{"id":{"repo_id":"cape-town","oai_identifier":"oai:open.uct.ac.za:11427/40463"},"canonical_url":"https://search.dev.ndltd.org/etd/cape-town/oai:open.uct.ac.za:11427/40463","repository":{"repo_id":"cape-town","name":"University of Cape Town","base_url":"https://open.uct.ac.za/oai/request"},"display":{"title":"Dynamic catch-effort models for the southern African hake populations","abstract":"Ur1til 1984, hake quota rec:·ottrttreridaticms made by the ICSEAF Scie·,.-1tific:· Advisory Cour1c:·il were based ors the prodtlcticn .. , 1trooe1 approach with evaluations made using a continuous eqi.ti l i br-i utrJ approx imat i ors. However, seri 01..1s di screpar1c·ies betwee't\"1 mooei. predic:·tior1s arid data bec:·artre appare·nt arid this thesis examines the exter1t to whic:·h these are c:·o'f\"1sequences of. the fa i 1 .t re t 0 a 11 ow f 0 .,.. oy·nartti cs i r1 fitting models to the data. The biology of the hake popttlatio·n and the history of the hake fisheries off the coast of southerl\"1 . Afric:·a · a'r-e reviewed b'r-iefly ;:rnd the obJectives of fishery tttar1age11'1e·nt defined. This is followed by a presentation of the data l..tsed ir1 subseql..te't\"1t calc::-l..tlations together with details of the sc:ti..lrces fr'otrJ whic:·h they were obtai't\"1ed. 1'he basis for the surpl tts prodtu:·t i o·,.-, 1t1odel for the evaluation of sustai't\"1able yields is discussed. It is show·f'\"s that the steady-state assumptior1 will pretbably lead to positively biased sustainable yield estimates for fisheries whose history is dotr1ir1ated by a dec:·lir:ir1g CPUE t rer1d. !r1 Em attempt to c:·orrect for suc:·h biases, evaluations a're also carried ottt usir1g Gt1llal\"1cFs method of averaging effort data. However it is riot c·lear to what extent this eqt1i 1 i bri um c:pprox itr1at i or1 approac:·h c::-ompemsates for Sl..tch errors. Col\"1sequerrt ly, discrete dynamic- versions of the Schaefer and Fo>t models are fitted, i..tsi ng nor11 l near tt1i ni1t1i Lat i or1 procedures, to catch-effort data for the fottr ICSEAF areas commonly chosen for hake stock assessment purposes, nEUl'lely Divisiol\"1S 1.3 + 1.4, 1.5, 1.6 and 2.1 + 2.2 (all of which indicate generally downward CPUE trends for the maJOT' part of their histories>. Monte Carlo simulation methods are employed to estitt1ate coefficients of variation for· the trJodel parameter and yield values assessed. The dyr1amic models aT'e show-n to p.,..ovide disti·nctly .ittrproved fits to the CPUE time series c:·ompared to those obtained ttsing the Gullcfl'\"1d FunctioY1al Regression <GFR> or the steady-state approaches. MSY estifrrates obtail\"1ed from dyr1atrtic:· model fits a.,..e, on average, appro>tifflately 1(>~ less than those resulting from the GFR procedu.,..e. Since the effects of 1..mcertainties (s1..tch as adverse environmental variability and the imprec::-ision of stoc~ biomass estittrates} can critically influence the outcoffle of mcmagement dec-i si ons, caution should be e>terci sed when 1t1ak i ng catch l i1rd t recomme·ndat ions. Various conservative approaches are advocated, arid the associated current catch limit recommendatior1s evaluated. These incltlde the Gulland and Boerefl'!a f 0 , 1 p\"rocedl..tre, and an approac::-h where the qttota is reduced by a fraction of the standard error of the initial quota estimate. v The dynamic moaei is also employed to predict future biomass (as well as CPUE and quota} values. A historical