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1 EFFECTS OF INTERCROPPING SWEET POTATO ON THE POPULATION DENSITY OF SWEET POTATO WEEVIL, û1as formicariys (F.) (COLEOPTERA: CURCULIONIDAE) By ALEXANDER YAKU A thes i s submi tted to the Facu l ty of Graduate Studies and Research in partial fulfillment of the requi rement for the degree of Master of Science Department of Entomology l d Campus of McGi 11 University, Montreal Quebec, Canada Il Al exander YakLc June 1992

Transcript of digitool.library.mcgill.cadigitool.library.mcgill.ca/thesisfile56673.pdf · ABSTRACT M.Sc ALEXANDER...

1

EFFECTS OF INTERCROPPING SWEET POTATO ON THE POPULATION DENSITY OF SWEET POTATO WEEVIL, û1as formicariys (F.)

(COLEOPTERA: CURCULIONIDAE)

By

ALEXANDER YAKU

A thes i s submi tted to the Facu l ty of Graduate Studies and Research in partial fulfillment

of the requi rement for the degree of Master of Science

Department of Entomology ~Iacdona l d Campus of McGi 11 University, Montreal Quebec, Canada

Il Al exander YakLc

June 1992

-l

Suggested short title:

Sweet potato weevil control by intercropping

Alexander Yaku

J

ABSTRACT

M.Sc ALEXANDER YAKU ENTOMOLOGY

EfFECTS OF INTERCROPPING SWfET POTATO ON THE POPULATION DENSITY OF SWEET POTATO WEEVIL, Cylas. formicarius (F.)

(COLEOPTERA: CURCULIONIDAE)

Fi el d experi ments were conducted duri ng the 1989 dry season

(Ju 1 y to Oecembe r) a t the Manggoapi Fa rm of the Facu l ty of

Agnculture, Cenderawasih University in Manokwari, Irian Jaya,

Indones i a. The obj ecti ves of the experiments were to determi ne the

effects of four sweet potato cropping systems on the population

densi ty of sweet potato weevils (SPW) and on the diversity of other

i nsec ts wi th in these ag roecosys tems .

Fewer SPW were found in i ntercropped sweet potato + corn

(2 weevi 1 s per kg infected tubers), sweet potato + soybean (21

wccvi 1 s), sweet potato + corn + soybean (8 weevi 1 s) than in

monoc u 1 tu re sweet potato (37 weevi 1 s); percentage of damaged tubers

followed the same trend, ranging from 2.6 % to 14.0 % in

lntercropped sweet potato, to 21.9 % in the sweet potato

monocul ture. However, the hi gher number of SPW and damaged tubers

in the monoculture did not reduce yield below that in the

l ntercropped plot s, wh i ch had lower yi el ds becaus e of reduced sweet

potato density and higher interspecific plant competition.

Consequently, numbers and weight of tubers per plant, as we" as

I11drketable yield, were highest in the monoculture.

i

Insect and spider populations were more diverse in the

i ntercropped sweet pota to sys tems than in monocu lture. Number of

arthropods increased throughout the growl ng season, reélching a peak

at 56 days after planting (DAP). Intercroppi ng may reduce the

popul ation densi ty of other insect pests associated Wl th sweet

potato ( e.g., the spotted tortoise bettle ~doll1orptlg sp. was

less abundant), and may increase the popul ation densi ty of natural

enemies (e.g., the spider Lycosa sp. was more abundant).

ii

.'

RESUME

M.Se ALEXANDER YAKU ENTOMOLOGIE

EFFETS DE DIVERS TYPES D'ASSOCIATIONS DE CULTURE DE LA PATATE DOUCE SUR LA DENSITE DE POPULATION DU CHARANÇON DE LA PATATE

DOUCE, Çy-l_~~ formicarius (F.) (COLEOPTERE: CURCULIONIDAE)

Des essa i s en champs ont été réa li sés pendant 1 a sa i son sèche

1989 (J U 111 et à Décembre) à l a ferme Manggoapi de la Facu l té

d'Agricultrure de l'Université Cenderawasih en Manokwari, de la

province d'Irian Jaya, en Indonésie. Les obj eet ifs de ces

ex péri en ces vis aient à détermi ner les effects de qua t re sys tèmes de

culture de la patate douce sur la densité de poplilation du

charancon de la patate douce et sur la diversité de l'entomofaune

à l'intérieur de ces divers agroécosystèmes.

Le nombre de cha rançon éta i t bas dans 1 es as soc ; at ions patate

douce - maïs (2 charançons [ch.] Ikg de tubercules i nfestp~ Et. i], patate douce - fève soya (21 ch. /kg de t. i ), patate douce - maïs -

fève soya (8 ch. /kg de t. i .) comparé au nombre de charançons

présent dans la monoculture de patate douce (37 ch./kg de t.i .).

Le pourcentage de tubercules attaqués suit cette même tendance; 2,6

à 14 7., des tubercules étdient attaqués dans les associations de

culture et 21.9 :1., dans la monoculture. Tout de même, le nombre

plus élevé de charançons et de plants infestés retrouvé en

l11onocu l tu re ne corres pond pas à une ba i sse de rendemen t de 1 a

patate douce car il était pl us élevé dans la monocul ture que dans

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· ..

T !

les cultures associées; le rendement inférieur dans ces dernières

est attribué à une densité plus faible de plants et li la

compétition interspécifique des plants. Par conséquent, le nombre

et le poids de tubercules frais ainsi que la récolte

commercialisable étaient donc plus élevés dans la monoculture.

L ' entomof aune éta i t plus divers i fi ée cians les sys tèmes de

polyculture que dans la monoculture. Le nombre d'arthropodes a

augmenté au cours de la saison, pour atteindrê un maximum 56 jours

aprè le repiquage. La polyculture a semblp réduire la densité de

population des autres insectes ravageurs de la patate douce (ex. la

casside, Aspidomorpha sp. y était moins abondante) et augmenter la

densité des ennemis naturels (ex. l'araignée Lycosa. sp. y était

plus nombreux).

iv

ACKNOWLEDMENTS

First of all, my greatest thanks and appreciation go to God,

Who by His infinite grace and faithfulness provided the

unpredictable opportunity to study in Canada. Only through His

power and guidance have 1 been able to undertake this work.

1 want to express my gratitude to the Indonesian Government,

especially to the Ministry of State for Population and Environment

and the Environmental Management Development of Indonesia (EMOI)

ProJect (a Joint proJect of the Indonesian Ministry of State for

Population and Envi!'or.ment, and the School for Resource and

~ Environmental Studies, Dalhousie University for the Environmental

Management Oevelopment of Indonesia) for granting me a scholarship

to study in Canada and to conduct the field research in Indonesia.

In this regard 1 am especiall.\1 indebted for the efforts of the

former EMOI Project Officers, Dr. Shirley A.M. Conover, Dr. Tania

Ll, George Green and the late Ors. Sjafran Sjamsuddin.

1 would also like to thank (1) Dr. Joan M. Campbell, E~1DI

ProJect Officer in Halifax, and her staff, especially Pauline

Lawrence and Lynnc Norrena who have given considerable attention

to the solving of various problems, (2) Barbara C. Duffield, former

EMOI Project Officer in Jakarta and her staff, especially Mrs.

P.M. Abclulkadir, Mrs Wisnu and Mr. Sony for their assistance

during my field research in Indonesia.

v

T

l wi sh to acknow1 ecge the he1 p of the Dean of the Facu l ty of

Agricd1ture, Cènderawash University, for providing facilities

during my field research in M~nok~ari.

1 am grateful ta my twa faithful assÎ::,tants, Cornelles Iji and

Paulus Jumame, for their help with field work, and their

willingness ta guard the crops against theft during the nights of

the last six weeks before harvest.

l would like to thank Or. Helene Chiasson, Tanya Searle and

Susan Johnson, fOl"' help in insect identification, writing style and

analysis of data during the preparation of the thesis.

l am extreme1y grateful ta my academic superVlsor, Dr. Stuart

B. Hi 11 for his encouragement and understanding, which gave me the

se l f-confi den ce n€:cessa ry to s ucceed in th i s endeavour. Hi s adVl ce

and patience in readirg and carrecting the manuscript are a1so

appreci ated.

My gra t i tude al so goes to fe 11 ow s tudents and fri ends, Joanny

Zongo and Dr. Graham Thurston for providing time for discussion,

both entomalogy, and on how ta adjust to 11fe in Canada.

Fina11y, 1 would like to thank my wife Poulla and daugther

Catherine for their support and understanding in patiently waiting

for the day of my graduation. 1 wou1d a1so like to thank my

father, mother, l rothers and sisters who have always support~d my

efforts in prayer.

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Ca nad ian Theses Service

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AVIS

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{:

.,

TABLE OF CONTENTS

ABSTRACT

RESUME

. . . . . . . . . . . . . . . . .. . . . . .

ACKNOWLEDGEMENTS

LIST OF TABLES

LIST OF FIGURES

CHAPTER

1 . 1 NTRODUCTION

11. LITERATURE REVIEW

Page

ï i i

v

x

xii

1

12

2. 1. B IOECOLOGY OF THE SWEET POTATO WEEVI L, ÇyJ éiS formicarius (F.) (COLEOPTERA: ~URCULIONIDm 13

2.1.1. 2.1.2. 2.1.3.

