THE INCIDENCE OF MAJOR LEPIDOPTERAN PESTS ON CABBAGE AND THEIR ASSOCIATED PARASITOIDS IN GHANA By MILLICENT ASAABA COBBLAH b I t cz THE INCIDENCE OF MAJOR LEPIDOPTERAN PESTS ON CABBAGE AND THEIR ASSOCIATED PARASITOIDS IN GHANA This Thesis is Submitted to the University o f Ghana, Legon, in Fulfillment o f the Requirements for the Award o f Doctor o f Philosophy (Ph. D.) Zoology Degree. By Millicent Asaaba Cobblah B.Sc. Honours (Zoology), University o f Ghana, Legon. Postgraduate Diploma & M.Sc. (Applied Insect Taxonomy), University o f Wales, Cardiff United Kingdom. Department o f Animal Biology and Conservation Science, Faculty o f Science, University o f Ghana, Legon. August, 2009 DECLARATION I hereby declare that the work herein submitted as a thesis for the Doctor of Philosophy Degree in Zoology (Entomology) is the result of my own investigations and has not been submitted for a similar degree in any other University. MILLICENT ASAABA COBBLAH (Ph.D. Candidate) DATE "T, 2o / / DATE.... DEDICATION To my daughter Amanda Aku Ahornam Awadey who I left several times as a little girl to carry out this work and to my family who took care of Amanda when I had to travel. . r' Y x ! I ACKNOWLEDGEMENTS \ j I wish to acknowledge the National Agricultural Research Programme (NARP) of the CSIR Ghana, the USA Embassy (Fulbright Scholarship), the FAO/UNDP Farmer Field Schools Programme, and the University of Ghana (Leventis Scholarship) for providing the funds to cany out this study. I specially thank my supervisors: Prof. Kwame Afreh - Nuamah (Institutes of Agricultural Research), Dr. D. D. Wilson and Prof. E. 0 . Owusu (Department of Animal Biology and Conservation Science, DABCS), all of the University of Ghana. I am grateful to the specialists at CABI Bioscience, U.K for identification and confirmation of the parasitoids and pests, Dr. Virendra Gupta under whom I worked for one year whilst on the Fulbright Scholarship and Dr. Butler who assisted with photography of the parasitoids, both of the Department of Entomology and Nematology. University of Florida. USA, Drs. J. Okine and E. R. Mitchell of the USDA, Gainesville, Florida who assisted with explanation on parasitoid biology. My gratitude goes to the staff of WEICO. Weija for providing the land and other resources for field work. 1 am also indebted to Ms. Joyce Heflide and, Messrs. Adzo and Aboah for assistance in the field and laboratory work, Mr. F. Ansah, the chief technician, Mr. F. Sekou of Botany Department and Prof. Chris Gordon (VBRP) who assisted with aspects of the photography. I cannot forget the role played by my loyal friend the late Mr. S. Mensah a technician of the then Department of Zoology who worked tirelessly with me in the field at Weija. My gratitude goes to the following: Prots. Obeng-Ofori and Ntiamoah-Baidoo, Drs. Bimi and Darpaah. I appreciate the assistance given by Mr. Osae of BNARI, GAEC and Mr. Avicor (ARPP1S) in the use of the SPSS software and sharing their knowledge in the statistical analysis and graphics. Finally, 1 thank Mr. E. Nyarko of the Ghana Science Association Secretariat, Legon, for typesetting this thesis. v COPYRIGHT All rights reserved. No part of this thesis may be reproduced, stored in any retrieval system or transmitted in any form or by any means; electronic, mechanical, recording or otherwise, without prior written permission from the author or the University of Ghana, Legon. vi ABSTRACT The study was carried out at the Weija Irrigation Company site at Tubaman, Weija, the Laboratories of the Department of Zoology (now Department of Animal Biology and Conservation Science, DABCS), University of Ghana, Legon and some selected districts of Ghana. It was designed to; identify and establish the major Lepidopteran pests on cabbage, Brassica oleracea (L.) var. capitata and their parasitoids, determine the effect of the commonly used insecticides on parasitism and the biology of the major parasitoid, describe and illustrate the pests and their parasitoids to aid in identification. The rationale for the study was to provide information for implementation of effective integrated pest management in cabbage production in Ghana. Field studies were carried out at the Weija site for three years. The design of the experiments was a randomized complete block design. Indirect and direct methods were used to investigate the effect of four insecticides namely, a synthetic pyrethroid (Karate), a Bacillus thuringiensis formulation, neem seed water extract and a commercial neem formulation, (Neemazal) on the major parasitoid. The illustrations were made using the scanning electron microscope, photomicroscope, a digital camera and Camera Lucida drawings. The pests recorded were Plulella xylostella L., Trichoplusia rti (Hvibner). Hellula undalis (F), Helicoverpa armigera (HUbner) and Spodoptera littoralis (Boisduval). Plulella xylostella was the most abundant pest recorded during the study period. There was no significant difference between its larval density per plant in the major rainy season (0.15 ± 0.04, p > 0.05) compared with the minor rainy season (0.20 ± 0.07, p > 0.05): and also between the minor rainy season and the dry season (0.29 ± 0.5, p > 0.05). On the other hand, T. ni was only abundant during the major rainy season. There was a significant difference between larval density per plant during this season (0.60 ± 0.11, p < 0.05) compared with the other seasons. With regard to S. litloralis, there was a significant difference between its larval density per plant in the minor rainy season (0.39 ± 0.10, p < 0.05) compared with the other seasons. The other pests occurred in insignificant numbers. Out of the 15 species of parasitoids recorded from the pests, 7 were identified to the species level, 6 to the generic level and 2 to species groups. Seven of the species: Charops sp.. Brachymeria sp.. Hockeria sp., Elasmus sp., Notanisomorphella sp., Tetrastichus atriclavus S.L., Pediobius sp. and Trichomalopsis sp. were recorded for the first time in Ghana and may also be new species. The major parasitoid was Cotesia plutellae (Kurdjumov) which accounted for 92% and 60.9% of the parasitoids recorded from P. xylosiella and T. ni, respectively. The second important parasitoid was Euplectrus laphygmae (Ferriere) and it was specific to T. ni and S. litloralis. The facultative hyperparasitoids of P. xylostella were Oomyzus sokolowskii (Kurdjumov), Elasmus sp.? Aphanogmus reticulatus (Fouts) and Trichomalopsis sp. via C. plutellae. Blepharella vasta (Karsh), Peribaea orbata (Wiedemann), Notanisomorphella sp and Chelonus cunirnaculaliis (Cameron) were specific to the larvae of S. littoralis. No parasitoids were recorded from H. armigera. No egg parasitoid was observed. There was seasonal variation in parasitism of P. xylostella by C. plutellae. The rate of parasitism (68 .6 ± 12.9%, p < 0.05) was significantly highest in the major rainy season and significantly least (9.9 ± 7.1 %, p < 0.05) in the minor rainy season. The rate of parasitism of P. xylostella by C. plutellae did not differ among the unsprayed and insecticide treated plots. However, adult C. plutellae emerging from pests collected from 'Karate' treated plots sometimes died in the process of eclosion or were short - lived. Neem seed water extract applied at 50 g/l also adversely affected the ability of the parasitoid larva to spin its cocoon for pupation. Of the three insecticides. ‘Karate’ was the most toxic causing 100% mortality to the adult Cotesia pluiellae within ten seconds of direct exposure. Neemazal and Bt. applied at 1.0% and 1 .Og/liter of water respectively, were the least toxic to the adult. It is concluded that P. xylostella is the major pest of cabbage in Ghana, while T. ni and S. littoralis are abundant only during the major and minor rainy seasons respectively. Cotesia pluiellae and E. laphygmae are the major parasitoids and they should be considered in the development of any integrated pest management on cabbage. Karate has a harmful effect on C. pluiellae adults. Even though, Neem seed applied at 50g/I adversely affected the development of C. pluiellae, lower doses, or Bacillus thuringiensis formulations could be applied in the development of an Integrated Pest Management programme on cabbage. TABLE OF CONTENTS DECLARATION................................................................................................................ «« DEDICATION.................................................................................................................... iv ACKNOWLEDGEMENTS............................................................................................... v COPYRIGHT..................................................................................................................... vi ABSTRACT....................................................................................................................... vii TABLE OF CONTENTS.................................................................................................. x LIST OF TABLES.............................................................................................................. xvi LIST OF FIGURES............................................................................................................ xvii LIST OF PLATES.............................................................................................................. xviii CHAPTER ONE............................................................................................................... I 1.0 GENERAL INTRODUCTION....................................................................... 1 CHAPTER TWO............................................................................................................. 6 2.0 LITERATURE REVIEW................................................................................. 6 2.1 Insect Pests of Cabbage.................................................................................... 6 2.2 Origin and Distribution of the Pests................................................................ 10 2.3 Description of the Pests.................................................................................... 11 2.4 Life History of the Pests................................................................................... 13 2.5 Host Range of the Pests.................................................................................... 16 2.6 Damage by the Pests to Cabbage..................................................................... 1 g 2.7 Seasonal Incidence of the Pests........................................................................ 20 2.8 Mortality Factors Influencing the Survival of the Pests.................................. 23 2.8.1 Plutella xylostella............................................................................................. 23 Page x €j*J * K- vHjv; 2.8.1.1 Rainfall , ^ T . .......................... 24 2.8.1.2 Parasitoids.............................................................................................................. 24 2.8.2 Trichoplusia ni....................................................................................................... 27 2.8.2.1 Parasitoids.............................................................................................................. 27 2.8.2.2 Nuclear Polyhedrosis Virus.................................................................................. 27 2.8.3 Hellula undalis....................................................................................................... 28 2.9 Control Measures Against the Pests.................................................................... 28 2.9.1 Chemical Control................................................................................................... 28 2.9.2 Biological Control................................................................................................. 31 2.9.3 Integrated Pest Management................................................................................. 37 CHAPTER THREE.............................................................................................................. 40 3 0 SEASONAL VARIATION OF PARASITOID-HOST ASSOCIATIONS AND EFFECT OF INSECTICIDES.................................................................. 40 3.1 Introduction............................................................................................................ 40 3.2 Materials and Methods......................................................................................... 41 3.2.1 The Experimental Site ......................................................................................... 41 3.2.2 Planting................................................................................................................. 42 3.2.3 The Experimental Layout..................................................................................... 43 3.2.4 Treatments Applied.............................................................................................. 43 3.2.5 Fertiliser Application............................................................................................ 44 3.2.6 Insecticide Application......................................................................................... 44 3.2.7 Incidence and Seasonal Abundance of Pests and Parasitoids.............................. 46 Table of Contents Cont’d. f c / ]:< i, xi Table o f Contents Cont'd. 3.2.8 Laboratory Rearing of Pests............................................................................. 47 3.2.9 Weekly Parasitism Trends by Cotesia pluiellae and Euplectrus laphygmae in Relation to Plutella xylostella and Trichoplusia ni .................................. 47 3.2.10 Identification of Pests and Parasitoids.............................................................. 48 3.2.11 Emergence and Mortality of Cotesia plutellae Exposed to Insecticides 48 3.2.12 Laboratory Studies on Mortality of Adults and Emergence of Pupae of C. pluiellae Exposed to Different Insecticides............................................ 49 3.2.12.1 Filter Paper Method.......................................................................................... 49 3.2.12.2 Direct Application Method............................................................................... 50 3.2.13 Statistical Analysis............................................................................................ 51 3.3 Results............................................................................................................... 52 3.3.1 Incidence and Seasonal Abundance of Lepidopteran Pests............................ 52 3.3.2 Comparative Abundance of Larvae of Lepidopteran Pests on Unsprayed Experimental Plots and on Farmer’s Plots at Weija.................... 55 3.3.3 Population Density of Larvae of P. xylostella, T. ni and 5. littoralis on Cabbage in the Three Seasons on Experimental Plots................................... 56 3.3.4 Incidence and Seasonal Abundance of the Parasitoids................................... 57 3.3.5 Weekly Parasitism Trends by C. pluiellae in Relation to P. xy lostella 60 3.3.6 Weekly Parasitism Trends by C. pluiellae and E. laphygmae in Relation to T. ni.............................................................................................................. 63 3.3.7 Parasitism of P. xylostella by C. plutellae in Three Seasons.......................... 64 3.3.8 Parasitism of P. xylostella by C. pluiellae on Insecticide Treated Plots 64 Page xii Table o f Contents Cont’d. 3.3.9 Parasitism of T ni by C. plutellae and E. laphygmae in the Major Rainy Season................................................................................................... 65 3.3.10 Parasitism of T. ni by C. plutellae and E. laphygmae on Insecticide Treated Plots.................................................................................................... 65 3.3.11 Emergence of C. plutellae Adults from Field Parasitised Pests .................... 66 3.3.12 Emergence of C. plutellae Adults Collected as Pupae Exposed to Different Insecticides in the Field................................................................... 67 3.3.13 Mortality of C. plutellae Adults and Emergence of Pupae Exposed to Insecticides in the Laboratory......................................................................... 68 3.4 Discussion.......................................................................................................... 69 CHAPTER FOUR........................................................................................................... 79 4.0 BIOLOGY AND ECOLOGY OF THE PARASITOIDS OF LEPIDOPTERAN PESTS OF CABBAGE.................................................... 79 4.1 Introduction........................................................................................................ 79 4.2 Materials and Methods..................................................................................... 81 4.2.1 Field Sampling and Rearing of Host - Plutella xylostella.............................. 81 4.2.2 Field Collection and Rearing of Parasitoids.................................................... 82 4.2.3 Life History and Lifestyle Studies of Cotesia plutellae ................................. 82 4.2.4 Longevity Studies of Cotesia plutellae............................................................ 83 4.2.5 Oviposition Preference of Plutella xylostella Larvae by Cotesia plutellae... 84 4.2.6 Field Observations on Biology and Ecology of the Parasitoids .................... 84 Page xiii Table o f Contents Cont’d. 4.3 Results.............................................................................................................. 85 4.3.1 Biology and Ecology of Cotesia plutellae...................................................... 85 4.3.1.1 Life History and Lifestyle of C. plutellae....................................................... 85 4.3.1.2 Longevity of Mated and Unmated Adult Cotesia plutellae............................ 87 4.3.1.3 Oviposition Preference of Plutella xylostella Larvae by Cotesia plutellae... 87 4.3.1.4 Field Observations on Parasitism by C. plutellae........................................... 88 4.3.2 Biology' and Ecology of Other Parasitoids...................................................... 90 4.4 Discussion......................................................................................................... 98 CHAPTER FIVE............................................................................................................. 104 5.0 DESCRIPTION OF STAGES OF LEPIDOPTERAN PESTS. BEHAVIOUR AND DAMAGE..................................................................... 104 5.1 Introduction....................................................................................................... 104 5.2 Materials and Methods.................................................................................... 105 5.2.1 Rearing of Lepidopteran Pests........................................................................ 105 5.3 Results.............................................................................................................. 106 5.3.1 Description of Stages of Lepidopteran Pests, Behaviour and Damage 106 5.3.1.1 Plulella xylostella (Linnaeus)......................................................................... 106 5.3.1.2 Trichoplusia ni (HUbner)................................................................................. I l l 5.3.1.3 Spodoptera littoralis (Boisduval).................................................................... 114 5.3.1.4 Helicoverpa armigera (HUbner)..................................................................... 1 ] 9 5.3.1.5 Hellula undalis Walker.................................................................................... 121 5.3.1.6 Spoladea recurvalis (Fabricius)...................................................................... 123 Page ;:iv Table o f Contents Cont’d. 5.4 Discussion......................................................................................................... 124 CHAPTER SIX................................................................................................................. 127 6.0 DESCRIPTION OF PARASITOIDS OF THE LEPIDOPTERAN PESTS OF CABBAGE.................................................................................. 127 6.1 Introduction....................................................................................................... 127 6.2 Materials and Methods.................................................................................... 129 62 .1 Identity and Description of Parasitoids............................................................ 129 6 2.2 Scanning Electron Microscopy........................................................................ 130 6.2.3 Photomicroscopy............................................................................................. 131 6.3 Results.............................................................................................................. 132 6.3.1 Identity of the Parasitoids................................................................................ 132 6.3.2 Descriptions of the Parasitoids........................................................................ 133 6.3.2.1 Ichneumonoidea............................................................................................... 133 6.3.2.2 Chalcidoidea..................................................................................................... 142 6.3.2.3 Ceraphronoidea................................................................................................ 169 6.3.2.4 Muscoidea......................................................................................................... 172 6.4 Discussion......................................................................................................... 173 CHAPTER SEVEN......................................................................................................... 182 7.0 GENERAL CONCLUSIONS AND RECOMMENDATIONS.................... 182 7.1 Conclusion........................................................................................................ 182 7.2 Recommendations............................................................................................ ] 85 REFERENCES CITED..................................................................................................... 187 APPENDICES................................................................................................................... 224 Page xv LIST OF TABLES Table 2.1: Major Pests of Cabbage and Damage Worldwide..................................... - 9 Table 3.1: Volumes of Insecticides Applied to Cabbage Plants................................. - 45 Table 3.2: Relative Abundance of Larvae of Lepidopteran Pests of Cabbage in the Three Cropping Seasons on the Unsprayed Plots at the Experimental Site, Weija........................................................................... - 54 Table 3.3: Relative Abundance of Larvae of Lepidopteran Pests of Cabbage in the Three Cropping Seasons on Farmer’s Plots at Weija.....................- 55 Table 3.4: Comparative Percentage Abundance of Lepidopteran Pests on Experimental Plots and on Farmer’s Plots.................................................- 56 Table 3.5: Population Density per Plant of Larvae of P. xylostella, T. ni and S. littoralis on Cabbage in the Three Seasons...........................................- 57 Table 3.6: Seasonal Occurrence of Parasitoid/Hyperparasitoid Species and Lepidopteran Host Species on Cabbage at the Experimental Site............- 58 Table 3.7: Mean Percentage Parasitism of P. xylostella by C. plutellae on Different Treatments in the Three Seasons...............................................- 65 Table 3.8: Mean Percentage Parasitism of T. ni by C. plutellae and E. laphygmae on Different Treatments in the Major Rainy Season.........- 65 Table 3.9: Emergence of C. plutellae Adults Reared from Field Parasitized P. xylostella from the Different Treatments in the Three Seasons...........- 66 Table 5.1: Percentage of Eggs Laid in a Batch by P. xylostella in the Field..............- 106 Table 6.1: Identity of the Parasitoids / Hypcrparasitoids Recorded from the Lepidopteran Pests on Cabbage................................................................ j 32 Page xvi LIST OF FIGURES Figure 3.1: Distribution Map of Pests of Cabbage in Southern Ghana........................ - 53 Figure 3.2: Trophic Relationships among P. xylostella, T. ni and Parasitoids and Hyperparasitoids on Cabbage.....................................................................- 60 Figure 3.3: Weekly Parasitism Trends by C. plutellae in Relation to P. xylostella in the Major Rainy Season. Coefficient of Correlation r = 0.97............- 61 Figure 3.4: Weekly Parasitism Trends by C. plutellae in Relation to P. xylostella in the Minor Rainy Season. Coefficient of Correlation r = 0.55 ...........