Chemical Defense in Tropical Marine Algae James N. Norris and William Fenical herbivores (Fraenkel, 1959; Whittaker and Fee- ABSTRACT ney, 1971). Since Janzen (1973) put forth the Chemical and taxonomic studies of the benthic working hypothesis that the primary role of sec- algae of Carrie Bow Cay, Belize, have revealed ondary compounds in higher plant vegetation that species of certain families of the Rhodophyta, and seeds is defense against herbivores and micro- Phaeophyta, and Chlorophyta produce unique or unusual secondary compounds. Analysis of the organisms, it has been generally recognized that structural organic chemistries of these natural these natural products may either serve as feeding products shows that the substances produced con- deterrents or attractants in terrestrial plant-ani- sist largely of halogenated and non-halogenated mal interactions (see, for example, Harbourne, terpenoids including monoterpenoids (Cio com- 1977), or function as allelopathic chemicals pounds), sesquiterpenoids (Cis compounds), and (Muller, 1970) or antibiotics. The same evolution- diterpenoids (C2 compounds), and larger com- pounds of mixed acetate-mevalonate origin. ary pressures responsible for the many biologi- These secondary compounds, hypothesized to be cally active compounds found in terrestrial vege- feeding deterrents developed as defenses against tation have been predicted to have parallels in herbivores, were examined for antibiotic activity marine vegetation (Whittaker and Feeney, 1971; and toxicity. Fish toxicity experiments using Eu- Kittredge, 1976). Predaceous fishes and inverte- pomacentrus leucostictus and these compounds re- vealed sublethal to lethal effects. One compound, brate animals have been important forces acting elatol, from Laurencia obtusa was found to inhibit as agents of natural selection in the evolution of sea urchin egg development totally. Field obser- protective mechanisms (Bakus, 1964; 1966; 1969). vations indicate that marine algae having these The world-wide distribution of herbivorous secondary metabolites are not eaten by many marine fishes shows a concentration, both in spe- herbivores, and biological activity testing suggests cies diversity and biomass, on tropical reefs (Hiatt that certain of these compounds may be respon- sible. In some cases, specialized grazers have ap- and Strasburg, 1960). Herbivorous fishes gener- parently co-evolved to tolerate these potential ally dominate fish communities on tropical reefs chemical “deterrents,” and may in turn use them (Bardach, 1959; Hiatt and Strasburg, 1960); and in their own defense against predation. the number and biomass of both vertebrate and invertebrate herbivores are two of the striking Introduction features of Caribbean coral reefs (Ogden, 1976). Marine algae have developed several defenses Land plants have evolved elaborate morpho- in response to herbivory (see for example, Paine logical and chemical defense mechanisms against and Vadas, 1969; Vadas, 1977; 1979). Algal Spc- cies may deter herbivores in one or more ae ae Jame sN N. orris D, epartmen ot Bf otany N, ationa Ml useum o Nf atural following ways: (1) by having a resistant or un- Flistory S, mithsonian Institution W, ashington D, .C .20560 ;and William Fenica lI,nstitut eo Mf arin eResources S,cripp sInstitution palatable physical structure (for example, the o fOceanography ,La Jolla ,Calif 92093. calcareous nature of some Rhodophyta, Chloro- 417 418 SMITHSONIAN CONTRIBUTIONS TO THE MARINE SCIENCES phyta, and Phaeophyta, or the tough texture of ics in marine algal-algal and algal-animal inter- certain Phaeophyta), or a morphology that makes actions. Unfortunately, there have been few it difficult for the herbivore to attach to feed (see quantitative studies on the diets of marine her- Hay, 1981); (2) by residing in habitats that are bivores, and our knowledge of feeding behavior cryptic or unfavorable for herbivore feeding (Og- and food preferences of tropical herbivores is still den et al., 1973; Adey and Vassar, 1975), such as too inadequate to be conclusive. What is known in crevices where they are inaccessible, in areas of on tropical fish diets can be found in Randall high surf or strong surge where herbivores cannot (1967), while sea urchin diets have. been summa- attach themselves for feeding, or