous species (Table Surprisingly, the concentrations of the examined 3). ions showed little variation from the active to the In general, high [Ca2+] seems characteristic of cryptobiotic state in specimens of Richtersius tardigrade fluids, just as reported for aquatic coronifer (Fig. 3B; Table 4). Excluding small yet insects (Sutcliffe, 1962). In contrast, [Mg2+] is significant changes in the K+ and Cl- contents, only + comparatively low in all limno-terrestrial species, NH4 was very significantly reduced from the + and ranges from 2-13 mM. Conversely, in the hydrated to the dehydrated state (Table 4). NH4 is marine tardigrade H. crispae the [Mg2+] remains a waste product of protein metabolism, so the relatively high (Table 3; Fig. 3), which is in observed reduction could reflect the general shut- agreement with the high [Mg2+] in SW (Table 3). down of metabolic processes during dehydration. 2+ + Comparable high [Mg ] have also been reported NH4 is a weak acid that easily converts to NH3 from marine crustaceans (Tentori and Lockwood, depending on the pH of the solution, so the 1990). However, it should be taken into account measured final biological concentration is no more that the measured cation pools include ions that than tentative. typically form complexes with proteins and other macromolecules. For example, the stylet and DISCUSSION stylet supports of tardigrades are known to be Ionic composition in tardigrades composed of CaCO3 (Bird and McClure, 1997), Our analyses of osmotic and ionic concentrations why the concentrations of e.g. Ca2+ in tardigrade have been performed on homogenates of the + fluids could be lower than measured. NH4 also investigated species with no distinction between appears to contribute to the total osmotic intra- and extracellular compartmentalization. concentrations measured in all species, with Nevertheless, our data provide a much needed values of 6-31 mM detected. indication of osmolyte composition in Tardigrada, Substantial [F-] was detected in all tardigrade which is fundamental to our understanding of samples, ranging from 7-52 mM (Table 3). This tardigrade physiology. ion is typically localized to hard tissue, such as Inorganic ion composition in Tardigrada charges) are listed; the polarity polarity the are listed; charges) cations and anions detected in each investig detected anions and cations as mean ± s.d. difference in ionic concentration, and total or osmometry nanoliter by measured as (mOsm/kg), concentration composition and Table 3. Ionic of the charge deficits is indicated in parent of the charge deficits total osmotic concentration of the investigated osmotic concentration), as well theosmotic obse ated species, as moss water (MS) as well vapor pressure osmometry, respect hesis. Numbers noted Numbers noted in hesis. species of tardigrades and the corresponding ext and 20 ‰ salt water (SW) samples, in addit rved charge deficits (calculated as the (calculated deficits rved charge brackets indicates the n brackets indicates ively. In addition, the osmotic umber of samples tested difference between and negativepositive ion to the correspo the to ion ernal media. Concen deficits (calculated as the . Data are expressed nding total osmotic trations (mM) of K. A. Halberg and others
In the present study we provide data on the ionic tardigradum resembles the heterotardigrades more composition of five different species of than the other eutardigrades (Table 5) tardigrades covering a large phylogenetic Sutcliffe (1962, 1963) argued that definitive spectrum. Our study is represented by members types of hemolymph are related to phylogenetic of Heterotardigrada (Echiniscoidea) and position within Insecta. Apart from small Eutardigrada (Apochela and Parachela), four differences in absolute concentrations of Na+ and 3- evolutionary distant families (Echiniscidae, PO4 , the ionic compositions and relative Milnesiidae, Macrobiotidae and Hypsibiidae), as contributions of the different components in well as both limno-terrestrial and marine habitats. Richtersius coronifer and Macrobiotus cf. Accordingly, we will discuss the ionic hufelandi (Eutardigrada: Macrobiotidae) are compositions of the respective species in relation similar (Tables. 3 and 5). As a testable hypothesis, to systematic position and habitat preference, as these similarities would suggest that the relative well as make comments on our data in relation to ion composition among the species relates to hemolymph composition in representatives of phylogeny and systematic position in Tardigrada. phylogenetically related groups (i.e. Arthropoda In contrast to the other groups of limno-terrestrial and Onychophora). tardigrades, the inorganic content of R. coronifer Echiniscus testudo (Heterotardigrada: and M. cf. hufelandi is characterized by a Echiniscidae) belongs to another evolutionary relatively small contribution of Na+ (~2-7 times lineage than the other tardigrades in the present lower) and Cl- (~2-3 times lower), and conversely, 2- study. Compared to limno-terrestrial members of a relatively large contribution of SO4 (~4-10 Eutardigrada, the ionic composition of this times higher). The physiological significance of heterotardigrade is characterized by a large these variations is unknown. contribution of Na+ and Cl- (~45%), and a very Halobiotus crispae (Eutardigrada: 2+ 2- low contribution of Mg (0.4%), SO4 (0.6%) Hypsibiidae) is a truly marine species, and is the 3- and PO4 (1.4%), respectively (Tab. 5). The large species with the highest total concentration of both contribution of Na+ and Cl- to total osmotic ions and total solutes measured. Na+ and Cl- concentration, which is comparable to that seen in account for more than 50% of its total osmotic the marine species H. crispae (Table 5), could concentration. The divalent cations, Ca2+ and reflect the supposed marine origin of tardigrades Mg2+, are also detected in high concentrations, (Jørgensen et al., 2010). This hypothesis can be both absolute and relative. In contrast to the tested by data on members of the ‘ancient’ and limno-terrestrial species, the total osmotic exclusively marine Arthrotardigrada. concentration of H. crispae is almost exclusively The family Milnesiidae, represented by the accounted for by the measured ionic predator Milnesium tardigradum, is currently concentrations, which becomes evident when considered the sister-group of all other considering the charge deficit indicated in Table 3. eutardigrades (Guidetti et al., 2009). M. The contribution of the total diffusible ions to tardigradum contains the highest total osmotic- as the total osmotic concentration of tardigrades is well as ionic concentration among the limno- roughly similar to that of the hemolymph of terrestrial species, with conspicuously high levels arthropods, nematodes and onychophorans (Table of both K+ and Ca2+ (Table 3). The high [K+] in 5). In fact, as Na+ predominantly is an M. tardigradum compared to the phytophagous extracellular ion, whereas K+ and Ca2+ mainly are species is somewhat surprising, as e.g. intracellular ions, the ionic composition of carnivorous insects typically contain low levels of tardigrade hemolymph is expected to resemble K+ (Sutcliffe, 1962). Conversely, phytophagous that of closely related animal groups, e.g. other tardigrades are known to feed on bryophytes high members of Panarthropoda (see Table 5). in K+ and low in Na+ (Smith, 1978), and were, It is relevant to compare concentrations of ions analogous to phytophagous insects (Sutcliffe, in tardigrade body fluids with those of the 1962), expected to reflect this relative ion respective external media (Table 3). The strongest composition in their extracellular body fluids. ability to concentrate ions is seen in limno- Interestingly, the relative ion contributions to terrestrial species, which hyper-regulate by as total osmotic concentration suggests that M. much as ~350-750 mOsm/kg (Fig. 3A). The marine H. crispae maintains hemolymph osmotic Inorganic ion composition in Tardigrada
Table 4. Changes in ionic composition during dehydra- tion. Concentrations (mg/l) of the respective cations and anions measured in hydrated, active specimens compared to dehydrated cryptobiotic animals of Richtersius coronifer. Both sets of samples contained near identical number of animals per unit volume (i.e. 0.8 animals/µl eluent), and were accordingly directly comparable. Numbers noted in brackets indicates the number of samples tested. Data are expressed as mean ± s.d. Significant difference in the concentration of the respective inorganic ion concentrations were tested using an unpaired, two-sample t-test with significance levels of P>0.05 (not significant, NS), P<0.05 (significant, *) and P<0.01 (very significant, **).
pressure ~300 mOsm/kg above that of the (Halberg et al., 2009b; Halberg and Møbjerg, environment, and does so over much larger range 2012). of external salinities compared to the limno- terrestrial species R. coronifer (Halberg et al., Changes in ionic composition during 2009b; Møbjerg et al., 2011). In this context it dehydration should be emphasized that the MW samples were Desiccation is the most severe form of osmotic acquired by rehydrating moss samples with stress, and tardigrades are among the most ddH2O, and not precipitation from the locality, desiccation tolerant animals on Earth (Møbjerg et however; as atmospheric precipitation generally al., 2011). As cryptobiotic tardigrades dehydrate, contains few dissolved particles, with a liquid water is slowly reduced to immeasurable concentration of less than 400 µM (Granat, 1972), levels (Westh and Ramløv, 1991), which leads to a this is likely to be of little consequence. gradual increase in dissolved particles and osmotic Accordingly, Na+ is concentrated by a factor of pressure of the body fluids. In general, the basis ×70-800, K+ by ×20-90, Ca2+ and Mg2+ by ×30- for osmotic stress tolerance includes the active 200, whereas Cl- is concentrated by ×20-50, and extrusion of inorganic ions combined with the 2- SO4 by ×30-150 in limno-terrestrial tardigrades. accumulation of organic ‘compatible’ osmolytes + - 2- In contrast, Na , Cl and SO4 are basically in (Yancey, 2005) – at very high concentrations, ionic equilibrium with respect to the external SW inorganic ions bind to and destabilize proteins and in H. crispae, while K+, Ca2+ and Mg2+ are nucleic acids, which invariably damages cellular concentrated by a factor of ×2-10. The large function (Yancey, 2005). In this regard it was osmotic and ionic gradients maintained by both surprising to learn that R. coronifer apparently do limno-terrestrial and marine species are indicative not exclude inorganic ions during dehydration of powerful ion retentive mechanisms in (Fig. 3B; Table 4), which indicates a concomitant Tardigrada – functions that presumably are accumulation of organic osmolytes. Organic maintained by such organ systems as the osmolytes can accumulated in large amounts Malpighian tubules (only found in eutardigrades, without perturbing cellular function, hence the see. e.g. Møbjerg and Dahl, 1996) and gut system term ‘compatible’, and hereby increase K. A. Halberg and others intracellular osmotic potential so that osmotic makes tardigrades especially interesting for equilibrium between intra- and extracellular identification of osmolytes with protective fluids is maintained. Moreover, organic functions, as well as for the study of their physio- osmolytes are known to stabilize macromolecular chemical mechanisms. The non-reducing sugar, structures by direct interaction with proteins and trehalose, has already received much attention membrane lipids (Crowe et al., 1987; Hincha and (Westh and Ramløv, 1991; Hengherr et al., 2007; Hagemann, 2004; Yancey, 2005). As evidenced Jönsson and Persson, 2010). Interestingly, by the large osmotic deficits, which appears however, trehalose is present only in minute restricted to cryptobiotic tardigrades (Fig. 3A; quantities in active tardigrades (e.g. 0.1% dry Table 3), it is tempting to suggest that a large weight in R. coronifer), and is accumulated to no quantity of organic osmolytes are synthesized in more than 2.9% of the dry weight in Macrobiotus these species, thus enabling the animals to islandicus (Jönsson and Persson, 2010). respond quickly to decreases in external water Obviously, it cannot account for the observed potential. Such a strategy seems favorable in light osmotic deficits demonstrated in the present study, of the continuous dehydration-rehydration cycles although it appears sufficient to confer protection that may occur in limno-terrestrial habitats, against dehydration in the investigated members additionally supported by the short time span of Macrobiotidae. In fact, cell concentrations of (<20 min) with which tardigrades can enter the trehalose for maximal cell survival during tun stage successfully. De novo synthesis of dehydration of murine fibroblasts are about 5.3 × osmolytes during dehydration of cryptobiotic 1010 molecules per cell (Chen et al., 2001). tardigrades has also been reported (Westh and Assuming that this applies to tardigrade cells also Ramløv, 1991; Hengherr et al., 2007; Jönsson and and that the cell number of Richtersius coronifer is Persson, 2010), and indirectly confirmed in our comparable to that of Halobiotus crispae (1058 ± study by the observed doubling of two 53 cells/animal excluding gametes; Møbjerg et al., (unidentified) osmolytes following dehydration of 2011), the estimated number of trehalose required R. coronifer (stitched square in Figs. 1, 2. would be about 5.6 × 1013 molecules per animal. Chromatograms of dehydrated animals are not Trehalose is accumulated to 2.3% of the dry shown). weight of R. coronifer (Westh and Ramløv, 1991), and using the measured dry weight of 2.9 µg per Cryptobiotic species contain large fraction of animal (Westh and Ramløv, 1991) a single unidentified solutes individual accumulates on average 6.67 × 10-8 g As evidenced by the differences between the trehalose. With a molecular weight of 342.3 g/mol calculated ionic concentrations of the known ions this corresponds to 1.96 × 10-10 mol per animal, and the measured total osmolalities in the and by multiplying with Avogadro’s constant different species (Fig. 3A, Table 3), it is inferred (6.023 × 1023 molecules per mol) this equals 1.18 that cryptobiotic tardigrades contain a large × 1014 trehalose molecules per animal, which is fraction of unidentified organic osmolytes. twice the estimated number of molecules required Because the osmotic deficits were restricted to for protection against dehydration. In fact, the cryptobiotic species, it is reasonable to assume calculated number of trehalose molecules is that the fraction of organic solutes includes probably several times higher than that required, elements associated with cryptobiotic survival. as tardigrade cells are much smaller than murine Organic osmolytes fall into a few major fibroblasts, and therefore have a smaller total area categories (sugars, polyols, amino acids and of membranes to be protected. However, trehalose various derivatives) and appear universally is only accumulated in significant amounts in exploited by both plants and animals (Yancey, selected species (Hengherr et al., 2007; Jönsson 2005). Several chemical compounds of the above and Persson, 2010), which suggests that a diverse groups have been shown to have protective pattern of dehydration mechanisms have evolved function during osmotic stress (Hincha and in Tardigrada. Accordingly, these as yet Hagemann, 2004; Yancey, 2005). The unidentified biochemical pathways, would have to demonstration of survival during extreme osmotic be identified and characterized in order to obtain a conditions – in both dehydrated and active states profound insight into the metabolic and chemical (Halberg et al., 2009b; Møbjerg et al., 2011) – mechanisms of cryptobiosis. Inorganic ion composition in Tardigrada nematodes, crustaceans, in inves the concentration in of internal each Table 5.
