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IMPACTOFA VALIDATED, COST EFFECTIVESCREEN FOR CIGUATERIC FISH RICHARD LEWIS J. Lewis, RJ. 1994 08 01: Impact of a validated, cost effective screen for ciguatcric fish. Memoirsofthe QueenslandMuseum34(3):549-553. Brisbane. ISSN0079-8835. Cigiutoxinscontaminatingciguateric fishmaybedetectedbyarangeofinvivo(e.g.mouse- cat,mosquitoorchicken),invitro(ELISA.atria)andchemicalassays.Currentresearchseeks a selective screen todetect low levels ofciguatoxin-1 (0.05-5.0ppb) in fish flesh or in an easy-to-prepareextract. Thisreviewsummarisesrequirementsforavalidated,costeffective screenforciguatericfish.Implementationofsuchascreenwillreduceadversehealtheffects. Anattendantbenefit will be theimproved marketabilityofreeffish. RichardJ.J^ewis.SouthernFisheriesCentre, QueenslandDepartmentofPrimaryInduslries, POBox76, DeceptionBay. Queensland4508; 22November.1993. One important goal of present-day ciguatera alsoundeTdevelopment and this approachholds research is the development of a cost-effective muchpromiseforthedetectionofciguatericfish. screen for the toxins contaminating ciguateric These assays remain to be validated for their fish (Lewis.1993). Therange oftoxins involved ability lo selectively detect ciguatoxins in crude in ciguatera hasbeenthe subjectofsomedebate. extractsoffish Wevalidatedthemouseassayfor fIte.agp.pgeaarrnsbtiheantooxnilnyst)hearceigiunavtoolxviends(aMnudraantaaloelguael.s, c&igSuealltionx,i1n99i3n)u.pThtois2a0smsgayowfaesthoenrlyexatbrlaectto(dIext:ewic*t 1990; Legrand et al.,1992; Lewis et a!.,1991) CTX-1 at>0.5ppb in fish flesh. Importantly, this These toxins are closely related in structure and study found that 63± 1496 of spiked ciguatoxin all activate voltage-dependent sodium channels. wasrecovered usingastandardextractionproce- Of these, CTX-1 typically contributes -90% of dure, thereby establishing its suitability for con- the toxicity ofciguateric carnivorous fish in the firming whether a fish sample was toxic or not. Pacific (Legrand et a!.,1992; Lewis & Sellin, The cost ofsuch an assay, as well as its insuffi- 3992) and should be considered the primary tar- cient sensitivity and ethical considerations. get of a screen for ciguateric fish. Other preclude the use ofthe mouse assay for routine dguatoxin analogues and toxins such as okadaic seafood monitoring programmes. This paper acid, maitotoxins or Trichodesmium toxins are summarisesrequirementsforavalidated,cost-ef- Likely to play a minor role in human illness fective screen for ciguateric fish and discusses However,theselowerpotencytoxinscouldinter- someofthe impactsofsuchatestonfisheriesand fere withtheresponseofascreen.Thechallenge fisheriesproducts. for researchers is to develop a method that can rapidly and selectively screen CTX-1 which is FEATURESOF A USEFUL SCREEN presentbetween0.1 and5ppb in the flesh offish thatcauseciguatera(Lewis,1992).Usinga2-fold A useful screen for delecting ciguateric fi^h risk factor to ensure public health is protected needstopossessthefollowingfeatures. 1, simple necessitatesthatthe screenbe capableofreliably implementation; 2, ready availability and long detecting CTX-1 in fish flesh atO.OSppb (50ppi) shelflife; 3, toxinselectivity proportional to the andabove. human oral potency ofthe ciguatoxin analogues A number of assays have been used to detect liehighestaffinity forCTX-1); 4, itshould yield ciguatoxin in fish. These include a range of in a linear response over the range of toxin con- vivo assays (e.g. mouse, cat chicken, mosquito; centrations encountered in ciguateric fish; 5, ac- Banneretal.,1960; Kimuraetta)..1982; Lewis & ceptable accuracy (±20%) atthe level of0.05ppb Endean,1984; Bagnisetal.,1985; Vemouxetal.. CTX-1 that is independent of the fish tested: ft. 1985), a number ofin vitro assays utilising anti- high recovery ofCTX-1 (>60%) during extrac- bodies (Hokama.1991) or isolated tissues tion and clean-up (>30% in exceptional u- (KimuraetaL!982)andchemicalassays