We thank James Maeda and Aaron Cooke for assistance with the filming and editing of this video. Funding was provided by the National Science Foundation (OCE-0550468, 1029515).

NOTE: Step 3 of this protocol involves vertebrate animal subjects. The procedure has been designed so that animals receive the most humane treatment possible and has been approved by the Institutional Animal Care and Use Committee (IACUC) at the University of North Carolina Wilmington.
1) Tissue Extraction
<ol>
	<li>Use tissue that is in its natural state of hydration and not squeezed, dried-out or overly wet as this will alter the volumetric concentration of secondary metabolites. Cut or chop tissue to pieces or slices that can be inserted into a 50 ml centrifuge tube. Note: Fresh tissue can be used in some cases, but it is often better to cut or chop frozen tissue, which is not subject to squeezing when cut.</li>
	<li>Add tissue pieces to 30 ml of a 1:1 mixture of dichloromethane (DCM) and methanol (MeOH) in a graduated centrifuge tube until a final volume of 40 ml is reached. Be sure to conduct all steps involving the transfer of solvent in a fume hood with adequate ventilation.</li>
	<li>Cap the tube and invert it several times, then agitate repeatedly during a 4 hr extraction period. Note: During this period, water combines with the MeOH and the resulting MeOH:water phase separates from the DCM phase. The tissue is alternately exposed to DCM and MeOH:water as an emulsion as the tubes are agitated.</li>
	<li>Transfer the DCM extract to a round-bottom flask and evaporate to dryness on a rotary evaporator using low heat (&#60;40 &#176;C). Using minimal solvent, transfer the dried extract to a 20 ml scintillation vial. Fit the vial with a rotary evaporator adapter and again evaporate to dryness on a rotary evaporator using low heat (&#60;40 &#176;C). 
	Note: The next step requires the use of a homemade compression instrument that may be assembled by screwing the following items in sequential order onto the end of a threaded rod: (1) nut, (2) washer, and (3) acorn nut. The washer must either be perforated or fitted so that it is less than the internal diameter of a 50 ml centrifuge tube.</li>
	<li>Returning to the graduated centrifuge tube that contains tissue and the MeOH:water extract, squeeze the extraction medium out of the tissue through compression. Transfer the MeOH:water extract to the same round-bottom flask and store chilled (&#60;10 &#176;C).</li>
	<li>Add MeOH to the graduated centrifuge tube until the now dehydrated tissue is submerged for a second extraction of 2 to 6 hr duration, then transfer the new MeOH extract to the chilled round-bottom flask containing the MeOH:water extract. If there is any concern that the tissue has not been fully extracted, repeat the 2 to 6 hr MeOH extraction.</li>
	<li>Dry off the MeOH on a rotary evaporator using low heat (&#60;40 &#176;C). Transfer the remaining aqueous extract from the round-bottom flask to the scintillation vial containing the dried nonpolar extract, using a minimal volume of MeOH to rinse the round-bottom flask.</li>
	<li>Evaporate the aqueous extract to dryness using low heat (&#60;40 &#176;C) on a vacuum concentrator. The scintillation vial now contains the total dry crude organic extract of 10 ml of tissue. Evacuate the head space of the vial with N2 gas to prevent oxidation, seal tightly, and store frozen (-20 &#176;C).</li>
</ol>
2) Food Preparation
<ol>
	<li>Prepare freeze-dried squid mantle powder. 
	Note: Squid mantle provides a source of nutrition that is comparable to that of other benthic invertebrates, and will be used as an ingredient in the substeps of 2.2.
	<ol>
		<li>Thaw frozen rings of squid mantle in warm deionized (DI) water, then puree them in a high-speed blender.</li>
		<li>Pour a thin layer of pureed squid mantle onto a shallow cookie sheet and freeze (-20 &#176;C), then break the sheet of frozen squid puree into small pieces to be lyophilized.</li>
		<li>Lyophilize the frozen squid mantle puree following the operating procedures of the freeze-drier.</li>
		<li>Pulverize the lyophilized pieces of squid mantle puree in a high-speed blender to form a powder.</li>
		<li>In a fume hood, pour the powdered squid mantle into a rotary flour sifter and sift to separate large chunks of tissue from the fine powder.</li>
		<li>Transfer the fine powdered squid mantle to a sealable container. Evacuate the container head space with N2 gas to prevent oxidation and store frozen (-20 &#176;C).</li>
	</ol>
	</li>
	<li>Prepare the food mixture. 
	Note: When running multiple consecutive assays, it is practical to prepare ~100 ml of food mixture, however this recipe may be scaled to smaller volumes if necessary.
	<ol>
		<li>Combine a mixture of 3 g alginic acid and 5 g freeze-dried squid mantle powder with 100 ml of DI water in a 150 ml beaker. Stir vigorously with a microspatula for a few minutes until the powder is fully hydrated and the mixture is homogeneous. 
		Note: If desired, food coloring may be added at this step: it is easier to add dye to the food mixture that will generate both treated and control mixtures (masking the natural pigment of the extract in the extract-treated mixture) rather than trying to match the color of the extract-treated mixture by adding dye to the control mixture. A greenish or brownish food color is often desirable to mask any pigments in the crude extract.</li>
		<li>Load exactly 10 ml of food mixture into a graduated syringe. Take care to avoid the inclusion of air bubbles during this process.</li>
		<li>Remove the 20 ml scintillation vial with dry crude organic extract from the freezer. Add a drop or two of MeOH, then stir the extract into a homogeneous mixture with a microspatula.</li>
		<li>Eject the loaded 10 ml syringe of food matrix into the 20 ml scintillation vial and stir with a microspatula to homogenize the extract-treated food mixture. 
		Note: It may help to eject the syringe in smaller increments (i.e., eject 2 ml and homogenize, then repeat until all 10 ml have been homogenized).</li>
	</ol>
	</li>
	<li>Prepare the assay pellets.
	<ol>
		<li>Load a very small volume of the extract mixture (~1 ml) into a syringe, and submerge the syringe tip in a solution of 0.25 M CaCl2. Eject the contents of the syringe to form a long, spaghetti-like strand.</li>
		<li>After a few minutes, remove the hardened strand, chop it into 4 mm long pellets on a glass cutting board with a razor blade, then rinse in seawater.</li>
		<li>Repeat steps 2.3.1 and 2.3.2 without including tissue extract to make control pellets. Be sure to treat control pellets with an equivalent volume of solvent (see addition of MeOH to treated mixture in step 2.2.3) to control for solvent addition. If a negative control is desired to confirm that assay fish can be deterred from feeding, add denatonium benzoate at a concentration of 2 mg ml-1 to the raw food mixture27.</li>
	</ol>
	</li>
</ol>
3) Palatability Bioassays
<ol>
	<li>Perform feeding assays with wild-caught yellow-phase bluehead wrasse, Thalassoma bifasciatum, kept in groups of three in opaque-sided compartments of laboratory aquaria.</li>
	<li>Deliver food pellets from a beaker of seawater using a glass pipette with a rubber bulb. Note: It may take a few days to train fish to receive food in this manner. A conditioning stimulus (e.g. a few taps of the pipette on the aquarium glass) that precedes the delivery of food may be helpful to train the fish to expect the addition of food pellets.</li>
	<li>Scoring pellets. Consider a pellet accepted if readily consumed by the fish. Consider a pellet rejected if not eaten after a minimum of three attempts by one or more fish to take it into their mouth cavity, or if the pellet is approached and ignored after one such attempt.</li>
	<li>Scoring samples. Note: The assay procedure is depicted as a flowchart in Figure 1. Groups of fish that refuse to eat control pellets at any step in the protocol are not considered further. There are two potential outcomes of a single run of the assay: the sample is either accepted or rejected.
	<ol>
		<li>Begin with a control pellet to confirm that the group of fish is cooperative. Offer a treated pellet. If the fish accept the treated pellet, score the sample as accepted. If the fish reject the treated pellet, offer a subsequent control pellet to determine whether the fish have ceased feeding. If the fish accept the subsequent control pellet, score the sample as rejected.</li>
	</ol>
	</li>
	<li>Replication. Repeat the assay procedure with ten independent groups of fish for each extract.</li>
</ol>
4) Evaluating Significance
<ol>
	<li>Evaluate the significance of differences in the consumption of control vs treated pellets with a modified version of Fisher&#8217;s exact test26. Modify the test so that the marginal totals for control and treated pellets are fixed, treating them both as random samples. Note: This provides p = 0.057 when 7 pellets are eaten; hence, any extract is considered deterrent if 6 or fewer pellets are eaten, and palatable if 7 or more pellets are eaten.</li>
	<li>To compare the relative palatability among groups of extracts, calculate a mean number of pellets eaten within each group. Keep the threshold at 6 pellets so a group of replicate extracts are considered deterrent if the mean number of pellets eaten + standard error (SE) &#8804;6. Note: In the representative results, the group assignment is species, so replicate extracts come from distinct individuals and the relative palatability may be compared among species.</li>
</ol>