2.1.4. 2.1.5. 2.1.6.

Taxonomie status and distribution Host range Life cycle a. Egg .. b. Larva . c. Pupa .. d. Adult .......... . Feedi ng habi ts and crop damage. Reproducti on . • . . . . . . . . . Factors affecting infestation by SPW

2.2. ROLE OF INTERCROPPING IN FOOD PRODUCTION.

2.2.1. 2.2.2. 2.2.3.

Definitions .......... . Status. . . . . . . . . . . . . . Advantages and di sadvantages. . .

2.3. EFFECTS OF INTERCROPPING ON INSECT PES rs. 2.3.1. Rate of eolonization ..•..

a. Visual effeets ...•.. b. 01 factory effects . • .. c. Di vers i on a ry hos t effeets

13 15 16 16 18 19 19 22 23 24

26

26 27 30

34

35 35 36 36

vii

111.

"

1 V •

2.3.2. 2.3.3. 2.3.4.

Oevelopment ......... . Di spersa 1 . . . . . . . . . . . Abundance of natura l enem; es. .

MATERIALS AND METHOOS . .

3.1.

3.2.

3.3.

Site description

Experimental design .

Crop arrangenment and spacing within each treatment ............. .

3.3.1. Sweet potato monocu l ture . . . . 3.3.2. Sweet potato and corn . . . . . 3.3.3. Sweet potato and soybean . . . . 3.3.4. Sweet potato, corn and soybean . 3.3.5. Sweet potato, tomato and cabbage

3.4. Field preparation and management

3.4.1. Land preparation ..... 3.4.2. Preparation of planting materials 3.4.3. Planting and fertilizing ....

3.5. Crop maintenance

3.6. Observations

3.6.1. 3.6.2.

Colonization by SPW ...... . Population density of SPW and percentage

3.6.3. 3.6.4. 3.6.5. 3.6.6.

of damaged tubers . . . . Number and fresh weight of Marketable yield .... . Monetary index ... . Insect diversity .... . a. Sweep net sampling b. Pitfall traps ....

tubers

37 38 38

40

41

43

43

43 43 44 44 44

45

45 45 45

47

47

47

48 49 49 49 50 50 51

3.7. Analysis of data 53

3.7.1. Effects of intercropping on populations of SPW and on sweet potato production. 53

3.7.2. Insect diversity 54

RESULTS . . .. . . . . . . . . . . . 55

4.1. Effects of intercropping on the population of sweet potato weevil (SPW) and sweet potato y; el d . . . . . . . . . . . . . . iii • • • • •• 59

viii

1

V.

4.1.1. Colonization of the sweet potato by SPW in four croppi ng systems . . . . . . .. 59

4.2.

4.3.

4.1.2.

4.1.3.

4.1.4.

Population density of SPW and percentage of dùmaged tubers . . . . . . . . . . . Number and fresh weight of sweet potato tubers. . . . . . . . . . . . Marketable yield and economic value of sweet potato and intercropped plants

Number of insect and spider fa mi lie j, and number of individuals of each family associated with sweet potato agroecosystems ..... .

Aspidomorpha sp. (Coleoptera: Chrysomelidae) and Lycosa sp. (Araneae): two population of arthropod species, within the monoculture and intercropping systems

DISCUSSION

60

61

63

65

70

74

5.1. Effects of intercropping on the population densi ty of the sweet potato weevi 1 (SPW). 75

5.1.1. Effects of intercropping on number of SPW and on percentage of damaged tubers

5.1.2. Level of atte.ck by SPW in relation to tuber formation ........... .

75

77

5.2. Number of insect and spider families associated with sweet potato agroecosystems 80

VI. CONCLUSIONS AND RECOMMENDATIONS FOR FURTHER RESEARCH 85

LITERATURE CITED 89

APPENDICES

1.

2.

3.

Field layout of the experiment

Cost of production for monoculture and i ntercropped sweet potato ......... .

Insect and spider families associated with the sweet potato cropping systems at 35, 42, 49 and 56 DAP Il .. .. • .. .. • .. .. • .. .. .. .. .. .. .. .. .. .. ..

106

107

108

111

ix

Number

1.

2.

3.

4.

5.

6.

7.

8.

9.

10.

11.

12.

LIST OF TABLES

Page

Insect pests of sweet potato in Iri an Jaya .. 8

Alternative hosts of Cylas formicarius (F.) (Coleoptera: Curcul ionidae) . . . . . . .. 15

Life cycle of the :weet potato weevil, Cv1a) f 0 rm i (. '1 ri us (F.) ( Col e 0 pt a ra: Cu r cul ion i da e , on sweet pota to . . . . . . . . . . . . . .. 17

Effect of temperature on development of Cylas formicarius elegantulus (F.) (Coleoptera: Curculionidae) on sweet potato (cv. 'Jewel') 18

Percentage of cul t i vated land under i nter:rops in selected countries . . . . . . . . . . 29

Total amount of nitrogen, phosphorous and pota3sium (kg/ha) applied to sweet potato, corn, soybean, toma to and cabbage . . . . .. 46

Colonization of sweet potato by the sweet potato weevi l (SPW) at 56 DAP ..... 59

Number of sweet potato weevils (SPW) per kilogram of damaged tubers and percentage of damaged tubers . . . . . . . . . . . . . 60

Effects of intercropping sweet potato on number of tubers per plant and on fresh weight of tubers per 10 plants .......... 63

Marketable yield, economic values, cost of production and monetary index of sweet potato and intercropped plants in intercropped sweet potato wi th corn and soybedn . . . . .. 64

Insect and sRider families (fam.) and individuals (ind.) of each family collected a t 35 DAP . . . . . . . . . . . . . . . . .. 65

Insect and sRider families (fam.) and individuals (ino.) Jf each family collected a t 42 DAP . . . . . . . . . . . . . . . . .. 66

x

13.

14.

15.

T

Insect and spider families (fam.) and individuals (ind.) of each ramily collected a t 49 DAP . . . . . . . .. . .. ..

Insect and spider families (fam.) and individuals (ind.) of each ramily collected at 56 DAP . . . . . . . . . . . . . . . . .

Number of spotted tortoise beetles collected dt 56 DAP and spider collected at 35 DAP, 42 DAP, 49 DAP and 56 DAP, in four sweet potato croppi ng sys tems . ....... .

66

67

71

xi

-_ ...

1 .

Number

1.

2.

3.

4.

5 .

6.

7 .

8.

9.

10.

11.

12.

13.

LIST OF FIGURES

Sweet potato intercropped with corn in Kamu valley of the western highland region of Irian Jaya, Indonesia ............... .

Sweet potato grown intercropped with corn, bean, cabbage in Baliem Valley of the eastern highland region of Iri an Jaya, Indonesi a ....... .

Sweet potato grown intercropped with sugar cane, tometo and cabbage in Baliem valley of the eastern highland region of Irian ~aya, Indonesia

Sweet potato grown with taro in Baliem valley of the eastern highllnd r€gion of Irian Jaya, Indonesia .................. .

Adult sweet potato weevil, Cylas formicarius (F.) (Co 1 eoptera: Curcu l i oni dae) . . . . . . . . . .

Head and antennae of adult Cylas formicarius (F.) (Coleoptera: Curcul ionidae) ....

Monthly rainfall recorded at Manggoapi

Page

4

4

5

5

7

21

experimental farm during 1989, and the average of monthly rainfall in Manokwari recorded during a previ ous 40-yea r peri od (1939 to 1979) . . . . .. 42

Arrangement of pitfall traps in each experimental unit . .. ................ 52

Heavily damaged tomato and cabbage intercropped with sweet potato (treatment E) ..•.••.. 56

Sweet potato monocu l ture (treatment A) . . . . . 57

Sweet potato intercropped with corn (treatment B) 57

Sweet potato intercropped with soybean (treatment C) ........... .

Sweet potato intercropped with corn and soybean (0) . . . . . . . . . . . . . .

58

58

xii

14.

15.

16.

17

,

Relationship between number of sweet potato weev ils and damaged tubers ... . . . . .

Number of insect and spider families associated wi th sweet potato croppi ng systems .. . . . .

Number üf spotted tortoise beetle, Aspidomorp-ha sp. (Coleoptera: Cassididae) collected from sweet potato cropping systems at 35, 42, 49 and 56 DAP.

Number of the spiders, Lycosa sp. (Areneae: Lycosidae)., collected from four sweet potato croppi ng systems at 35, 42, 49 and 56 DAP . . . .

62

69

72

73

xiii

CHAPTER 1

INTRODUCTION

$weet potato, Ipomoea batatas (L.) Lam, a earbohydrate

prod uei ng root erop, ran king seventh i I~ wor l d prod lIet l on a fter

wheat, riee, maize, potato, barleJ' and ea;sava (FAO 19~O), 1S a

staple food in many parts of the tropies (Y~n 1974, Onwueme 1978,

Vill areal 1982, Bouwkamp 1985, FAO 1986, NWJnyi 1987). Worldwide,

it supplies 3.9 % of the ealorie intdke and 1.7 % of the protein

for h uman eonsumpt ion (FAO 1986). 1 n eerta in pa rts of the t ropi es ,

where this crop is the only staple food, sweet potato eontributes

approximately 80 % to 90 % of the calorie intake of the population.