examirratio't'\"r of the ac:·c:·ttracy of suc:·h proJectiorrs· is used to c:·ott1<t1ent uporr the effic:·acy of the Schaefer and Fox ciy.,..1a111ic tt1odel s •. Dyr1att1ic model biomass estimates are co<t1pared to those provided by the Virtual Population Ar1cclysi s CVPA> p'r'oc:·edure for Division 1.6 • Large discrepancies in both recent t re·nds arid ccbsol .te val ttes cc re eviderrt, with biomass estimates bei't'\"rg much lower i·n the cccse of VPA. Vs ri ous ext ensi O't'\"1s to the dyl\"1cc<tti c model a re i .,..,t roduc:·ed i .,.., an at t e<t1pt to red uc:·e the difference bet ween dyrrc:<tr i c <ttode 1 ;:md VPA biomass estimates ir1 Division 1.6. In general, the ir1corporatiorr iY1 the dyY1a<tdc:· <t1odel of ti111e lag effects (ir1 the r1et growth fi..mctioY1> a'!'\"1d increased efficie'l'\"1cy factors Hrs the catching operatiO'l\"r) yield '!'\"10 obvious itnprove<trer1t ir1 agreefflent betwee'!'\"1 dyl'\"1amic:· <t1odel aY1d VPA results. I·l\"1 ac:iditio·l\"1, the effect of allowir19 the ratio of the biomccss at th.e start of the given CPUE series to· the ca·r\"ryiY19 capacity (y 1 /rO to assume val.tes oti\"rer thccYr tmity is exattiil'\"red. Results iY1dic·ate that this exter1ded model does ·not appear to have any advantages over models applied ear11er whic:·h asstt<tteo y 1 =r. The seemil'\"rgly i·nsig'f\"1ificant i<ttproveme·nts obtained S.tggest that the origi't'\"ral dynamic model ·r1eerly fully e){ploits the i't'\"1formatio't'\"1 ·c·o·nteYrt of the data arrti that the i'l\"1t1\"oductio'f\"1 of fttrther parattreters ca't'\"r caltse the su<t1 of squares S.trfac·e to become very flat i'f\"1 the vic:·inity of the <tiiriittrttm that is sought ir1 the fittir1g proc:-edttre. Dy·l\"rami.c model fits .tsing the Shepherd surpltts prodttc:·t i o·n forttr (which incorporates a skewness para<tseter> are per·fortned 0'1\"1 the c·atch-effort ciatcc. The ratio of the biotttass at MSY to the carryi'f\"1g capacity (YMsY /K) is shown to be very poorly determined by the catch-effort data (the average coefficie'f\"rt of variat iol\"1 of estimates is 30~>. Results indicate that the Shepherd model is a suitable, though not necessal\".ily S.tperior, alterr1ative to the Schaefer and Fox dynamic models. Possible extensio'l\"1s and ·amendme'f\"1ts to the dyna<ttic models are suggested. Thest? include the use of Clark's bioeco'l\"1omic 1ttodel to review the f 0 , 1 strategy with regard to economic optimality, and the replacement of the traditional Schaefer and Fox for1tts with a n1ore 9eY1erali:i::ed • surplus growth fur1ctio·l\"I. Also proposed. are an exa1ttination of the effects of changes in mesh si:i::e (on both catchabi l ity and growth parameters> and an adJ.tsted dyna<tric 1ttodel calculatio'f\"1al procedure i'l\"i which catches are 'discounted'. More appropriate weighting procedures for c·atc:·h-effort 1ttodel fits are sttggesteci a'f\"1d lastly, an analysis of vessel power factors is advised.","abstract_html":"Ur1til 1984, hake quota rec:·ottrttreridaticms made by the ICSEAF Scie·,.