<ol>
	<li>Paul, V. J., ed, <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=.">.</a> Ecological roles of marine natural products. , (1992).</li><li>Pawlik, J. R. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Marine+invertebrate+chemical+defenses.">Marine invertebrate chemical defenses.</a> Chemical Reviews. 93 (5), 1911 (1993).</li><li>Hay, M. E. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Marine+chemical+ecology:+what&#39;s+known+and+what&#39;s+next.">Marine chemical ecology: what&#39;s known and what&#39;s next.</a> Journal of Experimental Marine Biology and Ecology. 44 (5), 476-476 (1996).</li><li>McClintock, J. B., Baker, B. J. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=.">.</a> Marine Chemical Ecology. , (2001).</li><li>Amsler, C. D. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=.">.</a> Algal Chemical Ecology. , (2008).</li><li>Hay, M. E. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Marine+chemical+ecology:+Chemical+signals+and+cues+structure+marine+populations,+communities,+and+ecosystems.">Marine chemical ecology: Chemical signals and cues structure marine populations, communities, and ecosystems.</a> Annual Review of Marine Science. 1, 193-212 (2009).</li><li>Pawlik, J. R. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=The+chemical+ecology+of+sponges+on+Caribbean+reefs:+Natural+products+shape+natural+systems.">The chemical ecology of sponges on Caribbean reefs: Natural products shape natural systems.</a> BioScience. 61 (11), 888 (2011).</li><li>Pawlik, J. R. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Antipredatory+Defensive+Roles+of+Natural+Products+from+Marine+Invertebrates.">Antipredatory Defensive Roles of Natural Products from Marine Invertebrates.</a> Handbook of Marine Natural Products. , 677-710 (2012).</li><li>Pawlik, J. R., Amsler, C. D., Ritson-Williams, R., McClintock, J. B., Baker, B. J., Paul, V. J. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Marine+Chemical+Ecology:+A+Science+Born+of+Scuba.+.">Marine Chemical Ecology: A Science Born of Scuba. .</a> Research and Discoveries: The Revolution of Science through Scuba. 39, 53-69 (2013).</li><li>Randall, J. E., Hartman, W. D. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Sponge-feeding+fishes+of+the+West+Indies.">Sponge-feeding fishes of the West Indies.</a> Marine Biology. 1, 216-225 (1968).</li><li>Bakus, G. J., Green, G. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Toxicity+in+sponges+and+holothurians+&#8212;+geographic+pattern.">Toxicity in sponges and holothurians &#8212; geographic pattern.</a> Science. 185, 951-953 (1974).</li><li>Pawlik, J. R., Chanas, B., Toonen, R. J., Fenical, W. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Defenses+of+Caribbean+sponges+against+predatory+reef+fish.+1.+Chemical+deterrency.">Defenses of Caribbean sponges against predatory reef fish. 1. Chemical deterrency.</a> Marine Ecology Progress Series. 127, 183-194 (1995).</li><li>Schulte, B. A., Bakus, G. J. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Predation+deterrence+in+marine+sponges+&#8212;+laboratory+versus+field+studies.">Predation deterrence in marine sponges &#8212; laboratory versus field studies.</a> Bulletin of Marine Science. 50, 205-211 (1992).</li><li>Jackson, J. B. C., Buss, L. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Allelopathy+and+spatial+competition+among+coral+reef+invertebrates.">Allelopathy and spatial competition among coral reef invertebrates.</a> Proceedings of the National Academy of Sciences. 72, 5160-5163 (1975).</li><li>Bakus, G. J. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Chemical+defense+mechanisms+on+the+great+barrier+reef.">Chemical defense mechanisms on the great barrier reef.</a> Australia. Science. 211, 497-499 (1981).</li><li>Gemballa, S., Schermutzki, F. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Cytotoxic+haplosclerid+sponges+preferred:+a+field+study+on+the+diet+of+the+dotted+sea+slug+Peltodoris+atromaculata+(doridoidea:+nudibranchia).">Cytotoxic haplosclerid sponges preferred: a field study on the diet of the dotted sea slug Peltodoris atromaculata (doridoidea: nudibranchia).</a> Marine Biology. 144, 1213-1222 (2004).</li><li>Voogd, N. J., Cleary, D. F. R. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Relating+species+traits+to+environmental+variables+in+Indonesian+coral+reef+sponge+assemblages.">Relating species traits to environmental variables in Indonesian coral reef sponge assemblages.</a> Marine and Freshwater Research. 58, 240-249 (2007).</li><li>Mollo, E., et al. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Factors+promoting+marine+invasions:+a+chemolecological+approach.">Factors promoting marine invasions: a chemolecological approach.</a> Proceedings of the National Academy of Sciences. 105, 4582-4586 (2008).</li><li>Randall, J. E. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Food+habits+of+reef+fishes+of+the+West+Indies.">Food habits of reef fishes of the West Indies.</a> Studies in Tropical Oceanography. 5, 665-847 (1967).</li><li>O'Neal, W., Pawlik, J. R. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=A+reappraisal+of+the+chemical+and+physical+defenses+of+Caribbean+gorgonian+corals+against+predatory+fishes.">A reappraisal of the chemical and physical defenses of Caribbean gorgonian corals against predatory fishes.</a> Marine Ecology Progress Series. 240, 117-126 (2002).</li><li>Hines, D. E., Pawlik, J. R. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Assessing+the+antipredatory+defensive+strategies+of+Caribbean+non-scleractinian+zoantharians+(Cnidaria):+is+the+sting+the+only+thing.">Assessing the antipredatory defensive strategies of Caribbean non-scleractinian zoantharians (Cnidaria): is the sting the only thing.</a> Marine Biology. 159 (2), 389-398 (2012).</li><li>Walters, K. D., Pawlik, J. R. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Is+there+a+trade-off+between+wound-healing+and+chemical+defenses+among+Caribbean+reef+sponges.">Is there a trade-off between wound-healing and chemical defenses among Caribbean reef sponges.</a> Integrative and Comparative Biology. 45 (2), 352-358 (2005).</li><li>Leong, W., Pawlik, J. R. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Evidence+of+a+resource+trade-off+between+growth+and+chemical+defenses+among+Caribbean+coral+reef+sponges.">Evidence of a resource trade-off between growth and chemical defenses among Caribbean coral reef sponges.</a> Marine Ecology Progress Series. 