This situation, for example, oeeurs in the central highlands of the

the island of New Guinea, which ineludes Papua New Guinea (Bourke

1985, FAO 1986, Hadfield 1989) and the Irian Jaya province of

Indonesia (Oomen et QI. 1961, Ruin~rd 1969, Oomen 1971, Manwan &

Dimyati 1989, Karafir 1989). It is also the staple food in several

South Pacifie Islands, including the Solomon Islands and Tonga

(Onwueme 1978, Bradbury & Holloway 1988, Horton & Ewell 1991), in

the Visayas region of the Philippines (Villareal 1982, Palomar ~J

li. 1989, MaeKay 1989). in sorne A fri can countri es, i ne l ud i ng Rwanda

(Janssens 1982, Alvarez 1987, Horton & Ewell 1991), the Cameroons

(Pfeiffer 1982), Burundi and parts of Uganda (Alverez 1987), and i~

parts of the Carribean (Horton & Ewell 1991), especially during

drought periods (Bouwkamp 1985).

In addition to human food, sweet potato plays a significant

role as animal feed, and as the raw material of industrial starch

and alcohol production (Edmond & Ammerman 1971, Yen 1974, Hahn

1977, FAO 1986, Jansson & Raman 1991).

:2

,\ .. In Irlan Jaya, the indigenous people have cultivated sweet

potato since the crop was first introduced to the island of New

Gui nea in the 14'" century (Yen 1974). Since then, sweet potato has

become an important s tap le food of the i nd i genous people, and of a t

least one livestock species (the pig) in the central highland

region of the island (Rappaport 1984, Halfield 1989). Thus, based

on its role and importance as human food and animal feed, sweet

potato remains central to the agricultural system in Iri an Jaya

(Karaf, r 1989).

Today it is planted extensively, both in lowland and highland

regions, by various local tribes, each employing its own cropping

sys tem. In the 1 owl ands the crop i s pl anted in a mi xtu re wi th

other crops such as corn, taro, tanni a, cassava, sugar cane,

cucumber, banana, and Hibiscus manihot, whereas in areas of cleared

virgin or secondary forest it is planted under a shifting

cultivation system (Karafir 1989). It is also commonly planted in

ga rdens adj dcent to hou ses and vi 11 ages. In the hi gh 1 ands, sweet

potato is planted in fields in the valleys and on hill sides,

either dS a monoculture, or mixed with corn, taro, beans, cabbage,

tOll1ato and sugar cane (Figs.1-4.)

Although sweet potato has been cultivated for many years, the

yield level is usual1y low: less than three tons per hectare in the

lowlands (Ruinard 1969), to three to six tons per hectare in the

highlands (Pospisil 1963). Recent data (Karafir 1989), however,

indicate that sweet potato production in Irian Jaya has increased

to an average of seven tons per hectare.

3

1

l

Fig. 1. Sweet potato intercropped with corn in Kamu vdlley of the western highland region of Irian Jaya, Indonesia.

Fig. 2. Sweet potato grown intercropped with corn, bean, cabbage in Baliem valley of the eastern highland reglon of Irian Jaya, Indonesia.

--,

4

(.

(

f 1~. 3. Sweet patata grawn intercropped with sugar cane, tomdto and cabbage in Baliem valley of the eastern highland r(>~lion of Irian Jaya, Indanesia.

f Iq. 4. Sweet potata growth with taro in Baliem valley of thr eastern highland regian of Irian Jaya, Indonesia.

5

l

T

This level of production is still only 50 % of average world yield

data, which is 14 t/ha (Horton 1988, 1989). As a consequence,

production of sweet potato in Irian Jaya is sometimes insufficlent

to meet the needs of both humans and livestock. For example, the

consumption of sweet potato in the eastern hlghland reglon of Irian

Jaya in 198~ (359 tons) exceeded th~ production of sweet potato

(230 tons) by 56 %. Su ch production shortfalls (Karafir 1989) have

sometimes been followed by local famine (Oomen ~1 Çil. 1961).

Severa l factors l imi t product i on of sweet potata ln 1 rl an

Jaya. These include low sail fertility, a long dry season, the use

of low yip~ding varieties, poor management of cultivation

techniques, and little or no attempts at pest control.

Among the 16 main insect pests of sweet potato in Irian Jaya

(Table 1; Simon Thomas 1962), the sweet potato weevi l (SPW~, CylÇl~

formicarius (F.) (Figure 5), is the most Economically lmportant

pest (Szent-Ivany 1958, van Driest & Ruinard 1960, Lamb 1974). It

damages the sweet potato vi ne and tuber, and occas i ona lly the

foliage, thereby reducing both the yield and quality of the crop

(Sutherl and 1986a).

6

1

~ lq 5. f\dlllt sweet potato weevil, Cy7as formicarius (F.) (Coleoptera: Cllηlllllonidae). (Dr. G.V.H. Jackson, South Pacifie Commision, Noumea).

7

l

r 1 .

Table 1. Insect pests of sweet potato in Irian Jaya

Classification

Col eoptera Curcul iOllidae

Coccinellidae Chrysomelidae

Lepidoptera: Nympha1idae

Sphlngidae

Insect species

Cylas formicarius (F.) Oribius improvidus Mshl. Epilachna si9natipennis Boisd. Meroleptus Clnctor Mshl. Aspidomor~ adhaeren~ Weber A. austr31asiae Boisd. A. punctul11 F. Cassida diomma Boisd. ~ holmgreni multicolor Blackb. ~ papuana Speath ~ strigula F, Laccoptera impressa Blanch

Appias melania F. Precis orjthya F. P. villida Bod. Herse convolvu1i L.

Pa rt a t tacked 1

S, l , T L L S L L L L L L L L

L L L L

Source: Simon Thomas 1962. 1) S = stem; L = leaf; T = tuber

The fo 11 owi ng cont ro l methods have beeil proposed to reduce

y; el d los s cau s e d b yin sec t s : r es i st a n t cul t i var s ( M li 11 en et i!J '-

1985, AVRDC 1987,1988), cultural techniques such as crop rotation

(Re~nhard 1923, Gonzalez 1925, Cockerham et .9.l... 1954, Sherman &

Tamashiro 1954, Kalshoven 1981, AVRDC 1986, 198ï, 1988), removal of

volunteer plants and crop debris from harvested fields (Reinhard

1923, Gonza les 1925, Cockerham et .9.l... 1954), prompt ha rves t i ng

(Sherman & Tamashiro, 1954, Sutherland 1986"), removal of

alternative wild hosts (Cockerham ~t .9.l... 1954, Talekar 1983, AVRDC

1988), planting away from weevil-infected fields (Sherman & Tamashiro 1954, AVRnC 1988), intercropping (Singh et Ql... 1984,

AVRDC 1987), and maintaining soil to avoid cracking through banking

8

and irrigation (Pardales & Cerna 1987, Talekar 1987). Chemical

control wlth insecticides (Sherman & Tamashiro 1954, Wolfenbarger

& Walker 1974, Muruvanda 1985, Schalk & Jones 1985, AVRDC 1987),

and a synthetic sex pheromone (Proshold et ~ 1986) have also been

proposed. Often these methods are combined in an integrated pest

management strategy (Talekar 1988, 1991). Recent developments

include the use of natural control agents such as predators,

pa ras ito i ds, entomopathogen i c fungi, bacteri a, and nematodes

(Jansson 1991"). Among these agents, two entomopathogenic

nematodes, Heterorhabdit i s bacteri ophora strai n 1 HP88", and

Steinernema carpocapsae strain "All", are promising as biological

control agents of SPW (Jansson 1991b).

Based on the agricultural system in Irian Jaya, the farmers'

< ability, availability of control agents and economic limitations,

control of the SPW by cultural techniques is considered to be the

most appropri ate approach, and the one most 1 i kely to be adopted at

the present time.

Application of these control measures, however, should not be

applied directly without taking into account the traditional

agri cul tural systems employed by the farmers (Jansson & Raman

1991). Modlfication of certain cultural techniques would be useful

and appropriate as such modifications would not dramatical ly change

the farlllers' production system. Moreover, the modification of

production techniques does not usually require additional inputs or

fu rther k nowl edge of cu lt i vat ion techn i ques, al though i t may

9

1

y

requi re a better unders tandi ng of the i nsect and the factors

responsible for its pest status (Jansson & Raman 1991).

1 ntercroppi ng sweet potato with one or more crops i 5 one of

the cultural techniques that is already widely practiced in Irian

Jaya (Karafi r 1989). Genera 11 y, th i s pract i ce i ncreases crop

diversity, which provides both barriers to pest dispersal and more

habitats for natural enemies, thereby reducing both colonization of

the crop by pes ts and the; r subsequent cont ro 1 (l i ts i nge r & Moody

1976, Perrin 1977, Hare 1983, Andow 1983, Al tieri & Liebman 1986,

Altieri 1987, Risch 1987).