-1tific:· Advisory Cour1c:·il were based ors the prodtlcticn .. , 1trooe1 approach with evaluations made using a continuous eqi.ti l i br-i utrJ approx imat i ors. However, seri 01..1s di screpar1c·ies betwee&#x27;t&quot;1 mooei. predic:·tior1s arid data bec:·artre appare·nt arid this thesis examines the exter1t to whic:·h these are c:·o&#x27;f&quot;1sequences of. the fa i 1 .t re t 0 a 11 ow f 0 .,.. oy·nartti cs i r1 fitting models to the data. The biology of the hake popttlatio·n and the history of the hake fisheries off the coast of southerl&quot;1 . Afric:·a · a&#x27;r-e reviewed b&#x27;r-iefly ;:rnd the obJectives of fishery tttar1age11&#x27;1e·nt defined. This is followed by a presentation of the data l..tsed ir1 subseql..te&#x27;t&quot;1t calc::-l..tlations together with details of the sc:ti..lrces fr&#x27;otrJ whic:·h they were obtai&#x27;t&quot;1ed. 1&#x27;he basis for the surpl tts prodtu:·t i o·,.-, 1t1odel for the evaluation of sustai&#x27;t&quot;1able yields is discussed. It is show·f&#x27;&quot;s that the steady-state assumptior1 will pretbably lead to positively biased sustainable yield estimates for fisheries whose history is dotr1ir1ated by a dec:·lir:ir1g CPUE t rer1d. !r1 Em attempt to c:·orrect for suc:·h biases, evaluations a&#x27;re also carried ottt usir1g Gt1llal&quot;1cFs method of averaging effort data. However it is riot c·lear to what extent this eqt1i 1 i bri um c:pprox itr1at i or1 approac:·h c::-ompemsates for Sl..tch errors. Col&quot;1sequerrt ly, discrete dynamic- versions of the Schaefer and Fo&gt;t models are fitted, i..tsi ng nor11 l near tt1i ni1t1i Lat i or1 procedures, to catch-effort data for the fottr ICSEAF areas commonly chosen for hake stock assessment purposes, nEUl&#x27;lely Divisiol&quot;1S 1.3 + 1.4, 1.5, 1.6 and 2.1 + 2.2 (all of which indicate generally downward CPUE trends for the maJOT&#x27; part of their histories&gt;. Monte Carlo simulation methods are employed to estitt1ate coefficients of variation for· the trJodel parameter and yield values assessed. The dyr1amic models aT&#x27;e show-n to p.,..ovide disti·nctly .ittrproved fits to the CPUE time series c:·ompared to those obtained ttsing the Gullcfl&#x27;&quot;1d FunctioY1al Regression &lt;GFR&gt; or the steady-state approaches. MSY estifrrates obtail&quot;1ed from dyr1atrtic:· model fits a.,..e, on average, appro&gt;tifflately 1(&gt;~ less than those resulting from the GFR procedu.,..e. Since the effects of 1..mcertainties (s1..tch as adverse environmental variability and the imprec::-ision of stoc~ biomass estittrates} can critically influence the outcoffle of mcmagement dec-i si ons, caution should be e&gt;terci sed when 1t1ak i ng catch l i1rd t recomme·ndat ions. Various conservative approaches are advocated, arid the associated current catch limit recommendatior1s evaluated. These incltlde the Gulland and Boerefl&#x27;!a f 0 , 1 p&quot;rocedl..tre, and an approac::-h where the qttota is reduced by a fraction of the standard error of the initial quota estimate. v The dynamic moaei is also employed to predict future biomass (as well as CPUE and quota} values. A historical examirratio&#x27;t&#x27;&quot;r of the ac:·c:·ttracy of suc:·h proJectiorrs· is used to c:·ott1&lt;t1ent uporr the effic:·acy of the Schaefer and Fox ciy.,..1a111ic tt1odel s •. Dyr1att1ic model biomass estimates are co&lt;t1pared to those provided by the Virtual Population Ar1cclysi s CVPA&gt; p&#x27;r&#x27;oc:·edure for Division 1.6 • Large discrepancies in both recent t re·nds arid ccbsol .te val ttes cc re eviderrt, with biomass estimates bei&#x27;t&#x27;&quot;rg much lower i·n the cccse of VPA. Vs ri ous ext ensi O&#x27;t&#x27;&quot;1s to the dyl&quot;1cc&lt;tti c model a re i .,..,t roduc:·ed i .,.., an at t e&lt;t1pt to red uc:·e the difference bet ween dyrrc:&lt;tr i c &lt;ttode 1 ;:md VPA biomass estimates ir1 Division 1.6. In general, the ir1corporatiorr iY1 the dyY1a&lt;tdc:· &lt;t1odel of ti111e lag effects (ir1 the r1et growth fi..mctioY1&gt; a&#x27;!