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_________________________PROCEEDINGSOF THEFOURTHCONFERENCE_________________________FACULTY OF PURE AND APPLIED SCIENCESConference Organising Committee:Pr<strong>of</strong>. Han Reichgelt, <strong>Department</strong> <strong>of</strong> Mathematics <strong>and</strong> Computer Science – ChairmanMr Rafi Ahmad, <strong>Department</strong> <strong>of</strong> Geography <strong>and</strong> GeologyDr Anthony Chen, <strong>Department</strong> <strong>of</strong> PhysicsDr Kerith Golden, <strong>Department</strong> <strong>of</strong> Basic Medical Sciences (Biochemistry)Dr Ishenkumba Kahwa, <strong>Department</strong> <strong>of</strong> <strong>Chemistry</strong>Dr Neville McMorris, Dean, Faculty <strong>of</strong> Pure <strong>and</strong> Applied SciencesDr Ralph Robinson, <strong>Department</strong> <strong>of</strong> Life SciencesMiss Marvadeen Singh, Graduate Student, <strong>Department</strong> <strong>of</strong> <strong>Chemistry</strong>Dr Dale Webber, Sub-Dean, Faculty <strong>of</strong> Pure <strong>and</strong> Applied SciencesEditing:Typesetting:Dr Ralph Robinson <strong>and</strong> Pr<strong>of</strong>. Han ReichgeltDr Ralph RobinsonPublished by <strong>The</strong> Faculty <strong>of</strong> Pure <strong>and</strong> Applied SciencesISBN: 976 41 0126 7MONAJanuary 12-14, 1999


<strong>The</strong> Faculty gratefully acknowledges the generosity <strong>of</strong> the following donors:Trafalgar Development Bank Ltd<strong>The</strong> Shell Co (WI) LtdBWIA Intl LtdNational Foundation for the Development <strong>of</strong> Science <strong>and</strong> Technology<strong>The</strong> University <strong>of</strong> the West IndiesISBN : 976 41 0126 7Published by <strong>The</strong> Faculty <strong>of</strong> Pure <strong>and</strong> Applied Sciences, Mona2


Monday January 11 th 1999______________________________________________________________________________2:00 - 4:30 REGISTRATION(Conference Room, Faculty <strong>of</strong> Pure <strong>and</strong> Applied Sciences Office)6:00 - 8:00 PANEL DISCUSSION"Putting Science to Work for the Caribbean"LE MÉRIDIEN JAMAICA PEGASUS HOTELCoordinator - Dr Ishenkumba A. KahwaSenior Lecturer, <strong>Department</strong> <strong>of</strong> <strong>Chemistry</strong>, MonaModerator - Dr Jean DixonExecutive Director, <strong>The</strong> Scientific Research Council<strong>of</strong> JamaicaPanelists - Dr Donatus St. AiméSecretary, Caribbean Council on Science <strong>and</strong>Technology, Trinidad &Tobago- Dr Carlton DavisSecretary to the Cabinet, Government <strong>of</strong> Jamaica- Dr Conrad DouglasChairman, <strong>The</strong> Scientific Research Council <strong>of</strong> Jamaica- Mr Howard HamiltonPresident, Jamaica Chamber <strong>of</strong> Commerce- Pr<strong>of</strong>. Oliver HeadleyDirector, <strong>The</strong> Centre for Resource Management <strong>and</strong>Environmental Studies, Cave Hill, UWI- Mr Clifford HughesSenior Jamaica media representativeTransport to <strong>and</strong> from the Hotel has been arranged - pickup at 5:30pm sharp from<strong>The</strong> <strong>Department</strong> <strong>of</strong> <strong>Chemistry</strong> parking lot. Refreshments will be served.______________________________________________________________________________Notes:4


Tuesday January 12 th , 1999______________________________________________________________________________8:00 - 9:00 CONFERENCE REGISTRATION (Foyer, <strong>Chemistry</strong> Lecture Room #5)9:00 - 9:30 OPENING CEREMONY (<strong>Chemistry</strong> Lecture Room #5)9:30 - 10:45 PLENARY LECTUREPr<strong>of</strong>essor Han ReichgeltChairman, Conference Organising Committee, MonaPr<strong>of</strong>essor Kenneth HallPrincipal, <strong>The</strong> Mona Campus, <strong>The</strong> University <strong>of</strong> the West IndiesDr Donald RobothamPro Vice Chancellor <strong>and</strong> Dean <strong>of</strong> <strong>The</strong> School for Graduate Studies<strong>and</strong> Research, <strong>The</strong> University <strong>of</strong> the West IndiesDr Neville McMorrisDean, Faculty <strong>of</strong> Pure <strong>and</strong> Applied Sciences, Mona"Is Physics the only Science?"Chair: Pr<strong>of</strong>. Han Reichgelt<strong>Department</strong> <strong>of</strong> Mathematics <strong>and</strong> Computer Science, Mona______________________________________________________________________________10:45 - 11:15 COFFEE BREAK______________________________________________________________________________Notes:5


FREE ORAL PRESENTATIONS<strong>Chemistry</strong> Lecture Room #5______________________________________________________________________________BIOLOGY WITH BIO-MATHEMATICSChair:______________________________________________________________________________11:15 - 11:35 <strong>The</strong> dynamics <strong>of</strong> tropical insect populations(O-1)Brian Freeman11:35 - 11:55 Fluctuation in the population <strong>of</strong> two species <strong>of</strong> the Citrus Root(O-2) Weevils in JamaicaD.O. Clarke-Harris <strong>and</strong> Ajai Mansingh11:55 - 12:15 Statistical modeling in genetics(O-3)M. Richardson, Smail Madhi <strong>and</strong> L.L. Moseley12:15 - 12:35 Conditional testing in an exponential model(O-4)Smail Mahdi______________________________________________________________________________12:35 - 2:00 LUNCH______________________________________________________________________________Chair:______________________________________________________________________________2:00 - 2:20 Mongoose predation on isl<strong>and</strong> fauna: an experimental test in(O-5) a Jamaican dry forestByron S. Wilson <strong>and</strong> Peter Vogel2:20 - 2:40 <strong>The</strong> abundance <strong>and</strong> distribution <strong>of</strong> epibenthic bryozoans on the roots(O-6) <strong>of</strong> Rhizophora mangle in <strong>and</strong> around Kingston Harbour, JamaicaMarcia Marilyn Chevannes Creary2:40 - 3:00 Changes in polyp size in Monastrea annularis: an effect <strong>of</strong> bleaching(O-7)J. M. Mendes <strong>and</strong> J. D. Woodley6


3:00 - 3:20 Discovery Bay reefs: are they recovering? Comparison with past(O-8) studiesLe<strong>and</strong>ro Cho <strong>and</strong> Jeremy Woodley3:20 - 3:40 Sea urchins to the rescue: lagoonal grass-bed species appears(O-9) on weedy reefsJeremy Woodley, Peter Gayle <strong>and</strong> Nancy Judd______________________________________________________________________________3:40 - 4:10 COFFEE BREAKChair:______________________________________________________________________________4:10 - 4:30 Age, growth <strong>and</strong> reproduction <strong>of</strong> the lane snapper Lutjanus synagris(O-10) (Linnaeus, 1785) in Jamaican watersKarl A. Aiken4:30 - 4:50 Research into the biology <strong>of</strong> Jamaican freshwater macroinvertebrates(O-11) <strong>and</strong> fishes - directions <strong>and</strong> an overviewE. J. Hyslop4:50 - 5:10 Ecotoxicity <strong>of</strong> insecticides in the Jamaican environment(O-12) bioconcentration <strong>of</strong> chlorpyrifos residues in the fish Tilapiain fresh <strong>and</strong> brackish watersCarla N. Thomas <strong>and</strong> Ajai Mansingh5:10 - 5:30 <strong>The</strong> persistence <strong>of</strong> miral 500CS on two c<strong>of</strong>fee farms in Jamaica(O-13)Dwight E. Robinson______________________________________________________________________________6:30 - 9:00 COCKTAIL RECEPTIONPool-side, Senior Common Room Club______________________________________________________________________________Notes:7


Wednesday January 13 th , 1999______________________________________________________________________________9:00 - 10:15 PLENARY LECTUREPr<strong>of</strong>essor Dennis Gonsalves<strong>Department</strong> <strong>of</strong> Plant Pathology, Cornell University, Geneva, NY 14456."Pathogen-Derived Resistance: An Approach for DevelopingTransgenic Plants for the Practical Control <strong>of</strong> Virus Diseases"Chair: Dr Ralph Robinson<strong>Department</strong> <strong>of</strong> Life Sciences, Mona______________________________________________________________________________10:15 - 10:45 COFFEE BREAK______________________________________________________________________________BIOTECHNOLOGY AND BIOCHEMISTRYChair: Dr Arnoldo VenturaSpecial Advisor on Science <strong>and</strong> TechnologyOffice <strong>of</strong> the Prime Minister <strong>of</strong> Jamaica______________________________________________________________________________10:45 - 11:05 Engineering resistance to ringspot potyvirus in papaya(O-14)P. Tennant, D. Gonsalves <strong>and</strong> M. H. Ahmad11:05 - 11:25 Genetic diversity <strong>and</strong> relationships among geminiviruses from(O-15) Jamaica <strong>and</strong> BarbadosMarcia E. Roye <strong>and</strong> Wayne A. McLaughlin11:25 - 11:45 Tomato yellow leaf curl geminivirus infecting hot peppers(O-16) (Capsicum chinense)Sherline Brown, Conroy Green, Marcia Roye<strong>and</strong> Wayne McLaughlin11:45 - 12:05 Post-harvest storage <strong>of</strong> yam tubers: a biochemical perspective(O-17)Helen N. Asemota <strong>and</strong> Anthony U. Osagie12:05 - 12:25 Improvement <strong>of</strong> commercial cultivation <strong>of</strong> dendrobiums through(O-18) substrate <strong>and</strong> nutrient modification: biological <strong>and</strong> economicanalysisPaulette Tai Chun, Sasikala D.P. Potluri <strong>and</strong> P.V. Devi Prasad8


______________________________________________________________________________12:25 - 2:00 LUNCH______________________________________________________________________________Chair: Dr André GordonTechnological Solutions Ltd______________________________________________________________________________2:00 - 2:20 Cyanobacterial bi<strong>of</strong>ertilisers for rice in Jamaica(O-19)Frederick A.H. Boyd <strong>and</strong> P.V. Devi Prasad2:20 - 2:40 Diversity among populations <strong>of</strong> Xanthomonas campestris pv.(O-20) vesicatoria from five Eastern Caribbean isl<strong>and</strong>s with respect tosecretion <strong>of</strong> extracellular enzymes, polysaccharide production<strong>and</strong> pathogenicityHenry A..M., Hamilton M.A.E. <strong>and</strong> O'Garro, L.W.2:40 - 3:00 Physiology <strong>and</strong> biochemistry <strong>of</strong> salt stress on axillary bud cultures <strong>of</strong>(O-21) cassavaSasikala D.P. Potluri <strong>and</strong> P.V. Devi-Prasad3:00 - 3:20 Toward increasing yam production in challenged environments:(O-22) in vitro studies <strong>of</strong> the effect <strong>of</strong> salinity stress on some biochemicalparameters <strong>of</strong> yam (Dioscorea alata) plantletsA. O. Wheatley <strong>and</strong> H. N. Asemota______________________________________________________________________________3:20 - 3:50 COFFEE BREAK______________________________________________________________________________Chair:______________________________________________________________________________3:50 - 4:10 Effect <strong>of</strong> yam <strong>and</strong> dasheen extracts on lipid metabolism in(O-23) streptozotocin-induced diabetic ratsPhillip B. Grindley, Felix O. Omoruyi, Helen N. Asemota<strong>and</strong> Errol Y. Morrison4:10 - 4:30 Evaluation <strong>of</strong> spoilage microorganisms in Jamaican beef patties(O-24)Larry L. Daniels, Suzette Curtello <strong>and</strong> M.H. Ahmad9


GEOLOGY______________________________________________________________________________4:40 - 5:00 Haimea alta <strong>and</strong> Haimea ovumserpentis, what's the difference?(O-25)Deborah-Ann C. Rowe5:00 - 5:20 Cretaceous to Eocene evolution <strong>of</strong> central Jamaica(O-26)Simon MitchellThursday January 14 th , 1999______________________________________________________________________________PHYSICAL SCIENCESChair:______________________________________________________________________________9:00 - 9:20 Phase transitions <strong>and</strong> ordering phenomena in amphiphilic monolayers(O-27) at the air/water interfaceWillem Mulder9:20 - 9:40 Electrocatalytic dechlorination <strong>of</strong> chlororganic compounds in(O-28) aqueous mediaS. Kulikov9:40 - 10:00 Numerical simulation <strong>of</strong> galactic mergers(O-29)J. Lodenquai <strong>and</strong> J. McNamarah10:00 - 10:20 Limited area numerical atmospheric modeling for the Eastern(O-30) CaribbeanM. Mayers C. Depradine <strong>and</strong> L.L. Moseley10:20 - 10:40 A comparative analysis <strong>of</strong> silicon-basedphotovoltaic modules(O-31)Leary Myers <strong>and</strong> Sheryl Williams______________________________________________________________________________10:40 - 11:10 COFFEE BREAK______________________________________________________________________________10


MATHEMATICS AND COMPUTER SCIENCEChair:______________________________________________________________________________11:10 - 11:30 <strong>The</strong> use <strong>of</strong> genetic algorithms in the optomisation <strong>of</strong> logistic functions(O-32)A. C. Perrotte <strong>and</strong> Ch. Posth<strong>of</strong>f11:30 - 11:50 An improved algorithm for the dynamic Kawasaki model(O-33)P. W. Gibbs <strong>and</strong> L. L Moseley11:50 - 12:10 Exploring the 3x+1 problem(O-34)Charles Cadogan12:10 - 12:30 A scripting language for re-use <strong>of</strong> object-oriented classes(O-35)Colin A. Depradine <strong>and</strong> Brian G. Patrick12:30 - 12:50 Cryptography <strong>and</strong> the information society(O-36)Karl H. Robinson12:50 - 1:10 Ontogeny recapitulates phylogeny: true for mathematics education?(O-37)Raymond McEachin______________________________________________________________________________1:10 - 1:30 CLOSING CEREMONY- Dr Neville McMorrisDean, Faculty <strong>of</strong> Pure <strong>and</strong> Applied Sciences- Presentation <strong>of</strong> awards to graduate students for best oral <strong>and</strong> postercontributions to the Conference______________________________________________________________________________2:00 - 5:30 EXCURSION TO PORT ROYAL AND KINGSTON HARBOURLeaders: Rafi Ahmad <strong>and</strong> Dale Webber<strong>Department</strong>s <strong>of</strong> Geography <strong>and</strong> Geology,<strong>and</strong> Life Sciences, Mona11


POSTER PRESENTATIONSDisplayed in <strong>Department</strong> <strong>of</strong> <strong>Chemistry</strong>______________________________________________________________________________BIOLOGICAL SCIENCES_________________________________________________________________________________P-1 Synchronised spawning by brittle stars at the last quarter <strong>of</strong> the September moonJeremy Woodley, Judith Mendes <strong>and</strong> Robert MurrayP-2 Circulation patterns in Discovery BayChung R. <strong>and</strong> Webber, D.F.P-3 <strong>The</strong> status <strong>of</strong> reef communities in Discovery Bay back reefWayne WhittakerP-4 Seagrass populations <strong>of</strong> the south east coast <strong>of</strong> Jamaica: effects <strong>of</strong> ranging levels <strong>of</strong>eutrophicationGreen S.O. <strong>and</strong> Webber , D.F.P-5 <strong>The</strong> use <strong>of</strong> information systems technology to develop a regional marine science databaseDulcie M. LintonP-6 <strong>The</strong> phytoplankton community <strong>and</strong> water quality <strong>of</strong> a highly eutrophic estuarine bay:Hunt's Bay, Kingston Harbour, JamaicaRanston, E. <strong>and</strong> Webber, D.F.P-7 Microalgal community <strong>of</strong> a coastal lagoon: changes in water quality <strong>and</strong> the effect onsediment nutrient fluxesClarke, T.M. <strong>and</strong> Webber, D.F.P-8 Zooplankton distribution in a pristine tropical embayment, Discovery BayEdwards, E.A. <strong>and</strong> Webber, M.K.P-9 Individual zooplankton species show spatial distribution trends far better than totalabundancesDunbar, F.N <strong>and</strong> Webber, M.K.12


P-10 A preliminary assessment <strong>of</strong> the fishable resources <strong>of</strong> Portl<strong>and</strong> Bight, St. CatherineKarl A. AikenP-11 <strong>The</strong> reintroduction to the wild <strong>and</strong> subsequent monitoring <strong>of</strong> three isolated manatees(Trichechus manatus) from the Alligator Hole River, Clarendon, JamaicaRaymond Pryce <strong>and</strong> Eric GarrawayP-12 Longitudinal zonation <strong>of</strong> benthic macroinvertebrates in the Buff Bay River, JamaicaMeshagae Hunte <strong>and</strong> Eric HyslopP-13 <strong>The</strong> use <strong>of</strong> periphyton <strong>and</strong> benthic macroinvertebrates in the biomonitoring <strong>of</strong> the NorthElim River, St. Elizabeth, JamaicaKimberly John, Josette La Hee, Eric Hyslop <strong>and</strong> Dale WebberP-14 Evaluation <strong>of</strong> the benthic macroinvertabrate composition <strong>of</strong> the Rio Cobre <strong>and</strong> selectedtributaries, with special emphasis on the Family ThiaridaeAndrea Fender <strong>and</strong> Eric HyslopP-15 Eco-parasitological investigations <strong>of</strong> Thiara granifera at the Mona Reservoir,Kingston, JamaicaStacey McKoy, Eric Hyslop <strong>and</strong> Ralph RobinsonP-16 Parasitism <strong>of</strong> the C<strong>of</strong>fee Leaf Miner, Perileucoptera c<strong>of</strong>feella, in Jamaica <strong>and</strong> its potentialin the integrated management <strong>of</strong> the pestKathy M. Dalip <strong>and</strong> Ajai MansinghP-17 Transmission routes for Helicobacter pylori infections in a Jamaican communityAlicia E. Lyn-Sue, John F. Lindo, Carol J. Palmer, Peter Vogel, Michael G. Lee<strong>and</strong> Ralph RobinsonP-18 Risk factors for transmission <strong>of</strong> Toxocara canis (dog roundworm) in a humancommunityHugh E. Lounges, John F. Lindo, Michael G. Lee, Peter Vogel <strong>and</strong> Ralph RobinsonP-19 <strong>The</strong> development <strong>of</strong> resistance in sevaral Jamaican populations <strong>of</strong> the C<strong>of</strong>fee Berry Borer(Hypothenemus hampei) to various insecticidesDionne E. Witter-Newell <strong>and</strong> Ajai Mansingh13


P-20 <strong>The</strong> compatibility <strong>of</strong> a thiodan/copper mixture <strong>and</strong> the inclusion <strong>of</strong> mineral oil for thecombined control <strong>of</strong> the C<strong>of</strong>fee Leaf Rust <strong>and</strong> Berry BorerDwight E. Robinson <strong>and</strong> Janice ReidP-21 Antifeedent properties <strong>of</strong> various formulations <strong>of</strong> neem oil against Citrus Root WeevilsDwight E. Robinson <strong>and</strong> Ajai MansinghP-22 Ecotoxicity <strong>of</strong> insecticide residues in Jamaica: sub-lethal toxicity levels <strong>of</strong> endosulphan onthe fish Tilapia, <strong>and</strong> its effects on lipid content <strong>of</strong> gonadsWinroy O. Williams, Kerith D. Golden <strong>and</strong> Ajai MansinghP-23 Organochlorine residues in surface water <strong>and</strong> sediment <strong>of</strong> the Yallahs River: 1989-1991Raymomd Martin, Ajai Mansingh <strong>and</strong> Janice ReidGEOLOGY_________________________________________________________________________________P-24 <strong>The</strong> new Jamaica seismograph network: results after one yearMargaret D. Gr<strong>and</strong>isonP-25 Coastal erosion in southern Jamaica: an example from Clarendon ParishEdward RobinsonP-26 Jupiter L<strong>and</strong>slide, Rio Gr<strong>and</strong>e Valley, Jamaica: a large prehistoric slide damDionne V. Laughton <strong>and</strong> Edward RobinsonP-27 Biostratigraphic investigation <strong>of</strong> species <strong>of</strong> the larger foraminiferal genusCushmania silvestri in Eocene rocks, JamaicaGeorgette D'Aguilar <strong>and</strong> Edward Robinson14


BIOCHEMISTRY AND BIOTECHNOLOGY_________________________________________________________________________________P-28 Evaluation <strong>of</strong> media, methods <strong>of</strong> culture <strong>and</strong> fertilizer for the commercial cultivation <strong>of</strong>anthuriums in JamaicaPaulette Tai Chun, Sasikala D.P Potluri <strong>and</strong> P.V. Devi PrasadP-29 Shoot tip micrografting for obtaining virus-free citrus plantsSasikala D.P. PotluriP-30 Tissue culture techniques for the micropropagation <strong>of</strong> Blighia sapida (Achee)Erica Mills, P.V. Devi Prasad <strong>and</strong> Sasikala D.P. PotluriP-31 Physiological ecology <strong>of</strong> ten phycocolloid-producing marine algae from the environs <strong>of</strong>Kingston <strong>and</strong> Port RoyalJonathan H. Littau <strong>and</strong> P.V. Devi PrasadP-32 Mariculture <strong>of</strong> Gracilaria sp., using tank cultureJonathan H. Littau <strong>and</strong> P.V. Devi PrasadP-33 Agronomic <strong>and</strong> molecular characterisation <strong>of</strong> Jamaican Phaseolus vulgaris l<strong>and</strong>racesWinston A. Young <strong>and</strong> Wayne A. McLaughlinP-34 <strong>The</strong> use <strong>of</strong> nursery protection <strong>and</strong> plant growth promoting rhizobacteria to reducegeminivirus infection in tomato seedlingsJodi Spence <strong>and</strong> Wayne A. McLaughlinP-35 Characterisation <strong>of</strong> extracellular enzymes <strong>and</strong> exopolysaccharides produced byXanthomonas campestris pv phaseoli <strong>and</strong> some studies <strong>of</strong> their role in common blightdisease in beansEustace B. Smith <strong>and</strong> Wayne McLaughlinP-36 Identification, distribution, esterase <strong>and</strong> 16S rRNA sequence polymorphisms <strong>of</strong> whitefliesin JamaicaS. Brown, I. Torrez Jerez, W. McLaughlin <strong>and</strong> J.K. Brown15


P-37 Genetic diversity in dasheens (Colocasia sp.) <strong>and</strong> cocoyams (Xanthosoma sp.) grownin JamaicaBrown, V.M.D., Asemota, H.N., Thangavelu, M. <strong>and</strong> Mantel, S.H.P-38 Molecular analyses <strong>of</strong> bacterial pathogenicity in dasheen (Colocasia sp.) <strong>and</strong> cocoyam(Xanthosoma sp.) in JamaicaBrown, V.M.D., Asemota, H.N., Mansfield, J., Stevens, C.A. <strong>and</strong> Mantel, S.H.P-39 Sectional influence <strong>of</strong> yam (Dioscorea cayenensis) tubers used for miniset on somebiochemical parameters <strong>of</strong> resultant tubersAndrew O. Wheatley, Ose A. Iyare, Damian M. Glasgow, Helen N. Asemota,Phillip B. Grindley <strong>and</strong> Mohammed H. AhmadP-40 Biochemical changes associated with the cell wall <strong>of</strong> yam (Dioscorea cayenensis) tubersduring short-term storageKathleen Lobban, Andrew Wheatley <strong>and</strong> Helen AsemotaP-41 Cell wall degrading enzymes in in vitro-derived plantlets <strong>of</strong> round-leaf yellow yam(Dioscorea cayenensis) infected with Xanthomonas camprestrisKnight, O.S., Hamilton, M.A.E., Omoruyi, F.O. <strong>and</strong> Asemota, H.N.P-42 Quantification <strong>and</strong> identification <strong>of</strong> the cyanoglucosides in economically important yamvarietiesKeith A. Mullings, Helen N. Asemota <strong>and</strong> Errol E.Y. St.A. MorrisonP-43 Fractionation <strong>and</strong> characterization <strong>of</strong> anaerobic sludge to be used in the treatment <strong>of</strong>industrial wastewater <strong>and</strong> production <strong>of</strong> biogasEbanks, W.O., Hamilton, M.A.E. <strong>and</strong> Riley, D.P-44 Efficiency <strong>of</strong> petrifilm methods for the enumeration <strong>of</strong> coliforms <strong>and</strong> total aerobes inselected dairy productsDawkins, G.S., Hamilton, M.A.E.,<strong>and</strong> Hollingsworth, J.P-45 Use <strong>of</strong> PCR (Polymerase Chain Reaction) for the detection <strong>and</strong> typing <strong>of</strong> Salmonella inpoultryLarry L. Daniels, Fidel Fraser <strong>and</strong> M.H. Ahmad16


P-46 <strong>The</strong> study <strong>of</strong> Vibrio species in recreational waters, shell fishes, <strong>and</strong> shell fish farm areas bytraditional culture method <strong>and</strong> PCRPaul Mears, Larry L. Daniels <strong>and</strong> M.H. AhmadP-47 CLV, a defensive factor from the secretory trichomes <strong>of</strong> Cleome viscosa withinsecticidal activityLawrence A.D. Williams, Walton A. Reid <strong>and</strong> Roy PorterP-48 <strong>The</strong> botany <strong>and</strong> domestication potential <strong>of</strong> Cionosicyos pomiformis Griseb(“duppy pumpkin”)Patrick A.Lewis, K R.. Vaidya, H. Jacobs & L.A.D. WilliamsPHYSICAL SCIENCES_________________________________________________________________________________P-49 Indoor levels <strong>of</strong> NO2 measured using passive monitorsRaywattie Singh <strong>and</strong> Willard R. PinnockP-50 Qualitative analysis <strong>of</strong> Caribbean rums by GC/MS techniquesS. KulikovP-51 Magnetocardiography using a superconducting quantum interference device:preliminary assessment <strong>of</strong> cardiac patients in Trinidad <strong>and</strong> TobagoRamadhar Singh, R., Saunders, R., Rassi, D., Thomas, C., Addae, J.<strong>and</strong> Post<strong>of</strong>f, Ch.P-52 Calibration factors for I 131 mIBG radionuclide therapyMukesh Samlal, Sarah Chittenden, Glen Flux <strong>and</strong> Maggie FlowerP-53 Temperature <strong>and</strong> heat remote control in poultry by wireless automationLucien NgalamouP-54 <strong>The</strong> rheological properties <strong>and</strong> clip casting potential <strong>of</strong> some Trinidadian claysD.A.P. Robertson <strong>and</strong> J.C. Knight17


P-55 Trinidad clays as a potential component in clay-graphite refractoriesR. Ramgoolam, J.C. Knight <strong>and</strong> Ramsey SaundersP-56 Testing <strong>of</strong> bonding systems for dental materialsH. Baksh, R. Whiting <strong>and</strong> A. Campbell-RichardsonP-57 <strong>The</strong> electrodynamics <strong>of</strong> a Josephson Junction in a cavityAndrea Joseph, Roger Andrews <strong>and</strong> Robin WhitingP-58 Programmable state machineJoesph SkoblaP-59 Use <strong>of</strong> minimal spanning tree statistics for identification <strong>of</strong> voidsShirin Haque-Copilah <strong>and</strong> Anthony AchongP-60 Wind generated electricity at MunroA.M.D. Amarakoon <strong>and</strong> A.A. ChenP-61 On asymptopic stability <strong>of</strong> nonlinear stochastic difference equation with finite delay inmain termA. Rodkina <strong>and</strong> M. Goncharov_________________________________________________________________________________Notes:18


ABSTRACTS OF PRESENTATIONS_________________________________________________________________________________O-1 THE DYNAMICS OF TROPICAL INSECT POPULATIONSBrian Freeman<strong>Department</strong> <strong>of</strong> Life Sciences, Mona<strong>The</strong> dynamics <strong>of</strong> tropical insect populations have not been studied systematically apart from the work donehere <strong>and</strong> in Trinidad <strong>and</strong> Tobago by my research group from 1970 to 1995. Work in Africa has largelybeen directed to solving insect vector <strong>and</strong> plant pest problems. While this is admirable, it does not directlyimpact on the more fundamental subject <strong>of</strong> underst<strong>and</strong>ing <strong>of</strong> the regulation <strong>of</strong> insect numbers on a globalscale. A small amount <strong>of</strong> work has been done in tropical South America by Anthony Raw, one <strong>of</strong> my exresearchstudents. Our data thus provide the majority <strong>of</strong> information to be compared with a considerablebody <strong>of</strong> work published for temperate <strong>and</strong> Mediterranean zones. I must add that it is vital to carry out<strong>pure</strong> research in the Tropics as well as in other regions if we are to achieve a balanced underst<strong>and</strong>ing <strong>of</strong>any worldwide ecological process.For any fundamental knowledge <strong>of</strong> the regulation <strong>of</strong> animal numbers (<strong>and</strong> most <strong>of</strong> the research in this areahas been on insect populations), certain basic parameters need to be estimated. <strong>The</strong>y are:1. Developmental mortality - the mortality occurring between fertilisation <strong>of</strong> the egg <strong>and</strong> the achievement<strong>of</strong> adulthood. This is commonly believed to be the most influential parameter.2. <strong>The</strong> percentage <strong>of</strong> adults which are female. This <strong>of</strong>ten deviates significantly from 50%. Males aredeemed to be merely a factor in female fertility <strong>and</strong> are <strong>of</strong>ten numerically written <strong>of</strong>f.3. <strong>The</strong> percentage <strong>of</strong> adult females which survives to reproduce. This factor has <strong>of</strong>ten been disregarded.<strong>The</strong> mean fertility <strong>of</strong> reproducing females. In insects at least, this is <strong>of</strong>ten directly related to sizevariation within the species.If all these parameters can be estimated, <strong>and</strong> <strong>of</strong>ten they have not been, the validity <strong>of</strong> the conclusionsdrawn from the data depends on:1. <strong>The</strong> size <strong>of</strong> the sample;2. <strong>The</strong> duration <strong>of</strong> the sampling period;3. <strong>The</strong> spatial comprehensiveness <strong>of</strong> the sampling, i.e. how many places were looked at;4. <strong>The</strong> validity <strong>of</strong> the logic. For a majority <strong>of</strong> studies only a single locality has been sampled <strong>and</strong> for aduration <strong>of</strong> less than 10 generations.My research group has investigated a variety <strong>of</strong> contrasted insect groups:A. Solitary bees <strong>and</strong> wasps (18 species). For all species developmental mortality was low (typically 40 -60%) <strong>and</strong> directly related to the density <strong>of</strong> the population except in one important case (Trypoxylonpalliditarse in Trinidad) in which this relationship is inverse. Generally, the sex-ratio was slightly biasedtowards the females. Only 15 - 35 % <strong>of</strong> adult females survived to reproduce. Fertility was low at 6-15eggs /female. <strong>The</strong>se data are similar to those <strong>of</strong> Raw for Brazil <strong>and</strong> Watmough for the South AfricanKarroo.19


B. Bark beetles (3 species). <strong>The</strong> basic parameters were similar numerically to those above except thatfecundity was higher (60 - 100).C. Gall midges. (2 species). In the Boerhaavia gall midge developmental mortality was low (20%) at lowpopulation densities (dry season) <strong>and</strong> high ( 80%) at high densities (wet season). In the Cactus gall midge,however, this mortality was never more than 15%. Fecundity was 100 eggs/ female. Both species hadgreat variation in the sex ratio. Only a very small proportion <strong>of</strong> females <strong>of</strong> either species survived toreproduce.D. Parasitic wasps (1 species, Melittobia). Again, developmental mortality was low (25%), theproportion <strong>of</strong> females high (95%), the fecundity very high (450 eggs/female). Hence, the proportion <strong>of</strong>adult females surviving to reproduce was extremely low ( 90%)<strong>and</strong> the sex-ratio equality. We were unable to get any good estimate <strong>of</strong> fecundity, but related species areknown to achieve field fecundities <strong>of</strong> about 100. If this were true for Liriomyza it would imply that amajority <strong>of</strong> females survive to reproduce.Temperate species are generally thought to have population dynamics similar to those for our Liriomyzaspecies. That is to say: high fecundity balanced by high developmental mortality, an equality <strong>of</strong> numbers <strong>of</strong>the sexes, while the proportion <strong>of</strong> adult females surviving to reproduce, if it has been assessed, is high.Our data demonstrate a wide variety <strong>of</strong> population control mechanisms for tropical insect species. Inparticular:1. High fecundity may not be balanced by high developmental mortality, <strong>and</strong>2. Most commonly, however, only a small proportion <strong>of</strong> adult females finds suitable places for egglaying. Put another way, their powers <strong>of</strong> searching for <strong>and</strong> finding the reproductive resource are low.<strong>The</strong> implications for insect pest control devolving from conclusion two are quite radical. For example, inthe control <strong>of</strong> Aedes aegypti the most crucial strategy is to deny females breeding sites. Fogging to killadults is a waster <strong>of</strong> time, except as a public relations exercise, since >99% <strong>of</strong> the population will be in theunaffected juvenile stages at any instant. More studies <strong>of</strong> other insect groups, particularly the Diptera(flies), Coleoptera (beetles), Lepidoptera (moths) <strong>and</strong> Hemiptera (true bugs), need to be undertaken in thetropics. Additionally, in temperate research much greater emphasis needs to be placed on field studies <strong>and</strong>,in particular, the estimation <strong>of</strong> the losses <strong>of</strong> pre-reproductive females.O-2 FLUCTUATION IN THE POPULATION OF TWO SPECIES OFTHE CITRUS ROOT WEEVILS IN JAMAICAD. O. Clarke-Harris <strong>and</strong> A. Mansingh*Caribbean Agricultural Research <strong>and</strong> Development Institute, Mona;*<strong>Department</strong> <strong>of</strong> Life Sciences, MonaCitrus root weevil (CRW) larvae cause losses estimated at US $4,982 per hectare per year (Biggs-Allen,1990) which would amount to US $ 5,685,485 in 1996. Various mechanical, cultural <strong>and</strong> chemicalmethods <strong>of</strong> control have been used against CRW in the Caribbean <strong>and</strong> Florida for decades, but theyprovided only short term reprieve.20


Knowledge <strong>of</strong> seasonal population cycles <strong>and</strong> timing <strong>of</strong> major biological events with respect toenvironmental cycles is fundamental to the development <strong>of</strong> a suppression <strong>and</strong> management strategy(Knipling, 1979).This investigation was carried out to study population fluctuation <strong>of</strong> two species <strong>of</strong> the citrus rootweevils, Exophthalmus similis <strong>and</strong> Exophthalmus vittatus.Population studies were conducted on two Jamaica plantations, United Estates (UE) in St. Catherine<strong>and</strong> Greenwood Farms (GF) in St. Mary. At each locality, thirty trees were selected <strong>and</strong> taggedalong a " multiple Z" path using systematic sampling. Sampling <strong>of</strong> adult CRW was done every 28days from October 1990 to July 1993, by counting adult weevils at the cardinal points <strong>of</strong> each tree.All the weevils were observed carefully <strong>and</strong> samples collected regularly, for the identification <strong>of</strong>species <strong>of</strong> the CRW complex (Figure).<strong>The</strong> data were analysed statistically by Analysis <strong>of</strong> Variance. <strong>The</strong> correlation between population<strong>and</strong> rainfall was analysed by Pearson’s correlation.At UE, adult E. vittatus population increased from October (0.1/tree) to December (0.73/tree) 1991(Figure 1). No weevils were recorded in January 1992 <strong>and</strong> numbers remained low (< 0.13/tree) untilApril (0.8/tree), peaked to 3.53/tree in May 1992 before declining to low levels until April, 1993.At GF, the adult E. similis population was relatively low (0.03-1.2 adults/tree). <strong>The</strong> numbersrecorded decreased from October (0.63/tree) to December 1991 (0.1/tree), increased in January 1992(0.47/tree), declined again in February (0.1/tree) <strong>and</strong> remained low until October 1992 (0.03-0.23/tree). From December 1992 to April 1993 the population gradually increased ( range 0.13-0.3/tree) <strong>and</strong> peaked in May 1993 when 36 adults (1.2/tree), the maximum number <strong>of</strong> E. similisweevils, was recorded.Population fluctuation <strong>of</strong> E. vittatus at UE was not significantly related to rainfall (P>0.05) butwas significant (P


Figure:Population <strong>of</strong> adult weevils, Exophthalmus vittatus, <strong>and</strong> monthly rainfallat United Estates, St. Catherine between October 1991 <strong>and</strong> July 1993.22


ReferencesBiggs-Allen, G. E. (1990). Investigations on the population fluctuations, economic importance <strong>and</strong>chemical control <strong>of</strong> citrus root weevils Exophthalmus vittatus (Linne) <strong>and</strong> Pachnaeus citri Marshall(Coleoptera: Curculionidae). M.Phil. <strong>The</strong>sis, University <strong>of</strong> the West Indies, Jamaica. 168 pp.Knipling, E.F. (1979). <strong>The</strong> Basic Principles <strong>of</strong> Insect Population Dynamics Suppression <strong>and</strong>Management. U.S. Dept. <strong>of</strong> Agri., Agriculture H<strong>and</strong>book (512) 623 pp.McCoy, C. W. (1994). Citrus root weevils: Biology <strong>and</strong> current IPM strategies in Florida. In Proc. 3rdInternational Seminar on Citrus, Bebedouro, Brazil. 28pp.O-3 STATISTICAL MODELING IN GENETICSMatthew Richardson, Smail Mahdi <strong>and</strong> Leo. L. Moseley<strong>Department</strong> <strong>of</strong> Computer Science, Mathematics <strong>and</strong> Physics, Cave HillIn this presentation we intend to give an overview <strong>of</strong> statistical models developed by RussellL<strong>and</strong>e 1,2,3 for the study <strong>of</strong> the maintenance <strong>of</strong> genetic variability by mutation in polygenic characters.Change <strong>of</strong> genetic variability is described by the discrete dynamical system <strong>of</strong> the covariance matrixsystem corresponding allelic effects. When this dynamic system possesses a unique equilibrium, theequilibrium is globally stable 4 . Equilibrium has not yet been obtained explicitly in some models,particularly in the case <strong>of</strong> multivariate characters. Furthermore, the dynamic equations for thechange <strong>of</strong> genetic variability in some models, have been found using linear regression assumingstrong homoscedasticity. Our aim is to examine further the question <strong>of</strong> whether equilibrium can beobtained explicitly in L<strong>and</strong>e’s models for which an explicit solution was not given, <strong>and</strong> to examinethe homoscedasticity assumptions.References(1) L<strong>and</strong>e, R. (1976) <strong>The</strong> maintenance <strong>of</strong> genetic variability by mutation in a polygenic characterwith linked loci. Genetical Research 26: 221-235(2) L<strong>and</strong>e, R (1977) <strong>The</strong> influence <strong>of</strong> the mating system on the maintenance <strong>of</strong> genetic variability inpolygenic characters. Genetics 86: 485-498(3) L<strong>and</strong>e, R (1980) <strong>The</strong> genetic covariance between traits maintained by linked pleiotropicmutations. Genetics 91: 203-215(4) Mahdi, S. <strong>and</strong> Lessard, (1996) S. Convergence <strong>of</strong> Covariance Structures in Additive GaussianPolygenic Models Biometrics 52: 833-845.23