The si gn i fi cance of i ntercroppi ng in the contro 1 of SPW,

however, is poorly understood (O'Haïr 1991). Preliminary data that

are available from India (Singh et. li. 1984) and Taiwan (AVRDC

1987) indicate that intercropping a10ne is insufficient for

control l ing SPW, and that the level of control varies \'Iith the

i ntercrop spec i (lS th at i s used. For examp 1 e, i ntercropp i ng swee t

potato wi th proso-mi 11 et and ses ame in 1 ndi a reduced i nfes tat ion by

SPW to 9 % and 6 %, respectively, compared with 28 cy" in sweet

potato monoculture (Singh et li. 1984). Similarly, in Taiwan,

i ntercroppi ng sweet potato wi th ch i ckpea, cori ander, pumpk in,

radish, fennel, blackgram or yardlong bean also significantly

reduced the 1 eve 1 of i nfes tat ion (AVRDC 1987). When sweet pota to

was i ntercropped wi th a number of other crops, such as green gram

(Singh et li. 1984, AVRDC 1987), cabbage, peanut, and corn (AVRDC

1987), reduct ion in i nfes ta t ion by the SPW to 12 % from 20 % was

st i 11 cons i dered to be unacceptab 1 e. The ex tent to wh i cil

10

i ntercroppi ng can reduce i nfes tati on of the sweet potato by SPW and

other i nsect pes ts in 1 ri an Jaya was unknown pri or to the present

resea rch.

ln an attempt to obtain an appropiate method for controlling

SPW among t T'ad; t i ona l sweet potato farmers ; n 1 r; an Jaya, th; s

resea rch program was des i gned to determi ne (1), the effect; veness

of in tercroppi ng of sweet potato wi th corn, soybean, tomato and

cabbage in reduc i ng crop damage, (2), the popu lat; on dens i ty of

SPW a t ha rvest, and (3), the d; vers; ty of i nsects and other

arthropods in sweet potato agroecosystems.

Becaus eth; s resea rch was des; gned to be support ive of sma 11

sca le sweet pota to farmers, the ; ntercropp; ng sys tems tested were

chosen in relation to the farmers' traditional practices.

11

. A

T

CHAPT ER II

LITERATURE REVIEW

2.1.

2.1.1.

BIOECOLOGY OF THE SWEET POTATO WEEVIL r Cylas formicarius (F.) COLEOPTERA: CURCULIONIDAE)

Taxonomie status and distribution

Latreille in 1802 was the first entomologist to use the genus

WA~_ (Neave 1939) for deseribing weevils of the Cyladinae that

have the following characteristies: (a) slender, elongate bOdy with

a eylindrical beak, (b) posterior femora not as a rule exceeding

the tip of the elytra, and (3) the elytra not inflated (Pierce

1940, Subramani an 1957).

The genus Cyl as contai ns 27 spec i es (Scha 1 k & Jones 1985,

Austin et gl. 1991). Of these, h formicarius (Fabricius), h

tureipennis Boheman,_~ brunneus (Fabricius), ~ femoralis Faust,

and ~ puncticollis Boheman, are associated exclusively with sweet

potato (Pierce 1918, 1940, Austin et li. 1991).

A recent taxonomie and distributional study, however,

indicated that there may be as many as nine species of Cylas that

are potential pests of sweet potato. These nine species are

classified into three monophyletic species groups: ~ formicarius,

~ brunneus, Ç..... punctieollis (Wolfe 1988, 1991). Of the above

three main speeies groups, Cylas formiearius and ~ punctieolis are

the most widely distributed. h formicarius oecurs in Africa, the

Americas ~nd Asia, whereas ~ puncticollis occurs only in certain

African countries (Cor.:monwealth Institute of Entomology 1970, <;ingh

1977). ~2 brunneus may have a similar status and distribution

in West Africa as ~ puncticollis (Hahn et li. 1989).

13

Cylas formicarius was first described by Fabricius (1798) as

Brentus formicarius. This was based on specimens from India that

had a piceous-brown body, with a reddish thorax (Pierce 1918). His

description of this species is as follows:

"Habitat Tranquebariae. Parvus in hoc genere. Rostrum cylindricum, atrum antennis rufis, moniliformibus: articulo ultimo longiori, cylindrico, clavato. Thorax rufus, antice globosus. Elytra laevia, atra, nitida. Pedes rufi, femoribus cl a vat i s, a tin e rm i bus: a r. nul 0 n i gr 0" ( Pie r ce 19 18 )

This species seemed not to be the same as the common sweet

potato weevil found in the USA that has shiny blue-black elytra,

red thorax and appendages, and a black head and beak. For that

reason, Summers (1875) named the American species ~ elegantulus to

distinguish it from the Asian species (Pierce 1918).

The name was not, however, applied, partly out of respect to

Fabricius (Pierce 1918). But, based on the color of the elytra

(greenish for the Asian species and bluish for the American

species, Pierce 1918), and karyological differences in the sex

determi ni ng system (Hung 1985), two sub-speci es of Ç-Yl~s.

formicarius have now been recognized:

formicarius (F.), which is widespread throughout the Asian tropics,

and Cylas formicarius elegantulus (Summers), which occurs in

t ropi ca land s ub-trop i ca 1 reg i ons of the Ameri cas (Suther land

1986a , Talekar 1988). In subsequent chapters, unless otherwise

indicated, the use of .c. formicarius refers to .c. formiçariJ!.s.

formicarius, the Asian sub-species.

14

(

2.1.2. Host range

The prefered host for ç. formi cari us i s the sweet potato,

l~oJl!oeQ 12a ta tas (Cockerham 1943, Sherman & Tamas h i ro 1954, Hi 11

1983, Talekar 1989, Austin et M. 1991), although this insect also

a ttacks other Ipomoea and related species (Table 2).

Ta b l e 2. A 1t e r n a t ive ho s t s 0 f Cyl as f 0 rm i car jus ( F . ) (Coleoptera: Curculionidae)

Alternative host

Calonyction aculeata Çlll.Y~:teill sol dane 11 a IRom9.~Q batatas J. ararica T. IjarreTri oi des t. ço.nge~tQ 1. di ssecta r. heder-a-cea t. h'~iif~phyrLQ I. lacunosa f. lateraTT s 1. rëari,-T. rlTtoralis 1. rnacrorliTZa r. muri cata 1. palmata L Qalldura_ta 1. Qres-caprae J. Qurpuria 1. guam~cl i t 1. sa_9ittatQ t . ~~pj_QLiA 1. s.etosil

J. :trj.ç_~oca rpa I. trilobia 1. fTlpTda IJ2orn-oe,i ~. J_ÇlQ.uemontia tamnifolia ThJJllbe"'iLi a ~.

Source: Sutherland 1986d•

Common name

Moon-fl ower Bi ndweed Sweet potato

Blue morning glory A l arno-v; ne Engl i sh Ivy Bush morning 910ry Diminute mornlng glory

Blue dawn-flower

Man-of-the-earth Beach morning-glory Common morning-glory Cypress vi ne

Brazi1ian morning­glory

Clock vi ne

Country

Indi a Taiwan Worl dwi de Indi a Indi a Papua New Guinea U.S.A. U.S.A. U.S.A. U.S.A. India. India. U.S.A. U.S.A. U.S.A. Indi a U. S. A Indi a Indi a U. S.A U.S.A. Indi a

U.S.A. U.S.A/lndia Philipp.!India Indi a U. S.A/Taiwan Indi a Indi a

15

r

2. 1. 3 • li f e eye le

Research on the l i fe cyc le of SPW has been rev i ewed by

Sutherland (1986a; Table 3). Apparently it varies from one

location to another, probably mainly in relation to changes in

temperature (Mull en 1981, Sutherl and 1986a). At low temperatures,

fecundity ;s higher and the life cycle is longer (Table 4; Mullen

1981). Thus, these properties vary with the season (Gonzales 1925,

Rajamma 1983).

The optimum temperature for development is 27°C to 30 llC, wh en

the life cycle is completed in ca. 33 d. At 27°C and 60 % RH the

adul t weevi l lives for 94 d (Mu 11 en 1981).

a. Egg

! The adult female lays cream colored eggs (0.75 x 0.40 mm),

T

singly in a cavity in vines or tubers (Reinhard 1923, Sutherland

1986a) • After l ayi ng each egg, she sea l s the ca v ity wi th a grey

fecal plug. This conserves moisture, protects the eggs from

predacious mites, and "hides" the location of the oviposition site

( S h e rm a n & T am a 5 h i r 0 1954).

Recorded oviposition rates differ from one geographic area to

another in re lat ion to the temperatu re of the regi on. For examp le,

in India, Rajamma (1983) found that females lay 1 to 9 eggs per

day, wi th an average of 3 to 5 eggs. In the USA, however, r~ei nhard

( 1923) repo rted an ovi pos i t i on rate of up to 2 eggs per day.