&#x27;&quot;1d increased efficie&#x27;l&#x27;&quot;1cy factors Hrs the catching operatiO&#x27;l&quot;r) yield &#x27;!&#x27;&quot;10 obvious itnprove&lt;trer1t ir1 agreefflent betwee&#x27;!&#x27;&quot;1 dyl&#x27;&quot;1amic:· &lt;t1odel aY1d VPA results. I·l&quot;1 ac:iditio·l&quot;1, the effect of allowir19 the ratio of the biomccss at th.e start of the given CPUE series to· the ca·r&quot;ryiY19 capacity (y 1 /rO to assume val.tes oti&quot;rer thccYr tmity is exattiil&#x27;&quot;red. Results iY1dic·ate that this exter1ded model does ·not appear to have any advantages over models applied ear11er whic:·h asstt&lt;tteo y 1 =r. The seemil&#x27;&quot;rgly i·nsig&#x27;f&quot;1ificant i&lt;ttproveme·nts obtained S.tggest that the origi&#x27;t&#x27;&quot;ral dynamic model ·r1eerly fully e){ploits the i&#x27;t&#x27;&quot;1formatio&#x27;t&#x27;&quot;1 ·c·o·nteYrt of the data arrti that the i&#x27;l&quot;1t1&quot;oductio&#x27;f&quot;1 of fttrther parattreters ca&#x27;t&#x27;&quot;r caltse the su&lt;t1 of squares S.trfac·e to become very flat i&#x27;f&quot;1 the vic:·inity of the &lt;tiiriittrttm that is sought ir1 the fittir1g proc:-edttre. Dy·l&quot;rami.c model fits .tsing the Shepherd surpltts prodttc:·t i o·n forttr (which incorporates a skewness para&lt;tseter&gt; are per·fortned 0&#x27;1&quot;1 the c·atch-effort ciatcc. The ratio of the biotttass at MSY to the carryi&#x27;f&quot;1g capacity (YMsY /K) is shown to be very poorly determined by the catch-effort data (the average coefficie&#x27;f&quot;rt of variat iol&quot;1 of estimates is 30~&gt;. Results indicate that the Shepherd model is a suitable, though not necessal&quot;.ily S.tperior, alterr1ative to the Schaefer and Fox dynamic models. Possible extensio&#x27;l&quot;1s and ·amendme&#x27;f&quot;1ts to the dyna&lt;ttic models are suggested. Thest? include the use of Clark&#x27;s bioeco&#x27;l&quot;1omic 1ttodel to review the f 0 , 1 strategy with regard to economic optimality, and the replacement of the traditional Schaefer and Fox for1tts with a n1ore 9eY1erali:i::ed • surplus growth fur1ctio·l&quot;I. Also proposed. are an exa1ttination of the effects of changes in mesh si:i::e (on both catchabi l ity and growth parameters&gt; and an adJ.tsted dyna&lt;tric 1ttodel calculatio&#x27;f&quot;1al procedure i&#x27;l&quot;i which catches are &#x27;discounted&#x27;. More appropriate weighting procedures for c·atc:·h-effort 1ttodel fits are sttggesteci a&#x27;f&quot;1d lastly, an analysis of vessel power factors is advised.","abstract_has_math":false,"creators":["Andrew, P A"],"institution":"Department of Mathematics and Applied Mathematics","degree_name":null,"degree_level":null,"degree_discipline":null,"degree_department":null,"school":null,"contributors":[],"advisors":["Butterworth, D. S."],"committee_chairs":[],"committee_members":[],"year":1986,"date_issued":"1986","date_published":"1986","updated_at":"2026-07-22T22:23:45Z","subjects":["Mathematics"],"languages":[],"rights":[],"rights_urls":[],"identifier_entries":[]},"links":{"outbound_url":"http://hdl.handle.net/11427/40463","outbound_label":"Handle","outbound_source":"dc:identifier.uri"},"metadata_groups":[{"id":"people","label":"People","entries":[{"key":"dc:contributor.advisor","label":"Advisor","values":["Butterworth, D. S."]