O-4 CONDITIONAL ESTIMATION IN AN EXPONENTIAL MODELSmail Mahdi<strong>Department</strong> <strong>of</strong> Computer Science, Mathematics <strong>and</strong> Physics, Cave HillPreliminary test procedure is <strong>of</strong>ten used in statistical inference to fit appropriate models for data sets.In analysis <strong>of</strong> variance, the procedure is used to test whether interactions <strong>of</strong> higher order aresignificant before doing the final inference. In this paper, we present an overview <strong>of</strong> this procedure<strong>and</strong> apply it to estimate the parameters <strong>of</strong> an exponential population. We also present a study on theaccuracy <strong>of</strong> the proposed estimator.O-5 MONGOOSE PREDATION ON ISLAND FAUNA:AN EXPERIMENTAL TEST IN A JAMAICAN DRY FORESTByron S. Wilson <strong>and</strong> Peter Vogel<strong>Department</strong> <strong>of</strong> Life Sciences, MonaAn overriding theme in the extinction <strong>of</strong> isl<strong>and</strong> reptiles is the introduction (by man) <strong>of</strong> potentmammalian predators such as dogs, cats, rats, <strong>and</strong> most notoriously, the Indian mongoose, Herpestesauropunctatus (Pimm, 1986, Case <strong>and</strong> Bolger 1991). Although the evidence for the role <strong>of</strong> themongoose in causing reptile extinctions is largely correlative, it is nevertheless overwhelming(Barbour 1930, Case <strong>and</strong> Bolger 1991). Isl<strong>and</strong> extinctions following the introduction <strong>of</strong> themongoose have been reported frequently, especially in the Caribbean (Case <strong>and</strong> Bolger 1991,Schwartz <strong>and</strong> Henderson 1991, Corke 1992). Besides man, no exotic predator has ever beenimplicated in so many isl<strong>and</strong> extinctions. In Jamaica alone, the mongoose has been associated withthe extinction or near extinction <strong>of</strong> at least two endemic birds <strong>and</strong> four endemic reptiles.Unfortunately, little experimental research effort has been directed at the mongoose issue.Here we describe research aimed at determining the efficacy <strong>of</strong> using mongoose control as a longtermmanagement strategy for preserving biodiversity. Specifically, we outline an experimentalstudy that seeks to determine the community-wide consequences <strong>of</strong> mongoose removal. We haveestablished experimental (=mongoose removal) <strong>and</strong> control (no mongoose removal) plots in theinterior <strong>of</strong> the Hellshire Hills, <strong>and</strong> are currently employing a variety <strong>of</strong> census techniques to study theresponse <strong>of</strong> selected prey species <strong>of</strong> the mongoose. In particular, we are using an extensive series <strong>of</strong>pitfall traps to index the abundance <strong>of</strong> terrestrial species such as lizards, snakes, <strong>and</strong> largearthropods (e.g., arachnids,insects). In addition, we are using survey techniques to estimate the relative abundance <strong>of</strong> theCaribbean ground dove, <strong>and</strong> have established mark-recapture plots to examine the demographicresponse <strong>of</strong> Anolis lizards. Hence, our efforts focus on elucidating the demographic response <strong>of</strong>diverse taxa to the experimental removal <strong>of</strong> a potent exotic predator.In this presentation we will document the effectiveness <strong>of</strong> our mongoose removal program, <strong>and</strong>present some preliminary results concerning the demographic responses <strong>of</strong> targeted species. We alsoreport on some exciting results from our on-going efforts to document biodiversity in the HellshireHills. Specifically, we describe the discovery <strong>of</strong> a population <strong>of</strong> the rare <strong>and</strong> beautiful Jamaicanlizard, the Blue-tailed galliwasp -- known to science from only two specimens -- both collected over50 years ago at Portl<strong>and</strong> Ridge in Clarendon.24


We thus not only document that the species still exists, but also delineate a major range extension forthe species. In addition, we highlight the recent collection <strong>of</strong> two endemic snake species notpreviously recorded from the Hellshire Hills -- the Jamaican boa (or "yellow snake"), <strong>and</strong> a form <strong>of</strong>West Indian dwarf boa (unresolved taxonomically at the time <strong>of</strong> this writing).ReferencesBarbour, T. (1930). Some faunistic changes in the Lesser Antilles. Proc. New Engl<strong>and</strong> Zool. Club.11:73-85.Case, T. J. & D. T. Bolger (1991). <strong>The</strong> role <strong>of</strong> introduced species in shaping the distribution <strong>and</strong>abundance <strong>of</strong> isl<strong>and</strong> reptiles. Evolutionary Ecology 5:272-290.Corke, D. (1992). <strong>The</strong> status <strong>and</strong> conservation needs <strong>of</strong> the terrestrial herpet<strong>of</strong>auna <strong>of</strong> theWindward Isl<strong>and</strong>s (West Indies). Biological Conservation 62:47-58.Pimm, S. L. (1986). Community stability <strong>and</strong> structure. Pages 309-329 in M. E. Soule, editor.Conservation biology: the science <strong>of</strong> scarcity <strong>and</strong> diversity. Sinauer Associates, Inc.Sunderl<strong>and</strong>, Massachusetts, USA.Schwartz, A. & R. W. Henderson (1991). Amphibians <strong>and</strong> reptiles <strong>of</strong> the West Indies:descriptions, distributions, <strong>and</strong> natural history. University <strong>of</strong> Florida Press, Gainesville,Florida, USA.O-6 THE ABUNDANCE AND DISTRIBUTION OF EPIBENTHICBRYOZOANS ON THE ROOTS OF RHIZOPHORA MANGLE INAND AROUND KINGSTON HARBOUR, JAMAICAMarcia Marilyn Chevannes CrearyCentre for Marine Sciences, Mona<strong>The</strong> abundance <strong>and</strong> distribution <strong>of</strong> the bryozoan species on the prop roots <strong>of</strong> the red mangrove,Rhizophore mangle, at diverse locations around Kingston Harbour are described. Specificenvironmental parameters were examined to investigate their relative effects on the pattern <strong>of</strong>abundance <strong>and</strong> distribution observed. <strong>The</strong> study was carried out in four mangrove areas (PortRoyal, Great Salt Pond, Dawkins Pond <strong>and</strong> Hunt's Bay) over a 15 month period between September1994 <strong>and</strong> December 1995 <strong>and</strong> included a total <strong>of</strong> 12 stations.<strong>The</strong> submerged roots <strong>of</strong> some mangrove tree species provide a natural substrate for the attachment<strong>of</strong> a variety <strong>of</strong> sessile organisms including bryozoans. <strong>The</strong> phylum bryozoa is characterized byhaving lophophores <strong>and</strong> are mainly marine colonial organisms forming encrustations or tufts on anassortment <strong>of</strong> substrates. <strong>The</strong>y are found in a variety <strong>of</strong> habitats around Kingston Harbour whichexhibit differing degrees <strong>of</strong> exposure to pollution.This study identified 18 species <strong>of</strong> bryozoa inhabiting the rhizophore community. Diversity wasfound to be highest in Port Royal with 16 species while Hunt's Bay had the lowest diversity havingonly 3 species. Great Salt Pond <strong>and</strong> Dawkins Pond had 8 <strong>and</strong> 3 species respectively.25


Six growth forms were observed, all <strong>of</strong> which were represented in Port Royal. Dawkins Pond <strong>and</strong>Hunts Bay contained only those forms that covered the roots in a mat <strong>of</strong> creeping colonies. <strong>The</strong>highest abundance, measured as percentage cover, was observed in Hunts Bay (70.03 - 71.46%) <strong>and</strong>least in the Great Salt Pond (2.04 - 3.84%). Salinity, suspended solids, temperature <strong>and</strong> dissolvedoxygen were measured at all stations. Reduced salinity corresponded to periods <strong>of</strong> elevated rainfall<strong>and</strong> the salinity for Hunts Bay was consistently lower than that obtained at the other locations.Elevated levels <strong>of</strong> suspended solids appear to be associated with periods <strong>of</strong> lowered salinities. Watertemperature tended to be uniform throughout the water column with the highest temperaturesobserved in Hunts Bay <strong>and</strong> the lowest in Great Salt Pond. Dissolved oxygen was variable <strong>and</strong>tended to decrease with depth at all stations.Correlation coefficient calculations indicated a weak association between the environmental variables<strong>and</strong> the abundance <strong>and</strong> distribution patterns <strong>of</strong> the bryozoan communities, however, despite the weakcorrelation temperature <strong>and</strong> salinity, which were very variable in Hunts Bay, may <strong>of</strong>fer someexplanation.O-7 CHANGES IN POLYP SIZE IN MONTASTRÆA ANNULARIS:AN EFFECT OF BLEACHINGJ. M. Mendes 1 <strong>and</strong> J. D. Woodley 21<strong>Department</strong> <strong>of</strong> Life Sciences <strong>and</strong> 2 Centre for Marine Sciences, MonaFifteen (15) colonies <strong>of</strong> Montastræa annularis located at a depth <strong>of</strong> 5m were marked in August1994 or March 1995. Samples <strong>of</strong> tissue <strong>and</strong> skeleton were taken using a 1.5 inch hole saw, everyfull moon or every full moon <strong>and</strong> new moon until March 1996. Additional samples were takenoccasionally thereafter until October 1997. Measurement <strong>of</strong> polyp depth was made on skeletal slabsin which the tissue had been fixed <strong>and</strong> then air-dried. A bleaching event began at the end <strong>of</strong>September 1995. Six (6) <strong>of</strong> the 15 marked colonies bleached. <strong>The</strong> most severely effected coloniesremained completely bleached for 4 months.Prior to bleaching the polyps showed a regular variation in depth, with a mean depth <strong>of</strong> 3.88 ±0.3mm. During bleaching, polyp depth decreased. Reduction in polyp depth was directly related tothe length <strong>of</strong> time the colony remained bleached.Mean polyp depth after 4 months <strong>of</strong> bleaching was 2.00 ± 0.4 mm. Once the colonies had returnedto their normal colour, it took an additional 4 - 8 weeks for the polyps to return to their normal size.<strong>The</strong> results <strong>of</strong> this study support the suggestion <strong>of</strong> Barnes <strong>and</strong> Lough (1992) that polyp tissue depthcould be used as an indication <strong>of</strong> coral colony health / nutritional status. It could be particularlyuseful for bleaching events where observations are <strong>of</strong>ten sporadic, if the mean polyp depth waspreviously known.ReferenceBarnes, D.J. & Lough, J.M. (1992). Systematic variations in the depth <strong>of</strong> sketeton occupied bycoral tissue in marine columns <strong>of</strong> Porites from the Great Barrier Reef. J. Exp. Mar. Biol. Ecol.159: 113-128.26


O-8 DISCOVERY BAY REEFS: ARE THEY RECOVERING?COMPARISON WITH PAST STUDIESLe<strong>and</strong>ra Cho <strong>and</strong> Jeremy WoodleyCentre for Marine Sciences<strong>The</strong> coral reefs <strong>of</strong> Discovery Bay have suffered from large scale degradations since 1980 whichresulted in a decline <strong>of</strong> coral diversity <strong>and</strong> abundance. Phase shifts in community structure resultedin macroalga dominated reefs (Liddell & Ohlhorst, 1992; Andres & Witman, 1995; Hughes, 1994).<strong>The</strong> changes are believed to have been induced by decades <strong>of</strong> increasing chronic disturbance fromterrestrial run<strong>of</strong>f <strong>and</strong> overfishing followed by acute catastrophic events, with the advent <strong>of</strong> HurricaneAllen in 1980 <strong>and</strong> the mass mortality <strong>of</strong> the herbivorous sea-urchin Diadema antillarum. <strong>The</strong> result<strong>of</strong> such extensive disturbance in a relatively short period <strong>of</strong> time resulted in further decline <strong>of</strong> reefs.Studies from the last 15 years showed a decline in coral cover from 30-60% in 1977, to 5-25% in1984 after Diadema die-<strong>of</strong>f, to £5% coverage above depths <strong>of</strong> 30m in 1992. Macroalga coverincreased from 5% to 79%.<strong>The</strong> study area covered 10km <strong>of</strong> the coastline east <strong>of</strong> Rio Bueno to the west <strong>of</strong> Pear Tree River. Atotal <strong>of</strong> 27 sites was identified to investigate variation in coral abundance <strong>and</strong> diversity betweendifferent localities, <strong>and</strong> to determine if reported coral cover <strong>of</strong>


<strong>The</strong> difference in coral cover among depths is partly a result <strong>of</strong> physical factors which governdistribution <strong>and</strong> abundance <strong>of</strong> corals. Macroalga cover varies with depth, <strong>and</strong> is affected bybiological factors such as the level <strong>of</strong> herbivory.<strong>The</strong> substantial increase in coral cover <strong>and</strong> decrease in macrolaga cover, over the past decade,suggest that, while they have a far way to go, the reefs <strong>of</strong> Discovery Bay are on the road to recovery.However, since Acropora <strong>and</strong> Montastrea, the dominant frame-building corals <strong>of</strong> classic Jamaicanreefs (Goreau, 1959), are not doing well, the new reefs will differ from the old ones.ReferencesAndres, N.G. & Witman, J.D. (1995). Trends in community structure on a Jamaican reef. Mar.Ecol. Prog. Ser. 118: 305-310Goreau, T.F. (1959). <strong>The</strong> ecology <strong>of</strong> Jamaican coral reefs I. Species composition <strong>and</strong> zonation.Ecology 40, 67-90.Hughes, T.P. (1994). Catastrophes, phase shifts, <strong>and</strong> large-scale degradation <strong>of</strong> a Caribbean coralreef. Science 265: 1547-1551.Liddell, W.D. & S.L. Ohlhorst (1992). Ten years <strong>of</strong> disturbance <strong>and</strong> change on a Jamaican fringingreef. Proc. 7 th ICRS 1: 144-150.O-9 SEA-URCHINS TO THE RESCUE: LAGOONAL GRASS-BEDSPECIES APPEARS ON WEEDY REEFSJeremy Woodley, Peter Gayle <strong>and</strong> Nancy JuddCentre for Marine Sciences, MonaJamaican north coast coral reefs have suffered, in the last fifteen years, a phase shift to dominanceby macroalgae. Contributory factors include mass mortality <strong>of</strong> the herbivorous sea-urchin, Diademaantillarum, in 1983 (Liddell et al 1986, the removal <strong>of</strong> herbivores by over-fishing (Hughes 1994),<strong>and</strong> nutrient pollution (Lapointe 1997).Cho <strong>and</strong> Woodley (this conference, p 000) have suggested that, wherever it is locally abundant atDiscovery Bay, Diadema still exerts top-down control on macroalgae. <strong>The</strong> recovery <strong>of</strong> Diademapopulations since 1983 has been slow <strong>and</strong> restricted to depths shallower than about 10m: butnumbers have increased in recent years.Prior to 1983, the browsing sea urchin, Tripneustes esculentus, was abundant in Thalassia beds inthe back-reef at Discovery Bay, but was never seen on the fore-reef. Since the mid-1980s, smallnumbers <strong>of</strong> this urchin have recruited to the dense beds <strong>of</strong> algae on the shallow fore-reef. Since 1996,it has become abundant on the West Fore-reef (1.8 m -1 at 8m on Monitor Reef, a site monitored forCARICOMP). Tripneustes is a browser, reducing fleshy algae to a low turf, while ignoringcalcareous algae. <strong>The</strong> abundance <strong>of</strong> fleshy algae at that site decreased from about 1kg wet weightper m 2 in 1997 to about 300gm -2 in 1998. Diadema grazes down to (<strong>and</strong> into!) the rock surface, <strong>and</strong>eats everything.28


<strong>The</strong> combined impacts <strong>of</strong> these two urchins in shallow water may facilitate recruitment by corallarvae <strong>and</strong> may give massive corals a better chance <strong>of</strong> recovery from algal overgrowth. Deeper than20m, rocky substrata, including the flanks <strong>and</strong> crowns <strong>of</strong> massive corals, are still heavily overgrown.ReferencesHughes, T.P. (1994). Catastrophes, phase shifts, <strong>and</strong> large-scale degradation <strong>of</strong> a Caribbean coralreef. Science 265:1547-1551Lapointe, B.E. (1997). Nutrient thresholds for bottom-up control <strong>of</strong> macroalgal blooms on coralreefs in Jamaica <strong>and</strong> southeast Florida. Limnology <strong>and</strong> Oceanography 42:1119-1131Liddell, W.D. <strong>and</strong> Ohlhorst SL (1986). Changes in the benthic community composition followingthe mass mortality <strong>of</strong> Diadema at Jamaica. Journal <strong>of</strong> Experimental Marine Biology <strong>and</strong>Ecology 95:271-278.O-10 AGE, GROWTH & REPRODUCTION OF THE LANE SNAPPERLUTJANUS SYNAGRIS (LINNAEUS, 1785) IN JAMAICAN WATERSKarl A. Aiken<strong>Department</strong> <strong>of</strong> Life Sciences, Mona<strong>The</strong> lane snapper, Lutjanus synagris (Linnaeus, 1758) is the single most important species <strong>of</strong> the large <strong>and</strong>growing beach seine, Chinese (or tangle) net <strong>and</strong> trammel net fisheries which take place along the southcoast <strong>of</strong> Jamaica. Despite its importance, no directed study has ever focussed on the lane snapper.This study was intended to determine the age <strong>and</strong> growth patterns as well as to elucidate earlier findings onthe reproductive biology. <strong>The</strong> major difference between this <strong>and</strong> earlier studies is that the present studyprimarily used hard part (otolith) analysis, whereas previously studies were length-based. Otoliths, whichare small paired, oval crystalline structures, were removed with forceps from the inner ears' balance <strong>and</strong>hearing apparatus. Analytical methods included low power light microscopy <strong>of</strong> whole otoliths as well assections <strong>of</strong> sagittal otoliths viewed by compound microscope. Otolith sections were prepared by use <strong>of</strong> aBuehler Isomet low-speed circular diamond saw to cut through the primordium or centre <strong>of</strong> an epoxymountedotolith. Each thin section was attached to a special glass slide <strong>and</strong> ground to 300 microns with aseries <strong>of</strong> grinding <strong>and</strong> polishing powders on a lapping machine. Biological data such as length, weight, sex<strong>and</strong> maturity stage were also collected.Samples from the commercial fishery l<strong>and</strong>ings mainly at Old Harbour Bay, St. Catherine, were examinedbetween March 1996 <strong>and</strong> July, 1998 <strong>and</strong> showed a size range between 150 - 430 mm FL with mean sizes<strong>of</strong> 210 <strong>and</strong> 230 mm FL for males <strong>and</strong> females respectively. <strong>The</strong> weight range for these fish was 75 - 1,110g. Size at first maturity was 165 mm <strong>and</strong> 175 mm FL for male <strong>and</strong> female fish respectively. Sex ratio(F:M) was 2.3:1.0, but above 310 mm FL, the proportion <strong>of</strong> females was 100% A pronounced spawningmaximum occurred in July <strong>and</strong> August in both males <strong>and</strong> females, but spawning fish could be foundthroughout the year. This species was also found to have a very extended spawning season in Cuba with apeak in May - June (Claro, 1982).29


Examination <strong>of</strong> whole <strong>and</strong> sectioned sagittal otoliths showed clear patterns <strong>of</strong> marks with alternatinghyaline <strong>and</strong> opaque zones. Whole otoliths <strong>of</strong> specimens less than 270 mm FL were sufficiently transparentto allow ageing under low power light microscopy. Marginal increment analysis (temporal distribution <strong>of</strong>opaque <strong>and</strong> hyaline edges) indicated that there was one opaque (fast growth) zone laid down annually inJuly, <strong>and</strong> one hyaline (slow growth) zone laid down in March.Analyses <strong>of</strong> sagittal otoliths suggested differing ages based on the use <strong>of</strong> whole or sectioned otoliths.Whole otolith analysis indicates a maximum age <strong>of</strong> 6 years, but sectioned otoliths suggest a maximum <strong>of</strong>at least 14 years. This is older than previously known for this species in these waters. <strong>The</strong> majority <strong>of</strong> thel<strong>and</strong>ings nonetheless comprise individuals that are between 1 <strong>and</strong> at least 6 years old. <strong>The</strong> new estimatedages have management implications <strong>and</strong> these are briefly discussed. Otolith weight analyses produced arelationship where Y = 0.0403x - 1.543 (r 2 = 0.9407) for males <strong>and</strong> for females Y = 0.0405x - 1.1716 (r 2= 0.9711). Importantly it is suggested that otolith weight changes with fork length can be used to indicatechanges in overall growth. Otolith radius versus fork length relationship yielded the equation Y = 1.5262x- 3.9574 (r 2 = 0.850). Like otolith weight, these are significant relationships, <strong>and</strong> suggest that they may beused as an indicator <strong>of</strong> overall growth in the lane snapper.ELEFAN (a computerized iterative programme that compares actual with expected modes in lengthfrequencies <strong>and</strong> emphasises similarities) analyses suggest an asymptotic length (Loo) <strong>of</strong> 450 mm FL, <strong>and</strong> aVon Bertalannfy growth rate <strong>of</strong> K = 0.23, with t0 = 0.001 yr-1. <strong>The</strong> present results differ in several aspectsfrom the earlier work <strong>of</strong> Thompson & Munro (1983) who sampled only <strong>of</strong>fshore catches <strong>and</strong> the ages aregreater than Cuban findings based on whole otolith analyses (Claro, 1982; Claro & Reshetnickov, 1981).Similarly, they are somewhat less in maximum age than recent findings (19 years) for Bermudan lanesnapper (Luckhurst, Dean & Reichert, 1998).Management for this <strong>and</strong> other long lived, slower growing species must consider that any changes in thestocks <strong>of</strong> this <strong>and</strong> other fishes, will mean slower recovery from such changes, as compared to the relativelyfaster species recovery formerly suggested by earlier aging research.ReferencesClaro, R. 1982. Ecologia y ciclo de vida de la biajaiba, Lutjanus synagris (Linnaeus) en la plataformacubana. IV. Reproduccion. Rep. de investigacion del instituto de oceanologia. No. 5. Acad. de Cienc.de Cuba. 37pp.Claro, R. & Y.S. Reshetnikov. Ecologia y ciclo de vida de la biajaiba, Lutjanus synagris (Linnaeus), ena plataforma cubana. 1. Formacion de marcas de crecimiento en sus estrcturas. Informe cientificotechnicoNo. 174, Instituto de Oceanologia. Academia de ciencias de Cuba. 29pp.Luckhurst, B.E., Dean, J.M. & M. Reichert. 1998. Age <strong>and</strong> growth <strong>of</strong> lane snapper. Book <strong>of</strong> abstracts;2nd. International Symposium on Fish Otolith Research & Application, Bergen, Norway, June1998. p209.Thompson R. & J.L. Munro. 1983. <strong>The</strong> biology, ecology <strong>and</strong> bionomics <strong>of</strong> the snappers, Lutjanidae; inCaribbean Coral Reef Fishery Resources Ed. J.L. Munro. ICLARM Studies & Reviews 7: 94-10.30


O-11 RESEARCH INTO THE BIOLOGY OF JAMAICANFRESHWATER MACROINVERTEBRATES AND FISHES- DIRECTIONS AND AN OVERVIEWE. J. Hyslop<strong>Department</strong> <strong>of</strong> Life Sciences, MonaDespite being well provided with river systems, Jamaica has seen little published work particularlyon the benthic macroinvertebrate fauna <strong>of</strong> these water bodies. In addition, development, in somecases at a rapid pace, throughout the country, in conjunction with inadequate environmental controlhas resulted in considerable input from anthropogenic processes to the country's river systems, theeffects <strong>of</strong> which, on the faunal communities, have been inadequately documented.<strong>The</strong> present paper sets out to demonstrate that a research programme to address, at least in part, theabove problems is being implemented <strong>and</strong> to discuss in brief the main directions being followed <strong>and</strong>outline some <strong>of</strong> the preliminary findings. In addition the components <strong>of</strong> this research programme <strong>and</strong>their interrelationship are fully discussed.Taxonomic work is concerned with giving names to organisms <strong>and</strong> by extension to identifyingcommon associations or groupings, these include community composition <strong>and</strong> diversity. This in turncan be linked to information on the physico-chemical conditions under which the co munity isfound, including the presence <strong>of</strong> known or suspected pollutants. Rivers are longitudinal systems <strong>and</strong>it is necessary to establish whether changes in community composition <strong>and</strong>/or diversity are as aresult <strong>of</strong> altitudinal gradient (longitudinal zonation) or due to other factors. Some general publishedinformation on benthic macroinvertebrate distribution exists in relation to Jamaica (Boon, Jupp &Lee 1986). Recent detailed studies on the taxonomy <strong>of</strong> trichopterans (caddis flies) have resulted inthe description <strong>of</strong> seven new species <strong>and</strong> two sub-species for Jamaica (Botosaneanu & Hyslop, inpress 1 & 2 ) while work on freshwater Gastropoda indicates a predominance <strong>of</strong> two species <strong>of</strong> thefamily Thiaridae; Melanoides tuberculata <strong>and</strong> Thiara granifera, both <strong>of</strong> which are recentintroductions to the fauna, originally from Africa/Asia (Hyslop, unpublished data).<strong>The</strong> predominance <strong>of</strong> Thiaridae in most river systems has implications for the indigenous gastropodfauna <strong>and</strong> an analagous situation exists with regard to freshwater riverine fishes. Here again theJamaican freshwater ichthy<strong>of</strong>auna is dominated by an invading species or group <strong>of</strong> species, tilapia,belonging to the genus Oreochromis. <strong>The</strong> impact <strong>of</strong> Oreochromis on the indigenous fish fauna ispossibly minimal as the niche occupied by this species is unlikely to overlap significantly with themembers <strong>of</strong> the established ichthy<strong>of</strong>auna. One <strong>of</strong> the indigenous fish families found in Jamaicanfreshwaters is the Poeciliidae, the live-bearers or live-bearing toothcarps. Here again there isevidence <strong>of</strong> invaders in the form <strong>of</strong> species commonly imported as part <strong>of</strong> the aquarium trade. <strong>The</strong>seinclude guppies, Poecilia reticula, <strong>and</strong> swordtails <strong>and</strong> platies genus Xiphiphorus. <strong>The</strong> indigenousPoeciliidae consists <strong>of</strong> a number (at least 4) species <strong>and</strong> some concern must be expressed as to thecompetitive effects <strong>of</strong> invading species <strong>of</strong> the same family.<strong>The</strong> potential for utilizing widespread benthic invertebrate species such as those belonging toThiaridae as biological monitors is being investigated <strong>and</strong> initial observations suggest the utility <strong>of</strong>both species in the monitoring <strong>of</strong> heavy metal pollution in Jamaican river systems. Similarlyinvestigations into the sub-lethal effects <strong>of</strong> exposure to the widely-used pesticide, endosulphan on thegrowth <strong>and</strong> fecundity <strong>of</strong> T. granifera <strong>and</strong> M. tuberculata are also being carried out.31


Ultimately one <strong>of</strong> the aims <strong>of</strong> many <strong>of</strong> these disparate lines <strong>of</strong> research is to formulate observationson the basic invertebrate fauna which is "expected" within a river system <strong>and</strong> to determine whetherthere is a core component to this. Any deviations from this established norm would be taken asindications that some perturbation ("pollution") is occurring. Such a system is based uponcommunity composition <strong>and</strong>, in particular, on biological diversity. Additionally utilized inconjunction with information on tolerances, occurrence <strong>of</strong> macroinvertebrates can be employed togive a form <strong>of</strong> biotic index. Biotic indices are simple assessments <strong>of</strong> the composition <strong>of</strong> benthicinvertebrate communities which allow non-experts to make pronouncements upon water quality, withthe minimum <strong>of</strong> taxonomic knowledge. <strong>The</strong>y have widespread application in the field <strong>of</strong>environmental monitoring <strong>and</strong> while widely used elsewhere in the world, e.g. Europe, a successfulscheme has yet to be developed for employment in the Caribbean.ReferencesBoon, P.J., Jupp, B.P. & D.G. Lee (1986). <strong>The</strong> benthic ecology <strong>of</strong> rivers in the Blue Mountains(Jamaica) prior to construction <strong>of</strong> a water regulation scheme. Arch. Hydrobiol. Suppl. 74(3),315-355.Botosaneanu, L. & E.J. Hyslop (in press 1 ). A systematic <strong>and</strong> biogeographic study <strong>of</strong> the caddisflyfauna <strong>of</strong> Jamaica (Insecta - Trichoptera) - with description <strong>of</strong> a first known case <strong>of</strong>enantiomorphy in insects. Bulletin de l'Instituut Royal des Sciences Naturelles de Belgique.Ent. 68Botosaneanu, L. & E.J. Hyslop (in press 2 ). Additional contribution to the knowledge <strong>of</strong> the caddisflyfauna <strong>of</strong> Jamaica. Ent<strong>of</strong>auna.O-12 ECOTOXICITY OF INSECTICIDES IN THE JAMAICANENVIRONMENT: BIOCONCENTRATION OF CHLORPYRIFOSRESIDUES IN TILAPIA IN FRESH AND BRACKISH WATERSCarla N. Thomas <strong>and</strong> Ajai Mansingh<strong>Department</strong> <strong>of</strong> Life Sciences, MonaWidespread use <strong>of</strong> insecticides in Jamaica has contaminated its surface, ground <strong>and</strong> coastal waters(Mansingh et al., 1997). Chlorpyrifos is used in banana plantations, termite control <strong>and</strong> general pestcontrol <strong>and</strong> has been detected in several Jamaican rivers (Witter et al., 1998). It is not known,however, what effects these residues may be having on non-target organisms inhabiting these waters.<strong>The</strong> present study was, therefore, conducted on the uptake <strong>and</strong> degradation <strong>of</strong> chlorpyrifos residuesby Tilapia fish in fresh <strong>and</strong> brackish water.Red hybrid Tilapia fingerlings (6 - 9 cm long) were acclimatized to brackish water by gradualexposure to water <strong>of</strong> increasing salinity over time. <strong>The</strong> uptake <strong>of</strong> chlorpyrifos was studied through 6hr spiking exposure <strong>of</strong> the fish to 0.005mg/L <strong>of</strong> the insecticide for 96 hr in fresh water <strong>and</strong> 24 hrpulse exposure to 0.05 mg/L for 72 hr in fresh or brackish water. Three fish were exposed to theinsecticide in each <strong>of</strong> eight glass aquaria (three replicates), removed at regular intervals, rinsed,dried, weighed <strong>and</strong> homogenized in petroleum ether.32


Filtered extracts were partitioned in acetonitrile, cleaned in a florisil column <strong>and</strong> concentrated foranalysis according to the methodology described by Robinson (1997). Identification <strong>and</strong>quantification <strong>of</strong> residues were done by a Shimadzu 9A gas chromatograph equipped with an FPD.Analytical conditions were: glass column, 1.6 m by 2 mm packed with OV-17; carrier gas, nitrogen,at a flow rate <strong>of</strong> 30 - 35 mL/min; temperature settings - column 230 o C, injector <strong>and</strong> detector 260 o C.Detection levels ranged from 0.001 - 0.002 ng.Fish exposed to 0.005 mg/L chlorpyrifos in fresh water accumulated only 35% (1.35 mg/g) <strong>of</strong> theinsecticide within the first 2 hr. Accumulation fluctuated thereafter, reaching a maximum <strong>of</strong> 3.87mg/g after 48 hr <strong>of</strong> exposure followed by a decline within the next 48 hr to 2.45 mg/g. At higherconcentration (0.05 mg/L), there was rapid accumulation <strong>of</strong> chlorpyrifos by the fish as 51% (0.86mg/g) <strong>of</strong> the total 72-h accumulation <strong>of</strong> the insecticide was achieved after 1 hr <strong>of</strong> exposure. Uptakethen fluctuated before rapidly increasing to1.68 mg/g at the end <strong>of</strong> the 72-hr exposure period.<strong>The</strong>re was a two-fold accumulation <strong>of</strong> chlorpyrifos by fish in brackish water compared with freshwater as maximum bioconcentration (0.96 mg/g) in brackish water was achieved after 1 hr <strong>of</strong>exposure. Accumulation <strong>of</strong> the insecticide subsequently declined to 0.39 mg/g at the end <strong>of</strong> the 72-hrexposure period (Table). An unidentified organophosphorus metabolite <strong>of</strong> chlorpyrifos was alsodetected within 1 - 2 hr <strong>of</strong> exposure to the insecticide in fresh <strong>and</strong> brackish water.<strong>The</strong> rapid uptake <strong>of</strong> chlorpyrifos by Tilapia is consistent with the relatively high octanol-waterpartition coefficient (logKow = 4.82) <strong>of</strong> the insecticide which suggests that it readily partitions in fishtissues. Although the rapid formation <strong>of</strong> the metabolite implies that the chemical is quicklybiotransformed, the toxicity <strong>of</strong> this metabolite to the fish is unknown. Thus, further studies areneeded, including the elimination <strong>of</strong> the parent compound <strong>and</strong> its metabolite by the fish.ReferencesMansingh, A., Robinson, D.E. <strong>and</strong> Dalip, K.M. (1997). Insecticide contamination <strong>of</strong> the Jamaicanenvironment, Trends in Anal. Chem. 16 (3): 115-123.Robinson, D. E., Mansingh, A. <strong>and</strong> Dasgupta, T. P. (1997) Fate <strong>of</strong> endosulfan in river <strong>and</strong> coastalwaters <strong>of</strong> Jamaica. Proc. Int. Symp. on the Use <strong>of</strong> nuclear <strong>and</strong> related techniques forstudying environmental behaviour <strong>of</strong> crop protection chemicals, IAEA, Vienna, July 1 - 5,1996. pp. 301-311.Robinson, D.E. (1997). <strong>The</strong> fate, biological impact <strong>and</strong> management <strong>of</strong> endosulfan <strong>and</strong>ethoprophos in the Jamaican environment. Ph. D. <strong>The</strong>sis. Univ. West Indies, Mona,Jamaica. 289 pp.Witter, J.V., Robinson, D.E., Mansingh, A. <strong>and</strong> Dalip, K.M. (1998). Insecticide contamination <strong>of</strong>Jamaican environment. V. Isl<strong>and</strong>-wide rapid survey <strong>of</strong> residues in surface <strong>and</strong> groundwater. Environ. Monitor. & Assess. (In press).33


Table:Concentrations <strong>of</strong> chlorpyrifos <strong>and</strong> its metabolite accumulated by red hybridTilapia exposed to 0.005 <strong>and</strong> 0.05 mg/L insecticide in fresh <strong>and</strong> brackish water_________________________________________________________________Time (hr)Mean (± S.E.) conc. <strong>of</strong> chlorpyrifos (mg/g) <strong>and</strong> metabolite(units/g; data in parentheses) in:Fresh water Brackish water0.005 mg/L 0.05 mg/L 0.05 mg/L______________________________________________________________________________1 - 0.86 ± 0.017 0.96 ± 0.018- (234.22 ± 60.883) (289.06 ± 89.132)2 1.35 ± 0.314 - -(80.98 ± 3.116) - -4 - 0.99 ± 0.062 0.80 ± 0.030- (152.67 ± 46.493) (193.27 ± 71.201)8 1.50 ± 0.089 1.15 ± 0.004 0.59 ± 0.032(15.00 ± 2.974) (174.49 ± 40.869) (119.98 ± 30.852)12 1.47 ± 0.081 - -(72.13 ± 11.34) - -24 2.85 ± 0.224 0.72 ± 0.019 0.48 ± 0.062(395.37 ± 39.209) (241.10 ± 35.941) 216.65 ± 3.798)48 3.87 ± 0.418 0.77 ± 0.038 0.73 ± 0.03(286.96 ± 36.419) (309.06 ± 10.773) (326.85 ± 18.379)72 3.05 ± 0.335 1.68 ± 0.059 0.39 ± 0.39(570.15 ± 74.494) (176.07 ± 12.012) (142.97 ± 9.754)96 2.45 ± 0.109 - -(1144.4 ± 144.85) - -_______________________________________________________________________________34


O-13 THE PERSISTENCE OF MIRAL 500CS ON TWO COFFEEFARMS IN JAMAICADwight E. Robinson<strong>Department</strong> <strong>of</strong> Life Sciences, MonaSerious outbreaks <strong>of</strong> the c<strong>of</strong>fee leaf miner (CLM), Perileucoptera c<strong>of</strong>feella, during 1991 - 1995prompted the spraying <strong>of</strong> several insecticides, particularly Miral 500CS (isaz<strong>of</strong>os), which wasfound to be quite effective in suppressing the CLM (Reid <strong>and</strong> Robinson, 1994). However, concernsabout its persistence in the environment <strong>and</strong> possible impact on non-target organisms prompted thefollowing study which was aimed at determining its persistence in two varied c<strong>of</strong>fee cultivatingconditions <strong>of</strong> Jamaica.<strong>The</strong> study was carried out on a Blue Mountain plantation (Mavis Bank) <strong>and</strong> another in the highl<strong>and</strong>s<strong>of</strong> St. Catherine (Mountain Hill). Sample plots <strong>of</strong> 0.2 ha with about 250 trees were selected on eachfarm <strong>and</strong> treated with Miral 500CS at a concentration <strong>of</strong> 3 mL/L. A 625 m 2 area <strong>of</strong> soil under treeswas demarcated in a separate area <strong>and</strong> treated similarly. Thirty leaves <strong>and</strong> berries were r<strong>and</strong>omlypicked from treated trees <strong>and</strong> a 100g sub-sample <strong>of</strong> soil taken from a mixture <strong>of</strong> ten 60-g soilsamples taken at r<strong>and</strong>om from the treated soil area. Samples were collected 2 hours <strong>and</strong> 1, 3, 7, 14<strong>and</strong> 21 days after treatment for extraction <strong>and</strong> analysis in the laboratory. Rainfall was also recorded.Samples were weighed, extracted in methylene chloride by shaking on a wrist action shaker, filtered<strong>and</strong> cleaned on a florisil column. Cleaned extracts were concentrated to 10 mL <strong>and</strong> analyzed on aShimadzu 9A gas chromatograph equipped with an FPD chromatopack data system. Analyticalconditions were: glass column, 1.6 m by 2 mm packed with OV-17; carrier gas; nitrogen, at a flowrate <strong>of</strong> 30 - 35 mL/min; temperature settings <strong>of</strong> 230 o C for the column <strong>and</strong> 260 o C for the injector <strong>and</strong>detector. <strong>The</strong> detection limit for isaz<strong>of</strong>os was 0.004 ng. Probit analysis was used to determine thehalf life <strong>of</strong> the insecticide on each substrate.<strong>The</strong> half life <strong>of</strong> Miral 500CS on c<strong>of</strong>fee leaves <strong>and</strong> in soil was 7-fold greater in the Blue Mountainthan highl<strong>and</strong> plantation (Table). This trend was reversed for the berries as the loss <strong>of</strong> Miral 500CSfrom the berries was 3-fold greater on the Blue Mountain than the highl<strong>and</strong> plantation. Variations inpersistence <strong>of</strong> the insecticide on leaves <strong>and</strong> berries <strong>of</strong> the plantations may be attributed to differingenvironmental conditions such as precipitation, temperature, sunlight <strong>and</strong> wind velocity, whichwould all impact on the insecticide’s loss <strong>and</strong> degradation (Edwards, 1975; Hill <strong>and</strong> Wright, 1978).In addition to these factors, its persistence in the soil would also be influenced by soil properties suchas the organic matter content.<strong>The</strong>re is a direct correlation between the persistence <strong>of</strong> insecticides in soil <strong>and</strong> organic matter content<strong>of</strong> the soil (Arnold <strong>and</strong> Briggs, 1990) which would explain the greater persistence <strong>of</strong> Miral 500CS inMavis Bank than Mountain Hill soil which had 4.55 <strong>and</strong> 1.15% organic matter, respectively. Itshould be noted that the half-lives presented were obtained under conditions <strong>of</strong> high rainfall (94 <strong>and</strong>128 mm in Mountain Hill <strong>and</strong> Mavis Bank, respectively) which is indicative <strong>of</strong> the highenvironmental persistence <strong>of</strong> Miral 500CS. It is, therefore, obvious that encapsulation <strong>of</strong> the activeingredient, in an attempt to reduce its hazardous effects, has resulted in its increased persistence inthe environment, thus prolonging possible harmful effects.35


Table: Half life <strong>of</strong> Miral 500CS on leaves <strong>and</strong> fruit, <strong>and</strong> in soil on two c<strong>of</strong>feeplantations in Jamaica______________________________________________________________________________Plantation t50 days 95% confidence interval SlopeSample______________________________________________________________________________Mavis Bank (Blue Mountain)Leaves 14.0 52.2 - 239.7 0.740 ± 0.039Berries 3.5 1.0 - 10.6 0.926 ± 0.029Soil 59.8 37.1 - 145.0 1.029 ± 0.038Mountain Hill (Highl<strong>and</strong>)Leaves 2.0 1.0 - 3.2 1.382 ± 0.096Berries 10.0 5.0 - 23.2 1.307 ± 0.048Soil 9.9 5.6 - 19.2 1.281 ± 0.047______________________________________________________________________________ReferencesArnold, D.J. <strong>and</strong> Briggs, G.G. (1990). <strong>The</strong> fate <strong>of</strong> pesticides in soil: predictive <strong>and</strong> practical aspectsIn: Environmental Fate <strong>of</strong> Pesticides. (Eds. Hutson, D.H. <strong>and</strong> Roberts, T.R.), Wiley <strong>and</strong>Sons Ltd. Chichester 7: 101-102.Edwards, C.A. (1975). Factors that affect the persistence <strong>of</strong> pesticides in plants <strong>and</strong> soils.Pure <strong>and</strong>Appl. Chem. 42: 1-2.Hill, I.R. <strong>and</strong> Wright, S.J.L. (Eds.) (1978) Pesticide microbiology. London, Great Britain;Academic Press Inc. (London) Ltd. 844 pp.Reid, J. C. <strong>and</strong> D. E. Robinson. (1994). Assessment <strong>of</strong> different insecticides for the suppression<strong>of</strong> an outbreak <strong>of</strong> the c<strong>of</strong>fee leaf miner, Leucoptera c<strong>of</strong>feella in Jamaica, W. I. Turrialba.44(1): 112 - 116.O-14 ENGINEERING RESISTANCE TO RINGSPOT POTYVIRUSIN PAPAYAP. Tennant 1 , D. Gonsalves 2 <strong>and</strong> M. H. Ahmad 11<strong>The</strong> Biotechnology Centre, Mona;2<strong>Department</strong> <strong>of</strong> Plant Pathology, Cornell University, Geneva, NYPapaya ringspot virus (PRSV) is the major disease affecting papaya production in Hawaii, Florida,the Caribbean, South America, India <strong>and</strong> the Far East. Leaves <strong>of</strong> infected trees become mottled <strong>and</strong>distorted, ringspots appear on fruit, water-soaked streaks appear on stems <strong>and</strong> petioles <strong>and</strong> the treebecomes stunted, producing few small fruit.36