in areas where rized by Lawrence (1975). herbivores are subject to increased predation; (3) In this paper we provide an overview of inter- by having heteromorphic life histories, with a fast actions between tropical reef algae and herbivores growing stage and a resistant stage (Lubchenco in the Caribbean, with reference to our identifi- and Cubit, 1980); (4) by living in association with cation of specific compounds from Belize reef toxic or unpalatable algae (see plant defense algae. On the basis of the antimicrobial activity guilds of Atsatt and O’Dowd, 1976); (5) by being and fish toxicity of these compounds we present unpredictable in occurrence in time or space (for hypotheses of their ecological role in reef algal- example, ephemeral species, or species having animal interactions. rare or patchy distribution) (Littler and Littler, Over the past four years at Carrie Bow Cay, 1980); and/or (6) by producing secondary metab- off the coast of Belize, we have investigated the olites (Fenical, 1975), ranging from unpalatable systematics of the benthic algae as well as the to toxic, as chemical defense against herbivores. chemical nature of their secondary compounds. Since the pioneering work of Pratt et al. (1951) Some of the Chlorophyta, Phaeophyta, and Rho- reporting antibacterial activity of various sea- dophyta synthesized unusual secondary products weed extracts, several investigators have demon- which in the laboratory showed biological activity strated the antibiotic activity of extracts from against selected micro-organisms and a reef fish. some tropical algae (for example, Burkholder et Many of the relatively abundant algae that were al., 1960; Olesen et al., 1964; Sieburth, 1964; accessible to potential herbivores were found to Burkholder, 1973; Bhakuni and Silva, 1974; Nu- contain these biologically active substances. We nez and Serpa Sanabria, 1975). Studies of Boyd hypothesize that these compounds have been se- et al. (1966) on the effects of selected tropical lected for by the intense grazing pressure on algae on human erythrocytes found that the ex- tropical marine algae and that they function to tracts from six brown algae agglutinated blood minimize population losses by inhibiting or re- groups O and A. More recently, Targett and pelling herbivores. Our present analysis indicates Mitsui (1979) studied the effects of aqueous ex- that tropical reef algae are chemically defended tracts from tropical algae on fish erythrocyte from many generalist herbivores, while some spe- hemolysis and fish mortality, and Targett (1979) cialist herbivores have evolved a physiological developed a behavioral bioassay (gastropod ten- tolerance to these natural products. tacle withdrawal) to test extracts from marine ACKNOWLEDGMENTS.— We thank our colleagues algae for biological activity. In another study, who have discussed aspects of this research with both seasonal variability and locality differences us. Particularly helpful were the reviews of I. of the tropical algal extract’s antibiotic activity Abbott, W. Adey, S. Brawley, K. Bucher, D. against selected pathogenic bacteria was observed Cheney, J. Cubit, M. Hay, R. Houbrick, M. (Almodovar, 1964). Hornsey and Hide (1974) Littler, and R. Vadas, and the editoral comments found similar seasonal variation in their screening of V. Macintyre. We especially thank R. Jacobs experiments for antimicrobial activity of British (University of California, Santa Barbara) for pro- marine algae. Sieburth (1968) offered some eco- viding the data from his experiment for Figure logical interpretation of the role of algal antibiot- 182. NUMBER 12 419 Materials and Methods Fenical, 1979), and the crude extract. In each treatment (three replicates), either the extract or Field trips were made to Carrie Bow Cay on the pure compound was added directly to the the barrier reef of Belize (16°48’N; 88°05’W), seawater with the aid of an ethanol dispersant; during the spring (March-May) of 1976, 1977, controls were untreated seawater and seawater and 1978 (for a review of the biological and containing only the ethanol. Fish mortality geological features of Carrie Bow Cay, see Rutzler within one hour was considered to indicate a and Macintyre, herein: 9). During each expedi- toxic compound, and sublethal effects, such as tion, benthic macro-algae were collected for sub- loss of equilibrium and respiratory stress were sequent studies on their systematics and chemis- noted as “strong” or “mild.” Results of the anti- try. Homogeneous collections were identified and microbial and ichthyotoxic experiments are sum- separated into specimens for chemical analysis marized in Table 32. and vouchers for taxonomic verfication; the for- mer were preserved in isopropanol, the latter in Results and Discussion 4% Formalin-seawater. Voucher specimens have been deposited in the CHLoropHyta.