},{"key":"dc:creator","label":"Author","values":["Andrew, P A"]}]},{"id":"academic_context","label":"Academic Context","entries":[{"key":"dc:date.accessioned","label":"Dc Date Accessioned","values":["2024-07-23T13:07:48Z"]},{"key":"dc:date.available","label":"Dc Date Available","values":["2024-07-23T13:07:48Z"]},{"key":"dc:date.issued","label":"Date","values":["1986"]},{"key":"dc:publisher.department","label":"Dc Publisher Department","values":["Department of Mathematics and Applied Mathematics"]},{"key":"dc:type","label":"Dc Type","values":["Thesis / Dissertation"]},{"key":"dc:type.qualificationlevel","label":"Dc Type Qualificationlevel","values":["Masters","MSc"]}]},{"id":"subjects_keywords","label":"Subjects and Keywords","entries":[{"key":"dc:subject","label":"Dc Subject","values":["Mathematics"]}]},{"id":"identifiers","label":"Identifiers","entries":[{"key":"dc:identifier.uri","label":"Identifier URI","values":["http://hdl.handle.net/11427/40463"]}]},{"id":"additional","label":"Additional Metadata","entries":[{"key":"dc:description.abstract","label":"Abstract","values":["Ur1til 1984, hake quota rec:·ottrttreridaticms made by the ICSEAF Scie·,.-1tific:· Advisory Cour1c:·il were based ors the prodtlcticn .. , 1trooe1 approach with evaluations made using a continuous eqi.ti l i br-i utrJ approx imat i ors. However, seri 01..1s di screpar1c·ies betwee't\"1 mooei. predic:·tior1s arid data bec:·artre appare·nt arid this thesis examines the exter1t to whic:·h these are c:·o'f\"1sequences of. the fa i 1 .t re t 0 a 11 ow f 0 .,.. oy·nartti cs i r1 fitting models to the data. The biology of the hake popttlatio·n and the history of the hake fisheries off the coast of southerl\"1 . Afric:·a · a'r-e reviewed b'r-iefly ;:rnd the obJectives of fishery tttar1age11'1e·nt defined. This is followed by a presentation of the data l..tsed ir1 subseql..te't\"1t calc::-l..tlations together with details of the sc:ti..lrces fr'otrJ whic:·h they were obtai't\"1ed. 1'he basis for the surpl tts prodtu:·t i o·,.-, 1t1odel for the evaluation of sustai't\"1able yields is discussed. It is show·f'\"s that the steady-state assumptior1 will pretbably lead to positively biased sustainable yield estimates for fisheries whose history is dotr1ir1ated by a dec:·lir:ir1g CPUE t rer1d. !r1 Em attempt to c:·orrect for suc:·h biases, evaluations a're also carried ottt usir1g Gt1llal\"1cFs method of averaging effort data. However it is riot c·lear to what extent this eqt1i 1 i bri um c:pprox itr1at i or1 approac:·h c::-ompemsates for Sl..tch errors. Col\"1sequerrt ly, discrete dynamic- versions of the Schaefer and Fo>t models are fitted, i..tsi ng nor11 l near tt1i ni1t1i Lat i or1 procedures, to catch-effort data for the fottr ICSEAF areas commonly chosen for hake stock assessment purposes, nEUl'lely Divisiol\"1S 1.3 + 1.4, 1.5, 1.6 and 2.1 + 2.2 (all of which indicate generally downward CPUE trends for the maJOT' part of their histories>. Monte Carlo simulation methods are employed to estitt1ate coefficients of variation for· the trJodel parameter and yield values assessed. The dyr1amic models aT'e show-n to p.,..ovide disti·nctly .ittrproved fits to the CPUE time series c:·ompared to those obtained ttsing the Gullcfl'\"1d FunctioY1al Regression <GFR> or the steady-state approaches. MSY estifrrates obtail\"1ed from dyr1atrtic:· model fits a.,..e, on average, appro>tifflately 1(>~ less than those resulting from the GFR procedu.,..e. Since the effects of 