- 61 Figure 3.5: Weekly Parasitism Trends by C. plutellae in Relation to P. xylostella in the Dry Season. Coefficient of Correlation r = 0.66.......................... - 62 Figure 3.6: Weekly Parasitism Trends by C. plutellae and E. laphygmae in Relation to T. ni in the Major Rainy Season.............................................. - 63 Figure 3.7: Seasoned Variation in Mean Percentage Parasitism of P. xylostella by C. plutellae............................................................................................. - 64 Figure 3.8: Emergence of both C. plutellae and E. laphygmae Adults from Field Parasitized T. ni from the Different Treatments in the Major Rainy Season.............................................................................................. - 67 Figure 3.9: Percentage Emergence of C. plutellae Adults Collected as Pupae from the Different Treatments.................................................................... - 68 Figure 3.10: Mortality of Adults and Pupae of C. plutellae Exposed to Different Insecticides.................................................................................................. - 69 Page xvii LIST OF PLATES Plate 4.1: Newly emerged C. plutellae larva (arrowed) and ho s t..............................- 86 Plate 4.2: C. plutellae pupa (arrowed) and host..........................................................* 86 Plate 4.3: Unparasitised P. xylostella larva [xlO ].......................................................- 86 Plate 4.4: Empty pupal cocoon of C. plutellae (arrowed).......................................... - 86 Plate 4.5: Carcass of P. xylostella after parasitism..................................................... - 87 Plate 4.6: Pupa of Charops sp [x 12] hanging by thread after emergence of adult parasitoid............................................................................................ - 91 Plate 4.7: Newly hatched larvae of E. laphygmae [x 2.7] (arrowed) penetrating host to feed................................................................................................. - 93 Plate 4.8: Larvae of E. laphygmae (arrowed) about to migrate to pupate................. - 93 Plate 4.9: Mature larva of E. laphygmae migrating (arrowed) down the host to pupate.............................................................................................. - 93 Plate 4.10: Carcass of T. ni larva after parasitism by E. laphygmae ..........................- 94 Plate 4.11: Adult B. sp. nr. vasta [x 2.5] and pupal case of S. litloralis from which it had emerged............................................................................................. - 97 Plate 4.12: Adult P. orbata [x 14] and its pupal case....................................................- 98 Plate 5.1: Eggs of P. xylostella [x 6 ] on cabbage leaf................................................ - 107 Plates 5.2: Mature larvae of P. xylostella [x 3] and damage on cabbage leaf, faeces are arrowed......................................................................................- 108 Plate 5.3a: Pre-pupa of P. xylostella [x 6 ] ..................................................................... - 109 Plate 5.3b: Mature Pupa of P. xylostella (x 4]............................................................. 109 Plate 5.4: Adult P. xylostella (A-Female [x 3.8], B-Male [x 3.5])........................... - 110 Page List o f Plates Cont'd. Plate 5.5: Mature larva of T. ni [x 4.8]........................................................................" * * 3 Plate 5.6: Freshly pupated T. ni [x 3.7]........................................................................ • • ' 3 Plate 5.7: Adult of T. ni [x 4.0].................................................................................... - 113 Plate 5.8: Egg mass of S. littoralis[x 12].....................................................................- 114 Plate 5.9a-d: Variable colouration in young larvae of S. littoralis..................................- 115 Plate 5.10: Mature caterpillar of S. littoralis [x 3.5].................................................... - 116 Plate 5.11: Larva of S. littoralis [x 2.0] (arrowed) feeding on cabbage head............... - 117 Plate 5.12: Pupa of S. littoralis [x 5] spine arrowed..................................................... - 118 Plate 5.13: Adult of S. littoralis [x 2.7].........................................................................- 118 Plate 5.14a: Larva of H. armigera [x 1.5].......................................................................- 120 Plate 5.14b: Larva of H. armigera [x 1.7].......................................................................- 120 Plate 5.15: Adult of H. armigera [x 2 ] ..........................................................................- 121 Plate 5.16: Larva of H. undalis [x 2.2].......................................................................... - 122 Plate 5.17: Adult of H. undalis [x 3.6]...........................................................................- 123 Plate 5.18: Adults of S. recurvalis [x 2.0].....................................................................- 124 Plate 6.1a: Wing illustration of terminologies...............................................................- 130 Plate 6 .1 b: Antenna illustration of terminologies......................................................... - 130 Plate 6.2: Female Cotesia plutellae [x 13]................................................................... - 133 Plate 6.3: Schematic diagram of fore-wing and hind-wing of C. plutellae [x 17]...- 134 Plate 6.4 a: Schematic diagram of antenna of male C. plutellae [x 20]-.................... 135 Plate 6.4 b: Schematic diagram of antenna of female C. plutellae [x 20] .................. - 135 Page - — xix List of Plates Cont’d. Plate 6.5a: Scanning electron micrograph of female antenna [x 240]..........................- 136 Plate 6.5b: Scanning electron micrograph of male antenna [x 300].............................- 136 Plate 6 .6 : Scanning electron micrograph of facial view of C. plutellae [x 110]......- 137 Plate 6.7a: Scanning electron micrograph dorsal view of mesosoma [x 90]............... - 138 Plate 6.7b: Scanning electron micrograph lateral view of mesosoma [x 66 ] .............. - 138 Plate 6 .8 a: Adult Chelonus curvimaculatus [x 4.0]......................................................- 140 Plate 6 .8 b: Schematic diagram of C. curvimaculatus [x 15] to show carapace - 140 Plate 6.9: Female Charops sp. [x 7.0]......................................................................... - 141 Plate 6.10: Fore and hind wings Charops sp. [x 16].....................................................- 142 Plate 6.11: Female Brachymeria sp. [x 20]..................................................................- 143 Plate 6.12: Female Hockeria sp. [x 40]........................................................................ - 144 Plate 6.13: Schematic diagram of fore-wing of Hockeria sp. [x 40]........................... - 145 Plate 6.14: Adult male [x 17.5] and female [x 16] Elasmus sp.................................... - 146 Plate 6.15: Schematic diagram of antenna of female Elasmus sp. [x 120]....................- 147 Plate 6.16: Schematic diagram of hind leg of Elasmus sp. [x 55]............................... - 148 Plate 6.17: Schematic diagram of forewing of female Elasmus sp. [x 40]................ - 148 Plate 6.18: Adult male Elasmus sp. to show branched antennae [x 30].......................- 149 Plate 6.19: Male [x 44] and female [x 46] E. laphygmae.............................................- 150 Plate 6.20: Schematic diagram of fore-wing and hind-wing of male E. laphygmae [x 30 ]...................................................................................- 152 Plate 6.21: Schematic diagram of hind leg of E. laphygmae [x 90] ......................... - 153 Plate 6.22: Schematic diagram of antenna of female E. laphygmae [x 100]................- 154 Page List o f Plates Cont'd. Plate 6.23: Schematic diagram of antenna of male E. laphygmae [x 100] ................. - 155 Plate 6.24: Male Notanisomorphella sp. [x 21].................................................................• '56 Plate 6.25: Propodaeum and carina [x 29]........................................................................ - 156 Plate 6.26: Schematic diagram of male antenna Notanisomorphella sp. [x 90]......... - 157 Plate 6.27: Female [x 50] and male [x 53] O. sokolowskii.......................................... - 158 Plate 6.28: Schematic diagram of antenna of female [x 82] O. sokolowskii.............. - 159 Plate 6J29: Schematic diagram of antenna of male [x 65] O. sokolowskii................. - 159 Plate 6.30: Schematic diagram of fore-wing of O. sokolowskii [x 40]........................- 160 Plate 6.31: Female Tetrastichus atriclavus s.l. [x 68]..................................................- 161 Plate 6.32 Schematic diagram of antenna of female Tetrastichus atriclavus s.l [x 8 0 ] ....................................................................................- 162 Plate 6.33: Female Pediobius sp [x 29] and male [x 32] ........................................... - 163 Plate 6.34: Schematic diagram of antenna of female Pediobius sp [x 112]............... - 165 Plate 6.35: Schematic diagram of antenna of male Pediobius sp [x 98].....................- 165 Plate 6.36: Female [x 25] Trichomalopsis sp................................................................- 166 Plate 6.37: Male [x 22] Trichomalopsis sp................................................................... - 166 Plate 6.38 Schematic diagram of antenna of female Trichomalopsis sp. [x 67]....... - 167 Plate 6 .39: Schematic diagram of antenna of male Trichomalopsis sp. [x 72]............- 168 Plate 6.40: Schematic diagram of fore-wing of Trichomalopsis sp. [x 82].................- 169 Plate 6.41: Male [x 25] and female [x 41 ] Aphanogmus reticulatus........................... - 170 Plate 6.42: Male [x 40] A. reticulatus............................................................................. ] 70 Plate 6.43: Schematic diagram of antenna of male A. reticulatus [x 96]....................- 171 Page xxi List o f Plates Cont'd. Plate 6.44: Plate 6.45: Plate 6.46: Schematic diagram of antenna of female A. reticulatus [x 90] Blepharella sp. nr. vasta [x 3.8]............................................... Peribaea orbata [x 15]............................................................. CHAPTER ONE GENERAL INTRODUCTION The common cabbage, Brassica oleracea L. var. capitata belongs to the family Brassicaceae, commonly referred to as the Brassicas. It is a native of the Mediterranean regions and Southern England, Wales and Northern France (Norman, 1992). Cabbage is thought to have evolved from a leafy, unbranched, thin-stemmed kale, B. oleracea but it is now cultivated throughout the world for its foliage bud (Prakash and Rao, 1997). It is a biennial herb with short thickened stem surrounded by a mass of overlapping expanding leaves, which form a compact head (Norman, 1992; Obeng-Ofori el al., 2007). Cabbage is usually grown as an annual crop although it is a biennial, which can grow up to 90 cm (Watts and Watts, 1951). When left to complete its cycle, the crop will produce a large more or less dense head of leaves from a condensed stem in the first year, and then, an appreciable intemode elongation will occur in the second year terminating in the formation of inflorescence (Norman, 1992). There is a great variation in the cultivated varieties of cabbage. They differ in shape, size and colour of leaves and size, and in the shape, colour and texture of heads. However, in the common cabbage, the leaves are relatively smooth and form a compact head. Cabbage thrives best in a cool moist climate with temperature of 16-20 °C, but a number of varieties available now are well adapted to the tropics (Norman. 1992). There is no documented evidence as to when cabbage was introduced into Ghana. It is, however, believed to have been cultivated in the country as far back as the 1940's by the British (Sinnadurai, 1992). It may be grown throughout the year if irrigation or other supplementary water is available. It is produced throughout the country, but of less importance in the Upper East Region (Timbilla and Nyarko, 2004). It is popular in the urban areas of Ghana where it is produced mainly by backyard and market gardeners (Ninsin, 1997). In the forest zone, it tends to grow better in the minor rainy season, but on the Accra plains, better yields are obtained during the main season. It does remarkably well at cooler mountainous areas of the country such as Akwapim and Kwahu, and the moist high elevations around Tarkwa in the Western Region (Bangnikon. 1996). Cultivars suitable for production in Ghana are Copenhagen Market, Drumhead, Suttons Tropical, Japanese Hybrid Cabbage, Golden Acre, Suttons Pride of the Market, KK Cross, Oxylus and Marion. Cabbage is used raw in salads such as coleslaw, or as boiled vegetable. It is also used for cooked curries, pickles or sauerkraut. The older leaves discarded during harvesting are used as animal feed. Cabbage is fairly low in calories and proteins, but it is a good source of many minerals, particularly potassium, and it is relatively high in vitamins A, B and C (Norman, 1992). Yield of cabbage in Ghana varies according to the cultivar, weather and quantity of fertilizers applied. The average weight of an early maturing variety could be 1.5 kilogram per head. Thus, yield can vary from 18,000 kilograms per hectare for an early cultivar to 26,000 kilograms for a late cultivar (Obeng-Ofori et al., 2007). The cultivation of cabbage is threatened worldwide by the various lepidopterous pests that attack the crop (Oatman, 1966; Jusoh et. al., 1992; Pratissoli et al., 2008) and cause extensive damage to it (Goodwin, 1979; Hamilton et al., 2004). The major ones are the diamondback moth Plulella xylostella L., the cabbage looper, Trichoplusia ni 2 (Hubner), the imported cabbage worm, Pieris rapae (L.), the webworm, Hellula undalis (F.) and the cabbage head caterpillar, Crocidolomia binotalis Zeller (Smith and Brubaker, 1938; Harcourt, 1956; Sastrosiswojo and Sastrodihardjo, 1986; Walunj and Pawar, 2004; Obeng-Ofori et al., 2007). The control of these pests has depended mainly on the use of synthetic insecticides which has led to emergence of resistance and adverse effects on natural enemies (Verkerk and Wright, 1996; Ninsin, 1997; Dobson et al., 2002). In addition, the increasing cost of chemicals (Obeng-Ofori, 2000; Youdeowei, 2002) and the very frequent application of cocktails without achieving control (Ooi and Sudderuddin, 1978; Sarfraz et al., 2005) make alternative pest management strategies, especially biological control necessary (Abdel-Razek et al., 2006). Even though the diamondback moth, Plutella xylostella is considered the primary pest on cabbage, data on population trends and seasonal incidence are either lacking or poorly documented in many tropical countries (Kuwahara et al., 1995). In Ghana, P. xylostella, Trichoplusia ni and Hellula undalis are considered serious pests on cabbage (Bangnikon, 1996; Obeng-Ofori and Ankrah, 2002; Obeng-Ofori et al., 2007). However, there has neither been a systematic study on their seasonal incidence nor the occurrence of the other lepidopterous pests. Studies have been restricted to pesticide evaluations and a few short-term studies or observations on damage and behaviour. Virtually no study has been carried out to determine the correct identity, action and importance of the natural enemies of these pests on cabbage (Obeng-Ofori et al., 2007). Much of the available literature is on P. xylostella and it is from South East Asia, the Americas and Europe (Harcourt et al.. 3 1955; Oatman and Platner, 1969; Talekar, 1992; Pratissoli el al., 2008). It is therefore imperative that in Ghana, the seasonal incidence of the lepidopterous pests be determined, in order to provide a more sustainable basis for their management and to contribute to the existing body of knowledge. In this study, more emphasis will however, be placed on P. xylostella. Population studies are important for determining the times of the year when damage is caused, the levels of parasitism of the pests of cabbage, appropriate tuning for effective use o f insecticides and other control measures (Kuwahara et al., 1995; Liu et al., 2000; Mosiane et al., 2003). Generally, most of the field data on the relationships between parasitoids and host populations, lack a holistic approach (Guan-Soon, 1992). There is therefore, an urgent need for an in-depth study on the parasitoids in order to appreciate their role and to gain a better understanding of strategies that can be used to manipulate local populations (Mahr, 1996; Riba et al., 1996; Pratissoli et al., 2008). The diamondback moth populations’ native to different regions have morphological and biological differences, and specific parasitoid strains may be associated with the specific diamondback moth strains (Salinas, 1986; Sarfraz et al., 2005). Incorrect identification and the difficulty of associating pests with parasitoids have led to numerous occasions when biological control has either failed or delayed (Yaninek and Herren, 1989; Bio-NET INTERNATIONAL, 1999). The main objective of this study therefore, was to determine the incidence and seasonality of the major Lepidopteran pests of cabbage as well as the associated parasitoids and the levels of parasitism in southern Ghana. The specific objectives were: 1. To determine the major Lepidopteran pests on cabbage in southern Ghana. 2. To determine the parasitoid-host associations in an annual production of cabbage and the effect of commonly used insecticides on parasitism and development of the dominant parasitoid. 3. To study the biology of the parasitoids with emphasis on the dominant one that could be used in an integrated pest management programme. 4. To describe the pests in relation to damage and behaviour on cabbage in southern Ghana. 5. To describe the parasitoids associated with the pests in southern Ghana. 5 CHAPTER TWO 2.0 LITERATURE REVIEW 2.1 Insect Pests of Cabbage Cabbage, Brassica oleracea var. capitata, is a crucifer of economic value that is cultivated worldwide in both the tropics and temperate regions of the world. The crop supports a variety of insect fauna (Oatman and Platner, 1969; Talekar, 1992). Its successful cultivation is hampered by the incidence of various defoliating caterpillars (Srinivasan and Krishna-Moorthy, 1992; Hu et al., 1997; CAB International, 1999). The major insect pests are the diamondback moth, Plulella xylostella, the cabbage looper, Trichoplusia ni, the imported cabbage worm, Pieris rapae, the webworm, Hellula undalis, the variegated grasshopper, Zonocerus variegatus, and the cabbage head caterpillar, Crocidolomia binotalis (Harcourt, 1956; Youdeowei, 2002; Obeng- Ofori et al., 2007; Pratissoli et al., 2008). Other pests recorded on cabbage include the com earworm Helicoverpa armigera (Hubner), the African army worm, Spodoptera exempt a (Walker), cabbage maggot Hylemya brassica (Bouche), cabbage flea beetles Phyllotreta cruciferae (Goeze), and cabbage aphids Brevicoryne brassicae (L.). One or more of these are considered occasional or seasonal pests in various countries (Boling and Pitre, 1971; Waterhouse, 1992; Poelking, 1992; Berg and Cock, 2000). Plulella xylostella is considered the most destructive and occurs worldwide wherever cabbage and other crucifers are grown (Tadashi et al., 1986; Pratissoli et al.. 2008). Attack by P. xylostella can lead to total destruction of the crop at all stages of plant 6 growth, and the production of unmarketable heads (Sachan and Srivastava, 1972; Loke et al.. 1992; Syed, 1992; Sivapragasam and Abdul Aziz, 1992). The 1999 Annual Report of WE1CO, a vegetable growing and irrigation company in Ghana and Obeng-Ofori el al. (2007) indicate that the diamondback moth is a serious pest in various parts of Ghana. Sometimes the crop is harvested prematurely or abandoned due to diamondback moth infestation (Cobblah, 2000). Up to 1972, at least 128 countries or territories had reported the occurrence of P. xylostella (CAB International, 1999). It has been estimated that one billion US dollars is spent annually on its control worldwide in addition to the crop losses it causes (Talekar and Shelton, 1993; Vasquez, et al., 1997; Abdel-Razek et a l, 2006). The level of infestation of P. xylostella varies considerably (Harcourt el al., 1955; Dennill and Pretorius, 1995). It is serious in S. E. Asia (Talekar et al., 1992) and moderately so in parts of Canada and USA (Hardy 1938; Sutherland, 1966; Oatman and Plainer 1969; Hill and Foster, 2000). In Germany and France, it is not present in sufficient numbers to be considered a serious pest (Lim, 1986) whilst in South Africa, it is ranked substantially low (Bell and McGeoch 1996; Kfir, 1997; Mosiane et al.. 2003). A study by Weires and Chiang (1973), found the diamondback moth to be dominant in only three locations while Hellula undalis, Plusia orichalcea (Hubner). Agrotis ipsilon (Hufnagel), Helicoverpa armigera, Crocidolomia binotalis and Spodoplera sp. were dominant in four locations (cited from Sastrodihardjo. 1986). Even though Koshihara (1986) recognised the diamondback moth as an important pest in Japan, the author observed that, prior to head formation, the imported cabbage 7 worm, Pieris rapae and the cabbage armyworm Mamestra brassicae (L.) could cause heavier visual leaf damage. Hellula undalis is a major pest on cabbage seedlings in nurseries as well as transplanted young plants in the field in Guam (Muniappan and Marutani, 1992). It is of growing concern in the lowlands of Malaysia warranting serious attention (Sivapragasam and Abdul Azziz, 1992). However, Ooi (1979a) considered it as a minor pest in low altitudes with cooler temperatures as was observed in India (Sachan and Gangawar. 1980). In Hawaii, Jayma and Ronald (2007) observed that comparatively, the pest is not of great significance. Obeng-Ofori and Ankrah (2002) noted that H. undalis is a serious pest of cabbage in Ghana. Trichoplusia ni is considered a serious pest in many parts of the USA and Canada (Chalfant, 1992; Wyman, 1992; Capinera, 1999) overshadowing the diamondback moth because of its voracious feeding habits (Hill and Foster, 2000). In Thailand it is considered as a minor pest, though potentially very damaging to young plants from seedling to bolting (Rowell et al, 1992). The authors added that it appears to cause little damage after this stage. In Nigeria, the pest can reach epidemic levels on cabbage when not controlled (Anene and Dike, 1996). In Ghana, T. ni can cause considerable damage to the cabbage leaves and heart (Obeng-Ofori and Ankrah. 2002). Crocidolomia binotalis, though a secondary pest of cabbage in Indonesia, can be a serious problem in the dry season (Sastrosiswojo and Setiawati, 1992) and is important at certain times of the year in Malaysia where it occurs with the 8 diamondback moth (Kadir, 1992). Various species of armyworms such as Spodoptera exigua (Hubner) may be serious pests on cabbage in parts of S. E. Asia (Wakamura and Takai. 1992) but S. littura (F.) is seasonal in other countries (Muniappan and Marutani. 1992). A list of major pests of cabbage worldwide is presented in Table 2.1. Table 2.1 Major Pests of Cabbage and Damage Worldwide Name of species Order/Family Damage & Part Attacked Plulella xylostella (L.) Lepidoptera/Plutellidae Larvae feed on leaves Pieris rapae (L.) Lepidoptera/Pieridae Larvae defoliate leaves Pieris canidia (L.) Lepidoptera/Pieridae Larvae defoliate leaves Hellula undalis (F.) Lepidoptera/Pyralidae Larvae eat growing points Agrotis ipsilon (Hufnagel) Lepidoptera/Noctuidae Larvae are cutworms Agrotissegetum (Schiffermuller) Lepidoptera/Noctuidae Larvae are cut worms Brevicoryne brassicae (L.) Hemiptera/Aphididae Larvae Infest foliage Lipaphis erysimi (Kaltenbach) Hemiptera/Aphididae Larvae infest foliage Aleyrodes brassicae (L.) Hemiptera/AIeyrodidae Larvae infest foliage Delia brassicae (Bouche) Diptera/Anthomyiidae) Larvae eat roots Aulacophora similis (Olivier) Coleoptera/Chrysomelidae Adults chew leaves Phyllolreta spp Coleoptera/Chrysomel idae Adults chew leaves Leucopholis irroraia (Chevrolat) Coleoptera/Scarabaeidae Larvae chew roots Trichoplusia ni (Hubner) Lepidoptera/Noctuidae Larvae defoliate plant Zonocerus variegalus (L.) Orthoptera/Acrididae Chew leaves in nursery Sources: Hill, 19H3; Youdeowei. 2002; Obeng-Ofori and Ankrah, 2002 9 2.2 Origin and Distribution of the Pests The most probable origin of the diamondback moth has been postulated to be the Mediterranean region (Hardy, 1938). This is based on circumstantial evidence that the largest contiguous area of its distribution is Europe, where the Brassicas had been cultivated since ancient times (Strasburger, 1921, cited in Hardy, 1938). The complex of natural enemies present there and the effective natural control reported lend support to this assertion (Ooi, 1986). It is likely that the diamondback moth was spread along with the spread o f Brassicas from their original home. Kfir (1997) proposed that Plutella xylostella may have originated from South Africa. In addition to its effective control and the rich fauna of parasitoids which had been used as the basis for its European origin, the author argued that the lower pest status of the diamondback moth in South Africa compared with other countries with similar climates, the large number of indigenous Brassicas and parasitoids are more compelling reasons. However, Liu et al. (2000 ) indicated that the data from their study seem to add confusion to such speculations because most of the arguments used by Kfir (1997) seem to apply to China. Only a few agricultural pests are as cosmopolitan as the diamondback moth and they have been recorded beyond latitude 60°N in Iceland in the temperate region and in the tropics (Ooi, 1986). It has the ability to survive a wide range of temperatures both in the tropic and temperate regions (Salinas, 1986). The pest is completely cosmopolitan in distribution, extending northwards up to the Arctic Circle (Frost, 1949; Hill, 1983) and to the Tropics (Talekar, 1992). 