In Jamaica, some 40% <strong>of</strong> papaya orchards have been devastated by PRSV. Since genetic resistanceis not available, efforts were aimed at using transgenic resistance for the control <strong>of</strong> PRSV inJamaica. Reverse transcription <strong>and</strong> polymerase chain reaction were used to engineer coat protein(CP) gene constructs <strong>of</strong> a local PRSV isolate into plant transformation vectors. CP constructs weresubsequently introduced into Carica papaya L. embryogenic calli by microprojectile bombardmentusing NPTII <strong>and</strong> GUS as selectable markers. Some 150 transgenic lines were obtained from 18bombardment experiments. Under greenhouse conditions, R0 clones <strong>of</strong> 11 lines proved resistant torepeated manual inoculations with the virus. Similarly inoculated nontransgenic papaya plantsdeveloped symptoms 11 to 40 days after inoculation.Clones <strong>of</strong> R0 plants have since been transferred to a half-acre plot in Clarendon. Virus infectionwas first observed on nontransgenic plants 6 months after planting using natural aphid populationsas inoculum vectors. Twenty-eight transgenic lines remain symptomless <strong>and</strong> ELISA-negative.<strong>The</strong>se preliminary results suggest that transgenic resistance could be a practical solution to thePRSV problem in Jamaica.ReferencesGonsalves, D. (1994). Papaya ringspot Virus. In Compendium <strong>of</strong> Tropical Fruit Diseases. Eds RCPloetz, GA, Zentmyer, WT, Nishijima, KG <strong>and</strong> Rohrbach, HD Ohr. pp. 67-68. St Paul, MN, APSPress 88p.Yeh, S-D.<strong>and</strong> Gonsalves, D. (1994). Practices <strong>and</strong> perspectives <strong>of</strong> control <strong>of</strong> papaya ringspot virusby cross protection. In Advances in Disease Vector Research. Ed. KF Harris, 10: 237-257.New York :Springer-Verlag.O-15 GENETIC DIVERSITY AND RELATIONSHIPS AMONGGEMINIVIRUSES FROM JAMAICA AND BARBADOSMarcia E. Roye, Wayne A. McLaughlin, Medhat K. Nakhla <strong>and</strong> Douglas P. Maxwell<strong>Department</strong> <strong>of</strong> Basic Medical Sciences-Biochemistry; <strong>and</strong> <strong>The</strong> Biotechnology Centre, Mona;<strong>Department</strong> <strong>of</strong> Plant Pathology, University <strong>of</strong> Wisconsin-MadisonGeminiviral DNA probes, polymerase chain reaction <strong>and</strong> nucleotide sequencing was used to identify7 geminiviruses from Jamaica <strong>and</strong> 3 from Barbados. PCR-amplified products for DNA-A weregenerated from 80% <strong>of</strong> plants from Jamaica that gave hybridisation signals <strong>and</strong> 32% <strong>of</strong> plants fromBarbados. Nucleotide identity <strong>of</strong> the common regions <strong>of</strong> DNA-A <strong>and</strong> DNA-B, <strong>and</strong> partial nucleotidesequences <strong>of</strong> the ac1, av1, bc1, <strong>and</strong> bv1 genes confirmed the presence <strong>of</strong> bipartite geminiviruses inthe following crops from Jamaica: P. vulgaris <strong>and</strong> P. lunatus (bean golden mosaic virus, BGMV-JM2), L. esculentum <strong>and</strong> C. chinense (tomato dwarf leaf curl virus, TDLCV), <strong>and</strong> two distinctviruses infecting cabbage. <strong>The</strong> weeds associated with viruses included Sida spp. (sida golden mosaicvirus, SiGMV-JM), W. amplissima (wissadula golden mosaic virus, WGMV) <strong>and</strong> three distinctviruses in M.lathyroides (macroptilium golden mosaic virus strains 1 <strong>and</strong> 2, MacGMV-JM1,MacGMV-JM2 <strong>and</strong> SiGMV-JM).37


Nucleotide sequence analysis <strong>of</strong> the common region, ac1 <strong>and</strong> av1 indicate that geminiviral DNA wasassociated with C. papaya (papaya virus, PaGV).Nucleotide identity <strong>of</strong> the common regions <strong>of</strong> DNA-A <strong>and</strong> DNA-B, <strong>and</strong> partial nucleotide sequences<strong>of</strong> the ac1, av1, bc1, <strong>and</strong> bv1 genes confirmed the same bipartite geminiviruses (from Barbados) intomato, musk melon <strong>and</strong> water melon <strong>and</strong> two distinct geminiviruses in M lathyroides.Nucleotide sequence alignment <strong>of</strong> the common region <strong>and</strong> the 5’ end <strong>of</strong> ac1 was used to determinephylogenetic relationships <strong>of</strong> the new Jamaican viruses with other Western Hemispheregeminiviruses. Geminivirus isolate from P. vulgaris (BGMV-JM1) <strong>and</strong> an isolate from P. lunatus(BGMV-JM2) was placed in BGMV type II cluster. SiGMV-JM, <strong>and</strong> MacGMV-JM1, was closelyrelated to potato yellow mosaic geminivirus (PYMV). <strong>The</strong> viruses associated with W. amplissima(WGMV), C. papaya (PaGV), M. lathyroides (MacGMV-JM2) <strong>and</strong> tomato <strong>and</strong> pepper (TDLCV)were closely related to each other. <strong>The</strong> tomato virus from Barbados was a new previouslyunreported virus <strong>and</strong> was distinct from the two macrroptilium viruses. <strong>The</strong>se results indicate thatcrop-infecting <strong>and</strong> weed-infecting geminiviruses from Jamaica <strong>and</strong> Barbados are distinct, highlydiverse, <strong>and</strong> have several geographical origins <strong>and</strong> weeds are not host to crop-infecting geminivirusesin Jamaica.O-16 TOMATO YELLOW LEAF CURL GEMINIVIRUS INFECTINGHOT PEPPERS (CAPSICUM CHINENSE) IN JAMAICASherline Brown, Conroy Green, Marcia Roye, Wayne McLaughlin,Medhat K. Nakhla <strong>and</strong> Douglas P. Maxwell<strong>Department</strong> <strong>of</strong> Basic Medical Sciences (Biochemistry) <strong>and</strong> <strong>The</strong> Biotechnology Centre, Mona;<strong>Department</strong> <strong>of</strong> Plant Pathology, University <strong>of</strong> Wisconsin-MadisonSince 1991, farmers in southern <strong>and</strong> central Jamaica have reported losses <strong>of</strong> up to 100% in hotpepper (Capsicum chinense) crops, <strong>and</strong> the causal agent was presumed to be a whitefly-transmittedgeminivirus. Symptoms included mild chlorosis <strong>and</strong> upward leaf curling. A TYLCV intergenic(specific) DNA probe was used to confirm the presence <strong>of</strong> TYLCV in 44% <strong>of</strong> peppers (Capsicumsp) sampled. Polymerase chain reaction (PCR) primers specific for tomato yellow virus (TYLCV-Is) were used to amplify full-length as well as sub-genomic viral fragments from total DNAextracted from pepper (Capsicum sp.) with viral symptoms. <strong>The</strong>se viral fragments were cloned frompepper collected in November 1992 from St. Elizabeth Parish in Jamaica. Nucleotide sequencecomparisons <strong>of</strong> the intergenic region <strong>of</strong> the clone from pepper gave >97% identity to TYLCV-Is.Nucleotide sequence identities <strong>of</strong> the intergenic region among cloned TYLCV intergenic regions fromtomato <strong>and</strong> pepper infected with TYLCV were >99%. <strong>The</strong>se results indicate that the TYLCVassociated with tomato <strong>and</strong> pepper plants were all isolates <strong>of</strong> TYLCV-Is. Electric discharge particleacceleration inoculation <strong>of</strong> tomato <strong>and</strong> pepper using a TYLCV full-length clone associated withtomato from Jamaica <strong>and</strong> Bemisia tabaci transmission studies were used to confirm infectivity <strong>of</strong>TYLCV-Is on pepper.Our results suggest that pepper is a non-adapted host for TYLC. This reportis the first to show the association <strong>of</strong> TYLCV with pepper.38


O-17 POSTHARVEST STORAGE OF YAM TUBERS:A BIOCHEMICAL PERSPECTIVEHelen N. Asemota 1 <strong>and</strong> Anthony U. Osagie 21<strong>Department</strong> <strong>of</strong> Basic Medical Sciences (Biochemistry) <strong>and</strong> <strong>The</strong> Biotechnology Centre Mona;2<strong>Department</strong> <strong>of</strong> Biochemistry, University <strong>of</strong> BeninIn this study, healthy yam tubers were kept under local storage conditions <strong>and</strong> the carbohydratecompositional changes, metabolism <strong>of</strong> exogenously supplied 1-14 C <strong>and</strong> 6- 14 C-glucose by the storedtubers were monitored. <strong>The</strong> changes in the activities with storage <strong>of</strong> some enzymes <strong>of</strong> carbohydratemobilization <strong>and</strong> key enzymes <strong>of</strong> oxidative pathways were also assayed at regular intervals throughdormancy <strong>and</strong> sprouting <strong>of</strong> the stored tubers.Results show remarkable changes in the carbohydrate composition with tuber storage.Chromatographic analysis <strong>of</strong> the ethanol soluble sugars <strong>of</strong> non-dormant tubers showed the majorsugars to be glucose, fructose <strong>and</strong> sucrose.<strong>The</strong>re were also remarkable changes in the activities <strong>of</strong> enzymes involved in carbohydratemobilization i.e. Phosphorylase, Amylase <strong>and</strong> Invertase, <strong>and</strong> carbohydrate oxidation i.e. Glucose6-phosphate dehydrogenase (G6PD) <strong>and</strong> Phosph<strong>of</strong>ructokinase. <strong>The</strong> observations on the changes in theactivities <strong>of</strong> G6PD <strong>and</strong> PFK during storage, together with the distribution <strong>of</strong> radioactivity in tuberssupplied 1- 14 C <strong>and</strong> 6- 14 C glucose, indicate that the predominant pathway <strong>of</strong> oxidation <strong>of</strong>carbohydrate in stored yam tubers in glycolytic.This study provides evidence that the yam tuber is capable <strong>of</strong> metabolizing exogenously suppliedglucose <strong>and</strong> that free pentoses are not accumulated in the stored tubers.<strong>The</strong> results will be discussed as they relate to biochemical changes in the stored yam tubers, bearingin mind the possibility <strong>of</strong> producing yam tuber genotype with capacity for early sprouting orprolonged dormancy through genetic transformation.O- 18 IMPROVEMENT OF COMMERCIAL CULTIVATION OFDENDROBIUMS THROUGH SUBSTRATE AND NUTRIENTMODIFICATION: BIOLOGICAL AND ECONOMIC ANALYSISTai Chun, Paulette; Potluri, Sasikala D.P. <strong>and</strong> Devi Prasad, P.V.<strong>Department</strong> <strong>of</strong> Life Sciences, Mona<strong>The</strong> commercial cultivation <strong>of</strong> Dendrobiums has been identified as an area <strong>of</strong> significant potentialfor the horticulture industry in Jamaica because <strong>of</strong> its high market dem<strong>and</strong> <strong>and</strong> price. This crop ismainly cultivated in Thail<strong>and</strong> <strong>and</strong> Hawaii in a variety <strong>of</strong> different growing media <strong>and</strong> methods <strong>of</strong>culture. <strong>The</strong> present work was undertaken to determine the most suitable <strong>and</strong> pr<strong>of</strong>itable methodsfor the cultivation Dendrobium orchids in Jamaica. A 3 x 3 Latin Square design with split plotswas used to evaluate the performance <strong>of</strong> Dendrobiums in 7 different media/ culture treatments . <strong>The</strong>media employed were coconut husk shells, coconut husk pads , coconut husk, river gravel, brickchips, igneous rock in clay <strong>and</strong> plastic pots as well culture without any media. Three levels <strong>of</strong>nitrogen were employed - 136 or 272 or 544 Kg N hā 1 yr -1 . Data were collected for two years.39


Regardless <strong>of</strong> the level <strong>of</strong> fertilizer, the plants grown in coconut husk shells gave the best results interms <strong>of</strong> the number <strong>of</strong> spikes per plant, blooms per spike, spike length . Coconut husk shells alsoresulted in higher percentage <strong>of</strong> premium grade <strong>and</strong> export quality blooms. Increasing fertilizerlevels resulted in overall better production, spike quality <strong>and</strong> in greater percentages <strong>of</strong> high priced<strong>and</strong> export quality blooms. Overall best performance was obtained from the plants growing incoconut husk shells at the highest levels <strong>of</strong> fertilizer used, i.e. 544Kg N ha-1 yr -1 . <strong>The</strong> performance<strong>of</strong> the plants in coconut husk shells was associated with significantly higher percentages <strong>of</strong> tissue N,P <strong>and</strong> K. <strong>The</strong> beneficial economic implications <strong>of</strong> the results to the farmers <strong>and</strong> the country will bediscussed.O-19 CYANOBACTERIAL BIOFERTILISERS FOR RICEIN JAMAICABoyd, Frederick A.H. <strong>and</strong> Devi Prasad, P.V.<strong>Department</strong> <strong>of</strong> Life Sciences, Mona<strong>The</strong> wetl<strong>and</strong> cultivation <strong>of</strong> Oryza sativa provides a particularly suitable environment for thedevelopment <strong>and</strong> utilization <strong>of</strong> non-symbiotic nitrogen-fixing autotrophic cyanobacteria [blue greenalgae] as well as other diazotrophic ecotypes. While extensive work has been carried out in Asia<strong>and</strong> Africa on the suitablitiy <strong>of</strong> using cyanobacteria as bi<strong>of</strong>ertilisers, very little , if any, work hasbeen carried out in the Caribbean <strong>and</strong> Latin America. <strong>The</strong> present work has been undertaken toassess the suitability <strong>of</strong> cyanobacterial bi<strong>of</strong>ertilisers for rice under Caribbean conditions. Anabaenavariabilis , collected <strong>and</strong> isolated locally, was chosen based on its superior nitrogen fixing cpacity<strong>and</strong> shorter generation time over other local strains. <strong>The</strong> cyanobacteriaum was used in solitaryapplication as well as in combined application with the chemical fertilizer at the recommendeddosage [80kg N ha -1 ] <strong>and</strong> the reduced dosage [40 kg N hā 1 ].<strong>The</strong>r fertilizer regimen were tested in greenhouse trials initially, using two types <strong>of</strong> soils <strong>and</strong> finallyin two field crops. Analysis <strong>of</strong> yield parameters including grain <strong>and</strong> straw yields, 100-grain wt.,carbohydrate <strong>and</strong> protein content <strong>of</strong> the grain <strong>and</strong> straw were carried out in addition to growth <strong>and</strong>development parameters including tiller production <strong>and</strong> panicle emergence period in order todetermine any effects <strong>of</strong> the biological nitrogen fixation.<strong>The</strong> results <strong>of</strong> this study indicate that the solitary application <strong>of</strong> the cyanobacterium resulted toenhancement in the yield parameters <strong>of</strong> grain yield [23%] <strong>and</strong> straw yield [28%], 100-grainyield[26%], carbohydrate levels in the grain [10%] <strong>and</strong> straw [17%] . Protein content <strong>of</strong> the grain[22%] <strong>and</strong> the straw[19%] over the respective controls. In most cases this appreciation due to thecyanobacterium was equivalent to those <strong>of</strong> the reduced fertilizer dosage. <strong>The</strong>ir combinedapplication resulted in improvements in grain yield [83%] <strong>and</strong> straw yield [20%], protein content <strong>of</strong>the grain [45%] <strong>and</strong> straw [28%] over the respective controls. With the exception <strong>of</strong> the grain <strong>and</strong>straw yields, the combined application at the reduced fertilizer dosage had a greater stimulatoryeffect on the crop parameters than did the recommended fertilizer dosage <strong>applied</strong> alone. <strong>The</strong>increase in tiller production due to the cyanobacterium [27%] was less than that due to the reducedfertilizer dosage [53%] but their combined application [55%] was not significantly different fromthat due to the solitary application <strong>of</strong> the recommended fertilizer dosage [59%]. Panicle emergenceperiod was found to be directly dependent on the available nitrogen present, regardless <strong>of</strong> its source.40


<strong>The</strong>se results indicate that cyanobacteria when used as bi<strong>of</strong>ertilizers in the wetl<strong>and</strong> cultivation <strong>of</strong> rice<strong>of</strong>fers the potential supplimenting its chemical nitrogen fertilizer requirements <strong>of</strong> up to 40kg N -1 ha.This is particularly sutitable for small farmers <strong>of</strong> rice as this technolgoy <strong>of</strong>fers the prospect <strong>of</strong>decreased input costs while facilitating increased quantity as well as quality <strong>of</strong> yields.O-20 DIVERSITY AMONG POPULATIONS OF XANTHOMONASCAMPESTRIS PV. VESICATORIA FROM FIVE EASTERNCARIBBEAN ISLANDS WITH RESPECT TO SECRETION OFEXTRACELLULAR ENZYMES, POLYSACCHARIDE PRODUCTIONAND PATHOGENICITYHenry A.M. 1 , Hamilton M.A.E. 1 , <strong>and</strong> O’ Garro L.W. 21 Biochemistry Section, <strong>Department</strong> <strong>of</strong> Basic Medical Sciences,Mona;2<strong>Department</strong> <strong>of</strong> Biology, Cave HillXanthomonas campestris pv.vesicatoria (proposed: Xanthomonas axonopodis pv. vesicatoria) isthe causative agent <strong>of</strong> bacterial spot disease <strong>of</strong> tomato (Lycopersicon esculentum Mill.) <strong>and</strong> pepper(Capsicum annum L.) plants. 851 strains from five Eastern Caribbean isl<strong>and</strong>s (Antigua, Barbados,Grenada, St.Kitts, <strong>and</strong> St. Lucia) were screened for the production <strong>of</strong> amylase, glucanase, pectinase<strong>and</strong> protease. All the isolates were negative for the excretion <strong>of</strong> the glucanases <strong>and</strong> pectinasesindicating that these enzymes were not important in the pathogenicity <strong>of</strong> these strains. 85% <strong>of</strong> thestrains produced amylases <strong>and</strong> 77% produced proteases. Overall, 69% <strong>of</strong> the strains showed bothamylolytic <strong>and</strong> proteolytic activity. <strong>The</strong> quality <strong>of</strong> xanthan produced by the isolates was determinedby the flow rate <strong>of</strong> the gum, as this is directly proportional to viscosity. Bacterial strains thatproduced high viscosity xanthan showed higher cfu/11.5cm 2leaf area <strong>and</strong> faster symptomsdevelopment over a 10 – 15 day period, than strains <strong>of</strong> low viscosity gum production. <strong>The</strong> resultssuggest a possible relationship between enzyme pr<strong>of</strong>ile <strong>and</strong> pathogenicity as all the strains producinghigh viscosity gum produced both amylases <strong>and</strong> proteases.O-21 PHYSIOLOGY AND BIOCHEMISTRY OF SALT STRESS ONTHE AXILLARY BUD CULTURES OF CASSAVAPotlrui, Sasikala D.P. <strong>and</strong> Devi Prasad, P.V.<strong>Department</strong> <strong>of</strong> Life Sciences, MonaTwo local varieties <strong>of</strong> Cassava named UWI-1 <strong>and</strong> UWI-2 were brought in to tissue culture throughnodal cuttings <strong>and</strong> apical meristem cultures. Axillary bud cultures <strong>of</strong> these were used to study thephysiology <strong>and</strong> biochemistry <strong>of</strong> salinity stress, as tissue culture techniques <strong>of</strong>fer unique advantage insuch studies. <strong>The</strong> cultures were grown on Murashige <strong>and</strong> Skoog medium supplemented with micronutrients<strong>and</strong> vitamins . Various concentrations <strong>of</strong> salt in the medium were obtained by using crudesea salt ranging from 0 to 1.0%. Crude sea salt was used as it would provide salinities close tonaturally occurring salinities in providing not only sodium chloride but other salts as well.41


Various morphological, physiological <strong>and</strong> biochemical parameters were studied including shootheight, number <strong>of</strong> nodes, number <strong>of</strong> branches, proline , protein, carbohydrate, sodium <strong>and</strong> potassiumlevels <strong>of</strong> shoot <strong>and</strong> root, <strong>and</strong> the activity <strong>of</strong> the enzyme nitrate reductase in both shoot <strong>and</strong> root.Plantlet height <strong>and</strong> number <strong>of</strong> nodes decreased with increase in salinity over 0.4% but number <strong>of</strong>branches increased. Proline levels increased in both varieties but with different levels <strong>of</strong> increase.Total protein content increased in UWI-2 but did not show much change in UWI-2. <strong>The</strong> ratiobetween sodium <strong>and</strong> potassium was altered though the accumulation <strong>of</strong> both metals increased due tosalinity. In UWI-1, the activity <strong>of</strong> the enzyme nitrate reductase showed a significant decreasecompared to UWI-2. From the results <strong>of</strong> the present study, it may be assumed that the inhibitoryaffects are mainly due to inhibition or modification <strong>of</strong> the utilization <strong>of</strong> nitrogen nutrition <strong>and</strong> alsopossibly due to the affect on endogenous growth substances. Any tolerance observed seem to be dueto the increase in the accumulation <strong>of</strong> proline <strong>and</strong> carbohydrates. <strong>The</strong>se results will be discussedespecially in relation to the usefulness <strong>of</strong> axillary bud cultures in comparison to cell cultures <strong>and</strong>field experiments for physiological <strong>and</strong> biochemical studies <strong>of</strong> stress tolerance.O-22 TOWARD INCREASING YAM PRODUCTION INCHALLENGED ENVIRONMENTS: IN VITRO STUDIES OF THEEFFECT OF SALINITY STRESS ON SOME BIOCHEMICALPARAMETERS OF YAM (Dioscorea alata) PLANTLETSA.O. Wheatley <strong>and</strong> H.N. Asemota 1<strong>Department</strong> <strong>of</strong> Basic Medical Sciences (Biochemistry);1<strong>The</strong> Biotechnology Centre, MonaReducing l<strong>and</strong> waste through production <strong>of</strong> plantlets designed to survive in challenged environments,is one <strong>of</strong> the great promises <strong>of</strong> biotechnology. In sea-logged areas, problem <strong>of</strong> salinity rendersapproximately 25% <strong>of</strong> arable l<strong>and</strong> unproductive. In this study, yam plantlets were made salinetolerant/resistant <strong>and</strong> the biochemical basis <strong>of</strong> adaptation were analysed.In vitro plantlets <strong>of</strong> Dioscorea alata cultivar ‘Sweet yam’ were subcultured onto normalmultiplication media (MS basal media with 30g/L sucrose <strong>and</strong> 0.1mg/L BAP) <strong>and</strong> on saline mediasupplemented with 6g/l <strong>and</strong> 12g/l NaCl. Growth <strong>of</strong> plantlets <strong>and</strong> root formation were assessed alongwith changes in activities <strong>of</strong> invertase (EC 3.2.1.26) <strong>and</strong> peroxidase (EC 1.11.1.7) for six weeks inculture. Control plantlets were 100% rooted compared to the 70% rooting <strong>of</strong> plantlets under salinitystress <strong>of</strong> 6g/L by the third week in culture. No root formation was observe for plantlets on 12g/Lsalinity level. Leaf formation occurred two weeks earlier in the control plantlets than those on mediasupplemented with 6g/L NaCl. No new leaves were formed on explants subcultured on mediacontaining 12g/L NaCl.Control plantlets showed sharp increases in invertase activity from the second week in culture.Plantlets at 6g/L salinity level also showed increases in invertase activity from the second but <strong>of</strong> lessmagnitude reflecting less utilization <strong>of</strong> the sucrose carbon source <strong>of</strong> the in vitro conditions. At12g/L saline condition, plantlets could hardly utilize the carbon source as reflected by theinsignificant changes in invertase activity during the six weeks in culture, <strong>and</strong> hence no energy tosupport growth <strong>of</strong> transferred explants. Peroxidase activity was higher than control in plantletsunder salinity stress <strong>of</strong> 6g/L. At the higher salinity level <strong>of</strong> 12g/L, peroxidase exhibited only residuallevels <strong>of</strong> activities. <strong>The</strong>se results demonstrate the dynamic changes within the plantlets as theydevelop tolerance or resistance to salinity stress.42


O-23 EFFECT OF YAM AND DASHEEN EXTRACTS ON LIPIDMETABOLISM IN STREPTOZOTOCIN-INDUCED DIABETIC RATSPhillip B. Grindley, Felix O. Omoruyi, Helen N. Asemota <strong>and</strong> Errol Y. Morrison<strong>Department</strong> <strong>of</strong> Basic Medical Sciences (Biochemistry), MonaYams <strong>and</strong> dasheens are important sources <strong>of</strong> carbohydrates, some vitamins <strong>and</strong> minerals. <strong>The</strong>y alsocontain low levels <strong>of</strong> cyanoglucosides, essentially linamarin. A study was conducted onstreptozotocin-induced diabetic rats fed supplements containing extracts <strong>of</strong> yam <strong>and</strong> dasheen (groupC <strong>and</strong> D) for four weeks, during which lipid metabolism <strong>and</strong> transaminase activities in the liver wereassessed. Diabetic groups B, linamarin fed group E, groups C <strong>and</strong> D lost weight significantlydespite the non-significant difference in their food intake. Liver weights were significantly (p


O-25 HAIMEA ALTA AND HAIMEA OVUMSERPENTIS,WHAT’S THE DIFFERENCE?Deborah-Ann C. Rowe<strong>Department</strong> <strong>of</strong> Geography <strong>and</strong> Geology, Mona<strong>The</strong> oligopygoids are a group <strong>of</strong> irregular echinoidsunique to the Eocene <strong>of</strong> the Caribbean <strong>and</strong>adjacent regions. <strong>The</strong>se echinoids are the sister group to the clypeasteroids (=s<strong>and</strong> dollars), <strong>and</strong> arerepresented by a number <strong>of</strong> species in the genera Haimea Michelin <strong>and</strong> Oligopygus de Loriol. Bothgenera are locally common in the Eocene <strong>of</strong> Jamaica. <strong>The</strong> difficulty in distinguishing betweenspecies within the genus Haimea has long been documented. Two species are locally common withinthe Middle-Upper Eocene Swanswick Formation, but they cannot always easily be differentiated.Without taking measurements, the only feature that can be used to distinguish Haimea alta (Arnold<strong>and</strong> Clark) from Haimea ovumserpentis (Guppy) is the greater height <strong>of</strong> H. alta. This method issubjective <strong>and</strong> is reliable only in those cases where the test <strong>of</strong> H. alta is highly inflated, as that <strong>of</strong> H.ovumserpentis can also be inflated as well. H. alta may be so inflated as to resemble a fossilized golfball, whereas H. ovumserpentis is generally lower, more elongate <strong>and</strong> pentagonal in outline. Kier’s“Revision <strong>of</strong> the Oligopygoid Echinoids” (1967, Smithsonian Miscellaneous Contributions, vol.152, no. 2, 147 pp.) gives an outline <strong>of</strong> the morphological details which may be used to differentiatebetween the two species, including the shorter petal length <strong>and</strong> greater number <strong>of</strong> ambulacral platesbeyond the petals <strong>of</strong> H. alta. In an attempt to find other ways <strong>of</strong> telling the two species apart, 17measurements each have been made <strong>of</strong> 112 better preserved specimens <strong>of</strong> Haimea from an echinoidlocality in the Swanswick Formation at Beecher Town, in the parish <strong>of</strong> St. Ann, Jamaica. Based onthese measurements, bivariate statistical analyses were carried out in order to seek out the bestmeans <strong>of</strong> identifying each species. Using scatter diagrams <strong>and</strong> regression analysis, the parameters <strong>of</strong>test length, test height, <strong>and</strong> width <strong>and</strong> height <strong>of</strong> peristome, were found to be the most suitable to tellthe two species apartO-26 CRETACEOUS TO EOCENE EVOLUTIONOF CENTRAL JAMAICASimon Mitchell<strong>Department</strong> <strong>of</strong> Geography <strong>and</strong> Geology, Mona<strong>The</strong> Central Inlier exposes a suite <strong>of</strong> latest Cretaceous to Paleocene rocks that formed part <strong>of</strong> anextinct volcanic isl<strong>and</strong> arc system. Detailed mapping <strong>of</strong> the inlier has resulted in a new underst<strong>and</strong>ing<strong>of</strong> the geological history <strong>of</strong> Jamaica. <strong>The</strong> 1 st phase <strong>of</strong> active arc volcanism is represented by <strong>and</strong>esiticlavas, associated volcaniclastic sediments, <strong>and</strong> minor porphyritic basaltic dykes. This complex wasuplift <strong>and</strong> deeply eroded prior to the deposition <strong>of</strong> an inportant onlapping sedimentary successioncomprising the Slippery Rock <strong>and</strong> Guinea Corn formations. Sedimentary analysis <strong>of</strong> this successiondemonstrates the presence <strong>of</strong> a carbonate platform succession <strong>of</strong> restricted rudist-bearing carbonatefacies with associated shallow water clastics deposited closer to l<strong>and</strong>. Renewed volcanism in thePaleocene (with a probable hiatus at the Cretaceous-Tertiary boundary) saw extensive marine <strong>and</strong>terrestrial deposition <strong>of</strong> volcaniclastic s<strong>and</strong>stones <strong>and</strong> conglomerates which culminated in ignimbriteemplacement. This sedimentary succession was strongly deformed by tectonics in the early Eocenewith the formation <strong>of</strong> steep to vertical fold limbs associated with south-westerly verging folds <strong>and</strong>associated thrusting. After a period <strong>of</strong> renewed erosion, the deposition <strong>of</strong> the Yellow LimestoneGroup marked the first stage in the development <strong>of</strong> an extensive carbonate platform that persistedfrom Eocene to Miocene time.44


O-27 PHASE TRANSITIONS AND ORDERING PHENOMENA INAMPHIPHILICMONOLAYERS AT THE AIR/WATER INTERFACEWillem Mulder<strong>Department</strong> <strong>of</strong> <strong>Chemistry</strong>, Mona<strong>The</strong> surface activity <strong>of</strong> molecules such as lipids, proteins <strong>and</strong> fatty acids is associated with their dualcharacter; that is, one part is hydrophobic (“water-fearing”) <strong>and</strong> the other part is hydrophilic(“water-loving”). Such molecules are also called “amphiphiles”. <strong>The</strong> primary requirement for anamphiphile to be surface-active is that the balance between hydrophilic <strong>and</strong> hydrophobic parts besuch that the molecule has its lowest free energy when it is adsorbed at an interface between twoimmiscible bulk phases (water/oil or water/air). <strong>The</strong> amphiphile will then be present as amonomolecular film. Examples include the surfactant films in microemulsions, Langmuir filmsformed by spreading amphiphilic molecules on a water surface, the dense (Langmuir-Blodgett) films<strong>of</strong> chain molecules on solid supports, or the two lipid monolayers facing each other in biologicalmembranes.<strong>The</strong> most common experiment performed on Langmuir monolayers is the determination <strong>of</strong> surfacepressure vs. area isotherms using a film balance 1 . <strong>The</strong> surface pressure Π is defined as the differencebetween the surface tension γ0 <strong>of</strong> <strong>pure</strong> water <strong>and</strong> the surface tension γ<strong>of</strong> the surface covered by themonolayerΠ = γ0 − γ (1)A barrier can be slid across the water surface to change the area accessible to a fixed amount <strong>of</strong>surface-active material. <strong>The</strong> surface pressure can be measured by determining the force on a floatseparating the monolayer from a clean water surface. A typical Π-A isotherm for a <strong>pure</strong> fatty acid orphospholipid is shown in the figure, where two regions can be discerned in which different surfacephases coexist. At large areas the amphiphile behaves like a two-dimensional gas. Upon compressiona plateau is reached, marking the onset <strong>of</strong> 2D condensation <strong>of</strong> the gas into a so-called liquidexp<strong>and</strong>ed(LE) phase. At the end <strong>of</strong> the plateau the entire monolayer is in the LE phase. On furthercompression the lateral pressure again increases steeper until the start <strong>of</strong> a second transition regionwhere the LE phase condenses into a liquid-condensed (LC) phase which is associated withincreased chain ordering. At the end <strong>of</strong> the LE/LC coexistence region there is another steep increasein pressure until the collapse pressure is reached, which marks the transformation to more stablethree-dimensional (micellar) phases.<strong>The</strong> formation <strong>of</strong> LC from LE in the second coexistence region (sometimes called the “maintransition”) can be followed by fluorescence microscopy if one adds a small amount <strong>of</strong> surface activefluorescent dye which is less soluble in the LC compared to the LE phase. Alternatively, one can usethe more recently developed non-invasive technique known as Brewster angle microscopy. <strong>The</strong>micrographs obtained with both techniques reveal that the LC phase exists in the form <strong>of</strong> isolateddomains (sizes ~10µm) which, in the case <strong>of</strong> chiral amphiphiles, change their shape from circles viaellipses to stripes, spirals, triskelions, etc. <strong>The</strong>se have been established to represent equilibriumshapes <strong>and</strong> the result <strong>of</strong> a competition between lateral electrostatic repulsion between the polar (orcharged) head groups <strong>of</strong> surfactants <strong>and</strong> (anisotropic) line tension.45


A complete thermodynamic description has been given for the case <strong>of</strong> circular LC isl<strong>and</strong>s embeddedin a contiguous LE phase based upon the formulation <strong>of</strong> the Gibbs energy <strong>of</strong> the monolayer, definedas 2 G mono = µsN s − ΠA (2)where N s is the number <strong>of</strong> amphiphile molecules <strong>and</strong> µs their chemical potential. If contributions toG mono due to irregularities at the colloidal level are considered separately, a more detailed breakdowngives 2,3 (3)A m is the area occupied by the LE phase, N m, Πm <strong>and</strong> λ ∗ s,m are the number <strong>of</strong> amphiphiles, localspreading pressure <strong>and</strong> chemical potential for a uniform LE phase, respectively. <strong>The</strong> sum ∑ is takenover different categories <strong>of</strong> domains, defined according to the number <strong>of</strong> molecules j) ( they contain,n dj = number <strong>of</strong> isl<strong>and</strong>s in that category, R j = their radius, Λj = line tension, f edge el,j = electrostaticenergy <strong>of</strong> the fringe field <strong>of</strong> a domain due to polar head groups, λ ∗ s,j = molecular chemical potentialin a LC isl<strong>and</strong> <strong>of</strong> type j. <strong>The</strong> last term, G mix, is the free energy <strong>of</strong> mixing <strong>and</strong> contains the effects <strong>of</strong>electrostatic repulsion between domains, kinetic energy <strong>and</strong> polydispersity via a term –TS poly with T= absolute temperature <strong>and</strong> S poly = entropy <strong>of</strong> polydispersity.In equilibrium, G mono has its minimum value <strong>and</strong> the above expression can be shown to lead to threeequilibrium conditions: (i) mechanical equilibrium across every domain boundary, ii) ( uniformity <strong>of</strong>molecular chemical potential (µs) <strong>and</strong> (iii) the law <strong>of</strong> mass action: chemical potential per domain µd,j= jµs.Combination <strong>of</strong> these conditions yields the equilibrium distribution <strong>of</strong> domain sizes2 :(4)intwhere N d = total number <strong>of</strong> domains, δ= average distance between molecules in LC phase, f el =electrostatic work <strong>of</strong> inserting a domain <strong>of</strong> radius R into the film, k = Boltzmann’s constant. C is anormalisation constant.With G mix written as N dg mix, a m = A m/N m <strong>and</strong> n d = N d/A the expression for an arbitrary isothermpassing through the main transition region (thequation <strong>of</strong> state) follows from this treatment as 3(5)46


Here, we have assumed all isl<strong>and</strong>s to have equal sizes. This is based on numerical results obtainedwith eq 4 which imply a low degree <strong>of</strong> polydispersity (~ 10%) in most practical cases. From astability analysis <strong>of</strong> the solution to problem (i-iii) it has been concluded that even for this relativelysimple model system an instability may occur in the form <strong>of</strong> a negative lateral compressibility κ =−[A(∂Π/∂A) T] -1 . This strongly suggests that shape transitions (e.g. to more elongated domains) maybecome inevitable in order to restore monolayer stability.References1. Knobler, C.M. (1990). Adv. Chem.Phys. 77: 397.2. Mulder, W.H. (1997). J. Phys.Chem.B 101: 7744.3. Mulder, W.H. (1998) J. Phys.Chem.B 102: 5460.O-28ELECTROCATALYTIC DECHLORINATION OF CHLORORGANICCOMPOUNDS IN AQUEOUS MEDIAS. Kulikov<strong>Department</strong> <strong>of</strong> Biological <strong>and</strong> Chemical Sciences, Cave HillHalogenated organic compounds are being considered among the most widely spread pollutants inwater. Some <strong>of</strong> them are very dangerous even in small, on the border <strong>of</strong> analytical detectionconcentrations. <strong>The</strong>se compounds can be separated from water (liquid-liquid extraction, absorption,permeative technology .....) <strong>and</strong> then detoxified with known techniques.47


One <strong>of</strong> the promising methods <strong>of</strong> detoxification is electrochemical reductive dehalogenation inorganic media (MeCN, DMSO) which has been thoroughly investigated during last decade [1-3].However for practical purpose much more promising <strong>and</strong> much less studied is direct cathodicdehalogenation <strong>of</strong> those substances in aqueous media.<strong>The</strong> main problem in this case is overwhelming concentration <strong>of</strong> water molecules which discharge inthe first place sharply decreasing current efficiency <strong>and</strong> consequently almost canceling practicalapplication perspectives. However when instead <strong>of</strong> common electrodes hydrophobic carbon cloth orcarbon felt electrodes were tried it allowed to reach promising results, especially when electrode wasmodified with catalytically active metal [4]. In this work dehalogenation on carbon cloth <strong>and</strong> Znmodifiedcarbon cloth cathodes in water <strong>and</strong> water-alcohol mixture was studied. A flow-circulationTeflon electrolytic cell with membrane <strong>and</strong> electrode areas <strong>of</strong> about 40 cm 3 <strong>and</strong> a flow rate <strong>of</strong> 40 mlmin -1 was used. 200 - 400 ml <strong>of</strong> initial aqueous solution <strong>of</strong> 1,1,1-trichlorethane (20mg/L) with0.05M Na2SO4 as a supporting electrolyte circulated through the cathode compartment separatedfrom the anode compartment by a cation exchange membrane (Thomapor MC-3470). Cationexchange membrane was used to avoid oxidative destruction <strong>of</strong> the substrate on the anode <strong>and</strong>chlorinating <strong>of</strong> the products by anodically formed Cl2. Aqueous solution <strong>of</strong> Na2SO4 (0.1M)circulated through anode compartment. During the course <strong>of</strong> electrolysis the solution in cathodecompartment was sampled <strong>and</strong> analyzed by GC/MS <strong>and</strong> Cl - -selective electrode.Results <strong>of</strong> experiments have shown that 1,1,1-trichlorethane can be completely destroyed on thecathode giving as a products ethane <strong>and</strong> ethylene with 1,1-dichlorethane <strong>and</strong> chlorethane as anintermediates. Direct electrochemical reduction <strong>of</strong> trichlorethane on a carbon cloth cathode wascarried out with average current efficiency up to 30%. <strong>The</strong> modification <strong>of</strong> a carbon cloth cathode byZn permits indirect electrocatalytic dechlorination <strong>and</strong> can be carried out with much betterefficiency. Electrolysis time can be reduced approximately two times with average current efficiencyup to 75%.References1. H. Lund & M. Baizer (1991). Organic Electrochemistry. Marcel Dekker, New York.2. S. Kulikov, V. Plekhanov, A. Tsyganok, C. Schlimm & E. Heitz (1996). Electrochimica Acta41(4): 527-5313. V. Plekhanov, O. Sharkova, S. Kulikov, A. Tsyganok (1997). Russian Journal <strong>of</strong> Applied<strong>Chemistry</strong> 70(10): 1561-15634. A. Tsyganok & K. Otsuka (1998). Electrochimica Acta 43(18): 2589-2596.48