involv- cumstances); and 7, total cost ofscreen must be ing derivatisation and HPLC separation with acceptable totheconsumer. fluorescence detection (Legrand et al.,1992; Prototype stick tests (Hokanria,1985; Hokama Dickey et al.,1992). Biosensor-type assays are el a).,1985; Hokama 199l) have many of the ( *w» MEMOIRSOFTHEQUEENSLAND MUSBUM *bove features, but this or modified versions of give rise to false positive results*. Tb-date die the test are still not readily available Published CToss-reactivuy of the antibodies in use for the results of screening of fish suggest ("but do not variousciguatoxinanalogueshasnotbeenestab- prove) that these tests have sufficient sensitivity lished. n.c, few false positive results reported). How- Anacceptablecost forciguaterascreening has ever,theapparenthighfrequencyoffalsepositive nolbeendetermined.Thiswill relatetotheadded results (i.e. non-toxic fishrejected) suggeststhat value screened fish will attract in the market- theantibodyemployedmayhavearelatively low place. An add-on cost of less than 10% of the specificity forCTX-1 value of the product may be reasonable. The A screen that utilises high affinity binding of 'cost* of a screening programme should incor- ciguatoxintoa cheapprotein substrate(e.g. IgO) poratean estimateofthecost ofdiscarding non- andcouplesthisinteractiontoa simplymeasured toxic fish as a result of false positive results It response(e.g. acolourchange) has a high likeli- may be possible to reduce the cost ofscreening hood of achieving an adequate compromise be- by pooling fish samples priorto screening. Such tween accuracy and cost. Such antibody-based anapproachrequiresahighlysensitivescreenbut screens have the potenMtial to detect ievels of could work where ciguatera is a low level prob- analytc as low as IO"i2 in food (Gazzaz et aL lem (e.g. Australia). This approach could not 1992). Howrvrr, matrix effects associated with work where non-toxic fish have levels of thetypeofsamplescreenedcanoftendramatical- ciguatoxinwithinanorderofmagnitudeofleveK ly reduce assay sensitivity. The extent of sueh thatcausehumanpoisoning. matrix effects can also vary with the solubility A blind screening of ciguatenc fish ftoflfl characteristics of the analyte. For solid food Australia (specimens confirmed ciguatenc by matrices, enzyme linked immunosorbentassays human and mice assays! with a prototype ofthe (ELISA) detected okadaic acid in shellfish of Ciguatect™ test kit (November,1991) revealed 10-300ppb (DSP-ehcck, Ubc Industries. Ltd, that therewere few. if any. false positive results Tokyo) and detected aflatoxins above lOp-pb However,merewasastrongpossibilitymatsome (Domer & Cnle,1989; Trucfcsess et al.,1989) or ciguatoxic samples went undetected by the test more recently above 1 ppb in a range of solid In fact five of six ofthe ciguateric fish samples foods (Agri-Screen test for aflatoxins, Neogen are likely to have given a false negative result Corporation, Michigan). The challenge is to Furthertestingofthese fish usinglatermodifica- develop a rapid screen for ciguatoxins that has tionsofthe Ciguatect™ testare notreported and onetotwoordersofmagnitudegreatersensitivity nosatisfactoryexplanationhasbeengivenforthe than presently availableELISAassays. A variety conflicting results obtained. These results were ofapproaches may be used to improve the sen- obtained at a time when the test was being con- sitivity ofantibody-based assays: (i) production sidered for commercial release. Since this time ofhigheraffinityantibodies(ii)optimisingassay modifications to the test have been made but a conditions in which the antibody is used (ill] final format for the Ciguatect™ test remains amplifying the assay signal (not always accom- elusive. paniedbyimprovedsignal tonoise)(iv)optimis ing sample extraction and clean-up (can add a TYPESOFANTIBODYASSAYS significant cost). The potential of the latter ap- AVAILABLE proach is indicated for ciguatoxin which can be concentrated fromthelevelsin fleshof0.1-5ppb