10 Trichoplusia ni is very widely distributed throughout the tropics and sub-tropics, with the exception of Australasia, and extends up into the warmer parts of southern Canada and Europe (Hill, 1983). It is found wherever crucifers are grown. It is highly dispersive and adults have sometimes been found at high altitudes and far from shore. Flight ranges of approximately 200 km. have been estimated (Capinera, 1999). Hellula undalis was first identified in Italy but has now spread throughout the Middle East, Asia, North and West Africa, parts of Australia and to the Pacific islands (Hill, 1983; Muniappan and Marutani; 1992; Jayma and Ronald, 2007). Description of the Pests General descriptions of the developmental stages of the diamondback moth have been given by various workers (Hardy, 1938; Harcourt, 1956; Moriuti, 1986). However, the diamondback moth populations native to different regions have genetic and biological differences and the behavioural and morphological parameters of the developmental stages also vary (Salinas, 1972; Sarfraz et al., 2005). The adult is a small, slender, greyish-brown insect measuring 11-16 mm long with a wing span of about 10 mm (Hardy, 1938; Harcourt, 1956). It is also described as a greyish moth with a wing expanse of 14 mm, the male having an expanse of 12.97 mm and the female 13.0 mm (Chelliah and Srinivasan, 1986). The common name of the diamondback moth is based on the fact that, when at rest, the wings are closely applied to the sides of the body meeting above and presenting a slightly upturned diamond appearance at the rear end. Although colour variations occur, the females are generally lighter than the males (Harcourt, 1956; Moriuti, 1986). The egg of the diamondback moth is described as yellowish white to yellowish green, cylindrical to oblong in shape, and measuring 0.48 nun by 0.25 mm (Bhalla and Dubey, 1986). It has also been described as whitish yellow with a length of 0.5 mm (Chelliah and Srinivasan, 1986). The larva may be whitish yellow to pale green or pale white with a pale brown head when freshly hatched (Chelliah and Srinivasan, 1986). The authors described the fully grown larva as light green, moderately stout, smooth, with short scattered hairs and varying in length from 8.62 to 10 mm. The pupa is light brown with a mean length of 5.15 - 7 mm (Harcourt, 1956; Bhalla and Dubey, 1986). The adult of Trichoplusia ni is a dark brownish moth with a wing span of about 35mm (Hill, 1983). The fore wings are mottled grey-brown in colour and the hind wings are light brown at the base, with the distal portions dark brown (Capinera, 1999). The forewing bears silvery white spots centrally: a U-shaped mark and a circle or dots that are often joined or resemble a figure ‘8 ’ (Hill, 1983; Capinera, 1999). The egg of T. ni is hemispherical in shape, with the flat side affixed to foliage (Capinera, 1999). The author described it as yellowish white or greenish in colour, bears longitudinal ridges and measures about 0.6 mm in diameter and 0.4 mm in height The larva is basically green in colour, with a thin, white, lateral line and two white lines along the dorsal surface (Hill, 1983). The larva has three pairs of prolegs and move by arching its back to form a loop and then projecting the anterior section of the body forward. The thoracic legs and head are usually pale green and the mature larva measures about 3 - 4cm long (Capinera, 1999). The newly formed pupa 12 is green, but later turns dark brown or black. It measures about 2 cm in length (Capinera, 1999). The developmental stages of the cabbage webworm, Hellula undalis have been described by (Jayma and Ronald, 2007). The authors described the adult as a greyish- brown moth with a wing span of about 2 cm. The forewings have wavy grey markings, a curved pale patch subterminally and a kidney shaped mark about one third way towards the tip. The eggs of the cabbage webworm are ovoid in shape and about 0.52 mm long. The surface attached to the foliage is slightly flattened. When freshly laid, it is pearly white but becomes pinkish after a day and then turns brownish red, just before hatching (Hrakly, 1968a; cited in Jayma et al., 2007). The larvae are greyish - yellow with five broad, irregular reddish-brown bands that extend the length of the body. The pupae are about 12 mm long. The newly formed pupa is soft and pale yellowish, but becomes hard and light brown within a few hours. Life History of the Pests The life histoiy and other aspects of the biology of the diamondback moth, Plutella xylostella have been documented by various workers (Harcourt, 1960a & b; Talekar and Griggs, 1986; Talekar, 1992). In general, an increase in temperature leads to a shortening of the developmental time of all stages up to a certain optimum depending on the area (Bhalla and Dubey, 1986; Salinas, 1986). In tropical conditions where temperatures range from 28-31 °C, the life cycle is completed within 14 - 24 days (Alam, 1992). 14-21 days have been reported by Harcourt (1957) in Canada, 10.8 - 27 days in Malaysia by (Ho, 1965) and 25.3 - 27.2 days in northern India by Yadav et al. (1974). Even in the same region, Ko and Fang (1979) reported only 9 days for a single generation under favourable conditions while, in winter, one generation took 110 days. The eggs are laid singly or in batches of up to four under the leaves (Bhalla and Dubey, 1986). Incubation period varies between 3 - 8 days and larval periods range from 6-17.5 days (Harcourt, 1957; Salinas, 1986). Four larval instars were recorded by Harcourt (1956) and Jayarathnam (1977), whilst Patil and Pokharkar (1971) recorded five instars. The fully grown larva spins an open net silken cocoon which is open at both ends, or a loose mesh of silken cocoon and pupates inside it on the leaf (Chelliah and Srinivasan 1986; Ooi, 1986). The pupal period is reported to vary from 4 - 1 5 days depending upon the temperature (Abraham and Padmanabhan, 1968; Salinas, 1986). The adults are most active at dusk from 6.30 - 7.30 pm at temperatures of 20 - 21 °C and 90 - 95% relative humidity at which they mate and oviposit (Frost, 1949; Poe Iking, 1992). Longevity of the adults varies from location to location. Harcourt (1957) gave a range of 3 - 58 days for males and 7 - 4 7 for females whilst Salinas (1986) gave 8 - 1 6 days for females in the presence o f the host plant, and 11-27 days in the absence of the host plant The life history of the cabbage looper, Trichoplusia ni has been studied by Hill (1983) and Capinera (2008). They observed that the number of generations completed per year overlap and varies from 2 to 5 depending upon the temperature. The total developmental period may take between 1 8 - 2 5 days at 32 - 21 °C respectively 14 (Capinera, 1999). The lower limit for development is about 10 - 12 °C and 40 °C is fatal to some stages. The eggs of Trichoplusia ni are deposited singly on either the lower or upper surface of the leaf, although clusters of six to seven eggs are not uncommon (Capinera, 1999). The incubation period of the egg varies from 2 - 1 0 days and larval periods range from 20 - 35 days depending upon the temperature. Hill (1999) recorded five larval instars but, Capinera (2008) recorded four to seven instars. Pupation takes place in a white, thin, fragile cocoon formed on the underside of foliage, in plant debris, or among clods of soil. Capinera (1999) reported that the pupal period of T. ni takes 4 - 13 days depending upon the temperature. The adults of Trichoplusia ni are considered to be semi-noctumal because feeding and oviposition sometimes occurs around dusk (Capinera, 1999). Flight ceases at about 16 °C but activity is higher on warmer evenings (Hill, 1963; Capinera, 2008). The female oviposits readily at temperatures as low as 15.6 °C and may lay 300 - 600 eggs in her life time (Shorey, 1963). The life history of the cabbage webworm, Hellula undalis was studied by Jayma and Ronald (2007) in Hawaii. They observed that the upper and lower threshold for development is about 36.6 °C and 20 °C respectively, and that the complete life cycle varies from 17-52 days. The eggs are laid singly, or in groups of two or three on the leaves of cabbage near the bud. Incubation period of the egg varies from 2 - 3 days at a mean temperature of 15 27.8 °C (Awai, 1958; cited in Jayma and Ronald, 2007; Sivapragasam and Abdul Aziz, 1992). There are five larval stages which are completed in 14 days at 28 °C. Pupation occurs in a silken cocoon either in a tunnel constructed at the entrance of the feeding tunnel, between leaves, inside the stem and bases of dropped leaves or deep in the soil surrounding the plant. Pupal period lasts 8 days at 27.8 °C (Sivapragasam and Abdul Aziz. 1992). The adults of Hellula undalis live for 4 to 8 days depending upon the temperature. Oviposition begins within 24 hours of emergence and continues for 3 to 10 days (Sivapragasam and Abdul Aziz, 1992). Host Range of the Pests The diamondback moth is an oligophagous insect that feeds on plants that contain mustard glucosides (Thorsteinson, 1953; Gupta and Thomsteinson, 1960). The cruciferous plants are an important economic group of plants with mustard glucosides. thus, wherever they are found, the diamondback moth is present (Ooi, 1986). In some cases, it is restricted to introduced or cultivated species of Brassica (Salinas, 1986). Being a crucifer specialist, it has adapted to the unique secondary chemistry of this family of plants that is toxic to most generalist feeders (Verkerk and Wright, 1996). The diamondback moth has been observed as a major pest on Brussels sprouts in Canada (Butts and McEwen, 1981), radish, Raphanus sativus (L.) and watercress. Nasturtium officinale (Hill, 1983). Other host plants include collards (Brassica oleracea var acephala (L.), Chinese cabbage, B. campestris L. subspecies pekinensis (Lour) Olsson, (Talekar and Yang, 1991), Broccoli, Brassica oleracea (L.) var botrytis (Zhao et al, 1992; Mitchell et al., 1997a; Martinez-Castillo et al., 2002). Mosiane et al. (2003) reported that in South Africa, canola, Brassica napus (L.) is a major host plant of the diamondback moth. In Ghana, it is associated with the cauliflower, B. oleracea var botrytis (L.), B. oleracea var capitata (L.) and B. campestris L. subspecies pekinensis (Obeng-Ofori et al., 2007). Kmec and Weiss (1997) reported that this pest also occurred on the crop, crambe, Crambe abyssinica Hochst and the weed, field pennycress, Thlapsi arvense L. Other alternative hosts consist of a wide range of wild cruciferous plants (Hill, 1983). It had also been recorded on the non-crucifer, Amaranthus virdis L (Vishakantaiah and Visweswara Gowda. 1975) and on okra, Abelmoschus esculentum (L.) Moench (Gupta, 1991; Cobblah, 2000). The cabbage looper, Trichoplusia ni feeds on a variety o f crucifers and other cultivated plants and weeds. It has been reported damaging Brassica oleracea var capitata, B. oleracea var. acephala, B. campestris subspecies pekinensis, Brassica oleracea var botrytis in Canada and the United States of America (Harcourt. 1963; Capinera, 1999). It has also been recorded on cotton, tomatoes, legumes, sweet potato and water melon (Hill, 1983; Capinera, 1999). Capinera (1999) also noted that additional hosts are flower crops such as chrysanthemum, snapdragon and sweet pea and agricultural weeds such as wild lettuce, Lactuca spp.; dandelion. Taraxacum officinale; and curly dock, Rumex crispus. In Ghana, it is associated with the cauliflower, B. oleracea var botrytis and B. oleracea var capitata (Obeng-Ofori et al.. 2007). Hellula undalis is host specific to cruciferous crops in Guam and it is associated with Chinese cabbage, Brassica pekinensis, green mustard, B. juncea and the common cabbage, B. oleraceae (Muniappan and Marutani, 1992). In Thailand, Australia, North and West Africa, and Hawaii it is recorded on various crucifer crops (Hill, 1983; Rowell, et al., 2005; Jayman and Ronald, 2007). Obeng-Ofori et al. (2007) observed that in Ghana, H. undalis is associated with the common cabbage and cauliflower. Damage by the Pests to Cabbage The diamondback moth is the primary pest of cabbage worldwide and all the developmental stages occur on the plant The behaviour and feeding damage caused by the pest have been described by (Talekar and Griggs, 1986; Talekar, 1992; Obeng- Ofori et al. 2007). Its behaviour on the plant appears to be similar world-wide (Hardy, 1938; Harcourt, 1957; Sastrodihardjo, 1986). The newly hatched larva is essentially a leaf miner, forming shallow mines on the underside of the leaf and feeding in the spongy mesophyll (Dobson et al., 2002). These show up as numerous white markings on the leaves. Hardy (1938) contended that this behaviour is not obligatory but, it is an adaptation enabling the young larva to consume as much parenchyma without the necessity of chewing through much of the toughened epidermis with its comparatively weak mandibles. When provided with tender thin leaves they do not mine but behave as surface feeders. The subsequent instars are surface feeders, usually on the underside of the leaves. They chew all the leaf tissues with the exception of the veins and the upper epidermis, causing irregular transparent areas or patches on the leaves. This “windowing” effect is distinctive of P. xylostella damage. The attack may begin from the seedling stage to maturity but there is a preference for the central leaves of young plants (Koshihara, 1986). They may also feed on the outer leaves. These feeding activities retard vegetative growth, render the heads unmarketable, and may lead to total destruction of the crop. When disturbed, even slightly, the larvae wriggle backwards or drop down unto the lower leaves by suspending themselves on a silken thread. The larvae of the cabbage looper, Trichoplusia ni are leaf feeders and cause considerable damage to cabbage. The first three instars confine their feeding to the lower leaf surface leaving the upper surface intact (Capinera, 1999). The author also observed that the fourth and fifth instars chew large holes in the leaf, and feed on the wrapper leaves as well as the developing head. Obeng-Ofori et al. (2007) noted that the larvae bore irregular holes in the leaf lamina and attack the newly formed heads resulting in numerous feeding punctures that are filled with frass. Even though, the larvae are voracious and consume three times their weight in plant material daily, they are not always destructive (Capinera, 1999). In Thailand, Trichoplusia ni can be potentially damaging to young plants from the seedling stage until bolting, but appears to cause little damage to the seed crop thereafter (Rowell, et al.. 1992). On the other hand, Prasad (1963) observed that T. ni reduced yield of marketable crop by 64 - 78%. In the United States of America, moderate defoliation prior to head formation is irrelevant, but average population densities of 0.3 larvae per plant justify control (Kirby and Slosser, 1984; cited in Capinera, 1999). The larvae of Hellula undalis cause damage to the terminal shoots and midribs of leaves, and in severe cases, such damage result in the development of multiple heads. 19 which are small and unmarketable (Muniappan and Marutani, 1992). It may cause occasional damage to young plants in the pre-flowering stage (Rowell, et al., 1992). Sivapragasam and Abdul Azziz (1992) observed that damage is most severe between transplanting and the heading stage of cabbage, even though, the larvae are present in the field throughout the crop. Severe damage or death occurs when the larvae tunnel into the main stem (Jayma and Ronald, 2007). In Ghana, Obeng-Ofori and Ankrah (2002) reported that the larvae of H. undalis attack the leaves, stalk and heart of cabbage, and also spin together the leaves with silken thread. 2.7 Seasonal Incidence of the Pests Incidence and population trends vary for the various lepidopterous pests on cabbage. Seasonal incidence of the diamondback moth in relation to various factors has been described (Harcourt, 1957; Sachan and Srivastava, 1972; Butts and McEwen, 1981). In general, dry and warm weather triggers outbreaks (Sastrodihardjo, 1986) or favours population build up (Frost, 1949; Oatman and Platner, 1969; Alam, 1992). Similar trends have been found in India (Abraham and Padmanabhan, 1968; Yadav et al.. 1974). In India, Rustapakomchai and Vattanatangum (1986) also recorded high build-up of the larvae in the summer, dry season and the mid-rainy season whereas Nagarkatti and Jayanth (1982) recorded significantly higher build-up during the rainy season, compared with other seasons. Observations by several workers indicate that temperature is a limiting factor in the population dynamics of the diamondback moth. A high temperature of 33 °C led to low survival rates as it adversely affected the development and emergence rates (Wakisaka et al., 1992). Dennili and Pretorius (1995) reported 10.5 °C and 25.8 °C as 20 being within the critical limit. Koshihara (1986) reported a daily minimum range of 5 - 12 °C and a maximum of 21 - 36 °C as favourable for multiplication of the diamondback moth. The diamondback moth may occur all year round (Harcourt, 1963) and even in winter at a minimum temperature of 10 °C, but the population densities differ (Koshihara, 1986). The number of generations is higher in the hot lowlands than in the highlands of Thailand and survival rates are higher in the hot dry season than in the wet season (Keinmeesuke et al., 1992). Humidity has little influence on the development and survival, as the immature stages live in specialised microclimate (Hardy, 1938). The population of the diamondback moth is high early in the cropping season (Harcourt, 1986), peaking at 45 days after transplanting (Sastrodihardjo, 1986; Rowell et al., 1992), or before cupping (Chalfant et al., 1979; Dennill and Pretorius, 1995; Mosiane et al., 2003) and declining thereafter. The diamondback moth is a multivoltine species and several generations overlap in a single crop or annually, making it very difficult to study its life cycle in the field. In warm parts of Japan and South East Asia, up to 15 and 20 generations overlap annually (Talekar and Griggs, 1986; Poelking, 1992). The incidence of attack and population densities vary widely within plants and even within fields in the same growing season (Harcourt, 1960a, 1961; Hu et al., 1997). In certain areas of South Africa, 11.6 larvae per plant was observed by Ullyet (1947) while Denill and Pretorious (1995) recorded 0.42 larva per plant Peaks of 1.6 to 3.6 larvae/plant in four seasons were reported by Oatman and Plainer (1949) with pupae following the same trend. Densities of 2.5 - 20 larvae per plant had been recorded by 21 several workers in different areas (Prasad, 1963; Baker et al., 1982; Simonet and Murisak, 1982; Andaloro et al., 1982). High densities of 477 larvae/plant in an outbreak period and mean population densities of 2 to 78 larvae/plant, with a maximum of 160 larvae/plant, were reported by Wan (1970) and Ooi (1979a & b), respectively. Harcourt, et al. (1955) observed a mean population build up of 14.9 to 26.9 larvae/plant by the end of harvest. The infestation of cabbage by the diamondback moth varied from 5% to 100% in the growing season whilst between 3% and 73% of plants were infested with larval populations ranging between 3 and 415 per 100 plants (Prasad, 1963; Sachan and Srivastava, 1972). Weeds have been shown to maintain Plutella xylostella populations during the off­ season periods. Kmec and Weiss (1997) observed that, peak populations occurred first on weeds before the moths move onto the cultivated crop. Larval densities were higher on rows adjacent to weeds and bushes than in the interior of fields but these varied among fields (Hu et al., 1997). With regard to Trichoplusia ni, temperature has been found to be a limiting factor in its incidence and activity. Hill (1983) observed that in temperate areas the larvae continue to be active at low temperatures; generally flight ceases at about 16 °C and larval development at about 12 °C. In warm regions however, there may be 5 generations per year or more as a result of continuous breeding. Overwintering of the pest apparently occurs only in the southernmost states of the USA; it is erratic in occurrence, typically very abundant in one year, and then scarce for two to three years (Capinera, 1999). The author also noted that, the number of generations per year overlap and varies from two to seven. In Nigeria, Anene and Dike (1996) observed 22 that populations were high during the rainy season and could reach epidemic levels. On the other hand, Hofmaster (1961) cited in Capinera (1999) reported that cabbage looper populations in Virginia were highest during dry weather because rainfall assisted the spread of Nuclear Polyhedrosis Virus (NPV), which greatly suppressed the population. In India, populations of T. ni reach their peak by early September and remain high till the last week, and then declines greatly up to February. During the peak period 32% of plants are infested (Sachan and Srivastava, 1972). Wyman (1992) noted that in Central North America, populations were high in all fields in mid to late season. Chalfant et al. (1997) also reported that populations of the pest were heaviest after cupping until harvest. The adults o f Hellula undalis are primarily active at night (Jayma and Ronald, 2007). Populations reach their peak by about middle of August, declines during October, and it is negligible in winter in India (Sachan and Srivastava, 1972). Wyman (1992) noted that in Central North America H. undalis occurs in small numbers sporadically throughout season. 2.8 Mortality Factors Influencing the Survival of the Pests 2.8.1 PluteUa xylostella Factors affecting the abundance of the diamondback moth have been studied by a number of workers (Hardy, 1938; Harcourt, 1963; Kmec and Weiss, 1997). The major mortality factors are parasitoids and rainfall (Harcourt 1963; Lim, 1986; Keinmeesuke et al, 1992; Capinera, 2005). However, Hardy (1938) suggested that rainfall may be important only at certain critical periods in the life cycle and argued that temperature was more critical. 23 2.8.1.1 Rainfall The effect of rainfall is manifested by washing away and/or drowning of early instar larvae and eggs (Wakisaka et al., 1992; Capinera, 2005) and causing mortality of gravid females (Harcourt, 1963; Talekar et al., 1986). Harcourt (1963) found a positive correlation between intensity of rain and mortality of the diamondback moth, while Rowell et al. (1992) observed low diamondback moth populations after the rains. 2.8.1.2 Parasitoids All the developmental stages of the diamondback moth are attacked by parasitoids. Only a few species have been reared from the eggs and they belong to the genera Trichogramma and Trichogrammatoidea. These however, contribute little to mortalities in the diamondback moth (Yamada and Yamaguchi, 1985; Waterhouse. 