O-29 NUMERICAL SIMULATION OF GALACTIC MERGERSJ. Lodenquai <strong>and</strong> C. McNamarah<strong>Department</strong> <strong>of</strong> Physics, MonaRadio-loud active galactic nuclei (AGNs) are elliptical galaxies that emit unusually largeamounts<strong>of</strong> non-thermal electromagnetic radiation (EMR) over a wide spectrum. <strong>The</strong> merger hypothesispostulates that an AGN can form from the merger <strong>of</strong> two spiral galaxies containing supermassiveblack holes in their cores.During merger, some amount <strong>of</strong> matter eventually falls onto each black hole, just outside itsSchwartzschild radius, forming an accretion disk. Differential rotation within the accretion diskresults in the transformation <strong>of</strong> a significant fraction <strong>of</strong> the mass <strong>of</strong> the disk into the EMR observedfrom AGNs.In this paper, the merger <strong>of</strong> spiral galaxies is studied numerically. Each spiral galaxy is assumed tohave (i) a spheroidal halo <strong>of</strong> dark matter (ii) a spiral disk consisting <strong>of</strong> stars <strong>and</strong> gas <strong>and</strong> (iii) aspheroidal nucleus containing stars <strong>and</strong> gas with a supermassive black hole <strong>of</strong> mass about ten millionsolar masses in its core. Previous simulations, which used simplified models [Bekki <strong>and</strong> Noguchi(1994), Bekki (1995)], claim to be able to explain the onset <strong>of</strong> AGN-behaviour during the merger.However, the present work does not find that the energetics <strong>of</strong> AGNs can be accounted for duringmerger. However, sufficient infalling matter onto the black holes could occur considerably later aftermerger.Videos <strong>of</strong> typical merger simulations are presented.ReferencesBekki, K. & Noguchi, M. (1994). Gas fueling to the central 10pc in merging galaxies. Astron.Astrophys. 290: 7-18.Bekki, K. (1995). Gas dynamics <strong>of</strong> the central 1 kpc in galaxy mergers. Mon. Not. R. Astron. Soc.276: 9-19.O-30 LIMITED AREA NUMERICAL ATMOSPHERIC MODELINGFOR THE EASTERN CARIBBEANM. Mayers, C. Depradine 1 <strong>and</strong> L. L. Moseley<strong>Department</strong> <strong>of</strong> Computer Science, Mathematics <strong>and</strong> Physics, Cave Hill;1Caribbean Meteorological Institute, St. James, Barbados<strong>The</strong> objective <strong>of</strong> our research is to contribute to the development <strong>of</strong> a general limited areaatmospheric model appropriate to the Eastern Caribbean region. We will modify <strong>and</strong> extend existingmodels, where possible, to include phenomena ranging from weak tropical waves to hurricanes, <strong>and</strong>flooding due to rainfall, storm surge <strong>and</strong> wind generated waves. Current models are generally notwell tuned for our peculiar conditions.49


We aim at producing a model which can provide, if not real-time, n-hourly updated analyses throughthe use <strong>of</strong> a multiple processors <strong>and</strong> PVM. In this paper we describe the parallelization <strong>of</strong> the basicbarotropic model as a first step towards our goal.O-31A COMPARATIVE ANALYSIS OF SILICON-BASEDPHOTOVOLTAIC MODULESLeary Myers <strong>and</strong> Sheryl Williams<strong>Department</strong> <strong>of</strong> Physics, MonaThis study compares the photoconversion efficiency <strong>of</strong> commercially available silicon basedphotovoltaic modules. <strong>The</strong> modules were simultaneously irradiated with sunlight <strong>and</strong> the followingdata gathered: solar irradiance, panel <strong>and</strong> air temperature, relative humidity <strong>and</strong> air temperature. <strong>The</strong>data was collected, using a datalogger, <strong>and</strong> analysed.<strong>The</strong> information gathered to date suggest that the efficiency <strong>of</strong> the modules is 20-30% less than thatfor small -area laboratory cells, which is to be expected since the commercial modules are larger (1-3 m) <strong>and</strong> uniformity losses are implied. Silicon based photovoltaic cells are available in thefollowing types, amphorous, polycrystalline <strong>and</strong> single -crystal. It is known that single- crystallinesolar cells yield very good photoconversion efficiency but at a very high cost. Amphorous silicon (a-Si), with a lower photoconversion efficiency shows lots <strong>of</strong> promise because <strong>of</strong> its low productioncost.It is important that the different module efficiencies be well known as the initial capital outlaycontinues to be one <strong>of</strong> the greatest impediments to the wide scale use <strong>of</strong> photovoltaic systems. <strong>The</strong>cost <strong>of</strong> amphorous silicon modules continues to decrease as the thin-film manufacturing technologymatures.O-32 THE USE OF GENETIC ALGORITHMS IN THEOPTIMIZATION OF THE REPRESENTATION OF LOGICFUNCTIONSA. C. Perrotte <strong>and</strong> Ch. Posth<strong>of</strong>f<strong>Department</strong> <strong>of</strong> Mathematics <strong>and</strong> Computer Science, St. Augustine<strong>The</strong> optimization <strong>of</strong> the representation <strong>of</strong> logic functions byformulas remains a perpetual problem. In many ArtificialIntelligence applications, as well as in the logic design <strong>of</strong>circuits, the optimized representation <strong>of</strong> a logic function, orset <strong>of</strong> logic functions, is crucial for a successful solution <strong>of</strong>problems. [1, 2]This paper investigates the applicability <strong>of</strong> Genetic Algorithms for this kind <strong>of</strong> optimization problem.Genetic Algorithms are now, together with Fuzzy Logics <strong>and</strong> Neural Networks, part <strong>of</strong> the extension<strong>of</strong> Artificial Intelligence to Computational Intelligence.<strong>The</strong> implementation <strong>of</strong> the algorithm follows a strict object-oriented approach using UML <strong>and</strong>50


Java [3]<strong>The</strong> Optimization ProblemGiven a logic function, f: B n → B, with B = {0, 1}, find an optimal representation <strong>of</strong> f by:a) Exclusive-OR forms(XOR): f = C1 ⊕ C2 ⊕ … ⊕ Ck,b) Equivalence forms: f = D1 ∼ D2 ∼ … ∼ Dkc) Disjunctive forms: f = C1 ∨ C2 ∨ … ∨ Ckd) Conjunctive forms: f = D1 ∧ D2 ∧ … ∧ Dk“Optimal” can be defined as a minimum number <strong>of</strong> conjunctions, Ci, or disjunctions, Di, or as theminimum number <strong>of</strong> variables in the formula. For the XOR <strong>and</strong> equivalence forms, the optimizationcriteria will also be considered for different polarities: a formula has a given polarity if everyvariable appears only negated or only non-negated. For example, f = x1’ x2 x3 ⊕ x1’ x3 ⊕ x2, x1 isalways negated, x2, x3, <strong>and</strong> x4 are always non-negated.<strong>The</strong> challenge <strong>of</strong> these problems is the enormous complexity: for n variables, there are x 2functions,where x = 2 n but 2 y formulas <strong>of</strong> the given types, where y = 3 n . For practical applications, it is quitenormal to have values <strong>of</strong> n as high as 32 or even 64.A very import special case is the representation <strong>of</strong> logic functions by decision trees: <strong>The</strong> nodes <strong>of</strong>the trees are labelled by variables, the edges by values <strong>of</strong> variables (x=0 or x=1); the complexity <strong>of</strong>the trees depends on the order <strong>of</strong> the variables, hence, it is equal to n!, for n variables.Genetic Algorithms“Genetic Algorithms (GAs) are … stochastic algorithms whose search methods model some naturalphenomena: genetic inheritance <strong>and</strong> Darwinian strife for survival.” [4] <strong>The</strong>y start with a population<strong>of</strong> solution c<strong>and</strong>idates (the initial population). Genetic operators, mutation <strong>and</strong> crossover, are<strong>applied</strong> to individuals or pairs <strong>of</strong> individuals in the population to generate new members. A fitnessfunction is used to determine which individuals are solutions or the fittest at each stage <strong>of</strong> thealgorithm.Using a ternary coding <strong>and</strong> a complete enumeration <strong>of</strong> all conjunctions, every formula can berepresented (in principle) by a bit vector with the length 3 n . <strong>The</strong> Table gives examples <strong>of</strong> the ternarycoding scheme used to convert r<strong>and</strong>om numbers generated to the conjunctions they represent. <strong>The</strong>conjunctions that comprise a particular formula are coded into the bit vector <strong>of</strong> length n 3.Table:Correspondence between the numbers generated <strong>and</strong> the conjunctions theyrepresent, for 3 variables.R<strong>and</strong>om Numbers x1 x2 x3 Corresponding Conjunction5 0 1 - x1’x27 0 - 1 x1’x317 1 - - x120 - 0 - x2’Mutations change one or more bits r<strong>and</strong>omly, while crossover involves splitting two bit vectors intoparts <strong>and</strong> then recombining parts <strong>of</strong> different vectors. <strong>The</strong> new vectors (formulas) will be includedinto the population according to their fitness values. <strong>The</strong> number <strong>of</strong> function values that are correct51


in comparison to the function f gives these fitness values.<strong>The</strong> AlgorithmStep 1:Step 2:Step 3:Check for readily deducible forms or constant functions, if found the stop.Create the initial population.Determine the fitness <strong>of</strong> each individual.Step 4: Save potential solutions/individuals that fit the original function 100%.Step 5:Step 6:Select individuals for crossover; perform crossover.Determine the fitness <strong>of</strong> new individuals.Step 7: Save new individuals that fit the original function 100%.Step 8:Step 9: Repeat step 6.Step 10: Repeat step 7.Step 11:Step 12:Select individuals for mutation & for the selected individuals, select bits formutation; perform mutation.Reconstruct new generation based on fitness values.Repeat steps 5 to 11 for a predetermined number <strong>of</strong> generations.Step 13: Choose the minimal/optimal solution from all solutions that fit 100%.Conclusion<strong>The</strong> results that have been achieved so far show the successful implementation <strong>of</strong> this algorithm. <strong>The</strong>influence <strong>of</strong> parameters (like population size, mutation probability <strong>and</strong> crossover probability) is nowunder investigation <strong>and</strong> will be shown by diagrams. <strong>The</strong> application <strong>of</strong> object-oriented methodsallows a successful, fast <strong>and</strong> reliable implementation <strong>of</strong> the algorithm.References[1] McKanzie, L., Almaini, A. E. A., Miller, J. F., Thomson, P. (1993). Optimization <strong>of</strong> Reed-Muller Logic Functions. International Journal <strong>of</strong> Electronics 3(75).[2] Miller, J. F., Luchian, H., Bradbeer, P. V. G., Barclay, P. J. (1994). Using a GeneticAlgorithm for Optimizing Fixed Polarity Reed-Muller Expansions <strong>of</strong> BooleanFunctions. International Journal <strong>of</strong> Electronics 4(76).[3] Larman, C. (1998). Applying UML <strong>and</strong> Patterns. In An Introduction to Object OrientedAnalysis <strong>and</strong> Design. Prentice Hall.[4] Michalewicz, Z. (1996). Genetic Algorithms + Data Structures= Evolution Programs.Third, Revised <strong>and</strong> Extended Edition. Springer, 1996.52


O-34 EXPLORING THE 3X+1 PROBLEMCharles Cadogan<strong>Department</strong> <strong>of</strong> Computer Science, Mathematics <strong>and</strong> Physics, Cave Hill<strong>The</strong> function f is defined on the positive integers N as follows:<strong>The</strong> 3x+1 Problem, also known as the Collatz Problem, the Syracuse Problem, Ulam’s Problem,Kakutani’s Problem <strong>and</strong> Hasse’s Algorithm, asks if repeated iterations <strong>of</strong> f always reaches theintegerThis paper explores a method <strong>of</strong> approach to the solution <strong>of</strong> the problem by converting the originalconjecture to a 4n+1 problem, nÎN, through specific partitions <strong>of</strong> N generated by mean <strong>of</strong> aparticular subset <strong>of</strong> positive integers called the golden sequence <strong>and</strong> its effect on integers <strong>of</strong> the form1+4n.O-35 A SCRIPT LANGUAGE FOR RE-USE OF OBJECTORIENTED CLASSESColin A. Depradine <strong>and</strong> Brian G. Patrick<strong>Department</strong> <strong>of</strong> Computer Science, Mathematics <strong>and</strong> Physics, Cave Hill<strong>The</strong> concept <strong>of</strong> s<strong>of</strong>tware reuse was inspired by the electronic <strong>and</strong> mechanical industries whereintensive reuse <strong>of</strong> basic components has shortened product development time, reduced manufacturingcosts, increased worker productivity <strong>and</strong> improved product reliability. With a rapidly exp<strong>and</strong>ingstore <strong>of</strong> well-tested <strong>and</strong> readily available s<strong>of</strong>tware components <strong>and</strong> with the movement toward objectorientedparadigms <strong>of</strong> design <strong>and</strong> implementation, the reuse <strong>of</strong> s<strong>of</strong>tware has gained more <strong>and</strong> moreprominence (Meyer & Nerson, 1997).<strong>The</strong>refore, the functionality <strong>of</strong> many integrated development environments <strong>and</strong> CASE tools has beenextended to support s<strong>of</strong>tware reuse (Steigerwald et al, 1991; Terry et al, 1994). One such example,the reuse system for object-oriented classes (or ROOC), consists <strong>of</strong> three major components(Depradine & Patrick, in press).<strong>The</strong> repository or data store contains not only the reusable code but also the documents that describeit. <strong>The</strong>se documents, created either manually or automatically, are shaped into a structured but openformat. <strong>The</strong>refore, the repository is extensible <strong>and</strong> flexible. Furthermore, it permits the user todetermine the level <strong>of</strong> information complexity <strong>and</strong> to customize tools <strong>of</strong> manipulation.53


<strong>The</strong> scripting language described herein takes advantage <strong>of</strong> the st<strong>and</strong>ardized format <strong>of</strong> the repositorydocuments. <strong>The</strong> user is provided with an interface that facilitates the construction <strong>and</strong> execution <strong>of</strong>queries based on the required specifications <strong>of</strong> the desired components.<strong>The</strong> query is submitted to a search engine where a complete search <strong>of</strong> the repository is performed<strong>and</strong> results are returned. <strong>The</strong> administration tools provide important utilities that ensure theconsistency <strong>and</strong> correctness <strong>of</strong> the repository. <strong>The</strong> quality <strong>of</strong> data is monitored by checking thatminimal requirements are met <strong>and</strong> error-free. For example, a s<strong>of</strong>tware component is not added to therepository unless a suitable description is included. <strong>The</strong>se tools also include those utilities thatcollect, add <strong>and</strong> delete reuse information from the repository.In this paper, a scripting language for the reuse <strong>of</strong> object-oriented classes (S-ROOC) assumes thedocument format <strong>of</strong> the ROOC system (Depradine et al, 1997) <strong>and</strong> <strong>of</strong>fers the simplicity <strong>of</strong>commonly-used scripting languages such as Visual Basic. Hence, S-ROOC supports the overallobjective <strong>of</strong> the ROOC system, that is, to make code reuse an integral <strong>and</strong> unobtrusive part <strong>of</strong> thes<strong>of</strong>tware development cycle.<strong>The</strong> S-ROOC language is supported by a search engine. <strong>The</strong> search engine performs the scanning<strong>and</strong> accumulation <strong>of</strong> results based on the specifications given in the S-ROOC script. Thus, thequerying process involves three steps: To create a query in S-ROOC that details as much as possiblethe specifications <strong>of</strong> a required class, to submit the query to the search engine <strong>and</strong> to view thoseclasses returned by the search engine that best match the required specifications (Gibbs et al, 1990;Gougen et al, 1996).An S-ROOC query itself consists <strong>of</strong> two parts: A pattern <strong>and</strong> execution requirements. <strong>The</strong> patterndefines what type <strong>of</strong> class is required <strong>and</strong> is matched against the class data in the repository. <strong>The</strong>execution requirements on the other h<strong>and</strong> define how the query is to be executed <strong>and</strong> what form theresults are to be collected, processed <strong>and</strong> presented. <strong>The</strong> S-ROOC language is object-basedconsisting <strong>of</strong> a set <strong>of</strong> pre-defined objects <strong>and</strong> operators (Booch, 1986). To use the pre-definedobjects, however, no instance <strong>of</strong> an object need be created. As well, the operators replace the usualcontrol structures such as IF, WHILE <strong>and</strong> FOR. <strong>The</strong> list <strong>of</strong> the S-ROOC objects is given below:SessionSystemSpecReportCompareClassListCurrentClassStringDebugProvides facilities to modify the search parameters <strong>and</strong> to perform searches.Provides various types <strong>of</strong> input/output.Provides information about the specification that is currently active.Provides reporting functions.Provides comparison functions.Provides querying functions for the resultant list <strong>of</strong> classes from the last search.Provides access to the properties <strong>of</strong> a class in the resultant list <strong>of</strong> classes from thelast search.Provides string h<strong>and</strong>ling functions.Provides very simple <strong>and</strong> basic debuggingfunctions.Consider, now, the following simple example <strong>and</strong> note that a S-ROOC script may include more thanone specification.54


:define:end:spec Query1{@use "MEMORY_ALLOCATOR";};:spec Query2{@keyword "LEX?*";};:run#Session.SetRegExp( "exact" )#Session.MatchSpec( "Query1" )In this script, two query specifications are defined in the structures {Query1} <strong>and</strong> {Query2}. If aprogrammer formulates an S-ROOC query to return the list <strong>of</strong> classes that use the class{MEMORY\_ALLOCATOR} then the S-ROOC object {#Session} sets up the search engine for anexact GREP-like match using {SetRegExp} <strong>and</strong> submits to the search engine the specificationsfound in the structure {Query1} using S<strong>of</strong>tware reuse, object-oriented programming, querylanguages.ReferencesBooch G. (1986). Object-oriented development. Transactions on S<strong>of</strong>tware Engineering 12(2): 211-221.Depradine C.A., Patrick B.G. <strong>and</strong> Posth<strong>of</strong>f C. (1997). A document format for the reuse <strong>of</strong> objectorientedclasses. Proceedings <strong>of</strong> the Third Conference <strong>of</strong> the Faculty <strong>of</strong> Pure <strong>and</strong> AppliedSciences, University <strong>of</strong> the West Indies, pp 26-27, Jan. 1997Depradine, C.A. & Patrick, B.G., A s<strong>of</strong>tware tool for the reuse <strong>of</strong> object-oriented classes.Caribbean Journal <strong>of</strong> Mathematical <strong>and</strong> Computer Sciences (to appear).Gibbs S., Tsichritzis D., Casais E., Nierstrasz O. & Pintado X. (1990). Class management fors<strong>of</strong>tware communities. Communications <strong>of</strong> the ACM 33(9): 90-103.Goguen J., Nguyen D., Meseguer J., Luqi, Zhang D. & Berzins V. (1996). S<strong>of</strong>tware componentsearch. Journal <strong>of</strong> Systems Integration 6(1): 93-134.Meyer, B. & Nerson, J. (1997). Object-Oriented Applications. Prentice Hall, 1997Steigerwald R., Luqi & McDowell J. (1991). CASE tool for reusable component storage <strong>and</strong>retrieval prototyping. Information <strong>and</strong> S<strong>of</strong>tware Technology 33(9): 698-706.Terry A., Hayes-Roth F., Coleman N., Devito M., Papanagopoulos G. <strong>and</strong> Hayes-Roth B. (1994).Overview <strong>of</strong> Teknowledges domain specific s<strong>of</strong>tware architecture program. ACM SIGSOFTS<strong>of</strong>tware Engineering Notes 19(4) 68-76, Oct. 1994.55


O-36 CRYPTOGRAPHY AND THE INFORMATION SOCIETYKarl H. Robinson<strong>Department</strong> <strong>of</strong> Mathematics <strong>and</strong> Computer Science, Mona“<strong>The</strong> Information Society” <strong>and</strong> “<strong>The</strong> Information Age” are terms <strong>of</strong>ten used to express the fact thatmodern societies expend a lot <strong>of</strong> effort on the processing <strong>of</strong> digital information <strong>and</strong>, that they areincreasingly dependent <strong>of</strong> the reliable storage, processing <strong>and</strong> transmission <strong>of</strong> such information.In recent years, cryptography – the science <strong>of</strong> secret writing – has been evolving as an essential tool forhelping to secure digital information <strong>and</strong> to authenticate electronic transactions.In earlier years, cryptography was cloaked in much secrecy. However, modern cryptographicalgorithms are publicly discussed, because an objective is to have systems whose security depend onthe inherent strength <strong>of</strong> the system, rather than on one’s lack <strong>of</strong> familiarity with the techniques beingused. (Someone who is determined to break a system will make the effort to familiarizehimself/herself with the techniques being used.) Modern cryptographic systems also have amathematical base because <strong>of</strong> the need to be able to prove results about the level <strong>of</strong> security theyprovide.United States laws classify encryption s<strong>of</strong>tware as munitions <strong>and</strong>, therefore, such s<strong>of</strong>tware is subjectto export restrictions. <strong>The</strong> restriction is based on the size <strong>of</strong> the key used to encrypt the information.Currently, encryption s<strong>of</strong>tware using keys <strong>of</strong> size 128 bits are being made widely available within theUnited States, but such s<strong>of</strong>tware may not be exported. More vulnerable versions <strong>of</strong> the s<strong>of</strong>tware maybe exported.In this talk we discuss the increasing importance <strong>of</strong> cryptography, <strong>and</strong> we compare the level <strong>of</strong>computational effort needed to break the RSA cryptographic scheme for keys <strong>of</strong> sizes 64 <strong>and</strong> 128bits.O-37ONTOGENY RECAPITULATES PHYLOGENY:TRUE FOR MATHEMATICS EDUCATION?Raymond McEachin<strong>Department</strong> <strong>of</strong> Mathematics <strong>and</strong> Computer Science, Mona<strong>The</strong> phrase, "ontogeny recapitulates phylogeny'' is a familiar onein the life <strong>sciences</strong>. However, as a biological principle it isalso generally discredited. We argue, nevertheless, that thisphrase is a useful metaphor for teachers <strong>of</strong> mathematics.This talk is speculative in nature, <strong>and</strong> in particular it is not aresearch report. Rather, it is a discussion that may lead to aresearch agenda in mathematics education that is particularlyrelevant to the Caribbean.<strong>The</strong>re are striking parallels between the historical development<strong>of</strong> certain mathematical ideas on one h<strong>and</strong>, <strong>and</strong> young students'mental development on the other h<strong>and</strong>. For example, in the earlystages <strong>of</strong> any child's life negative numbers will beincomprehensible, if not frightening.56


Eventually, however, almost every schoolchild can at leastmanipulate negative numbers reasonably well. Ultimately, mosttake them for granted. Historically, one also sees that negativenumbers were initially unimagined. For various reasons, mostlyutilitarian, however, negatives gained acceptance as things thatcould be manipulated both consistently <strong>and</strong> usefully. Ultimately,<strong>of</strong> course, we now take them for granted.<strong>The</strong> most significant parallels are, in the author's view, relatedto the development <strong>of</strong> the number system itself. At the heart <strong>of</strong>the issue is what we'll call the "sigma-zero" dilemma. Looselyspeaking, there is an apparent paradox in the number system thatis extremely important historically. This arises from the factthat presumably "zero-dimensional" points can be assembled intoone-dimensional line segments. This raises the perplexingquestion <strong>of</strong> whether points have dimension. We look briefly atarguments on both sides, giving plausible reasons why pointscannot have dimension but yet must have dimension. We alsobriefly describe the modern underst<strong>and</strong>ing <strong>and</strong> resolution <strong>of</strong> thisapparent paradox.Once we resolve this crucially important dilemma, <strong>and</strong> considerother episodes in the history <strong>of</strong> mathematics, how can we becomebetter mathematics teachers? Clearly there are two questions toconsider:(i) What topics should we be teaching, <strong>and</strong> when (<strong>and</strong> in whatorder)?(ii) Given any topic we teach, how should we go about teachingit?We will give some ideas that may prove interesting <strong>and</strong> effectivehere in the Caribbean <strong>and</strong> elsewhere.57


ABSTRACTS OF POSTER PRESENTATIONS______________________________________________________________________________P-1 SYNCHRONISED SPAWNING BY BRITTLE-STARS AT THELAST QUARTER OF THE SEPTEMBER MOONJeremy Woodley, Judith Mendes <strong>and</strong> Robert MurrayCentre for Marine Sciences, MonaIn recent years, many observers have dived on Caribbean coral reefs in late summer, about the lastquarter <strong>of</strong> the Moon, in order to witness the synchronised spawning <strong>of</strong> stony corals. Some havereported that other invertebrates were apparently spawning at the same time, including some brittlestars,notably Ophiocoma wendtii (Van Veghel, 1993)We made observations at two <strong>of</strong> the Port Royal Cays, Lime Cay (5m depth, September 1995),Drunkenman's Cay (5m depth, September 1996) <strong>and</strong> at Dairy Bull, about 2km east <strong>of</strong> DiscoveryBay (9m depth, August, September <strong>and</strong> October 1998). At each site was a gently sloping terracesupporting a community dominated by massive corals; mostly Montastraea annularis <strong>and</strong> M.faveolata, but also M. cavernosa, Siderastrea siderea, Colpophyllia natans, Diploria strigosa, <strong>and</strong>D. labyrinthiformis, with patches <strong>of</strong> Acropora cervicornis, <strong>and</strong> many lesser corals. All dives tookplace within the period two to five hours after sunset, on the fifth, sixth, seventh or eighth eveningafter the Full Moon.Every year, active brittle-stars were seen; notably Ophioderma rubicundum, which is known to benocturnally active, <strong>and</strong> Ophiomyxa flaccida, which is generally cryptic in behaviour. <strong>The</strong>y climbedto the tops <strong>of</strong> coral heads <strong>and</strong>, if they found other individuals there, would pile together.Spawning behaviour in one or other species was observed in 1995, <strong>and</strong> definitely in O. flaccida in1998, seven <strong>and</strong> eight days after the Full Moon. St<strong>and</strong>ing alone on top <strong>of</strong> the coral heads, they wereseen to raise the disc above the substratum, sometimes holding that attitude for many minutes, <strong>and</strong>wisps <strong>of</strong> material, presumably spermatozoa, issued from the bursal slits. Apparent females wereseen to adopt an extreme "pentapod" position (as described for Amphiura filiformis; Woodley, 1975)<strong>and</strong> emitted clouds <strong>of</strong> eggs which drifted away in the water.In 1998, no brittle-stars were seen on the following evening, ninth after the Full Moon. In October, afew O. rubicundum, but no O. flaccida were observed. Clearly, we had observed a tightlysynchronised spawning event.ReferencesVan Veghel, M.L.J. (1993). Multiple species spawning on Curaçao. Bulletin <strong>of</strong> Marine Science52:1017-1021.Woodley, J.D. (1975). <strong>The</strong> behaviour <strong>of</strong> some amphiurid brittle-stars. Journal <strong>of</strong> ExperimentalMarine Biology <strong>and</strong> Ecology 18: 29-46.58


P-2 CIRCULATION PATTERNS IN DISCOVERY BAYChung, R. <strong>and</strong> Webber, D.F.<strong>Department</strong> <strong>of</strong> Life Sciences, MonaDiscovery Bay can be described as a highly dynamic, variable <strong>and</strong> complex coastal embaymentwhere circulation patterns may be driven by tidal action, freshwater inflow from subterraneanpercolation or wind. <strong>The</strong> relative importance <strong>of</strong> these forces was examined using r<strong>and</strong>om, known <strong>and</strong>24 hour sampling <strong>of</strong> current speeds <strong>and</strong> direction at 18 stations. Physical parameters (primarilytemperature <strong>and</strong> salinity) were also recorded.Results indicated that Discovery Bay is spatially stratified, both horizontally <strong>and</strong> vertically.Horizontally three zones were recognized, each responding differently to meteorological <strong>and</strong> tidalforces. <strong>The</strong> zones were (a) the mouth <strong>of</strong> the bay which could have been an extension <strong>of</strong> the shippingchannel, (b) the small western bay <strong>and</strong> ( c) the larger eastern bay. Each zone had its owncharacteristic feature(s) <strong>and</strong> dominant current producing forces. Vertically, Discovery Bay wasstratified into: a surface layer (maximum 5 m deep), a sub surface layer (5 - 16 m deep) <strong>and</strong> a deeplayer (16 - 40 m deep). Stratification was related to seasonality which otherwise played a minorrole in influencing the circulation <strong>of</strong> the waters at Discovery Bay. Meteorological events were theprimary driving mechanism in the surface layer in all three zones.Surface current velocities were faster under high wind conditions (max. av. speed <strong>of</strong> 0.09 <strong>and</strong> 0.11ms -1 for the large eastern <strong>and</strong> small western Bay respectively) than under no/low wind conditions.<strong>The</strong> highest current velocity under no/low wind conditions were less than 0.01 ms-1 for both the small<strong>and</strong> larger bays. Tidal activities had minimal impact on the surface circulation in the entire Baywhile temperature <strong>and</strong> salinity driven currents were only significant in the small western bay. <strong>The</strong>surface layers <strong>of</strong> the other two zones were thermally homogenous. As expected, the sub - surfacelayer was not affected by meteorological events but tidal currents were responsible for the flow <strong>and</strong>circulatory pattern in this layer. This was only applicable to the large eastern bay <strong>and</strong> the bayentrance. <strong>The</strong> small western bay was too shallow to facilitate the formation <strong>of</strong> a sub-surface layer.<strong>The</strong> sub-surface layer was further stratified. Tidal forces only controlled the circulation <strong>of</strong> the firstten meters (10 m) <strong>of</strong> the sub-surface layer. Below this depth (av. 16 m) some other mechanism wasresponsible for driving deeper sub-surface waters.P-3 THE STATUS OF REEF COMMUNITIES INDISCOVERY BAY BACK REEFWayne H. A. WhittakerCenter for Marine Sciences, MonaCoral reefs at Discovery Bay are significant among the sites studied in the preliminary development<strong>of</strong> coral reef studies around the world. However the hard bottom communities actually withinDiscovery Bay, <strong>and</strong> probably within bays generally have been neglected by researchers. <strong>The</strong> reefs <strong>of</strong>Discovery Bay have undergone many natural <strong>and</strong> anthropogenic stresses with alarming results some<strong>of</strong> which are well documented for the fore reef only.59


<strong>The</strong> varied range <strong>of</strong> effects to the sessile marine macro benthos while difficult to isolate <strong>and</strong> quantifyprecisely, allow for general characterization <strong>of</strong> the area. At Discovery Bay I surveyed reefs to 30m<strong>and</strong> evaluated benthic community composition by point intercept transects at 5m,10m, <strong>and</strong> 15m.<strong>The</strong>refore I present qualitative <strong>and</strong> quantitative data on the status <strong>of</strong> reefs in the bay for futuremonitoring. Sampling was conducted over an 18 month period April 16th, 1996 to February 8, 1998.Three data sets were collected as follows:1. PROFILE TRANSECT DATA SET: Twenty-five pr<strong>of</strong>ile transects were run throughout the bay.Each pr<strong>of</strong>ile started at the allowed depth (


<strong>The</strong> anthropogenic effects on the bay seem to over ride the biological factors such as competition<strong>and</strong> herbivory which govern distribution <strong>and</strong> abundance <strong>of</strong> say corals <strong>and</strong> possibly macroalgae. Thusfor the observed status <strong>of</strong> the Discovery Bay reefs to be meaningful in an ecologically scientificcontext, requires an appreciation <strong>of</strong> the disturbance history, both natural <strong>and</strong> anthropogenic.ReferencesBonem, R.M.. & Stanley G.D. (1982). Ecologic zonation <strong>of</strong> the Red Buoy patch reef. Tom GoreauLibrary #1823.Liddell, W.D. & Olhorst S.L. (1987). Patterns <strong>of</strong> reef community structure, north Jamaica. Bull.Mar. Sci. 40: 311-329.P-4 SEAGRASS POPULATIONS OF THE SOUTHEAST COAST OFJAMAICA: EFFECTS OF RANGING LEVELS OFEUTROPHICATIONGreen, S.O. 1 <strong>and</strong> Webber, D.F. 2Centre for Marine Sciences <strong>and</strong> 2 <strong>Department</strong> <strong>of</strong> Life Sciences, MonaSix seagrass meadows located within <strong>and</strong> near the eutrophic Kingston Harbour were investigatedfrom October 1994 to June 1995. Shoot productivity, leaf turnover rate, leaf area, total biomass<strong>and</strong> shoot density <strong>of</strong> the seagrass were measured during the period. In addition, the water quality atall the sites was monitored, using phytoplankton biomass as the primary index <strong>of</strong> water quality.<strong>The</strong>se data were supplemented with data collected on the water temperature, salinity, dissolvedoxygen content, nutrient content (nitrates + nitrates <strong>and</strong> phosphates), <strong>and</strong> light extinction coefficientat these sites.Although there were no significant differences in nutrient data at the six sites, the phytoplanktondata confirmed previous observations <strong>of</strong> a range <strong>of</strong> water qualities from the eutrophic KingstonHarbour, to mesotrophic Hellshire Bays <strong>and</strong> oligotrophic Port Royal Cays. <strong>The</strong> seagrass at thesesites exhibited an increased leaf turnover rate <strong>and</strong> leaf productivity with increasing eutrophicationstress, while total biomass <strong>and</strong> shoot density decreased with increased eutrophication.When compared with previous studies, the seagrass turnover rate <strong>and</strong> leaf productivity in <strong>and</strong> nearKingston Harbour were much higher in response to increased eutrophication.61


P-5 THE USE OF INFORMATION SYSTEMS TECHNOLOGY TODEVELOP A REGIONAL MARINE SCIENCE DATABASEDulcie M. LintonCentre for Marine Sciences, MonaCaribbean Coastal Marine Productivity (CARICOMP) is a regional scientific program to studyl<strong>and</strong>-sea interaction processes. Based on a cooperative network <strong>of</strong> marine laboratories, parks, <strong>and</strong>reserves, CARICOMP focuses on underst<strong>and</strong>ing productivity, structure <strong>and</strong> function <strong>of</strong> the threemain coastal ecosystems in the Caribbean: mangroves, seagrasses <strong>and</strong> coral reefs. As the primaryproductivity <strong>of</strong> mangrove, seagrass <strong>and</strong> coral reef ecosystems is the basis <strong>of</strong> present <strong>and</strong> potential futureyields <strong>of</strong> shallow water marine resources in the region, a primary goal <strong>of</strong> CARICOMP is to determine thefactors that regulate the variability <strong>of</strong> production by these systems. <strong>The</strong> program documents <strong>and</strong> monitorsthe distribution, structure, <strong>and</strong> function <strong>of</strong> the major coastal ecosystems <strong>and</strong> the extent to which theseattributes are influenced by contact with l<strong>and</strong>. Data are collected using 14 different protocols as outlined inthe CARICOMP Methods Manual (1994).Of 29 sites in 22 countries in the Caribbean, 20 are collecting data. A Data Management Centre (DMC),located at the Centre for Marine Sciences, performs data storage <strong>and</strong> distribution functions <strong>and</strong> is thecommunication node in this regional network. Data entry is decentralized utilizing Quattro Pro spreadsheettemplates, which provide the network with the required flexibility for localized data entry. Data sent to theDMC are currently stored in QPRO files.While the spreadsheet system worked well as a data entry tool, there were obvious disadvantages forit as a data storage system. File management became cumbersome as more sites became active.Maintaining relationships between countries, sites, stations etc. became difficult <strong>and</strong> involvedcreation <strong>of</strong> additional tables that stored related data. Data duplication, <strong>and</strong> the associated update <strong>and</strong>deletion errors <strong>and</strong> inconsistencies increased. Data analyses were time-consuming. A solution tothese major obstacles was necessary.A scientific approach to solving the problem was undertaken. Firstly, there was a Problem Definitionphase. This required knowledge <strong>of</strong> the old system, identifying the inherent problems. Possible solutionswere examined <strong>and</strong> the most cost-effective solution identified. Development <strong>of</strong> a database utilizing existingDatabase Management System (DBMS) technology was identified as the best option.A Database Management System (DBMS) allows a computer to control data resources. Itmanipulates the database through the use <strong>of</strong> special s<strong>of</strong>tware. <strong>The</strong> two main components <strong>of</strong> theDBMS are: the Data Definition Language (DDL) that defines the way that data are stored <strong>and</strong>provides natural <strong>and</strong> logical linkages between data, <strong>and</strong> the Data Manipulation Language (DML)which allows data to be manipulated, sorted, queried <strong>and</strong> retrieved. Micros<strong>of</strong>t Access was chosenafter careful considerations. Its Jet Database Engine is powerful <strong>and</strong> its integration <strong>of</strong> Visual BasicAccess Interface tools makes User Interface development relatively easy <strong>and</strong> smooth, reducing therisk <strong>of</strong> development incompatibilities. In addition it is relatively inexpensive as it comes as part <strong>of</strong>the st<strong>and</strong>ard Micros<strong>of</strong>t Office suite, is SQL-89 compatible <strong>and</strong> therefore <strong>of</strong>fers the full functions <strong>of</strong>SQL for data retrieval. It is compatible with other Micros<strong>of</strong>t s<strong>of</strong>tware such as Micros<strong>of</strong>t Excel.<strong>The</strong> first phase <strong>of</strong> project development involved the logical mapping <strong>of</strong> the objects in the system. EntityRelationship (E-R) diagramming technique was used. Much attention was given to this design phase as theE-R diagrams formed the foundation for the database development. A correct E-R model ensured correctproblem solving.Data tables in the DBMS built on the E-R diagrams. Data fields <strong>and</strong> properties were developed <strong>and</strong>62


elationships established between the data tables. From these forms for data entry <strong>and</strong> display weredeveloped. User interfaces, which allow users <strong>of</strong> the system to access data without knowledge <strong>of</strong> theunderlying database structure, were developed using Visual Basic Access (VBA). Finally, queriesthat manipulate <strong>and</strong> extract data according to specified criteria were constructed using St<strong>and</strong>ardQuery Language (SQL). Data transfers, from spreadsheet files to the DBMS, were effected throughthe use <strong>of</strong> Open Database Connectivity (ODBC) Drivers. <strong>The</strong>se allowed data in spreadsheet files tobe reorganized to match data in the tables in Micros<strong>of</strong>t Access, effecting transfer without thenecessity for re-entry <strong>of</strong> data, reducing the risk <strong>of</strong> data entry errors <strong>and</strong> the time required for datatransfer to the DBMS.<strong>The</strong> development <strong>and</strong> testing <strong>of</strong> queries with the results <strong>of</strong> the st<strong>and</strong>ard spreadsheet templates weredone next. Reports were generated based on these queries. Finally, the linking <strong>of</strong> the discretedatabase objects: tables, forms, queries <strong>and</strong> reports into an integrated whole, which provides logicalguidance to users in extracting relevant information from the database was done.This database represents the use <strong>of</strong> Information Systems to provide management <strong>of</strong> an importantregional scientific dataset. It has allowed the program to fulfil its scientific m<strong>and</strong>ate, providing dataon an accurate <strong>and</strong> timely basis, while providing the flexibility required to respond to increasedregional data collection needs, <strong>and</strong> achieving these within the constraints <strong>of</strong> limited personnel <strong>and</strong>financial resources.ReferenceCARICOMP (1994). CARICOMP Methods Manual - Level 1, 66 pp.P-6 THE PHYTOPLANKTON COMMUNITY AND WATERQUALITY OF A HIGHLY EUTROPHIC ESTUARINE BAY:HUNT'S BAY, KINGSTON HARBOUR, JAMAICARanston, E. <strong>and</strong> Webber, D. F.<strong>Department</strong> <strong>of</strong> Life Sciences, Mona<strong>The</strong> phytoplankton community composition, abundance <strong>and</strong> size fractionated biomass (Chlorophylla ) along with various physical <strong>and</strong> chemical parameters were assessed on a monthly basis at 9stations with 2 sampling depths, hroughout the Bay. Sampling was conducted between December1993 <strong>and</strong> February 1995. This study was conducted primarily to characterize the phytoplanktoncommunity <strong>of</strong> the Bay <strong>and</strong> investigate the forcing functions which determine the spatial <strong>and</strong> temporaldistribution <strong>of</strong> the community. A further objective was to determine the present status <strong>of</strong> the waterquality <strong>of</strong> the Bay in comparison to results obtained from previously conducted studies.Results indicated significant deterioration in the water quality <strong>of</strong> Hunt's Bay since the last studyconducted 20 years ago by Grahame (1977). <strong>The</strong> increased eutrophic state <strong>of</strong> the Bay was indicatedby the consistently higher phytoplankton biomass, highest average concentration <strong>of</strong> 18.69 mg -3mchlorophyll a, compared to the lower value <strong>of</strong> 6.21 mg m -3 obtained by Grahame (1977).63


<strong>The</strong> present maximum phytoplankton abundance within the Bay (2.9x108 cells l -1 ) was also higherthan the previous maximum <strong>of</strong> 5x10 7 cells l -1 determined in 1977. Higher nutrient concentrationswere also observed, with maximum labile Nitrate <strong>and</strong> Phosphate concentrations determined at45.30microMol. <strong>and</strong> 3.96 microMol., respectively.Stratification <strong>of</strong> the highly eutrophic water body <strong>of</strong> Hunt's Bay was confirmed with the watercolumn being stratified into a fresh or brackish water surface layer due to freshwater input fromrivers <strong>and</strong> gullies which empty into the Bay, <strong>and</strong> a saline deeper layer. Surface waters were <strong>of</strong>tensupersaturated, in contrast to deeper waters which were regularly subject to oxygen deficiency.<strong>The</strong> stratification <strong>of</strong> the Bay was an important factor determining the distribution <strong>and</strong> composition <strong>of</strong>the phytoplankton community which was found to vary both spatially <strong>and</strong> temporally. Physicalfactors such as seasonality (rainfall) <strong>and</strong> nutrient loading also played a significant role indetermining the phytoplankton community composition, distribution <strong>and</strong> size.Biological factors such as zooplankton grazing appeared to have some influence on the size <strong>of</strong> thephytoplankton community.ReferenceGrahame, S. (1977). <strong>The</strong> ecology <strong>of</strong> plankton in Kingston Harbour Jamaica. <strong>The</strong> Phytoplankton.Research Report 4(2) <strong>Department</strong> <strong>of</strong> Zoology p. 104.P-7 MICROALGAL COMMUNITY OF A COASTAL LAGOON:CHANGES IN WATER QUALITY AND THE EFFECT ONSEDIMENT NUTRIENT FLUXESClarke, T. M. 1 <strong>and</strong> Webber, D. F. 21Centre for Marine Sciences <strong>and</strong> 2 <strong>Department</strong> <strong>of</strong> Life Sciences, MonaBetween July 1992 <strong>and</strong> June 1996, the water quality in the Great Salt Pond, Southeast Jamaica wasmonitored using biological, physical <strong>and</strong> chemical parameters. Microalgal (phytoplankton) biomass<strong>and</strong> community structure were found to be the most suitableindicators <strong>of</strong> the water quality. Effluentfrom the Greater Portmore Sewage Treatment system, adjacent to the Great Salt Pond was found tosignificantly affect water quality within the pond. Effluent release before completion <strong>of</strong> theconstruction phase <strong>of</strong> the treatment system resulted in microalgal (phytoplankton) blooms withmaximum biomass values <strong>of</strong> 39.79 mg m -3 <strong>and</strong> maximum abundances <strong>of</strong> 46,142,652 cells L -1 .Increased flow from the treatment plant further exacerbated the eutrophication, while the fullyoperational treatment system resulted in a 25% improvement in water quality (reduction inphytoplankton biomass). Increased flow rates from the fully operational treatment system furtherimproved the water quality by dilution.<strong>The</strong> microalgal biomass <strong>and</strong> community structure associated with the sediments in the pond wereinvestigated after improvements in the water column were observed. As a result <strong>of</strong> prolongedeutrophication <strong>of</strong> the pond the sediments were now a significant source <strong>of</strong> inorganic nutrients to thewater column.64