Several approaches are available for incor- tolevelsof-3O-5.0O0ppbinacrude lipidextract porating antibodies (or similar proteins) into an withatwo-step clean-upprocedure thathas63% assay format for detecting haptens such as efficiency (Lewis& Sellin.1993). ciguatoxin (Fig.l). In all cases a label, be n a Toxins responsible forciguatera anse through radioisotope, an enzyme or a luminescent or the biotransformation of a number of gambier- fluorescent probe, is used to detect the targeted toxins produced by Gambierdiscus toxicity compound. Each approach has strengths and (Murataetal ,1990; HolmesetaL1991;Legrand weaknesses hut all require a high affinity an- et al.,1992). Soa rangeoflow potency formsof tibody that is selective and specific for the tar- the ciguatoxins and gambiertoxins (including geted hapten. The first assay considered is the CTX-2 and CTX-3) could accumulate in fish. indirecthapten assay which requires thatthetar- These low potency forms may be detected with geted hapten (eg. ciguatoxin) is first non-selec- antibodies raised to CTX-1 and ifso they could tivelyimmobilisedtoa solidsupport(alongwith SCREENFORCIGUATERICFISH 551 INDIRECT HAPTEN ASSAY extraction step. Tests developed for ciguatoxins by Hokama (1991) and morerecentlyby Hawaii Chemtect (Pasadena) have used this approach in the development ofa screen forciguateric fish. The second approach is to develop a sandwich assay. This requires development of two an- £><>(—) tibodies which can mutually bind the targeted hapten.Thisassaycanbemoreselectivethanthe direct assay although binding reactions in two- non-selective adsorption o( haptens to the solid phase site immunoassays are complex and not easily predicted (Boscato et al.,1989). This assay is limitedbythedifficultiesassociated withobtain- SANDWICH ASSAY ing two antibodies which don't interfere with each others binding to a small hapten such as ciguatoxin. The third approach is the direct competitive assay which requires that a second hapten is available that competes with the targeted hapten for binding to an antibody. With this approach eitherthe hapten or the antibody can be fixed to the solid phase. Unlike the first two assays, the unlabeled antibodies HgGI selctively fixed to the solid phase responseis inversely proportional to thetargeted hapten, but such a response is likely to be more specific for the targeted hapten than the former assays. Thedirectcompetitive assay likely holds DIRECT COMPETITIVE ASSAY mostpromise foran accurate screen but requires a competing hapten to be found. While it is pos- sible that the sandwich and competitive assays couldbedevelopedforthedirectsamplingoffish flesh, it is likely is that extraction and clean-up steps will be required. The solubility require- ments of the hapten and stability of antibody in solvent need to be considered if the assay is unlabeled antibodies HgGI selctively fixed to ihe solid phase designed to detect solubilised hapten. FIG.l. Antibody assays available for the detection of haptens suchasciguatoxin(CTX). Eitherthe IgGor SCREENVALIDATION hapten are labelled (L) with probe to indicate the presence ofthetargeted hapten. Other shapes repre- A number of criteria need to be met before a sent the range ofcompounds present along with the screen forciguateric fish can be considered use- targetedhapten.TheIgGcouldbereplacedwithother ful, including: 1, the screen must detect all fish proteins possessing a high affinity for the targeted samples confirmed ciguateric following human hapten (eg the sodium channel could be used for detectingciguatoxin).Thelargeboxineachdiagram consumption; 2, the screen musthave an accept- surrounds the interaction responding tothepresence ably low rate offalse positives (i.e. a false posi- oftargetedhapten,whileinteractionsbeyondthisbox tive rate within an order of magnitude of the resultinareduced(falsenegative)orenhanced(false reported ciguatera incidence for the species positive) assay response that is unrelated to the tested) and