406, 71-78 (2010).</li><li>Leong, W., Pawlik, J. R. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Comparison+of+reproductive+patterns+among+7+Caribbean+sponge+species+does+not+reveal+a+resource+trade-off+with+chemical+defenses.">Comparison of reproductive patterns among 7 Caribbean sponge species does not reveal a resource trade-off with chemical defenses.</a> Journal of Experimental Marine Biology and Ecology. 401 (1-2), 80-84 (2011).</li><li>Pawlik, J. R., Loh, T. -. L., McMurray, S. E., Finelli, C. M. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Sponge+Communities+on+Caribbean+Coral+Reefs+Are+Structured+by+Factors+That+Are+Top-Down,+Not+Bottom-Up.">Sponge Communities on Caribbean Coral Reefs Are Structured by Factors That Are Top-Down, Not Bottom-Up.</a> PLoS ONE. 8 (5), e62573 (2013).</li><li>Loh, T. -. L., Pawlik, J. R. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Chemical+defenses+and+resource+trade-offs+structure+sponge+communities+on+Caribbean+coral+reefs.">Chemical defenses and resource trade-offs structure sponge communities on Caribbean coral reefs.</a> Proceedings of the National Academy of Science. 111, 4151-4156 (2014).</li><li>Miller, A. M., Pawlik, J. R. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Do+coral+reef+fish+learn+to+avoid+unpalatable+prey+using+visual+cues.">Do coral reef fish learn to avoid unpalatable prey using visual cues.</a> Animal Behaviour. 85, 339-347 (2013).</li><li>Pawlik, J. R., Fenical, W. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=A+re-evaluation+of+the+ichthyodeterrent+role+of+prostaglandins+in+the+Caribbean+gorgonian+coral,+Plexaura+homomalla.">A re-evaluation of the ichthyodeterrent role of prostaglandins in the Caribbean gorgonian coral, Plexaura homomalla.</a> Marine Ecology Progress Series. 52, 95-98 (1989).</li><li>Fenical, W., Pawlik, J. R. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Defensive+properties+of+secondary+metabolites+from+the+Caribbean+gorgonian+coral+Erythropodium+caribaeorum.">Defensive properties of secondary metabolites from the Caribbean gorgonian coral Erythropodium caribaeorum.</a> Marine Ecology Progress Series. 75, 1-8 (1991).</li><li>Pawlik, J. R., Fenical, W. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Chemical+defense+of+Pterogorgia+anceps,+a+Caribbean+gorgonian+coral.">Chemical defense of Pterogorgia anceps, a Caribbean gorgonian coral.</a> Marine Ecology Progress Series. 87, 183-188 (1992).</li><li>Chanas, B., Pawlik, J. R. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Does+the+skeleton+of+a+sponge+provide+a+defense+against+predatory+reef+fish.">Does the skeleton of a sponge provide a defense against predatory reef fish.</a> Oecologia. 107 (2), 225-231 (1996).</li><li>Chanas, B., Pawlik, J. R., Lindel, T., Fenical, W. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Chemical+defense+of+the+Caribbean+sponge+Agelas+clathrodes+(Schmidt).">Chemical defense of the Caribbean sponge Agelas clathrodes (Schmidt).</a> Journal of Experimental Marine Biology and Ecology. 208 (1-2), 185-196 (1997).</li><li>Wilson, D. M., Puyana, M., Fenical, W., Pawlik, J. R. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Chemical+defense+of+the+Caribbean+reef+sponge+Axinella+corrugata+against+predatory+fishes.">Chemical defense of the Caribbean reef sponge Axinella corrugata against predatory fishes.</a> Journal of Chemical Ecology. 25 (12), 2811-2823 (1999).</li><li>Chanas, B., Pawlik, J. R. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Defenses+of+Caribbean+sponges+against+predatory+reef+fish+II.+Spicules,+tissue+toughness,+and+nutritional+quality.">Defenses of Caribbean sponges against predatory reef fish II. Spicules, tissue toughness, and nutritional quality.</a> Marine Ecology Progress Series. 127 (1), 195-211 (1995).</li><li>Albrizio, S., Ciminiello, P., Fattorusso, E., Magno, S., Pawlik, J. R. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Amphitoxin,+a+new+high+molecular+weight+antifeedant+pyridinium+salt+from+the+Caribbean+sponge+Amphimedon+compressa.">Amphitoxin, a new high molecular weight antifeedant pyridinium salt from the Caribbean sponge Amphimedon compressa.</a> Journal of Natural Products. 58 (5), 647-652 (1995).</li><li>Assmann, M., Lichte, E., Pawlik, J. R., K&#246;ck, M. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=.">.</a> Chemical defenses of the Caribbean sponges Agelas wiedenmayeri and Agelas conifera. Marine Ecology Progress Series. 207, 255-262 (2000).</li><li>Kubanek, J., Fenical, W., Pawlik, J. R. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=New+antifeedant+triterpene+glycosides+from+the+Caribbean+sponge+Erylus+Formosus.">New antifeedant triterpene glycosides from the Caribbean sponge Erylus Formosus.</a> Natural Product Letters. 15 (4), 275-285 (2001).</li><li>Pawlik, J. R., McFall, G., Zea, S. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Does+the+odor+from+sponges+of+the+genus+Ircinia+protect+them+from+fish+predators.">Does the odor from sponges of the genus Ircinia protect them from fish predators.</a> Journal of Chemical Ecology. 28 (6), 1103-1115 (2002).</li><li>Waddell, B., Pawlik, J. R. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Defenses+of+Caribbean+sponges+against+invertebrate+predators.+I.+Assays+with+hermit+crabs.">Defenses of Caribbean sponges against invertebrate predators. I. Assays with hermit crabs.</a> Marine Ecology Progress Series. 195, 125-132 (2000).</li><li>Waddell, B., Pawlik, J. R. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Defense+of+Caribbean+sponges+against+invertebrate+predators.+II.+Assays+with+sea+stars.">Defense of Caribbean sponges against invertebrate predators. II. Assays with sea stars.</a> Marine Ecology Progress Series. 195, 133-144 (2000).</li><li>Burns, E., Ifrach, I., Carmeli, S., Pawlik, J. R., Ilan, M. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Comparison+of+anti-predatory+defenses+of+Red+Sea+and+Caribbean+sponges.+I.+Chemical+defense.">Comparison of anti-predatory defenses of Red Sea and Caribbean sponges. I. Chemical defense.</a> Marine Ecology Progress Series. 252, 105-114 (2003).</li><li>Jones, A. C., Blum, J. E., Pawlik, J. R. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Testing+for+defensive+synergy+in+Caribbean+sponges:+Bad+taste+or+glass+spicules.">Testing for defensive synergy in Caribbean sponges: Bad taste or glass spicules.</a> Journal of Experimental Marine Biology and Ecology. 322 (1), 67 (2005).</li></ol>