Results <strong>of</strong> microcosm experiments showed that over 90% <strong>of</strong> the inorganic nitrogen <strong>and</strong> 58% <strong>of</strong> theorthophosphate available in the water column were derived from the sediments with the rate <strong>of</strong>absorption <strong>of</strong> the microalgae <strong>and</strong> current flow, determining the diffusion rates from sediment towater.Further work with microcosms indicated that it is possible to predict the rate <strong>of</strong> recovery toacceptable water quality conditions in the Great Salt Pond <strong>and</strong> this provides a tool for recoverypredictions in similar enclosed, coastal embayments.P-8 ZOOPLANKTON DISTRIBUTION IN A PRISTINE TROPICALEMBAYMENT, DISCOVERY BAYEdwards, E. A. <strong>and</strong> Webber, M. K.<strong>Department</strong> <strong>of</strong> Life Sciences, Mona<strong>The</strong>re are several investigations using zooplankton as indicators <strong>of</strong> water quality in Jamaican <strong>and</strong>Caribbean Bays. However, few are conducted before there are some obvious effects <strong>of</strong>pollution/eutrophication. <strong>The</strong>refore most <strong>of</strong> our “baseline” data for bays represent populationsalready affected by pollution. This study was conducted with the aim <strong>of</strong> assessing zooplanktonabundance, species composition <strong>and</strong> community structure in Discovery Bay, on the north coast <strong>of</strong>Jamaica. It was believed that the bay was experiencing unknown levels <strong>and</strong> types <strong>of</strong> stress through arange <strong>of</strong> activities.<strong>The</strong> system was monitored over a 12 month period (October 1995 to September 1996) using a range<strong>of</strong> indices (temperature, salinity, dissolved oxygen, REDOX, nutrients, size fractionatedphytoplankton biomass <strong>and</strong> zooplankton). <strong>The</strong> zooplankton (sampled using vertical hauls) <strong>and</strong>water quality data were collected contemporaneously. 107 zooplankton species were identified, 48<strong>of</strong> which were copepods. <strong>The</strong> species were represented by a mix <strong>of</strong> neritic <strong>and</strong> oceanic species.Mean abundances for the area ranged from 1,077 m -3 for an area just outside <strong>of</strong> the bay (station 1)to 3,794 m -3 at a station very close to the south shore (station 6). Stations closest to shore hadgreater abundances than centrally located bay stations <strong>and</strong> stations close to oceanic influence.Acartia tonsa was dominant in shoreline areas <strong>of</strong> the bay, Calanopia americana at deeper stationswith significant oceanic influence, <strong>and</strong> Oithona plumifera <strong>and</strong> Temora stylifera were dominant atstations closest to oceanic influences. <strong>The</strong>se species were thus considered as indicators <strong>of</strong> thesedifferent areas within the bay.Calanoids <strong>and</strong> cyclopoids were the dominant taxa at most stations while Larvae <strong>and</strong> Larvaceanswere also prevalent. With the nutrients <strong>and</strong> phytoplankton values being well within the ranges forpristine systems, we can conclude that this zooplankton assemblage represents that <strong>of</strong> a pristine bay<strong>and</strong> thus provides useful <strong>and</strong> real baseline data for a tropical embayment.65


P-9 INDIVIDUAL ZOOPLANKTON SPECIES SHOW SPATIALDISTRIBUTION TRENDS FAR BETTER THANTOTAL ABUNDANCESDunbar, F.N. <strong>and</strong> Webber, M.K.<strong>Department</strong> <strong>of</strong> Life Sciences, Mona<strong>The</strong> purpose <strong>of</strong> this study was to investigate the zooplankton communities <strong>of</strong> the highly eutrophicKingston Harbour in an attempt to provide a new baseline <strong>of</strong> conditions, the previous study beingconducted in the 1970’s. Routine sampling was conducted monthly at twenty-four stations in theHarbour over a 18 month period. <strong>The</strong> abundance, species composition <strong>and</strong> community structure <strong>of</strong>the zooplankton populations were examined along with selected physical <strong>and</strong> chemical parameters.<strong>The</strong>se indices were evaluated for appropriateness in defining the zooplankton communities <strong>and</strong>characterising water masses.A total <strong>of</strong> seventy-three taxa were identified <strong>of</strong> which the copepods were most important numerically(thirty-eight species). Mean numbers for the area were high ranging from 3,662 animals -3 m in Hunts Bayto 80,464 animals m -3 in the Inner Harbour (station 8). This maximum value was more than three timesthe maximum figure reported by Grahame (1976) (25 248 animals m -3 ).Results <strong>of</strong> the community similarity index (PSC) suggested that there are four zones in KingstonHarbour: Upper Basin (stations 1 to 6), Inner Harbour (stations 7 to 12), Middle Harbour (stations13, 14, 15 <strong>and</strong> 17) <strong>and</strong> Outer Harbour (stations 16 <strong>and</strong> 18 to 23). Hunts Bay (station 24) was notincluded in any <strong>of</strong> these zones.Values for most <strong>of</strong> the parameters examined were higher in the Inner Harbour identifying this zoneas the most productive in the Harbour. However, spatial distribution between zones was moreclearly demonstrated by individual species rather than total abundances. Temora turbinata wasfound to be very important in the Upper Basin, Lucifer faxoni <strong>and</strong> Penilia avirostris in the InnerHarbour, Paracalanus crassirostris in the Outer Harbour <strong>and</strong> Acartia tonsa in Hunt's Bay. In fact,these species may be used as indicator <strong>of</strong> the respective zones. <strong>The</strong>re was some seasonal variation inthe zooplankton communities but like spatial variation, it was more significantly displayed byindividual species rather than by the total abundances.ReferenceGrahame, J. (1976). Zooplankton <strong>of</strong> a tropical harbour: numbers, species composition <strong>and</strong> responseto physical factors <strong>of</strong> zooplankton in Kingston Harbour, Jamaica. J. Exp. Mar. Biol. Ecol. 24:219-237.66


P-10 A PRELIMINARY ASSESSMENT OF THE FISHABLERESOURCES OF PORTLAND BIGHT, ST. CATHERINEKarl Aiken, Br<strong>and</strong>on Hay* & Steven Montemuro*<strong>Department</strong> <strong>of</strong> Life Sciences, Mona;*South Coast Conservation Foundation, KingstonDaytime sampling <strong>of</strong> mangrove, seagrass (Thalassia, Syringodium <strong>and</strong> Halodule) <strong>and</strong> s<strong>and</strong>y habitatsfrom east to west with approximately one trip per month over a 13 month period (April 1997 to April,1998) in Portl<strong>and</strong> Bight, St. Catherine <strong>and</strong> Clarendon parishes, using two types <strong>of</strong> seine nets, showeddistinctive mangrove, seagrass <strong>and</strong> s<strong>and</strong>y shore fish <strong>and</strong> crustacean faunas. Due to the schedule, nostatistically valid repeat sampling was carried out except for three sites. Nevertheless, the present studyyielded 89 finfish species from 41 families, including 3 cartilaginous fish families (rays <strong>and</strong> sharks group),8 crustacean species from 6 families, <strong>and</strong> two molluscan species from 2 families. Adult, sub-adult <strong>and</strong>postlarval fishes were captured with both types <strong>of</strong> seines nets, but the smaller meshed (3 mm diameter)seine net caught more postlarval <strong>and</strong> subadult fish than the larger mesh (18 mm) net.A total <strong>of</strong> 18.159 kg <strong>of</strong> fishable species were taken consisting <strong>of</strong> 2,389 individuals. Portl<strong>and</strong> Bight <strong>and</strong> themanagement area west <strong>of</strong> Portl<strong>and</strong> Point) possess important juvenile <strong>and</strong> adult fishable resources. Fishableresources occupy the shallow nearshore zones as well as deeper areas fished commercially. <strong>The</strong> very smalltotal weight l<strong>and</strong>ed suggests that the area supports mainly small young specimens.<strong>The</strong> adults <strong>and</strong> juveniles <strong>of</strong> two commercially important marine shrimp species Penaeus ( schmitti <strong>and</strong> P.notialis, the southern white <strong>and</strong> southern pink shrimps) were caught exclusively in the Carlisle Bay <strong>and</strong>Macarry Bay area <strong>and</strong> dominated the crustacean catches there. Despite limited sampling, it was apparentthat some areas functioned as critical nursery areas for many species <strong>and</strong> that the entire area as a whole,appears to function as a giant nursery for many useful species. <strong>The</strong>se young fishery resources areinextricably linked with those resources l<strong>and</strong>ed at Old Harbour Bay beach, the nations's largest fishingbeach site through movement from the Portl<strong>and</strong> Bight area into deeper reef areas <strong>and</strong> through indirectlysupporting the commercially fished reef species by providing food for their prey. <strong>The</strong> economic value <strong>of</strong>the fishable resources is such that development loss <strong>of</strong> these nursery areas will directly affect thelivelihoods <strong>of</strong> several thous<strong>and</strong> fishers, dependent vendors <strong>and</strong> their respective families in St. Catherine,Clarendon <strong>and</strong> elsewhere that fish from the study area is consumed. <strong>The</strong> ecological importance <strong>of</strong> thesefishable resources is such that the demise <strong>of</strong> these resources would mean eventual irreparable harm toother aquatic resources (through e.g. food chain linkages). Existing threats such wetl<strong>and</strong> degradation <strong>and</strong>related pollution there, will cause negative changes in the earnings <strong>of</strong> fishers <strong>and</strong> others, as well as havingnegative impact on the biodiversity <strong>of</strong> the marine habitat.Some 81% <strong>of</strong> finfish came from mangrove-seagrass habitats, <strong>and</strong> 19% from s<strong>and</strong>y substrate sites west <strong>of</strong>Portl<strong>and</strong> Point. Most (68%) <strong>of</strong> the 89 finfish species were represented entirely by juveniles. <strong>The</strong> top fivefinfish species numerically were Anchoa lyolepis (dusky anchovy), Eucinostomus gula (silver jenny),Sardinella anchovia (Spanish sardine), Diapterus rhombeus (Caipita mojarra), Haemulon sciurus(Bluestriped grunt) <strong>and</strong> Callinectes spp. (swimming crabs), the most common crustacean. <strong>The</strong> top 10species in abundance accounted for 69.8% by number <strong>and</strong> 39.7% by weight <strong>of</strong> the total catch. Three <strong>of</strong>the top 10 species are important as baitfish <strong>and</strong> therefore as forage fish for valuable commercialcarnivores such as snapper <strong>and</strong> groupers. <strong>The</strong> 10 most abundant finfish families comprised 87.1% bynumber <strong>of</strong> all finfish from all families. Four <strong>of</strong> the 8 crustacean species are commercially important <strong>and</strong>included three types <strong>of</strong> marine shrimp (Penaeus spp.) <strong>and</strong> the spiny lobster (Panulirus argus).67


<strong>The</strong> most abundant crustacean captured in the study was the swimming crab species Callinectes ( spp.).This marine crab is edible as adults. <strong>The</strong> two molluscan species were <strong>of</strong> commercial importance (conch<strong>and</strong> flat or false oyster). Densities <strong>of</strong> small juveniles <strong>and</strong> sub-adult fishes were significantly higher inmangrove-seagrass than over open s<strong>and</strong>y ground. Fishable resources were relatively more abundant <strong>and</strong>diverse in eastern Portl<strong>and</strong> Bight mangrove-seagrass than western habitats. <strong>The</strong> lowest diversity was west<strong>of</strong> Portl<strong>and</strong> Point.<strong>The</strong> Eastern Portl<strong>and</strong> Bight "lagoon-mangrove-seagrass complex" (Manatee Bay west through GalleonHarbour, including Goat Isl<strong>and</strong>s) should be put aside as a Protected Area - Critical Nursery Area "A" <strong>and</strong>protected from all forms <strong>of</strong> fishing. Similarly, Outer West Harbour (Holmes Bay, Miller's & LittleMiller's Bay <strong>and</strong> the associated Portl<strong>and</strong> Cays) should be put aside as Protected Area - Critical NurseryArea "B". Also, ALL the Portl<strong>and</strong> Bight Cays should be protected as Special Areas "C" for fisheries,coastal protection, recreational <strong>and</strong> biodiversity purposes. Importantly, the complex <strong>of</strong> wetl<strong>and</strong>s <strong>and</strong>numerous lagoons stretching west from Jackson's Bay, across the Rio Minho delta, to Beauchamps,Clarendon, is almost completely ecologically unknown <strong>and</strong> MUST be put aside as Special Protected Area,protected <strong>and</strong> studied. Waterborne pollution from sugar cane production near the Rio Minho river delta,is affecting the fishable resources adjoining that area. Effort should be made to incorporate sugar canepollution-abatement measures into any development plan for the study area.P-11 THE REINTRODUCTION TO THE WILD AND SUBSEQUENTMONITORING OF THREE ISOLATED MANATEES (TRICHECHUSMANATUS) FROM THE ALLIGATOR HOLE RIVER,CLARENDON, JAMAICA.Raymond Pryce <strong>and</strong> Eric Garraway<strong>Department</strong> <strong>of</strong> Life Sciences, MonaManatees are fluvial mammals which feed on plants growing in the euphotic zone, they thereforefrequent shallow near shore waters <strong>and</strong> rivers as they forage for food daily, (Ronald K. et al 1978).For over eighteen years three adult female manatees have been living in the enclosed river systemknown as the Alligator Hole River in Clarendon, Jamaica. Having been placed there as a rescueeffort by the then Natural Resources Conservation Division, NRCD, since renamed the NaturalResources Conservation Authority, NRCA. Each was caught accidently, at seperate times, in thenets <strong>of</strong> fishermen <strong>of</strong>f Farquhar's Beach in Clarendon. In fact, there were initially four manatees, thefourth however, also a female, believed to have been pregnant at the time she was placed in the river,died some weeks after she was observed to have been 'thinner' <strong>and</strong> the carcass <strong>of</strong> a foetus was foundfloating in the river, (Hurst, 1987).In the time which has elapsed the three remaining manatees have almost completely consumed thevegetation found in the river which comprised mainly Ceratophyllum <strong>and</strong> their diets have had to besupplemented by the daily addition <strong>of</strong> 'river weed' at a feeding bay constructed at the NRCA's CanoeValley facility. A programme which has proven quite expensive to maintain <strong>and</strong> which, ifdiscontinued, will be detrimental to the manatees. Further to this, <strong>and</strong> more importantly, theirseparation from an already small <strong>and</strong> diminished manatee population in Jamaican waters has meantthe denial <strong>of</strong> a potential thirty reproductive events for the three manatees, as it is approximated thatthree healthy 'cows' could possibly have carried some eight to ten full term pregnancies each oversuch an extensive period, (Marsh, 1995)68


Realizing this, a decision has been taken to prepare the manatees for reintroduction to the sea. Thishas included the construction <strong>of</strong> a 'guillotine' style trap/cage at the feeding bay. In which themanatees are now being fed. <strong>The</strong> reintroduction <strong>and</strong> sinking <strong>of</strong> sea grasses (mainly Thalassia) totheir diets. <strong>The</strong> sea grass is being sank to reacquaint the manatees with cropping food from thebottom. <strong>The</strong> taking <strong>of</strong> morphometric <strong>and</strong> genetic data <strong>and</strong> the utilization <strong>of</strong> radio telemetry as themode <strong>of</strong> tracking <strong>and</strong> monitoring, ( Bonde & Powell, 1997). This last is to be done for a two yearperiod, primarily to see if the manatees rejoin the wild population <strong>and</strong> are accepted into a matingherd <strong>and</strong> eventually breed. <strong>The</strong>re is also a secondary goal, which is to use this opportunity to testthe response <strong>of</strong> the general public to laws <strong>and</strong> policies which declare species as 'protected' as well asto promote further public education on the importance <strong>of</strong> preserving the country's natural history.AcknowledgementsThis project is being conducted in conjunction with the NRCA, <strong>The</strong> Save <strong>The</strong> Manatee Club,(U.S.A.), <strong>and</strong> <strong>The</strong> Sirenia Project, U.S. Fish <strong>and</strong> Wildlife Service.ReferencesBonde, R. K. <strong>and</strong> Powell J.A. (1997). Consultation report on the feasibility <strong>of</strong> reintroduction tothe wild <strong>of</strong> captive manatees from alligator hole river, Jamaica.Hurst, L.A. (1987). <strong>The</strong> status <strong>and</strong> distribution <strong>of</strong> the west indian manatee (trichechus manatus)in Jamaica with an evaluation <strong>of</strong> the aquatic vegetation <strong>of</strong> alligator hole river. UnpublishedM.S.thesis. University <strong>of</strong> Florida.Marsh, H. (1995). <strong>The</strong> life history, pattern <strong>of</strong> breeding <strong>and</strong> population <strong>of</strong> the dugong. <strong>Department</strong><strong>of</strong> Tropical Environment Studies <strong>and</strong> Geography. James Cook University, Townsville, Australia.P-12 LONGITUDINAL ZONATION OF BENTHICMACROINVERTEBRATES IN THE BUFF BAY RIVER, JAMAICAMeshagae Hunte <strong>and</strong> Eric Hyslop<strong>Department</strong> <strong>of</strong> Life Sciences, MonaMost lotic (flowing water) systems rise in the mountains <strong>and</strong> flow to the sea; thus there is a gradientin the environmental conditions that will affect the biota <strong>of</strong> any stream. Longitudinal zonation is theprocess <strong>of</strong> subdividing rivers based on these changes in the physical, chemical <strong>and</strong> biological nature<strong>of</strong> a river along its course. Thus the biological community observed at any point is a response to adelicate balance <strong>of</strong> the prevailing environmental conditions at that point.Many classification systems have been developed for rivers but one <strong>of</strong> the earliest is that <strong>of</strong> rhithron<strong>and</strong> potamon, which divides the river based on its environmental characteristics rather than itsbiological nature (Illies <strong>and</strong> Botosaneanu 1963). Rhithronic characteristics include turbulent flow,high dissolved oxygen (DO), substrate chiefly <strong>of</strong> stones <strong>and</strong> boulders, very little primary production<strong>and</strong> mean monthly temperature


Potamic characteristics include sluggish flow, lower DO, finer substrates (s<strong>and</strong>s, silt, mud) <strong>and</strong>higher levels <strong>of</strong> primary production. One <strong>of</strong> the major aims <strong>of</strong> this project is to investigate thelongitudinal zonation <strong>of</strong> the benthic macroinvertebrates in the Buff Bay River, Jamaica, WI. Similarstudies have been conducted elsewhere in the Caribbean (Harrison <strong>and</strong> Rankin 1976). In Jamaica,information on the Buff Bay River fauna is given in Boon, Jupp <strong>and</strong> Lee (1986) as part <strong>of</strong> a widerstudy <strong>of</strong> Blue Mountain rivers. However, this is a more detailed study as it relates to longitudinalzonation within a single river, <strong>and</strong> involves more sites on the Buff Bay River including higheraltitude sites that are missing from the earlier study.Six sites were chosen along the Buff Bay River, ranging from altitudes <strong>of</strong> approximately 1,000m tosea level. <strong>The</strong>re is a wide range <strong>of</strong> external influences on this river <strong>and</strong> the dominant factors changefrom site to site. <strong>The</strong>se factors include periodic drying up, occasional s<strong>and</strong> mining, c<strong>of</strong>fee farming<strong>and</strong> heavy domestic usage. Various microhabitats have been identified within sites <strong>and</strong> sampledindividually. <strong>The</strong>se include Riffle-sediment, Riffle-under stones, Pool-sediment, Pool under stones<strong>and</strong> Under Vegetation. Qualitative sampling was done over a period <strong>of</strong> 18 months. <strong>The</strong> methodemployed was "timed kick sampling", where the substrate allowed for this <strong>and</strong> inspection <strong>and</strong>removal <strong>of</strong> invertebrates from the lower surface <strong>of</strong> stones where kick sampling was not possible.Quantitative samples were taken 4 times over the period <strong>of</strong> the project <strong>and</strong> the method used in eachcase was "timed Surber sampling." <strong>The</strong> invertebrates collected from the different microhabitats atthe various sites are then identified with the aid <strong>of</strong> microscopes <strong>and</strong> enumerated, where applicable.Analysis <strong>of</strong> the data reveals many interesting trends. It is found that many families not only occurmore frequently at certain sites, but have obvious microhabitat preferences. <strong>The</strong> damselfly family,Coenagrionidae, for example is found at sites 3, 4 <strong>and</strong> 5 only <strong>and</strong> almost exclusively undervegetation. It is also found that the number <strong>of</strong> species in each class generally declines moving fromthe top to the lower reaches <strong>of</strong> the river. Variability in some physico-chemical factors appears tocorrelate with macroinvertebrate diversity. <strong>The</strong> relative importance <strong>of</strong> each class at each site wasalso assessed <strong>and</strong> Trichoptera (Caddis flies) <strong>and</strong> Coleoptera (Beetles) are found to be dominant at allsites, while some groups (like the Diptera) are absent from the lowest site. <strong>The</strong> aspect <strong>of</strong> seasonalitywas also investigated.<strong>The</strong> relevance <strong>of</strong> this project is that it provides a base line study <strong>of</strong> community structure with respectto the physico-chemical conditions, ultimately allowing lay persons to both make predictions oncommunity structure, based on the physico-chemical factors, as well as to assess water quality basedon community structure.References1. Boon, P. J., Jupp, B. P. & Lee, D.G. (1986). <strong>The</strong> benthic ecology <strong>of</strong> rivers in the BlueMountains (Ja.) prior to construction <strong>of</strong> a water regulation scheme. Arch. Hydrobiol./Suppl.74(3): 315-3552. Harrison, A.D. & Rankin, J.J. (1976). Hydrobiological Studies <strong>of</strong> Eastern Lesser AntilleanIsl<strong>and</strong>s II St. Vincent: Freshwater fauna, its distribution, tropical river zonation <strong>and</strong>biogeography. Arch. Hydrobiol./Suppl. 50(2/3): 175-311.3. Illies, J. & Botosaneanu, L. (1963). Problèms et mèthods de la classification et de lazonation ecologique des eaus covant considerèes surtout du point du vue faunistique.Mitt. Int. Ver. <strong>The</strong>or. Ang. Limnol. 12: 1-57.70


P-13 THE USE OF PERIPHYTON AND BENTHICMACROINVERTEBRATES IN THE BIOMONITORING OF THENORTH ELIM RIVER, ST. ELIZABETH, JAMAICAKimberly John, Josette La Hee, Eric Hyslop <strong>and</strong> Dale Webber<strong>Department</strong> <strong>of</strong> Life Sciences, MonaFreshwater biomonitoring is the use <strong>of</strong> the biota inhabiting water, to detect <strong>and</strong> evaluate ecologicallysignificant changes within the aquatic environment. Macroinvertebrates <strong>and</strong> algae, have proven to bereliable indicator organisms <strong>and</strong> are widely used in contemporary studies, (Whitton et al., 1991;Abel, 1996). Periphytic algal species, such as some diatoms, green <strong>and</strong> blue-greens, are <strong>of</strong> great usein monitoring lotic systems. <strong>The</strong>se algae are intimately associated with their aquatic surroundings<strong>and</strong> being sessile in nature, are continually subjected to environmental conditions in the habitat.<strong>The</strong>refore any physico-chemical changes which occur, may be manifest in such features as speciesdensity, composition, biomass or morphology.<strong>The</strong> great diversity, limited mobility <strong>and</strong> high abundance <strong>of</strong> benthic macroinvertebrates have madethem invaluable in ecological surveys, as well as the protracted monitoring <strong>of</strong> lotic habitats (APHA,1995). <strong>The</strong> term ‘benthic macroinvertebrates’, refers to the larger organisms inhabiting the bottomsubstrates <strong>of</strong> an aquatic environment, such as annelids, molluscs, crustaceans, flatworms <strong>and</strong>insects. <strong>The</strong> structure <strong>of</strong> benthic macroinvertebrate communities is governed by the prevailingphysical <strong>and</strong> chemical conditions which, because <strong>of</strong> fluctuations, may not be detected by watersample analysis alone.<strong>The</strong> North Elim River, in St. Elizabeth, Jamaica, is a low altitude (


Preliminary results have indicated significant increases in the composition, diversity <strong>and</strong> abundance<strong>of</strong> the macroinvertebrate community with increasing distance from the point source <strong>of</strong> pollution.<strong>The</strong>se have been related primarily to faunal inputs from tributaries <strong>of</strong> the North Elim such as theSouth Elim <strong>and</strong> the Smith/Blake Rivers. <strong>The</strong> capacity <strong>of</strong> the North Elim to support a richermacroinvertebrate community, also increased downstream as is evidenced by the rising dissolvedoxygen levels, increases in the discharge <strong>and</strong> habitat complexity <strong>of</strong> the river, <strong>and</strong> falling currentvelocity. <strong>The</strong> community is dominated at the first two sites by taxa tolerant <strong>of</strong> low oxygenconditions; Tubifex <strong>and</strong> Eristalis. Pulmonate snails (with lungs), <strong>and</strong> various insect groups wereadded after the South Elim junction; <strong>and</strong> Prosobranch snails (with gills) were added after theconfluence with the Smith/Blake Rivers. Crustacea <strong>and</strong> bivalves were found only after the BlackRiver junction. This gradual aggradation <strong>of</strong> the macroinvertebrate community took place over adistance <strong>of</strong> seven kilometres.With regards to the algal aspect <strong>of</strong> the investigation, results so far obtained have been indicative <strong>of</strong>differences in the composition <strong>of</strong> the communities at the three sites. Insufficient time has elapsedhowever, to allow a significant temporal analysis <strong>of</strong> the environmental conditions <strong>and</strong> associatedchanges in the periphyton. <strong>The</strong> North Elim periphyton community is dominated by fungal species,whereas the South Elim has a predominant community <strong>of</strong> an, as yet, unidentified, unicellular, greenalga. <strong>The</strong> Black River community exhibits initial colonisation by the same unicellular, green algalspecies, but the climax community is inclusive <strong>of</strong> a number <strong>of</strong> green <strong>and</strong> blue-green filamentousforms.ReferencesAbel, P.D. (1996). Water Pollution Biology. Taylor & Francis, London; pp 286.APHA (1995). St<strong>and</strong>ard methods for the Examination <strong>of</strong> Waters <strong>and</strong> WastewatersAmerican Public Health Association, Water Environment Federation. American Water WorksAssociation, Washington; pp 1058 - 1059Whitton et al (1991). <strong>The</strong> use <strong>of</strong> algae for monitoring rivers. Institute <strong>of</strong> Botany, InnsbruckUniversity, Austria; 193 pp.P- 14 EVALUATION OF THE BENTHIC MACROINVERTEBRATECOMPOSITION OF THE RIO COBRE AND SELECTEDTRIBUTARIES, WITH SPECIAL EMPHASISON THE FAMILY THIARIDAEAndrea Fender <strong>and</strong> Eric Hyslop<strong>Department</strong> <strong>of</strong> Life Sciences, MonaAn ecological study is being carried out on the Rio Cobre <strong>and</strong> selected tributaries to ascertain the influence<strong>of</strong> various physicochemical parameters such as bed rock composition <strong>and</strong> water quality on:i. Density <strong>and</strong> distribution <strong>of</strong> the benthic macroinvertebrate fauna.ii. <strong>The</strong> growth <strong>of</strong> the snails <strong>of</strong> the FamilyThiaridae.iii. Species diversity <strong>of</strong> the benthic macroinvertebrate community.72


In (i) <strong>and</strong> (ii) above, emphasis is being placed upon 2 freshwater viviparous prosobranch snailsThiaragranifera (Lamarck) <strong>and</strong> Melanoides tuberculata (Muller).In 1940, M. tuberculata was introduced into Southern U.S.A <strong>and</strong> later spread to Puerto Rico, Grenada,St. Lucia <strong>and</strong> Venezuela. Pointier in 1983 recorded T. granifera <strong>and</strong> M. tuberculata in Guadeloupe,Dominica <strong>and</strong> Martinique. <strong>The</strong> exact time <strong>of</strong> introduction into Jamaica is not known, however members<strong>of</strong> the Family Thiaridae occur extensively in our freshwater systems.<strong>The</strong> Rio Cobre (Figure), a principal river, stretches a length <strong>of</strong> 50.9 km <strong>and</strong> flows south <strong>and</strong> west in theparish <strong>of</strong> St. Catherine. It is supplied by a number <strong>of</strong> tributaries most <strong>of</strong> which join it at Bog Walk.Figure: <strong>The</strong> Rio Cobre systemFour sites were selected on the Rio Cobre according to their bedrock characteristics. <strong>The</strong>se can besubdivided into two groups:a. Those with predominantly limestone bedrock - Broadleaf Spring <strong>and</strong> Deeside;b. Those with bedrock <strong>of</strong> predominantly volcanic origins in the outlier <strong>of</strong> the Blue Mountains- Rio Pedro <strong>and</strong> Rio Magno.Four samples <strong>of</strong> snails were collected, on sampling occasions, at each site using a quadrat <strong>of</strong> 0.25 m 2 . Alllive snails are h<strong>and</strong>picked from the substrate within each quadrat.T. granifera was found to be a characteristic inhabitant <strong>of</strong> the selected sites. Populations <strong>of</strong> 285-481organism/m 2 on average <strong>of</strong> T. granifera have been found at Rio Pedro <strong>and</strong> Rio Magno, with a greaterdensity being recorded <strong>of</strong> Rio Pedro. Sites on the limestone bedrock recorded lower densities than sites onvolcanic bedrock.73


M. tuberculata was found only at two sites, Broadleaf Spring <strong>and</strong> Deeside <strong>and</strong> in extremely lowquantities. Occurring at a ratio <strong>of</strong> 19:1 with T. granifera. <strong>The</strong> latter was consistently the more dominantspecies. <strong>The</strong>re was a reduction in snail numbers during the months <strong>of</strong> August <strong>and</strong> September whencompared to the previous months <strong>of</strong> May-July, 1998.On a monthly basis the average snail length occurred within the range <strong>of</strong> 10-12.4 mm with the exception<strong>of</strong> Broadleaf Spring where the snails were smaller having an average length <strong>of</strong> 8.5 mm. <strong>The</strong> growth rate<strong>of</strong> both species is yet to be determined as research is still being conducted.Extensive faunal surveys determined the species diversity <strong>of</strong> the sites. United Estates was recorded asbeing the most diverse, not only in the number <strong>of</strong> families occurring but also the number <strong>of</strong> speciesoccurring within each family.ReferencesPointier, J.P. (1983). La lutte biologique contre le Mollusques hotes intermediaires de Bilharzioses a l'aidede Mollusques competiteurs. Symbiose 15(2): 85-91.Starmuhlner, V.F.1988. Ergebnisse der Osterreichisch- Franzosischen Hydrobiologischen Mission 1979nach Guadeloupe, Dominica <strong>and</strong> Martinique (Kleine Antillen). Tiel II: Beiltrage Zur Kenntnis der SubundBrackwassermollusken von Guadeloupe, Dominica Martinique. Ann. Naturhist. Mus. Wien, vol.90, Part B, pp. 221-340.Starmuhlner, V.F.1988. Ergebnisse der Osterreichisch- FranzosischenHydrobiologischen Mission 1979 nach Guadeloupe, Dominica <strong>and</strong> Martinique (Kleine Antillen). TielII: Beiltrage Zur Kenntnis der Sub-und Brackwassermollusken von Guadeloupe, DominicaMartinique. Ann. Naturhist. Mus. Wien. 90(B): 221-340.Starmuhlner, V.F.1988. Ergebnisse derOsterreichisch- Franzosischen Hydrobiologischen Mission 1979 nach Guadeloupe, Dominica <strong>and</strong>Martinique (Kleine Antillen). Tiel II: Beiltrage Zur Kenntnis der Sub-und Brackwassermollusken vonGuadeloupe, Dominica Martinique. Ann. Naturhist. Mus. Wien, vol. 90, Part B, pp. 221-340.Starmuhlner, V.F.1988. Ergebnisse der Osterreichisch- Franzosischen Hydrobiologischen Mission1979 nach Guadeloupe, Dominica <strong>and</strong> Martinique (Kleine Antillen). Tiel II: Beiltrage Zur Kenntnisder Sub-und Brackwassermollusken von Guadeloupe, Dominica Martinique. Ann. Naturhist. Mus.Wien, vol. 90, Part B, pp. 221-340.Statistical Yearbook <strong>of</strong> Jamaica (1994). pp.4-5.P-15 ECO-PARASITOLOGICAL INVESTIGATION OF THIARAGRANIFERA AT THE MONA RESERVOIRStacey Mckoy, Eric Hyslop <strong>and</strong> Ralph Robinson<strong>Department</strong> Life Sciences, MonaMona reservoir is a man-made lake constructed in 1946, with a capacity <strong>of</strong> 808.5 megalitres(1) . Itexhibits lentic characteristics, i.e. there is no significant directional flow as water movement ismostly wind driven. <strong>The</strong> reservoir is an important habitat for a variety <strong>of</strong> aquatic <strong>and</strong> terrestrialanimals that depend on it for shelter, food <strong>and</strong> breeding sites. One such animal is the herbivorousprosobranch snail Thiara granifera (Lamarck). This common resident provides a habitat for a rich74


symbiotic fauna, which includes nematodes, protistans, the annelid Aeolosoma sp. <strong>and</strong> larvae <strong>of</strong>digenetic trematodes (monostone <strong>and</strong> distome varieties). <strong>The</strong> latter symbionts are <strong>of</strong> particularinterest since they use T. granifera as an intermediate host (I.H) in their life cycle.75


Thiara granifera is gregarious, providing opportunity for infection by trematode larvae. Presently,more is known <strong>of</strong> the biology <strong>of</strong> the monostomes than distomes as there is an overall monostomeprevalence <strong>of</strong> 21% (n=1175) compared with only ~1% for distome infections. <strong>The</strong> monostomelarval stages found in the I.H., are sporocysts, mother <strong>and</strong> daughter rediae <strong>and</strong> cercariae. It has notyet been determined whether the miracidium hatches within or outside the I.H. <strong>The</strong> larval forms areparthenitae <strong>and</strong> they multiply abundantly. <strong>The</strong> rediae <strong>and</strong> cercariae reside almost totally in thedigestive gl<strong>and</strong> where the gonad is also located; there is some evidence that nutrients are lost by thesnailas a result <strong>of</strong> infection <strong>and</strong> that fecundity <strong>of</strong> the snail is adversely affected; juveniles are absentwithin the I.H. when monostomes or distomes are present.Four sites were selected at the reservoir, two are roosting sites for birds (sites 1&3), the third is abird nesting site (site 2) <strong>and</strong> the fourth is a non-roosting/non-nesting site (site 4). <strong>The</strong> highestaverage density <strong>of</strong> T granifera is seen at site 1; 785.2 snails/m 2 , followed by site 3; 702.2 snails/m 2 .Sites 2 <strong>and</strong> 4 have snail densities <strong>of</strong> 449.3 <strong>and</strong> 407.5 snails/m 2. . Snail density is positivelycorrelated with the volume <strong>of</strong> water in the reservoir (Fs>F0.05, p0.1). <strong>The</strong> prevalence <strong>of</strong>monostomes is not equally distributed at each site (X 2 =150, p


P-16 PARASITISM OF THE COFFEE LEAF MINER,PERILEUCOPTERA COFFEELLA, IN JAMAICA AND ITSPOTENTIAL FOR INTEGRATED MANAGEMENT OF THE PESTKathy M. Dalip <strong>and</strong> Ajai Mansingh<strong>Department</strong> <strong>of</strong> Life Sciences, Mona<strong>The</strong> c<strong>of</strong>fee leaf miner (CLM), Perileucoptera c<strong>of</strong>feella (Guér.-Ménv. 1842), present in Jamaicasince 1921 (Gowdey, 1921) attains pest status periodically, with the latest outbreak occurring in theearly 1990s. It would appear, therefore, that the CLM population is normally kept in check byseveral factors, including natural enemies. Hence, a study was carried out to assess the composition<strong>of</strong> parasitoids <strong>of</strong> the CLM <strong>and</strong> their potential as biological control agents in any proposed integratedmanagement <strong>of</strong> the pest. Nineteen c<strong>of</strong>fee plantations in the major c<strong>of</strong>fee growing regions in eachparish <strong>of</strong> the isl<strong>and</strong> were visited at least once <strong>and</strong> a quick appraisal was made at each farm todetermine whether the CLM was present <strong>and</strong> if so, a rapid count was made to establish itsinfestation level. Between 30 <strong>and</strong> 60 recently-mined leaves were r<strong>and</strong>omly collected <strong>and</strong> taken to thelaboratory, placed in plastic containers lined <strong>and</strong> covered with paper towels which were kept moistat all times. <strong>The</strong> containers were the covered with nylon mesh held in place by elastic b<strong>and</strong>s <strong>and</strong> keptunder laboratory conditions <strong>of</strong> 27 - 29 o C <strong>and</strong> 65 - 70% relative humidity for at least three weeks oruntil the emergence <strong>of</strong> the CLM <strong>and</strong> its parasiotids. Emerged adult CLM <strong>and</strong> parasitoids in thecontainers, <strong>and</strong> mines with larval remains or pupae <strong>and</strong> those with signs <strong>of</strong> adult emergence werethen recorded. Mines <strong>and</strong> cocoons from which the CLM or parasitoid had not emerged weredissected <strong>and</strong> the condition <strong>of</strong> the dead larvae noted.Fourteen species <strong>of</strong> parasitoids belonging to at least three families <strong>of</strong> the order Hymenoptera wererecorded; two species belonged to the family Braconidae, eight to Eulophidae, one to Pteromalidae,one belonged either to Pteromalidae or Eupelmidae, <strong>and</strong> two others could not be classified.<strong>The</strong> highl<strong>and</strong> Mt. Pleasant Estates plantation had the most diverse parasitoid complex <strong>of</strong> elevenspecies while Christiana, Mt. Hill <strong>and</strong> Sligoville (also highl<strong>and</strong> plantations), <strong>and</strong> Clydesdale, GoodHope <strong>and</strong> Silver Hill Gap (Blue Mountain plantations) had between 7 <strong>and</strong> 10 species. <strong>The</strong> leastdiverse complex <strong>of</strong> two species was found in Bolo in the Blue Mountains.<strong>The</strong>re was significant (P = 0.05) variation in the mean level <strong>of</strong> parasitism among the plantations(Table 1). Parasitism was highest in the highl<strong>and</strong> plantations <strong>of</strong> Retirement <strong>and</strong> Warsop while it waslowest in the Blue Mountain plantations <strong>of</strong> Bolo, Good Hope <strong>and</strong> Flamstead <strong>and</strong> in the highl<strong>and</strong>Oxford plantation. Plantations with the lowest levels <strong>of</strong> parasitoids such as Bolo, Good Hope,Flamstead <strong>and</strong> Oxford, were regularly sprayed with insecticides. <strong>The</strong> total CLM mortality due toparasitism <strong>and</strong> natural causes (predation, disease) was less than 50% in approximately 42% <strong>of</strong> theplantations <strong>and</strong> was more than 70% in three plantations. About 50% <strong>of</strong> the plantations had fairlyhigh levels <strong>of</strong> parasitism (> 40%), they were not always associated with low CLM infestationlevels.<strong>The</strong> parasitoid complex in Jamaica is comparable to Latin American countries such as Brazil(7 braconids <strong>and</strong> 10 eulophids; Parra et al., 1977; Guimaraes, 1983) <strong>and</strong> Puerto Rico (2 braconids,one scelionid <strong>and</strong> 12 eulophids; Gallardo-Covas, 1988). It is quite possible that more species thanwere found in this study are present since the CLM infestation was <strong>of</strong>ten low when the sites weresampled.77