Total osmotic concentration (mOsm/ concentration Total osmotic sects and onychophorans is included fo is included and onychophorans sects tigated species of tardigrades. Correspondi species of tardigrades. tigated kg) of the external medium and internal body body and internal the external medium kg) of r comparative purposes ng data on hemolymph concentration and co and concentration hemolymph on ng data . TR, terrestrial; fluids, as well the ─ , not measured. , not measured. osmotic contribution (%) contribution osmotic mposition of selected species of selected species of mposition of the respective ions to the K. A. Halberg and others
We would like to thank Anne Lise Maarup for technical Halberg, K. A. & Møbjerg, N. (2012). First evidence of assistance and Reinhardt Møbjerg Kristensen (Natural History epithelial transport in tardigrades: Comparative Museum of Denmark) for loan of the Olympus BX 51 investigation of organic anion transport. J. Exp. Biol., microscope. Station Linné (Porten til Alvaret), Ölands Skogsby, Sweden is warmly thanked for accommodation during sampling 215:497-507. of tardigrades. Funding came from the Carlsberg Foundation Halberg K. A., Persson, D., Jørgensen, A. Kristensen, and the Freja-Programme (Faculty of Science, University of R. M. and Møbjerg, N. submitted. Population Copenhagen). dynamics of a marine tardigrade: Temperature limits geographical distribution of Halobiotus crispae. Mar. Biol. Res. Hengherr, S., Heyer, A. G., Köhler, H. R. & Schill, R. LIST OF ABBREVIATIONS (2009). Trehalose and anhydrobiosis in tardigrades – FPD freezing point depression evidence for divergence in response to dehydration. HPAEC high-performance anion-exchange chromatography IC ion chromatography FEBS. J., 275:281-288. MW moss water Hincha, D. K. & Hagemann, M. (2004). Stabilization SW salt water of model membranes during drying by compatible solutes involved in the stress tolerance of plants and microorganisms. Biochem. J. 383:277-283. Hobsen, A. D., Stephenson, W. and Eden A. (1952). REFERENCES Studies on the physiology of Ascaris lumbricoides: Campiglia, S. (1976). The blood of Peripatus acacioi II. The inorganic composition of the body fluid in Marcus & Marcus (Onychophora) – III. The ionic relation to that of the environment. J. Exp. Biol., composition of the hemolymph. Comp. Biochem. 29:22-29. Physiol., 54(A):129-133. Hronowski, L. & Armstrong, J. B. (1977). Ion Chen, T., Acker, J. P., Eroglu, A. flere authors composition of the plasma of Ambystoma (2001). Beneficial effect of intracellular trehalose on mexicanum. Comp. Biochem. Physiol. A, 58:181-183. the membrane integrity of dried mammalian cells. Jönsson, K. I. & Persson, O. (2010). Trehalose in three Cryobiol. 43:168-181. species of desiccation tolerant tardigrades. Open Crowe, J. H., Crowe, L. M., Carpenter, J. F. and Zool. J., 3:1-5. Wistrom, C. A. (1987). Stabilization of dry Jørgensen, A., Faurby, S., Hansen, J. G., Møbjerg, N. phospholipid bilayers and proteins by sugars. and Kristensen, R. M. (2010). Molecular phylogeny Biochem. J., 242:1-10. of Arthrotardigrada (Tardigrada). Mol. Phylogen. Bird, A. F., McClure, S. G. (1997). Composition of the Evol., 54:1006-1015. stylets of the tardigrade, Macrobiotus cf. Normant, M., Kubicka, M., Lapucki, T., Czarnowski, pseudohufelandi. Trans R Soc. S Aust., 121:43-50. W. and Michalowska M. (2005). Osmotic and ionic Eagers, R. Y. (1969). Toxic properties of inorganic haemolymph concentration in the Baltic Sea fluoride compounds. Elsevier, Amsterdam London amphipod Gammarus oceanicus in relation to water New York, 382 pp. salinity. Comp. Biochem. Physiol. A, 141:94-99. Granat, L. (1972). On the relation between pH and the Macallum, A. B. (1910). The inorganic composition of chemical composition in atmospheric precipitation. the blood in vertebrates and invertebrates, and its Tellus XXIV, 6. origin. Proc. R. Soc. Lond. B, 82(559):602-624. Guidetti, R., Altiero, T. & Rebbecchi, L. (2010). On Møbjerg N, Dahl C. (1996). Studies on the morphology dormancy strategies in tardigrades. J. Insec. and ultrastructure of the Malpighian tubules of Physiol., 57(5):567-576. Halobiotus crispae Kristensen, 1982 (Eutardigrada). Guidette, R., Schill, R. O., Bertolani, R., Dandekar Zool. J. Linn. Soc., 116:85-99 T. & Wolf, M. (2009). New molecular data for Møbjerg, N., A. Jørgensen, J. Eibye-Jacobsen, K. A. tardigrade phylogeny, with the erection of Halberg, D. Persson & R. M. Kristensen (2007). Paramacrobiotus gen. nov. J. Zool. Syst. Ecol. Res., New Records on cyclomorphosis in the marine 47(4):315-321. eutardigrade Halobiotus crispae (Eutardigrada: Halberg, K. A., Persson D., Møbjerg N., Wanninger Hypsibiidae). J. Limnol., 66 (suppl. 1): 132-140. A. & Kristensen R. M. (2009a). Myoanatomy of Møbjerg, N. M., Halberg, K. A., Persson., D., the Marine Tardigrade Halobiotus crispae Jørgensen, A. & Kristensen R. M. (2011). Survival (Eutardigrada: Hypsibiidae). J. Morphol., 270:996- in extreme environments – on current knowledge of 1013. adaptations in tardigrades. Acta Physiol., 202: 409- Halberg, K. A., Persson, D., Ramløv, H., Westh, P., 420. Kristensen, R. M. & Møbjerg, N. (2009b). Persson, D., Halberg K. A., Jørgensen A., Ricci C., Cyclomorphosis in Tardigrada: Adaption to Møbjerg N. & Kristensen R. M. (2010). Extreme environmental constraints. Journal of Experimental stress tolerance in tardigrades: Surviving space Biology, 212:2803-2811. Inorganic ion composition in Tardigrada
conditions in low earth orbit. J. Zool. Syst. Evol. Res., 49: 90-97. Persson, D., Halberg K. A., Jørgensen A., Møbjerg N. & Kristensen R. M. (2012). Neuroanatomy of Halobiotus crispae: Tardigrade brain structure suggests inclusion into Panarthropoda. J. Morphol. (in review). Robertson, J. D. (1949). Ionic regulation in some marine invertebrates. J. Exp. Biol., 26:182-200. Robertson, J. D. (1954). The chemical composition of the blood of some aquatic chordates, including members of the Tunicata, Cyclostomata and Osteichthyes. J. Exp. Biol., 31:424-442. Sands, M, Nicol, S. & McMinn, A. (1998). Fluoride in Antarctic marine crustaceans. Mar. Biol., 132:591- 598. Smith R. I. L. (1978). Summer and winter concentrations of sodium, potassium and calcium in some maritime Antarctic cryptogams. J. Ecol., 66 (3):891-909. Sutcliffe, D. W. (1962). The composition of haemolymph in aquatic insects. J. Exp. Biol., 39:325-343. Sutcliffe, D. W. (1963). The chemical composition of haemolymph in insects and some other arthropods, in relation to their phylogeny. Comp. Biochem. Physiol., 9(2):121-135. Tentori E. and Lockwood, A. P. M. (1990). Haemolymph magnesium levels in some oceanic crustaceans. Comp. Biochem. Physiol. A, 4:545-548. Wilder, M. N., Ikuta, K., Atmomarsono M., Hatta, T. and Komuro, K. (1998). Changes in osmotic and ionic concentrations in the hemolymph of Macrobrachium rosenbergii exposed to varying salinities and correlation to ionic and crystalline composition of the cuticle. Comp. Biochem. Physiol. A, 119:941-950. Wyatt, G. R. (1961). The biochemistry of insect hemolymph. Ann. Rev. Entomol., 6:75-102. Westh, P. and Kristensen, R. M. (1992). Ice formation in the freeze-tolerant eutardigrades Adorybiotus coronifer and Amphibolus nebulosus studied by differential scanning calorimetry. Polar Biol. 12:693-699. Westh, P. and Ramløv, H. (1991). Trehalose accumulation in the tardigrade Adorybiotus coronifer during anhydrobiosis. J. Exp. Zool. 258:303-311. Yancey, P. H. (2005). Organic osmolytes as compatible, metabolic and counteracting cytoprotectants in high osmolarity and other stresses. J. Exp. Biol., 208:2819-2830.