The authors declare that they have no competing financial interests.

The procedure described herein provides a relatively simple, ecologically relevant laboratory protocol for assessing antipredatory chemical defenses in marine organisms. Here we review the important criteria that are satisfied by this set of methods:
(1) Appropriate predator. This feeding assay employs the bluehead wrasse, Thalassoma bifasciatum, one of the most abundant fishes on coral reefs throughout the Caribbean. The bluehead is a generalist carnivore known to sample a w...

Chemical ecology developed through the collaboration of chemists and ecologists. While the subdiscipline of terrestrial chemical ecology has been around for some time, that of marine chemical ecology is only a few decades old but has provided important insights into the evolutionary ecology and community structure of marine organisms1-8. Taking advantage of the emergent technologies of SCUBA diving and NMR spectroscopy, organic chemists rapidly generated a great number of publications describing novel metabolites from benthic marine invertebrates and algae in the 1970s and 1980s9. Assuming that secondary metabolites must serve some purpose, many of these publications ascribed ecologically important properties to new compounds without empirical evidence. At about the same time, ecologists were also taking advantage of the advent of SCUBA diving and describing the distributions and abundances of benthic animals and plants previously known from relatively ineffective sampling methods such as dredging. The assumption of these researchers was that anything sessile and soft-bodied must be chemically defended to avoid consumption by predators10. In an effort to introduce empiricism to what was otherwise descriptive work on species abundances, some ecologists began extrapolating chemical defenses from toxicity assays11. Most toxicity assays involved the exposure of whole fish or other organisms to aqueous suspensions of crude organic extracts of invertebrate tissues, with subsequent determination of the dry mass concentrations of extracts responsible for killing half the assay organisms. However, toxicity assays do not emulate the manner in which potential predators perceive prey under natural conditions, and subsequent studies have found no relationship between toxicity and palatability12-13. It is surprising that publications in prestigious journals used techniques having little or no ecological relevance14-15 and that these studies are still widely cited today. It is even more alarming to note that studies based on toxicity data continue to be published16-18. The bioassay method described herein was developed in the late 1980s to provide an ecologically relevant approach for marine chemical ecologists to assess antipredatory chemical defenses. The method requires a model predator to sample a crude organic extract from the target organism at a natural concentration in a nutritionally comparable food matrix, providing palatability data that are more ecologically meaningful than toxicity data.
The general approach to assessing the antipredatory activity of the tissues of marine organisms includes four important criteria: (1) an appropriate generalist predator must be used in feeding assays, (2) organic metabolites of all polarities must be exhaustively extracted from the tissue of the target organism, (3) the metabolites must be mixed into a nutritionally appropriate experimental food at the same volumetric concentration as found in the organism from which they were extracted, and (4) the experimental design and statistical approach must provide a meaningful metric to indicate relative distastefulness.
The procedure outlined below is designed specifically to assess antipredatory chemical defenses in Caribbean marine invertebrates. We employ the bluehead wrasse, Thalassoma bifasciatum, as a model predatory fish because this species is common on Caribbean coral reefs and is known to sample a wide assortment of benthic invertebrates19. Tissue from the target organism is first extracted, then combined with a food mixture, and finally offered to groups of T. bifasciatum to observe whether they reject the extract-treated foods. Assay data using this method have provided important insights into the defensive chemistry of marine organisms12,20-21, life history trade-offs22-24, and community ecology25-26.