1..mcertainties (s1..tch as adverse environmental variability and the imprec::-ision of stoc~ biomass estittrates} can critically influence the outcoffle of mcmagement dec-i si ons, caution should be e>terci sed when 1t1ak i ng catch l i1rd t recomme·ndat ions. Various conservative approaches are advocated, arid the associated current catch limit recommendatior1s evaluated. These incltlde the Gulland and Boerefl'!a f 0 , 1 p\"rocedl..tre, and an approac::-h where the qttota is reduced by a fraction of the standard error of the initial quota estimate. v The dynamic moaei is also employed to predict future biomass (as well as CPUE and quota} values. A historical examirratio't'\"r of the ac:·c:·ttracy of suc:·h proJectiorrs· is used to c:·ott1<t1ent uporr the effic:·acy of the Schaefer and Fox ciy.,..1a111ic tt1odel s •. Dyr1att1ic model biomass estimates are co<t1pared to those provided by the Virtual Population Ar1cclysi s CVPA> p'r'oc:·edure for Division 1.6 • Large discrepancies in both recent t re·nds arid ccbsol .te val ttes cc re eviderrt, with biomass estimates bei't'\"rg much lower i·n the cccse of VPA. Vs ri ous ext ensi O't'\"1s to the dyl\"1cc<tti c model a re i .,..,t roduc:·ed i .,.., an at t e<t1pt to red uc:·e the difference bet ween dyrrc:<tr i c <ttode 1 ;:md VPA biomass estimates ir1 Division 1.6. In general, the ir1corporatiorr iY1 the dyY1a<tdc:· <t1odel of ti111e lag effects (ir1 the r1et growth fi..mctioY1> a'!'\"1d increased efficie'l'\"1cy factors Hrs the catching operatiO'l\"r) yield '!'\"10 obvious itnprove<trer1t ir1 agreefflent betwee'!'\"1 dyl'\"1amic:· <t1odel aY1d VPA results. I·l\"1 ac:iditio·l\"1, the effect of allowir19 the ratio of the biomccss at th.e start of the given CPUE series to· the ca·r\"ryiY19 capacity (y 1 /rO to assume val.tes oti\"rer thccYr tmity is exattiil'\"red. Results iY1dic·ate that this exter1ded model does ·not appear to have any advantages over models applied ear11er whic:·h asstt<tteo y 1 =r. The seemil'\"rgly i·nsig'f\"1ificant i<ttproveme·nts obtained S.tggest that the origi't'\"ral dynamic model ·r1eerly fully e){ploits the i't'\"1formatio't'\"1 ·c·o·nteYrt of the data arrti that the i'l\"1t1\"oductio'f\"1 of fttrther parattreters ca't'\"r caltse the su<t1 of squares S.trfac·e to become very flat i'f\"1 the vic:·inity of the <tiiriittrttm that is sought ir1 the fittir1g proc:-edttre. Dy·l\"rami.c model fits .tsing the Shepherd surpltts prodttc:·t i o·n forttr (which incorporates a skewness para<tseter> are per·fortned 0'1\"1 the c·atch-effort ciatcc. The ratio of the biotttass at MSY to the carryi'f\"1g capacity (YMsY /K) is shown to be very poorly determined by the catch-effort data (the average coefficie'f\"rt of variat iol\"1 of estimates is 30~>. Results indicate that the Shepherd model is a suitable, though not necessal\".ily S.tperior, alterr1ative to the Schaefer and Fox dynamic models. Possible extensio'l\"1s and ·amendme'f\"1ts to the dyna<ttic models are suggested. Thest? include the use of Clark's bioeco'l\"1omic 1ttodel to review the f 0 , 1 strategy with regard to economic optimality, and the replacement of the traditional Schaefer and Fox for1tts with a n1ore 9eY1erali:i::ed • surplus growth fur1ctio·l\"I. Also proposed. are an exa1ttination of the effects of changes in mesh si:i::e (on both catchabi l ity and growth parameters> and an adJ.tsted dyna<tric 1ttodel calculatio'f\"1al procedure i'l\"i which catches are 'discounted'. More appropriate weighting procedures for c·atc:·h-effort 1ttodel fits are sttggesteci a'f\"1d lastly, an analysis of vessel power factors is advised."]