1992; Alam, 1992). The greatest control is provided by the endo-larval parasitoids (Ooi, 1970; Talekar, 1992; Liu et al., 2000; Mustata et al., 2006). The main larval parasitoid species that are reported to cause significant mortalities belong to the Hymenoptera genera, Diadegma Foerster (Ichneumonidae), Microplitis Foerster and Cotesia Cameron Braconidae) (Waterhouse and Norris, 1987; Waladde et al., 1997; Rowell et al., 2005). Even though, the importance of the different genera varies from place to place (Mustata, 1992), several accounts on parasitism of the diamondback moth indicate that, of the three genera, Diadegma species are superior to the others (Putnam, 1968; Sastrosiswojo and Sastrodihardjo, 1986; Talekar et al., 1992). As a result of this observed superiority, Diadegma species have been introduced into several countries, sometimes to augment the impact of other species of the genus 24 Cotesia or some other indigenous species (CIBC, 1977; Ooi and Chua, 1986; Lim, 1986). The degree of parasitism varies from species to species and from country to country, or even from locality to locality in the same area (Hardy, 1938; Ooi, 1992; Talekar et al., 1992; Mustata, 1992). Some species can be effective under specific conditions and yet ineffective under other conditions even in the same field or year (Salinas, 1986). The three most important species of Diadegma are D. (Angila) eucerophaga Horstm. D. insulare (Cress) and D. semiclausum (Hellen) (Sastrodihardjo and Sastrosiswojo, 1986; Ooi and Chua, 1986 and Alam, 1992). A number of reports exist on the widespread occurrence of Cotesia (Apanteles) plutellae Kurdjumov in many countries (Chiu and Chien, 1972; Ooi, 1979b&c; Loke et al., 1992; Ingham and Kfir, 1997). However, in Indonesia and Central America, it is not common (Waterhouse, 1992; Andrews et al, 1992.). Reports and observations from laboratory studies regarding the superiority of D. semiclausum over C. plutellae contradict some field and laboratory observations. Despite D. semiclausum being intrinsically superior to C. plutellae, the latter is more dominant in field studies (Ooi, 1992). Hyperparasitoids broadly defined as parasitoids that seek parasitized hosts and lay their eggs into the host or into the developing parasitoid within the host (Greathead et al., 1992) have been suggested as contributing to the apparent ineffectiveness of C. plutellae and its inability to establish in the field (Ooi, 1979a; Lim, 1982; Alam, 1992; Morallo-Rejesus and Sayaboc, 1992). Ooi (1979c & d) reared eight hyperparasitoids 25 from field collected cocoons of C. plutellae and observed hyperparasitism levels of between 11.7 - 26.6% whilst Lim (1982) recorded an average of 21%. High hyperparasitism rates of 56% (Alam, 1992) and 80% - 90% (Poelking, 1992) by Spilochalcis sp. on C. plutellae have also been recorded. Ten different species of hyperparasitoids belonging to nine genera had been reared from C. plutellae by Chelliah and Srinivasan (1986), Liu et al. (2000), and Mosiane, et al. (2003). Of these, the important ones were Aphanogmus fijiensis Ferriere (Ceraphronidae), Hockeria atra Masi (Chalcididae), Pediobius imbreus Walker (Chalcididae), Pteromalus sp. (Pteromalidae), Tetrastichus sp. (misre group) (Tetrastichidae), Brachymeria excarinata (Gahan) (Chalcididae), and Tetrastichus sokolowskii Kurdjumov (=Oomyzus sokolowskii), with the last two acting as facultative hyperparasitoids. They also found the lowest hyperparasitism level o f 3 - 13% and the highest of 39.13%. This high level of hyperparasitism coincided with peak parasitism by C. plutellae on the diamondback moth. Morallo-Rejesus and Sayaboc (1992) recorded Trichomalopsis sp. as an important hyperparasitoid reducing the efficiency of C. plutellae. The negative effect of hyperparasitoids has, however, been disputed by other workers who noted that their effects are of little significance (Robertson, 1939), and of no economic impact (Mustata, 1992; Mustata et al., 2006). The commonest pupal parasitoids belong to the Ichneumonid genus Thyraella (-Diadromus), and the Eulophids Tetrastichus Halida^ and Oomvzus Rondani. The only one with potential for biological control of the diamondback moth is the facultative hyperparasitoid Oomyzus sokolowskii Kurdjumov (Fitton and Walker. 1992; Liu et al., 2000). It is a gregarious larval-pupal parasitoid exhibiting a density independent relationship with the diamondback moth (Ooi and Chua, 1986; Alam. 26 1992). However, T. ayarri (Ollifl) was regarded as a common parasitoid of the diamondback moth in S. E. Asia (Ooi, 1986; Fitton and Walker, 1992). 2.8.2 Trichoplusia ni The cabbage looper Trichoplusia ni is attacked by numerous natural enemies, and the effectiveness of each seems to vary greatly. Wasp and tachinid parasitoids, and a nuclear polyhedrosis virus (NPV) have particularly been noted to be effective (Capinera, 2008). The author noted that predation on the pest has however, not been well studied. 2.8.2.1 Parasitoids Egg parasitism by Trichogramma sp., though variable, could reach about 35% in California (Oatman and Platner, 1969). Hill (1983) reported that high field mortality of Trichoplusia ni can sometimes be attributed to parasitoids. Larval parasitism has been found to average 38.9% with the tachinid Voria ntralis (Fallen) being the dominant species in autumn and winter months (Capinera, 2008). Even though, a total of twenty four parasitoid species were observed, the authors concluded that they are not key factor affecting populations. 2.8.2.2 Nuclear Polyhedrosis Virus The Trichoplusia ni NVP is reported to be the key factor affecting populations of the pest in California (Oatman and Platner, 1969). However, Sutherland (1966) observed that in New York, although T. ni NVP is an important mortality factor, natural incidence does not appear to be adequate to protect the crop from damage. The erratic 27 occurrence and abundance of the pest in parts of the USA has been attributed to the nuclear polyhedrosis virus which is spread by rain (Capinera, 1999). 2.83 Hellula undalis Very little is known regarding the mortality factors that influence populations of the cabbage webworm. In Hawaii, Zimmerman (1958) cited in Jayma and Ronald (2007) reported that Chelonus blackburni Cameron is an egg - pupal parasitoid of the pest However, its importance in managing webworm population densities is unknown. 2.9 Control Measures Against the Pests Several control measures have been applied against the major Lepidopteran pests of cabbage, especially the diamondback moth in many countries. Simonet and Morisak (1982) observed that several factors have to be considered in a pest management programme for cabbage feeding caterpillars. Capinera (1999) and Jayma and Roanld (2007) on the hand proposed that management strategies should include consideration of the complex of crucifer-feeding caterpillars. The control measures include the use of various insecticides, biological control, resistant varieties, pheromones, cultural and physical methods or combinations of these. 2.9.1 Chemical Control In many countries, attempts to control P. xylostella have been by the use of synthetic insecticides (Chelliah and Srinivasan, 1986; Wyman, 1992). These include relatively new chemicals such as avermectins, neonicotinoids and insect growth regulators (Abdel-Razek et al, 2006), microbial insecticides such as Bacillus thuringiensis Berliner (Bt) (Mahar et al., 2004; Abdel-Razek et al., 2006) and plant based products 28 such as neem, Azadirachta indica A. Juss (Verkerk and Wright 1996; Rowell et al, 2005; Condor 2007). In Ghana, the main synthetic insecticide used is lambda cyhalothrin formulated as Karate 2.5% EC (Obeng-Ofori and Ankrah, 2002). Other types are Dimethoate (400g/l) and Fipronil (25 g/1) (Koomson, 2008). Bacillus thuringiensis (Bt.) based products are also commonly used (Cobblah, 2000). Extracts o f seed, kernel, or leaves of neem have been found to be effective against P. xylostella (Bamby et al., 1989; Schmutterer, 1992; Verkerk and Wright 1996; Youdeowei, 2000; Charleston, 2002). Water extracts have proven to be most effective at concentrations as low as 12.5 g of seed per litre of water (Youdeowei, 2000). The use of neem seed water extract against the diamondback moth is common in some regions in Ghana according to Obeng-Ofori and Akuamoah, (1998). Morallo-Rejesus (1986) and Charleston et al. (2005) listed 88 plants mainly of the families Asteraceae, Euphorbiaceae and Meliaceae as having some insecticidal action against the diamondback moth. In parts of Asia and Africa, farmers use cocktails of insecticide and spray more frequently without satisfactory control (Muckenfuss et al., 1992; Obeng-Ofori, 2000; Lohr, 2003; Mosiane et al., 2003). The pest is now widely known to have become resistant or tolerant to most insecticides such as Esfenvalerate, Diazinon, Permethrin (Miyata et al., 1986; Beck and Cameron, 1992; Walunj and Pawar, 2004). Some populations of the diamondback moth have developed resistance to certain B. thuringiensis based products (Tanaka, 1992, Tabashnik et al, 1992). However, of all the commercial biopesticides, Bt constitutes the most significant control option (Cherry et al, 2002). 29 The cabbage looper, Trichoplusia ni is the most difficult crucifer pest to control in parts of the USA and chemical control is difficult to achieve (Chalfant et al, 1979). Hill (1983) reported that the pest is resistant to carbaryl, parathion and methomyl. Capinera (1999) observed that even though, insecticide resistance is a problem in cabbage looper control, susceptibility varies widely among locations. In Thailand, Bacillus thuringiensis Berliner (Florbac FC, 8500 IU/mg) is used exclusively for control of T. ni (Rowell et al. 1992). Botanical insecticides such as rotenone are less effective, but neem functions as both a feeding deterrent and growth regulator (Capinera, 1999). Wyman (1992) reported that one to two applications of esfenvalarate provided excellent control. Obeng-Ofori and Ankrah (2002) reported that Neem extracts have great potential against several pests on cabbage in Ghana. The authors indicated that neem seed applied at the rate of 50 g/litre of water can be used as an alternative to synthetic insecticides to control cabbage pests and that, 300g of neem leaves and 100 g of hot pepper/litre of water are effective. With regard to chemical control of the cabbage webworm Hellula undalis, Jayma and Roanld (2007) have drawn attention to the difficulty of chemical sprays penetrating the webbing produced by the larvae on cabbage. However, Rowell et al. (1992) reported that in Thailand, mevinphos (Phosdrin, 24EC) is effective in controlling the pest. In Guam Dibrom 8 EC has been observed to be most effective, providing 100% control (Muniappan and Marutani, 1992). Tests of Bacillus thuringiensis in Hawaii and elsewhere suggest that, they are only partially effective, and it is not recommended as standard treatments (Jayma et al., 2007). 30 2.9.2 Biological Control Biological control, which involves principally the introduction, augmentation and conservation of natural enemies, is a valuable weapon in pest control on a number of crops. Biological control may be the exclusive method of control (Verkerk and Wright, 19%), or integrated with other methods such as the use of insecticides in some geographic areas and at certain times within the crop cycle (Loke et al., 1992; Lim, 1992; Klemm and Schmutterer, 1993). Although over 130 species of parasitoids are known to attack various life stages of the diamondback moth, most worldwide control is achieved by relatively few Hymenopteran species belonging to the Ichneumonid genera, Diadegma and Diadromus-, the Braconid genera Microplitis and Cotesia; and the Eulophid genus Oomyzus (Mahmood et al., 2004; Sarfraz et al., 2005). The use of parasitoids alone has led to varying degrees of success (Mitchell et al., 1997a & b; Rowell et al., 2005; Mustata et al., 2006). Complete and partial controls of the diamondback moth by Cotesia plutellae have been reported in the Cape Verde Islands and Togo, respectively (Carl, K. P. British Museum Natural Hsitory personal communication). Biological control of the eggs of Plutella xylostella varies from country to country. Liu et al. (2000) noted that rates of parasitism of the diamondback eggs by Trichogramma chilonis Ishii was very low and did not go beyond 1 - 11% in the suburbs of Hangzhou, China. According to Haji et al. (2002, cited in Pratissoli et al., 2008), the use of Trichogramma species is increasing because it is cheap and easy to mass produce and can quickly suppress pest populations prior to crop damage. Laboratory evaluation of three species of done to identify the most suitable for use in 31 biological control programmes showed that T. atopovirilia (Oatmam and Platiner) had the strongest affinity for the eggs of the diamondback moth causing 42.33% parasitism (Pratissoli et al.. 2008). Mass release of Trichogrammatoidea bactrae Nakaraja in Thailand in the I990’s caused parasitism of between 16 - 45% of the diamondback moth eggs in unsprayed fields (Rowell, 2008). Eighty percent parasitism of the larvae of the diamondback moth by Diadegma eucerophaga was reported by Sastrosiswojo and Sastrodihardjo (1986) and also by Ooi and Chua (1986); but Sastrodihardjo (1986) reported a low rate of below 30%. A combination of D. insulare and Microplitis plutellae (Mues) caused 68% parasitism in the first generation o f the diamondback moth in Canada (Putnam, 1968). In the Philippines, the introduction of Diadegma semiclausum led to a reduction of the diamondback moth infestation from an average of 18.7 larvae/plant to 9.8 larvae/plant (Poelking, 1992). Ooi (1986) observed that even though Cotesia plutellae reduced the diamondback moth populations by 47 fold in the laboratory, field studies suggested limited ability of the parasitoid to control this pest because of its poor searching ability. Despite this, some introductions of this species have been successful (Muniappan and Marutani. 1992). In Central America, attempts to complement the native Diadegma insidare (Cresson) with exotics have not been successful, but C. plutellae had been introduced and occasional recoveries made (Andrews et al., 1992). In the Caribbean, parasitism by the indigenous C. (Apanteles) glomeratus group was found to be low and erratic with the highest parasitism of 5%. However, the introduction of C. plutellae resulted 32 in parasitism of between 5.4 and 88.7% resulting in a marked reduction diamondback moth population (Alam, 1992). Wide variations in parasitism by C. plutellae had been reported from locality locality and from country to country, even in areas with similar climates (Yaseen, 1978; Ooi and Chua, 1986). Most reports indicate that the level o f parasitism by C. plutellae cannot exceed 60% (Ooi, 1979a & b; Ooi, 1992). It had been reported as the commonest parasitoid in Malaysia causing only 12 - 19%, or an average of 14.4% with a range of 0 - 33% (Ooi and Chua, 1986). Poelking (1992) reported 1 - 70% parasitism over different locations, seasons and years in the Phillipines whilst Morallo-Rejesus and Sayaboc (1992) recorded percentages between 1.9 - 16.5 in the same country. The latter authors also indicated that different strains have different abilities to parasitise, with exotic ones being superior. In the lowlands o f Malaysia, parasitism by Cotesia plutellae ranged from 12.7 - 48.6% (Loke et al., 1992). Martinez-Castillo et al. (2002) reported that in Central Mexico, biological control of Plulella xylostella larvae by Diadegma insulare could reach as high as 42.7% on cabbage. Cotesia plutellae was not effective in places where percentage parasitism was between 2.3 and 35.8% but, in areas where parasitism ranged from 59.3 - 6 6 .6%, it was very effective in keeping the diamondback moth populations in check (Ooi. 1992). A high level of parasitism of 78.8% at both larval and pupal threshold of about 3 per plant was reported by Ooi (1986), but this was attributed to low host numbers. This author, however, noted that C. plutellae was not effective and could not prevent pest numbers from rising in the dry season. On the contrary, Ingham and Kfir, (1997) 33 indicated that parasitism by C. plutellae was effective when the diamondback moth populations were high. A combination of various parasitoid species had also given very good results (Yaseen, 1978; Ooi and Chua, 1986). Cotesia plutellae and O. sokolowskii had been reported to cause 10 - 60% larval parasitism at peak populations of the diamondback moth in parts of China and Romania (Liu et al., 2000; Mustata et al., 2006). In Kenya, the indigenous parasitoid species of Diadegma and Itoplectis, O. sokolowskii and an unidentified braconid caused a total of 20.8% parasitism while in Tanzania, C. plutellae, D. mollipla and O. sokolowskii caused a total of 10.1% parasitism (Lohr, 2003). This author also reported that the introduction of the exotic larval parasitoid D. semiclausum into these countries surpassed the combined parasitisation of P. xylostella by the indigenous parasitoids. High levels of parasitism of the diamondback moth by pupal parasitoids belonging to the genera Tetrastichus and Diadromus (=Thyraella) Gravenhorst have been reported (Ooi and Keiderman, 1977; Keinsmeesuke el al., 1992). In several countries of South East Asia D. collcaris has been reared and released and contributes significantly to natural control of the diamondback moth pupae (Rowell, 2008). Oomyzus sokolowskii caused parasitism levels of up to 100% and 10% when acting as a primary or secondary parasitoid, respectively (Cock, 1985). Liu et al. (2000) reported secondary parasitism of 18% of the diamondback moth by this species in the laboratory. Mustata et al. (2006) considered O. sokolowskii as a dominant and constant secondary parasitoid in the field in Romania Its ability to also act as a hyperparasitoid does not make it a bad candidate as a primary parasitoid (Waterhouse and Norris, 1987; Mustata et al., 2006). This species was also the most abundant species recorded by other workers (Yaseen, 1978; Alam, 1992; Waiganjo, 1997). It 34 had also been used in combination with other species (Ooi, 1980; Chellia and Srinivasan, 1986) but very low parasitism rates ranging from zero to a maximum of 20% were noted after the initial rate of 100%. Diadromus collaris Gravenhorst occurred when the diamondback moth populations were low late in the growing season and in the dry season when temperatures were high (Andrews et al., 1992; Rowell et al., 1992). Ooi and Kelderma (1977) and Ooi (1979a & b) considered Tetrastichus ayyari Rohw (=71 howardi = T. Israeli) to be of little importance as it occurred in negligible numbers. Mass release of Trichogramma spp. has been investigated for Trichoplusia ni suppression. Oatman and Platner (1971) cited in Capinera (1999) observed that cabbage looper egg parasitism can be increased several fold by careful timing of the parasitoid release. Baculoviruses have long been recognized as safe and effective biological pesticides for the control of Lepidopteran pests and in West Africa the baculovi ruses of Plulella xylostella are amenable to mass production and field application (Cherry, 2001). To a limited extent, baculoviruses have been used (Kadir, 1992; Cherry, et al., 2002). Osae et al. (2006) found that an East African strain of baculovirus was effective against a West African population of P. xylostella. Trichoplusia ni NVP is effective, but has not been commercialised because of the narrow host range (Capinera, 1999). The author observed that home gardeners in parts of the United States of America sometimes collect and grind loopers dying of the virus, and concoct their own effective microbial control agent. 35 The practice of biological control has however, been hindered in some countries by the overuse of insecticides leading to ineffectiveness of Cotesia plutellae and other parasitoids of the diamondback moth in the cabbage ecosystem (Mustata, 1992; Waiganjo, 1997). The effects of insecticides on all developmental stages of parasitoids of the diamondback moth had been documented in parts of Asia and the USA (Keinmeesuke et al., 1992; Kao and Tzeng, 1992; Hu et al., 1997; Hill and Foster, 2000; Charleston et al., 2005). However, very little information exists on the effects of insecticides on parasitoids of the diamondback moth in Ghana (Obeng- Ofori, 2000). Different authors have given contradictory observations on the adverse effects of insecticides on C. plutellae. Poelking (1992) noted that it resulted in reduced efficiency. Mustata (1992) and Waiganjo (1997) also attributed low levels of parasitism by a complex of diamondback moth parasitoids to the overuse and continued use of broad spectrum insecticides. Similarly, Alam (1992) noted that the failure of Cotesia plutellae to establish themselves in the field could have resulted from excessive use of chemicals. Some reports, however, indicated that the species was either tolerant or had achieved a certain level of resistance to insecticides in the field (Ooi, 1992; Liu et al., 2000; Rowell et al., 2005). In a field survey. Loke et al. (1992) recorded a high mean parasitism of 48.6%, even under very heavy insecticidal pressure. A mean parasitism of 75% by C. plutellae on the diamondback moth larvae was observed in spite of 1 - 3 weekly applications of insecticide cocktails (Lim. 1992). Liu et al. (2000) similarly observed substantial rates of parasitism by the parasitoid on many occasions in China despite the heavy application of insecticide into the crop system. Intermittent Bacillus thuringiensis (Bt) sprays led to a reduction 36 in parasitism by C. plutellae (Morallo-Rejesus and Sayaboc, 1992). A strain, NRD-12 (SAN 415) of Bt s.sp kurstaki was found to be more harmful to adults of C. plutellae than Bt s.sp kurstaki strain HD-1 (Kao and Tzeng, 1992). In addition, it has been observed that even though most of the other synthetic insecticides were harmful to the adults, the pupae were relatively tolerant (Mani and Krishnamoorthy, 1984). Diadegma insulare seems to be less tolerant to pesticides than C. plutellae. Reduction of chemical insecticides allowed its full potential of to be realized, with C. plutellae becoming less dominant (Ooi, 1992). The inability of D. insulare to establish in some parts of Malaysia was reported to be partly due to high levels of insecticide use (Talekar et al., 1992). Hill and Foster (2000) observed that the Actinomycetes-derived produc, Spinosad caused 100% mortality to adults of D. insulare after eight hour exposure to leaves treated with the chemical. The effectiveness of Diadromus collaris (Gravenhorst) was reduced from 63% to 31% due to frequent use of broad spectrum insecticides (Rowell et al., 1992); but Bacillus thuringiensis, was found to exert less adverse effect it (Ooi, 1992). Keinmeesuke et al. (1992) observed that, even though Bt and certain synthetic insecticides had low toxicities to adults of the diamondback moth and the egg parasitoid, Trichogramma bactrae, few others were highly toxic to the diamondback moth eggs parasitised by this species and led to low emergence. 3 Integrated Pest Management rhe problems associated with controlling P. xylostella and other l.epidopteran pests of cabbage with insecticides alone have stimulated interest in the use of a combination of strategies (Reddy and Guerrero, 2000; Lohr, 2003). Examples of successful 37 Integrated Pest Management (IPM) strategies abound in the literature (Talekar and Griggs, 1986; Lim, 1990; Talekar and Yang, 1991; Liu, 2001). There is also widespread recognition of the crucial role played by natural enemies (Hamilton et al.. 2004). Emphasis has been placed on the use of selective toxicants, particularly Bacillus thuringiensis-based products, which have little or no adverse effect on key parasitoids (Verkerk and Wright, 1996; Abdel-Razek et al., 2006), or spraying of insecticides only when predetermined thresholds have been reached (Chen and Su. 1986; Reddy and Guerrero, 2000). At the Asian Vegetable Research and Development Centre (AVRDC), a successful integrated pest management programme had been developed to effectively control the diamondback moth by combining the use of the parasitoid Diadegma semiclausum and Bacillus thuringiensis (Talekar et al., 1992; Talekar, 1992). Other methods include a combination of two or more of sprinkler systems, C. plutellae, granulosis virus and insecticides (Nakahara et al.. 1986; Andrews el al., 1992; Loke el al.. 1992). A combination of yellow sticky traps for diamondback moth adults and action threshold for larvae had given good results in Thailand (Rushtapakomchai ei al.. 1992; Hallett et al., 1995). Reddy and Guerrero (2000) reported that an IPM programme based on the pheromone trap catch threshold of eight moths per trap per night, which included utilization of C. plutellae, (250 adults ha'1), the predator Chrysoperla carnea (2500 eggs ha'1), neem based chemical nimbecidine (625 ml ha' '), B. thuringiensis (500 ml ha'1) and the synthetic insecticide Phosalone (2.8 litre ha' ') induced reduction of trap catches, egg and larval populations. It also led to economic savings of $410 ha'1 in 1997. In Ghana the advent of the IPM-Farmer Field Schools (IPM/FFS) programmes in 1999-2001 encouraged farmers to do Aero- 38 Ecosystem Analysis (AESA) before applying any control measure. The AESA involved assessment of the health of the plant, the moisture content of the soil and the role of the different arthropods with special reference to the presence of natural enemies and, thus, made informed decisions (Youdeowei, 2002). Muniappan and Marutani (1992) observed that in Guam, a combination of Dibrom 8 EC, natural enemies and insecticides can potentially give satisfactory control of crucifer pests. Wyman (1992) reported that the integration of biological control, cultural control, host plant resistance and other management techniques will play an increasingly important role in insecticide resistant management for all crucifer pests. 