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The Journal of Experimental Biology 215, 497-507 © 2012. Published by The Company of Biologists Ltd doi:10.1242/jeb.065987
RESEARCH ARTICLE First evidence of epithelial transport in tardigrades: a comparative investigation of organic anion transport
Kenneth Agerlin Halberg* and Nadja Møbjerg Department of Biology, The August Krogh Building, University of Copenhagen, Universitetsparken 13, DK-2100 Copenhagen Ø, Denmark *Author for correspondence ([email protected])
Accepted 31 October 2011
SUMMARY We investigated transport of the organic anion Chlorophenol Red (CPR) in the tardigrade Halobiotus crispae using a new method for quantifying non-fluorescent dyes. We compared the results acquired from the tardigrade with CPR transport data obtained from Malpighian tubules of the desert locust Schistocerca gregaria. CPR accumulated in the midgut lumen of H. crispae, indicating that organic anion transport takes place here. Our results show that CPR transport is inhibited by the mitochondrial un-coupler DNP (1mmoll–1; 81% reduction), the Na+/K+-ATPase inhibitor ouabain (10mmoll–1; 21% reduction) and the vacuolar H+-ATPase inhibitor bafilomycin (5mmoll–1; 21% reduction), and by the organic anions PAH (10mmoll–1; 44% reduction) and probenecid (10mmoll–1; 61% reduction, concentration-dependent inhibition). Transport by locust Malpighian tubules exhibits a similar pharmacological profile, albeit with markedly higher concentrations of CPR being reached in S. gregaria. Immunolocalization of the Na+/K+-ATPase -subunit in S. gregaria revealed that this transporter is abundantly expressed and localized to the basal cell membranes. Immunolocalization data could not be obtained from H. crispae. Our results indicate that organic anion secretion by the tardigrade midgut is transporter mediated with likely candidates for the basolateral entry step being members of the Oat and/or Oatp transporter families. From our results, we cautiously suggest that apical H+ and possibly basal Na+/K+ pumps provide the driving force for the transport; the exact coupling between electrochemical gradients generated by the pumps and transport of ions, as well as the nature of the apical exit step, are unknown. This study is, to our knowledge, the first to show active epithelial transport in tardigrades. Key words: organic anion transport, Chlorophenol Red, 2,4-dinitrophenol, ouabain, bafilomycin, probenecid, para-aminohippuric acid, tardigrade, insect, V-type H+-ATPase, Na+/K+-ATPase, Malpighian tubule.
INTRODUCTION specialized reproductive and excretory organs (Dewel and Dewel, The ability to excrete metabolic waste products as well as 1979; Rebecchi and Bertolani, 1994; Møbjerg and Dahl, 1996; environmental toxins (xenobiotics) is a fundamental prerequisite Schmidt-Raesa and Kulessa, 2007; Pelzer et al., 2007; Zantke et al., for animal life. One of the earliest identified systems involved in 2008; Halberg et al., 2009a; Møbjerg et al., 2011; Rost-Roszkowska such an excretion is the classic organic anion transport system et al., 2011). The alimentary canal can be divided into several (Marshall and Vickers, 1923). In vertebrates, this system is morphologically distinct regions i.e. bucco-pharyngeal apparatus, (especially) well known in the proximal tubule where it rids the oesophagus, midgut and hindgut, with the Malpighian tubules (MTs) organism of various xenobiotic and endobiotic compounds, of eutardigrades positioned at the junction between these last two through an ATP-dependent, net transepithelial secretory pathway sections. Interestingly, the same basic organizational pattern is found (reviewed by Dantzler, 2002; Burckardt and Burckardt, 2003; in insects, and has been used as a strong argument for the homology Russel, 2010). The importance and understanding of similar of these two organ systems (Greven, 1982; Møbjerg and Dahl, 1996). transport activities in various invertebrate phyla, however, is Among multi-cellular animals, tardigrades exhibit an extraordinary extremely limited. In this study, we expand on the current ability to resist environmental extremes, and are known to survive knowledge by investigating organic anion transport in the conditions greatly exceeding those encountered in their natural habitat tardigrade Halobiotus crispae (Tardigrada), as compared with the – even in space (Jönsson et al., 2008; Rebecchi et al., 2008; Persson desert locust Schistocerca gregaria (Arthropoda). et al., 2011). The biochemical and physiological mechanisms The phylum Tardigrada consists of a group of minute, eight-legged, mediating this unique tolerance, however, remain largely unidentified. multicellular animals that, like arthropods and nematodes, belong to Previously, we have shown that the marine eutardigrade H. crispae the invertebrate superclade Ecdyzosoa (Aguinaldo et al., 1997). They tolerates large changes in external salinity surviving periods of osmotic are considered essential to our understanding of early metazoan stress by maintaining haemolymph osmotic pressure above that of evolution, yet fundamental questions concerning their basic biology the external medium (Halberg et al., 2009b); an adaptive mechanism remain unanswered (Møbjerg et al., 2011). In spite of their small size likely present in all eutardigrades (Møbjerg et al., 2011). Here, we (~50–1200mm), tardigrades are relatively complex animals; they are identify organs involved in transepithelial transport of organic anions composed of >1000 cells, and possess a well-developed musculature and investigate the transport characteristics with the aim of providing and nervous system, as well as a complex alimentary canal and a better understanding of the unique biology in these animals.
THE JOURNAL OF EXPERIMENTAL BIOLOGY 498 K. A. Halberg and N. Møbjerg
Organic anion transport has previously been described in other groups of invertebrates (George et al., 1999; Torrie et al., 2004; 6000 Faria et al., 2010). Notably, the alimentary canal and MTs of insects, pH 11 r2=0.996 which collectively form the functional analogue of the vertebrate 5000 kidney, have been studied (reviewed by Phillips, 1981; O’Donnell pH 7–10 r2=0.987 et al., 2003; Dow and Davies, 2006). As in vertebrates, the excretory 4000 organs of insects transport a wide range of organic solutes and pH 6 r2 exogenous toxins through organic anion transporters (Oats), organic 3000 =0.994 anion-transporting peptides (Oatps), P-glycoproteins (Mdr/P-gp) as 2000 well as multidrug resistance-associated proteins (Mrps) (Maddrell relationship (%) et al., 1974; Bresler et al., 1990; Lanning et al., 1996; Linton and O’Donnell, 2000; Torrie et al., 2004; Neufeld et al., 2005; Leader 1000 and O’Donnell, 2005; O’Donnell and Leader, 2006; Chahine and O’Donnell, 2009; Chahine and O’Donnell, 2010). Organic anions 0
Difference in red spectrum/green spectrum Difference 0 1 2 3 4 5 are divided into type I and type II organic anions, on the basis of –1 structural and chemical properties (e.g. Wright and Dantzler, 2004). [CPR] (mmol l ) The different groups of transporters vary in their transport Fig.1. Standard curves showing the percentage difference in the red mechanisms, but overlap in their substrate specificity, as they spectrum/green spectrum relationship as a function of Chlorophenol Red (CPR) concentration at different pH values (pH6, 7–10 and 11). The curves transport carboxylates and sulphonates interchangeably (Neufeld et were fitted by regression analysis using OriginPro 7.5 with a third order al., 2005; Chahine and O’Donnell, 2009). Oats and Oatps (solute polynomial providing the best fit with r2 values close to unity. carriers belonging to the SLC22 and SLC21/SLCO family) transport both small (<400–500Da) hydrophilic type I organic anions (Oats) and large (>450Da) hydrophobic type II organic anions (Oatps), changes in spectral light to that of dye concentration (Fig.1). As whereas Mdr/P-gp and Mrps (ABC transporters, ABCB and ABCC CPR exhibits a pH-dependent shift in colour (from yellow to violet) subfamilies) generally transport large (>500Da) polyvalent type II between pH4.6 and 7.0, and a secondary shift (to purple) at pH>10, organic anions (Wright and Dantzler, 2004; Russel, 2010). From a standard curve was constructed at three discrete colours relevant the insect’s perspective, the clearance of exogenous toxins is of to our investigation (red, violet and purple corresponding to particular interest, as insects often live in environments with high pH6–11). This was done in order to correct for potential pH xenobiotic exposure, potentially at harmful or lethal concentrations. dependent effects on CPR quantification caused by the tissue. The Accordingly, they are forced to process naturally occurring plant standard curves were constructed from optical analysis of toxins (Torrie et al., 2004; Neufeld et al., 2005), as well as micrographs taken of samples (40ml) with known dye concentrations anthropogenic contaminants, such as insecticides (Lanning et al., (ranging from 0.1 to 5mmoll–1) at each respective pH value. The 1996; Neufeld et al., 2005; Buss and Callaghan, 2008). The optical measurements provided relative, arbitrary values for the light physiological importance of this detoxification system – and intensities of the red, green and blue spectrum of spectral light from implicitly the MTs – is emphasized by the fact that transcripts for each sample, and were acquired using the image analysis and these transporters are enriched in the transcriptome of the MTs visualization software Imaris 6.4 (Bitplane, Zurich, Switzerland). (Wang et al., 2004), and because the expression of several Oatp and The standard curves are expressed as percentage difference in the Mdr transporters is significantly upregulated upon dietary exposure red spectrum/green spectrum relationship as a function of CPR to Oatp and Mdr substrates (Mulenga et al., 2008; Chahine and concentration (Fig.1). The curves were fitted by regression analysis O’Donnell, 2009; Chahine and O’Donnell, 2010). Indeed, it has been using OriginPro 7.5 (OriginLab, Northampton, MA, USA) with a suggested that organic solute excretion is the most significant third order polynomial providing the best fit with r2 values close to function of the insect MT (Dow and Davies, 2006). Nevertheless, unity. The CPR concentration in a given tissue was subsequently in spite of significant efforts in the past decades, the mechanisms calculated by employing the appropriate standard curve. The underlying transepithelial transport of organic anions is far from standard curve was chosen by visually comparing the colour of the understood, and our knowledge is limited to relatively few taxa. accumulated CPR with that of the respective standard curves. In this study we examined epithelial transport in tardigrades. Contrary to our expectations, the midgut of H. crispae was the Using a comparative approach, we investigated the sites, only organ in which CPR accumulation was clearly visualized. characteristics and pharmacological profile of the net transepithelial No accumulation was observed in the tardigrade MTs. As such, transport of Chlorophenol Red (CPR; 3Ј,3Љ-dichlorophenol- quantification of dye accumulation was only performed from the sulphone-phthalein), a pH indicator and a prototypic substrate of tardigrade midgut, and compared with the accumulation in the the classic organic anion secretory pathway, in the tardigrade H. MTs of S. gregaria. Specifically, 6–12 regions from areas of the crispae and the desert locust S. gregaria. Our results show that the tardigrade midgut containing the highest dye intensity were tardigrade midgut is the principal site of CPR transport, and that selected arbitrarily, in addition to a similar number from the this transport is active and transporter mediated. Additionally, our adjacent haemolymph, while four different regions were selected data show that the pharmacological profiles of CPR transport in the from each insect MT. Each region selected represented a circle tardigrade midgut and locust MT are surprisingly similar. with a diameter of 5mm for H. crispae and 25mm for S. gregaria. The average light intensity within these circles was measured by MATERIALS AND METHODS the Imaris program. Averaging the measured intensity of all Quantification of CPR accumulation selected regions provided an overall average intensity for the red, The quantification of CPR accumulation was performed by green and blue colour spectrum within each investigated organ introducing a new method for quantifying non-fluorescent dyes. The following each exposure. As CPR predominantly appears red (to method exploits the optical properties of CPR by relating relative violet) in the midgut of H. crispae and in the MTs of S. gregaria,