},{"key":"dc:title","label":"Title","values":["Dynamic catch-effort models for the southern African hake populations"]}]}],"canonical_facts":{"dc:contributor.advisor":["Butterworth, D. S."],"dc:creator":["Andrew, P A"],"dc:date.accessioned":["2024-07-23T13:07:48Z"],"dc:date.available":["2024-07-23T13:07:48Z"],"dc:date.issued":["1986"],"dc:description.abstract":["Ur1til 1984, hake quota rec:·ottrttreridaticms made by the ICSEAF Scie·,.-1tific:· Advisory Cour1c:·il were based ors the prodtlcticn .. , 1trooe1 approach with evaluations made using a continuous eqi.ti l i br-i utrJ approx imat i ors. However, seri 01..1s di screpar1c·ies betwee't\"1 mooei. predic:·tior1s arid data bec:·artre appare·nt arid this thesis examines the exter1t to whic:·h these are c:·o'f\"1sequences of. the fa i 1 .t re t 0 a 11 ow f 0 .,.. oy·nartti cs i r1 fitting models to the data. The biology of the hake popttlatio·n and the history of the hake fisheries off the coast of southerl\"1 . Afric:·a · a'r-e reviewed b'r-iefly ;:rnd the obJectives of fishery tttar1age11'1e·nt defined. This is followed by a presentation of the data l..tsed ir1 subseql..te't\"1t calc::-l..tlations together with details of the sc:ti..lrces fr'otrJ whic:·h they were obtai't\"1ed. 1'he basis for the surpl tts prodtu:·t i o·,.-, 1t1odel for the evaluation of sustai't\"1able yields is discussed. It is show·f'\"s that the steady-state assumptior1 will pretbably lead to positively biased sustainable yield estimates for fisheries whose history is dotr1ir1ated by a dec:·lir:ir1g CPUE t rer1d. !r1 Em attempt to c:·orrect for suc:·h biases, evaluations a're also carried ottt usir1g Gt1llal\"1cFs method of averaging effort data. However it is riot c·lear to what extent this eqt1i 1 i bri um c:pprox itr1at i or1 approac:·h c::-ompemsates for Sl..tch errors. Col\"1sequerrt ly, discrete dynamic- versions of the Schaefer and Fo>t models are fitted, i..tsi ng nor11 l near tt1i ni1t1i Lat i or1 procedures, to catch-effort data for the fottr ICSEAF areas commonly chosen for hake stock assessment purposes, nEUl'lely Divisiol\"1S 1.3 + 1.4, 1.5, 1.6 and 2.1 + 2.2 (all of which indicate generally downward CPUE trends for the maJOT' part of their histories>. Monte Carlo simulation methods are employed to estitt1ate coefficients of variation for· the trJodel parameter and yield values assessed. The dyr1amic models aT'e show-n to p.,..ovide disti·nctly .ittrproved fits to the CPUE time series c:·ompared to those obtained ttsing the Gullcfl'\"1d FunctioY1al Regression <GFR> or the steady-state approaches. MSY estifrrates obtail\"1ed from dyr1atrtic:· model fits a.,..e, on average, appro>tifflately 1(>~ less than those resulting from the GFR procedu.,..e. Since the effects of 1..mcertainties (s1..tch as adverse environmental variability and the imprec::-ision of stoc~ biomass estittrates} can critically influence the outcoffle of mcmagement dec-i si ons, caution should be e>terci sed when 1t1ak i ng catch l i1rd t recomme·ndat ions. Various conservative approaches are advocated, arid the associated current catch limit recommendatior1s evaluated. These incltlde the Gulland and Boerefl'!a f 0 , 1 p\"rocedl..tre, and an approac::-h where the qttota is reduced by a fraction of the standard error of the