<table border="0" cellpadding="0" cellspacing="0">
	<tbody>
		<tr>
			<td>Dichloromethane</td>
			<td>Fisher Scientific</td>
			<td>D37-20</td>
			<td></td>
		</tr>
		<tr>
			<td>Methanol</td>
			<td>Fisher Scientific</td>
			<td>A41220</td>
			<td></td>
		</tr>
		<tr>
			<td>Anhydrous Calcium Chloride</td>
			<td>Fisher Scientific</td>
			<td>C614-500</td>
			<td></td>
		</tr>
		<tr>
			<td>Cryocool Heat Transfer Fluid</td>
			<td>Fisher Scientific</td>
			<td>20-548-146</td>
			<td>For vacuum concentrator</td>
		</tr>
		<tr>
			<td>Alginic Acid Sodium Salt High Viscosity</td>
			<td>MP Biomedicals</td>
			<td>154723</td>
			<td></td>
		</tr>
		<tr>
			<td>Squid mantle rings</td>
			<td>N/A</td>
			<td>N/A</td>
			<td>Can be purchased at grocery store</td>
		</tr>
		<tr>
			<td>Denatonium benzoate</td>
			<td>Aldrich</td>
			<td>D5765</td>
			<td></td>
		</tr>
		<tr>
			<td>50 ml graduated centrifuge tube</td>
			<td>Fisher Scientific</td>
			<td>14-432-22</td>
			<td></td>
		</tr>
		<tr>
			<td>20 ml scintillation vial</td>
			<td>Fisher Scientific</td>
			<td>03-337-7</td>
			<td></td>
		</tr>
		<tr>
			<td>Disposable Pasteur pipets</td>
			<td>Fisher Scientific</td>
			<td>13-678-20D</td>
			<td></td>
		</tr>
		<tr>
			<td>Rubber bulbs for Pasteur pipets</td>
			<td>Fisher Scientific</td>
			<td>03-448-24</td>
			<td></td>
		</tr>
		<tr>
			<td>Red bulbs for pellet delivery</td>
			<td>Fisher Scientific</td>
			<td>03-448-27</td>
			<td></td>
		</tr>
		<tr>
			<td>250 ml round-bottom flask</td>
			<td>Fisher Scientific</td>
			<td>10-067E</td>
			<td></td>
		</tr>
		<tr>
			<td>Scintillation vial adapter for rotavap</td>
			<td>Fisher Scientific</td>
			<td>K747130-1324</td>
			<td></td>
		</tr>
		<tr>
			<td>Weightboats</td>
			<td>Fisher Scientific</td>
			<td>02-202B</td>
			<td></td>
		</tr>
		<tr>
			<td>Microspatula</td>
			<td>Fisher Scientific</td>
			<td>21-401-10</td>
			<td></td>
		</tr>
		<tr>
			<td>5 ml graduated syringe</td>
			<td>Fisher Scientific</td>
			<td>14-817-53</td>
			<td></td>
		</tr>
		<tr>
			<td>10 ml graduated syringe</td>
			<td>Fisher Scientific</td>
			<td>14-817-54</td>
			<td></td>
		</tr>
		<tr>
			<td>Razor blade</td>
			<td>Fisher Scientific</td>
			<td>S17302</td>
			<td></td>
		</tr>
	</tbody>
</table>

a fish-feeding laboratory bioassay to assess the antipredatory activity of secondary metabolites from the tissues of marine organisms

Marine chemical ecology is a young discipline, having emerged from the collaboration of natural products chemists and marine ecologists in the 1980s with the goal of examining the ecological functions of secondary metabolites from the tissues of marine organisms. The result has been a progression of protocols that have increasingly refined the ecological relevance of the experimental approach. Here we present the most up-to-date version of a fish-feeding laboratory bioassay that enables investigators to assess the antipredatory activity of secondary metabolites from the tissues of marine organisms. Organic metabolites of all polarities are exhaustively extracted from the tissue of the target organism and reconstituted at natural concentrations in a nutritionally appropriate food matrix. Experimental food pellets are presented to a generalist predator in laboratory feeding assays to assess the antipredatory activity of the extract. The procedure described herein uses the bluehead, Thalassoma bifasciatum, to test the palatability of Caribbean marine invertebrates; however, the design may be readily adapted to other systems. Results obtained using this laboratory assay are an important prelude to field experiments that rely on the feeding responses of a full complement of potential predators. Additionally, this bioassay can be used to direct the isolation of feeding-deterrent metabolites through bioassay-guided fractionation. This feeding bioassay has advanced our understanding of the factors that control the distribution and abundance of marine invertebrates on Caribbean coral reefs and may inform investigations in diverse fields of inquiry, including pharmacology, biotechnology, and evolutionary ecology.

Here we report results of this bioassay for six species of common Caribbean sponges (Figure 2). These data were initially published in 1995 by Pawlik et al.12 and demonstrate the power of this approach to survey differences in chemical defense strategies among co-occurring taxa. Results were reported as a mean number of food pellets eaten + standard error (SE) for each species. Almost no pellets were eaten in assays with crude organic extracts from Agelas clathrodes, Amph...

Watch this Scientific Journal Video about A Fish-feeding Laboratory Bioassay to Assess the Antipredatory Activity of Secondary Metabolites from the Tissues of Marine Organisms at JoVE.com

A Fish-feeding Laboratory Bioassay to Assess the Antipredatory Activity of Secondary Metabolites from the Tissues of Marine Organisms

This bioassay employs a model predatory fish to assess the presence of feeding-deterrent metabolites from organic extracts of the tissues of marine organisms at natural concentrations using a nutritionally comparable food matrix.