16

Table 3. Life cycle of the sweet potato weevil, Cylas formicarius (F.) Coleoptera: Curculionidae), on sweet potato

Stage

Temperature (OC)

Egg (d)

Larva (d)

No. of instars

Pre-pupa (d)

Pupa (d)

Pre-oviposition (d)

Oviposition (d)

No. of eggs

Longev. female (d)

Longev. male (d)

Egg to egg (d)

Reinhard Sherman & Kemner

(1923) USN

28

5-11

20

1-3

15

6-9

104

56

53

Tamashiro (1954 )

Hawai il

27

8

15

3

4

8

32

(l924 ) Indone-si aZ

5-9

25-26

6-7

7-9

43-51

Gonzales

(1925) Philippi­nes2

6-9

4-6

63-120

256

26-52

Trehan & Subramanian Bagal (1957) (1959) Jndi a Indi a2

6

17

7

83

83

31

6

24

5

1-2

10

7

80

148

94

110

47

Source: Sutherland 1986". l) Cylas formicarius eleçantulus (Summers) Z) Cyl as formi cari us formi cari us (F.) - = data unavailable

Jayaranaiah Rajamma

(1975) (1983) India2 India2

9

28

5

7

90

166

46

6

16

4

8

83

30-36

17

l

T À

Stage

Egg

Larva

Pupa

Tabl e 4. Effect of temperature on development of Cylas formjcorius e7egafitulus (Summers) (Coleoptera: Curculianidae) on sweet potato (cv.'Jewel')

Average durat i on (d) of deve l opment stages of the SPW at di Herent temperatures

7.9 5.7 4.8 4.0

58.2 23.7 16.3 16.2

10.7 5.0 5.5 8.6

Pre-ovipos i ti on 7.7 6.5 6.3 4.5

Egg ta egg 84.5 40.9 32.9 33.3

Source: Mullen 1981.

The egg stage 1 asts 4 to 8 d (Sutherl and 1986"). Over the 60 to

120-day ovi pos; t i on peri od, the total number of eggs 1 ai d ranges

from 50 to over 250.

b. larva

The newl y hatched 1 a rva has a de 1 i ca te appea rance and i s

initially white in color (Reinhard 1923, Gonzales 1925, Cockerhan

et QI. 1954, Trehan & Bagal 1957). As it matures its body darkens

(Reinhard 1923, Cockerhan et QI. 1954) and becomes slightly curved

(Trehan & Baga l 1957, Sutherl and 1986a).

Its body si ze i ncreases through the four 1 arva 1 i ns tars from

< 1 mm a t h a t chi n 9 t 0 u p t 0 8 . 5 mm dur i n g the fin a 1 i n s t a r

(Re; nha rd 1923, Cockerhan et QI. 1954, Trehan & Baga 1 1957).

18

c. Pupa

The flnal larval stage excavates a pupal cavity , measuring

two or three times the size of its body, inside the tuber (Reinhard

1923, Cockerhan et .li. 1954, Sherman & Tamashiro 1954, Sutherland

1986") . 1 t then 5 tops feed i ng and becomes qu i escen t for one or

more days before pupating (Cockerhan et QI. 1954).

The first external indication of pupation is the splitting of

the head capsul e of the prepupa between the rudimentary antennae

and the skin of the dorsal thoracic region (Reinhard 1923,

Cockerhan et QI. 1954).

The pupa usually remains motionless, but if disturbed it makes

a circular twisting movement of the abdomen, and sometimes turns

over (Reinhard 1923, Cockerhan et QI. 1954).

At first the pupa is white (Reinhard 1923, Trehan & Bagal

1957), and later it becomes yellowish. It gradually darkens, pr;or

to transformation to the adult (Reinhard 1923).

lhe pupa is ca. 5 mm long by 1.5 mm wide (Reinhard 1923,

Sutherland 1986d). The length of the pupal period varies with

temperature, from 5 to Il d (Table 4; Mullen 1981).

d. Adult

At the end of the pupal stage, the pupal skin splits down the

back begi nni ng near the head. The new adul t pull s i ts head and

th en its legs out of the old skin. As soon as the legs become hard

they are used to push the skin off the rear of the body.

19

t j ~

The partially exposed hind wings are wrinkled at first, but,

after a short period of time, body fluids flow into them, expanding

them to their full length beyond the elytra, in which position they

rema in unt i l ha rdened. The wi ngs are then fo 1 ded in the norma 1

position under the elytra.

The newl y t rans formed adu 1 t i s al mos t wh He and ra ther

helpless. A min'imum of 4 d is required before it is able to eut a

passageway to the surface of the potato and emerge.

The adult weevil (Asian subspecies) is black ln color with ~

reddi sh brown prothorax (Gonzales 1925, Trehan & Bagal 1957,

Rajamma 1983, Sutherland 1986a). The elytra and head are black and

the 1 egs are redd i sh-brown and b lac k (Ka l s hoven 1981, Sutherland

1986a) •

T Body size and antennal structure differ in males and females. l

,. 1 1

The adult female is usually smaller than the male ( 5.8 x 1.5 mm

compared with 6.1 x 1.6 mm, for the male; Rajamma 1983). Body

size, however, is not a reliable criterion for sex determination,

since it varies significantly in nature (Gonzales 1925, Trehan &

Bagal 1957).

The sexes can be separated reliably on the basis of

di fferences in the si ze and shape of the lOlh anten n a 1 segment

(Fig. 6).

20

1

(a) ( b.)

Fi gu re 6. Head and an tenna of 'âdu 1 t ~las formi ca ri us (F.) (Coleoptera: Curculionidae). (a) femaTeand (b) male. Sou rce: Su therl and 1986".

f

21

, •

.,

2.1.4. Feeding habits and crop damage

Adult weevils feed on the exposed parts of the sweet potato

plant, including the foliage, vine, stem, and tuber (Reinhard 1923,

Gonzales 1925, Cockerham et Ql. 1954, Trehan & Bagal 1957,

Kalshoven 1981, Rajamma 1983, Sutherland 1986"), although the tuber

i s the preferred food source (Rei n hard 1923, Gonza les 1925,

Cockerham et QI. 1954).

The adult weevil feeds on the tuber surface, parti~ularly if

it is shaded (Reinhard 1923). On tubers, the damage appears as

patches of shallow feeding punctures (Reinhard 1923). Females also

deposit eggs, which are usually covered with frass, on the tubers.

On the vine, the adult weevil feeds by gnawing rather than by

making distinct punctures; on the stems, petioles and leaf veins

the feeding scars often run together or overlap (Cockerham ~1 SLl.

1954).

The larvae feed inside the tubers and underground inside the

lower portions of the stems by tunnelling into them (Trehan & Bagal

1957, Cockerham et. gl. 1954, Rajamma 1983). The tunnels inside the

tubers follow a zig-zag pattern (Reinhard 1923, Rajamma 1983).

The tunnels are usually closed with excreta or remains of food

materials (Rajamma 1983); feeding rarely occurs in open tunnels.

The level of damage that results depends on the parts of the

plant that are attacked. Damage to above ground stems, vines and

foliage is usually not significant, in contrast to underground

damage, especially to the tuber, which can be devastating. The

greenish black color and bitter taste of infested tubers containing

22

terpenoids (Akazawa et ~ 1960, Uritani et g~ 1975, Sato et ~

1977) make them unfit for human and animal consumption (Rajamma

1983, Raman 1989).

In addition to attacking tubers in the field, losses of sweet

potatoes in storage to the SPW are also significant (Rajamma 1983,

Raman 1989).

The level of damage both in the field and in storage ranges

from 5 % to 90 % (Sutherland 1986a, Raman 1989). Loss of production

was found to be 10 % to 20 % in Hawaii (Sherman & Tamashiro 1954),

60 % in Papua New Guinea (Szent-Ivany 1958), 60 % to 70 % in

Malaysia (Ho 1970), 16% to 80 % in India (Rajamma 1983), 12 % to

90 % in Africa (Alverez 1987) and 5 % to 20 % in China (Lu et gl.

1989). Therefore, 10s5 of yield caused by the SPW can be one of

the ma in l imi ts on product i on (Raman 1989, Horton & Ewell 1991).

2.1.5. Reproduction

Sexual attraction in SPW has been claimed to be poorly

deve l oped, si nce in the l aboratory ma 1 es were found to show no

response to the presence of females (Reinhard 1923). Recent

s tud i es, hO\'Iever, have shown tha t the ma l es are a t t racted to sex

pheromones released by the females (Nottingham et gl. 1986). These

pheromones are released only when the females have found and fed

upon an appropriate hosto

Copulation takes place after both sexes have fed on a tuber;

it occurs several times (Reinhard 1923). During copulation, the

weevils remain relatively motionless. If disturbed, however, the

23

female immediately begins to crawl, either carrying the male with

her or separating (Reinhard 1923).

At first the eggs are laid inside the vines, and then, when

the tubers develop, inside them (Reinhard 1923). The female can

l ay eggs in a 11 parts of the tuber, in especi a 11 y prepared

cavities. The egg cavities are usually wider, but shallower than

the feeding punctures, and are oriented obliquely.

After digging out the cavity, the female turns around and

inserts the tip of the abdomen, which moves from side to side.