—Of the benthic algae in the U.S. National Herbarium, Smithsonian Institu- vicinity of Carrie Bow Cay (Norris and Bucher, tion. The following algal species were chemically herein: 167), the green algae are perhaps the most investigated in this study. Chlorophyta: Caulerpa abundant in biomass, having representatives cupressoides (Vahl) C. Agardh, C. mexicana (Sonder) throughout the diverse intertidal and subtidal Kutzing, C. racemosa (Forsskal) J. Agardh, C. ser- habitats. Three families predominate, the Codi- rulata (Forsskal) J. Agardh emend Bgrgesen, C. aceae with species of Avrainvillea and Codium, sertularioides (Gmelin) Howe, C. verticillata J. Udoteaceae with Halimeda, Penicillus, Rhipoce- Agardh, Rhipocephalus phoenix (Ellis and Solander) phalus, and Udotea, and the Caulerpaceae with Kutzing, and Udotea flabellum (Ellis and Solander) species of its monotypic genus, Caulerpa. Howe. Phaeophyta: Dictyota bartayrest:1 Lamour- The species we investigated from these families oux, Stypopodium zonale (Lamouroux) Papenfuss, produced unusual secondary metabolites. Of six Sargassum polyceratim var. ovatum (Collins) Taylor, species of Caulerpa from Carrie Bow Cay, C. cu- and Turbinaria turbinata (Linnaeus) Kuntze. Rho- pressoides, C. mexicana, C. racemosa, C. serrulata, C. dophyta: Liagora farinosa Lamouroux, Asparagopsis sertularioides, and C. verticillata, all but C. mexicana taxiformis (Delile) Trevisan; Ochtodes secundiramea contained the known compound caulerpin (Fig- (Montagne) Howe, Laurencia caraibica Silva, and ure 18la, compound I). This substance was orig- L. obtusa (Hudson) Lamouroux. inally isolated from C. racemosa, C. serrulata, and The biological activity of the secondary com- C. sertularioides by Aguilar-Santos and Doty pounds produced by the marine algae was inves- (1968). In recent studies of C. taxifolia (Vahl) C. tigated by nutrient agar plate disc assay methods Agardh, Maiti and Thomson (1977) re-examined in the laboratory of W. Fenical, and by fish the structure of caulerpin (Aguilar-Santos, 1970) toxicity experiments. Antibacterial activity was and found it to be a derivatized indole dimer. examined on the basis of inhibition of Staphylococ- We found that species of Caulerpa, Halimeda, cus aureus Rosenbach, Bacillus subtilis (Ehrenberg) Penicillus, Rhipocephalus, and Udotea also produce Cohn, and Escherichia coli (Migula) Castellani and terpenoids of rather complex structure. Although Chalmers, and antifungal activity was assessed it is difficult to analyze many of these compounds against the human pathogen Candida albicans (Ro- thoroughly because of their instability, we have bin) Berkhout. Toxicity to fish was tested using isolated from Rhipocephalus phoenix two sesquiter- Eupomacentrus leucostictus (Muller and Troschel) penoids, rhipocephenal and rhipocephalin, des- with serial dilutions of the alga’s natural com- ignated as compounds II and III respectively pounds in seawater (as outlined by Sun and (Figure 1815). These compounds typify the struc- 420 SMITHSONIAN CONTRIBUTIONS TO THE MARINE SCIENCES TasLe 32.—Compounds identified from tropical benthic algae of Carrie Bow Cay, and results of biological activity tests (compound designations identified in Figures 181, 182; 0 = no response, + = positive response, NT = not tested) Shresies Antimicrobial Toxicity Compound activity to fish CHLOROPHYTA Caulerpa cupressoides I 0 NT C. racemosa I 0 +! C. serrulata I 0 ING C. sertularioides I 0 NT C. verticillata I 0 NT Rhipocephalus phoenix II =F +? R. phoenix Iil ste ate PHAEOPHYTA Sargassum polyceratinum var. ovatum IV +° NT Turbinaria turbinata IV SF Nt Dictyota bartayresi Vv ts 0 Stypopodium zonale VI aF + RHODOPHYTA Asparagopsis taxiformis vil a NT Ochtodes secundiramea Vill at NT O. secundiramea IX