Marine chemical ecology is a young discipline, having emerged from the collaboration of natural products chemists and marine ecologists in the 1980s with ...

a-fish-feeding-laboratory-bioassay-to-assess-antipredatory-activity

Research

JoVE Journal

Environment

9.4K 次观看.  University of North Carolina Wilmington. 这种生物测定采用模型肉食性鱼类，以评估喂食威慑代谢产物从海洋生物的天然浓度的组织有机提取物用营养可比食品基质的存在。 

视频: A Fish-feeding Laboratory Bioassay to Assess the Antipredatory Activity of Secondary Metabolites from the Tissues of Marine Organisms

A Small Volume Bioassay to Assess Bacterial/Phytoplankton Co-culture Using WATER-Pulse-Amplitude-Modulated (WATER-PAM) Fluorometry

Conventional methods for experimental manipulation of microalgae have employed large volumes of culture (20 ml to 5 L), so that the culture can be subsampled throughout the experiment1&#8211;7. Subsampling of large volumes can be problematic for several reasons: 1) it causes variation in the total volume and the surface area:volume ratio of the culture during the experiment; 2) pseudo-replication (i.e., replicate samples from the same treatment flask8) is often employed rather than true replicates (i.e., sampling from replicate treatments); 3) the duration of the experiment is limited by the total volume; and 4) axenic cultures or the usual bacterial microbiota are difficult to maintain during long-term experiments as contamination commonly occurs during subsampling.
The use of microtiter plates enables 1 ml culture volumes to be used for each replicate, with up to 48 separate treatments within a 12.65 x 8.5 x 2.2 cm plate, thereby decreasing the experimental volume and allowing for extensive replication without subsampling any treatment. Additionally, this technique can be modified to fit a variety of experimental formats including: bacterial-algal co-cultures, algal physiology tests, and toxin screening9&#8211;11. Individual wells with an alga, bacterium and/or co-cultures can be sampled for numerous laboratory procedures including, but not limited to: WATER-Pulse-Amplitude-Modulated (WATER-PAM) fluorometry, microscopy, bacterial colony forming unit (cfu) counts and flow cytometry. The combination of the microtiter plate format and WATER-PAM fluorometry allows for multiple rapid measurements of photochemical yield and other photochemical parameters with low variability between samples, high reproducibility and avoids the many pitfalls of subsampling a carboy or conical flask over the course of an experiment.

A Small Volume Bioassay to Assess Bacterial/Phytoplankton Co-culture Using WATER-Pulse-Amplitude-Modulated WATER-PAM Fluorometry

The goal of this procedure is to demonstrate the reproducibility and adaptability of using a microtiter plate format for microalgal screening. This rapid screen combines WATER-Pulse-Amplitude-Modulated (WATER-PAM) fluorometry to measure photosynthetic yield as an indicator of Photosystem II (PSII) health with small volume bacterial-algal co-cultures.

Conventional methods for experimental manipulation of microalgae have employed large volumes of culture (20 ml to 5 L), so that the culture can be ...

Automated Gel Size Selection to Improve the Quality of Next-generation Sequencing Libraries Prepared from Environmental Water Samples

Next-generation sequencing of environmental samples can be challenging because of the variable DNA quantity and quality in these samples. High quality DNA libraries are needed for optimal results from next-generation sequencing. Environmental samples such as water may have low quality and quantities of DNA as well as contaminants that co-precipitate with DNA. The mechanical and enzymatic processes involved in extraction and library preparation may further damage the DNA. Gel size selection enables purification and recovery of DNA fragments of a defined size for sequencing applications. Nevertheless, this task is one of the most time-consuming steps in the DNA library preparation workflow. The protocol described here enables complete automation of agarose gel loading, electrophoretic analysis, and recovery of targeted DNA fragments. 
In this study, we describe a high-throughput approach to prepare high quality DNA libraries from freshwater samples that can be applied also to other environmental samples. We used an indirect approach to concentrate bacterial cells from environmental freshwater samples; DNA was extracted using a commercially available DNA extraction kit, and DNA libraries were prepared using a commercial transposon-based protocol. DNA fragments of 500 to 800 bp were gel size selected using Ranger Technology, an automated electrophoresis workstation. Sequencing of the size-selected DNA libraries demonstrated significant improvements to read length and quality of the sequencing reads.

This manuscript describes an automated gel size selection approach for purifying DNA fragments for next-generation sequencing. The Ranger Technology provides complete automation of the entire process of agarose gel loading, electrophoretic analysis, and recovery of targeted DNA fragments allowing for high-throughput and high quality next-generation sequencing libraries.

Next-generation sequencing of environmental samples can be challenging because of the variable DNA quantity and quality in these samples. High quality DNA ...

Laboratory Simulation of an Iron(II)-rich Precambrian Marine Upwelling System to Explore the Growth of Photosynthetic Bacteria

A conventional concept for the deposition of some Precambrian Banded Iron Formations (BIF) proceeds on the assumption that ferrous iron [Fe(II)] upwelling from hydrothermal sources in the Precambrian ocean was oxidized by molecular oxygen [O2] produced by cyanobacteria. The oldest BIFs, deposited prior to the Great Oxidation Event (GOE) at about 2.4 billion years (Gy) ago, could have formed by direct oxidation of Fe(II) by anoxygenic photoferrotrophs under anoxic conditions. As a method for testing the geochemical and mineralogical patterns that develop under different biological scenarios, we designed a 40 cm long vertical flow-through column to simulate an anoxic Fe(II)-rich marine upwelling system representative of an ancient ocean on a lab scale. The cylinder was packed with a porous glass bead matrix to stabilize the geochemical gradients, and liquid samples for iron quantification could be taken throughout the water column. Dissolved oxygen was detected non-invasively via optodes from the outside. Results from biotic experiments that involved upwelling fluxes of Fe(II) from the bottom, a distinct light gradient from top, and cyanobacteria present in the water column, show clear evidence for the formation of Fe(III) mineral precipitates and development of a chemocline between Fe(II) and O2. This column allows us to test hypotheses for the formation of the BIFs by culturing cyanobacteria (and in the future photoferrotrophs) under simulated marine Precambrian conditions. Furthermore we hypothesize that our column concept allows for the simulation of various chemical and physical environments &#8212; including shallow marine or lacustrine sediments.

Laboratory Simulation of an IronII-rich Precambrian Marine Upwelling System to Explore the Growth of Photosynthetic Bacteria

We simulated a Precambrian ferruginous marine upwelling system in a lab-scale vertical flow-through column. The goal was to understand how geochemical profiles of O2 and Fe(II) evolve as cyanobacteria produce O2. The results show the establishment of a chemocline due to Fe(II) oxidation by photosynthetically produced O2.