<strong>The</strong> population <strong>of</strong> the CLM in Jamaica appears to be held in check - with varying degrees <strong>of</strong> success- by a complex <strong>of</strong> its parasitoids. Thus, regular augmentation with laboratory-reared parasitoidsshould be an integral component in the integrated management <strong>of</strong> the CLM.ReferencesGallardo-Covas, F. (1988). Faunal survey <strong>of</strong> the c<strong>of</strong>fee leaf miner, Leucoptera c<strong>of</strong>feella, parasitoidsin Puerto Rico. J. Agric. Univ. P.R. 72(2): 255-263.Guimaraes, P.M. (1983). Flutuacao populacional do bicho mineiro (Perileucoptera c<strong>of</strong>feella,Guérin Méneville - 1842), parasitos e predadores (Hymenoptera) em duas regioes do Estado doParaná. 10 oCongr. Bras. de Pesquisas Caf., pocos de Caldas (MG), 29 de agosto a 1 desetembro de 1983 : café do Brasil. Rio de Janeiro, Brasil; Min. da Industr. e do Com., Inst.Bras. do café-GERCA. pp. 238-245.Gowdey, C.C. (1921). Rep. Govt. Entomologist, Rep. Dept. Agric., Jamaica, 1920. Kingston,Jamaica. pp. 25-27.Parra, J.R.P., Goncalves, W., Gravena, S. <strong>and</strong> Marconato, A.R. (1977). Parasitos e predadores debicho-mineiro de cafeeiro Perileucoptera c<strong>of</strong>feella (Guérin-Méneville, 1842) em Sâo Paulo.Anais da Soc. Entomol. do Brazil. 6(1): 138-143.P-17 TRANSMISSION ROUTES FOR HELICOBACTER PYLORIINFECTIONS IN A JAMAICAN COMMUNITYAlicia E. Lyn-Sue 1, John F. Lindo 2 , Carol J. Palmer 3 , P. Vogel 1 ,Michael G. Lee 4 <strong>and</strong> Ralph D. Robinson 1<strong>Department</strong>s <strong>of</strong> 1 Life Sciences, 2 Microbiology <strong>and</strong> 3 Medicine, Mona;4Centre for Disease Prevention, University <strong>of</strong> Miami School <strong>of</strong> MedicineAssociations were sought between environmental <strong>and</strong> demographic factors, <strong>and</strong> householdprevalence <strong>of</strong> Helicobacter pylori infection in a Jamaican suburban community. <strong>The</strong> study designwas based on a household cluster sampling technique: 43 domestic yards, enclosing 62 separatehouseholds, were r<strong>and</strong>omly selected from a local community. All household members (n=346) wereinvited to participate following informed consent; the overall compliance rate was 61.8%. Acommercial enzyme immunoassay (HM·CAP ) was used to detect IgG antibodies raised against H.pylori. Environmental <strong>and</strong> demographic information was obtained by questionnaire from residents(n = 202) <strong>of</strong> 43 households accommodating more than one person. <strong>The</strong> seroprevalence <strong>of</strong> H. pyloriwas 69.9% (n=219). A strong age-specific association (Χ 2 = 21.2, df = 3, p < 0.001) showed a lowseroprevalence <strong>of</strong> H. pylori (27%) in children less than 6 years old which quickly becameasymptopic (> 70%) in older age classes. Univariate analysis (ANOVA) revealed household use <strong>of</strong>municipal water supply, use <strong>of</strong> communal toilet, <strong>and</strong> ownership <strong>of</strong> cats <strong>and</strong> dogs as potential riskfactors for infection. In comparison, multiple regression retained only use <strong>of</strong> municipal water supply(p = 0.003) <strong>and</strong> ownership <strong>of</strong> cats (p = 0.008) as independent risk factors for H. pylori infection. Noassociation was found between H. pylori infection <strong>and</strong> recent history <strong>of</strong> intestinal aliments. <strong>The</strong>study points to the potential importance <strong>of</strong> environmental <strong>and</strong> zoonotic components in thetransmission <strong>of</strong> H. pylori in a tropical community.78


P-18 RISK FACTORS FOR TRANSMISSION OF TOXOCARA CANIS(DOG ROUNDWORM) IN A HUMAN COMMUNITYHugh E. Lounges 1 , John F. Lindo 2 , Michael G. Lee 3 , Peter Vogel 1 <strong>and</strong> Ralph D. Robinson 1<strong>Department</strong>s <strong>of</strong> 1 Life Sciences, 2 Microbiology <strong>and</strong> 3 Medicine, MonaAssociations are sought between environmental/demographic factors <strong>and</strong> human infection with thedog roundworm, Toxocara canis, in a Jamaican community. Forty one domestic yards containing 62separate households were selected r<strong>and</strong>omly from a local community. All members were invited toparticipate, following informed consent. T. canis infection (toxocariasis) was confirmed by anenzyme-linked immunosorbent assay (ELISA). A high degree <strong>of</strong> sensitivity <strong>and</strong> specificity wasachieved resulting from the use <strong>of</strong> excretory/secretory (E/S) antigen in the diagnostic tests.Environmental <strong>and</strong> demographic information was obtained by questionnaire. <strong>The</strong> data weresubjected to univaraite <strong>and</strong> multivariate analyses in an attempt to reveal the major risk factors fortransmission <strong>of</strong> the parasite in the community. Thirty one households, having 3-11 members, wereincluded in the study. Community prevalence <strong>of</strong> serum immunoglobulin G (IgG) to T. canis E/Santigen (ELISA) was 50.7% (n = 215) indicating a high level <strong>of</strong> sub-clinical toxocariasis in thestudy community. Discriminant analysis revealed the following associations with T. canis positiveserology: poor sanitation/hygiene, the presence <strong>of</strong> young persons in the household <strong>and</strong> absence <strong>of</strong> adelimiting fence around the household. Multiple regression analysis confirmed these associations<strong>and</strong> predicted poor personal hygiene (e.g. finger sucking), high male sex ratio <strong>and</strong> ownership <strong>of</strong>puppies as major risk factors for exposure to T. canis. Further, positive T. canis serology wasassociated with a history <strong>of</strong> respiratory signs (viz. lingering cough), possibly indicating the presence<strong>of</strong> migrating larvae in the pulmonary system (visceral larva migrans, VLM). This work points tothe potential public health significance T. canis infections in Jamaica.P-19 THE DEVELOPMENT OF RESISTANCE IN SEVERALJAMAICAN POPULATIONS OF THE COFFEE BERRY BORER(HYPOTHENEMUS HAMPEI) TO VARIOUS INSECTICIDESDionne E. Witter-Newell <strong>and</strong> Ajai Mansingh<strong>Department</strong> <strong>of</strong> Life Sciences, Mona<strong>The</strong> c<strong>of</strong>fee berry borer, Hypothenemus hampei (Coleoptera: Scolytidae), was first reported inJamaica in 1978 <strong>and</strong> since then has become the major pest <strong>of</strong> c<strong>of</strong>fee (Reid <strong>and</strong> Mansingh, 1985). Itslevel <strong>of</strong> damage to a single bean can be up to 50% as the larvae feed on only one endosperm. Withinthe first five years <strong>of</strong> its presence on the isl<strong>and</strong>, it had dispersed extensively in both lowl<strong>and</strong> <strong>and</strong>highl<strong>and</strong> plantations (Rhodes, 1987). As a result, farmers isl<strong>and</strong> wide relied heavily on the use <strong>of</strong>insecticides as the sole means <strong>of</strong> controlling the pest. <strong>The</strong> most effective <strong>and</strong> popularly usedinsecticide was endosulfan while others, such as Actellic <strong>and</strong> Decis, were less commonly used.Failure to incorporate cultural practices on c<strong>of</strong>fee farms resulted in ecological <strong>and</strong> environmentalbacklashes <strong>of</strong> pesticide usage. Subsequently, continuous complaints by farmers on theineffectiveness <strong>of</strong> endosulfan against the borer suggested that resistance to endosulfan <strong>and</strong> crossresistanceto other insecticides may have developed in the pest. Resistance in the c<strong>of</strong>fee berry borerto endosulfan has already been reported in New Caledonia (Brun et al., 1989).79


<strong>The</strong> present studies were undertaken to confirm the percieved resistance <strong>and</strong> cross-resistance to theinsecticides. <strong>The</strong> mechanism <strong>of</strong> resistance, which is still questionable, is also being investigated.Infested berries were collected from c<strong>of</strong>fee plantations across the isl<strong>and</strong> <strong>and</strong> taken to the laboratoryfor assaying with insecticides. Each <strong>of</strong> ten berries was dipped for one second in a beaker containingthe experimental concentration <strong>of</strong> each formulation, drip-dried for five seconds, then placed in a petridish <strong>and</strong> covered with muslin. After twenty-four hours each berry was dissected <strong>and</strong> the mortality <strong>of</strong>the borer recorded. Experiments were done in triplicate. Probit analysis was used to determine theLC50 (% concentration <strong>of</strong> active ingredient) <strong>of</strong> the insecticide formulations to the borer <strong>and</strong> thevalues compared to those reported by Rhodes (1987).Susceptible <strong>and</strong> resistant strains <strong>of</strong> c<strong>of</strong>fee berry borer from the bioassays were separated <strong>and</strong> placedin hexane for residue extraction. Extracts were concentrated <strong>and</strong> analysed on a Hewlett-Packard HP5890 Series II gas chromatograph equipped with a 30 m HP-1 capillary column <strong>and</strong> a63 Ni-ECD todetermine the presence <strong>of</strong> endosulfan <strong>and</strong> its metabolites. Analytical conditions were: carrier gas -nitrogen, at a flow rate <strong>of</strong> 10 - 15 mL/min; temperature settings - column, initial 100o C, rate20 o C/min., final 250 o C; injector 280 o C; detector 300 o C.<strong>The</strong> 24-hour LC50 <strong>of</strong> selected insecticides against adult borers, <strong>and</strong> their resistance levels relative tothe LC50 <strong>of</strong> these insecticides found by Rhodes (1987) are presented in Table 1. <strong>The</strong> results indicatethat between 100- <strong>and</strong> 700-fold resistance has developed in local population <strong>of</strong> the c<strong>of</strong>fee berry borerover a 15-year period. <strong>The</strong> populations have also developed cross-resistance to diazinon, Actellic<strong>and</strong> Decis.Chromatograms <strong>of</strong> hexane extracts <strong>of</strong> susceptible <strong>and</strong> resistant strains <strong>of</strong> the c<strong>of</strong>fee berry borer,which were exposed to endosulfan, produced peaks corresponding to a- <strong>and</strong> b-endosulfan. However,two additional peaks were present in chromatograms <strong>of</strong> extracts from the resistant strains <strong>of</strong> theborer. <strong>The</strong>se may be due to metabolites <strong>of</strong> endosulfan, suggesting the possibility <strong>of</strong> a biochemicalmode <strong>of</strong> resistance <strong>of</strong> the borer to endosulfan. Information on the mode <strong>of</strong> resistance providestremendous opportunities for creating alternative means <strong>of</strong> controlling the c<strong>of</strong>fee berry borer.ReferencesBrun, L.O., Marcillaud, C., Gaudichon, V., <strong>and</strong> Suckling, D.M. (1989). Endosulfan resistance inHypthenemus hampei (Coleoptera: Scolytidae) in New Caledonia. J. Econ. Entomol. 82(5):1311-1316.Reid, J. <strong>and</strong> Mansingh, A. (1985). Economic losses due to Hypothenemus hampei, Ferrari duringprocessing <strong>of</strong> c<strong>of</strong>fee berries in Jamaica. Trop. Pest Manag. 31(1): 55-59.Rhodes, L.F. (1987). Infestation pattern <strong>and</strong> insecticidal susceptibility <strong>of</strong> Hypothenemus hampei(Ferrari) (Coleoptera: Scolytidae). <strong>The</strong> University <strong>of</strong> the West Indies; M. Phil. thesis. 192 pp.80


P-20 THE COMPATIBILITY OF A THIODAN/COPPER MIXTUREAND THE INCLUSION OF MINERAL OIL FOR THE COMBINEDCONTROL OF THE COFFEE LEAF RUST AND BERRY BORERDwight E. Robinson <strong>and</strong> *Janice Reid<strong>Department</strong> <strong>of</strong> Life Sciences;*Caribbean Agricultural Research Development Institute, Kingston<strong>The</strong> c<strong>of</strong>fee berry borer (CBB), Hypothenemus hampei Ferr., <strong>and</strong> c<strong>of</strong>fee leaf rust (CLR), Hemileiavastatrix Berk. <strong>and</strong> Br., are major pests <strong>of</strong> c<strong>of</strong>fee in Jamaica (Reid <strong>and</strong> Mansingh, 1985). In orderto reduce the cost <strong>of</strong> pesticide application, farmers have combined Thiodan <strong>and</strong> copper (Martin,1996) incognizant <strong>of</strong> possible compatibility problems. <strong>The</strong> present study was conducted to assess theimpact <strong>of</strong> simultaneously applying both pesticides, with <strong>and</strong> without mineral oil, for the control <strong>of</strong>the CBB <strong>and</strong> CLR. <strong>The</strong> study was carried out on a 1.2-ha site at Mountain Hill, St. Catherine, overtwo cropping seasons. A split plot design consisting <strong>of</strong> four main plots with six split plots <strong>of</strong> 20 treeseach was used. Each split plot was treated with one <strong>of</strong> six chemical treatments - endosulfan asThiodan 35EC, copper as copper oxychloride 75WP, a combination <strong>of</strong> Thiodan <strong>and</strong> copperoxychloride <strong>and</strong> each <strong>of</strong> these treatments with mineral oil - <strong>and</strong> three branches from the inner sixtrees r<strong>and</strong>omly selected <strong>and</strong> tagged for monitoring CBB infestation <strong>and</strong> CLR infection. Thiodan was<strong>applied</strong> at 4.2 mL/L, copper at 14.7 g/L <strong>and</strong> mineral oil at 4.2 mL/L at a rate <strong>of</strong> approximately 0.15L <strong>of</strong> <strong>of</strong> solution per tree. All plots received a second application after six to eight weeks.At the end <strong>of</strong> a 90-day monitoring period, the increase in borer infestation <strong>and</strong> bean damage in plotstreated with Thiodan was 21.5 <strong>and</strong> 24.9%, respectively, <strong>and</strong> 14.8 <strong>and</strong> 23.6%, respectively, in plotstreated with a Thiodan/copper mixture. Mortality <strong>of</strong> the CBB ranged from 46 to 85% in plots treatedwith Thiodan compared with 66 to 86% in plots treated with the Thiodan/copper mixture. <strong>The</strong> 4.5%reduction in rust infestation in plots treated with the Thiodan/copper mixture was significantly (P 0.05) effect on borer infestation or rust infection.However, mortality <strong>of</strong> the CBB was significantly (P = 0.032) higher in plots treated with Thiodan<strong>and</strong> mineral oil (60 - 90%) compared to those treated with the insecticide alone (42 - 77%).<strong>The</strong> data clearly suggest that the mixing <strong>of</strong> copper <strong>and</strong> Thiodan did not affect the efficacy <strong>of</strong> theinsecticide against the CBB <strong>and</strong> is consistent with recommendations made by Reid (1987). However,it did reduce the efficacy <strong>of</strong> the fungicide against the CLR, while the inclusion <strong>of</strong> mineral oil had noimpact on the efficacy <strong>of</strong> either pesticide.ReferencesMartin, R. (1996). An integrated approach to c<strong>of</strong>fee production in Jamaica. Presented at th 7AnnualConf. Jam. Soc. for Agric. Sc., May 28 - 30, 1996, Kgn., Jamaica.Reid, J. C. (1987). Economic status <strong>and</strong> integrated management <strong>of</strong> the c<strong>of</strong>fee berry boreHypothenemus hampei (Ferr.). Mona, Jamaica; <strong>The</strong> Univ. <strong>of</strong> the West Indies; Ph.D. thesis.Reid, J. C. <strong>and</strong> Mansingh, A. (1985). Economic losses due to Hypothenemus hampei Ferr., duringprocessing <strong>of</strong> c<strong>of</strong>fee berries in Jamaica. Trop. Pest Manag. 31(1): 55-59.81


P-21 ANTIFEEDANT PROPERTIES OF VARIOUS FORMULATIONSOF NEEM OIL AGAINST CITRUS ROOT WEEVILSDwight E. Robinson <strong>and</strong> Ajai Mansingh<strong>Department</strong> <strong>of</strong> Life Sciences, Mona<strong>The</strong> citrus root weevil (CRW) is a pest <strong>of</strong> citrus seedlings in many plantations in Jamaica. Its controlhas been entirely based on spraying insecticides against the adults <strong>and</strong> soil treatment against thelarvae (Clarke-Harris, 1998). <strong>The</strong> heavy load <strong>of</strong> pesticide residues in Rio Cobre (Mansingh et al.,1997) is attributed to use <strong>of</strong> dieldrin <strong>and</strong> other organochlorines by citrus farmers. <strong>The</strong> present studywas conducted to test our own formulations <strong>of</strong> neem (Azadirachta indica, A. Juss), known to havediverse insecticidal activity (Williams <strong>and</strong> Mansingh, 1996), extracts as antifeedants against theCRW.Dried neem kernels were homogenized in methanol, placed in dark brown bottles <strong>and</strong> allowed toextract for three days under laboratory conditions. Extracts were shaken, filtered, concentrated invacuo to oily residues <strong>and</strong> made into different formulations by adding an emulsifier <strong>and</strong> varyingconcentrations <strong>of</strong> sticker, spreader, penetrants <strong>and</strong> photo-stabilizers. A commercial formulation <strong>of</strong>neem <strong>and</strong> <strong>pure</strong> neem preparation obtained from private developers were also used.<strong>The</strong> activity <strong>of</strong> the formulations was studied in the laboratory by spraying field-collected stems with6 - 8 days young citrus leaves with different concentrations <strong>of</strong> the neem extracts, formulations oremulsifier <strong>and</strong> water as a control. Three treated stems were then fed to ten CRW adults held in 30-Lglass chambers. In greenhouse studies, one-metre high citrus seedlings were treated as describedabove. Treated seedlings were placed in a mesh cage into which 20 adult CRW were released. Inboth experiments, the number <strong>of</strong> leaves damaged <strong>and</strong> area consumed were recorded at regularintervals. All experiments were conducted in triplicate.In the first <strong>of</strong> two field trials, young citrus leaves on trees were treated with 5 cc/L <strong>of</strong> the neemformulations. Six stems with treated leaves were removed from the trees after 3, 6 <strong>and</strong> 9 days <strong>and</strong> apair <strong>of</strong> branches fed to three sets <strong>of</strong> ten adult CRW in the laboratory. <strong>The</strong> leaf consumption wasrecorded at three-day intervals. A second trial was done on a one-ha plot <strong>of</strong> trumpet trees (Fam.:Moraceae, Cercopia peltata L.) in Portl<strong>and</strong>. Six trees were r<strong>and</strong>omly selected from each <strong>of</strong> three 20-tree plots in three blocks <strong>and</strong> sprayed with one <strong>of</strong> two neem formulations or water. <strong>The</strong> number <strong>of</strong>leaves damaged <strong>and</strong> the leaf area consumed by the CRW were recorded before, <strong>and</strong> 10, 19 <strong>and</strong> 29days after treatment.In the laboratory, 13 - 41.0% <strong>of</strong> leaves treated with Ashima III, Abhijai <strong>and</strong> Dejoun were attackedcompared to 24 - 61 % <strong>of</strong> leaves in the controls. <strong>The</strong> formulations inhibited feeding by 26 - 80%.Under greenhouse conditions, where the CRW had a feeding choice, leaves treated with Dejoun werenot attacked during the 21-day experimental period. <strong>The</strong>re was no significant ( P > 0.05) differencebetween the damage to leaves <strong>of</strong> untreated seedlings (31 - 65%) <strong>and</strong> those treated with neem oil (8 -35%) <strong>and</strong> Ashima I (15 - 38%); however, there was significantly (P < 0.05) less damage to leavestreated with Ashima II (8 - 32%), Ashima III (9 - 25%) <strong>and</strong> Abhijai (12 -19%). Feeding wasinhibited 56 - 100% during the 21-day period by Ashima III, Abhijai <strong>and</strong> Dejoun.During the nine-day field trial in Mona, significantly (P = 0.006) fewer number <strong>of</strong> leaves (19.4 -50.0%) treated with Dejoun were damaged when compared with other treatments (45.8 - 80.6%;see Table).82


<strong>The</strong>re was increased consumption <strong>of</strong> treated leaves between days 6 <strong>and</strong> 9, possibly as a result <strong>of</strong> the16.5 mm <strong>of</strong> rain which fell during that period. In field trials in Portl<strong>and</strong>, between 30 - 90 <strong>and</strong> 32 -86% <strong>of</strong> treated <strong>and</strong> untreated trumpet tree leaves, respectively, were damaged but the difference wasnot significant (P > 0.05). Feeding was inhibited by 63 - 72% <strong>and</strong> 40 - 60% on trees treated withAshima III <strong>and</strong> Dejoun, respectively. Ashima III, Abhijai <strong>and</strong> Dejoun are being further developed forcommercialization.Table:Consumption <strong>of</strong> citrus leaves which were removed from trees <strong>of</strong> a Monaorchard at different time intervals after they were treated with differentformulations <strong>of</strong> neem, at a concentration <strong>of</strong> 5cc/L, <strong>and</strong> fed to CRW adults inthe laboratory_______________________________________________________________________________Treatment Days post Total No. Leaves Total leaf I.F. a Cumulativetreatment leaves damaged area consumed (%) mortality b(%) (cm 2 ) (%)_______________________________________________________________________________Control 0 30 60.0 69.9 - 03 28 71.4 69.0 - 06 28 78.6 74.3 - 09 31 80.6 71.8 - 12.5Ashima II 0 28 46.0 23.3 66.7 03 29 82.8 31.3 54.6 25.06 24 45.8 27.5 63.0 25.09 24 66.7 40.9 43.0 37.5Ashima III 0 32 53.1 32.6 53.4 03 32 53.1 38.5 44.2 18.86 29 44.8 58.1 21.8 37.59 33 78.8 60.1 16.3 37.5Dejoun 0 31 19.4 2.4 96.6 03 31 29.0 7.6 89.0 14.36 33 48.5 14.8 80.1 42.99 22 50.0 50.7 29.4 42.9_________________________________________________________________________a. % inhibition <strong>of</strong> feeding by the CRW where:I.F. = (Mean leaf area consumed in the control - Mean leaf area consumed in the treated) x 100Mean leaf area consumed in the controlb. On each sample day, the total mortality after treatment was recorded83


ReferencesClarke-Harris, D.O. (1998). Investigations on the potentials <strong>of</strong> biological <strong>and</strong> cultural methods inthe integrated management <strong>of</strong> citrus root weevils in Jamaica. Mona, Jamaica; Univ. <strong>of</strong> theWest Indies; M.Phil. thesis.Mansingh, A., Robinson, D.E. <strong>and</strong> Dalip, K.M. (1997). Insecticide contamination <strong>of</strong> the Jamaicanenvironment. Trends in Anal. Chem. 16 (3): 115-123.Williams, L.A.D <strong>and</strong> Mansingh, A. (1996). A review <strong>of</strong> the insecticidal <strong>and</strong> acaricidal actions <strong>of</strong>compounds from Azadirachta indica (A. Juss) <strong>and</strong> their scope in tropical pest management.Integ. Pest Manag. Rev. 1: 133-145.P-22 ECOTOXICITY OF INSECTICIDE RESIDUES IN JAMAICA:SUB-LETHAL TOXICITY LEVELS OF ENDOSULFAN ON THEFISH TILAPIA AND ITS EFFECTS ON LIPID CONTENT OFGONADSWinroy O.Williams, *Kerith D. Golden <strong>and</strong> Ajai Mansingh<strong>Department</strong>s <strong>of</strong> Life Sciences <strong>and</strong> *Basic Medical Sciences, MonaEndosulfan is widely used in the c<strong>of</strong>fee industry <strong>and</strong> its residues have been detected in surface,ground <strong>and</strong> coastal waters <strong>and</strong> in aquatic fauna all over Jamaica (Mansingh et al., 1997). <strong>The</strong>residues bioaccumulate mainly in the gonads (Robinson, 1997) <strong>and</strong> could have deleteriousconsequences on the fish’s reproductive physiology (Hiraoka et al., 1989). <strong>The</strong> present study isexpected to elucidate the toxicity <strong>of</strong> sub-lethal concentrations <strong>of</strong> endosulfan <strong>and</strong> its impact on thereproductive physiology <strong>of</strong> the fish.Twenty-eight day sub-lethal toxicity <strong>of</strong> endosulfan to Tilapia (9 - 14 cm long; 20 - 40g) wereassayed under static conditions in continually aerated glass aquaria containing 20 L <strong>of</strong> dechlorinatedwater <strong>and</strong> 15 fish at 27 - 28°C. <strong>The</strong> following concentrations <strong>of</strong> endosulfan - 0.005, 0.0075, 0.008,0.009 <strong>and</strong> 0.01 ppm - were assayed in three replicates <strong>and</strong> repeated. Fish were fed daily oncommercial tilapia ration <strong>and</strong> the water changed every five days to avoid accumulation <strong>of</strong> toxicmetabolic products.Symptoms (darting, shuddering, side-swimming <strong>and</strong> death)were observed for the first 8 hrs <strong>and</strong>every 4 hrs thereafter. <strong>The</strong> results were then subjected to Probit analysis in order to determine thedifferent toxicity concentrations: the no-observable-toxic-effect-concentration (NOTEC), leastobservable-toxic-effect-concentration(LOTEC), pronounced-observable-toxic-effect-concentration(PROTEC) <strong>and</strong> least-acute-toxic-effect-concentration (LATEC).At the end <strong>of</strong> the period, three fish from each <strong>of</strong> three replicates were removed, held on ice untildead, dried <strong>and</strong> weighed. Gonads were dissected out <strong>and</strong> pooled. <strong>The</strong> whole body or gonads <strong>of</strong> thefish were then cut into small pieces <strong>and</strong> extracted with a 2:1 (v/v) chlor<strong>of</strong>orm-methanol mixture(1g:5ml) in the cold using a M.S.E homogenizer. <strong>The</strong> homogenates were filtered, residues washed<strong>and</strong> crude extracts quantified. Extracts were purified <strong>and</strong> the sulphophosphovanillin reaction (Barnes<strong>and</strong> Blackstock, 1973) executed. <strong>The</strong> total lipid content <strong>of</strong> each sample was then determined bycomparison to the st<strong>and</strong>ard curve.84


Toxicity data suggest that 0.0025 - 0.005 ppm may be defined as NOTEC, since only 0 - 10% <strong>of</strong> thefish were affected but all recovered within the experimental period. <strong>The</strong> 0.008 ppm dose may beregarded as LOTEC, since 22% <strong>of</strong> the fish were affected for a while, but all recovered within theexperimental period. Hyperactivity was visible in all the fish at 0.009 ppm; however only 14% <strong>of</strong>them had pronounced toxic effects, but 7% died between days 11 <strong>and</strong>15. Thus, 0.009 ppm may beregarded as PROTEC. At 0.01 ppm, all the individuals were hyperactive from the beginning; 9%showed toxic symptoms, while 3% died within 6 - 10 days <strong>of</strong> exposure.However, between days 11 <strong>and</strong> 15, while 17% showed toxic symptoms, 47% died. Within the next 5days, all the fish were dead.<strong>The</strong> data presented in the Table show that lipid content <strong>of</strong> the fish <strong>and</strong> its gonads changedsignificantly (P < 0.05) over the 28-day period when exposed to NOTEC, LOTEC <strong>and</strong> PROTEC <strong>of</strong>endosulfan. Percentage decreases in total lipid were 19.50, 53.96 <strong>and</strong> 67.50 for fish exposed toNOTEC, LOTEC, <strong>and</strong> PROTEC, respectively. This overall decrease in total lipid may indicateincreased lipid hydrolysis to produce the energy required to overcome pesticidal stress (Rao et al.,1985). While there was 6.99 <strong>and</strong> 32.85% decrease in total lipid <strong>of</strong> gonads for fish exposed toNOTEC <strong>and</strong> LOTEC, respectively, there was a 25.56% increase for fish exposed to PROTEC -which may have been due to an experimental artifact.TableChanges in lipid content in whole body <strong>and</strong> gonads <strong>of</strong> Tilapia after 28-dayexposure to endosulfan______________________________________________________________________________Total lipid (mg lipid/g wet wt.) Percentage changeWhole body Gonads Whole body Gonads______________________________________________________________________________Control 32.30 ± 0.268 10.05 ± 0.013 0 00.005 ppm 26.80 ± 0.195 9.35 ± 0.008 19.50 6.990.008 ppm 14.87 ± 0.111 6.75 ± 0.363 53.96 32.850.009 ppm 10.49 ± 0.207 13.51 ± 0.013 67.50 25.56______________________________________________________________________________Mean fish weight (g) ± S.E. = 30.725 ± 1.227ReferencesBarnes, H. <strong>and</strong> Blackstock, J. (1973). Estimation <strong>of</strong> lipids in marine animals <strong>and</strong> tissues: detailedinvestigations <strong>of</strong> the sulphophosphovanillin method for ‘total’ lipids. J. Exp. Mar. Biol. Ecol. 12:103-118.Hiraoka, Y., Tanaka, J., Okuda, H. (1989). Toxicity to Medaka (red variety <strong>of</strong> Oryzias latipes)<strong>of</strong> solutions <strong>of</strong> Fenitrothion degraded by strong alkali. Environ. Pollut. 58: 35-42.85


Mansingh, A., Robinson, D.E. <strong>and</strong> Dalip, K.M. (1997). Insecticide contamination <strong>of</strong> the Jamaicanenvironment, Trends in Anal. Chem. 16(3):115-123.Rao, K.S.P., Rao, K.R.S.S., Sahib, I.K.A. <strong>and</strong> Rao, K.V.R. (1985). Combined action <strong>of</strong> carbaryl<strong>and</strong> phenthoate on tissue lipid derivatives <strong>of</strong> mussel, Channa punctatus (Bloch.) Ecotoxicol.Environ. SAF. 9 (1): 107-111.Robinson, D.E. (1997). <strong>The</strong> fate, biological impact <strong>and</strong> management <strong>of</strong> endosulfan <strong>and</strong>ethoprophos in the Jamaican environment. Ph. D. <strong>The</strong>sis. Univ. West Indies, Mona, Jamaica.289 pp.P-23 ORGANOCHLORINE RESIDUES IN SURFACE WATER ANDSEDIMENT OF THE YALLAHS RIVER: 1989-1991Raymond Martin, Ajai Mansingh 1 <strong>and</strong> Janice Reid 21<strong>Department</strong> <strong>of</strong> Life Sciences, Mona; 2 P.O. Box 501, Kingston 10<strong>The</strong> Yallahs River watershed covers 180 sq. km approximately 70% <strong>of</strong> which consists <strong>of</strong> slopes over 30degrees. It rises under Silver Head peak in the Blue Mountains at an elevation <strong>of</strong> 1600m, is 37 km inlength <strong>and</strong> is the main river draining the southern slopes <strong>of</strong> the Blue Mountains. <strong>The</strong> watershed is a majorc<strong>of</strong>fee producing area <strong>and</strong> a range <strong>of</strong> insecticides such as endosulfan, diazinon <strong>and</strong> dimethoate are used(Martin et al., 1996). <strong>The</strong> use <strong>of</strong> insecticides in mountainous watersheds where springs <strong>and</strong> riversoriginate, has resulted in the contamination <strong>of</strong> rivers <strong>and</strong> coastal waters <strong>of</strong> the isl<strong>and</strong> (Mansingh etal., 1997). Many <strong>of</strong> these watersheds experience heavy rainfall which results in massive soil erosiondue to deplorable agronomic <strong>and</strong> deforestation activities by people (Eyre, 1990). Contamination <strong>of</strong>the river is <strong>of</strong> great concern because it is a major source <strong>of</strong> domestic water for the rural population aswell as for Kingston <strong>and</strong> St. Andrew. Inthe past, insecticides have been implicated as a possible cause<strong>of</strong> fish kills in the vicinity <strong>of</strong> the river (Aiken <strong>and</strong> Jupp, 1985).A survey <strong>of</strong> farms in the watershed was conducted to collect data on the crops grown <strong>and</strong> the types<strong>and</strong> amounts <strong>of</strong> pesticides used. In addition, water <strong>and</strong> sediment samples were collected on 9occasions from 17 locations between July 1989 <strong>and</strong> September 1991. Eighty five percent <strong>of</strong> farmsin the watershed were


Levels were generally higher during wet periods than dry periods <strong>and</strong> during the spray period thanoutside the spray period (Table 1). About 20% <strong>of</strong> samples from the Yallahs River exceeded theUSEPA maximum <strong>of</strong> 0.22 µg/L. Levels unacceptable for human health (74 µg/L ) were notobserved.TableComparison <strong>of</strong> frequency <strong>of</strong> detection <strong>and</strong> mean residue levels detected in theYallahs River watershed during spray <strong>and</strong> non-spray periodsPeriodType <strong>and</strong>Number <strong>of</strong>SampleDetection frequency <strong>and</strong> (mean)α-endosulfanβ-endosulfanEndosulfansulfateDieldrinDiazinonSprayPeriodWater8048%(1.41)34%(0.660)6.6%(14.9)6.2%(0.285)38%(1.74)Sediment6733%(2330)11%(1430)bdl22%(20.2)41%(148)Non-SprayPeriodWater8616%(0.995)5.8%(0.242)bdlbdlbdlSediment72bdlbdl12%(27.5)bdlbdlbdl = below the detectable levelReferencesAiken, K. <strong>and</strong> Jupp. B. (1985). <strong>The</strong> St .Thomas fish kill. Jamaica Journal. 18(3): 53-56.Eyre, L.A. (1990). Forestry <strong>and</strong> watershed management. Min. Dev. Planning <strong>and</strong> Prod. Natl. Cos.Strat. Consltn. Workshop, April 25-27, 1990, Kingston, Jamaica.Mansingh, A., Robinson, D.E., Dalip, K.M. (1997). Insecticide contamination <strong>of</strong> the Jamaicanenvironment. Trends in Analytical <strong>Chemistry</strong> 16(3): 115-123.Martin, R.D., Reid, J.C. <strong>and</strong> Reid, H. (1996). An integrated approach to c<strong>of</strong>fee production. SeventhAnnual Conference <strong>of</strong> the Jamaican Society <strong>of</strong> Agricultural Scientists, May 28-30, 1996, KingstonJamaica.87


P-24 THE NEW JAMAICA SEISMOGRAPH NETWORK:RESULTS AFTER ONE YEARMargaret D. Gr<strong>and</strong>isonEarthquake Unit, <strong>Department</strong> <strong>of</strong> Geography <strong>and</strong> Geology, Mona<strong>The</strong> Jamaica Seismograph Network (JSN) was totally rebuilt . All dated hardware was replacedwith new st<strong>and</strong>ard industrial models, more modern <strong>and</strong> effective s<strong>of</strong>tware for data capture <strong>and</strong>analysis were acquired, <strong>and</strong> all seismographs were calibrated. <strong>The</strong> basic network was completed byJuly 1997. Since then some expansion <strong>of</strong> the network took place so that by July 1998, there were10 short period seismograph stations, <strong>of</strong> which 2 were complete or 3-component stations. Duringthis first year <strong>of</strong> operation, 655 earthquakes were recorded including by category, 127 teleseismic ordistant events, 91 regional (within the Caribbean Basin), 125 Near (within about 400 km <strong>of</strong>Jamaica) <strong>and</strong> 322 Local earthquakes. <strong>The</strong> Local region is bounded by latitudes 17.6 to 18.6 North<strong>and</strong> longitudes 76.0 to 78.5 West, encompassing the isl<strong>and</strong> <strong>of</strong> Jamaica <strong>and</strong> the coastal zone. This isthe region best covered by the seismograph network, where earthquake locations are most reliable,<strong>and</strong> where earthquakes are likely to be most hazardous to Jamaica.<strong>The</strong> subject <strong>of</strong> this paper is part <strong>of</strong> on-going analyses <strong>of</strong> the 322 local earthquakes using SEISANEarthquake Analysis S<strong>of</strong>tware. <strong>The</strong> earthquakes are being relocated, <strong>and</strong> the response functions forthe seismographs registered. Some <strong>of</strong> the early goals include: (i) defining 2 magnitude scales forJamaica that are calibrated to the st<strong>and</strong>ard body-wave (Mb) <strong>and</strong> moment magnitude (Mw) scales;(ii) refining the crustal velocity model; <strong>and</strong> (iii) characterizing how seismic waves attenuate in thelocal crust. <strong>The</strong>se will be commented on with regard to methods <strong>and</strong> preliminary results.P-25 COASTAL EROSION IN SOUTHERN JAMAICA:AN EXAMPLE FROM CLARENDON PARISHEdward Robinson<strong>Department</strong> <strong>of</strong> Geography <strong>and</strong> Geology, MonaExamination <strong>of</strong> maps <strong>and</strong> air photographs dating back to 1941, <strong>and</strong> <strong>of</strong> maps dating back to the early19 th Century, has yielded complex patterns <strong>of</strong> relatively large scale coastline changes between themouth <strong>of</strong> the Rio Minho <strong>and</strong> Milk River, south coast <strong>of</strong> Jamaica. <strong>The</strong>se include up to half akilometre <strong>of</strong> coastal recession since 1941, immediately west <strong>of</strong> the Rio Minho. This is probably thelargest loss <strong>of</strong> coastal l<strong>and</strong> in Jamaica over the past half century, <strong>and</strong> is relatively large on a globalscale. It is also a finding contrary to previous reports (Wood, 1976) which have suggested coastalaccretion in this region.Changes in coastline geometry since 1941 were examined by comparing four maps <strong>of</strong> the area,derived from aerial photographic surveys. <strong>The</strong> 1:50,000 topographic maps, released about 1950,were derived from photography flown in 1941. A second map series, at 1:12,500 scale, wasproduced for the L<strong>and</strong> Valuation <strong>Department</strong> in 1958, based on 1953 photography. <strong>The</strong> 1:12,500scale topographic maps, produced by the Survey <strong>Department</strong> in the 1970s, are based on 1968photography. <strong>The</strong> current 1:50,000 scale metric maps are based on aerial photography flown in1980. <strong>The</strong>se maps provide precise control for the evaluation <strong>of</strong> coastline changes.88


<strong>The</strong> original photographs were used to check the maps derived from them, <strong>and</strong> to confirm that nosubsequent changes in coastal configuration had been incorporated in the maps. Three additional airphotograph runs, <strong>of</strong> 1961, 1971 <strong>and</strong> 1991 were also consulted. Three sets <strong>of</strong> satellite imagery wereexamined, but only the most recent (1997) data set proved to be <strong>of</strong> value in making semi-quantitativeassessments <strong>of</strong> coastline changes, because <strong>of</strong> inferior resolution <strong>and</strong> poor definition <strong>of</strong> subtlechanges in coastal features in the earlier imagery.<strong>The</strong> Figure summarizes coastal changes between 1941 <strong>and</strong> 1980. Erosion has led to coastalrecession, amounting to nearly half a kilometre in some places, in the last fifty years. In the vicinity<strong>of</strong> Milk River, coastal changes have been more complex, with periods <strong>of</strong> accretion alternating withtimes <strong>of</strong> erosion. In particular the spit at the mouth <strong>of</strong> Milk River has shown spectacular, rapidchanges in size <strong>and</strong> shape.Maps produced before the advent <strong>of</strong> aerial photography <strong>and</strong> geodetic control suffer from a number<strong>of</strong> defects, including distortion <strong>and</strong> scale changes arising from survey errors <strong>and</strong> lack <strong>of</strong> integration<strong>of</strong> different parts <strong>of</strong> the same map. <strong>The</strong> Robertson map for this area, compiled about 1804 (e.g. inHigman, 1988), <strong>and</strong> the inch to a mile Parish map, dating from early this century, were consulted.<strong>The</strong> coastline shown on the Parish map, adjusted for scale errors, has been added to Figure 1. <strong>The</strong>Robertson map (Fig. 1, 4) shows major differences in the orientation <strong>of</strong> the mouth <strong>of</strong> the RioMinho, confirmed by examination <strong>of</strong> ab<strong>and</strong>oned river channels, visible on some photographs.<strong>The</strong> cause <strong>of</strong> recession has not yet been ascertained, but the time period involved would appear to betoo long for it to have been due, for example, to s<strong>and</strong> removal from the bed <strong>of</strong> the Rio Minho,probably the main sediment source for these beaches. S<strong>and</strong> mining was relatively unimportant in the1940s <strong>and</strong> 50s, <strong>and</strong> may be only one <strong>of</strong> a variety <strong>of</strong> factors, such as sediment supply, storm damage,<strong>and</strong> sea level change. On a global scale, coastlines are dominated by recession at the present day(Bird, 1985; Pilkey, 1991), probably in response to a slowly rising sea level.Before the current recession phase, this stretch <strong>of</strong> coastline had been prograding seawards from alow cliff cut into the Rio Minho alluvial fan, as indicated by a well-developed beach ridge system<strong>and</strong> associated morass. <strong>The</strong> cliff itself is evidence <strong>of</strong> an even earlier period <strong>of</strong> coastal erosion.Incidental to the coastline study was the identification, on several aerial photographs, dating back as far as1953, <strong>of</strong> significant volumes <strong>of</strong> effluent being released into the sea between Carlisle Bay <strong>and</strong> the RioMinho, apparently originating near the Monymusk factory.ReferencesBird, E.C.F. (1985). Coastline changes - a global review. John Wiley, 219 p.Higman, B.W. (1988). Jamaica Surveyed. Institute <strong>of</strong> Jamaica, 307 p.Pilkey, O.H. (1991). Coastal erosion. Episodes, 14, 46-51.Wood, P.A. (1976). Beaches <strong>of</strong> accretion <strong>and</strong> progradation in Jamaica. Journal <strong>of</strong> the GeologicalSociety <strong>of</strong> Jamaica, 15, 24-31.89