Eventually the ovipositor is protruded into the cavity and an egg

is laid (Reinhard 1923). Adults mate within 3 to 5 d of emerging

(Subramanian 1959) and after feeding (Reinhard 1923).

2.1.6. Factors affecting infestation by SPW

Infestation of sweet potato crops by SPW is affected direct1y

and i ndi rect l y by the age of plants, type of soi l , season,

especialy rain fall, elevation, source of the weevi 1s, and the

cultural techniques being used.

The age of plants influences the level of infestation by SPW

(Q'Hair 1991). This reaches a peak at the same time as storage

root formation and development, which starts as early as 28 DAP and

reachs its peak between 56 and 84 DAP (Wilson & Lowe 1973, Wilson,

1982).

Soils with a higher clay content tend to shrink when dry and

form cracks through which weevils can enter and reach underground

tubers (Hahn & Leuschner 1982, Eusebio 1983, Q'Hare 1991). When

24

thlS occurs, high infestations are common, as has been documented

in Papua New Guinee (Bourke 1985). Soil pH also affects the level

of SPW infestation, high weevil infestation being associated with

high soil acidity (pH 4.6 to 5.5), and low infestation with low

soil acidity (pH 8.6 to 9.5; Abella 1982). Thus, applying lime to

adJust soil pH to approximately neutral is often suggested as part

of a weevil control program.

Infestation by SPW is claimed to be low at high altitudes,

since the lower temperatures slow the developmental rate of SPW

(Eusebio 1983); however, the situation may be reversed if there is

a long dry season. Consequent 1 y, h; gh damage to tubers us ua 11 y

occurs in highland regions during longer th an usual dry seasons.

For examp le, the dry season of 1954 in Bena-Bena, Goroka, and

Chimbu subdistricts of the eastern highland region of Papua New

Guinea, coincided with devastation of the sweet potato crop, and

resulted in food shortages (Zsent-Ivany 1958, Anas 1960).

Infestation may also be a symptom of poor farm practices, such

as a 11 owi ng the s pread of the SPW from a prey i ous crop, from

adjacent alternative hosts, or from infected planting materials.

It is also affected by poor land preparation, failure to hill-up

the plants, and by late harvesting (Franssen 1934, Kalshoven 1981,

O'Hare 1991).

25

1

1

2.2. ROLE OF INTERCROPPING IN FOOD PRODUCTION

2.2.1. Definitions

Intercropping is a form of multiple cropping in which two or

more crops are planted simu1taneous1y in the same field (Andrews & Kassam 1976). Thus, cropping is intensified in both time and

space, as is inter-specific competition (Andrew & Kassam 1976, Roy

& Braun 1983, Gomez & Gomez 1983, Francis 1986). Consequently,

ach i ev i ng success requ ires a hi gher l eve l of management ski 11 s than

in a monocropping system.

Intercropping may be classified into mixed intercropping (no

distinct rows), row intercropping (single rows), strip

intercropping (several rows) and relay intercropping (overlapping

in time) (Andrews & Kassam 1976, Roy & Braun 1983, Gomez & Gomez

1983, Francis 1986).

Intercropping is commonly practiced by subsistence farmers in

tropical developing countries, at all levels of agricultural

technology (Andrews & Kassam 1976, Gomez & Gomez 1983)

Traditionally, two or more crops are grown on the same field,

primarily to achieve optimal use of space, diversify the range of

products, and reduce risk in the face of a crop failure (Gomez &

Gomez 1983).

Today, with the increasing 1055 of agricu1tural land and soi1

degradation, intercropping is being recognized as a way to enhance

efficiency and conserve soi1 (Gomez & Gomez 1983).

26

~~--J

2.2.2. Status

1 ntercropp i ng has long been recogn i zed as a way in whi ch

fa rmers in the t ropi cs and s ubt ropi cs, wi th li mi ted land resources,

can more effciently and economically produce food and cash crops

(Beets 1982, Kass 1978, Willey 1979, Roy & Braun 1982). It now

plays a significant role in the production of staple crops in

Africa (Okigbo & Greenland 1976, Steiner 1982), Latin America, and

Asia (Harwood & Price 1976, Gomez & Gomez 1983).

The significance of intercropping in developing countries is

appa rent from the large a rea of land that i s devoted to thi s

cropping system. In Africa, for example, almost 80 % of cultivated

land is intercropped (Steiner 1984), and this is probably also the

case for much of Latin America and Asia, where most staple crops

ft are produced in intercropping systems.

The type of i ntercroppi ng and s peci es used vari es wi th

geography and culture. For example, 98 % of cowpeas in Africa, and

more than 60 % of maize and beans in Latin America, are grown in

crop mixtures (Francis et M. 1976); whereas in Asia, especially

India, 5 to 6 % of rice, and 70 to 80 % of other crops, are grown

as mi x tures (Kas s 1978) . The commones t i ntercropped plants in

Asia include upland rice, sorghum, millet, maize, rainfed wheat,

and soybean.

Even though intercropping is prevalent in tropical areas where

farm5 are 5mall and farmers lack capital (Roy & Braun 1982, Liebman

1987), sorne farmers in temperate regions who have large farms and

.1df'quate capital are starting to practice intercropping, for a

27

, ,

1

l

range of reasons. Such farmers may be using intercropping to solve

problems of soil depletion and contamination (Poincelot 1986),

which are often associated with long periods of monoculture

agriculture.

Monocul ture agri cul ture i s characteri zed by a heavy dependence

on petrochemi ca l energy for opera t i ng fa rm mach i nery, and on

synthetic fertilizers and pesticides (Hill & Ramsay 1977).

Extens ive use of energy has i ncreased food product ion (Horwi th

1985, Power & Follett 1987), but it has also resulted in changes in

farrning rnethods (Horwith 1985, Power & Follett 1987, Altieri 1987,

Poincelot 1986), and a decrease in energy efficiency (Hill &

Rams ay, 1977).

Monocult~re tends to degrade the environment by accelerating

soil erosion, increasing the potential for depleting or degrading

ground water resources, reducing the quality of surface ~ater, and

using up fossil energy resources (Power & Follett 1987). It also

causes hea 1 th hazards and pest prob 1 ems as a resul t of the wi de use

of pesticides and fertilizers (Poincelot 1986), and supplementary

fertilization may be unable to compensate for the drop in yield

(Power & Follett 1987).

As 3. resu 1 t of energy rel ated prob lems, i ne l ud i ng i ncreased

costs, environrnental damage and health hazards, sorne farrners in

developed countries have become rnotivated to practice

i ntercroppi ng.

Estimation of the percentage of crops that are planted ~~

intercrops in various countries are given in Table 5.

28

Table 5. Percent age of cultivated land under intercrops in selected countries

Country

Dominican Rep. El Salvador Jamalca Mexico Braz il

Paraguay

Venezue la

Col umbi a Guatema 1 a Bhutan 1 ndones i a

Pakistan

Cenl.African Rep.

Senegal

Nigeria

Uganda

Malawi

Main crop

Maize Maize Maize Maize Rice Maize Bean Beans Sweet potato Maize Rice Maize Bean Cassava Cotton Bean Bean Potato Maize Rice Wheat Barley Cotton Cotton Coffee Cassava Groudnuts Mi 11 et Cowpeas Groundnut Melon Mi llet Cocoyam Cotton Ma ize Maize Bean Pi geon peas Coffee Cowpeas Goundnut Ma l awi

% Intercropped

> 40%

50 % 20 % 6 %

11% 80 % 33 % 10 % 10 % 16 % 33 % 20 % 20 % 50 % 90 % 73 % 40 %

25 % 33 % 20 % 25 % 25 % 99 % 95 % 93 % 90 % 86 % 80 % 76 % 84 % 81 % 76 % 63 % 62 % 56 % 90 %

Intercropl

b,s, * b, s, ')t'

* * * * * * * * * * * * * * *

m,b * * * * * -t

* * * * * * * * * * * * * * * * m

21) b = bean; s= sorghum; m= maize; * other crops

) 1 = FAO, 1973; 2. Francis, 1986; 3. Okigbo & Greenland, 1976; 4. Francis et al., 1976; 5. Os;ru, 1982; 6. Edje, 1982; 7. Roder et al. 1992; 8. Coaker 1990.

References2

1 1 1 1 1 1 4 1 1 1 1 1 1 1 1

4,8 4 7 1 1 1 1 1 1 1 1 1 1 2 2 2 2 2 2 2 3

3,5 3 3 3 3

6,8

29

2.2.3. Advantanges and disadvantanges

The advantanges of intercropping that are likely to appedl to

subsistence farmers include: the possibility of obtaining a higher

yield, reduced risk of total crop failure, enhanced resource use,

reduced fertilizer and pesticide requirement, absorption of excess

farm labor, and improved nutrition (Gliessman 1985, Vandermeer

1990).

The posibility of achieving a greater yield from the limited

area available is often the main reason why more and more farmers

are choosing to ir1tercrop (Kass 1978, Liebman 1987, Gliessman

1985). Total yield per area is usually greater in intercropped

systems, even though the individual species invariably yield more

in monocultures (Trenbath 1974, Hardwood & Price 1976, Willey 1979,

f Gliessman 1985). The greater total yield in intercropping OCCt!rs

if the relative yield total (RYT), which is the sum of the

intercropped yield divided by yields of monoculture crops, is

greater than 1.0 (Gliessman, 1985).