39 CHAPTER THREE 3.0 SEASONAL VARIATION OF PARASITOID-HOST ASSOCIATIONS AND EFFECT OF INSECTICIDES 3.1 Introduction The most damaging insect pests of the common cabbage. Brassica oleracea var. capitata are the Lepidopterans: Plutella xylostella, Pieris rapae, Trichoplusia ni and Hellula undalis (Talekar, 1992; Anene and Dike, 1996; Dobson el al., 2002; Hamilton et al., 2004). The relative importance of these species varies from country to country or may even be seasonal (Harcourt et al., 1955, Oatman, 1966; Bell and McGeoch, 1996; Liu et al., 2000). However, P. xylostella is cosmopolitan and it is considered the most important pest worldwide causing production losses of up to 60% (Pratissoli et al.. 2008). For this reason, insecticides are frequently applied on cabbage in order to produce marketable heads. This practice has led to the development of multiple resistance to insecticides by P. xylostella (Ninsin, 1997; Abdel-Razek et al., 2006). In order to address this problem, the use of biological control agents and the development of integrated pest management programmes, are considered feasible options (Hill and Foster, 2000; Pratissoli et al., 2008). Significant control by biological control agents had been reported in various countries (Liu et al, 2000; Mahar et al., 2004). Despite this recognition, very few studies have been done to assess the effect of commonly used insecticides and insect growth regulators on the natural enemies (Fan and Ho, 1971; Martinez-Castillo et al., 2002). In Ghana. Ninsin (1997) observed that various synthetic insecticides applied on cabbage had adverse 40 effects on non-target insects and other beneficial organisms. Many pesticides are also known to be more toxic to consumers and natural enemies than to the pests (Wilkinson et al., 1975; Schuster, 1994; Pratissoli et al., 2008). Mani and Krishnamoorthy (1984) observed that some insecticides had adverse effects both on the cocooned stages and adults of C. plutellae an important parasitoid of P. xylostella in parts of India. However, contradictory reports on the adverse effects of insecticides on C. plutellae have also been given by various authors. Ooi (1992), Kao and Tzeng (1992), Liu et al. (2000), Rowell et al. (2005) indicated that this species was either tolerant to or had achieved a certain level of resistance to insecticides in the field. In Ghana, little or nothing is known regarding the relative and seasonal importance of the Lepidopteran pests of cabbage, the identity of their parasitoids and the effect of commonly used insecticides on the parasitoids (Obeng-Ofori, 2000). The objective of this study was to determine the seasonality of parasitoid-host associations on cabbage, levels of parasitism and the effect of the commonly used insecticides on the development of the major parasitoid. 3.2 Materials and Methods 3.2.1 The Experimental Site The study was carried out on plots at the Weija Irrigation Company (WE1CO) site at Tubaman near Weija in the Greater Accra region (Fig. 3.1) between 1996-1997 and 2000-2008. This site was chosen for four main reasons: The commercial production of cabbage and other vegetables including export crops that spans over 10 years (Annual Reports WE1CO, 1999) with the consistent use of insecticides against the key 41 pests of cabbage. Besides, Plulella xylostella was known to be resistant to the common insecticides in use in that area (Annual Reports WE1CO, 1999). Field surveys were also carried out to investigate the occurrence of the major pests and associated parasitoids in parts of the Greater Accra, Eastern, Volta, Western and Ashanti regions (Fig. 3.1). The WE1CO study site is located at latitude 5° 31’ N and longitude 0° 21’ W. It lies about 21 km west of the city of Accra on the road to Winneba, Cape Coast and Takoradi. It is about 4.2 km. from the said link road towards the sea (Atlantic Ocean) in the south. It is a generally windy area with average minimum and maximum temperatures of 23 °C and 31 °C, respectively. Relative humidity during the study period ranged from 31 - 62%, with an average of 44%. 3.2.2 Planting Planting of the cabbage variety KK cross was done in the major and minor rainy seasons as well as the dry season. The first season planting was done from April to July of 1996 to coincide with the major rainy season. Cabbage seeds were nursed for four weeks and transplanted in a RCBD on 2nd May. Prevailing temperatures at the experimental site ranged from 23 °C - 30 °C. The second planting was done from August to December of 1996 and fell within the minor rainy season. Cabbage seeds were nursed and transplanted on 4111 October in a RCBD. Prevailing temperatures at the site ranged from 23.5 °C - 31.5 °C. 42 The third planting was done in the dry season between January and April 1997. Transplanting of seedlings was done on 28lh February after four weeks in the nursery in a RCBD. Prevailing temperatures ranged from 26 °C - 31 °C. 3.2.3 The Experimental Layout The experiment consisted of four treatments arranged in a randomised complete block design (RCBD) with four replications. The experimental area of 38.64 m2 was separated from other vegetable farms by approximately 100 meters. The land was ploughed and harrowed and then watered before the beds were raised using a hoe. Each bed was later leveled by raking and pieces of stone and other unwanted materials were removed before transplanting of cabbage seedlings. Each plot measured 4.2 by 2.3 meters. There were 3 rows per plot and each row had 7 plants, giving a total of 21 plants per plot The distance between blocks was 1.5 m and between plots in a block was 1 m. Plant spacing was 60 cm within rows and 75 cm between rows. 3.2.4 Treatments Applied The treatments applied were: 1. Lambda-Cyhalothrin formulated as Karate 2.5 E.C at the rate of 2.4 ml/ litre of water 2. 1.0 g Bacillus Ihuringiensis wettable powder (Dipel 2x)/ litre of water 3. 50 g neem (Azadirachta indica) seed powder/litre of water extract (applied only once) 4. Unsprayed Control (Water only) 43 Neem Seed Water Extract was prepared as follows: Dried neem seeds were purchased and stored in jute sacks in an air-conditioned room with an average temperature of 23.0 ± 2 °C and relative humidity of 45 ± 1.0%. Based on the concentration of 50 g/litre of water, 194.1 g. were weighed and ground using a Moulinex mill of capacity 95.1 cm3. The mill was, each time, filled to the brim and the seeds milled for about two minutes into fine powder. The powder was then mixed with the 3.9 litres of water and three spoonfuls of *Omo’ detergent was added to reduce the surface tension of the mixture. The mixture was kept overnight and then sieved through a fine plastic strainer to obtain the extract 3.2.5 Fertiliser Application The dose and timing of application of fertiliser recommended by Sinnadurai (1992) were followed. This involved a split application of 450 kg/ha of 15:15:15 NPK at seven days and twenty seven days after transplanting. A single dose of Sulphate of ammonia at 250 kg/ha was also applied at 34 days after transplanting. Basal applications of the fertilizer were done at a distance of 10 - 15 cm away from the plant at a depth of 5 - 6 cm. For each plant, 10 g. of the fertilizer was applied in the evenings as recommended. 3.2.6 Insecticide Application The concentrations of the lambda cyaholothrin and Bacillus thuringiensis used were based on manufacturer’s recommendations for field applications. For the neem seed water extract in addition to the recommended rates, a preliminary study was done to determine the concentration because of the varying potency cffects of neem. The dosages tested were 25 g/l, 50 g/1 and 75 g/1. The application rates in litres per 44 hectare required for the total land area of 38.64 m2 for the experiment is shown in (Table 3.1). The neem seed water extract treatment was added during the minor rainy and dry seasons. This was because after the major rainy season study, it was observed that damage was high on the unsprayed plots and parasitoid activity was very low till about 5 weeks after transplanting. The additional neem treatment was, therefore, imposed to complement the effect of the parasitoids during the first four to five weeks before pest numbers built up to appreciable levels. Table 3.1: Volumes of Insecticides Applied to Cabbage Plants Insecticide Fourth WAT Quantity/ha Sixth WAT Quantity/ha Eighth WAT Quantity/ha Karate 4.661 7.45 1 9.321 Bt 1.94 kg. 3.11 kg. 3.88 kg. NSWE 194.1 kg. nil nil NSWE=Neem seed water extract WAT= Week after transplanting The insecticides were applied using a calibrated 15 - litre tank capacity knapsack sprayer (Cooper Pegler, U.K. Ltd.) fitted with a fine plastic hollow cone nozzle obtained from (Chemico Chemical Ltd., Ghana). Bionex was added to the spray solution as a spreader. Insecticide applications started on the fourth week after transplanting. This was done in the evenings after the first sampling and. thereafter, every two weeks, except for the neem treatment which was applied only once in the fourth week after transplanting. Separate spray equipment was used for each treatment to avoid contamination. 45 3.2.7 Incidence and Seasonal Abundance of Pests and Parasitoids Sampling for insects on the experimental plots was started between eighteen and twenty days after transplanting when the first signs of insect attack on the leaves were observed and was done till harvest. Sampling was carried out once a week on the seven central plants in each of the treatment plots from 08 hours in the morning. During sampling, all developmental stages of insects on the five upper leaves as well as the two leaves surrounding the bud and the bud itself were carefully collected into petri dishes lined with filter paper and provided with a piece of cabbage leaf. Larvae which fell to the ground or spun a thread to escape were collected. On plants with multiple heads, the same head was tagged and sampled each time. All samples were labeled and taken to the laboratory for rearing until adult emergence of pest or parasitoid for subsequent identification and counting. A replication of the experiment could not be done for another year because two cropping seasons were lost to the diamondback moth. In the year 2000 - 2001 a fanner’s farm at the Weija Irrigation Company site was sampled for three cropping seasons. It was considered as a farmer’s practice. The farmer applied various insecticides such as Rimon (a Benzoylphenyl Urea), Lamda-Cyhalothrin (Karate), Bacillus thuringiensis (Biobit) and neem seed water extract on his plots. He applied insecticides from two weeks after transplanting or when in his opinion there were many insects. The cabbages were planted in long rows. Insects were sampled as described for the experimental plots. 46 3.2.8 Laboratory Rearing of Pests The eggs, larvae and pupae of the pests collected in the field were kept separately in petri-dishes. The eggs still attached to cabbage leaves were placed on moist filter paper in petri dishes on the laboratory bench for incubation. The larvae were separated and each was placed on a piece of cabbage leaf on a wet filter paper in a petri dish. Each larva was transferred into a clean petri dish with a fresh piece of cabbage leaf daily and observed until it pupated or either parasitoid larvae or pupae emerged. Emerged pupae of pests were kept in petri dishes lined with dry filter paper till adult emergence. The insects that emerged were stored in 70% alcohol or mounted for identification. All the rearings were done at a temperature of 23 ± 2 °C and relative humidity of 45 ± 1%. 3.2.9 Weekly Parasitism Trends by Cotesia plutellae and Euplectrus laphygmae in Relation to Plutella xylostella and Trichoplusia ni All the parasitoid larvae, pupae and adults emerging from the field collected immature stages of pests from the seven central plants of all the treatments were recorded daily in the laboratory. Parasitoid larvae or pupae that emerged from hosts were each kept in separate glass tubes plugged with cotton wool until the adults emerged. The larvae and pupae of pests that did not develop into adults were dissected to determine whether they had been parasitized and numbers recorded. Parasitism was therefore determined from rearing of pests as well as from the dissections. The parasitoids that emerged from its host were recorded for each week’s sample to determine parasitism and relationship between the parasitoids and the host till harvest of the cabbage. The parasitoids that emerged were stored in 70% alcohol or mounted for identification. All insects were maintained at a temperature of 23 ± 2 UC and relative humidity of 45 47 ± 1%. Mean percentage parasitism was determined for all the treatments for comparison. 3.2.10 Identification of Pests and Parasitoids The pests and parasitoids collected or observed were identified using the reference collections at the Entomology and Nematology Department of the University of Florida, USA. Specimens were also sent to CABI Bioscience, U.K. for confirmation and in some cases for the initial identification. 3Jt.ll Emergence and Mortality of Cotesia plutellae Exposed to Insecticides Emergence rates of C. plutellae adults were determined for all the parasitoid pupae that emerged from the pests collected from the seven central plants for all the treatments in the three seasons. In addition, all the pupae of C. plutellae were also collected from the seven central plants for all the treatments 3 weeks after transplanting during the major rainy season of May to July and the dry season from February to April on a single crop. Each pupa was kept in a separate glass tube and plugged with a piece of absorbent cotton wool till emergence of the adults in the laboratory at an average temperature of 23 ± 2 °C and RH of 45 ± 1 %. On emergence, each parasitoid adult was identified. Those that did not emerge after two weeks were kept for a further three weeks. Non-emergence after this period was considered to be mortality due to the insecticide. They were then dissected to determine their state of development and species where possible. 48 3.2.12 Laboratory Studies on Mortality of Adults and Emergence of Pupae of C. plutellae Exposed to Different Insecticides A synthetic insecticide Lambda-Cyhalothrin marketed as Karate 2.5 EC, a biopesticide Bacillus thuringiensis as wettable powder and a commercial neem formulated product, Neemazal, were evaluated against the most abundant parasitoid Cotesia plutellae. All the tests were carried out in the laboratory with a mean temperature of 28 ± 2 °C and relative humidity of 55 ± 1%. Two parameters (direct mortality to adults and non-emergence from pupae) were used to determine the effect of the insecticides (Gaitonde, 1978). Two methods of application were used to determine the residual effect and toxicity of the three insecticides to the pupae and adults of C. plutellae. These were the filter paper and direct contact application methods, respectively (Gaitonde, 1978). Concentrations of insecticides used were 2.4 ml. Karate/litre of water, 1.0 g Bacillus thuringiensis wettable powder/ litre of water, 1.0 ml. Neemazal/litre of water and water only as control. 3.2.12.1 Filter Paper Method A strip of filter paper measuring 11 cm in diameter was cut into two and one half dipped into the insecticide solution, air dried for 20 minutes and placed in a transparent jar measuring 12 cm deep and 9.5 cm in diameter as described by Wilkinson el al. (1975). The jar was covered with nylon mesh secured with a rubber band. Ten day - old adults of C. plutellae were introduced into the set up through a slit made in the mesh which was subsequently plugged with a cotton wool. The parasitoids were held in the jar for six hours. A piece of cotton wool soaked in 10% 49 honey solution was provided as food through a slit made in the side of the jar. After six hours, the parasitoids were transferred into a clean jar containing a piece of cotton wool soaked with 10% honey solution and observed for a further 48 hours. A control was set up with the other half of the filter paper soaked with water. Adult mortality was recorded at the end of the 6-hour exposure period, 24 hours and 48 hours after treatment (Gaitonde, 1978). Each treatment was replicated four times and each replicate had 10 adults of C. plutellae 3.2.12.2 Direct Application Method For the direct contact insecticide application, two methods were used to determine the direct effect of contact application of the test insecticides on the adult parasitoids. In the first method, a piece of cabbage leaf with the same dimensions as the filter paper described above was dipped once in each treatment. This was done to simulate natural conditions in the field as much as possible. The treated leaf was immediately placed in a transparent jar and 10 one-day old adults of C. plutellae were introduced and provided with food as described above. The parasitoids were transferred after six hours and mortality recorded after 48 hours following the same procedure described above. For the second method, adult parasitoids were introduced into a jar immediately after one puff of the insecticide solution had been sprayed into it from an Atomiser. The same procedure, with regard to feeding and recording mortality described above was followed. A control was set up using water in place of the insecticide solution. Each treatment was replicated four times. 50 A similar experiment was carried out using the pupae of C. plutellae. Each of the treatments was replicated four times and each replicate had 10 pupae. The filter paper and cabbage leaf procedures described above were followed for the pupae of C. plutellae. For the spray method, 10 day - old pupae were placed uniformly on a glass plate and sprayed quickly with one puff of the insecticide from an Atomiser filled with 2 ml of the insecticide solution. For the direct contact application method, the pupae were left to air-dry on the laboratory bench for 20 minutes after the 6 hour insecticide exposure period. After that each pupa was transferred into a clean separate specimen tube which was then plugged with cotton wooland left to stand in trays on the laboratory bench till adult emergence. For the control experiment, pupae were treated with water. Failure of pupae to emerge was taken as mortality due to the effect of the treatment Pupae which failed to emerge were kept and observed for a further three weeks after which they were dissected to determine their state of development (Day, 1994). 3.2.13 Statistical Analysis All mortality data were corrected for natural mortality using Abbot’s formula (Abbot 1925). All percentages were transformed using arcsine transformation and counts transformed using natural log prior to Analysis of Variance. Mean separation was done using Duncan’s Multiple Range Test (DMRT). Pearson’s correlation was used to determine the relationship between populations of P. xylostella and its parasitoid. All the analyses were done with the Statistical Programme for the Social Sciences (SPSS) version 16 software. 51 3.3 Results 33.1 Incidence and Seasonal Abundance of Lepidopteran Pests Larvae and pupae of six species of Lepidoptera were recorded on cabbage in all the three seasons at the Weija site. Five of the species were pests that fed directly on the plant and caused damage. These were the diamondback moth, Plutella xylostella, the cabbage looper. Trichoplusia ni, the cabbage webworm, Hellula undalis, the leaf worm Spodoptera littoralis and the African bollworm, Helicoverpa armigera. The distribution map of the pests recorded in this study is shown in Figure 3.1. The sixth species, the beet webworm, Spoladea recurvalis was occasionally found on cabbage, but was usually associated with the weed Cyperus rotundus (nut grass). Single specimens of Spodoptera triturata (Walker) were collected twice on cabbage at the experimental site during the minor rainy season. It was also collected once at the University of Ghana farms on Legon campus during the minor rainy season whilst the cutworm, Agrotis sp was recorded at Denche in the Western Region during a field survey. 52 PEST DISTRIBUTION MAP Figure 3.1: Distribution Map of Pests of Cabbage in Southern Ghana In vegetable growing areas (Fig.3.1 and Appendix 3.1) where fanners were encouraged to diversify under the Agro-skills Development and Farmer Field Schools Programme of the FAO/UNDP Poverty Reduction Programme of 1999-2001, the diamondback moth was not observed. The cabbage flea beetle, Phylothreta cheiranthei Weise, and Hellula undalis were present in the nursery and transplanted cabbage. Subsequent surveys in 2005 in Dodowa and Moyose in the Greater Accra region showed that the diamondback moth was still not present. The diamondback moth was also not recorded on cabbage in villages within the Homasi concession of Anglogold Ashanti (Ghana) Ltd. near Obuasi Mines in the Ashanti region where peasant farmers were introduced to the cultivation of cabbage in a vegetable diversification programme (Darpaah, 2008). 53 In general, it was observed that the abundance of pests at the experimental site was dependent on the prevailing season. In all seasons damage was observed three weeks after transplanting. The relative percentage abundance of pest species from the unsprayed plots for the three seasons is shown in Table 3.2. P. xylostella was most abundant in the dry season (69.6%) while Trichoplusia ni was most abundant in the major rainy season (79%). However, S. littoralis was most dominant in the minor rainy season, constituting 59% of the pest population. Helicoverpa armigera and H. undalis occurred in significant numbers during the dry season, but were both absent during the major rainy season Table 3.2 Relative Abundance of Larvae of Lepidopteran Pests of Cabbage in the Three Cropping Seasons on the Unsprayed Plots at the Experimental Site, Weija. Percentage Abundance Season Total No. of larvae P. xylostella T. ni S. littoralis H. armigera H. undalis S. recurvalis Major Rainy 329 20.4° 79.0a 0.6C 0.0k 0.0" 0.0b Minor Rainy 227 30.4b 9.3b 59.0” 0.4b 0.9b 0.0b Dry 296 69.6° 11.5b 5.4b 7.1“ 3.4* 3.0* TOTAL 8S2 40.0 37.0 17.9 2.6 1.4 1.1 Means in the same column with same letters as superscripts are not significantly different at the 5% confidence level (Duncan's Multiple Range Test). 54 On the farmer's farm, where various insecticides were applied, Plutella xylostella formed 88.8% of the total pests and T. ni formed 5.3% in an annual production of cabbage (Table 3.3). Plutella xylostella was significantly most abundant during the minor rainy season and T. ni occurred in significant numbers during the major rainy season. Hellula undalis populations were highest in the dry season and least in the minor rainy season. H. armigera was most abundant during the dry season. Table 3J: Relative Abundance of Larvae of Lepidopteran Pests of Cabbage in the Three Cropping Seasons on Farmer’s Plots at Weija. Percentage Abundance Season Total No. of larvae P. xylostella T. ni s. littoralis H. armigera H. undalis £ recurvalis Major Rainy 144 45.lb 36.1“ Thise 02. lb 09.0b 1.4* Minor Rainy 958 97.1“ 00.6C 00.9C 00. lb 01.0C 0.1“ Dry 69 47.8b 05.8b 10.1“ 18.8“ 17.4“ 0.0“ TOTAL 1171 88.8 05.3 02.1 01.5 02.0 0 3 Means in the same column with same letters as superscripts are not significantly different at the 5% confidence level (Duncan’s Multiple Range Test). 33.2 Comparative Abundance of Larvae of Lepidopteran Pests on Unsprayed Experimental Plots and on Farmer’s Plots at Weija On both experimental plots and farmer’s plots, Plutella xylostella was the most abundant during the study. There was a significantly higher number of P. xylostella larvae on the farmer’s plots compared with the experimental plots (p < 0.05) (Table 55 3.4). Conversely, Trichoplusia ni and S. littoralis were significantly more abundant on the experimental plots. Table 3.4: Comparative Percentage Abundance of Lepidopteran Pests on Experimental Plots and on Farmer’s Plots Plot Total No. of larvae P. xylostella T. ni S. littoralis H. armlgera H. undalis S. recurvalis Experimental Plots 852b 40.0b 37.0* 17.9* 2.6* 1.4* 1.1* Farmer's Plots 1171a 88.8* 5.3b 2.1b 1.5* 2.0* 0.3* Means in the same column with same letters as superscripts are not significantly different at the 5% confidence level (Duncan’s Multiple Range Test). 33 3 Population Density of Larvae of P. xylostella, T. ni and S. littoralis on Cabbage in the Three Seasons on Experimental Plots The population density of P. xylostella was highest in the dry season. A significantly high mean density of 0.29 ± 0.05 larvae per plant (p < 0.05) (Table 3.5) was recorded during this season compared with the other pests. The least was observed during the major rainy season. There were many instances where several larvae of the diamondback moth were observed drowned in water that had collected on cabbage leaves after rains. However, it was the only species that occurred in significant numbers for all the seasons. On the other hand, a significantly high mean density of 0.60 ± 0.11 larvae per plant (p < 0.05) of T. ni was recorded in the major rainy season compared with the other seasons (Table 3.5). With regard to S. littoralis. a significantly high mean density of 0.39 ±0.10 larvae per plant (p< 0.05) was recorded in the minor rainy season compared with the other seasons. Table 3.5 Population Density per Plant of Larvae of P. xylostella, T. ni and S. littoralis on Cabbage in the Three Seasons Pest Major Rainy Season Minor Rainy Season Dry Season S. littoralis 0.003 ± 0.003** 0.39 ± 0.10*** 0.05 ± 0.02** P. xylostella 0.15 ± 0.04** 0.20 ± 0.07‘b* 0.29 ± 0.05b* T. ni 0.60 ±0 .11b** 0.06 ± 0.03 b* 0.09 ± 0.02** Means in the same column with same letters as superscripts are not significantly different at the 5% confidence level (Duncan’s Multiple Range Test). *Means in the same row with same number of asterisk are not significantly different at the 5% confidence level (Duncan’s Multiple Range Test). 