THE JOURNAL OF EXPERIMENTAL BIOLOGY Epithelial transport in tardigrades 499 the red spectrum/green spectrum relationship offered an estimate A 1 μmol l–1 10 μmol l–1 100 μmol l–1 1 mmol l–1 5 mmol l–1 of dye accumulation, as calculated from the appropriate standard curve. The final CPR concentration was normalized according to tc tc the background light intensity, i.e. the tardigrade haemolymph or tc lu lu lulu lu untreated (control) insect MTs. For tardigrades, only regions lu tc without gut content were selected for quantification, in order to avoid the influence of gut content on the wavelength of captured B 2.2 light. Deviations in animal depth did not influence CPR –1 Km=81.8 μmol l 2.0 –1 quantification within the variation encountered in this study. The Vmax=1.58 mmol l MTs of S. gregaria consist of three structurally distinct regions, 1.8 i.e. proximal, middle and distal relative to the gut (Garret et al., ) 1.6 1988). Dye accumulation was estimated from the proximal region –1 1.4 and parts of the middle region within 5mm of the junction with 1.2 200 the gut, as dye accumulation was highest here. (mmol l 1.0 150
lumen Test solutions 0.8 The haemolymph osmolality of H. crispae, kept at a salinity of 100
[CPR] 0.6 20p.p.t., was previously measured by nanolitre osmometry to 50 ~950mOsmkg–1 (Halberg et al., 2009b). At present we do not know 0.4 Lumen/bath ratio 0 the composition of tardigrade extracellular fluids. As such, the 0.2 0 0.5 1 5 experimental solution (control solution) was prepared from 0 evaporative reduction of seawater (SW; salinity 20p.p.t., pH8) 0 1 2 3 4 5 collected at the locality, and 35mmoll–1 glucose was added to [CPR] (mmol l–1) alleviate potential variation in experiments caused by differences bath in nutrient availability. This yielded a final measured osmolality of 950±3mOsmkg–1 (N3). For S. gregaria an insect saline (control Fig.2. Accumulation of CPR as a function of external CPR concentration in solution) was prepared containing (in mmoll–1): 130 NaCl, 10 KCl, Malpighian tubules (MTs) of Schistocerca gregaria. (A)Representative light micrographs of the MTs following exposure to different concentrations 4 NaHCO3, 2 MgSO4, 2 CaCl2, 6 NaH2PO4, 35 glucose and 5 Hepes, (1 mol l–1, 10 mol l–1, 100 mol l–1, 1 mmol l–1 and 5 mmol l–1) of CPR. –1 m m m titrated to pH7.2, with a measured osmolality of 336±2mOsmkg Scale bars, 100mm. lu, lumen; tc, trachea. (B)Luminal CPR concentration (N3). as a function of bath CPR concentration, revealing the kinetic parameters In order to explore the kinetics of CPR transport by MTs of S. Km and Vmax for CPR transport. Each point shows the mean ± s.d. for gregaria, a concentration–response curve was constructed over a N4–6 animals with 3–5 MTs providing the estimate for each animal. The 5000-fold range of CPR concentrations (1mmoll–1 to 5mmoll–1) solid line represents the fit to the Michaelis–Menten equation by non-linear regression analysis (using error as weight). Insert shows the lumen/bath (Fig.2). These data revealed that CPR transport is saturated at an –1 –1 ratio of CPR as a function of external CPR concentration. external CPR concentration of ~1.6mmoll (Vmax1.58mmoll , –1 Km81.8mmoll ; Fig.2). However, the MTs are unable to concentrate the dye at high concentrations of CPR (>1mmoll–1; Fig.2, inset). Experiments, on both animals, were performed at a Specimens of S. gregaria Forskål 1775 were acquired from a concentration of 1mmoll–1 CPR. specialized animal shop (www.exopark.dk), and kept at room Test solutions were prepared from the two control solutions temperature (RT) with light:dark periods of 16h:8h and fed annual containing 1mmoll–1 CPR, and one of the following inhibitors: 2,4- meadow grass (Poa annua) ad libitum. dinitrophenol (DNP, 1mmoll–1), ouabain (10mmoll–1), bafilomycin –1 –1 A1 (5mmoll ), para-aminohippuric acid (PAH; 10mmoll ) or Exposure to test solutions probenecid (0.1–10mmoll–1). The final osmolality of the solutions Halobiotus crispae was measured on a Vapro 5520 vapour pressure osmometer (Wescor, Evaluation of CPR transport by tardigrade epithelia was performed Logan, UT, USA). All solutions were titrated with NaOH to pH8 on whole animals immersed in the dye solution. Data obtained from for H. crispae and pH7.2 for S. gregaria. 82 animals were used for the study – no distinction was made between male and female specimens. Initial observations revealed Experimental animals that the animals did not take up dye through the mouth or cuticle Specimens of H. crispae Kristensen 1982 were collected on 11 (CPR non-punctured, Fig.3) and test solutions were therefore February 2008 and 17 January 2010 at Vellerup Vig, Isefjord, introduced to the haemolymph of single specimens (length Denmark (55°44.206ЈN, 11°51.258ЈE) (see Fig.3A). Bottom samples 300–500mm) through a small hole made in the cuticle in the anterior were collected with a mini van Veen grab at a depth of 1–2m (salinity part of the animal. The animal was incubated for a period of 60min ~20p.p.t., pH8). Rocks, algae and sediment collected with the grab at RT in the respective test solution, and quickly washed in SW were freshwater shocked. The debris was decanted into a conical net prior to photography. Light micrographs of the specimens were taken (mesh size 63mm) and subsequently transferred to SW from the in bright-field at a ϫ40 magnification, using an Olympus DP20 locality and kept at 4°C. Animals in the active stage (see Kristensen, camera mounted on an Olympus BX50 microscope (Olympus, 1982; Møbjerg et al., 2007; Halberg et al., 2009b) were identified Hamburg, Germany). Additionally, in order to investigate whether using a dissection microscope. The tardigrades were kept for a period the test solutions were ingested during the experimental period, intact of up to 6months at 4°C in SW (salinity 20p.p.t., pH8) and regularly non-punctured animals were incubated in the CPR test solution for supplied with fresh substrate, consisting mainly of sediment, organic a corresponding period. The animals were washed and photographed debris, filamentous algae and diatoms. as described above.
THE JOURNAL OF EXPERIMENTAL BIOLOGY 500 K. A. Halberg and N. Møbjerg
+Bafilomycin Fig. 3. CPR accumulation in the gut lumen of Halobiotus crispae, SW CPR non- +DNP +Ouabain +DMSO +PAH +Probenecid control punctured CPR –81% –21% –21% –44% –61% and the effect of inhibitors on dye accumulation. (A)Light B nn nn micrograph of H. crispae from a ventral view showing the animalʼs basic morphology. mg, midgut. Asterisks indicate MTs. Scale bar, mg mg mg mg mg mg mg mg 100mm. (B)Representative light micrographs of the midgut (mg) following exposure to the various test solutions. Seawater control shows the midgut of a punctured animal following immersion in 1.6 C A seawater, while CPR non-punctured shows the midgut of an intact animal after immersion in CPR solutions. Estimations of luminal 1.4 Leg 1 CPR concentration were performed solely from areas devoid of gut content, i.e. brown material in the gut. The percentage change in CPR concentration, compared with experiments on CPR alone, is ) 1.2 mg Leg 2
–1 noted. Scale bars, 50mm. (C)Corresponding luminal concentrations Leg 3 of CPR. Data are depicted as means ± s.d. Asterisks refer to a 1.0 * * * significant difference from CPR alone (*P<0.05, significant;
(mmol l 0.8 (13) **P<0.01, highly significant). Numbers in parentheses indicate the Leg 4 number of animals tested.
luminal * 0.6 (6)* (8) **
[CPR] (11) 0.4 ** ** (10) 0.2 (5) (12) (6) 0
DNP PAH –1 CPR –1 –1 –1 ouabain SW control bafilomycin –1 –1 probenecid 1 mmol l +1 mmol l +10 mmol l CPR non-punctured +10 mmol l +5 μmol l +10 mmol l A separate experiment was performed to evaluate whole-organism MTs of S. gregaria were fixed for 60min at RT in an aldehyde activity of H. crispae following puncture of the cuticle and exposure fixative containing: 1.2% glutaraldehyde, 1% paraformaldehyde, to a pure SW control and the various test solutions, following the 0.05moll–1 sucrose and 0.05moll–1 sodium cacodylate buffer procedure described above. The animals were scored with a (pH7.4) and subsequently rinsed and stored in 0.05moll–1 sodium numerical value according to their activity, which was defined as: cacodylate buffer with 0.05moll–1 sucrose. Following 1h post- –1 0, no movement discerned; +1, small movement of leg or claw; +2, fixation in 2% OsO4 with 0.1moll sodium cacodylate, tubules clear movement of body and extremities. Thirty specimens were were dehydrated through a graded series of ethanol and used for each test solution, and a cumulative score was given for propylenoxide and embedded in Araldite®. Semi-thin sections each group (see Fig.4). were cut on a Leica ultramicrotome EM UC6 (Leica,
Schistocerca gregaria 60 The entire alimentary canal including ~233 MTs (Garret el al., 1988) * Clear was dissected from adult specimens (see Fig. 5A) (imago females movement and males; 2–10 days post-fifth instar nymph) under insect saline; 94 45 animals were used in total. Prior to transfer into the test solutions, Small 30 several MTs were randomly chosen and removed, and micrographs * movement were taken in order to acquire an estimate of the background light intensity for each animal. The background light intensity was later Activity score 15 used for normalizing the estimate of the CPR concentration (see * * No movement above). The gut systems were incubated in the respective test 0 solutions for 60min at RT. Following a quick rinse in insect saline, CPR DNP –1 –1 –1 PAH individual MTs representative of overall dye intensity were –1 ouabain SW control bafilomycin –1 –1 probenecid subsequently isolated under microscope (Zeiss Stemi 200-CS, Carl Not punctured 1 mmol l +1 mmol l Zeiss International, Oberkochen, Germany), and prepared for +10 mmol l +10 mmol l photography. MTs obviously damaged during dissection (i.e. that did +5 μmol l not accumulate CPR) were avoided. Details pertaining to the method +10 mmol l of photography were as described above. Five to 11 locusts with 3–5 Fig.4. Animal activity of H. crispae (with punctured cuticle) following MTs per specimen were used in estimations of the CPR concentration exposure to test solutions. Thirty animals were tested for each exposure. for each exposure; a minimum of 20 and a maximum of 40 MTs Each animal was scored with a numerical value according to their activity, were analysed in total for each test solution. defined as: 0, no movement discerned; +1, small movement of leg or claw; +2, clear movement of body and extremities. A cumulative score was given for each group. The statistical significance of differences in activity score Midgut and MT structure and immunostaining was tested using Mann–Whitneyʼs U-test. Asterisks refer to significant Whole animals of H. crispae and MTs dissected from S. gregaria difference from 1mmoll–1 CPR (no asterisk, P>0.05, not significant; were prepared for structural investigation and immunostaining. *P<0.05, significant).