the cost offalse positive results must presenceofthetargetedhapten. beincluded inthecostofscreening; 3, thescreen must detect spiked CTX-1 in crude fish extracts numerous othercontaminants) priorto its detec- at levels occurring naturally and should detect tion with a labelled antibody specific forthe part CTX-1 spiked in a fish flesh homogenate; 4, the ofthe hapten left exposed following binding. In screen should produce appropriately accurate practice, it is often not possible to obtain an results for toxic and non-toxic fish both within antibody that can still 'see' small haptens bound andbetween laboratories. Whereverappropriate, toasolidphase,butthisapproachcanallowrapid negative controls should be run in a pair-wise detection ofa hapten without a time-consuming design and results forthese shouldbenegative. 552 MF.MOrRS OPTHEQL^ENSLANDMUSEUM Absence of readily available tefeience toxins increase if more than one point of testing is re- of the ciguatoxin class and lack ofa validated quired. It is interesting tospeculateon the fateof analytical methodtoquantify the level amitypes a screening product thai is shown to have failed of toxins present in samples of fish hinder at- todelectatoxic fish,especially ifthe fish results tempts to validate screening tests for ciguateric in apoisoningepisode. fish. The use of the mouse bioassay to assess Anotherissuetobe considered is what fishare ciguatoxin levels (Lewis & Sellin in press) is to be screened In some areas it might be ap- presently the best available alternative to an in propriate toscreen all potentially ciguateric reef vitro approach. It could prove misleading to use fish, whereas in other areas only the high risk otherhivivobioassaystovalidatescreening tests species presently marketed may need lo be atthistime,especiallytheunreliablebrineshrimp screened.Otherclassesoffish thatmay requirea assay(RJ. Lewisunpuhl. data) winchhas recent- differential approach include (i) fish presently ly been used by D.L. Park to characterise the banned as a result ofthe threatofciguatera they toxins presentin fish screened by the S-PIA ver- pose (li) fish destined for export and (lii) large sionofthe Ciguatect™test(Hungerford,1993). whole fish inoneofthe abovecategories. Toensurcreliabilityofascreen,anylimitations of a screen with regard to species, sample LITERATURECITED preparationand storageetcshouldbe well docu- mented- Ideally, the screenshould 'work' forall 8ACNIS, R., CHANTEAU, S_. CHUNGUE, E., mptohuteseytnatribeaelclaryueggcuhilgtauorarltyehraiencvdallSeu$dab,tperdiiorrrweitsotphseaclrteie.vfAeecroecfnucrneaoctwyo TDAERMTO.ALRLPIEOAT,M,PCOJN.1H9,.8,5A..L,CEoPmCRpHIaABrUTiRs.,onIC.o,.fLtRhEOeGUcaKXt.AbiNJo,Das&,- toxic and non-toxu- Speci0ie.Q$ to ensure ay, (he mouse bioassay and the mosquitubtoas- reliability over time. A sound basis needs to be tw10itd,eGtec&tcSiagluavatto,xiBc.it(yedisn),fi'shP.roPcpe.e4d9i1n-gs49o6f.ihIen establishedforany variation in methodologybe- Fifth International Coral Reef Congress, Tahiti, tweencontrol and tesi pcocedw Vol4*.(Antenne Muscum-F.phe: Mooreai, BANNER, A.H.. SCHEUER, PJ., SASAKI. S IMPACTOFA SCREEN FOR HELFR1CH,P.&ALENDER.CB. I960.Obser-. CIGUATERIC FISH vations on ciguatera-lype toxin in fish. Annals New York Academy ofScience90: 770-787. BOSCATO, L.M., EGAN. G.M. & STUART. M.C. Implementationofausefulscreenwillresultin 1989 Specificityoftwo-siteimmunoassays*Jour- improved marketability of seafood captured in nalofImmunological Methods 117: 221-229. ciguatera endemic areas. Removal of toxic fish DICKUY,R.W.,BENCSATH,F.A.,GRANADE,H.R. before consumption will lead to improved com- & LEWIS, RJ, 1992. Liquid chromatographic- munity health standards. With the availability of nasispectrometricmethodsforthedetermination i a screencome possibilities for opening fisheries ofmarine polycthcrtoxins. Bulletin de laSociere forspecieswhicharepresentlyrestrictedbecause dcPathologicExotique 85: 514-515. ofciguatera. In Queensland new and potentially