33.4 Incidence and Seasonal Abundance of the Parasitoids A total of 15 species of parasitoids, some of which also acted as hyperparasitoids were reared from the Lepidopteran pests at the experimental site (Table 3.6). Cotesia plutellae was the most important parasitoid of the major pest P. xylostella as well as T. ni, and was present throughout the year whenever cabbage was grown. Euplectrus laphygmae (Ferriere) was recorded in the major rainy season and minor rainy season and parasitized third instar larvae T. ni. None was collected in the dry season (February - March) when the incidence of T. ni was extremely low. It also parasitized S. littoralis on four occasions during the minor rainy season. The parasitoids C. curvimaculatus, Notanisomorphella sp and the two Tachinid species were specific to S. littoralis and they each parasitized this species only on two occasions during the minor rainy season and dry season. Only a single H. undalis was parasitized by C. plutellae. No parasitism of H. armigera was recorded and no egg parasitoids were observed from any of the pests during the study period. 57 Table 3.6 Seasonal Occurrence of Parasitoid/Hyperparasitoid Species and Lepidopteran Host Species on Cabbage at the Experimental Site Parasitoids/ Hyperparasitoids Host species Seasonality of Parasitoid Ichneumonoidea Cotesia plutellae P. xylostella and T. ni larvae All 3 seasons Chelonus curvimaculatus S. littoralis larvae MiRS Charops sp. T. ni & 5. littoralis larvae MiRS & DrS Chalcidoidea Brachymeria sp. T. ni larva via Charops sp MiRS & DrS Hockeria sp. P. xylostella larvae MiRS Elasmus sp. P. xylostella larvae via C. plutellae DrS Euplectrus laphygmae T. ni. & S. littoralis larvae MaRS&MiRS Notanisomorphella sp. S. littoralis larva DrS Oomyzus sokolowskii P. xylostella larvae via C. plutellae MaRS P. xylostella larva-pupa Tetrastichus atriclavus S.L T. ni larvae via C. plutellae MaRS Pediobius sp. P. xylostella larvae & pupae MaRS Trichomalopsis sp. P. xylostella larvae via C. plutellae MaRS T. ni larvae via C. plutellae MaRS Ceraphronoidea Aphanogmus reticulatus P. xylostella pupae via C. plutellae MaRS T. ni larvae via C. plutellae Tachinidae Blepharella sp near vasta S. littoralis larval-pupal MiRS Peribaea orbata S. littoralis larva MiRS MaRS = Major rainy season MiRS = Minor rainy season DRS= Dry season via C. plutellae means Parasitism of C. plutellae occurred inside P. xylostella. 58 Elsewhere in Ghana, C. plutellae was recorded in parts of the Greater Accra Region at the Kotobabi-PIant Pool (Accra), La Bawaleshi near Legon, Miotso near Dodowa, Dawhenya, and at Mampong in the Eastern region. The facultative hyperparasitoid O. sokolowskii was recorded in Dawhenya. Cotesia plutellae was the dominant and most important parasitoid observed. Seven hundred and six (706) parasitoids were recorded from P. xylostella in the three seasons and 92% were C. plutellae. The rest (8%) comprised of facultative hyperparasitoids; O. sokolowskii, Aphanogmus reticulatus, Trichomalopsis sp. Elasmus sp. and two primary parasitoids Pediobius sp. and Hockeria sp. Thus, the primary parasitoid C. plutellae was attacked by 4 parasitoids. In the major rainy season when T. ni was more abundant than P. xylostella, of the 110 parasitoids observed from the former, 60.9% and 35.5% consisted of C. plutellae and E. laphygmae respectively. The remaining included the hyperparasitoids Trichomalopsis sp. A. reticulatus and Tetrastichus atriclavus. Only 12 out of the 152 S. litloralis larvae were parasitized by the five species of parasitoids recorded from it during the whole study period at the experimental site. Cotesia plutellae and Oomyzus sokolowskii were the only primary parasitoid and facultative hyperparasitoid respectively, observed on the farmer’s farm. Cotesia plutellae parasitized 1% of the total diamondback moth larvae of 1,040 (88.8%) sampled. The parasitoids were observed during the major rainy season in May. Out of the twelve diamondback moth larvae parasitized by C. plutellae. 42% were hyperparasitised by O. sokolowskii 59 Based on the parasitoids and hyperparasitoids of P. xylostella and T. ni, the trophic relationships among species on cabbage is presented in figure 3.2. Figure 3.2: Trophic Relationships among P. xylostella, T. ni and Parasitoids and Hyperparasitoids on Cabbage. 33.5 Weekly Parasitism Trends by C. plutellae in Relation to P. xylostella Population build up of C. plutellae in relation to its host the diamondback moth during cabbage production on the unsprayed plots was a density dependent relationship where an increase in diamondback numbers resulted in a corresponding increase in parasitism (Figs. 3.3 - 3.5). The results indicated that there was a distinct time lag of one to two weeks in the major rainy and minor rainy seasons (Figs. 3.3 and 3.4) after which parasitism became closely synchronized with host numbers from 25 DAT in the former season. 60 ♦ P. xylostella C. plutellae 18 25 32 39 46 53 60 74 PEST DIRBU OUENTMAENR♦N— Figure 3 J : Weekly Parasitism Trends by C. plutellae in Relation to P. xylostella in the Major Rainy Season. Coefficient of Correlation r = 0.97 PEST DIRBU OUENTMAENR♦N— — *— P. xylostella — * — C. plutellae Figure 3.4: Weekly Parasitism Trends by C. plutellae in Relation to P. xylostella in the Minor Rainy Season. Coefficient of Correlation r = 0.55 61 In the dry season when build up of the pest was highest, there was no time lag between host numbers and parasitism (Fig. 3.5) and parasitism rates also increased as diamondback numbers increased. Figure 3.5: Weekly Parasitism Trends by C. plutellae in Relation to P. xylostella in the Dry Season. Coefficient of Correlation r = 0.66 The association between diamondback numbers and parasitism varied among the seasons and was strongest in the major rainy season. The Correlation coefficient r between diamondback numbers and numbers parasitized during the major rainy season was r = 0.97 whilst in the minor season r = 0.55. In the dry season the Correlation coefficient r = 0.66. The Coefficient of determination, R2 which is defined as the variation in parasitism that is dependent on the variation in diamondback numbers was R2 = r2 = 0.9709212 = 0.9427 = 94.3% in the major rainy season. Hence, 94.3% of the variation in parasitism was due to the variation in host numbers. In the minor rainy season, 30.8% of the variation in parasitism was due to the variation in diamondback moth numbers whilst in the dry season it was 44.0%. It was very common to find many cocoons of C. plutellae scattered on the leaves at 62 harvest of the cabbage in the major rainy and dry seasons. The overall Correlation Coefficient r. between the diamondback numbers and C. plutellae was 0.51. The Coefficient of determination R2 = 0.262. Hence, in an annual production of cabbage 26.2% of the variation in parasitism is due to the variation in the number of the diamondback moth. 33.6 Weekly Parasitism Trends by C plutellae and E. laphygmae in Relation to T. ni The relationship between the parasitoids C. plutellae and E. laphygmae and their host T. ni. was considered only for the major rainy season because no parasitism was observed during the minor rainy season and the population of the pest during the dry season was so low that any meaningful comparison was not possible. There was one week time lag after which the two parasitoids generally acted in a density dependent manner and the population started to build up around 25 DAT (Fig 3.6). Figure 3.6: Weekly Parasitism Trends by C. plutellae and E. laphygmae in Relation to T. ni in the Major Rainy Season 63 3.3.7 Parasitism of P. xylostella by C. plutellae in Three Seasons Wide seasonal variations were observed in the rates of parasitism. Mean percentage parasitism of P. xylostella by C. plutellae was highest (p < 0.05) during the major rainy season (68.6% ± 12.9) and least during the minor rainy season (9.9% ± 7.1). There was no significant difference (p > 0.05) in the rates of parasitism between the Figure 3.7: Seasonal Variation in Mean Percentage Parasitism of P. xylostella by C. plutellae Bars with same alphabets are not significantly different at the 5% confidence level (Duncan’s Multiple Range Test). 33.8 Parasitism of P. xylostella by C. plutellae on Insecticide Treated Plots Parasitism of larvae of P. xylostella was substantial despite the insecticide pressure imposed. Parasitism rates were higher on the Karate treated plots but these were not significantly different (p. > 0.05) from the unsprayed. Bt. and neem seed water extract (NSWE) treated plots for all three seasons (Table 3.7). 64 Table 3.7 Mean Percentage Parasitism of P. xylostella by C. plutellae on Different Treatments in the Three Seasons % Parasitism Treatment Major Rainy Season Minor Rainy Season Dry Season Unsprayed 68.6 ± 12.9a* 9.9 ± 7.1a** 43.7 ± 8.9a* Bt 78.3 ± 12.1a 60.6 ± 4.2a Karate 81.3 ± 4.1a 11.1 ± 6.6a 61.3 ± 4.1a NSWE - 3.3 ± 3.3a 50.3 ± 8.8a Means with the same letters in the same columns are not significantly different at the 5% confidence level. Duncan’s Multiple Range Test. ♦Means in the same row with different number of asterisks as superscripts are significantly different at the 5% confidence level (Duncan’s Multiple Range Test). 33.9 Parasitism of T ni by C. plutellae and E. laphygmae in the Major Rainy Season Mean percentage parasitism of T. ni by C. plutellae and E. laphygmae during the major rainy season was 29.4% ± 7.5. 33.10 Parasitism of T. ni by C plutellae and E. laphygmae on Insecticide Treated Plots There was no significant difference (P > 0.05) in parasitism of T ni by C. plutellae and E. laphygmae irrespective of treatments (Table 3.8). Table 3.8 Mean Percentage Parasitism of T. ni by C plutellae and £ laphygmae on Different Treatments in the Major Rainy Season Treatment % Parasitism Unsprayed 29.4 ± 7.5a Bt 36.7 ± 9.4a Karate 41.7 ± 20.1a Means with the same letters in a column are not significantly different at the 5% confidence level, (Duncan’s Multiple Range Test). 65 33.11 Emergence of C. plutellae Adults from Field Parasitised Pests The proportion of C. plutellae adults that emerged from field parasitized P. xylostella was not significantly different (p > 0.05) between unsprayed and Karate treated plots in all seasons (Table 3.9). In the major rainy season the highest mean percentage adult parasitoid emergence was recorded from hosts collected from Bt treated plots. The single P. xylostella larva collected from the neem treated plots in the dry season emerged, hence, the 100% emergence of parasitoid adults. Table 3.9 Emergence of C. plutellae Adults Reared from Field Parasitized P. xylostella from the Different Treatments in the Three Seasons Season Unsprayed Karate Bt Neem Major rainy season 79.17 ± 10.63'*’ 71.64 ± 10.39“* 100±0.00b* - Minor rainy season 75.00 ±25.00*' 53.35 ± 18.84"* - 100 ±0.00* Dry season 80.18 ± 10.49"* 65.69 ±6.80“* 70.91±11.25’** 64.57 ±6.04* Means in the same row with same letters as superscripts are not significantly different at 5% confidence level (Duncan’s Multiple Range Test). 'Means in the same column with different number of asterisks as superscripts are significantly different at 5% confidence level (Duncan’s Multiple Range Test). Where there is no asterisk, data was not included in analysis. It was also observed that it was only C. plutellae adults recorded from the diamondback moth collected from Karate treated plots that died in the process of eclosion (could not push the cap of the pupal case), or died the same day, lived for only a day or were malformed (twisted wings or twisted abdomens). With regard to T. ni the highest proportion of adult parasitoids emerged from pest samples collected from Bt. treated plots (100%) and unsprayed plots (85.70 ± 6.33) and the least (53.96 ± 29.14) from samples collected on Karate treated plots (Figure 66 100 | 80 §> _ t 60 f 40S* 20 0 120 Unsprayed Karate Bt OUBER*BNR Neem Figure 3.8: Emergence of both C. plutellae and E. laphygmae Adults from Field Parasitized T. ni from the Different Treatments in the Major Rainy Season Bars with the same letters are not significantly different at the 5% confidence level (Duncan’s Multiple Range Test). 33.12 Emergence of C plutellae Adults Collected as Pupae Exposed to Different Insecticides in the Field Seasonal differences were observed in the abundance and adult emergence from parasitoid pupae collected in the field (Figure 3.9 and Appendix 3.2). The highest total numbers of parasitoid pupae were collected from the Karate treated plots in both seasons. Percentage emergence of parasitoids was significantly higher (p > 0.05) in the major rainy season samples than the dry season samples in all treatments (Figure 3.9). In the major rainy season, there was no significant difference (p > 0.05) between the rates of adult emergence of parasitoid pupae collected on Karate treated plots and the unsprayed plots. There was also no significant difference (p > 0.05) between the rates of emergence from samples collected from the Bt and unsprayed plots (Figure 3.9). In the dry season, the rate of emergence in samples collected from all treatments was similar. 67 100 90 80 70 60 50 40 30 20 10 0 Unsprayed m II li. |. |ii ■ i Karate Bt Treatment Neem OMajor Rainy Season ■ Dry Season Figure 3.9: Percentage Emergence of C. plutellae Adults Collected as Pufiae from the Different Treatments. Bars of the same colour with different letters are significantly different at 5% confidence level (Duncan’s Multiple Range Test). Component bars with different number of asterisks are significantly different at 5% confidence level (Student’s t-Test). 33.13 Mortality of C plutellae Adults and Emergence of Pupae Exposed to Insecticides in the Laboratory. The test insecticides differed with respect to the mortality caused to adults and pupae of C. plutellae (Figure 3.10). Generally, mortality was higher in the adult parasitoids than in the pupae. Of the insecticides tested. Karate had the most adverse effect on adults of C. plutellae irrespective of application method. It resulted in 100% mortality of C. plutellae within ten seconds of direct exposure. 68 ■Karate ■Bt □Neemazal Key: FP= Filter paper CL=Cabbage leaf dip S = Spray Figure 3.10: Mortality of Adults and Pupae of C. plutellae Exposed to Different Insecticides. Bars of the same colour with different letter are significantly different at the 5% confidence level (Duncan’s Multiple Range Test). Neemazal had the least adverse effect on the adults after 48 hours. Bt. at 1.0 g/iitre and Neemazal at 1% caused a significantly higher mortality in the pupae than in the adults. The application methods of the insecticides had variable effects on both the adults and pupae of the parasitoid. A significantly higher mortality of 31% (p < 0.05) was recorded in the pupae exposed directly to Neem Azal as spray whereas Karate caused only 3.6% after 48 hours. Discussion The Lepidopteran species found on cabbage in Ghana were similar to species recorded in some countries (Talekar, 1992; Anene and Dike, 1996; Dobson et al, 2002). However, other pests such as Pieris rapae (Linnaeus) (Oatman and Platner. 1969) and Crocidolomia binotalis (Zeller) (Sastrosiswojo and Setiawati, 1992) recorded elsewhere in South East Asia were not observed in the present study. Forsyth (1966) however, reported C. binotalis on cabbage in Aburi and Tafo both in the Eastern region of Ghana. Plutella xylostella is considered as a serious pest worldwide and occurs in significant numbers in parts of South East Asia (Talekar, 1992) but in France, Germany and South Africa it is ranked substantially low (Lim, 1986; Mosiane, et al., 2003). Results of this study have shown that it occurred in abundance on cabbage in areas where the crop had been traditionally grown for at least 10 years in Ghana. However, contrary to reports by Tadashi et al. (1986), Walunj and Pawar (2004) and (Pratissoli) et al. (2008) that P. xylostella occurs wherever cabbage is grown, the field surveys carried out during this study, showed that the pest had not yet invaded some areas in the Greater Accra region where farmers were introduced to grow cabbage for the first time under the Agro-skills Development and Farmer Field Schools Programme of the FAO/UNDP National Poverty Reduction Programme in (1999 - 2001). In these areas where cabbage had been recently introduced, the cabbage flea beetle, Phyllotreta cheiranthei and Hellula undalis were present. Plutella xylostella was also not present in villages located near the Homasi concession of Anglogold Ashanti Ghana Ltd. in the Amansie Central District in the Ashanti Region. Spoladea recurvalis is not considered a pest of cabbage as it was more associated with the weed, Cyperus rotundus. Its population was only 1.1% of the total Lepidoptera pests in an annual production of cabbage at the experimental site and may have moved onto the crop from the weeds. Adults were usually observed resting on weeds rather than on the cabbage. 70 This study has demonstrated, for the first time, the seasonality of the major Lepidopteran pests in Ghana. Trichoplusia ni was more abundant than P. xylostella in the major rainy season but the latter was present in significant numbers throughout the year and may therefore, cause more damage in an annual production of three seasons. Plulella xylostella consumes more foliage than T. ni in an annual production of cabbage despite the voracious feeding habit of T. ni (Harcourt et al., 1955; Capinera, 1999). It overshadows T. ni because of its ability to quickly develop resistance to virtually all insecticides used to control it (Hill and Foster, 2000). It is the most important of the crucifer pests and causes severe economic damage to cabbage (Sarfraz et al; 2005). The continuous presence of this pest on the same plants that were sampled weekly throughout the study period also suggests that there may be as many as 20 generations per year. Keinmeesuke et al. (1992) and Abdel-Razek et al. (2006) reckoned that as many as 20 - 25 generations can occur in a year in the tropics. There were several instances when whole crops were lost to Plulella xylostella at the experimental site and farmers had to prematurely harvest their cabbage or abandon their farms because of the pest (Cobblah, 2000). Attention must be paid to Trichoplusia ni during the major rainy season, having constituted 79% of the total pest population during the period of this study. This would be in agreement with observation by Anene and Dike (1996) who observed that in Nigeria, the population of T. ni can reach epidemic levels. Hellula undalis constituted only 1.4% of the total pests, and was only present during the minor rainy season and dry season. The pest is known to cause extensive damage to cabbage seedlings in the nursery as well as young plants in the field (Muniappan and Marutani, 1992; Jayma and Ronald, 2007). It has been reported as a major pest of cabbage in Ghana (Obeng-Ofori et al.. 2007). Spodoptera littoralis has not been recorded on cabbage in Ghana before and may be 71 considered seasonal as it occurred in significant numbers only in the minor rainy season during the study. Helicoverpa armigera accounted for 2.6% of the pest population throughout the study. Various Spodoptera species, as well as Helicoverpa armigera are considered occasional or seasonal pests on cabbage in various countries (Boling and Pitre. 1971; Waterhouse. 1992; Poelking, 1992; Berg and Cock, 2000). Findings from the present study also indicate that the incidence and importance of a particular species and. its seasonal trends may vary from place to place and with time of planting as observed by Dennill and Pretorius (1995) and Mosiane et al. (2003). Ooi (1986) and Alam (1992) noted that dry season or warm weather favours the build­ up of P. xylostella. This observation has been confirmed in the present study with the populations of P. xylostella significantly higher during the dry season than in the major rainy season when T. ni was more abundant. Conversely, Nagarkatti and Jayanth (1982) observed a significantly higher build-up of P. xylostella during the rainy season compared with other seasons. Of the fifteen species of parasitoids and hyperparasitoids recorded from the pests. Cotesia plutellae was the most dominant parasitoid and was active in all the three seasons at the experimental site. It accounted for over 90% parasitism of the diamondback moth as have been observed in parts of China by Liu et al. (2000) and in South Africa by Mosiane et al. (2003). It comprised 60.9% of parasitism of T. ni. Apart from C. plutellae, about 30 species of Chalcidoidca have been recorded in the literature as primary parasitoids or hyperparasitoids of P. xylostella (Fitton and Walker, 1992). The authors, however, believe that most of these may well be hyperparasitoids identified from rather dubious, single, casual rearings and, therefore. 72 require confirmation from further studies. Of the six species recorded in the present study, and which are also included in the above previous records, only Elasmus sp was obtained from a single rearing. The present study has, therefore, confirmed five species as credible records at least in Ghana. The other five species were both parasitoids and hyperparasitoids. Of these, O. sokolowskii, the commonest hyperparasitoid obtained in this study, had been reported as indigenous to various Islands in the West Indies, occurring wherever cabbage was grown (Alam, 1992). Euplecirus laphygmae was the second most important parasitoid of T. ni having accounted for 35.5% of its parasitism. Parasitoids of the pest are however, not considered key mortality factors (Oatman and Platner (1969) cited in Capinera, 2008). The six species of parasitoids recorded from S. littoralis caused only 8% parasitism during the study period. When C. plutellae occurred together with Euplectrus laphygmae, a gregarious parasitoid which was found in this study to be restricted to Trichoplusia ni and Spodoptera littoralis, it caused a higher rate of parasitism in T. ni than did E. laphygmae. Only a single Hellula undalis was parasitized by C. plutellae during the study. However, in Malaysia, Sivapragasam and Chua (1997) reared a braconid. Bassus sp. and an ichneumonid Trathala flavoorbitalis (Cameron) from the larvae on cabbage. The authors nevertheless, noted that these parasitoids were not important mortality factors of the pest as they were present only at the end of the season and also in very low numbers. Apart from the effects of parasitoids, the low incidence of P. xylostella in the major rainy season could also be attributed to the rains washing off the relatively small larvae. There were many instances in the present study when several larvae of 73 Plulella xylostella were observed drowned in water on the lower leaves of the cabbage plant after rains. In addition, during heavy rains on three occasions in the major rainy season (June), not a single P. xylostella larva was recorded on plants which were sampled after the rains. This seasonality can be exploited in the timing of planting to avoid heavy infestation and also to reduce irrigation costs. The drowning effect of rain on P. xylostella has been simulated in Asia where sprinkler irrigation systems in experiments considerably reduced pest numbers (Nakahara et al., 1986; Tabashnik and Mau, 1996). Wide variations in parasitism levels by C. plutellae had been recorded from locality to locality, season to season, and from country to country, even in areas with similar climates (Jayarathnam, 1977; Ooi and Chua, 1986; Hu et al., 1997; Rowell et al.. 2005). It had also been observed that parasitism levels by this parasitoid could not exceed 60% (Ooi, 1979 a & b; Ooi. 1992). In the present study, mean parasitism rate recorded was significantly higher in the major rainy season (68.6 ± 12.9%) than in the minor rainy season (9.9 ± 7.1%). Seasonal variations of parasitism by this parasitoid were also noted by Yadav et al. (1974) but he on the contrary, observed that the rains reduced percentage parasitism. In China Liu et al. (2000) recorded 10 - 60% whilst in Thailand Rowell et al. (2005) recorded between 14 - 78%. In addition, the combined mean parasitism of 29.4 ± 7.5% caused by C. plutellae and £. laphygmae to T. ni in the major rainy season suggests the need to conserve these parasitoids. They are unquestionably valuable agents for biological control of P. xylostella and T. ni on cabbage in Ghana. 