THE JOURNAL OF EXPERIMENTAL BIOLOGY Epithelial transport in tardigrades 501
Microsystems, Wetzlar, Germany) with glass knives and Saline +DNP +Ouabain +Bafilomycin +PAH +Probenecid control CPR –80% –20% –26% –40% –77% subsequently stained with Toluidine Blue. B For immunocytochemistry, whole animals of H. crispae and MTs tc lu lu tc lu of S. gregaria were fixed in 3% paraformaldehyde in 0.1moll–1 lu lu tc tc tc tc lu lu sodium cacodylate buffer (pH7.4) for 60min and subsequently –1 transferred to 0.1moll sodium cacodylate buffer. The tissue was A then dehydrated through a graded series of ethanol and xylene, 1.6 C embedded in paraffin and sectioned into ~10mm sections, or (11) 1.4 transferred to PBS and used as whole mounts for immunostaining. (10)* Paraffin sections were deparaffinized through a graded series of xylene 1.2 (10)* Leg 3 Leg 2 Leg 1 and alcohol, washed in saline (control solution; see ‘Test solutions’ ) –1 ** above) and blocked with 10% normal goat serum (Invitrogen, 1.0 (9) Carlsbad, CA, USA) for 30min, prior to incubation with primary antibody. Paraffin sections, as well as whole mounts, were incubated (mmol l 0.8
overnight at 4°C in insect saline (MTs) or PBS (tardigrades) containing luminal 10% normal goat serum, 0.1% Triton-X and primary antibody. The 0.6
+ + [CPR] ** (8)** Na /K -ATPase -subunit monoclonal mouse primary antibody 5- 0.4 (8) IgG (10mgml–1) was developed by D. M. Famborough, and obtained from the Developmental Studies Hybridoma Bank (University of 0.2 Iowa, Iowa City, IA, USA). This antibody has been used to identify the Na+/K+-ATPase in numerous excretory tissues, including MTs of 0.0 Drosophila melanogaster (Lebovitz et al., 1989; Torrie et al., 2004), CPR DNP PAH the gills of the blue crab Callinectes sapidus (Towle et al., 2001) and –1 –1 –1 –1 ouabain bafilomycin the pronephros of Ambystoma mexicanum (Haugen et al., 2010). –1 probenecid Saline control –1 1 mmol l +1 mmol l Following an extensive wash in saline, the tissue was incubated with +10 mmol l +10 mmol l (anti-mouse) Alexa Fluor 594 (1:100) secondary antibody (Invitrogen) +5 μmol l overnight at 4°C. The tissue was rinsed with saline then counterstained +10 mmol l with Alexa Fluor 488-conjugated phalloidin (luminal marker; 1:40; –1 Fig.5. CPR accumulation in MTs of S. gregaria, and the effect of inhibitors Invitrogen) and DAPI (50mgml ; Invitrogen) for 2h, washed and on dye accumulation. (A)Photo of S. gregaria. Scale bar, 1cm. mounted on glass coverslips in Vectashield (Vector Laboratories Inc., (B)Representative light micrographs of the MTs from exposure to the Burlingame, CA, USA). Images were acquired using a Leica DM various test solutions. Control saline shows an MT prior to immersion in RXE 6 TL microscope equipped with a Leica TCS SP2 AOBS CPR solution. The percentage change in CPR concentration, compared confocal laser scanning unit (Leica Microsystems, Wetzlar, Germany). with experiments on CPR alone, is noted. Scale bars, 100mm. The tissue was scanned employing sequential scanning (setting: (C)Corresponding luminal concentration of CPR in the MTs. Asterisks refer to significant difference from 1mmoll–1 CPR alone (*P<0.05, significant; between frames) using the 488nm line of an argon/krypton laser and **P<0.01, highly significant). Numbers in parentheses indicate the number the 594nm line of a helium laser, in addition to the 405nm UV laser of animals tested. For S. gregaria, measurements on 3–5 MTs provided a line. The image series was processed and edited using Imaris software. mean for each animal. Confocal images are based on 240 optical sections of a Z-series performed at intervals of 0.7mm. Experiments were conducted multiple times with corresponding results. All control preparations performed solely on this structure (slight residual coloration was without primary antibody were negative for immunostaining. occasionally observed in the haemolymph). These results were compared with the accumulation in S. gregaria MTs. The luminal Chemicals concentration of CPR in the gut of H. crispae and in the MT of S. All chemicals were obtained from Sigma-Aldrich (St Louis, MO, gregaria when exposed to a 1mmoll–1 CPR solution, in the presence USA). Bafilomycin was dissolved and stored in dimethyl sulphoxide or absence of inhibitors, is shown in Figs3 and 5. Activity of H. crispae (DMSO). Inhibitors were allowed to dissolve in the CPR solution during the corresponding exposures is depicted in Fig.4. overnight prior to use. In H. crispae, areas void of gut contents appear transparent, whereas those with gut contents are a light to dark brown colour Statistics (Fig.3B, SW control). Only areas devoid of gut content were used Data are expressed as means ± s.d. unless otherwise stated. The for quantification of dye accumulation. In order to expose internal statistical significance of differences between the various exposures epithelia to the test solutions a small hole was made in the cuticle was tested using one-way ANOVA followed by a Tukey multiple in the anterior part of the animal. Although clearly affected by the comparisons of means. The statistical tests were performed using punctured cuticle compared with untreated specimens, animal the data analysis program OriginPro 7.5 (OriginLab). Significance activity was surprisingly high under control conditions, even 60min levels were P>0.05 (not significant), P<0.05 (significant, *) and after the small hole in the cuticle was made (Fig.4). This implies P<0.01 (highly significant, **). that the osmolality as well as the ionic composition of the used SW are within tolerable limits of extracellular fluid conditions. RESULTS When intact, non-punctured animals were exposed to the CPR accumulation 1mmoll–1 CPR solution, no internal CPR accumulation was evident, During our initial observations on CPR transport in punctured H. showing that the surrounding medium is not ingested by the animals crispae, dye accumulation was almost exclusively observed in the within the experimental period (Fig.3B). However, following tardigrade midgut, and for this reason subsequent analyses were exposure of punctured animals to the same 1mmoll–1 CPR solution,
THE JOURNAL OF EXPERIMENTAL BIOLOGY 502 K. A. Halberg and N. Møbjerg
+Bafilomycin +Bafilomycin Fig. 6. The effect of bafilomycin and dimethylsulphoxide (DMSO) on +DMSO +DMSO +DMSO +DMSO CPR –14% –21% CPR +5% –26% CPR accumulation. (A)Representative light micrographs of the A C tardigrade midgut (mg) following exposure to the test solutions. The percentage change in CPR concentration, compared with experiments with CPR alone, is noted. Scale bars, 50 m. mg mg gm lu tc m tc lu tc lu (B)Corresponding luminal concentration of CPR in midgut lumen. (C)Representative light micrographs of locust MTs following exposure to the test solutions. The percentage change in CPR ** concentration, compared with experiments on CPR alone, is noted. 1.6 B 1.6 D ** Scale bars, 100mm. (D)Corresponding luminal concentration of (11) CPR in the MTs. Asterisks refer to significant difference from (10) –1 1.4 1.4 1mmoll CPR alone (*P<0.05, significant; **P<0.01, highly significant). Numbers in parentheses indicate the number of animals tested. For S. gregaria, measurements on 3–5 MTs 1.2 1.2 (8) ) provided a mean for each animal. –1 ** 1.0 * 1.0 (13) (mmol l 0.8 * 0.8
lumen 0.6 (5) (8) 0.6
[CPR] 0.4 0.4
0.2 0.2
0 0
CPR –1 –1 CPR
bafilomycin –1 –1 bafilomycin 1 mmol l +DMSO (0.5%) 1 mmol l +DMSO (0.5%) μmol l +DMSO (0.5%) +DMSO (0.5%) +5 μmol l +5 dye accumulation was readily visible in the midgut lumen, experiment showed that the observed inhibition is partly due to suggesting that organic anion transport is mediated by the midgut DMSO – see below). Although the mean CPR concentration in the epithelium; CPR concentration in the midgut lumen reached a mean presence of bafiolmycin A1 was higher in S. gregaria, i.e. of 0.68±0.1mmoll–1 (Fig.3B,C). Similarly, dye accumulation was 0.97±0.18mmoll–1 (Fig.5), a corresponding 26% reduction was evident in the lumen of the insect MTs, reaching a mean CPR observed. The activity of H. crispae was markedly affected by –1 concentration of 1.3±0.13mmoll (Fig.5B,C). bafilomycin A1, with most animals showing movements only DNP is a mitochondrial un-coupler that inhibits mitochondrial following tactile stimuli (Fig.4). Notably, visual colour changes to ATP production. For H. crispae, ~81% reduction in the mean CPR CPR were observed (i.e. the dye turned purple) in some specimens concentration was detected in experiments using DNP, resulting in immediately after transfer to SW, and in all animals 10min post- a midgut CPR concentration of only 0.1±0.07mmoll–1 (Fig.3). The exposure, suggesting an alkalization of the midgut content, which tardigrades almost all became passive (Fig.4), indicating that a range is consistent with the specific inhibition of an apical H+-ATPase. of tissues was affected by the DNP application. In comparison, a Because bafilomycin was dissolved in DMSO, we tested whether similar reduction of ~80% was observed in the MTs of S. gregaria, the used concentrations of DMSO (0.5%) had an effect on CPR with CPR concentrations of 0.26±0.12mmoll–1 (Fig.5). This finding accumulation in both animals. In S. gregaria, no significant change shows that CPR accumulation is ATP dependent. The Na+/K+- in CPR accumulation was detected (Fig.6C,D), but in H. crispae, ATPase and vacuolar H+-ATPase are likely ATP-consuming a significant change was observed in the presence of 0.5% DMSO candidates, which could energize transepithelial dye transport. We (Fig.6A,B). A significant difference between 0.5% DMSO-treated therefore investigated CPR transport during applications of known animals and 0.5% DMSO + bafilomycin-treated specimens, pump inhibitors. however, was also detected (Fig.6A,B), revealing that the observed Solutions containing ouabain, a plant alkaloid that binds to and inhibition is only partly caused by bafilomycin in H. crispae. The inhibits the Na+/K+-ATPase, revealed a significant effect on CPR observation that DMSO has an effect on CPR transport in tardigrades transport in both H. crispae and S. gregaria. The mean CPR is in contrast to previous reports from insects, stating that a concentration was 0.44±0.11mmoll–1 (Fig.3) in H. crispae, which concentration of DMSO below 1% has no effect on the fluid is a 21% reduction in luminal CPR concentration, and secretion rate in the MTs of Drosophila (Linton and O’Donnell, 1.04±0.19mmoll–1 (Fig.5) in S. gregaria, corresponding to ~20% 2000). reduction. Activity of H. crispae was not affected by this test solution Furthermore, we investigated the impact of two well-known (Fig.4). substrates of organic anion transporters, PAH and probenecid, on + The vacuolar H -ATPase inhibitor bafilomycin A1 similarly the ability to accumulate CPR. Both PAH and probenecid are type affected CPR transport significantly, showing a mean CPR I organic anions (carboxylates), which appeared to reduce the CPR concentration of 0.44±0.13mmoll–1 (Fig.3) in H. crispae, which is concentration in our pilot experiments on both H. crispae and S. a 21% reduction compared with animals treated with CPR alone gregaria. Addition of 10mmoll–1 PAH caused a reduction of ~44% (note, bafilomycin was dissolved in DMSO, and a control in luminal CPR concentration in H. crispae and ~40% in S.