initial quota estimate. v The dynamic moaei is also employed to predict future biomass (as well as CPUE and quota} values. A historical examirratio't'\"r of the ac:·c:·ttracy of suc:·h proJectiorrs· is used to c:·ott1<t1ent uporr the effic:·acy of the Schaefer and Fox ciy.,..1a111ic tt1odel s •. Dyr1att1ic model biomass estimates are co<t1pared to those provided by the Virtual Population Ar1cclysi s CVPA> p'r'oc:·edure for Division 1.6 • Large discrepancies in both recent t re·nds arid ccbsol .te val ttes cc re eviderrt, with biomass estimates bei't'\"rg much lower i·n the cccse of VPA. Vs ri ous ext ensi O't'\"1s to the dyl\"1cc<tti c model a re i .,..,t roduc:·ed i .,.., an at t e<t1pt to red uc:·e the difference bet ween dyrrc:<tr i c <ttode 1 ;:md VPA biomass estimates ir1 Division 1.6. In general, the ir1corporatiorr iY1 the dyY1a<tdc:· <t1odel of ti111e lag effects (ir1 the r1et growth fi..mctioY1> a'!'\"1d increased efficie'l'\"1cy factors Hrs the catching operatiO'l\"r) yield '!'\"10 obvious itnprove<trer1t ir1 agreefflent betwee'!'\"1 dyl'\"1amic:· <t1odel aY1d VPA results. I·l\"1 ac:iditio·l\"1, the effect of allowir19 the ratio of the biomccss at th.e start of the given CPUE series to· the ca·r\"ryiY19 capacity (y 1 /rO to assume val.tes oti\"rer thccYr tmity is exattiil'\"red. Results iY1dic·ate that this exter1ded model does ·not appear to have any advantages over models applied ear11er whic:·h asstt<tteo y 1 =r. The seemil'\"rgly i·nsig'f\"1ificant i<ttproveme·nts obtained S.tggest that the origi't'\"ral dynamic model ·r1eerly fully e){ploits the i't'\"1formatio't'\"1 ·c·o·nteYrt of the data arrti that the i'l\"1t1\"oductio'f\"1 of fttrther parattreters ca't'\"r caltse the su<t1 of squares S.trfac·e to become very flat i'f\"1 the vic:·inity of the <tiiriittrttm that is sought ir1 the fittir1g proc:-edttre. Dy·l\"rami.c model fits .tsing the Shepherd surpltts prodttc:·t i o·n forttr (which incorporates a skewness para<tseter> are per·fortned 0'1\"1 the c·atch-effort ciatcc. The ratio of the biotttass at MSY to the carryi'f\"1g capacity (YMsY /K) is shown to be very poorly determined by the catch-effort data (the average coefficie'f\"rt of variat iol\"1 of estimates is 30~>. Results indicate that the Shepherd model is a suitable, though not necessal\".ily S.tperior, alterr1ative to the Schaefer and Fox dynamic models. Possible extensio'l\"1s and ·amendme'f\"1ts to the dyna<ttic models are suggested. Thest? include the use of Clark's bioeco'l\"1omic 1ttodel to review the f 0 , 1 strategy with regard to economic optimality, and the replacement of the traditional Schaefer and Fox for1tts with a n1ore 9eY1erali:i::ed • surplus growth fur1ctio·l\"I. Also proposed. are an exa1ttination of the effects of changes in mesh si:i::e (on both catchabi l ity and growth parameters> and an adJ.tsted dyna<tric 1ttodel calculatio'f\"1al procedure i'l\"i which catches are 'discounted'. More appropriate weighting procedures for c·atc:·h-effort 1ttodel fits are sttggesteci a'f\"1d lastly, an analysis of vessel power factors is advised."],"dc:identifier.uri":["http://hdl.handle.net/11427/40463"],"dc:publisher.department":["Department of Mathematics and Applied Mathematics"],"dc:subject":["Mathematics"],"dc:title":["Dynamic catch-effort models for the southern African hake populations"],"dc:type":["Thesis / Dissertation"],"dc:type.qualificationlevel":["Masters","MSc"]},"updated_at":"2026-07-22T22:23:45Z"}