74 The relationship between diamondback moth and C. plutellae, was observed to be a clear and distinct density dependent one, with a positive correlation between them in all the three seasons in the present study. Cock (1985) also made similar observations and observed that rates of parasitism by C. plutellae was between 89 - 100% in the Carribean, whilst Alam (1992) noted that parasitism rates could go up to 100% in Jamaica. The least correlation of 0.55 and the highest of 0.97 were observed in the minor rainy season and major rainy season respectively. The initial time lag between the parasitoid and its host in the present study during the minor rainy season and the major rainy season could be attributed to the very low infestation levels of the diamondback moth early in the crop season. Hu et al. (1997) and Mitchell et al. (1997b) considered this parasitoid inefficient because of its poor searching ability when pest populations were low. Ooi (1986) and Ooi (1992) also contended that in Malaysia, this parasitoid could not prevent diamondback moth numbers from rising in the dry season when pest populations were high. Among the reasons advanced for the inability of C. plutellae to increase with increasing pest numbers are the lack of understanding of its biology (Fitton and Walker, 1992) or the consequences of environmental factors such as temperature and humidity (Loke et al.. 1992). However, Ingham and Kfir (1997) indicated that in South Africa this parasitoid was effective when diamondback moth populations were high. Contrary to the observation by Ooi (1992), in the present study, C. plutellae caused a mean parasitism of 43.7 ± 8.9% of P. xylostella with a coefficient correlation of 0.66 during the dry season when pest populations were highest. Notwithstanding these contrasting observations, the presence of C. plutellae in all three seasons and its ability to increase with increasing pest numbers make it a good candidate for biological control of the 75 major Lepidopteran pest, P. xylostella as well as T. ni in the cabbage ecosystem in Ghana. The ineffectiveness of C. plutellae in keeping diamondback moth populations down in some countries had also been attributed to activities of hyperparasitoids (Moral lo- Rejesus and Sayaboc, 1992). The negative effect of hyperparasitoids had however, been refuted by other workers who argued that they are of little significance and of no economic impact (Robertson, 1939; Mustata, 1992). In the present study, the total composition of the four hyperparasitoid species was less than 8.0% and was mainly the facultative species O. sokolowskii. The high parasitism rates caused by C. plutellae to diamondback moth on karate- treated plots at Weija, provide some support to the findings by Ooi (1992) that, this parasitoid has developed resistance or is tolerant to insecticides in the field. Furlong et al. (1994) noted that C. plutellae was more tolerant to pyrethroids than other parasitoids of P. xylostella. Loke et al. (1992) observed a mean parasitism of 48.6% whilst Liu et al. (2000) recorded substantia) rates of parasitism even under very heavy insecticide pressure. In the present study, the mean parasitism of 81.3 ± 4.1% observed on the Karate treated plots in the major rainy season and 61.3 ± 4.1% in the dry season lend further credence to these observations. Nevertheless, further and more direct studies are required to determine the insecticide resistance status of this parasitoid on cabbage in Ghana in order to draw firmer conclusions. The extremely low parasitism of the diamondback moth observed on the farmer’s farm could be attributed to the indiscriminate use of the variety of insecticides applied 7 A from very early in the season. Rowell et al. (1992) noted that, the main ‘gap’ in the occurrence and activity of diamondback moth parasitoids appears to be the critical period early in the season when farmers are most likely to treat with broad spectrum insecticides. Even though substantial numbers of the parasitoids reared from P. xylostella hosts collected from Karate and neem seed water extract treated plots emerged, the parasitoids were adversely affected. Neem inhibited or arrested growth and development, and prevented the larvae that emerged from field parasitized hosts from pupating or spinning cocoon. Even when they spun their cocoon, on dissection, it was found that the larva had not undergone structural differentiation. Adult parasitoids that emerged from pests collected from Karate treated plots were short lived, living for only a day, or dying soon after eclosion or during eclosion. In some cases the thin line of weakness along the pupal case from where the adult would emerge was visible but they could not emerge and their heads were broken off. There was no significant difference between emergence rates of C. plutellae collected as pupae from Karate- treated plots (81.3 ± 8.19%) and unsprayed plots (69.10 ± 90%) in the major rainy season. This observation may be due to the rains diluting the effects of the insecticide. The results of the laboratory studies on the direct effect of Karate on C. plutellae adults is similar to observations made by Condor (2007), who observed that the insecticide caused 100% mortality to adult Diadegma mollipla. another important parasitoid of P xylostella. The implications of these are that Karate could reduce the 77 effectiveness of C. plutellae by directly eliminating them, or causing a decrease in the numbers that will be available to sustain succeeding generations of the parasitoids. Even though the neem adversely affected development of the parasitoid in this study at the concentrations used, there is also evidence that, neem treatments do not affect parasitoids and can be compatible with Integrated Pest Management programmes when lower doses are used or depending upon the formulations (Charleston et al., 2005; Haseeb et al., 2006). Previous studies had shown that certain pesticides were highly toxic to adult C. plutellae when sprayed directly at the recommended rates while others showed little to no toxicity (Kao and Tzeng, 1992; Perez et al, 1995). The results also indicate that the choice of insecticide that could be integrated with C. plutellae for pest management on cabbage should be properly understood. Variation in the response of C. plutellae to the test insecticides, imply that an effective pest management strategy for P. xylostella that would include this parasitoid and chemical control can be developed. The results have also contributed in clarifying the relationships that are important in the integrated pest management of the diamondback moth and the other pests. Integrated pest management programme that is focused on conservation of local parasitoids will help alleviate the growing public concern regarding the effects of pesticides on vegetable growers and consumers. From the results obtained, an integrated pest management strategy based on either the use of lower doses of neem seed water extract or Bacillus thuringiemis and Cotesia plutellae, coupled with appropriate timing is recommended for the Weija vegetable irrigation company WEICO. 78 CHAPTER FOUR 4.0 BIOLOGY AND ECOLOGY OF THE PARASITOIDS OF LEPIDOPTERAN PESTS OF CABBAGE 4.1 Introduction Parasitoids alone, or in combination with other control measures, have been employed against various cabbage pests with varying degrees of success (Mitchell et al., 1997a, b; Mahar et al., 2004). They are nevertheless a valuable control component and resource and. unless the important ones are made a part of any management strategy against the pests of cabbage, the plague of the major pest, P. xylostella and other related problems are likely to persist (Clausen, 1978; Lim, 1986; Liu, et al., 2000; Pratisolli et al.. 2008). Parasitoids provide considerable impact and effective check on multiplication of the diamondback moth (Lim, 1992; Ooi, 1992; Hamilton et al., 2004). In some countries, there is direct evidence that the action of parasitoids arrest or obliterate infestations of P. xylostella or keeps it under control (Ingham and Kfir, 1997). In some instances, reduction in pest population is so marked that the use of insecticides could become unnecessary (Waterhouse, 1992). Indeed, there are known cases of successful P. xylostella control in which the basic control component constituted parasitoids (Lim, 1986; Mustata et al., 2006). However, investigations into the biology and ecology of the important parasitoids of P. xylostella are limited (Lim, 1986; Pratisolli et al, 2008). Fitton and Walker (1992) suggested that the contradictory reports regarding the effectiveness of C. plutellae in reducing the population of the diamondback on cabbage could be due to a lack of understanding of the biology of this parasitoid in various countries. On the other hand, contribution of parasitoids in the control of the other pests on cabbage has not been encouraging or 79 clear (Talekar N. S. 1992; Sivapragasam and Chua, 1997; Capinera, 2008; Jayma and Ronald. 2007). The guild of parasitoids recorded on the diamondback moth is large and varies from region to region, though not all of them are effective (Lim, 1986; Mustata el al.. 2006). Only a few species of Trichogramma and Trichogrammatoidea have been reared from the eggs. These, however, gave satisfactory results and good searching ability in the laboratory, but did not show promise in the field (KJemm el al., 1993). Nevertheless, Keinmeesuke et al. (1992) observed that Trichogrammatoidea bactrae Nagaraja caused parasitism of 16.2 - 45.2% from diamondback moth eggs collected from the field. The greatest control is provided by the larval parasitoid species belonging to the Hymenoptera genera, Diadegma, Cotesia and Microplitis (Sarfraz el al., 2005). Attention is therefore increasingly being given to their use in controlling the major pest of cabbage worldwide. However, in Africa in general, and Ghana in particular, the identities and biology of members of the parasitoid complex are either not known or are very poorly known (Quicke, 1997; La Salle, CABI Bioscience UK Personal communication). Indeed, for any meaningful exploitation of the parasitoids associated with either the major pest or the other lepidopterous pests of cabbage in Ghana, it is vital that their biology and especially their behaviour in the field are very- well understood. Understanding the biology of local populations of parasitoids would yield valuable information on host ranges in nature that can also be useful in rearing for augmentative releases in biological control. 80 The objective of this study was to determine the biology (life history, lifestyle, longevity and host preference) and ecology (searching and oviposition behaviour) of the parasitoids of the pests observed in this study, with emphasis on the dominant one based on laboratory and field data. 42 Materials and Methods 4,2.1 Field Sampling and Rearing of Host - Plutella xylostella Cotesia plutellae was the predominant species observed from the Lepidopteran pests and was, therefore further studied in the laboratory in the Department of Zoology’ (now Department of Animal Biology and Consercation Science, DABCS) of the University of Ghana. In order to study the parasitoid, the host had to be obtained and reared. Larvae of P. xylostella were collected from cabbage at the experimental site at Weija. The larvae still attached to cabbage leaf were kept in petri dishes lined with wet filter paper and brought to the laboratory. Prevailing laboratory conditions were a mean temperature of 23 ± 2 °C and relative humidity of 45 ± 1.0%. The larvae were individually placed on moist filter paper in petri dishes on the laboratory bench and were fed with fresh pieces of cabbage leaf daily and observed till the adult pest emerged. Emerging adults were put in mating and oviposition wooden cages measuring 45 x 45 x 45 cm and provided with 10% honey solution soaked in cotton wool and placed in a petri dish. A small cabbage seedling was placed in a beaker containing water and placed inside the cage for oviposition by P. xylostella. The eggs that were laid by P. xylostella were harvested still attached to the leaf and incubated in a petri dish lined with wet filter paper till hatching. Upon hatching, the newly emerged larvae were placed separately in a petri dish and fed with cabbage leaves. 81 4.2.2 Field Collection and Rearing of Parasitoids Cotesia plutellae pupae that emerged from P. xylostella larvae that had been collected in the experimental plots were kept in tubes till emergence of adult parasitoids. In addition, parasitoid pupae still attached to pieces of cabbage leaves were carefully detached with a pair of forceps and brought to the laboratory. The adult parasitoids that emerged were fed on 10% honey solution and allowed to mate in small plastic transparent cages (11.0 x 7.0 cm) fitted with gauze for 24 hours before being used for the study. Data for the other parasitoids (Euplectrus laphygmae, Chelonus curvimaculatus, Oomyzus sokolowskii. Tetrastichus atriclavus s.L, Aphanogmus reticulatus, Charops sp, Brachymeria sp. Hockeria sp, Notanisomorphella sp, Elasmus sp. Pediobius sp, Trichomalopsis sp, Blepharella vasta and Peribaea orbata) were taken from the field samples as well as in the laboratory where possible. As a result, the numbers of each species used varied depending upon availability. 4.23 Life History and Lifestyle Studies of Cotesia plutellae A male C. plutellae was exposed to a female for 24 hours to allow mating in a transparent glass jar (7.0 x 6.0 cm) that had been provided with a streak of 10% honey solution and covered with a piece of gauze. The female was then aspirated through a slit made in the cover of the rearing jar into another prepared transparent jar (7.0 x 6.0 cm) containing a three-day old P. xylostella larva reared in the laboratory as described above (4.2.1), a piece of cabbage leaf and a streak of 10% honey solution as food for the pest and parasitoid respectively. The interaction between the adult female parasitoid and the diamondback moth host was observed. After 24 hours, the adult 82 female parasitoid was allowed to escape into a rearing cage and the host larva transferred into a petri dish lined with a wet filter paper and provided with a piece of cabbage leaf. The larva was observed daily till the parasitoid larva emerged or the host pupated. Food for the host was changed every other day till pupation of host or emergence of parasitoid larva. It was not possible to determine the egg incubation period inside the host so the total egg incubation and larval duration was determined for each individual parasitoid. The duration of the pupal period of the parasitoids was recorded. The nature of the newly emerged parasitoid larva and its appearance were noted. The spinning of the pupal case by the parasitoid larva and the position from which the adult parasitoid emerged from the pupal case were also noted. The sex of the parasitoid was determined after adult emergence based on the presence or absence of an ovipositor. Four replicates each consisting of five adult C. plutellae were used in the studies. The data were then pooled and the mean developmental periods determined. 4.2.4 Longevity Studies of Cotesia plutellae To determine the longevity of mated and unmated C. plutellae adults, two experiments were set up. In the first experiment, 10 day-old unmated adult male and female parasitoids were kept singly in tubes and plugged with absorbent cotton wool. Each parasitoid was fed on a streak of 10% honey solution which was replenished every third day. In the second set-up, a newly emerged male was exposed to a female for 24 hours to allow mating in a transparent glass jar (7.0 x 6.0 cm). They were then separated and placed singly in glass tubes plugged with absorbent cotton wool and provided with a streak of 10% honey solution as food. Each parasitoid was observed daily till it died. The period between the beginning of the experiment and death was 83 recorded as longevity in days for each individual parasitoid. The data were pooled for each category and the mean longevity determined. 4J.5 Oviposition Preference of Plutella xylostella Larvae by Cotesia plutellae In order to determine the preferred diamondback moth host stages by C. plutellae, a no-choice experiment was conducted. Twelve newly mated parasitoid females were individually exposed to each of 3 day old (2nd instar), 6 day-old (3rd instar) and 8 day old (4lh instar) larvae o f the diamondback as described above. After 24 hours, the parasitoid was allowed to escape and the host larva transferred into a petri-dish lined with a wet filter paper and provided with a piece of cabbage leaf. The larva was observed daily and the piece of cabbage changed every other day till the host pupated or the parasitoid larva emerged. The number of diamondback moth larvae from which parasitoid larvae emerged for each larval instar was pooled and the percentage preference calculated. 42.6 Field Observations on Biology and Ecology of the Parasitoids Field observations were carried out on the seven central plants of the unsprayed plots at the experimental site at Weija as the pests were sampled. The part of the plant where parasitism of pests occurred in the field was recorded. Searching and oviposition behavior of adults in the field were recorded. The number of parasitoids that emerged from a host, the developmental stage and the behavior of the parasitoid were also recorded. Parasitoid lifestyle was recorded as solitary when only one adult emerged from its host and gregarious when more than one adult emerged from its host. In addition, where possible the duration of larval and pupal stages of the other parasitoids were recorded from field samples of pests described in Sections 3.2.7 and 84 3.2.8 of this thesis. The sex ratios were calculated for each parasitoid species from the numbers of male and female adult parasitoids reared from field samples of pests but the numbers used varied according to availability. For C. plutellae, the sex ratio was calculated from 151 individuals reared from field-collected larvae of the diamondback moth 43 Results 43.1 Biology and Ecology of Cotesia plutellae 43.1.1 Life History and Lifestyle of C. plutellae The duration of the total life cycle of Cotesia plutellae in the laboratory at an average temperature o f 23 °C ± 2 and relative humidity of 45 % ± 1 was similar for males and females. It averaged 16.0 ± 0.5 days and 16.1 ± 03 days for males and females, respectively. The egg incubation plus larval developmental period averaged 9.1 ± 0.4 days for males and 9.1 ± 0.2 days for females. Pupal period was 6.9 ± 0.3 days and 7.1 ± 0.3 days for males and females, respectively. The adult parasitoids mated on the same day that they emerged. During courtship, the males intensively fanned their wings around the females as they attempted to mount them. Cotesia plutellae behaves as a solitary endoparasitoid and lays one egg per host. Thus, only one adult emerges from a parasitized host. The adult C. plutellae, after laying her egg in the larval host exhibited koinobiosis, allowing the host larva to feed and develop for some time. The final larval instar of the parasitoid emerged after about 9 days and immediately began spinning a creamish to off white cocoon whilst remaining very close to the host, most probably soliciting the needed physical support 85 from its host (Plate 4.1). The newly emerged final larval instar of C. plutellae was translucent, yellowish green and slightly curved. It usually emerged from the posterior part of the host near the proleg and stayed close to the host. The sclerotised mandibles of the parasitoid larva were distinctly visible as it spun the cocoon. Within 24 hours, it pupated on the leaf surface near the host (Plate 4.2). The pupa was firmly attached to the leaf surface. The newly formed cocoon was slightly rough and appeared as a thin net-like cover around the pupa. By this time the host had stopped feeding and looked pale. It became deformed as a result of the parasitoid exit hole and assumed a characteristic more or less ‘C’ shape (Plate 4.2) but was still capable of some movements. The unparasitised diamondback moth larva maintains its spindle shape (Plate 4.3). Plate 4.1: Newly emerged C. plutellae Plate 4.2: C. plutellae larva (arrowed) and host pupa (arrowed) and host Plate 4.3: Unparasitised |»|atl. 4.4 : Empty pupa| cocoon P. xylostella larva |xlO| of c. plutellae (arrowed) 86 At the end of the pupal period, the cocoon opened at one end through which the adult parasitoid emerged (Fig. 4.4). Sometimes the cap remained attached or it was completely detached from the rest of the pupal case. By the time the adult parasitoid eclosed, the host carcass had dried up (Plates 4.4 and 4.5). Plate 4.5: Carcass of P. xylostella after parasitism .3.1.2 Longevity of Mated and Unmated Adnlt Cotesia plutellae Mated and unmated females lived for an average of 13.7 ± 1.1 days and 7.7 ± 0.6 days, respectively. On the other hand, mated and unmated males lived for an average of 15.8 ± 1.5 days and 7.0 ± 0.6 days respectively. 3 .1 3 Oviposition Preference of Plutella xylostella Larvae by Cotesia plutellae In the no-choice experiments, adult Cotesia plutellae attacked 2nd instar (3 day-old), 3rd instar (6 day-old) and 4lh instar (8 day-old) larvae of Plutella xylostella, but with a preference for second and third instar larvae. Eighty percent (10/12) and 50% (6/12) of second and third instar larvae of the diamondback moth were parasitized, respectively as opposed to 33% (4/12) of the fourth instar larvae. 87 When presented with the large hosts (i.e 3rd - 4th instars), the parasitoid had more difficulty inserting her ovipositor to lay eggs. The host always put up a defensive behaviour, vigorously wriggling around the parasitoid and either dropping via a silken thread, or dislodging the parasitoid. Sometimes, the host flipped off the parasitoid so vigorously that it hit one side of the glass tube. After such an encounter the parasitoid always spent some time cleaning itself after which it made another attempt., 1.3.1.4 Field Observations on Parasitism by C. plutellae Cotesia plutellae normally parasitises the second or third instar larvae of the various Lepidopteran pests of cabbage, namely; Plutella xylostella, Trichoplusia ni, Spodoptera littoralis and Hellula undalis in the field. C. plutellae is, therefore, not strictly host specific though the results obtained from the field indicated that it preferred P. xylostella. In the field, the emerging parasitoid larva always laid very close to its host as was observed in the laboratory and pupation usually occurred on the ventral surface of the leaf. As the pupa aged, the thin cocoon which covered it was sometimes lost or washed off after rains. The pupae of C. plutellae emerging from P. xylostella were smaller than those from T. ni and they had an average length of 3.05 ± 0.01 mm (N = 20) compared to an average of 3.64 ± 0.06 (N = 20) mm for T. ni. Cotesia plutellae was sometimes observed to attack older larvae of T. ni in the field, but the host was not killed and continued to develop till the parasitoid emerged after which the adult moth also emerged. In such cases, the emergence hole could still be seen on the host larva obviously not having been adversely affected. For example, five adults of C. plutellae emerged from three 3rd and two 5lh instar larvae of T. ni 88 which later pupated and normal adult moths also emerged. Large larvae of T. ni were observed to be exceptionally defensive when the parasitoid attempted to oviposit in them. In the cases when C. plutellae parasitised larvae of S. littoralis and H. undalis, the adult parasitoid failed to emerge from its pupa. On the two occasions that multiple parasitism of Cotesia plutellae, Euplectrus laphygmae and another unidentified gregarious parasitoid was observed, C. plutellae out-competed them, with the adults emerging whilst the other species died. When both C. plutellae and £. laphygmae parasitised T ni larva the former species emerged, with only a few of the latter emerging. As the crop matured and was ready for harvest, it was common to see a number of parasitised hosts, parasitoid pupae and newly emerged parasitoid larvae close by the hosts together on one leaf. Adult parasitoids were often observed in the field systematically and vigorously tapping their antennae and ovipositor along the cabbage leaf surfaces from the edges, obviously searching for hosts. This was particularly common when Plutella xylostella populations were low. When the crop had matured, several of the parasitoids were observed hovering above the plant. The sex ratio was slightly higher for males than for females. Field collected samples gave a sex ratio ratio of 1: 1.06 (73 females: 78 males). 89 43 2 Biology and Ecology of Other Parasitoids Charops sp (Ichneumonidac) This was found to be a solitary parasitoid of late larval instar of Trichoplusia ni and Spodoptera littoralis. It was in turn parasitised by a Brachymeria sp and was present during the dry and minor rainy seasons from October to March. The larva (N = 2) that emerged from field parasitized host was amorphous in shape, pale brown (off white) and was very soft and flexible. It pupated within an hour or two after emergence from the host. It formed a brown oval shaped pupal case which had a ring of conspicuous black spots close to either ends of the pupal case (Plate 4.6). The pupal case measured between 6.0 - 6.9 mm long in females and 5.2 - 5.5 mm in males. The ends were slightly flattened and in the field, it hanged on the ventral side of the leaf by means o f a strong silken thread (Plate. 4.6). The pupal period ranged from 6 - 9 days in females with an average of 6.5 days. The male pupal period lasted seven days for each of a sample of five pupae. The adult parasitoid emerged through the sub-dorsal side of the case above the ring of black spots (Plate 4.6). 