THE JOURNAL OF EXPERIMENTAL BIOLOGY Epithelial transport in tardigrades 503
+0.1 mmol l–1 +1 mmol l–1 +10 mmol l–1 +0.1 mmol l–1 +1 mmol l–1 +10 mmol l–1 Fig.7. Titration of the inhibitory effect of CPR –26% –56% –61% CPR –9% –47% –77% probenecid. (A)Representative light A CPR C micrographs of the tardigrade midgut (mg) lu following exposure to the different mg –1 mg mg mg lu lu lu tc concentrations (0.1, 1 and 10mmoll ) of tc probenecid. The percentage change in CPR concentration, compared with experiments with CPR alone, is noted. Scale bars, 50mm. ** (B)Corresponding luminal concentration of 1.6 B 1.6 D ** CPR in midgut lumen. (C)Representative (11) ** light micrographs of the insect MTs following 1.4 1.4 (5) exposure to the different concentrations (0.1, ** 1 and 10mmoll–1) of probenecid. The 1.2 1.2 percentage change in CPR concentration,
)
–1 ** compared with experiments on CPR alone, is 1.0 ** 1.0 ** noted. Scale bars, 100mm. (D)Corresponding ** (5) luminal concentration of CPR in the MTs. (mmol l 0.8 (13) 0.8 Asterisks refer to significant difference from * 1mmoll–1 CPR alone (*P<0.05, significant;
lumen 0.6 0.6 **P<0.01, highly significant). The numbers in (7) parentheses indicate the number of animals
[CPR] (9) 0.4 0.4 tested. For S. gregaria, measurements on (4) (10) 3–5 MTs provided a mean for each animal. 0.2 0.2
0 0
CPR –1 –1 CPR
probenecid probenecid probenecid probenecid –1 –1 –1 –1 –1 probenecid–1 probenecid 1 mmol l 1 mmol l
+1 mmol l +1 mmol l +0.1 mmol l +10 mmol l +0.1 mmol l +10 mmol l gregaria, with a mean concentration of 0.31±0.07mmoll–1 (Fig.3) noticeably passive during probenecid exposure (Fig.4), indicating and 0.78±0.19mmoll–1 (Fig.5), respectively. In solutions containing that, at the high concentration given, probenecid affects processes 10mmoll–1 probenecid, dye accumulation was drastically reduced in addition to organic anion transport. Indeed, there is evidence that in H. crispae by ~61% compared with solutions containing CPR probenecid inhibits cellular oxidative metabolism at concentrations only, averaging merely 0.21±0.05mmoll–1 in luminal concentration of >1mmoll–1 (Masereeuw et al., 2000). Consequently, we titrated (Fig.3). Dye accumulation was even more reduced in S. gregaria the effect of probenecid through successive dilution of the inhibitor, (by ~77%), averaging 0.31±0.1mmoll–1 in luminal concentration using 0.1 and 1mmoll–1 concentrations, in addition to 10mmoll–1 of probenecid-exposed tubules (Fig.5). Halobiotus crispae became (Fig.7). These results show an inverse relationship between
mu. f. α Fig.8. MT structure and subcellular localization of the - A D G -subunit + + F-actin subunit of the Na /K -ATPase in S. gregaria. (A–C) Sections DAPI (2mm Araldite®) stained with Toluidine Blue. A prominent brushborder is present, as well as several transverse muscle mv fibers; contraction creates peristalsis, which aids in luminal lu clearance (visual observation). Mononucleated principal-like cells and double-nucleated cells (dashed circles) were tc observed. (D)Imaris reconstruction (shadow projection mode) of a partial confocal laser scanning microscopy stack B displaying a median, longitudinal cross-section. (E)Imaris reconstruction (shadow projection mode) displaying the mu. f. E tubular lumen. Basal localization of the -subunit is evident. (F) Immunohistochemistry on paraffin sections confirms the mu. f. mv basal localization of the pump. (G)Imaris three-dimensional lu mv lu reconstruction of an entire stack, again showing that the Na+/K+-ATPase localizes to the basal plasma cell membranes. A longitudinal muscle fiber (mu. f.) runs the mu. f. length of the MT. lu, lumen; mv, microvilli. Scale bar, 75mm. C mu. f. F
lu lu tc mv
THE JOURNAL OF EXPERIMENTAL BIOLOGY 504 K. A. Halberg and N. Møbjerg probenecid concentration and CPR accumulation (and activity; data ATPase (bafilomycin and ouabain reduce CPR accumulation), and not shown). At a concentration of 0.1mmoll–1 probenecid, CPR possibly transporter mediated (inhibited by the prototypic organic concentration was reduced by 26% with a luminal concentration of anions PAH and probenecid). The latter suggests that CPR transport 0.42±0.07mmoll–1 in H. crispae, and by 9% corresponding to a is (at least partly) transcellular. Comparing the transport characteristics concentration of 1.2±0.14mmoll–1 in S. gregaria. When applied at of CPR transport between the tardigrade midgut and the insect MT a concentration of 1mmoll–1, probenecid reduced CPR concentration reveals a surprisingly similar overall pharmacological profile of the by 56% corresponding to a luminal concentration of investigated tissues, albeit with markedly higher concentrations of 0.25±0.05mmoll–1 in H. crispae, and by 47% equivalent to CPR observed in the insect MT. In addition to transcellular transport 0.7±0.16mmoll–1 in S. gregaria (Fig.7). of the dye, fluid secretion may augment transport of organic anions by convective secretion through the paracellular pathway, and/or Midgut and MT structure and immunostaining reduce diffusive back-flux of organic anions from the tubule lumen Our transport studies indicate that CPR transport is active and to the haemolymph (O’Donnell and Leader, 2006; Chahine and transporter mediated in the midgut of H. crispae as well as the MTs O’Donnell, 2010). Consequently, without a measure of fluid secretion of S. gregaria. It is well established that the vacuolar H+-ATPase rates, and thereby a measure of net CPR secreted, we cannot conclude is important for energizing transepithelial transport in insects, whether the difference in relative concentration of CPR in the gut whereas (and in contrast to vertebrate literature) the role of the lumen of H. crispae, compared with the MTs of S. gregaria, is a Na+/K+-ATPase is controversial (e.g. Torrie et al., 2004; Beyenbach consequence of a lower dye transport capacity, or whether it reflects et al., 2010). The data obtained in the present study using ouabain differences in fluid transport rates. Also, we cannot be certain that would suggest that the Na+/K+-ATPase is important for CPR the concentration of CPR in the haemolymph of H. crispae is exactly transport in both animals. Conversely, ouabain could act as a the same as that of the surrounding bath – although, the relatively competitive inhibitor, being transported by the same transporters as high dye concentration used along with the small diffusion distances CPR. We therefore investigated whether the Na+/K+ pump is involved, the relatively long exposure time (60min) and the animal expressed in the epithelia. movements that facilitate fluid exchange, would make potential Unfortunately, our attempt to localize Na+/K+-ATPase in concentration differences negligible. tardigrades was unsuccessful, both on whole mounts and on paraffin A vast number of papers have investigated various aspects of sections, and also in attempts at antigen retrieval. organic anion transport in insect MTs. In the present study we Our observations on the MTs of S. gregaria generally correspond observed a mean CPR concentration of 1.3±0.13mmoll–1 when no with those previously described (Garret et al., 1988), when focusing inhibitors were added. This concentration is elevated above the bath on the proximal region and parts of the middle region used in the concentration (1mmoll–1), albeit by a much smaller factor than that present study. In general, we observed a prominent brushborder reported from other insects (Maddrell et al., 1974; Bresler et al., (Fig.8B,C) and at least two cell types. One type, a principal-like cell, 1990; Linton and O’Donnell, 2000; Leader and O’Donnell, 2005). has a single nucleus, while the other is a very large double-nucleated However, when exposed to external CPR concentrations of 1, 10 cell (dashed circles in Fig.8). Cross-striated muscle fibers are present and 100mmoll–1, the mean luminal CPR concentrations were in both the transverse (Fig.8A,B) and longitudinal direction 0.16±0.03, 0.73±0.09 and 0.89±0.07mmoll–1, respectively, which (Fig.8E,G). The transverse muscle fibers were only observed in the is a factor of ~160, 70 and 9 above bath concentrations (Fig.2). proximal-most region of the MTs, whereas the longitudinal muscle When exposed to a bath concentration of 5mmoll–1 CPR, the mean extended the entire length of the tubule. Visual observations revealed luminal concentration was 1.79±0.33mmoll–1, a factor of 2.8 below that the transverse muscles aid the clearance of luminal content into external concentrations. Consequently, the luminal CPR the midgut through peristaltic contractions. Our immunocytochemical concentration is maximally elevated (~160-fold) above that in the analysis shows that the Na+/K+-ATPase is expressed in the MTs of bathing medium when the latter contains CPR at a concentration of S. gregaria, and is localized to the basal plasma membranes 1mmoll–1. This concentrative ability is among the highest measured (Fig.8D–G), although to a lesser extent in the double-nucleated cells for insects, and is an additional confirmation of active transport of (Fig.8D,G). The localization was confirmed by counterstaining of CPR by the insect MTs. nuclei by DAPI and staining apical microvilli with phalloidin. This Ouabain, a well-characterized, potent inhibitor of the Na+/K+- is, to our knowledge, the first study showing immunolocalization of ATPase, reduced the CPR concentration in both the tardigrade the Na+/K+-ATPase in S. gregaria MTs. Interestingly, the localization midgut and the insect MTs by ~20–21%. A similar 23% reduction of the transporter substantiates previously published data on isolated in PAH secretion in the presence of 1mmoll–1 ouabain was reported basal membrane fractions from MTs and hindgut from S. gregaria, from MTs of D. melanogaster (Linton and O’Donnell, 2000), while which show a prominent Na+/K+-ATPase activity (Al-Fifi, 2007). fluorescein uptake was reduced in MTs of Blaberus giganteus by 30% and in MTs of Locusta migratoria by 20%, when ouabain was DISCUSSION used at 1 and 0.1mmoll–1, respectively (Bresler et al., 1990). Our Our study is significant in two main aspects: (i) we are the first to immunocytochemical investigation on the MTs of S. gregaria provide evidence for active epithelial transport in tardigrades, and revealed expression of the Na+/K+-ATPase in the basal cell (ii) our data show that tardigrades possess an organic anion transport membranes, although to a lesser extent in the double-nucleated cells. system. Consequently, our study is important for understanding the A basal localization of the Na+/K+-ATPase in principal cells of MTs evolution of transport systems. of D. melanogaster has previously been reported (Torrie et al., 2004). CPR is categorized as a sulphonate, but is known to compete with The fact that there is expression of the Na+/K+-ATPase in the basal substrates for both solute carriers (SLC22 and SLC21/SLCO) and membranes, and that CPR transport is ouabain sensitive, suggests ABC transporters in a number of organisms (Pritchard et al., 1999; that the pump is important for CPR transport. Alternatively, it could Linton and O’Donnell, 2000; Chahine and O’Donnell, 2009). In H. be argued that the inhibitory effects of ouabain are due to competitive crispae, CPR transport is ATP dependent (strong inhibition by DNP), inhibition, rather than to non-competitive inhibition, given the fact probably energized by both the Na+/K+-ATPase and the V-type H+- that ouabain is actively transported by members of the SLC21/SLCO