P-26 JUPITER LANDSLIDE, RIO GRANDE VALLEY, JAMAICA:A LARGE PREHISTORIC SLIDE DAMDionne V. Laughton <strong>and</strong> *Edward RobinsonMines <strong>and</strong> Geology Division, Kingston;*<strong>Department</strong> <strong>of</strong> Geography <strong>and</strong> Geology, Mona<strong>The</strong>re is geological evidence for a number <strong>of</strong> large l<strong>and</strong>slide events that have taken place in the RioGr<strong>and</strong>e valley, Portl<strong>and</strong> parish, Jamaica. One <strong>of</strong> these, at Millbank, occurred in 1937, causingseveral deaths <strong>and</strong> creating a dam with the debris, flooding the valley <strong>and</strong> forming a lake whichremained in existence for about six months. Just downstream from Millbank the remains <strong>of</strong> a muchlarger l<strong>and</strong>slide deposit were identified at Jupiter. <strong>The</strong>re is no confirmed historical record <strong>of</strong> thisslide event <strong>and</strong> it is presumed to be prehistoric, although its morphology has undergone very littlemodification (Robinson <strong>and</strong> Laughton, 1997). However, a historical record is possible (Robinson etal., 1996).An attempt to cut a new highway over the debris, <strong>and</strong> the effects <strong>of</strong> the January 1998 flood rains inthe area have revealed extensive new exposures, confirming that the slide originated from the scarp<strong>of</strong> the John Crow Mountains, <strong>and</strong> that the slide debris extends over the river channel <strong>and</strong> across tothe southwestern side <strong>of</strong> the valley. <strong>The</strong> debris covers an area <strong>of</strong> some four km 2 , <strong>and</strong> may be theresult <strong>of</strong> more than one slide event. <strong>The</strong> debris mound in the valley floor rises about 52 m above thepresent river bed, the river having cut a path through the mound on its northeastern side Figure). (Assuming that the highest point <strong>of</strong> the debris mound (174 m) represents the original height <strong>of</strong> themound <strong>and</strong> that it formed a temporary natural dam, the extent <strong>of</strong> the impounded lake is estimated tobe about 155 hectares. <strong>The</strong> valley floor <strong>of</strong> the Rio Gr<strong>and</strong>e above the slide site is flat <strong>and</strong> coveredwith extensive alluvial deposits. Its extent approximately coincides with the area enclosed by the174m contour, suggesting that the alluvial flat may have formed by sediment deposition behind thedam.ReferencesRobinson, E., Ahmad, R., Phillip-Jordan, C. <strong>and</strong> Armstrong, M. 1996. <strong>The</strong> Burlington l<strong>and</strong>slide,mouth <strong>of</strong> the Rio Gr<strong>and</strong>e, Jamaica: example <strong>of</strong> an ancient slide dam? Journal <strong>of</strong> the GeologicalSociety <strong>of</strong> Jamaica, 31, 37-42.Robinson, E. <strong>and</strong> Laughton, D.V. 1997. Burlington <strong>and</strong> Jupiter l<strong>and</strong>slides, Rio Gr<strong>and</strong>e valley,Jamaica: comparison with Millbank l<strong>and</strong>slide as examples <strong>of</strong> processes producing natural dams.In Ahmad, R. (ed) Proceedings <strong>of</strong> the Second Caribbean Conference on Natural Hazards <strong>and</strong>Disasters, Kingston, 9-12 October, 1996, 56-61.91


Figure:Map showing present extent <strong>of</strong> debris from the Jupiter l<strong>and</strong>slide (solid line) <strong>and</strong>the area within which a temporary lake may have been impounded, marked bythe 174 m contour (dash <strong>and</strong> dot line). Alluvial flat is shown by dotted line.92


P-27 BIOSTRATIGRAPHIC INVESTIGATION OF SPECIES OFTHE LARGER FORAMINIFERAL SPECIES CUSHMANIASILVESTRI IN EOCENE ROCKS, JAMAICAGeorgette D’Aguilar <strong>and</strong> Edward Robinson<strong>Department</strong> <strong>of</strong> Geography <strong>and</strong> Geology, MonaCushmania Silvestri is one <strong>of</strong> a group <strong>of</strong> fossil larger foraminifera (Phylum Protista) characterizedby a conical shell, sometimes reaching 4 mm in diameter, with a complex internal skeleton. <strong>The</strong> test(shell) is made up <strong>of</strong> a stack <strong>of</strong> saucer-shaped chambers that increase gradually in size from aspherical proloculus (first formed chamber) at the apex <strong>of</strong> the cone. Internally the chambers aresupported by a variety <strong>of</strong> pillars <strong>and</strong> small partitions (Figure). <strong>The</strong> group <strong>of</strong> conical forms includingCushmania were globally distributed in tropical regions throughout the Cretaceous <strong>and</strong> EarlyCenozoic periods, but are now extinct.Cushmania itself has been recorded from sedimentary rocks <strong>of</strong> early to late Eocene age (51 to 37million years ago) <strong>and</strong> appears to have been restricted to southern North America <strong>and</strong> the Caribbeanregion. It has potential use as a guide fossil for some <strong>of</strong> the very shallow marine paleoenvironmentsthat are recorded from the Caribbean Eocene, <strong>and</strong> which are difficult to date biostratigraphically.Three species <strong>of</strong> Cushmania have been erected, with type localities in St. Bartholomew, Haiti <strong>and</strong>Jamaica. <strong>The</strong>y are supposedly distinguished by differences in the size <strong>and</strong> shape <strong>of</strong> the test, <strong>and</strong>differences in the density <strong>and</strong> number <strong>of</strong> internal structures (Hottinger & Drobne, 1980). However,the original descriptions are inadequate, <strong>and</strong> previous workers have frequently regarded the genus asmonospecific (Cole, 1956).<strong>The</strong> purpose <strong>of</strong> this study is to use fossil material from the Jamaican Eocene, as well as from the typelocalities mentioned above, to examine the variation which exists among populations <strong>of</strong> Cushmania, todetermine if more than one species is present. In addition the study seeks to determine to what extentdifferences in population characteristics may be related to differences in stratigraphical horizon <strong>and</strong>/orpaleoenvironment <strong>of</strong> the samples collected.ReferencesCole, W.S. (1956). Jamaican larger forminifera. Bulletins <strong>of</strong> American Paleontology, 36: 205-233.Hottinger, L., & Drobne, K. (1980). Early Tertiary conical imperforate. Rasprave IV. razr. SAZU 22:188-276.Robinson, E., And Wright, R. M. (1993). Jamaican Paleogene larger foraminifera. In Wright, R. M.,<strong>and</strong> Robinson, E., eds., Biostratigraphy <strong>of</strong> Jamaica: Geological Society <strong>of</strong> America, Inc., 283 – 245.93


Figure:External view <strong>of</strong> Cushmania americana (a – c):(a) lateral, showing conical shape(b) apical, showing symmetrical position <strong>of</strong> the proloculus(c) basal, illustrating the apertural face(d) cross section <strong>of</strong> (a) showing internal structure <strong>of</strong> the organism(after Robinson & Wright, 1993)94


P-28 EVALUATION OF MEDIA, METHODS OF CULTURE ANDFERTILIZER FOR THE COMMERCIAL CULTIVATION OFANTHURIUMS IN JAMAICATai Chun, Paulette, Potluri , Sasikala D.P. <strong>and</strong> Devi Prasad, P.V.<strong>Department</strong> <strong>of</strong> Life Sciences, Mona<strong>The</strong> once thriving Anthurium industry in Jamaica has in recent years been beset by problems withdisease <strong>and</strong> low productivity. This study, therefore, focused on the evaluation <strong>of</strong> methods to reducethe incidence <strong>of</strong> disease <strong>and</strong> increase plant productivity by the manipulation <strong>of</strong> nutritional <strong>and</strong>environmental factors. Four media - coconut husk, brick chips, gravel <strong>and</strong> basalt igneous rock -were evaluated using two methods <strong>of</strong> culture, viz. beds <strong>and</strong> pots, at three levels <strong>of</strong> fertiliser - 244,448 <strong>and</strong> 896 kg N ha -1 yr -1 . <strong>The</strong> plants in the pots were cultivated at double the planbting density <strong>of</strong>the beds. Increasing levels <strong>of</strong> fertilizer resulted in an increase in growth for the plants in beds butdecreased growth in pot cultures. Overall production increased quadratically in response t<strong>of</strong>ertilizer. Bloom size <strong>and</strong> stsem leangth increased linearly with the application <strong>of</strong> additionalamounts <strong>of</strong> fertilizer for the plants in beds but decreased for the plants in pots. <strong>The</strong> production <strong>of</strong>hifgher priced export quality blooms improved at the higher fertilizer levels <strong>and</strong> was also greater forthe plants in bed culturea. <strong>The</strong> plants cultivated in coconut husk gave the best performance ingrowth, production, export qualtiy <strong>and</strong> in the percentages <strong>of</strong> larger sized <strong>and</strong> higher priced blooms.Production in the beds was significantly higher than the plants in pots. This culture method alsoresultsed in the produdction <strong>of</strong> larger sized <strong>and</strong> export quality blooms. However, the increasedplanting density <strong>of</strong> the pots resulted in a significantly greater production per square meter than thebeds.Overall best performance was obtained from the plants in coconut husk followed by the plants inbrick chips with little difference being observed for gravel <strong>and</strong> basalt igneous rock. Leaf tissueanalysis indicated margainally higher levels <strong>of</strong> nitrogen <strong>and</strong> potassium <strong>and</strong> significantly higher levelspf phosphorus in the leaf tissue <strong>of</strong> the plants cultivated in coconut husk.P-29 SHOOT TIP MICROGRAFTING FOR OBTAININGVIRUS FREE CITRUS PLANTSPotluri, Sasikala D.P.,<strong>Department</strong> <strong>of</strong> Life Sciences, MonaCitrus Industry in Jamaica has been in recent times severely affected by various diseases, especiallyby the Citrus Tristeza Virus [CTV]. Trees with sour orange rootstocks are highly susceptible for theinfection <strong>of</strong> this virus. <strong>The</strong> traditional way <strong>of</strong> obtaining the planting material for citrus industry bygrafting <strong>and</strong> budding cannot get rid <strong>of</strong> the virus in the planting material easily. Tissue culturetechniques are very useful under these conditions. Shoot tip / apical meristem culture has been usedextensively to obtain pathogen free planting material. Usually this requires thermo-therapy [heattreatment] <strong>and</strong> not all the plants can withst<strong>and</strong> this. In recent years, shoot tip grafting in tissueculture plants has been developed to overcome this. In the present work, shoot tip micrografting hasbeen studied to determine the suitability <strong>of</strong> this method for obtaining plantlets.95


<strong>The</strong> method involved the removal <strong>of</strong> a shoot tip [0.1to 1.0mm] from a certified budwood source.Seeds <strong>of</strong> the desired rootstocks were germinated <strong>and</strong> the embryos grown in vitro. After two weeks<strong>of</strong> growth <strong>of</strong> the root stock plants in the tubes, the tips were removed under aseptic conditions <strong>and</strong>the excised shoot tip from the budwood was grafted. <strong>The</strong>se grafts were allowed to grow for four tosix weeks.This technique was successful <strong>and</strong> would be very useful to recover plants free <strong>of</strong> all the viruses incitrus. This technique will be also useful in other tree crops.P-30 TISSUE CULTURE TECHNIQUES FOR THEMICROPROPAGATION OF BLIGHIA SAPIDA [ACKEE]Mills, Erica , Devi Prasad, P.V. <strong>and</strong> Potluri, Sasikala D.P.<strong>Department</strong> <strong>of</strong> Life Sciences, MonaAckee [Blighia sapida Koenig] is an important tree crop in Jamaica. It is one <strong>of</strong> the majorconstituents <strong>of</strong> Jamaican National dish. In addition, it has an export potential <strong>of</strong> about $15 million ayear to North America <strong>and</strong> Canada. If the existing restrictions are lifted <strong>and</strong> when a free flow isallowed, the export potential increases significantly. Ackee is not an orchard crop yet in Jamaica inspite <strong>of</strong> its importance to the economy. Very little research has been carried out on the tree itself,while important work was carried out on the hypoglycine content <strong>and</strong> its poisonous effects onhumans. Information on the cultural practices <strong>and</strong> propagation <strong>of</strong> ackee is very limited. <strong>The</strong>re is awide variation in the types <strong>of</strong> ackee available. This is mainly because <strong>of</strong> the natural propagationby seed , which is subject to variation. Rooting <strong>of</strong> cuttings <strong>and</strong> some grafting have beenexperimented with some success [Stair, 1992].No work has been carried out on the tissue culture propagtion <strong>of</strong> ackee so far. Hence the presentproject was undertaken to develop tissue culture methods for the micropropagarion <strong>of</strong> Ackee, Thiswould be beneficial in producing uniform planting material. Various explant sources have been used- leaf, axillary buds, cotyledons, embryo <strong>and</strong> aril tissue. For all the treatments, MS medium wasused as a basal medium with various additions <strong>of</strong> growth substances. <strong>The</strong>se included 2,4-D, BA <strong>and</strong>NAA. 2,4-D was used at three different concentrations -1mg, 5mg <strong>and</strong> 10mg -1 L; NAA was usedat three different levels - 0.1mg, 1.0mg <strong>and</strong> 3.0mg L -1 ; <strong>and</strong> BA was also used at three different levels- 1, 3 <strong>and</strong> 5mg L -1 . <strong>The</strong>se growth substances were used individually <strong>and</strong> in combination with eachother . <strong>The</strong> leaf tissue showed callus formation after about 6-7 weeks in the medium containing2,4-D at 5 <strong>and</strong> 10mg L -1individually or when combined with low concentrations <strong>of</strong> NAA <strong>and</strong> BA.<strong>The</strong> callus was not embryogenic. Axillary buds were slow in responding to any treatment but didrespond to BA[3mg] + NAA[1mg]. <strong>The</strong> Aril tissue did not show much response to any treatmentswhile the cotyledons showed some signs <strong>of</strong> callus formation.. Both the cotyledons <strong>and</strong> the embryotissue showed the initiation <strong>of</strong> direct organogenesis in all combinations <strong>of</strong> BA <strong>and</strong> NAA withhighest results obtained in the combination <strong>of</strong> 1mg each <strong>of</strong> BA <strong>and</strong> NAA.<strong>The</strong>se results indicate that there is a regeneration potential for various tissues <strong>of</strong> Ackee to be used intissue culture, unlike some tree crops.96


P-31 PHYSIOLOGICAL ECOLOGY OF TEN PHYCOCOLLOIDPRODUCING MARINE ALGAE FROM THE ENVIRONSOF KINGSTON AND PORT ROYALLittau, Jonathan H. <strong>and</strong> Devi Prasad, P.V.<strong>Department</strong> <strong>of</strong> Life Sciences, MonaJamaican coastline has several species <strong>of</strong> agar producing seaweeds, some <strong>of</strong> which are harvested asIrish moss. Most <strong>of</strong> the harvest is from natural sources, which makes it important to manage thisnatural resource. A basic underst<strong>and</strong>ing <strong>of</strong> the environmental factors to which Jamaicanphycocolloid producing species are exposed <strong>and</strong> the physiological reactions to these changes wouldbe very useful to determine the species, which are worth further investigation for mariculturepurposes <strong>and</strong>/or coastal resource management. <strong>The</strong> present work was undertaken to study thephysiological ecology <strong>of</strong> ten agar-producing seaweeds from seven different stations around theenvirons <strong>of</strong> Kingston <strong>and</strong> Port Royal. <strong>The</strong> stations for collection were selected from Palisadoes inthe east to the great salt pond in the west, Drunkenmans cay in the south <strong>and</strong> the Port Royal MarineLab in the North. <strong>The</strong>se stations were 1. <strong>The</strong> lighthouse station [LHS], 2.<strong>The</strong> Port Royal MarineLab [PRML], 3. <strong>The</strong> great salt pond [GS], 4. <strong>The</strong> Nago Head station [NH], 5. Drunkenmans cay[DC], 6. <strong>The</strong> lime cay station [LC] <strong>and</strong> 7. <strong>The</strong> Port Royal South Station [PRS]. Following specieswere included in the study based on our preliminary investigations as to their occurrence in theselocalities. 1. Polycavernosa debilis[Gracilaria debilis or Gracilaria cornea or Hydropuntiadebilis], 2. G.mammilaris, 3. G. cylindrica, 4. G. verrucosa, 5. G. sjoestidii, 6. G. ‘terete’ , 7. G.cervicornis, 8. G. domingensis, 9. Agardhiella tenera <strong>and</strong> 10. Gelidiella acerosa. It was observedthat increase in protein levels was positively correlated to nutrient levels while there was an inverserelationship between protein content <strong>and</strong> nutrient levels. Carbohydrate content appears to beinversely related to protein <strong>and</strong> highest levels were obtained during the summer months.Carbohydrate levels in species with high surface area to volume ratios like those with a flattenedmorphology [G.domingensis] or a narrow cross section [G. sjoestidii] were found to be positivelycorrelated to salinity. Agar yields ranged from 16 to 66% these <strong>and</strong> other results will be discussedin relation to the suitability <strong>of</strong> various species for mariculture <strong>and</strong> general coastal plant ecology.P-32 MARICULTURE OF GRACILARIA SP. USINGTANK CULTURE METHODSLittau, Jonathan H. <strong>and</strong> Devi Prasad, P.V.<strong>Department</strong> <strong>of</strong> Life Sciences, MonaSpecies <strong>of</strong> Gracilaria , popularly known as ‘Irish Moss’ in Jamaica <strong>and</strong> sea moss elsewhere in theCaribbean, are also a good source <strong>of</strong> agar. <strong>The</strong> dem<strong>and</strong> for Irish moss outstrips the supply fromnatural sources. Traditional rope culture methods have been tried in Jamaica <strong>and</strong> other Caribbeancountries. This was more successful in St. Lucia. However, In Jamaica, the areas suitable for openIrish moss culture are also suitable for development as tourist areas. In addition rope culture haslimitations in terms <strong>of</strong> nutrient supply <strong>and</strong> the control <strong>of</strong> epiphytes. Also, the incidents <strong>of</strong> theft <strong>and</strong>praedial larceny also are a limiting factor. Hence an alternative method is needed to over come some<strong>of</strong> these problems. A tank culture method was studied as a suitable alternative for the mariculture<strong>of</strong> species <strong>of</strong> Gracilaria in Jamaica. Initially, experiments were carried out in small aquarium tanksin the lab. Based on the results obtained a series <strong>of</strong> tanks were set up outdoors with running seawater<strong>and</strong> aeration.97


Species studied include Gracilaria mammilaris, G. cylindrica, G. verrucosa, G. ‘terete’, <strong>and</strong>Polycavernosa debilis [also called Gracilaria debilis or Hydropuntia debilis ]. Following factorswere studied: Effect <strong>of</strong> running seawater verses static conditions <strong>and</strong> once per week change <strong>of</strong> water;Effects <strong>of</strong> nitrogen nutrition – pulse feeding verses flow through <strong>and</strong> static conditions; effects <strong>of</strong>light <strong>and</strong> temperature. Growth rates <strong>and</strong> chemical composition <strong>of</strong> the algae in response to the abovefactors were studied. Temperatures above 28 o C were found to be detrimental to many species,fragmenting the algae <strong>and</strong> reducing the agar content. Running seawater was found not to benecessary <strong>and</strong> once per week change was observed to be beneficial, giving growth rates <strong>of</strong> up to9.8% day -1 in G. verrucosa. This has also reduced epiphyte growth significantly compared torunning seawater. Pulse feeding was observed to be the best method <strong>of</strong> supplying nutrients to thecultures. Based on these <strong>and</strong> other results, tank culture system for mariculture <strong>of</strong> several species <strong>of</strong>Gracilaria is very promising <strong>and</strong> economically feasible. This method uses much less space thanrope method, can be easily protected, can be better controlled for nutrient supply <strong>and</strong> epiphytecontrol <strong>and</strong> can be set up in places which do not compete for tourist beach development.P-33 AGRONOMIC AND MOLECULAR CHARACTERIZATION OFJAMAICAN PHASEOLUS VULGARIS LANDRACESWinston A. Young <strong>and</strong> Wayne .A. McLaughlin<strong>Department</strong> <strong>of</strong> Basic Medical Sciences (Biochemistry) <strong>and</strong> <strong>The</strong> Biotechnology Centre, MonaRed kidney beans (Phaseolus vulgaris) are affected by some major diseases, Bean Golden Mosaicvirus (BGMV), Rust (Uromyces appendiculatus) <strong>and</strong> Common Bacterial Blight (CBB), which canlead to up to 100% crop loss (1). Some Jamaican l<strong>and</strong>races <strong>of</strong> the kidney bean show some level <strong>of</strong>tolerance to the pathovars <strong>of</strong> diseases (2). L<strong>and</strong>races have proven to be a significant genepool in theimprovement <strong>of</strong> a crop.Phaseolus vulgaris l<strong>and</strong>races <strong>of</strong> Jamaica are divided into three groups based on traditional morphoagronomicmethods <strong>of</strong> characterization. Seeds <strong>of</strong> these l<strong>and</strong>races were collected from the majorbean growing parishes <strong>of</strong> the isl<strong>and</strong> in 1994 <strong>and</strong> continued over three successive growing seasons.<strong>The</strong> seeds were sorted into twenty-seven accessions divided among the three major groups <strong>and</strong> afourth unassigned group based on their seed morphology. <strong>The</strong> accessions were propagated initiallythrough single seed descent, followed by single pod bulking to produce seed stock <strong>of</strong> plants that aretrue breeding, <strong>and</strong> to evaluate the agronomic characteristics <strong>of</strong> each accession.<strong>The</strong> genetic relationship between the 27 accessions was done usingthe RAPD (R<strong>and</strong>om Amplified Polymorphic DNA) PCR-based markersystem (3). Five primers were used in this screening process <strong>and</strong>produced molecular markers sufficient to differentiate the majormorpho-agronomic groups. In addition genetic variation withinthe morpho-agronomic groups were revealed indicating that thegroups were not completely homogeneous.References1. Beecher, C.P. 1994. Genetic <strong>and</strong> Morpho-Agronomic Characterization <strong>of</strong> New Lines <strong>of</strong>red Kidney Beans. MPhil. <strong>The</strong>sis, UWI, Mona.98


2. Stavely, J.R., Steadman, J.R. 1992. An Overview <strong>of</strong> the Rust Problem <strong>and</strong> Potential forControl. BIC. 35: 7-8.3. Kang, F.Y., Allen, V. D., Pauls, K.P. 1993. R<strong>and</strong>om amplified polymorphic DNA analysis.In Methods in Plant Molecular Biology <strong>and</strong> Biotechnology. CRC Press Inc.P-34 THE USE OF NURSERY PROTECTION AND PLANTGROWTH PROMOTING RHIZOBACTERIA TO REDUCEGEMINIVIRUS INFECTION IN TOMATO SEEDLINGSJodi Spence <strong>and</strong> Wayne McLaughlin<strong>Department</strong> <strong>of</strong> Basic Medical Sciences (Biochemistry) <strong>and</strong> <strong>The</strong> Biotechnology Centre, MonaTomato yellow leaf curl virus (TYLCV) is the most devastating disease <strong>of</strong> tomato world-wide <strong>and</strong>can result in 100% crop loss (1). Tomato yellow leaf curl virus is transmitted by the whiteflyBemisia tabaci. To reduce TYLCV infection caused by whiteflies on tomato seedlings theeffectiveness <strong>of</strong> eight nursery protection strategies were evaluated. Field trials were conducted overtwo planting seasons in 1997 <strong>and</strong> 1998 at the Bodles Agricultural Research Station, in St. Catherine<strong>and</strong> at CARDI (Caribbean Agricultural Research <strong>and</strong> Development Institute) at Mona. Fourcommercial tomato varieties, Gem Star, Gem Pride, UC82 <strong>and</strong> Castle Rock were used. Gem Star<strong>and</strong> Gem Pride varieties were recently developed by Peto Seed Co. USA, <strong>and</strong> are claimed to beresistant to geminivirus, where as UC82 <strong>and</strong> Castle Rock are susceptible to geminivirus. Gem Star,Gem Pride <strong>and</strong> Castle Rock tomato varieties were evaluated at Bodles, while Gem Star, Gem Pride<strong>and</strong> UC 82 tomato varieties were evaluated at CARDI.Treatments were <strong>applied</strong> during a six-week nursery period after which leaf samples were taken <strong>and</strong> theseedlings transplanted. DNA extracted from the leaf samples was tested for the presence <strong>of</strong> the virus byDNA hybridisation with a TYLCV-specific intergenic DNA probe. <strong>The</strong> transplants were monitored in thefield for development <strong>of</strong> disease symptoms up until fruiting. Only one treatment, the use <strong>of</strong> the insecticidePegasus 500 (diafenthiuron) was shown to be effective in reducing TYLCV transmission by whiteflies inthe plants up to ten weeks old.<strong>The</strong>re was also a significantly lower disease incidence in Gem Star <strong>and</strong> Gem Pride tomato varieties. GemPride tomato showed no disease symptoms up to the end <strong>of</strong> the experimental period, whereas, Gem Starshowed slight leaf curling 13 weeks after transplanting. Geminivirus DNA was detected in Gem Startomato variety but not in Gem Pride. <strong>The</strong>se results suggest that Gem Star is a tolerant variety as symptomexpression was suppressed, whereas Gem Pride is a resistant variety because replication <strong>of</strong> the virus wasinhibited.Currently, several strains <strong>of</strong> plant growth promoting rhizobacteria (PGPR) are being tested to evaluatetheir effectiveness to induce systemic resistance (ISR) to TYLCV <strong>and</strong> promoting the growth <strong>of</strong> tomatoseedlings.Reference(1) Czosnek, H. <strong>and</strong> Laterrot, H. 1997. A worldwide survey <strong>of</strong> tomato yellow leaf curlviruses. Arch. Virology 142: 1391-1406.99


P-35 CHARACTERISATION OF EXTRACELLULAR ENZYMES ANDEXOPOLYSACCHARIDES PRODUCED BY XANTHOMONASCAMPESTRIS PV PHASEOLI AND SOME STUDIES OF THEIR ROLEIN COMMON BLIGHT DISEASE IN BEANSEustace B. Smith <strong>and</strong> Wayne McLaughlin<strong>Department</strong> <strong>of</strong> Basic Medical Sciences (Biochemistry) <strong>and</strong> <strong>The</strong> Biotechnology Centre, Mona<strong>The</strong> relationship between the intrinsic levels <strong>of</strong> the extracellular enzymes protease, amylase, phosphatases,<strong>and</strong> extracellular polysaccharides (EPS) in Xanthomonas campestris pv. phaseoli phaseoli (X. c. pv.phaseoli) strains <strong>and</strong> pathogenesis on three cultivars <strong>of</strong> Phaseolus vulgaris L. were examined. Ourresults showed that there was no correlation between disease symptom development (virulence) <strong>and</strong> highlevels <strong>of</strong> extracellular enzyme activity <strong>and</strong> EPS production in X. c. pv phaseoli strains.Protease <strong>and</strong> amylase from two pathogenic strains, X. c. pv. phaseoli strain V4S1 <strong>and</strong> X. c. pv. phaseolifuscans strain EK-11, <strong>and</strong> an epiphytic non pathogenic strain 395-86 were partially purified <strong>and</strong>characterised. Enzyme inhibitor studies indicated that proteolytic enzymes from the three X. c. pv.phaseoli strains were metalloenzymes, their different reactions to metal chelators indicated that theseenzymes were different. Proteolytic enzyme from strain V4S1 was a zinc metalloprotein <strong>and</strong> had a similarβ-casein digestion pattern with protease PRT3 from X. c. pv campestris (Dow et al. 1993). Amylolyticactivities from all three X. c. pv. phaseoli strains reacted differently to enzyme inhibitors indicating thatthey were different enzymes.HPLC <strong>of</strong> the starch digestion products along with the iodine blue value <strong>and</strong> reducing sugar curves indicatethat the amylase is an α- amylase. <strong>The</strong> temperature optimum for protease activity from X. c. pv. phaseolistrains V4S1, X. c. pv. phaseoli fuscans strain EK-11, <strong>and</strong> epiphytic strain 395-86 were 37 0 C, 37 0 C, <strong>and</strong>42 0 C, respectively. <strong>The</strong> optimum temperature for all three amylolytic activity was 42 0 C. <strong>The</strong> pHoptimum for proteolytic activity <strong>and</strong> amylolytic activities were pH 6.0 <strong>and</strong> pH 6.5, respectively.Chemical mutagenesis <strong>of</strong> X. c. pv. phaseoli strain V4S1 using NTG <strong>and</strong> EMS produced two types <strong>of</strong>EPS - mutants, three Amȳ Prot - mutants (lacking both amylolytic <strong>and</strong> proteolytic activities) <strong>and</strong> one Amy++Prot ++ mutant (high levels <strong>of</strong> amylase <strong>and</strong> protease). One EPS - <strong>and</strong> all the Amȳ Prot - mutants wereavirulent. <strong>The</strong> second EPS - mutant <strong>and</strong> the Amy ++ Prot ++ mutants were virulent. <strong>The</strong> growth rates <strong>of</strong> X. c.pv. phaseoli V4S1 wild type <strong>and</strong> mutants were evaluated in broth culture <strong>and</strong> on the leaf surface. <strong>The</strong>growth rates <strong>of</strong> the wild type <strong>and</strong> avirulent mutants were similar in broth culture, however the avirulentmutant failed to multiply on the leaf surface. Revertants <strong>of</strong> Amy - Prot - mutants produced reducedamounts <strong>of</strong> the amylase <strong>and</strong> protease enzymes <strong>and</strong> were avirulent indicating that both the type <strong>and</strong>quantity <strong>of</strong> extracellular enzymes could be important for pathogenicity. Similarly, the ability toeffectively colonise the leaf surface appears to be important in establishing pathogenicity.ReferenceDow, J. M., M. J. Fan, M. A. Newman <strong>and</strong> M. .J. Daniels. 1993. Differential expression <strong>of</strong> conservedprotease genes in crucifer-attacking pathovars <strong>of</strong> Xanthomonas campestris. Appl. Env. Microbiol. 59:3996-4003.100


P-36 IDENTIFICATION, DISTRIBUTION, ESTERASE AND 16SRRNA SEQUENCE POLYMORPHISMS OF WHITEFLIESIN JAMAICAS. Brown, I. Torrez Jerez 1 , W. McLaughlin, <strong>and</strong> J. K. Brown 1<strong>Department</strong> <strong>of</strong> Basic Medical Sciences (Biochemistry) <strong>and</strong> <strong>The</strong> Biotechnology Centre, Mona;1<strong>Department</strong> <strong>of</strong> Plant Sciences, University <strong>of</strong> ArizonaNon specific esterases were used to differentiate four whitefly species <strong>and</strong> also confirm the presence<strong>of</strong> the B-biotype <strong>of</strong> Bemisia tabaci in Jamaica. Esterase b<strong>and</strong>ing patterns were analysed by nativepolyacrylamide gel electrophoresis (PAGE). B<strong>and</strong>ing patterns <strong>of</strong> over two hundred <strong>and</strong> sixteen B.tabaci adults from 27 populations in Jamaica matched the B-type esterase b<strong>and</strong>ing pattern producedby the B-biotype st<strong>and</strong>ard from Arizona. B<strong>and</strong>ing patterns representative <strong>of</strong> two non-B biotypes <strong>of</strong>B. tabaci were also identified. Eighty-six percent (86%) <strong>of</strong> the plants that were sampled in Jamaicawere hosts <strong>of</strong> the B-biotype <strong>of</strong> B. tabaci. Select whitefly populations that were typed as B <strong>and</strong> non-B biotypes were subjected to molecular analysis <strong>of</strong> a fragment <strong>of</strong> the 16S rRNA gene as well as thecytochrome oxidase II protein coding gene. Maximum parsimony analysis <strong>of</strong> the sequences obtainedfrom CV3-CV4 region <strong>of</strong> the 16S gene indicated that the B-biotype <strong>of</strong> B. tabaci found in Jamaica is<strong>of</strong> Old World Origin <strong>and</strong> the non-B biotypes are <strong>of</strong> New World origin. Geminivirus was confirmedonly in the B-biotype <strong>of</strong> B. tabaci.P-37 GENETIC DIVERSITY IN DASHEENS (COLOCASIA SP.) ANDCOCOYAMS (XANTHOSOMA SP.) GROWN IN JAMAICABrown, V. M. D.; Asemota, H. N.; Thangavelu*, M. <strong>and</strong> Mantel*, S. H.<strong>Department</strong> <strong>of</strong> Basic Medical Sciences (Biochemistry) <strong>and</strong> <strong>The</strong> Biotechnology Centre, Mona;*Wye College, University <strong>of</strong> LondonTropical tuber crops such as Alocasia sp., dasheen (Colocasia sp.) <strong>and</strong> cocoyam (Xanthosoma sp.)are important sources <strong>of</strong> dietary starch. Approximately 57 million tons <strong>of</strong> cocoyam <strong>and</strong> 40 milliontons <strong>of</strong> dasheen were produced in 1995 (FAO, 1995). Although there is an increase in the quantity<strong>of</strong> dasheen <strong>and</strong> cocoyam produced, very little is known about the taxonomic groupings within thespecies <strong>and</strong> sub-species levels <strong>and</strong> even less about the cultivated varieties for these two plants.Using 17 accessions <strong>of</strong> cocoyam <strong>and</strong> 18 accessions <strong>of</strong> dasheen collected r<strong>and</strong>omly from 14 farms in8 parishes <strong>of</strong> Jamaica, PCR-based analyses were carried out to assess the genetic diversity within<strong>and</strong> between species <strong>of</strong> Colocasia <strong>and</strong> Xanthosoma, <strong>and</strong> to develop markers linked to importanttraits, useful for the assessment <strong>and</strong> control <strong>of</strong> bacterial infections. RAPD analyses using selectedr<strong>and</strong>om 10-mer primers <strong>and</strong> the 3’-anchored microsatellite primer, -(CA) 8RY-, revealed groups <strong>of</strong>accessions that shared a similar <strong>and</strong> highly diverged amplification pr<strong>of</strong>iles in the collection <strong>of</strong>samples used. PCR-based analyses <strong>of</strong> mitochondrial sequence using NAD 4.2 - NAD 4.3 <strong>and</strong> rps14- COB <strong>and</strong> chloroplast sequence using trnL 03 - trnL 04 <strong>and</strong> trnR 01 - trnQ 01 revealedpolymorphism within plastid <strong>and</strong> mitochondrial genomes <strong>of</strong> Xanthosoma sp. <strong>and</strong> Colocasia sp. <strong>The</strong>absence <strong>of</strong> a NAD 4.2 - NAD 4.3 amplified fragment for Colocasia sp. indicates that it can be usedto differentiate between species <strong>of</strong> Xanthosoma <strong>and</strong> Colocasia. Restriction analysis <strong>of</strong> amplifiedfragments provides evidence that at least 2 accessions <strong>of</strong> Xanthosoma sp. <strong>and</strong> Colocasia sp. possess2 trnL sequences. This is unusual because plants only possess a single trnL sequence. Analysisalso revealed that there are at least 4 species <strong>of</strong> Xanthosoma <strong>and</strong> 2 species <strong>of</strong> Colocasia in Jamaica.101


Xanthosoma violaeceae <strong>and</strong> Colocasia esculenta were among the species identified. <strong>The</strong>re is alsoextensive varietal diversity within both species. <strong>The</strong>re are at least 4 groupings or varieties <strong>of</strong>Xanthosoma violaeceae <strong>and</strong> 3 varieties <strong>of</strong> Colocasia esculenta. <strong>The</strong>se results suggest that by usingone or more <strong>of</strong> these tools it should be possible to group accessions which have not previously beencharacterised <strong>and</strong> classified. <strong>The</strong>se observations are significant in the use <strong>of</strong> nucleic acids basedprocedures for germplasm collection, characterisation <strong>and</strong> management, the detection <strong>of</strong> viralpathogens in plants <strong>and</strong> the development <strong>of</strong> a comprehensive strategy for sustainable improvement <strong>of</strong>these crops.P-38 MOLECULAR ANALYSES OF BACTERIALPATHOGENICITY IN DASHEEN (COLOCASIA SP.) ANDCOCOYAM (XANTHOSOMA SP.) IN JAMAICABrown, V. M. D.; Asemota, H. N.; Mansfield*, J; Stevens*, C. A. <strong>and</strong> Mantel*, S. H.<strong>Department</strong> <strong>of</strong> Basic Medical Sciences (Biochemistry) <strong>and</strong> <strong>The</strong> Biotechnology Centre, Mona;*Wye College, University <strong>of</strong> LondonDasheen (Colocasia sp.) <strong>and</strong> cocoyam (Xanthosoma sp.) are economically important tropical tubercrops widely grown in many rural areas in Jamaica, essentially by traditional production methods.<strong>The</strong>se methods are problematic <strong>and</strong> associated with the transfer <strong>of</strong> pathogens from generation togeneration. <strong>The</strong>se pathogens are effective in areas <strong>of</strong> high rainfall <strong>and</strong> average temperatures <strong>of</strong> 20 -30 o C <strong>and</strong> can result in a 20 - 100% reduction in crop yield. In this study, samples <strong>of</strong> dasheen <strong>and</strong>cocoyams from different parishes in Jamaica were screened for bacterial pathogens with a view tounderst<strong>and</strong>ing the molecular basis <strong>of</strong> their pathogenesis for the purpose <strong>of</strong> engineering resistance.Pathogens identified included: Erwinia chrysanthemi pv. dieffenbachiae, Xanthomonas campestrispv. dieffenbachiae, Psuedomonas syringae <strong>and</strong> a Non-fluorescent Psuedomonads. <strong>The</strong> effects <strong>of</strong>X. campestris pv. Dieffenbiache, the causal agent <strong>of</strong> Common Leaf Blight on greenhouse growndasheen <strong>and</strong> cocoyam plants were further investigated at the molecular <strong>and</strong> physiological levels.Yellow spots that develop into water-soaked lesions appeared on the leaves. <strong>The</strong> lesions spread <strong>and</strong>coalesced to form extended chlorotic regions which frequently degenerated into holes on older leavesresulting in considerable dieback <strong>of</strong> the leaves. PCR analyses <strong>of</strong> the bacterial DNA revealed that itcontained sequences from the hrpB6, hrpC - hrpD <strong>and</strong> ORF1 - ORF2 <strong>of</strong> a pathogenicity gene <strong>of</strong> X.campestris pv. glycines. <strong>The</strong> hrp cluster <strong>of</strong> the gene is usually responsible for phytopathogenicinfection <strong>of</strong> X. campestris. <strong>The</strong>se genes are conserved within the genus (Todd et. al. 1990) <strong>and</strong> theirsequences were found to be homologous to similar hrp gene sequences from other Xanthomonas sp.<strong>The</strong>se genes are likely to be specific, they represent basic compatibility genes (Ellingboe, 1976,1982) <strong>and</strong> may be required for the disease symptom expression once the initial recognition eventshave occured.ReferencesEllingboe A. H. (1976). Genetics <strong>of</strong> host parasite interactions. In Encyclopaedia <strong>of</strong> PlantPhysiology, Vol 4: Physiological Plant Pathology (Ed by R. Heitefuss & P. H. Williams) pp761 - 778, Springer-Verlag, Berlin <strong>and</strong> New York.Ellingboe A. H. (1982). Genetic aspects <strong>of</strong> active defense. In: Wood RKS (ed.) Active defensemechanisms <strong>of</strong> plants. Plenum, New York, pp. 199 - 192.102


Todd G. A., Daniels M. J. <strong>and</strong> Callow J. A. (1990). Xanthomonas campestris pv. oryzae has DNAsequences containing genes is<strong>of</strong>unctional with Xanthomonas campestris pv. campestris genesrequired for pathogenicity. Physiol. And Mol. Plant Path. 36: 73 - 87.P-39 SECTIONAL INFLUENCE OF YAM (DIOSCOREACAYENENSIS) TUBERS USED FOR MINISETT ON SOMEBIOCHEMICAL PARAMETERS OF RESULTANT TUBERSAndrew O. Wheatley, Ose A. Iyare, Damian M. Glasgow, Helen N. Asemota,Phillip B. Grindley <strong>and</strong> Mohammed H. Ahmad<strong>Department</strong> <strong>of</strong> Basic Medical Sciences (Biochemistry) <strong>and</strong> <strong>The</strong> Biotechnology Centre, Mona<strong>The</strong> traditional method <strong>of</strong> producing yams is the planting <strong>of</strong> tuber pieces or minisetts. <strong>The</strong> yamtuber is known to vary in some biochemical parameters along the length <strong>of</strong> the tuber <strong>and</strong> this mayhave implication if this method is used for producing yams. <strong>The</strong> effect <strong>of</strong> the section <strong>of</strong> yam tuberfrom which minisetts are derived on some biochemical properties <strong>and</strong> nutrient content <strong>of</strong> theresulting harvested tubers was studied for round leaf yellow yam <strong>and</strong> black wiss yellow yam (D.cayenensis).<strong>The</strong> activities <strong>of</strong> some physiologically important enzymes such as polyphenol oxidase, invertase,peroxidase <strong>and</strong> acid phosphatase were found to be generally highest in tubers grown from middlederived minisetts. For polyphenol oxidase, middle derived tubers had the highest activity, followedby the tail derived tubers while the head minisett derived tubers had the least level <strong>of</strong> activity forboth the round leaf <strong>and</strong> black wiss yellow yam cultivars.<strong>The</strong> same trend was observed for peroxidase in the round leaf yellow yam, for black wiss the middlederived tuber had the highest activity, followed by tubers derived from the head with tubers from thetail region having the lowest enzyme activity. Invertase activity was highest for tubers derived frommiddle derived minisett, followed by tubers derived from the head with those derived from the tailshowing the least enzyme activity for both cultivars. For acid phosphatase the highest enzymeactivity was obtained from tubers derived from the middle minisett, followed by head derived tuberswhile the tail minisett derived tubers had the least level <strong>of</strong> activity for both cultivars.Highest starch content was found in tubers derived from middle section minisetts, followed by thetail minisett derived tubers while the head derived tubers had the least level <strong>of</strong> starch. On the otherh<strong>and</strong>, total free sugar content was found to be highest in tubers derived from head minisetts,followed by tail tubers while middle tubers had the least.103