90 Chelonus curvimaculatus (Ichnenmonidae) This species was observed to be a solitary parasitoid of larvae of Spodoptera littoralis. Only two males were recorded in the minor rainy season. Brachymeria sp (Chalcididae) A species of Brachymeria was recorded as both a primary solitary parasitoid of pupa (N = 5) of T. ni and a secondary parasitoid of T. ni via Charops sp. Specimens that were reared as hyperparasitoids from T. ni via Charops sp were smaller measuring between 3.0 - 3.2 mm long compared to those that acted as primary parasitoids which measured between 5.4 - 5.6 mm long. 91 Hockeria sp (Chalcididae) A species of Hockeria was recorded only on two occasions from the diamondback moth larvae. It was a gregarious parasitoid with a male to female sex ratio of 1:1.5 (N = 10). Elasmus sp. (Elasmidae) This was observed as a gregarious hyperparasitoid of diamondback moth larva via Cotesia plutellae. The adults emerged from the lateral side of the parasitoid pupa It was recorded only once (N = 4) during the dry season in March when the cabbage was ready for harvesting. Euplectrus laphygmae (Eulophidae) These were active gregarious koinobiont ectoparasitoids of third to fourth larval instars of T. ni and S. littoralis. When E. laphygmae attempted to oviposit in the host caterpillar it flipped off the parasitoid with its abdomen. The adult parasitoid always persisted until the ovipositor was successfully inserted after which the caterpillar did not attempt to flip it off but continued to struggle till the parasitoid left. The female laid more than one egg in a host. The newly hatched parasitoid larvae were small green, round to oval bodies with thin pale transverse bands on the body. They partially buried themselves in the host and fed on the tissues from the outside (Plate 4.7). The mature larvae formed aggregations on the dorsal surface of the host, usually around the middle patch from where they all fed (Plate 4.8). The larvae when matured were barrel or spindle shaped and fully emerged from the caterpillar host. Unlike the unparasitised T. ni caterpillar which was bright green, the host at this time became very pale, sluggish and stopped feeding (Plate 4.8). The parasitoid larvae 92 later turned slightly pale and migrated to align themselves along the entire ventral surface of the host and pupated within twenty-four hours (Plate 4.9). Plate 4.7: Newly hatched larvae of E. laphygmae [x 2.7] (arrowed) penetrating host to feed Plate 4.8: Larvae of E. laphygmae (arrowed) about to m igrate to pupate Plate 4.9: Mature larva of E. laphygmae migrating (arrowed) down the host to pupate 93 Each larva spun a loose cocoon within which it pupated such that each remained separated from the other. A secretion fixed the cocoons to the host and also to the substrate (cabbage leaf) which rendered it difficult to dislodge. By this time, the host was a dead dark brown flattened carcass with remnants of the cocoons (Plate 4.10). Plate 4.10: Carcass of T. ni larva after parasitism by E. laphygmae The pupal period varied ranging from 4 to 13 days depending upon temperature in the laboratory which ranged from 22.5 - 28 °C. The progeny size per host varied from 2 - 17 individuals depending upon the size of the host and was sex biased towards females. The mean ratio of males to females recorded from field parasitism of T. ni: was 1.0:6.5 (N = 45). Size variation was observed in adults of E. laphygmae depending on the number emerging from a particular host. Larger hosts ranging in length from 16 - 20 mm had more progeny (7 - 13) than smaller ones less than 10 mm. Where 2 - 3 individuals emerged from large hosts, they were bigger in size. Where progeny size was large (15 - 17) a mixture of small and big females were observed. Where progeny size was not more than four (N = 5), only females were produced. In four instances a male each emerged from fourth instar larva of T. ni. 94 Notanisomorphella sp. (Eulophidae) A solitary parasitoid species of Notanisomorphella (N = 2) was reared from third instar caterpillar of Spodoptera littoralis and were both males. It was recorded at Weija during the dry season when the cabbage was cupping. The larva that emerged from the host in the laboratory was soft, pinkish, and apodous. PrcpupaJ period was three days during which the integument hardened to form a pupa The pupa was creamish, exarate and did not spin a cocoon. The two brown eyes were clearly visible. Antennae and legs became visible after three days, after which the adult emerged the following day giving a pupal period of four days. Oomyzus sokolowskii (Eulophidae) This was both a gregarious larval-pupal parasitoid of Plulella xylostella and a hyperparasitoid of the same host larva via Cotesia plutellae in the rainy season (April and May). The parasitoid emerged from the diamondback moth larvae that had been parasitized by C. plutellae as well as pupae of the diamondback moth that was collected as larvae from the field. At three different temperatures and relative humidity conditions of 25 °C and 70%, 22 °C and 45%, 20 °C and 37% in the laboratory, the pupal periods of field parasitized larvae were 11 (N = 6), 19 (N = 11) and 21 (N = 5) days respectively. The adults emerged through a small opening in the middle of the dorsal surface of the host. The size of the progeny when it behaved as a parasitoid was greater than when as a hyperparasitoid. Ratio of male to female from diamondback moth pupae (N = 24) was 1:11 and from C. plutellae (N = 17) was 1:4.7. 95 Tetrastichus atriclavus W aterston s.l. (Eulophidac) This was a gregarious primary parasitoid of both Trichoplusia ni larva and a secondary parasitoid via Cotesia plutellae. The adults (N = 13) emerged through a small opening in the center of the dorsal surface of the host. Pediobius sp. (Euiophidae) A gregarious species of Pediobius was recorded as a parasitoid of the diamondback moth larvae and pupae (N = 4) in the major rainy season (May - June). Trichomalopsis sp. (Pteromalidae) This was a primary solitary parasitoid and a hyperparasitoid of the diamondback moth via C. plutellae. The adult was not active and emerged by a small opening on the sub- dorsal side towards the apex of the cocoon (N = 35). This species was observed in the major rainy season from July to August. Aphanogmus reticulatus (Fouts) (Ceraphronidae) This is a gregarious endoparasitoid and hyperparasitoid of the pupa of Plutella ylostella via C. plutellae (N = 33) in the major rainy season. It was not active and flew for short distances giving the impression of hopping. Emergence hole of the adult was around the middle portion of the pupal cocoon. The number of individuals emerging per host was 3 - 11 and was female biased. Ratio of males to females was 1:9.8. Blepharella sp. near vasta (Karsch) (Tachinidae) This species is a Koinobiont larval-pupal endoparasitoid which attacked late larval instars of Spodoptera littoralis. For a period of three days before pupation, the host larva became quiescent and shortened and its cuticle became brown and crinkled after which it pupated. The parasitoid continued to develop within the pupa of S. littoralis from which it emerged as a solitary species (N = 2) (Plate 4.11). Plate 4.11: Adult B. sp. nr. vasta |x 2.5) and pupal case of S. littoralis from which it had emerged Peribaea orbata (Wiedemann) (Tachinidae) This species was collected during the minor rainy season from October to December when the cabbage had headed. It is a gregarious parasitoid of the larvae of S. littoralis. The parasitoid larvae (N = 29) fed within the host larva and reduced it to a slightly liquid mass of tissue and later emerged as pale maggots by which time the host was dead. They then continued to feed externally on the mass of liquefying tissue for 3 - 4 days after which they pupated in small dark reddish puparia (Plate 4.12). The pupal period lasted for 6 to 11 days at 26 °C in the laboratory. Five to eleven adults emerged from a single host. The adult parasitoid emerged from the puparium through a neatly cut opening or a rugged opening. 97 Plate 4.12: Adult P. orbata [x 14) and its pupal case Discussion The most abundant and important primary parasitoid of P. xylostella and T. ni recorded in this study is Cotesia plutellae. It is one of the three most important species recorded elsewhere in Asia, parts of Africa and Central Europe (Waladde et ai. 1997; Anene and Dike, 1996; Mitchell et al., 1997 a & b; Ingham and Kfir 1997). The mean total developmental period of 16.1 days of the parasitoid suggests that it may take at least, this length of time before the first adults would emerge from the eggs laid by the first females to arrive on cabbage, by which time pest numbers would have increased. It has usually been assumed that Cotesia plutellae is host specific to P. xylostella (Talekar and Griggs, 1986; Talekar, 1992; Fitton and Walker, 1992). However, Fitton and Walker (1992) have compiled from the literature twenty Lepidopteran host species, but questioned the identity of most of these records, and suggested the need for a critical appraisal of host specificity. The results obtained from this study indicated that, at least in southern Ghana, C. plutellae is not host specific. It was observed to parasitize four other Lepidopteran pests on cabbage, i.e. Trichoplusia ni, Spodoptera littoralis and Hellula undalis but it, undoubtedly, showed a preference for P xylostella. Contrary to observations in parts of South East Asia (Talekar, 1992), in the present study, none of the first larval instars of P. xylostella collected from the field was parasitized by C. plutellae. This parasitoid may also be adapted to specific host size and therefore likely to shift to any other hosts which fall within that size range in the absence of adequate numbers of P. xylostella. It was observed that large host larvae of T. ni and P. xylostella were more defensive than smaller ones and always vigorously flipped them off when this parasitoid tried to oviposit. Baur and Yeargan (1994) and Brodeur et al. (1996) also recorded that defensive behaviour increased with host age of caterpillars. Kawaguchi and Tanaka (1999) and Shi et al. (2002) concluded that parasitism by C. plutellae decreased sharply with increasing host age in the fourth instar and approached zero in host larvae that had gone beyond 37% of the fourth stadium. This suggests that the acceptance phase might be used as a reliable indicator of its host specificity to P. xylostella and younger stages of T ni. The fact that C. plutellae was not restricted to P. xylostella is not expected to have negative implications on its use for biological control of P. xylostella as it has a preference for it. It was also able to out-compete other parasitoids including £. laphygmae when there was multiple parasitism. Fitton and Walker (1992) have suggested that records of species of the Braconid genus Chelonus, as parasitoids of the diamondback moth should be treated as doubtfully correct. The present study has 99 however, confirmed that in Ghana, Chelonus curvimaculatus Cameron does not parasitise P. xylostella instead, it parasitised S. littoralis. Quartey (1975) referred to a species of Chelonus parasitizing a stem borer species in Eastern Ghana, but it has not been possible to recover this specimen for examination and comparison with the specimen observed on cabbage in the present study. This is the first time a parasitoid species belonging to the genus, Chelonus has been recorded from S. littoralis on cabbage in Ghana Charops species have been reared from rice stem borers and Acraea terpsicore L. in various parts of Ghana such as Goaso, Kumasi, Atwoabo and Tokwabo (Forsyth, (1966; Duodu and Lawson, 1983), but the observation of a new Charops sp as a parasitoid of T. ni and S. littoralis in Ghana is a first record. Species of Brachymeria had been recorded as parasitoids mainly from pupae of Lepidoptera, a few Coleoptera, Hymenoptera and Diptera. Boucek (1988) noted that some species are obligatory or occasional hyperparasitoids but others are known to be solely primary parasitoids. Members of this genus can act as both parasitoids and hyperparasitoids as shown in this study and earlier observed by Boucek (1988) and Ganeshan et al. (1997). Several species of Hockeria are known to parasitise pupae of small to medium sized Lepidoptera, some of which are Totricidae, Pyralidae and Yponomeutidae (Boucek 1988), (La Salle, pers. comm.). The present record from the diamondback moth pupae on cabbage has added to the list of recognized hosts. 100 Elasmus species had been recorded as hyperparasitioids of the diamondback moth by Fitton and Walker (1992). This is the first record of this hyperparasitoid of the diamondback moth via C. plutellae on cabbage and in Ghana. Euplectrus laphygmae is widely distributed in Africa, and had been recorded mainly from species of Plusia Latreille and S. littoralis, all in the family Noctuidae (Ferriere, 1941; 1947; Boucek, 1988; Ganeshan et al., 1997). However, this is the first record of £ laphygmae in Ghana and also as a parasitoid of T. ni on cabbage. Zhu and Huang (2003) did not list Ghana among the African countries with records of this species in their study of the Genus Euplectrus. Notanisomorphella species had been recorded as parasitoids of small leaf mining insects (Lepidoptera and Hispine beetles). One species had been recorded from spider egg sacs, possibly as a hyperparasitoid (Boucek, 1988). Various species had been recorded in Southern Europe, throughout Africa and warmer parts of Asia and Australia It is recorded here in Ghana for the first time as a solitary parasitoid of young larvae of S. littoralis. The status of O. sokolowskii in the trophic system of cabbage appears to be controversial. It had been recorded as parasitoids, mainly of Coleoptera (Boucek, 1988) and as hyperparasitoids of the diamondback moth (Chelliah and Srinivasan, 1986; Mahmood et al., 2004). Wakisaka et al. (1991) (cited in Talekar and Hu, 1996) had also observed that (). sokolowskii was a pupal parasitoid of the diamondback moth. Talekar and Hu (1996) showed that in the laboratory, (). sokolowskii failed to parasitise pupae of the diamondback moth and argued that it was a larval parasitoid. In the present study, however, this parasitoid was reared from both field collected diamondback moth larvae that had been parasitized by C. plutellae, as well as from field collected diamondback moth larvae that later pupated in the laboratory. These suggest that it acted as a hyperparasitoid of the diamondback larvae via C. plutellae as well as a larval-pupal parasitoid of the diamondback moth. . 2006). Tetrastichus atriclavus s. L had been recorded in this study as a primary and a hyperparasitoid of T. ni via C. plutellae. They had also been observed from pupae of Lepidoptera and sometimes, as hyperparasitoids (Boucek, 1988) as observed in this study. Elsewhere, species of Pediobius had been recorded as primary or secondary parasitoids of eggs, pupae and sometimes larvae of Lepidoptera, Coleoptera, Diptera, Hymenoptera and a few others, including spider egg masses (Burks, 1966). Forsyth (1966). in his book on the agricultural insects of Ghana, made no record of Pediobius species. The observation of a Pediobius sp as a parasitoid of the diamondback moth larvae and pupae on cabbage appears to be a first record in Ghana. Graham (1969) indicated that, the typical hosts of Trichomalopsis species are pupae of Coleoptera and Lepidoptera. In the present study, they were reared as primary parasitoids and hyperparasitoids of the diamondback moth larvae via C. plutellae. This is the first time A. reticulatus has been recorded as a hyperparasitoid of Cotesia plutellae via P. xylostella on cabbage in Ghana. The species is a widespread indigenous African species, hyperparasitic on lepidopteran hosts via Apanteles sp. and 102 Cotesia sesamia (Cameron) (Polaszek and La Salle, 1995). The authors reared A. fijiensis (Ferriere) from stem borers in Ghana. The species was also recorded as a hyperparasitoid of C. plutellae in Barbados by Cock (1985). Peribaea orbata parasitized only Spodoptera littoralis in Ghana. It is known to be a common African species and parasitizes various species of Noctuidae including Helicoverpa and Spodoptera spp. (pers. com. N. Wyatt, British Museum Natural History). Blepharella sp. near vasta is also restricted to S. littoralis. The species probably parasitizes lepidopterous larvae, as do other members of this genus (pers. com. N. Wyatt, British Museum Natural History). For the first time in Ghana, this study has provided and illustrated the guild and complex of parasitoids and hyperparasitoids of the major Lepidopteran pests on cabbage in three seasons at the experimental site. Of the species of the three important genera of parasitoids recognized worldwide, Cotesia plutellae is the most important in southern Ghana. Very little information on parasitoids attacking T. ni exists possibly because of its relatively insignificant pest status on cabbage. The results of this study have laid a good foundation for further research in Ghana on the biology and ecology of parasitoids that would help in our understanding of the dynamics in the entire cabbage ecosystem and be exploited for integrated pest management strategy to control the pests. 103 CHAPTER FIVE 5.0 DESCRIPTION OF STAGES OF LEPIDOPTERAN PESTS, BEHAVIOUR AND DAMAGE 5.1 Introduction Cabbage is an important vegetable crop worldwide and in Ghana it is the most important in the family Cruciferae. However, attack and damage by the complex of Lepidopteran pests make its production difficult (Bangnikon, 1996; Obeng-Ofori et al., 2007). These pests are however, of unequal importance and their ecological characteristics and nature of damage may also differ depending on local climatic conditions, country and variety of cabbage (Ooi, 1986; FAO, 1992; Abdel-Razek et al.. 2006). There are also variations in biological and morphological parameters of the different stages of the pests on cabbage in different locations and countries (Salinas. 1986; Sarfraz et al., 2008). It is, therefore, necessary that the specific niches that these pests occupy on the plant and the nature of damage caused in relation to the cabbage variety, and local conditions should be well understood in order to implement effective management strategies. This will also ensure that the parasitoids are protected through targeted and more efficient application and appropriate timing of insecticides in an Integrated Pest Management programme. The objective of this study therefore, was to describe the stages of the pests observed in this study in relation to behaviour and damage on cabbage to enable their recognition, identification and management. 104 5.2 Materials and Methods 5.2.1 Rearing of Lepidopteran Pests Eggs of P. xylostella. T. ni and S. littoralis attached to cabbage leaves were cut off with a pair of scissors from cabbage plants on an unsprayed plot at the experimental site in Weija. 39 days after transplanting and taken to the laboratory in the Department of Zoology. University of Ghana. Eggs of H. undalis and H. armigera were not included as they were not observed. One, three and 10 leaves of cabbage were sampled for P. xylostella, T. ni and S. littoralis respectively. Records of the distribution and sizes of egg batches on the leaves were taken on the same day. Each leaf was cut into six pieces and kept separately on a wet filter paper in a petri dish placed on a bench in the laboratory. They were maintained at 12:12 hours of light/dark regime till they hatched. Ten newly emerged larvae of each species were separated singly into petri dishes on the 3rd day and provided with pieces of young cabbage leaves (KJC cross variety) placed on wet tissue paper. The food was changed every day till pupation. Daily observations were made on the development, behaviour and morphology of the developmental stages of each species till the adults emerged. In addition, the patterns of damage by the larvae maintained singly in petri dishes (14 cm wide) with a whole cabbage leaf and also on cabbage plants in cages in the laboratory were observed and photographed. Forty newly emerged adult males and females of P. xylostella were kept in each of two wooden oviposition cages (45 x 45 x 45 cm) with young cabbage plants in water and maintained on 10% honey solution soaked in a petri dish. Courtship, mating, and ovopisition behaviour were observed at 8 hours, 12 hours, 17 hours and 21 hours for 5 days. The cages were observed daily and the leaves with eggs were either removed or 105 the whole plant was removed and replaced. Morphological studies were made of the larvae, pupae and the adults. All the experiments were carried out at a mean temperature of 27 ± 0.2 °C and relative humidity of 55 ± 1.0%. Visual observations were also made in the field of all the pests (P. xylostella, T. ni, S. littoralis. H. undalis and H. armigera) on the seven central plants of the unsprayed plots at the experimental site as they were sampled. Observations regarding when they appeared on the cabbage plant, their location, posture, feeding pattern and movements were recorded and photographs taken. 53 Results 5.3.1 Description of Stages of Lepidopteran Pests, Behaviour and Damage 53.1.1 Plulella xylostella (Linnaeus) Eggs of P. xylostella were observed on cabbage plants 18 - 19 days after transplanting. The female laid her eggs singly or in small batches of two to six, usually on the ventral surface of the leaf. For a total of 150 batches of eggs collected from the three leaves, 69.3 % were laid on the ventral surface and 30.7% on the dorsal surface. Of the 150 egg batches, 48.7% were laid singly, 31.3% in groups of two and the rest in groups of three to six (Table 5.1 and Plate 5.1). Table S.l Percentage of Eggs Laid in a Batch by P. xylostella in the Field Number of Eges in a Batch % of Total 1 48.7 2 31.3 3 8.7 4 5.3 5 2.0 6 4.0 Number of Batches = 150 106 in the laboratory, the eggs were usually concentrated at the lowest part of leaves of plants standing in water. On two occasions egg batches of 12, 17, and 18 were observed very close to the base of the leaf. Sometimes the eggs were deposited very close to the leaf stalk. Eggs were also laid on the sides of the cage. The eggs were always cemented to the substrate in a way that made it impossible to remove them without causing damage to either the eggs or the leaf. In the field, eggs were often laid close to leaf veins and in depressions on the leaf. The eggs were creamy and sausage or oval shaped (Plate 5.1). Plate 5.1: Eggs of P. xylostella (x 6| on cabbage leaf The newly emerged caterpillars were pale green, slightly hairy and had black heads. As they grew the colour deepened and they lose their hairs. The larvae of P. xylostella were more or less spindle-shaped (Plate 5.2). The first instar caterpillars buried their heads in the underside of the leaf and fed from there, leaving small punctures which made the surface of the leaf looked densely punctured. Even though the second to fourth instars also fed from the ventral surface, they chewed from the 107 surface leaving the upper epidermis looking like a pale or white patched area which later dried up to form the characteristic ‘windowing’ associated with damage by this pest (Plate 5.2). The characteristic black faeces were always associated with damage on cabbage. Plates S.2: Mature larvae of P. xylostella [x 3] and damage on cabbage leaf, faeces are arrowed The caterpillars of P. xylostella started attacking cabbage from two-week old seedlings to maturity. They were usually found on all parts of the plant but often concentrated on young leaves in the inner portions of the plant and on the upper leaves. The young caterpillars sometimes hid in the growing point of the plant and may go unnoticed. Sometimes, mature caterpillars bored into the developing head or small mature heads and some effort was usually needed to pull them out. They often fed close to each other on the leaf and also aggregated on a few plants whilst others had zero to few individuals on them. The caterpillars were very active and wriggled violently backwards or dropped off the plant via a silken thread when disturbed. They hung unto the thread and later climbed back unto the plant. The mature caterpillar 108 could grow up to 12 mm at a mean temperature of 27 ± 0.2 °C and relative humidity of 55 ± 1.0%. Mature caterpillars moved to the lower parts, usually on the ventral surface of the leaf, to pupate. They also pupated on the heads when cabbage was maturing. Pupation took place after a pne-pupal period of one day. 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Hellula undalis (Fabricius) Crop Knowledge Master, ^PP- http://www. extento. hawaii. edit. 223 APPENDICES APPENDIX 3.1 Towns where cabbage was grown for the first time in 1999-2001 or 2008 Region/Town(s) P. cheiranthei H. undalis GREATER ACCRA Dodowa + Moyose + - EASTERN Donkorkrom - + Amankwa Tano + WESTERN Suiano + - Denche/Moasue + - Senyaguakrom + - ‘ASHANTI Prago - + *Cabbage grown for first time in 2008 + Means present - Means not present 224 APPENDIX 3.2 Total Numbers of C. plutellae pupae collected from the different plots exposed to insecticides in the field. Treatment Major rainy season Dry season Total no. of pupae Total no. of pupae Unsprayed 194 178 Bt 94 160 Karate 518 828 NSWE - 177 Total 806 1343 APPENDIX 3.3 Percentage emergence of C. plutellae adults collected as pupae exposed to different insecticides in the field Species Major rainy season (N=865) Dry season (N=1302) C. plutellae 84.0 95.2 A. reticulatus 6.35 - Trichomalopsis sp 8.20 4.1 Others 1.41 0.7 225