THE JOURNAL OF EXPERIMENTAL BIOLOGY Epithelial transport in tardigrades 505 subfamily (Oatps) in D. melanogaster (Torrie et al., 2004). Whether Haemolymph this is ubiquitous in insects is at present not known; however, several Solute carrier (SLC21/SLCO) members of the Oatp family are known to transport ouabain in Na+/K+-ATPase human tissue (see Hagenbuch and Gui, 2008). Competition studies Basal lamina using fluorescently labeled ouabain would help in clarifying this K+ OA– matter. Considering the striking similarities between the pharmacological profiles of the tardigrade midgut and insect MT, ATP + + + it seems reasonable to assume that the Na /K -ATPase is similarly Pi+ADP Na present in the basal cell membranes of the tardigrade midgut (in spite of failed attempts to localize this transporter). In support of Tardigrade Nucleus midgut cell this interpretation is the fact that transcripts for the -subunit of the + + Na /K -ATPase were found in the expressed sequence tags (EST) H+ OA– library from Hybsibius dujardini Doyère, 1840 (TardiBASE cluster Pi+ADP ATP ID: HDC01733 TardiBASE; http://xyala.cap.ed.ac.uk/research/ tardigrades/tardibase.shtml). Bafilomycin is a specific inhibitor of the V-type H+-ATPase and was found to reduce CPR accumulation in both H. crispae and S. V-type H+-ATPase gregaria. This observation is consistent with the fact that the V-type Apical junction H+-ATPase is viewed as being central to the transport activities of Lumen complex the MT in insects (Weng et al., 2003; Beyenbach et al., 2010) and perhaps also for transport in tardigrades; the B-, C-, D-, E-, G- and Fig.9. Tentative model of the tardigrade midgut cell derived from the H-subunits of the V-type H+-ATPase were found in the EST library current study on H. crispae. Based on the pharmacological profile of the of H. dujardini (TardiBASE). Indeed, visual changes to CPR colour tardigrade midgut epithelium, both the Na+/K+-ATPase and the V-type H+- were observed in the midgut of H. crispae (CPR became purple; data ATPase are potential candidates for providing an electrochemical driving force for the transepithelial movement of organic anions. Transport not shown) 10min post-incubation, suggesting an alkalization of the characteristics and the presence in tardigrade EST libraries suggest that a midgut content. This observation is in accordance with specific member of the SLC21/SLCO transporter family may mediate the + inhibition of an apical V-type H -ATPase in the tardigrade midgut. basolateral entry of organic anions in tardigrades. The exact coupling PAH is a prototypical substrate of the classic organic anion transport between electrochemical gradients generated by the pumps and transport system (i.e. the SLC22 subfamily) and was shown to be an effective of ions, as well as the nature of the apical exit step, are not known. inhibitor of CPR transport in both H. crispae and S. gregaria (~40% reduction in both animals). This finding is a strong indication that PAH (carboxylate) and CPR (sulphonate) transport are mediated by oxidative phosphorylation (Masereeuw et al., 2000). It is therefore a common transporter, or alternatively through two separate transport possible that the reduction in CPR transport is non-specific when systems overlapping in affinity, in both investigated epithelia. Whether the drug is applied in concentrations ≥1mmoll–1. At lower carboxylates (e.g. PAH and probenecid) and sulphonates (e.g. CPR) concentrations of probenecid (<1mmoll–1), however, animal motility are handled by a common transporter (Bresler et al., 1990), or by two was regained (in a concentration-dependent manner), and was not separate transport systems (Maddrell et al., 1974; Linton and significantly different from that in solutions containing CPR only O’Donnell, 2000; Chahine and O’Donnell, 2009), appears to be highly (data not shown). Noticeably, the relative inhibition of CPR transport variable and/or species specific. Indeed, transport of PAH and by probenecid was of a greater magnitude in the midgut of H. crispae probenecid (carboxylates) and CPR and methotrexate (MTX; than in the MT of S. gregaria at the lower (specific) concentrations sulphonates) are all mediated by one tranporter (OAT1) in humans, of probenecid. This could indicate a higher specificity for probenecid but not in rats (Burckardt and Burckardt, 2003), whereas MTX uptake by the tardigrade transporter(s) compared with that of S. gregaria. is competitively inhibited by CPR and probenecid, but not PAH in D. melongaster (Cahine and O’Donnell, 2009). The tardigrade midgut cell transports organic anions Probenecid is implicitly regarded as a competitive inhibitor of The observed CPR transport by the tardigrade midgut and insect MT organic anion transport, and has been shown to compete with both presumably takes place because CPR is structurally and chemically solute carrier and ABC transporter substrates (Bresler et al., 1990; similar to compounds encountered in the natural habitat of these Linton and O’Donnell, 2000; Neufeld et al., 2005; Leader and animals. In terrestrial insects, organic anion transport seems especially O’Donnell, 2005). It is typically applied in a concentration of important for excreting xenobiotics such as plant toxins and pesticides 1mmoll–1; here, we examined the effects of probenecid on CPR (Lanning et al., 1996; Torrie et al., 2004; Neufeld et al., 2005; Buss transport in the range 0.1–10mmoll–1. In H. crispae, probenecid and Callaghan, 2008); however, a similar physiological requirement reduced CPR accumulation by 26%, 56% and 61% at a concentration is not as readily apparent in tardigrades. The handling of endogenous of 0.1, 1 and 10mmoll–1, respectively, whereas the corresponding toxins derived from metabolism, in contrast, is a ubiquitous reduction in CPR concentration was 9%, 47% and 77% in S. prerequisite for all organisms, and it is likely that this is the primary gregaria. In the presence of very high probenecid concentrations function of the organic anion transport system in tardigrades. (10mmoll–1), we observed an almost total loss of motility in H. Because of the broad overlap in substrate specificity between the crispae. Indeed, the level of animal movement was comparable to different groups of organic anion transporters, we cannot definitively that in treatments containing DNP. This observation suggests that identify, on the basis of the data presented here, the type of the drug affected processes in addition to CPR transport at the given transporter(s) responsible for the observed CPR transport. However, concentration. In fact, when applied at concentrations of 1mmoll–1 searching the EST library of H. dujardini (TardiBASE) revealed or above, probenecid is reported to induce a range of non-specific that putative genes of Oatp (cluster ID: HDC00927) (SLC21/SLCO effects presumably initiated by the uncoupling of mitochondrial protein family), P-gp (cluster ID: HDC01698) and Mrps (cluster
THE JOURNAL OF EXPERIMENTAL BIOLOGY 506 K. A. Halberg and N. Møbjerg
ID: HDC00004, HDC02687 and HDC03352) (ABCB and ABCC Burckardt, B. C. and Burckardt, G. (2003). Transport of organic anions across the basolateral membrane of proximal tubule cells. Rev. Physiol. Biochem. Pharmacol. 146, protein families) are present and expressed in tardigrades – just as 95-158. they are in insects (Maddrell et al., 1974; Lanning et al., 1996; Buss, D. S. and Callaghan, A. (2008). Interaction of pesticides with p-glycoprotein and other ABC proteins: A survey of the possible importance to insecticides, herbicide and Bresler et al., 1990; Linton and O’Donnell, 2000; Torrie et al., 2004; fungicide resistance. Pestic. Biochem. Physiol. 90, 141-153. Neufeld et al., 2005; Leader and O’Donnell, 2005; O’Donnell and Chahine, S. and OʼDonnell, M. J. (2009). Physiological and molecular characterization of methotrexate transport by Malpighian tubules of adult Drosophila melanogaster. J. Insect Leader, 2006; Chahine and O’Donnell, 2009). Comparing the Physiol. 55, 927-935. transport characteristics of the different groups of transporters reveals Chahine, S. and OʼDonnell, M. J. (2010). Effects of acute or chronic exposure to dietary organic anions on secretion of methotrexate and salicylate by Malpighian tubules of that it is unlikely that members of the ABC transporter family (i.e. Drosophila melanogaster larvae. Arch. Insect Biochem. Physiol. 73, 128-147. P-gps and Mrps) mediate the basolateral entry of CPR in H. crispae Dantzler, W. H. (2002). Renal organic anion transport: a comparative and cellular perspective. Biochim. Biophys. Acta 1566, 169-181. and S. gregaria. This assumption is based on the fact that P-gp Dewel, R. A. and Dewel, W. C. (1979). Studies on the tardigrades. J. Morphol. 161, 79- transporters predominantly recognize large cationic species (Russel, 110. 2010), and because Mrp transporters mainly transport large Dow, J. A. T. and Davies, S. A. (2006). The Malpighian tubule: rapid insights from post- genomic biology. J. Insect. Physiol. 52, 365-378. (>500Da) polyvalent type II organic anions (Wright and Dantzler, Faria, M., Navarro, A., Luckenbach, T., Piña, B. and Barata, C. (2010). Characterization 2004; Russel, 2010) – the apical transporter MRP2, however, was of the multixenobiotic resistance (mxr) mechanism in embryos and larvae of the zebra mussel (Dreissena polymorpha) and studies on its role in tolerance to single and mixture shown to transport PAH in humans (see below). In addition, PAH combinations of toxicants. Aqua. Toxicol. 101, 78-87. does not compete with MTX (an Mrp substrate) in D. melongaster, Garret, M. A., Bradley, T. J., Meredith, J. E. and Phillips, J. E. (1988). Ultrastructure of the Malpighian tubules of Schistocerca gregaria. J. Morphol. 195, 313-325. suggesting distinct transport systems for these compounds in insects George, R. L., Wu, X., Huang, W., Fei, Y. J., Leibach, F. H. and Ganapathy, V. (1999). (Chahine and O’Donnell, 2009). In contrast, both members of the Molecular cloning and functional characterization of a polyspecific organic anion transporter from Caenorhabditis elegans. J. Pharmacol. Exp. Ther. 291, 596-603. SLC22 and SLC21/SLCO protein families (Oats and Oatps) have Greven, H. (1982). Homologues or analogues? A survey of some structural patterns in been reported to transport all the investigated organic anions, Tardigrada. In Proceedings of the Third International Symposium on the Tardigrada (ed. D. R. Nelson), pp. 55-76. Johnson City, Tennessee: East Tennessee State University including probenecid, PAH and CPR (Pritchard et al., 1999; Lee Press. and Kim, 2004; Torrie et al., 2004). Therefore, it seems probable Hagenbuch, B. and Gui, C. (2008). Xenobiotic transporters of human organic anion transporting polypeptides (OATP) family. Xenobiotica 38, 778-801. that an Oat or Oatp homologue mediates the basolateral entry of Halberg, K. A., Persson, D., Møbjerg, N., Wanninger, A. and Kristensen, R. M. CPR in the tardigrade midgut cell as well as the insect MTs (Fig.9). (2009a). Myoanatomy of the marine Tardigrade Halobiotus crispae (Eutardigrada: Hypsibiidae). J. Morphol. 270, 996-1013. At present, our data do not allow us to make assumptions on the Halberg, K. A., Persson, D., Ramløv, H., Westh, P., Kristensen, R. M. and Møbjerg, N. nature of the luminal exit. Evidence suggests that MRP2 is involved (2009b). Cyclomorphosis in Tardigrada: adaption to environmental constraints. J. Exp. Biol. 212, 2803-2811. in the efflux of organic anions across the brush-border membrane Haugen, B. M., Halberg, K. A., Jespersen, Å., Prehn, L. R. and Møbjerg, N. (2010). in the human kidney proximal tubule (Leier et al., 2000), and a Functional characterization of the vertebrate primary ureter: structure and ion transport mechanisms of the pronephric duct of axolotl larvae (Amphibia). BMC Develop. Biol. 10, similar situation could exist in tardigrades and insects. Our data 56. tentatively suggest that the V-type H+-ATPase, and perhaps also Jönsson, K. I., Rabbow, E., Schill, R. O., Ringdahl, M. H. and Rettberg, P. (2008). + + Tardigrades survive exposure to space in low Earth orbit. Curr. Biol. 18, R729-R731. the Na /K -ATPase, provide the driving force for the transepithelial Kristensen, R. M. (1982). The first record of cyclomorphosis in Tardigrada based on a transport of organic anions in both H. crispae and S. gregaria new genus and species from Arctic meiobenthos. Z. zool. Syst. Evolut.