T 1

Not a 11 the i ntercroppi ng sys tems, however, ach i eve RYT' s

greater than 1.0. Trenbath (1986), for example found that among

572 comparisons of crop mixtures, only 66 % had RYT's close to 1.0,

i n d i ca tin 9 no dis tin c t a d van t age t 0 the sem i x t ure sin te rm s 0 f

yield. On the other hand, 20 % of the mixtures had RYT's greater

th an 1.0, ranging up to 1.7, indicating a distinct advantage over

the monocultures. Only 14 % had RYT's less than 1.0, indicating

distinct disadvantages.

30

1 n add i t ion to yi el d advantages, i ntercroppi ng may reduce

economic loss because of the failure of a particular crop within

the system. Even wh en the RYT is close to 1 (e.g., shows no

i ne reased yi el d ove r the monocu l ture), the other benefi ts of

intercropplng, such as lower energy costs and less pest problems,

will serve to make intercropping competitive with the monoculture

system (Harwood & Price 1976, Willey 1979, Horwith 1985, Liebman

1987, Gliessman 1985).

Ava i l ab le li ght, wa ter and nut ri ent resou rces maya l so be used

more efficiently in intercropping systems (Liebman 1987). Thus,

because total densities are usually higher in such systems, more

light can be intercepted early in the growing season. This has

been demons t ra ted fo r mi xtu res of ma i ze and mungbean, peanut or

sweet potato (Liebman 1987). Moreover, because intercropped plants

have non-synchronous patterns of canopy development and different

matu rat ion t imes, the l eaf a rea produced over the growi ng season i s

greater and therefore abl e to i ntercept more li ght than are

monocultures (Liebman 1987).

One outcome of the i ncreased canopy cover i s that a greater

proportion of available soil water is channelled through the crops

as transpiration, rather than being lost as evaporation from the

soi 1 surf ace. Futhermore, i ncreased canopy coverage can al so

increase penetration of rainfall into the soil, and decrease soil

erosion by lessening the impact of rain and wind on the soil

surface. This has been documented, for example, with maize

intercropped with cassava (Lal 1986, 1989).

31

T ,

Intercropping of plants with different rooting patterns

permi ts greater exp loi tat i on of a l arger vo l ume of soi land

impro"es access to relatively immobile nutrients. As a result,

i ntercropped pl ants tend to absorb more nutrients th an those in

monocultures (Horwith 1985, Liebman 1987).

In addition, ir.tercropping with legumes may enhance nutrient

avai labi l ity for the non-legume crop, e.g., maize with soybean,

cowpea or mungbean. The l egumes may prov i de bath add i t i ona l

nitrogen through theirmutualistic association with nitragen-fixing

bacteri a such as Rh i zobi um (Ni co l 1935, Gomez & lands t ra 1977,

Horwi th 1985) , and phasphorous thraugh thei r mutua 1 i st i c

as soci at ion wi th ves i cu la r arbuscu 1 a r mycorrhi za l (VAM) fung i

(Hetrick 1984). The mutualistic associations, especial1y those

involving VAM, may also occur with non-legume intercrops

(Ch i ari e 11 0 et QI, 1982). Such rel at i onsh i p can reduce the need

for imported nutri ents, whether as manures or synthet i c

fertilizers.

Intercropping may increase or reduce pest populations.

Reduction mechanisms include the provision of physical barriers to

the pest's ability to find suitable hosts (Litsinger & Maody 1976,

Perrin 1977); the production of chemicals that disrupt the

searching behaviour of the pest and pravide associational

resistance (Perrin 1977); and the provision of shelter and

alternative food sources for predators and parasites (Litsinger & Moody 1976, Perrin 1977, Horwith 1985, Liebman 1987). By taking up

excess available nutrients, especially nitrogen, intercropping may

32

prevent the main crop from becoming more attractive to pests, such

as through the accumulation of free amine acids and sugars in the

plant tissue.

Intercropping can affect the deve10prnent of diseases,

nematodes and weeds (Litsinger & Moody 1976, Liebman 1987). Thus,

a susceptible crop planted between a resistant crop may be

protected from a di sease by the i ntercept i on of the i nocu l um

(Liebrnan 1987). Also, the microclimate provided by the intercrop

may be less or more favorable for disease development (Litsinger & Moody 1976, Li ebman 1987). Sorne crops are known to excrete

substances that are toxi c to nematodes, thereby 1 oweri ng the

incidence of infection in susceptible hosts (Liebman 1987).

The more complete canopy and plant cover associ ated wi th

intercropping is a1so an effective way to control weeds (Litsinger

& Moody 1976, Li ebman 1987). 1 fi these ways, i ntercroppi ng can

reduce the need for pesticides in crop production, and so reduce

production costs.

Because intercropping requires more labor and management than

monoculture (Andow 1983, Gomez & Gomez 1983, Liebman 1987), it can

dbsorb exces s fa rm l abor (Gomez & Gomez 1983). Consequent 1 y,

intercropping is like1y to be most profitable in labor intensive

production systems (Andow 1983, Hare 1986; Liebrnan 1987).

There are, however, sorne di sadvantanges. These i nc 1 ude yi el d

reduct i on of the Ina in crop, loss of product i vi ty duri ng drought

periods, and high labor inputs in regions where labour is scarce

and expensive (G1iessman 1985).

33

T

j

l

T

It is we11 documented that in most cases the main crop in an

i ntercroppi ng system wi 11 not reach as hi gh a yi el d as in il

monoeu1 ture, beeause there i s compet i t ion among i ntercropped

plants for light, soil nutrients and water (Willey 1979, Fordham

1983, Gliessman 1985). This yield reduction may be economieally

significant if the main crop has a higher market priee than the

other intereropped plants.

Another disadvantange that is like1y to oeeur is the higher

cost of maintainance, in partieular, weeding, which may have to be

done by hand. Th i sis not a seri ous prob lem in count ri es where

excess farm labor ;s cheap, but for eountr;es laeking such a labour

force, intereropping will result in inereased costs. Furthermore,

harvesting of one crop may cause daw.age to the others (Gliessman

1985). Finally, the increased canopy cover may result in a

microelimate with a higher relative humidity conducive to disease

outbreaks, especially of fungal pathogens (Gliessman 1985).

2.3. EFFECTS OF INTERCROPPING ON INSECT PESTS

Intereropping can result in a signifieant reduction of insect

pest problems within agroecosystems (Altieri & Letourneau 1982,

1984, Cromatie 1983, Perrin 1977, Altieri & Liebman 1986). This

occurs because intercropping may disturb the insect's activities

and deve l opment, make the hos t 1 es s av a il ab le, and en hance the

development of the pest's natural enemies.

34

The activities that are affected include the rate of

colonization, movement, and development (Perrin 1977, Altieri &

liebman 1986). The main ways in which intercropping has

significant effects on insect populations are explained below.

2.3.1. Rate of colonization

Intercropping affects the rate of insect colonization by

disturbing the visual and olfactory responses that are employed by

many insects in searching for suitable host plants (Cromatie 1983,

Ferro 1987). As a result, they do not easily recognize and locate

suitable hosts that are dispersed amongst other vegetation

(Cromatie 1983, Kareiva 1983).

Colonization of large, closely spaced fields of the same crop

is likely to be more efficient than if the fields are small and

widely spaced. Thus, colonization by insects may be less intense

when the agroecosystem contains a relatively low proportion of food

useable by the particular insect pest (Cromatie 1983).

a. Visual effects

In an intercropping system, host plants are usually scattered

among other crop plants, 50 that the plant is camouflaged by the

non -hos t crop (Perri n 1977, Croma t i e 1983). Conseq uent l y, for a

pest that is flying over the field, intercropping makes host

recognition more difficult (Perrin 1977).

35

... b. Olfactory effects

Intercroppi ng of host and non-host plants may produce a

mixture of odors that fill the air and 50 mask the smell of host

plants and disorient insect pests as they attempt to locate their

hosts (Perrin 1977, Cromatie 1983). As a result, intercropping

makes it more difficult for insects ta find their ho~~ plant, and

50 results in less plant damage. For example, when cabbages are

in tercropped wi th tomato, they are somet i mes protected aga lrlS t fl ea

beetle infestation (Burroughs 1982). Also, certain intercropped

species release chemicals that reppl and antagonize insect pests of

other crops. For example, the diamond-back math, Plutella

xylostella, causes less damage on cabbage intercropped with tomato,

as the tomato odors repel the math and sa reduce colonization on

1 the cabbage crop (Buranday & Raros 1975).

T l

Sorne insect species, however, may be attracted ta the mixed

odor produced by part i cu 1 a r combi na tians of i ntercropped plants

(Kayumbo 1976). Therefore, to avoid the undesired result of

in creas i ng i nsect pes ts as ares u 1 t of i ntercroppi ng, ca refu l

consideration must be given in selecting the species to be

intercropped (B~rroughs 1982).

c. Diversionary host effects

In intercropping, the combination of crop plants may shift

insect feeding to the more tolerant or less valuable crop, or the

pest may colonize one particular crop in a mixture, thereby

36

protectl ng and reduci ng the feeding damage to the more economically

valuablc crops, which may be more susceptible (Perrin 1977,

Cromatie 1983). In this way, economic losses can be decreased.