A conventional concept for the deposition of some Precambrian Banded Iron Formations (BIF) proceeds on the assumption that ferrous iron [Fe(II)] upwelling ...

Ecotoxicological Method with Marine Bacteria Vibrio anguillarum to Evaluate the Acute Toxicity of Environmental Contaminants

Bacteria are an important component of the ecosystem, and microbial community alterations can have a significant effect on biogeochemical cycling and food webs. Toxicity testing based on microorganisms are widely used because they are relatively quick, reproducible, cheap, and are not associated with ethical issues. Here, we describe an ecotoxicological method to evaluate the biological response of the marine bacterium Vibrio anguillarum. This method assesses the acute toxicity of chemical compounds, including new contaminants such as nanoparticles, as well as environmental samples. The endpoint is the reduction of bacterial culturability (i.e., the capability to replicate and form colonies) due to exposure to a toxicant. This reduction can be generally referred to as mortality. The test allows for the determination of the LC50, the concentration that causes a 50% decrease of bacteria actively replicating and forming colonies, after a 6 h exposure. The culturable bacteria are counted in terms of colony forming units (CFU), and the &#34;mortality&#34; is evaluated and compared to the control. In this work, the toxicity of copper sulphate (CuSO4) was evaluated. A clear dose-response relationship was observed, with a mean LC50 of 1.13 mg/L, after three independent tests. This protocol, compared to existing methods with microorganisms, is applicable in a wider range of salinity and has no limitations for colored/turbid samples. It uses saline solution as the exposure medium, avoiding any possible interferences of growth medium with the investigated contaminants. The LC50 calculation facilitates comparisons with other bioassays commonly applied to ecotoxicological assessments of the marine environment.

Ecotoxicological Method with Marine Bacteria Vibrio anguillarum to Evaluate the Acute Toxicity of Environmental Contaminants

This work describes a new protocol to assess the ecotoxicity of pollutants, including emerging contaminants such as nanomaterials, using the marine bacterium Vibrio anguillarum. This method allows for the determination of the LC50, or mortality, the concentration that causes a 50% decrease in bacteria culturability, after a 6 h exposure.

Bacteria are an important component of the ecosystem, and microbial community alterations can have a significant effect on biogeochemical cycling and food ...

Extraction of Organochlorine Pesticides from Plastic Pellets and Plastic Type Analysis

Plastic resin pellets, categorized as microplastics (&#8804;5 mm in diameter), are small granules that can be unintentionally released to the environment during manufacturing and transport. Because of their environmental persistence, they are widely distributed in the oceans and on beaches all over the world. They can act as a vector of potentially toxic organic compounds (e.g., polychlorinated biphenyls) and might consequently negatively affect marine organisms. Their possible impacts along the food chain are not yet well understood. In order to assess the hazards associated with the occurrence of plastic pellets in the marine environment, it is necessary to develop methodologies that allow for rapid determination of associated organic contaminant levels. The present protocol describes the different steps required for sampling resin pellets, analyzing adsorbed organochlorine pesticides (OCPs) and identifying the plastic type. The focus is on the extraction of OCPs from plastic pellets by means of a pressurized fluid extractor (PFE) and on the polymer chemical analysis applying Fourier Transform-InfraRed (FT-IR) spectroscopy. The developed methodology focuses on 11 OCPs and related compounds, including dichlorodiphenyltrichloroethane (DDT) and its two main metabolites, lindane and two production isomers, as well as the two biologically active isomers of technical endosulfan. This protocol constitutes a simple and rapid alternative to existing methodology for evaluating the concentration of organic contaminants adsorbed on plastic pieces.

Microplastics act as vector of potentially toxic organic contaminants with unpredictable effects. This protocol describes an alternative methodology for assessing the levels of organochlorine pesticides adsorbed on plastic pellets and identifying the polymer chemical structure. The focus is on pressurized fluid extraction and attenuated total reflectance Fourier transform infrared spectroscopy.

Plastic resin pellets, categorized as microplastics (&#8804;5 mm in diameter), are small granules that can be unintentionally released to the environment ...

Development of New Methods for Quantifying Fish Density Using Underwater Stereo-video Tools

The use of video camera systems in ecological studies of fish continues to gain traction as a viable, non-extractive method of measuring fish lengths and estimating fish abundance. We developed and implemented a rotating stereo-video camera tool that covers a full 360 degrees of sampling, which maximizes sampling effort compared to stationary camera tools. A variety of studies have detailed the ability of static, stereo-camera systems to obtain highly accurate and precise measurements of fish; the focus here was on the development of methodological approaches to quantify fish density using rotating camera systems. The first approach was to develop a modification of the metric MaxN, which typically is a conservative count of the minimum number of fish observed on a given camera survey. We redefine MaxN to be the maximum number of fish observed in any given rotation of the camera system. When precautions are taken to avoid double counting, this method for MaxN may more accurately reflect true abundance than that obtained from a fixed camera. Secondly, because stereo-video allows fish to be mapped in three-dimensional space, precise estimates of the distance-from-camera can be obtained for each fish. By using the 95% percentile of the observed distance from camera to establish species-specific areas surveyed, we account for differences in detectability among species while avoiding diluting density estimates by using the maximum distance a species was observed. Accounting for this range of detectability is critical to accurately estimate fish abundances. This methodology will facilitate the integration of rotating stereo-video tools in both applied science and management contexts.

We describe a new method for counting fishes, and estimating relative abundance (MaxN) and fish density using rotating stereo-video camera systems. We also demonstrate how to use distance from camera (Z distance) to estimate species-specific detectability.

The use of video camera systems in ecological studies of fish continues to gain traction as a viable, non-extractive method of measuring fish lengths and ...