-forsch. 20, 249- 270. (Fig.9). It is likely that a large lumen-positive transepithelial Lanning, C. L., Fine, R. L., Corcoran, J. J., Ayad, H. M., Rose, R. L. and Abou-Donia, potential, generated by an apical H+-ATPase provides a significant M. B. (1996). Tobacco budworm P-glycoprotein: biochemical characterization and its involvement in pesticide resistance. Biochim. Biophys. Acta. 1291, 155-162. driving force for the accumulation of anions in the lumen. However, Leader, J. P. and OʼDonnell, M. J. (2005). Transepithelial transport of fluorescent p- the exact coupling between electrochemical gradients generated by glycoprotein and MRP2 substrates by insect Malpighian tubules: confocal microscopic analysis of secreted fluid droplets. J. Exp. Biol. 208, 4363-4376. the pumps and transport of the ions is not known. Lebovitz, R. M., Takeyasu, K. and Fambrough, D. M. (1989). Molecular characterization In future studies, it would be of interest to investigate whether and expression of the (Na+ + K+)-ATPase alpha-subunit in Drosophila melanogaster. EMBO J. 8, 193-202. substrates of Mrps (e.g. Texas Red and MTX) also accumulate in Lee, W. and Kim, R. B. (2004). Transport and renal drug elimination. Annu. Rev. the midgut of tardigrades, and whether transport of these anions Pharmacol. Toxicol. 44, 137-166. occurs via a separate or a common transporter to CPR. Similarly, Leier, I., Hummel-Eisenbeiss, J., Cui, Y. and Keppler, D. (2000). ATP-dependent para- aminohippurate transport by apical multidrug resistance protein MRP2. Kidney Int. 57, an understanding of the electrophysiological properties of the 1636-1642. midgut epithelium would be highly relevant in our ongoing struggle Linton, S. M. and OʼDonnell, M. J. (2000). Novel aspects of the transport of organic anions by Malpighian tubules of Drosophila melanogaster. J. Exp. Biol. 203, 3575-3584. to understand the complex biology of these amazing animals. Maddrell, S. H. P., Gardiner, B. O. C., Pilcher, D. E. M. and Reynolds, S. E. (1974). Active transport by insect Malpighian tubules of acidic dyes and of acylamides. J. Exp. Biol. 61, 357-377. ACKNOWLEDGEMENTS Marshall, E. K., Jr and Vickers, J. L. (1923). The mechanism of the elimination of We would like to thank Reinhardt M. Kristensen for the use of the Olympus BX50 phenolsulphonephthalein by the kidney - a proof of secretion by the convoluted tubules. stereomicroscope, Jette Lyby Michelsen for technical assistance and Dennis K. Bull. Johns Hopkins Hosp. 34, 1-6. Persson and Aslak Jørgensen for help during sampling. Masereeuw, R., van-Pelt, A. P., van-Os, S. H. G., Willems, P. H. G. M., Smits, P. and Russel, F. G. M. (2000). Probenecid interferes with renal oxidative metabolism: a potential pitfall in its use as an inhibitor of drug transport. Br. J. Pharmacol. 131, 57-62. FUNDING Møbjerg, N. and Dahl, C. (1996). Studies on the morphology and ultrastructure of the Malpighian tubules of Halobiotus crispae Kristensen 1982 (Eutardigrada). Zool. J. Linn. Funding came from the 2008 Faculty of Science, University of Copenhagen Freja- Soc. 116, 85-99. Programme and from the Carlsberg Foundation. Møbjerg, N., Jørgensen, A., Eibye-Jacobsen, J., Halberg, K. A., Persson, D. and Kristensen, R. M. (2007): New records on cyclomorphosis in the marine eutardigrade Halobiotus crispae (Eutardigrada: Hypsibiidae). J. Limnol. 66 Suppl.1, 132-140. REFERENCES Møbjerg, N. M., Halberg, K. A., Jørgensen, A., Persson. D., Bjørn, M., Ramløv, H. and Aguinaldo, A. M. A., Turbeville, J. M., Linford, L. S., Rivera, M. C., Garey, J. R., Raff, Kristensen, R. M. (2011). Survival in extreme environments – on the current knowledge R. A. and Lake, J. A. (1997). Evidence for a clade of nematodes, arthropods and other of adaptations in tardigrades. Acta Physiologica 202, 409-420. moulting animals. Nature 387, 489-493. Mulenga, A., Khumthong, R., Chalaire, K. C., Strey, O. and Teel, P. (2008). Molecular Al-Fifi, Z. I. A. (2007). Comparative of effect of inhibitors on the ATPase from the and biological characterization of the Amblyomma americanum organic anion transporter excretory systems of the usherhopper, Poekilocerus bufonius and desert locust, polypeptide. J. Exp. Biol. 211, 3401-3408. Schistocerca gregaria. Am. J. Cell Biol. 2, 11-22. Neufeld, D. S. G., Kaufmann, R. and Kurtz, Z. (2005). Specificity of the fluorescein Beyenbach, K. W., Skaer, H. and Dow, J. A. T. (2010). The developmental, molecular, transport process in Malpighian tubules of the cricket Acheta domesticus. J. Exp. Biol. and transport biology of Malpighian tubules. Annu. Rev. Entomol. 55, 351-374. 208, 2227-2236. Bresler, V. M., Belyaeva, E. A. and Mozhayeva, M. G. (1990). A comparative study on OʼDonnell, M. J. and Leader, J. P. (2006). Changes in fluid secretion rate alter net the system of active transport of organic acids in Malpighian tubules of insects. J. Insect transepithelial transport of MRP2 and p-glycoprotein substrates in Malpighian tubules of Physiol. 36, 259-270. Drosophila melanogaster. Arch. Insect Biochem. Physiol. 63, 123-134.
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OʼDonnell, M. J., Ianowski, J. P., Linton, S. T. and Rheault, M. R. (2003). Inorganic and Russel, F. G. M. (2010). Transporters: importance in drug absorption, distribution, and organic anion transport by insect renal epithelia. Biochim. Biophys. Acta 1618, 194-206. removal. In Enzyme- and Transporter-Based Drug-Drug Interactions (ed. K. S. Pang, A. Pelzer, B., Dastych, H. and Greven, H. (2007). The osmoregulatory/excretory organs of Rodrigues and R. M. Peter), pp. 27-49. Heidelberg: Springer. the glacier-dwelling eutardigrade Hypsibius klebelsbergi Mihelcic, 1959 (Tardigrada). Schmidt-Rhaesa, A. and Kulessa, J. (2007). Muscular architecture of Milnesium Mitt. Hamb. Zool. Mus. Inst. 104, 61-72. tardigradum and Hypsibius sp. (Eutardigrada, Tardigrada) with some data on Persson, D., Halberg, K. A., Jørgensen, A., Ricci, C., Møbjerg, N. and Kristensen, R. Ramazzottius oberhaeuseri. Zoomorphology 126, 265-281. M. (2011). Extreme stress tolerance in tardigrades: surviving space conditions in low Torrie, L. S., Radford, J. C., Southall, T. D., Kean, L., Dinsmore, A. J., Davies, S. A. earth orbit. J. Zool. Syst. Evol. Res. 49, 90-97. and Dow, J. A. T. (2004). Resolution of the insect ouabain paradox. Proc. Natl. Acad. Phillips, J. (1981). Comparative physiology of insect renal function. Am. J. Physiol. Regul. Sci. USA. 101, 13689-13693. Integr. Comp. Physiol, 241, R241-R257. Towle, D. W., Paulsen, R. S., Weihrauch, D., Kordylewski, M., Salvador, C., Lignot, J. H. and Spannings-Pierrrot, C. (2001). Na++K+-ATPase in gills of the blue crab Pritchard, J. B., Sweet, D. H., Miller, D. S. and Walden, R. (1999). Mechanism of Callinectes sapidus: cDNA sequencing and salinity-related expression of -subunit organic anion transport across the apical membrane of choroid plexus. J. Biol. Chem. mRNA and protein. J. Exp. Biol. 204, 4005-4012. 274, 33382-33387. Wang, J., Kean, L., Yang, J., Allan, A. K., Davies, S. A., Herzyk, P. and Dow, J. A. T. Rebecchi, L. and Bertolani, R. (1994). Maturative pattern of ovary and testis in (2004). Function-informed transcriptome analysis of Drosophila renal tubule. Gen. Biol. eutardigrades of fresh-water and terrestrial habitats. Invert. Rep. Dev. 26, 107-117. 5, R69. Rebecchi, L., Altiero, T., Guidetti, R., Cesari, M., Bertolani, R., Negroni, M. and Weng, X.-H., Huss, M., Wieczorek, H. and Beyenbach, K. W. (2003). The V-type H+- Rizzo, A. M. (2008). Tardigrade resistance to space effects: first results of ATPase in Malpighian tubules of Aedes aegypti: localization and activity. J. Exp. Biol. experiments on the LIFE-TARSE mission on FOTON-M3 (September 2007). 206, 2211-2219. Astrobiology 6, 581-591. Wright, S. W. and Dantzler, W. H. (2004). Molecular and cellular physiology of renal Rost-Roszkowska, M. M., Poprawa, I., Wójtowicz, M. and Kaczmare, L. (2011). organic cation and anion transport. Physiol. Rev. 84, 987-1049. Ultrastructural changes of the midgut epithelium in Isohypsibius granulifer granulifer Zantke, J., Wolff, C. and Scholtz, G. (2008). Three-dimensional reconstruction of the Thulin, 1928 (Tardigrada: Eutardigrada) during oogenesis. Protoplasma 248, 405- central nervous system of Macrobiotus hufelandi (Eutardigrada: Parachela): implications 414. for the phylogenetic position of Tardigrada. Z. Morphol. 127, 21-36.
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Paper III
Acta Physiol 2011, 202, 409–420
REVIEW Survival in extreme environments – on the current knowledge of adaptations in tardigrades
N. Møbjerg,1 K. A. Halberg,1 A. Jørgensen,2 D. Persson,1,2 M. Bjørn,3 H. Ramløv3 and R. M. Kristensen2 1 Department of Biology, University of Copenhagen, Copenhagen, Denmark 2 Natural History Museum of Denmark, University of Copenhagen, Copenhagen, Denmark 3 Department of Science, Systems and Models, University of Roskilde, Roskilde, Denmark
Received 17 October 2010, Abstract revision requested 13 November Tardigrades are microscopic animals found worldwide in aquatic as well as 2010, terrestrial ecosystems. They belong to the invertebrate superclade Ecdysozoa, revision received 6 January 2011, accepted 10 January 2011 as do the two major invertebrate model organisms: Caenorhabditis elegans Correspondence: N. Møbjerg, and Drosophila melanogaster. We present a brief description of the tardi- Department of Biology, August grades and highlight species that are currently used as models for physio- Krogh Building, Universitetsparken logical and molecular investigations. Tardigrades are uniquely adapted to a 13, DK-2100 Copenhagen Ø, range of environmental extremes. Cryptobiosis, currently referred to as a Denmark. reversible ametabolic state induced by e.g. desiccation, is common especially E-mail: [email protected] among limno-terrestrial species. It has been shown that the entry and exit of cryptobiosis may involve synthesis of bioprotectants in the form of selective carbohydrates and proteins as well as high levels of antioxidant enzymes and other free radical scavengers. However, at present a general scheme of mechanisms explaining this phenomenon is lacking. Importantly, recent research has shown that tardigrades even in their active states may be ex- tremely tolerant to environmental stress, handling extreme levels of ionizing radiation, large fluctuation in external salinity and avoiding freezing by supercooling to below )20 C, presumably relying on efficient DNA repair mechanisms and osmoregulation. This review summarizes the current knowledge on adaptations found among tardigrades, and presents new data on tardigrade cell numbers and osmoregulation. Keywords cell numbers, cryptobiosis, evolution, osmoreglation, supercool- ing, tardigrade.
Tardigrades, also known as water bears, are micro- 2007). Tardigrades are exceptional among metazoans in scopic metazoans (approx. 0.1–1.2 mm). They were their adaptations to the most extreme environments. As discovered in the 18th Century with the development of is also known from selected species of arthropods, early microscopes and were first described by the nematodes and rotifers, many species have the ability to German zoologist Goeze in 1773, who named them enter cryptobiosis; a state of suspended animation ‘kleiner Wasserba¨r’ or little water bear because of their believed to be ametabolic (Keilin 1959, Clegg 2001). strong resemblance to a little bear (see e.g. Ramazzotti Corti already noted these adaptations in tardigrades in & Maucci 1983, Nelson 2001, Schill 2010). Shortly 1774, when he observed that these animals could be after in 1776, the current name, Tardigrada (from Latin revived after desiccation (Kinchin 1994). In 1962, tardigradus, slow-moving), was given by the Italian Tardigrada was recognized as a phylum by Ramazzotti natural scientist Spallanzani (see e.g. Rebecchi et al. in Il Phylum Tardigrada (Ramazzotti 1962). There are