DORNER. J.W. & COLE, RJ. 1989. Comparison of lucrative fisheries for red bass and perhaps twoELISAscreeningtestswithliquidchromatog- chinamanfishandpaddletailcouldbeestablished raphy foi determination of anatoxins in raw pemutB. Journal Association Official Analytical once an effective screen is available. Chemists 72: 962-964. Screening forciguatera could be conducted at GAZZAZ* S.S.. RASCO, BA & DONG, F.M 1992. anumberalevelsinthechainofmarketingoifish Application of immunochemical assays to food that includes fisherpersons, wholesaler?, com- analysis. Critical Reviews in Food Science and mercialcompanies,governmentagenciesorcon- Nutrition 32: 197-229. sumer. Problems are likely to exist fot the HOKAMA, Y. 1985. A rapid, amplifiedenzyme im- consumerseekingcompensationtoprovethatthe munoassay stick test for the detection of testwasindeedperformedonthe fishinvolved in ciguatoxin and related polyetbers from fish tis- sttethhnreedusptctoouixioipsnnoscn.ioinnInvtdgomulacavctyecidonerwgvdaeitsnnhgeibnettdoenesteethcdeweiasmlsaclainrgudyufeaapttcoeotnsxudihrnoe.owrnWsththihanoe-t HHOOKKAAosmuMgoMelyAsAe.-c..TuTlooYaxYx.ri.i.cnw1oe9nROi9eSg12vL.h3tiI:IeGm9mwIa3ms,r9ui-n1nA09oe..4lM6to1.o.g-x.i3icn5saH.lOJNaonuDarlAnya.slisTSooxAficJAool*-1 finalformatofthetest, government requirements MATSUO.M.K. 1985. Monoclonalantibodiesin. and the level ofrisk ofciguateraassociated with the detection Of ciguatoxin and other toxic the fish being screened. Cost of screening will polyeiber*infishtissuesbyarapidpokesticktetf. SCREEN FORCIGUATERIC FISH 553 Pp. 449^55. In Gabrie, C. & Salvat, B., (eds), LEWIS, R.J. & ENDEAN, R. 1984. Ciguatoxins from 'ProceedingsoftheFifthInternationalCoralReef thefleshandvisceraofthebarracuda,Sphyraena Congress, Tahiti, Vol 4*. (Antenne Museum- jello.Toxicon 22: 805-810. Ephe: Moorea). LEWIS,R.J.&SELLIN,M. 1992.Multipleciguatoxins HOLMES, M.J.. LEWIS, R. J., POLI, M.A. & GIL- inthefleshoffishes.Toxicon 30: 915-919. LESPIE,N.C. 1991. Straindependentproduction LEWIS, R.J. & SELLIN, M. in press. Recovery of ofciguatoxinprecursors(gambiertoxins)byGam- ciguatoxinfromfishflesh.Toxicon. bierdiscus toxiciis (Dynophyceae) in culture. LEWIS, R.J., SELLIN, M., POLI, M.A., NORTON, Toxicon29: 761-775. R.S., MACLEOD. J.K. & SHEIL, M.M. 1991. HUNGERFORD, J.M. 1993. Seafood toxins and Purification and characterization of ciguatoxins seafood products. Journal AOAC International from moray eel {Lycodontis javanicus, 76: 120-130. Muraenidae).Toxicon29: 1115-1127. KIMURA, L.H., HOKAMA, Y., ABAD, M.A., MURATA, M., LEGRAND, A.M., ISHIBASHI, Y., OYAMA, M. & MIYAHARA, J.T. 1982. Com- FUKUI,M.&YASUMOTO,T. 1990. Structures parisonofthreedifferentassaysfortheassessment and configurations ofciguatoxin from the moray ofciguatoxin in fish tissues: radioimmunoassay, eel Gymnothoraxjavanicusand its likelyprecur- mouse bioassay and in vitro guinea pig atrium sor from the dinoflagellate Gambierdiscus assay.Toxicon20: 907-912. toxicus. Journal of the American Chemical LEGRAND, A-M., FUKUI, M., CRUCHET, P., Society 112:4380-^386. ISHIBASHI,Y.&YASUMOTO,T. 1992.Char- TRUCKNESS, M.W., STACK, M.E., NESHEIM. S., acterization of ciguatoxins from different fish PARK,D.L.,&POHLAND,A.E. 1989.Enzyme- speciesandwildGambierdiscustoxicus. Pp. 25- linked immunosorbentassayofaflatoxinsBi,B2, 32. In Tosteson, T.R., (ed.), * ProceedingsThird andGi incorn,cottonseed,peanuts,peanutbutter, International Conference on Ciguatera Fish andpoultry feed: acollaborative study.Journal o Poisoning, Puerto Rico*. (Polyscience Publica- ftheAssociationOfficialAnalyticalChemists72: tions: Quebec). 957-962. LEWIS, R.J. 1992. Ciguatoxins are potent ich- VERNOUX, J.P., LAHLOU, N., MAGRAS, L.Ph. & thyotoxins.Toxicon 30: 207-211. GREAUX,J.B.I985.Chickfeedingtest:asimple LEWIS, R.J. 1992. Socioeconomic impacts and system to detect ciguatoxin. Acta Tropica 42: managementofciguatera in the Pacific. Bulletin 235-240. delaSocietedePathologicExotique85:427-434.

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