The Barnacle Balanus improvisus as a Marine Model - Culturing and Gene Expression

Barnacles are marine crustaceans with a sessile adult and free-swimming, planktonic larvae. The barnacle Balanus (Amphibalanus) improvisus is particularly relevant as a model for the studies of osmoregulatory mechanisms because of its extreme tolerance to low salinity. It is also widely used as a model of settling biology, in particular in relation to antifouling research. However, natural seasonal spawning yields an unpredictable supply of cyprid larvae for studies. A protocol for the all-year-round culturing of B. improvisus has been developed and a detailed description of all steps in the production line is outlined (i.e., the establishment of adult cultures on panels, the collection and rearing of barnacle larvae, and the administration of feed for adults and larvae). The description also provides guidance on troubleshooting and discusses critical parameters (e.g., the removal of contamination, the production of high-quality feed, the manpower needed, and the importance of high-quality seawater). Each batch from the culturing system maximally yields roughly 12,000 nauplii and can deliver four batches in a week, so up to almost 50,000 larvae per week can be produced. The method used to culture B. improvisus is, probably, to a large extent also applicable to other marine invertebrates with free-swimminglarvae. Protocols are presented for the dissection of various tissues from adults as well as the production of high-quality RNA for studies on gene expression. It is also described how cultured adults and reared cyprids can be utilized in a wide array of experimental designs for examining gene expression in relation to external factors. The use of cultured barnacles in gene expression is illustrated with studies of possible osmoregulatory roles of Na+/K+ ATPase and aquaporins.

The Barnacle Balanus improvisus as a Marine Model - Culturing and Gene Expression

The barnacle Balanus (Amphibalanus) improvisus is a model for studying osmoregulation and antifouling. However, natural seasonal spawning yields an unpredictable supply of cyprid larvae. Here, a protocol for the all-year-round culturing of B. improvisus is described, including the production of larvae. The use of cultured barnacles in gene expression studies is illustrated.

Barnacles are marine crustaceans with a sessile adult and free-swimming, planktonic larvae. The barnacle Balanus (Amphibalanus) improvisus is particularly ...

Long-term Video Tracking of Cohoused Aquatic Animals: A Case Study of the Daily Locomotor Activity of the Norway Lobster (Nephrops norvegicus)

We present a protocol related to a video-tracking technique based on the background subtraction and image thresholding that makes it possible to individually track cohoused animals. We tested the tracking routine with four cohoused Norway lobsters (Nephrops norvegicus) under light-darkness conditions for 5 days. The lobsters had been individually tagged. The experimental setup and the tracking techniques used are entirely based on the open source software. The comparison of the tracking output with a manual detection indicates that the lobsters were correctly detected 69% of the times. Among the correctly detected lobsters, their individual tags were correctly identified 89.5% of the times. Considering the frame rate used in the protocol and the movement rate of lobsters, the performance of the video tracking has a good quality, and the representative results support the validity of the protocol in producing valuable data for research needs (individual space occupancy or locomotor activity patterns). The protocol presented here can be easily customized and is, hence, transferable to other species where the individual tracking of specimens in a group can be valuable for answering research questions.

Long-term Video Tracking of Cohoused Aquatic Animals: A Case Study of the Daily Locomotor Activity of the Norway Lobster Nephrops norvegicus

Here we present a protocol to individually track animals over a long period of time. It uses computer vision methods to identify a set of manually constructed tags by using a group of lobsters as case study, simultaneously providing information on how to house, manipulate, and mark the lobsters.

We present a protocol related to a video-tracking technique based on the background subtraction and image thresholding that makes it possible to ...

Microfocus X-ray CT (microCT) Imaging of Actinia equina (Cnidaria), Harmothoe sp. (Annelida), and Xenoturbella japonica (Xenacoelomorpha)

Traditionally, biologists have had to rely on destructive methods such as sectioning in order to investigate the internal structures of opaque organisms. Non-destructive microfocus X-ray computed tomography (microCT) imaging has become a powerful and emerging protocol in biology, due to technological advancements in sample staining methods and innovations in microCT hardware, processing computers, and data analysis software. However, this protocol is not commonly used, as it is in the medical and industrial fields. One of the reasons for this limited use is the lack of a simple and comprehensible manual that covers all of the necessary steps: sample collection, fixation, staining, mounting, scanning, and data analyses. Another reason is the vast diversity of metazoans, particularly marine invertebrates. Because of marine invertebrates&#8217; diverse sizes, morphologies, and physiologies, it is crucial to adjust experimental conditions and hardware configurations at each step, depending on the sample. Here, microCT imaging methods are explained in detail using three phylogenetically diverse marine invertebrates: Actinia equina (Anthozoa, Cnidaria), Harmothoe sp. (Polychaeta, Annelida), and Xenoturbella japonica (Xenoturbellida, Xenacoelomorpha). Suggestions on performing microCT imaging on various animals are also provided.

Microfocus X-ray CT microCT Imaging of Actinia equina Cnidaria, Harmothoe sp. Annelida, and Xenoturbella japonica Xenacoelomorpha

Here, protocols for performing microfocus X-ray computed tomography (microCT) imaging of three marine invertebrate animals are explained in detail. This study describes steps such as sample fixation, staining, mounting, scanning, image reconstruction, and data analyses. Suggestions on how the protocol can be adjusted for different samples are also provided.

Traditionally, biologists have had to rely on destructive methods such as sectioning in order to investigate the internal structures of opaque organisms. ...

Rapid Testing of Resistance of Timber to Biodegradation by Marine Wood-Boring Crustaceans

Wood-boring invertebrates rapidly destroy marine timbers and wooden coastal infrastructure, causing billions of dollars of damage around the globe every year. As treatments of wood with broad spectrum biocides, such as creosote and chromated copper arsenate (CCA), are now restricted in marine use by legislation, naturally durable timber species and novel preservation methods of wood are required. These methods undergo testing in order to meet regulatory standards, such as the European standard for testing wood preservatives against marine borers, EN 275. Initial investigation of durable timbers species or wood preservative treatments can be achieved quickly and inexpensively through laboratory testing, which offers many advantages over marine field trials that are typically costly, long-term endeavours. Many species of Limnoria (gribble) are marine wood-boring crustaceans. Limnoria are ideal for use in laboratory testing of biodegradation of wood by marine wood-borers, due to the practicality of rearing them in aquaria and the ease of measuring their feeding rates on wood. Herein, we outline a standardizable laboratory test for assessing wood biodegradation using gribble.

This protocol presents a method for assessing the feeding rate of the wood-boring crustacean, Limnoria, by measuring faecal pellet production. This method is designed for use in non-specialist labs and has potential for incorporation into standard testing protocols, to evaluate enhanced wood durability under marine conditions.

Wood-boring invertebrates rapidly destroy marine timbers and wooden coastal infrastructure, causing billions of dollars of damage around the globe every ...