P-40 BIOCHEMICAL CHANGES ASSOCIATED WITH THE CELLWALL OF YAM (DIOSCOREA CAYENENSIS) TUBERS DURINGSHORT-TERM STORAGEKathleen Lobban, Andrew Wheatley <strong>and</strong> Helen Asemota<strong>Department</strong> <strong>of</strong> Basic Medical Sciences (Biochemistry), MonaFreshly harvested mature cut yam tubers <strong>of</strong> D. cayenensis cv. Round Leaf Yellow Yam were storedon indoor shelves in a dark room at the Biotechnology Centre for seven weeks under ambientcondition. <strong>The</strong> cell wall enzymes, polygalacturonase, pectin methyl esterase <strong>and</strong> cellulase weremonitored using st<strong>and</strong>ard procedures at weekly intervals during this short-term storage <strong>of</strong> the yamtubers. After seven weeks the tubers began to rot. Significant differences were assigned using theDuncan's multiple range test. Increases in pectin methyl esterase were observed up to the third week<strong>of</strong> storage, after which enzyme activity decreased towards the end <strong>of</strong> the storage period.Polygalacturonase activity remained basically constant up to the fourth week, after which theactivity increased drastically by the fifth week. This increase in PG activity continued for theremaining period <strong>of</strong> the study. Cellulase activity also increased throughout the storage period.<strong>The</strong> trends observed in the activity <strong>of</strong> the cell wall enzymes reflect the dynamic biochemistry involvein the cell wall <strong>of</strong> the cut tubers during storage. Cutting <strong>of</strong> the yam tubers at harvest predisposes thetubers to active cell wall degrading enzymes which contribute to early spoilage.P-41 CELL WALL DEGRADING ENZYMES IN IN-VITRODERIVED PLANTLETS OF ROUND-LEAF YELLOW YAM(DIOSCOREA CAYENENSIS) INFECTED WITHXANTHOMONAS CAMPESTRISKnight, O. S., Hamilton, M. A. E., Omoruyi, F. O., Asemota, H. N.<strong>Department</strong> <strong>of</strong> Basic Medical Sciences (Biochemistry), MonaExtracts <strong>of</strong> shoots <strong>and</strong> roots from in-vitro derived plantlets <strong>of</strong> Round-leaf yellow yam (Dioscoreacayenensis) infected with Xanthomonas campestris were assayed for the activities <strong>of</strong> the cell walldegrading enzymes cellulase, polygalacturonase <strong>and</strong> pectin methyl esterase. <strong>The</strong> activities <strong>of</strong> thethree enzymes increased in the shoots <strong>of</strong> the infected plantlets. A similar trend was observed in theroots. However, the activities in the roots increased in excess <strong>of</strong> ten times that <strong>of</strong> the level in theshoots.<strong>The</strong>se results suggest that Xanthomonas campestris can infect Round–leaf yellow yam <strong>and</strong> that itmay be one <strong>of</strong> the factors mitigating against increased yam production in Jamaica.104


P-42 QUANTIFICATION AND IDENTIFICATION OF THECYANOGLUCOSIDES IN ECONOMICALLY IMPORTANT YAMVARIETIESMullings, Keith A; Asemota, Helen N. <strong>and</strong> Morrison, Errol E.Y. St A.<strong>Department</strong> <strong>of</strong> Basic Medical Sciences (Biochemistry), Mona<strong>The</strong>re are over 600 species <strong>of</strong> Dioscorea <strong>of</strong> which some 50 are eaten worldwide. World production isestimated at some 20 million tonnes annually. In tropical <strong>and</strong> subtropical countries such as West <strong>and</strong> EastAfrica, the Caribbean, South America, India, <strong>and</strong> South East Asia, yam tubers constitute an economicallyimportant food crop. In some <strong>of</strong> these countries yam constitute an important part <strong>of</strong> the daily staple,serving as an ideal source <strong>of</strong> calories <strong>and</strong> contributing vitamins <strong>and</strong> minerals vital to health (FAO, 1968).Antinutritional components are however also a part <strong>of</strong> the total composition, one class among these beingthe cyanoglucosides. This study centers on the extraction, quantification <strong>and</strong> identification <strong>of</strong> thecyanoglucosides in economically important yam varieties.High Performance Liquid Chromatography Studies on purified extracts <strong>of</strong> cyanoglucosides in differentvarieties <strong>of</strong> four Dioscorea species namely: D alata, D cayenensis, D. esculenta <strong>and</strong> D. rotundata, haveconfirmed linamarin as the main cyanoglucoside in yams. Among the twelve cultivars studied, linamarinlevels varied from 165.7 ± 17.5 ppm for D. rotundata cv . lucea to 573.7 ± 193.6 ppm for D. cayenensiscv. roundleaf. This result could be <strong>of</strong> relevance in appropriate selectivity in the promotion <strong>of</strong> desirablecultivars <strong>of</strong> yam for the Food <strong>and</strong> Health Industries, since cyanide from Linamarin, apart from interferingwith oxidative processes <strong>of</strong> metabolism, also by free radical mechanism reactions produces pancreaticdamage, <strong>and</strong> is therefore thought to be a factor in malnutrition related diabetes. This effect is most likelywhen there is ingestion <strong>of</strong> cyanide containing food, coupled with low protein intake. <strong>The</strong>re is a definitecoincidence <strong>of</strong> malnutrition related diabetes <strong>and</strong> the consumption <strong>of</strong> staples containing cyanide yieldingsubstances. Against this background, cultivars with low enough levels <strong>of</strong> cyanoglucoside shall befavoured, since there are safe limits for cyanide ingestioṅP-43 FRACTIONATION AND CHARACTERIZATION OFANAEROBIC SLUDGE TO BE USED IN THE TREATMENT OFINDUSTRIAL WASTEWATER AND PRODUCTION OF BIOGASEbanks, W. O. 1 , Hamilton, M. A. E. 1 <strong>and</strong> Riley, D. 21 <strong>Department</strong> <strong>of</strong> Basic Medical Sciences (Biochemistry Section),Mona;2 Scientific Research Council <strong>of</strong> JamaicaFractionation <strong>of</strong> sludge in an Upflow Anaerobic Sludge Blanket (UASB) pilot plant by graduallyincreasing the rate <strong>of</strong> influent to the plant was investigated. Fractions were collected on the basis <strong>of</strong>the upflow velocity at which they were washed out <strong>of</strong> the plant using influent velocities <strong>of</strong> 0.4, 0.8,1.8 <strong>and</strong> 1.9 m/h. A composite sample <strong>of</strong> the remaining plant contents was collected <strong>and</strong> BiochemicalMethane Potential tests were conducted on each set <strong>of</strong> fractions. <strong>The</strong> fractions collected at 1.8 m/hshowed the highest activity with an optimum sludge loading between 0.13 – 0.26g Chemical OxygenDem<strong>and</strong> (COD)/ g Mixed Liquor Volatile Suspended Solids (MLVSS) <strong>and</strong> this is indicative <strong>of</strong>maximum gas production with minimal sludge washout. <strong>The</strong>se results indicate that sludgefractionated <strong>and</strong> used in small UASB plants may result in improved activity <strong>and</strong> characteristicsleading to greater efficiency <strong>of</strong> gas production <strong>and</strong> wastewater treatment.105


P-44 EFFICACY OF PETRIFILM METHODS FOR THEENUMERATION OF COLIFORMS AND TOTAL AEROBESIN SELECTED DAIRY PRODUCTSDawkins, G. S. 1 , Hamilton, M. A. E. 1 , Hollingsworth, J. 21 <strong>Department</strong> <strong>of</strong> Basic Medical Sciences (Biochemistry Section),Mona;2 Jamaica Bureau <strong>of</strong> St<strong>and</strong>ards.Enumeration <strong>of</strong> total aerobes was conducted on three types <strong>of</strong> dairy products; powdered milk,pasteurised liquid milk <strong>and</strong> ice cream, while comparing the st<strong>and</strong>ard milk agar poured plate methodwith the 3M petrifilm aerobic count plate method. Data from the three types <strong>of</strong> samples, analysedboth individually <strong>and</strong> collectively, showed good correlation between both methods, with correlationcoefficients <strong>of</strong> ∃0.998. Significant differences were not obtained for the mean log10 cfu / g at P


P-46 A STUDY OF VIBRIO SPECIES IN RECREATIONALWATERS, SHELL FISHES, AND SHELL FISH FARM AREAS BYTRADITIONAL CULTURE METHOD AND PCRPaul Mears, Larry L. Daniels, <strong>and</strong> M. H. Ahmad<strong>The</strong> Biotechnology Centre, MonaWater samples from tourist resort areas <strong>and</strong> oyster farm sites were taken <strong>and</strong> tested for the presence<strong>of</strong> Vibrios. Additionally, Vibrios were isolated from oysters, fresh water <strong>and</strong> marine fishes. Whilethe non-pathogen Vibrio vulnificus was the most prevalent species, we were able to recover Vibrioparahaemolyticus from some oyster <strong>and</strong> fish samples. PCR analysis <strong>of</strong> the DNA from the isolatedVibrio species indicates the potential <strong>of</strong> this method for typing. DNA-based methods were also ableto detect the presence <strong>of</strong> Vibrios in water samples when traditional culture methods failed.P-47 CLV - A DEFENSIVE FACTOR FROM THE SECRETORYTRICHOMES OF CLEOME VISCOSA WITHINSECTICIDAL ACTIVITYLawrence A. D. Williams 1 , Walton A. Reid 2 , <strong>and</strong> Roy Porter 1<strong>Department</strong> <strong>of</strong> <strong>Chemistry</strong> 1 <strong>and</strong> Electron Microscope Unit 2 , Mona<strong>The</strong> phenomenon <strong>of</strong> plant resistance to insect attack is governed largely by the plants chemicalfactors (Kubo <strong>and</strong> Hanke, 1988). <strong>The</strong>se chemicals are fundamental in underst<strong>and</strong>ing theevolutionary <strong>and</strong> ecological processes <strong>of</strong> the insect-plant interaction, but there are practicalapplication <strong>of</strong> these molecules. For example, several <strong>of</strong> these compounds are <strong>of</strong> significanteconomic importance in the management <strong>of</strong> pests as, insecticides, allomones, growth regulators etc(Shrama, 1982).In our on going exploration <strong>of</strong> West Indian plants for medicinal <strong>and</strong> agrochemical compounds wehave decided to explore the surface compounds <strong>of</strong> Cleome viscosa L (Capparaceae) for insecticidalactivity for the following reasons: the leaves <strong>and</strong> stems <strong>of</strong> C. viscosa are not eaten by herbivores inthe wild <strong>and</strong> it secretes a waxy/<strong>of</strong>fensive chemical mixture from its trichomes. This mixture iscapable <strong>of</strong> trapping a wide range <strong>of</strong> insects from the hymenopteran, dermopteran, coleopteran <strong>and</strong>hemipteran orders on the leaves <strong>and</strong> stems <strong>of</strong> the plant.Scanning electron microscopy studies <strong>of</strong> the stems <strong>and</strong> leaves <strong>of</strong>C. viscosa revealed threemorphologically distinct groups <strong>of</strong> trichomes 1. beaded spheres, 2. Columnar spheres <strong>and</strong> 3Cylinders.Hexane extraction <strong>of</strong> the wax from the leaves <strong>and</strong> stems <strong>of</strong> C. viscosa followed by separationchemistry lead to the isolation <strong>of</strong> a major compound which was termed “CLV”. This compound wasevaluated for insecticidal activity against Cylas formicarius Summer (Coleoptera: Curculionidae)one <strong>of</strong> the most destructive pests <strong>of</strong> the sweet potato, Ipomoea spp (Sorensen, 1987).107


<strong>The</strong> compound demonstrated a toxicity pattern similar to that <strong>of</strong> “unformulated naturally occurringpyrethroids” i.e. CLV induced 50 % <strong>and</strong> 80 % knock down activity <strong>of</strong> the test insects at 40 <strong>and</strong> 80ug/insect, respectively at 24 hrs. However, only 10 % <strong>and</strong> 30.0 % mortality was recorded for theabove mentioned doses after 48 hrs; thus 40 % <strong>and</strong> 50 % <strong>of</strong> the test insect recovered from the toxin.<strong>The</strong> controls had 0.0 % knock down at 24 hr <strong>and</strong> 5.0 % mortality at 48 hr (N= 30 insects in tworeplicates <strong>of</strong> 15 at each dose level). <strong>The</strong> study also revealed that piperonyl butoxide (PB), a knowninhibitor <strong>of</strong> the mixed function oxidases enzyme complex <strong>and</strong> pepper mint Mentha ( spp.) oleoresinat 0.05% (v/v) in acetone enhanced the toxicity <strong>of</strong> CLV. Thus, the 48 hr Lc50 (concentration <strong>of</strong>CLV in each carrier required for killing 50 % <strong>of</strong> the test insects) values obtained in PB <strong>and</strong>peppermint oleoresin were 40.0 ug/insect <strong>and</strong> 35.6 ug/insect, respectively. <strong>The</strong> equivalent volumes<strong>of</strong> 0.05 % PB <strong>and</strong> peppermint oleoresin in acetone (positive controls) inflicted 0.0 % <strong>and</strong> 10.0 %mortality at 48 hrs, respectively.<strong>The</strong>se studies revealed that CLV has a typical pyrethroid knock down action against adult C.formicarius. However, formulating the compound in piperonyl butoxide <strong>and</strong> pepper mint oleoresinenhanced the insecticidal action <strong>of</strong> the molecule.ReferencesBowers, W. S. (1998). Phytochemical resources for plant protection. In Recent Advances in the<strong>Chemistry</strong> <strong>of</strong> Insect Control. N. F. James (ed.) Henry Ling Ltd, Dorset, pp. 272-91.Kubo, I <strong>and</strong> Hanke, J. F. (1988). Chemical methods for isolating <strong>and</strong> identifying phytochemicalsbiologically active in insects. In Insect-Plant Interactions J. R. Miller <strong>and</strong> T. A. Miller (eds.)Springer-Verlag, New York. pp. 225-249.Sharma, R. N. (1982). Development <strong>and</strong> utilization <strong>of</strong> plant products for insect control- Acomprehensive approach. In Cultivation <strong>and</strong> utilization <strong>of</strong> medicinal plants. C. K. Atal<strong>and</strong> B. M. Kapur (eds.) pp. 659-668.Sorensen, K. A. (1987). Cultural, regulational <strong>and</strong> educational programmes on the sweet potatoweevil in the United States. Insect Sci. Applic. 8: 825-30.P-48 THE BOTANY AND DOMESTICATION POTENTIAL OFCIONOSICYOS POMIFORMIS GRISEB (“DUPPY PUMPKIN”)Patrick A.Lewis, K R.. Vaidya, H. Jacobs* & L.A.D. Williams*<strong>Department</strong>s <strong>of</strong> Life Sciences <strong>and</strong> *<strong>Chemistry</strong>, MonaCionosicyos pomiformis is a fairly commom climber in the moist forests <strong>of</strong> Jamaica. Adams in his“Flowering Plants <strong>of</strong> Jamaica” (1972) listed it as endemic. <strong>The</strong>re is a “similar” plant which growsin Cuba, but it is not very common, the last Cuban collection having been done in the 1950’s. <strong>The</strong>seeds are rich in oil (12%) which may have use as a cooking oil or as a Cosmetic oil.This prelimonary work documents what is known botanically about Cionosicyos pomiforms so far, looksat the potential uses <strong>of</strong> the plant.Including the oily seeds <strong>and</strong> looks at the action <strong>of</strong> the methanol extractoncattle ticks <strong>and</strong> sweet potato weevil.108


P-49 INDOOR LEVELS OF NO2 MEASURED USINGPASSIVE MONITORSRaywattie Singh <strong>and</strong> Willard R. Pinnock<strong>Department</strong> <strong>of</strong> <strong>Chemistry</strong>, MonaMeasurements <strong>of</strong> indoor <strong>and</strong> outdoor levels <strong>of</strong> NO2 have been made at ten selected sites in an effortto investigate the possibility that indoor sources may present a greater threat to health than outdoorsources, as has been observed elsewhere 1 . Measurements were made using passive monitors, whichhave been used in an earlier study 2 <strong>and</strong> have been shown to provide reliable measurements <strong>of</strong>ambient NO2 levels quite inexpensively.Results <strong>of</strong> the measurements show outdoor levels to be typically in the region <strong>of</strong> about 10 to 30 µgm -3at these sites, with the indoor levels <strong>of</strong> NO2 to be on average about 1.2 to 2 times thecorresponding outdoor value where there are no identifiable indoor sources. However in kitchenswhere gas cookers or gas water heaters are installed, the levels are much greater than outdoors. Attwo such sites the levels observed are consistently greater than the 100 µg m -3 limit suggested forambient air by the National Resources Conservation Authority in its Air Quality St<strong>and</strong>ards3 .<strong>The</strong>se results suggest that unacceptably high levels <strong>of</strong> NO2 can in fact occur indoors, even inclimates such as ours where the ventilation <strong>of</strong> houses is generally assumed to be significantly betterthan in temperate climates. <strong>The</strong> levels observed suggest also that the increasing use <strong>of</strong> gas cookers inpoorly ventilated kitchens may well be one <strong>of</strong> the factors contributing to the increased incidence <strong>of</strong>respiratory illness said to be observed by local Medical personnel.Plans are being formulated to extend the survey to include a larger number <strong>of</strong> houses <strong>and</strong> to coverthe variety <strong>of</strong> fuels used for cooking locally.References1. Building Research Establishment (1996) Indoor Air Quality in Homes: <strong>The</strong> BuildingResearch Establishment Indoor Environment Study. In BRE Reports 299-300. CRC Ltd.London3. Pinnock, Willard R; Singh, Raywattie; (1997) Use <strong>of</strong> PassiveMonitors to Measure Atmospheric Nitrogen Dioxide Levels.Jamaican Journal <strong>of</strong> Science <strong>and</strong> Technology 7-8:13 – 21.3. Natural Resources Conservation Authority (1995). Ambient Air Quality St<strong>and</strong>ards.Jamaica.109


P-50 QUALITATIVE ANALYSES OF CARIBBEAN RUMSBY GC/MS TECHNIQUESS. Kulikov<strong>Department</strong> <strong>of</strong> Biological <strong>and</strong> Chemical Sciences, Cave HillSeries <strong>of</strong> rums produced in Barbados, Jamaica, Trinidad, Puerto-Rico <strong>and</strong> Bahamas were analyzedqualitatively by GC/MS. Besides ethanol <strong>and</strong> water which are the main components <strong>of</strong> any rum a lot<strong>of</strong> organic compounds containing in very low concentrations can be found in rum. Such compoundsas ethers give rums a specific, sometimes unique taste <strong>and</strong> odor. On the other h<strong>and</strong>, compounds suchas methanol, alcohols C3, C4 <strong>and</strong> higher, acetone, acetaldehyde, ehtylenglicol, glycerol <strong>and</strong> someethers can be unhealthy or even dangerous if contained in relatively high concentrations. For theanalysis GC/MS Fison 8000 with fused silica capillary column SPB-608, 30m, 0.25 mm ID,0.25? m film thickness was used. Temperature program - 6 0 C for 5 min, 5 o /min till 100 0 C, 10 minat 100 0 C, split/splitless injection, 70 eV, He as a carrier gas. Samples were analyzed as received,without internal st<strong>and</strong>ard, 1? l probe. This preliminary qualitative assessment <strong>of</strong> about 15 differentrums has shown very different quality even for the products <strong>of</strong> the same manufacturer. Generally,over pro<strong>of</strong>ed rums (with alcohol concentration more than 80 % vol.) contain much more impuritiescompared with rums with 40-43% vol. <strong>of</strong> alcohol. Significant concentrations <strong>of</strong> the impurities suchas butanols <strong>and</strong> pentanols, ethyl ester <strong>of</strong> pentanoic <strong>and</strong> hexanoic acids, butyl- <strong>and</strong> pentyl- acetates,propanetriol, naming only a few, were identified in over pro<strong>of</strong>ed rums. Rums with alcoholconcentration <strong>of</strong> about 40% vol. contain usually only isomers <strong>of</strong> butanol <strong>and</strong> pentanol in more orless significant concentrations. Some <strong>of</strong> them did not contain any <strong>of</strong> impurities at all. For the sametrade name <strong>of</strong> rum, quality depends upon whether it is stored in plastic or glass bottle. Concentration<strong>of</strong> impurities were significantly lower for the plastic containers, probably because <strong>of</strong> absorption <strong>of</strong>them by plastic.P-51 MAGNETOCARDIOPATHY USING A SUPERCONDUCTINGQUANTUM INTERFERENCE DEVICE: PRELIMINARYASSESSMENT OF CARDIAC PATIENTS INTRINIDAD AND TOBAGORamadhar Singh R 1 , Saunders R 1 , Rassi D 2 , Thomas C 3 , Addae, J 3 <strong>and</strong> Posth<strong>of</strong>f C 4<strong>Department</strong>s <strong>of</strong> 1 Physics, 3 Medicine <strong>and</strong> 4 Mathematics <strong>and</strong> Computer Science, St Augustine;2Swansea College, University <strong>of</strong> WalesSuperconduction Quantum Interference Devices (SQUIDs) greatly improve the extent to whichbiomagnetic fields can be studied. Analyses <strong>of</strong> these biomagnetic fields, specifically those whichemanate from the heart, can be <strong>of</strong> significant diagnostic value. Using a second order SQUIDgradiometer, magnetic components perpendicular to the frontal plane (normal component) <strong>of</strong> thethorax were recorded at thirty six equally spaced points <strong>of</strong> a 6 x 6 grid located above the region <strong>of</strong>the heart. <strong>The</strong> results were analyses using BIOMAG s<strong>of</strong>tware. Averaging <strong>of</strong> the signals was doneby sampling sixteen low noise epochs. Isomagnetic maps were then constructed by interpolating allthirty six signals. It is expected that cardiac conduction pathways would also affect the associatedmagnetic fields.110


Qualitative assessment <strong>of</strong> these signals <strong>and</strong> maps could lead to more extensive clinical informationfor diagnosis <strong>and</strong> treatment than that which the current diagnostic tools can provide. <strong>The</strong> patientsfor this study were from <strong>The</strong> Heart Care Clinic <strong>and</strong> the <strong>Department</strong> <strong>of</strong> Nuclear Medicine at the Mt.Hope Hospital in Trinidad. This preliminary study presents cases <strong>of</strong> patients with myocardialinfarction, WPW syndrome <strong>and</strong> left bundle branch block, compared with a normal (no cardiacdisease) subject. <strong>The</strong> results show marked differences in the magnetic dipoles <strong>of</strong> the heart for theabnormal cases. This information can be used to evaluate conduction pathways in the heart <strong>and</strong>locate the site <strong>of</strong> infarcts or non-conductive regions <strong>of</strong> the heart.P-52 CALIBRATION FACTORS FOR I-131 mIBG RADIONUCLIDETHERAPYMukesh Samlal, +Sarah Chittenden, +Glenn Flux, +Maggie Flower<strong>Department</strong> <strong>of</strong> Physics, St. Augustine;+Joint <strong>Department</strong> <strong>of</strong> Physics, <strong>The</strong> Royal Marsden National Health Service Trust, Engl<strong>and</strong>.Neuroblastoma is a rare childhood cancer with a poor long term prognosis. <strong>The</strong> Royal MarsdenNational Health Service Trust specialises in treating this disease with 131I metaiodobenzylguanidine(mIBG), where the maximum permitted dose is usually limited by bone marrow toxicity. Prior totreating the cancer, therefore, an administration <strong>of</strong> 123I mIBG is given to determine the wholebodydose resulting from a given activity <strong>and</strong> for diagnostic purposes. <strong>The</strong> MIRD method is used toquantify the absorbed dose to a tumour which requires the cumulated activity to be obtained frompatient scans. For this, counts are converted to activity using calibration factors derived fromphantoms.Calibration factors covering a large range <strong>of</strong> typical clinical situations were obtained. Two groups<strong>of</strong> calibration phantoms (sources) were investigated:1) sources where the diameter <strong>and</strong> length were the same2) sources where the length was equal to 10 cmFor each source, two calibration factors were calculated:1) <strong>The</strong> Maximum Voxel Count Calibration Factor2) <strong>The</strong> Total Volume Count Calibration Factor<strong>The</strong> results were displayed graphically to enable easy interpolation <strong>of</strong> calibration factors. Graphicalfunctions were obtained that provided a best fit to the data, so that the results could be incorporatedinto the dosimetry s<strong>of</strong>tware, which is being developed at the hospital. For each group <strong>of</strong> calibrationphantoms, it was noted that for the smaller source sizes, there was a rapid increase in the calibrationfactors with increasing size, although, as the sizes (volumes) increased, the calibration factors variedless rapidly.Overall, similar trends were observed for both I-123 <strong>and</strong> I-131 studies. It was noted that thecalibration factors obtained for the I-123 sources were always higher than the calibration factorsobtained for the relative I-131 sources. Also, a general observation was that for any source theMVCCF was always greater than the TVCCF.111


P-53 TEMPERATURE AND HEAT REMOTE CONTROL INPOULTRY BY WIRELESS AUTOMATION.Lucien Ngalamou<strong>Department</strong> <strong>of</strong> Physics, MonaAnalysis <strong>of</strong> the mortality pr<strong>of</strong>ile <strong>of</strong> chickens' growth in the Caribbean region reveals an abnormalrate during the first two weeks (2 to 3 %) comparing to the normal rate <strong>of</strong> 1.25% -1.5%.<strong>The</strong> first two weeks correspond to the brooding period where baby chickens have to adjust to theenvironmental temperature. <strong>The</strong>y must be held at a temperature <strong>of</strong> 90o F for the first week with asubsequent decrease <strong>of</strong> 5o F every week. <strong>The</strong> first two weeks are very critical for the finalperformances (body weight, feed consumption <strong>and</strong> feed conversion) at 42-45 days.<strong>The</strong> actual brooding techniques used by the majority <strong>of</strong> companies in the Caribbean need manualadjustment <strong>of</strong> brooders (gas brooder or electric brooder) from farm to farm. <strong>The</strong>re are few caseswhere thermostats are being used. As result, baby chickens are either overheated or chilled, which isa damage for the productivity. Actual house temperatures are recorded using temperature recorder,but they do not allow any instantaneous adjustment, or automatic correction. In order to improvethe production <strong>and</strong> the quality <strong>of</strong> the chickens, we present an electronic system for automatic control<strong>of</strong> temperature <strong>and</strong> heat.<strong>The</strong> electronic system is designed as a network having a central unit (computer), connected to the differentcontrol units available in each poultry by wireless techniques. In real time we can have information aboutthe temperature <strong>and</strong> the energy. <strong>The</strong> control unit is designed to measure the temperature within anadjustable sampling period. It regulates the amount <strong>of</strong> energy (heat) available in the poultry, <strong>and</strong> is able tocommunicate with the central unit.P-54 THE RHEOLOGICAL PROPERTIES AND SLIP CASTINGPOTENTIAL OF SOME TRINIDADIAN CLAYSD. A. P. Robertson <strong>and</strong> J. C. Knight<strong>Department</strong> <strong>of</strong> Physics, St. AugustineDue to economic realities, the past decade has shown renewed interest in the use <strong>of</strong> clay-basedindustrial products in developing countries. However, in terms <strong>of</strong> chemical, mineralogical <strong>and</strong>physical character, no two clay deposits are ever identical. Further, in any given deposit, thevariability can be considerable. Consequently quality assurance, through st<strong>and</strong>ardization <strong>of</strong>production cycles, necessitates a sound knowledge <strong>of</strong> the variability factors in order to formulate forhigh <strong>and</strong> consistent quality. This is particularly critical in processes involving aqueous suspensions,where the end product is highly sensitive to intrinsic <strong>and</strong> processing variables such as impuritycontent, cation exchange capacity, viscosity, thixotropy, <strong>and</strong> specific gravity. In this respect,Caribbean clays have not been properly <strong>and</strong> systematically researched. This in part, accounts for theunder-exploitation <strong>of</strong> regional clays, particularly for fine-finished products. Thus, starting withsamples from various deposits in Trinidad, a study aimed at elucidating the rheological potential <strong>of</strong>regional raw materials (such as clays, silica s<strong>and</strong>s, <strong>and</strong> volcanic ash) is underway.112


P-55 TRINIDAD CLAYS AS A POTENTIAL COMPONENT IN CLAY-GRAPHITE REFRACTORIESR. Ramgoolam, J.C. Knight <strong>and</strong> Ramsey Saunders<strong>Department</strong> <strong>of</strong> Physics, St. AugustineTrinidad clays are currently used in the manufacture <strong>of</strong> structural clay blocks, tiles <strong>and</strong> potterywithout consideration <strong>of</strong> their possible use in the production <strong>of</strong> technical ceramics. As part <strong>of</strong> awider study focussed on the development <strong>of</strong> commercial refractory products from Caribbeanregional raw materials, the suitability <strong>of</strong> certain Trinidad clays as a component in clay-graphitesystems is under investigation. Clay-graphite refractories have many uses in the metal meltingindustry. In steel-making mini-mills the normal operating temperature is &#61566;900ºC, it istherefore necessary that the refractory materials used maintain their refractoriness at thistemperature. Clays have inherent good strength when fired, with the inclusion <strong>of</strong> graphite in suchrefractories to provide the conducting element for heat transfer.This paper addresses some <strong>of</strong> the formulation parameters <strong>of</strong> possible refractory products with theLongdenville clay <strong>of</strong> central Trinidad as a major constituent. <strong>The</strong> emphasized processing variablesare body composition <strong>and</strong> firing temperature. In the temperature range 800–1100ºC preliminaryresults show that for any given graphite content in the range 20-40% optimum mechanical propertiesoccurred at 900ºC, where the graphite oxidation is least (14%). Thus, this clay-graphite system<strong>of</strong>fers the possibility <strong>of</strong> a lower production cost since satisfactory mechanical properties are attainedat a relatively low firing temperature. Further, scanning electron microscopy (SEM) indicatesadvanced vitrification <strong>of</strong> the clay with highest porosity confined to superficial regions.P-56 TESTING OF BONDING SYSTEMS FOR DENTALMATERIALSH. Baksh, R. Whiting, A. Campbell-Richardson+<strong>Department</strong> <strong>of</strong> Physics, St Augustine;+School <strong>of</strong> Dentistry, Eric Williams Medical Sciences Complex, Mt. Hope.In conservative dentistry, due to the introduction <strong>of</strong> new adhesive formulations, there is currentinterest in the bonding <strong>of</strong> fresh restorative materials to old restorations. At present, there is a wideselection <strong>of</strong> the adhesives available <strong>and</strong> so there is a great need for in vitro laboratory evaluation <strong>of</strong>potential adhesive systems prior to their clinical application.In this study, several bonding systems were investigated using two test methods, a non-destructivevibrational test, <strong>and</strong> a destructive shear test. <strong>The</strong> vibrational testing involves the flexural resonance<strong>of</strong> a three-layer cantilever beam <strong>and</strong> indicates the elastic <strong>and</strong> damping properties <strong>of</strong> each layer,which can then be related to surface defects, aging, etc. <strong>The</strong> shear test employed is superior toprevious methods because <strong>of</strong> the symmetric arrangement <strong>of</strong> the loading forces about the bondedarea. It determines the true shear strength <strong>of</strong> the adhesive joint. Tests were carried out using twoamalgam-bonding resin cements <strong>and</strong> three substrates, a traditional high copper amalgam, a galliumbasedalloy <strong>and</strong> a composite resin.<strong>The</strong> results showed the effectiveness <strong>of</strong> the bonding systems employed <strong>and</strong> indicated that the testingmethods selected were appropriate for such systems.113


P-57 THE ELECTRODYNAMICS OF A JOSEPHSON JUNCTIONIN A CAVITYAndrea Joseph, Roger Andrews <strong>and</strong> Robin Whiting<strong>Department</strong> <strong>of</strong> Physics, St. Augustine<strong>The</strong> radioactive properties <strong>of</strong> a biased Josephson junction in a Fabry-Pert resonator are investigated.Solutions to Maxwell’s equations for transverse magnetic (T.M.) <strong>and</strong> transverse electric (T.E.)modes are provided, <strong>and</strong> their properties described in terms <strong>of</strong> controllable physical parameters <strong>of</strong>the system. Possible device applications are also discussed.P-58 PROGRAMMABLE STATE MACHINEJoseph Skobla<strong>Department</strong> <strong>of</strong> Physics, MonaTypical N bit sequential machine is designed as a combination <strong>of</strong> the digital circuits - gates <strong>and</strong> flipflops.This circuit is operating as a synchronous circuit with a common clock signal. As acharacteristic describing operation is either a state diagram, a state table or the timing diagram. Anyclassic sequential state machine is hardware specific <strong>and</strong> usually the design is a fixed sequence <strong>of</strong>the output signals Q0,Q1, ..QN. <strong>The</strong> circuit changes the output state with a rising or a trailing edge <strong>of</strong>the clock signal, where the timing period <strong>of</strong> the outputs is derived from the period <strong>of</strong> the clocksignal.This article is describing a MCU - 8 bit microcontroller operating as a 32 bit programmablesequential machine having 32 output control signals, shown in Fig.1. <strong>The</strong> state table in Fig.1 issimplified showing only first 3 states. An example <strong>of</strong> this machine is the design using MotorolaMC68HC11 8 bit micorocontroller <strong>and</strong> 32 bit output interface circuit.P-59 USE OF MINIMAL SPANNING TREE STATISTICS FORIDENTIFICATION OF VOIDSShirin Haque-Copilah <strong>and</strong> Anthony Achong<strong>Department</strong> <strong>of</strong> Physics, St. AugustineVoids are regions in space that are significantly underdense in the galaxy population from anexpected count. In general, a void tends to be spherical <strong>and</strong> may contain about 10% the amount <strong>of</strong>galaxies from a regular distribution. Visual cues are not adequate in astronomy to identifystructures, especially in three dimensional surveys where there may be contamination fromforeground <strong>and</strong> background objects. In light <strong>of</strong> this, it has been found that the Minimal SpanningTree (MST) statistic can actually be used to confirm the presence <strong>of</strong> voids. <strong>The</strong> MST statistic relieson nearest- neighbour algorithm to identify linear structures <strong>and</strong> in particular filaments in galaxydistribution. Two further reducing procedures known as separation <strong>and</strong> pruning (where extraneousbranches are removed) are done on the samples to delineate the structures.114


<strong>The</strong> procedure was <strong>applied</strong> to the Pisces-Perseus sample containing originally 7223 galaxies butreduced to 4501 galaxies for the complete working sample, limited to apparent magnitude 15.7 <strong>and</strong>heliocentric velocities <strong>of</strong> 15000 km/s. Subsamples representing the most conspicuous galaxies (thebrightest <strong>and</strong> largest ones) <strong>and</strong> those representing the least conspicuous galaxies (the faintest <strong>and</strong>smallest ones) were also tested. Apart from identifying filamentary structure in the samples, <strong>and</strong>further highlighting the well-known supercluster in this region <strong>of</strong> the sky, it was noted that severalwell known voids were also delineated. As such we conclude, having used Pisces-Perseus as atesting ground, that MST’s can be used to identify voids as well in a distribution <strong>of</strong> galaxies <strong>and</strong> notonly linear features.P-60 WIND GENERATED ELECTRICITY AT MUNROA.M.D.Amarakoon <strong>and</strong> A.A.Chen<strong>Department</strong> <strong>of</strong> Physics, MonaA lot <strong>of</strong> emphasis has been placed by the government <strong>of</strong> Jamaica in the recent times on thedevelopment <strong>of</strong> alternative energy resources, including solar <strong>and</strong> wind energy. A realisation in thisdirection was the commissioning <strong>of</strong> the 225 kW wind turbine(Vestas 27-225) at Munro, St.Elizabethin 1996. This was a follow up <strong>of</strong> the work <strong>of</strong> Chen et.al.(1990) on the potential <strong>of</strong> wind power inJamaica, which included Munro area.This presentation sumarises the preliminary results <strong>of</strong> the analysis carried out on the performance <strong>of</strong>the wind turbine using data collected over a period <strong>of</strong> approximately one year starting from July,1996. For the period <strong>of</strong> July, 1996 to July, 1997, the results show that :(i) <strong>The</strong> monthly average wind speed at a height <strong>of</strong> 30m at Munro is greater than 5.5 m/s,exceptin the winter month <strong>of</strong> December (about 4.7 m/s).<strong>The</strong> summer month <strong>of</strong> June records thehighest average speed <strong>of</strong> 9.6 m/s;(ii) <strong>The</strong> availability factor <strong>and</strong> the capacity factor <strong>of</strong> the turbine are estimated to be 97.5%percent <strong>and</strong> 34.4 %, respectively;(iii) <strong>The</strong> expected electrical energy from the turbine is 626.4 MWh;(iv) <strong>The</strong> estimated cost <strong>of</strong> generation <strong>of</strong> electricity is J$ 3.51 per kWh.Acknowledgements<strong>The</strong> authors wish to thank the Environmental Foundation <strong>of</strong> Jamaica (EFJ) for financial assistancethroughout the project. Special thanks are due to Mr. N.Thomas <strong>of</strong> the <strong>Department</strong> <strong>of</strong> Physics,Mona for his assistance at various stages <strong>of</strong> this project including data collection.ReferencesChen , A.A., Daniel, A.R., Daniel, S.T. <strong>and</strong> Gray, C.R. (1990). Wind Power in Jamaica.Solar energy 44(6):355-365.USAID/OLADE (1996). Notes from the Renewable Energy Project Development Workshop;Oct.14-18 (1996. Kingston, Jamaica.WinSite; User’s Guide to Wind Data Presentation for Windows. Second Wind Inc., Somerville,Massachusetts, USA.115


P-61 ON ASYMPTOTIC STABILITY OF NONLINEAR STOCHASTICDIFFERENCE EQUATION WITH FINITE DELAY IN MAIN TERMRodkina A <strong>and</strong> *Goncharov M.<strong>Department</strong> <strong>of</strong> Mathematics <strong>and</strong> Computer Science, Mona;*Voronezh State Academy <strong>of</strong> Construction <strong>and</strong> Architecture, RussiaStochastic equations appear in numerous technical problems (see, for example [1]. To describe theprocesses functional-differential Ito equations (see [2]) as well as stochastic difference equations <strong>of</strong>Volterra type have been used. <strong>The</strong> main tools for obtaining the asymptotic stability results areLyapunov-Krasovkii functionals method <strong>and</strong> some approaches from the theory <strong>of</strong> r<strong>and</strong>om processes.We consider the following equation:xi+1=k∑j=0ai,jxi−j+f [ i,x , xii−1,..., x0] +σ[i,x , xii−1,..., x ] ξ ,0i(1)where k is a given number <strong>and</strong> for every i= 1, 2,...,θi=k⎛⎜⎜⎝k∑ ∑l= 0 j=0ai+l,j⎞⎟⎟⎠ai+l,l< 1,θi−2i1 = −γ,∞∑i=02iγ = ∞.(2)For noisesf<strong>and</strong>σwe suppose the following restricitons to be fulfilledf [ i,x , xii−1,..., x ]02,σ[i,x , xii−1,..., x0]2≤i∑j=0~ 2λi,jL(x2i−j),whereem∑= expe∞ηi= 0 i+lm−1,∑ln ( x)= x,0∞ 2λl= 0 i+l,l< ∞,L(u)=ln ( x)= lnii−1∏mi=0(ln x),1n ( u + eim+ ε),i = 1,2,..., m;for e0= 0, ex,u,ε > 0.1= 1,It is proven that under theconditions above the trivialsolution <strong>of</strong> Eqn (1) is almost surelyasymptotic stable.References[1] Kolmanovskii, V. B., Myshkis, A. D. (1992). Applied <strong>The</strong>ory <strong>of</strong> Functional DifferentialEquations, Kluwer Academic Publishers. Dortrecht-Boston-London.[2] Rodkina, A. E. (1997). Rate Control <strong>of</strong> Manipulator Robot. Proceedings <strong>of</strong> 15 th IMACSWorld Congress. Berlin. V.5. System Engineering. Germany. Wessenschaft <strong>and</strong> TechnikVerlag. pp. 305-310.116


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