The intercropped plants may function as divers;onary hosts

for a particular pest (Cromatie 1983). This may involve careful

timing of planting so that the particular growth stage of the

intercrop that is most attractive to the pest is present at the

time when the main crop is most susceptible (Perrin 1977).

2.3.2. Deve10pment

The degree of shadi ng and the nature of cul tura l practi ces

often differ between multiple and monoculture systems, and this

us Uà 11 y a ffects the c rop mi cro-c l i mate, whi ch may become l ess or

more favourab le for a part i cu l ar i nsect pest (Suryatna & Harwood

1976). Also, the confusing olfactory and visual stimuli received

from hos t sand non-hos ts may dis rupt norma l feed i ng and mati ng

behaviours (Tahvanainen & Root 1972). In addition, the pests that

dre associated with a particular crop combination m;ght disperse

el sewhere because of the low qua l i ty of food obta i ned from the

intercropped plants This may interfere with the insects' growth

and development (Kare;va 1983), and, as a result, the population

of i nsect s, as we 11 as the crop damaged, will be low .

37

, , 1

2.3.3. Dispersal

Intercropp i ng affects the movement of both adu l t and 1 arv a l

stages of i nsect pes ts because i t may provi de a phys i ca l barri er

that prevents their dispersal (Perrin 1977, Cromatie 1983). For

example, tall i ntercrops grown as rows between shorter crops may,

by reduc i ng air fl ow, cause more i nsect pests to set t 1 e thù (J if the

air flow were uni nterupted (Lits i nger & Moody 1976). Moreover, as

a physical barrier, intercropping may be valuable in reducing

colonization, thus preventing high infestation and crop damage

(Cromati e 1983). For exampl e, the cabbage rootfly, Del; a DJtkMm,

can be i mpeded from 1 ayi ng i ts eggs in fi e"1 ds that have a cover of

clover (Burroughs 1982).

2.3.4. Abundance of natural enemies

By providing a more diverse environment, intercropping may

createmore favorable conditions fornatural enemies, both in terms

of numbers and diversity (Perrin 1977, Cromatie 1983). This may

occur through the provision of essenti al resources for predators

and parasites, and 50 enable them ta obtain all of the; r

requirements near to the pest population, rather than having to

seek it farther away (Cromatie 1983). Important resources include

food, cover and alternative prey (Way 1977).

Intercropping provides more pollen and nectar sources, which

may attract natura 1 enemi es and i ncrease the; r reproduct; ve

38

potential (Kareiva 1983, Altieri 1987). Moreover, it may ;ncrease

9 round cover, wh i ch favors certa in predators such as ca rabi d and

s taphy 1 in id beet 1 es, and i ncrease the divers i ty of herb; vorous

i nsects that can serve as al ternati ve food sources for natural

enemies. Therefore, creating an environment suitable for a

diversity of insect species will help prevent the 10s5 of

benefi ci al i n sects (preda tors and pa ras; toi ds) when the; r ma in

hosts are in low number5 ( Altier; 1987). In these various ways,

i nterc r0pDi ng can i ndi rect lys upport the benef; ci al i nsects that

prey on the pests (Burroughs 1982, Fl; nt 1990).

39

r 1

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,

CHAPTER III

MATERIALS AND METHODS

40

CHAPTER III

MATERIAlS AND METHODS

,. \

3.1. Site description

A fi el d experiment was conducted duri ng the dry season in

1989 (July to December) at the Manggoapi Experimental Station of

the Faculty of Agriculture, Cenderawasih University in Manokwari

(134°05'E, 0°50'5). The station is 110 m above sea level, with

plate topography and a red-yellow Mediterranean soil type, with a

pH of 5 to 7 (Karyoto et gl. 1987).

The average rainfall and rainy days per month during the field

experiment were 187 mm and 16 days, respectively. 8ased on average

monthly rainfall recorded during 40 years , the location is

classified as having 5 to 6 months wet period and < 2 months of dry

period, with an annual rainfall of approximately 2390 mm (Oldeman

et gl. 1980). Low rainfall « 200 mm) occurs during May to

October, and high rainfall (> 200 mm) occurs during November to

April each year (Fig. 7); these periods are considered as dry and

wet season, respectively.

Accord i ng to 1 and use hi s tory, the experi menta l l oca t ion was

previously planted with mungbean, Phaseolus radiatlJs, corn, lJ~a

mQ.ll, and sweet potato, Ipomoea batatas., after which it was

abandoned for fou r yea rs, and had become weed in fes ted. Vegetation

analysis carried out prior to land clearing showeo that elephant

grass, Pennisetum purpureum, as well as Sida rhomlLifoliQ., and

Callopogon;um mucuniodes, were the dominant weeds.

41

1

nRla~ln~f~.I~I~(m~m~) ________________________________ ~ 360.-

300

FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEe Month

- 1989 ralnfaJl ~ 1939-1979 ralnfall

Fi g. 7. Nonth 1 y ra in fa 11 recorded at Manggoapi experi menta 1 farm during 1989 and the average of monthly rainfall in Nanok\Yari recorded during a prev10us 40-year period (1939 to 1979).

42

1

l

3.2. Experi menta l des i gn

The fol 1 ow; ng fi ve t reatments were tes ted us i ng a randomi zed

complete block design with three repl;cations of 150 ml plots

(Appendi x 1).

A = sweet pota to monocul ture

B = sweet pota to + COl~n

C = sweet pota to + soybean

0 = sweet potato + corn + soybean

E = sweet pota to + tomato + cabbage

3.3. Crop arrangement and s,paci ng wi thin each treatment

3.3.l. Sweet potato monoculture

A sweet potato monocul ture was pl anted with a spaci ng of 100

cm between ridges and 40 cm within rows, giving a density of 370

plants per 150 m2 plot (24.668 sweet potato plants per ha).

3.3.2. Sweet potato and corn

Two ri dges of sweet potato were planted between two double

rows of corn plants. The corn s pac; ng between rows was 50 cm, 50

that the populations obtained were 240 corn plants and 222 sweet

potato plants per plot (16.000 corn plants and 14.800 sweet potato

pl ants per ha).

43

1

1

J

3.3.3. Sweet potato and soybean

Three rows of soybean were pl anted, fo 11 owed by two rows of

sweet potato. The soybean spaci ng was 25 x 25 cm. The sweet

patata spacing was the same as in the monoculture treatment. The

popu 1 at ion s of soybean and sweet potato in th; s t reatment were 720

and 222 plants per plot, respectively (48.002 soybean plants and

14.800 sweet potato Dl ants per ha).

3.3.4. Sweet potato, corn and soybean

One row of corn was pl anted between two rows of soybean, to be

fo 11 owed by two rows of sweet potato. The same arrangement was

repeated for the rest of the plot, 50 that the populations of

soybean, corn and sweet potato were 720, 90 and 148 plants per

'f plot, respectively (48.002 soybean plants, 6.000 corn plants, and

9.867 sweet potato plants per ha).

3.3.5. Sweet potato, tomato and cabbage

Two rows of cabbage were pl anted between two rows of tomato,

fo11owed by two rows of sweet potato. Th; s arrangement was

repeated for the rest of the plot. The popul ations of tomato,

cabba ge and sweet pota to were 180, 222 and 148 plants per plot,

respect ive 1 y (12.000 tomato plants, 14.800 cabbage plants, and

9.867 sweet potato plants per ha).

44

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3.4. Fiel d preparation and management

3.4.1. Land preparation

The experimental site was cleared of grasses and shrubs, and

then plowed. The land was then divided into 15 plots of 150 ml'

each, and ri dges for sweet potato were formed in each plot.

3.4.2. Preparation of planting materials

Termi na 1 cut t i ngs of sweet pota to vi nes, about 25 to 35 cm in

length with a few leaves at the tip, were prepared three days

before planting. The cuttings were tied in groups of 10; wet jute

sack was wrapped around the cut end and the bundl es were stored in

a col d and shady place to acce l erate root growth.

Loca 1 vari et i es of corn, soybean, tomato and cabbage were

~ sel ected. The seeds of cabbage (cv. K-K Cross) and a l oca l va ri et y

l

of tomato were sown in the nursery four weeks pri or to plant i ng

out. After one week the seedl i ngs were transfered ta Pandanus-leaf

corta i ners .

3.4.3. Planting and fertilizing

All crops were planted simultaneously; the sweet potato

cutt i ngs, one per ho le, on the ri dge tops, and corn and soybean, 3

or 4 seeds per hole, according ta planting design.

Transp l anti ng of tomato and cabbage was carri ed out by openi ng

the containers and planting the seedlings in holes that had been

filled with 250 gram chicken manure. as a basic fertilizer, three

days before planting.

45

~--

A 11 c rops recei ved one or two app li cat i ons of i norgani c

sources of nit rogen t phosphorous and potass i um. Total amounts

applied are given in Table 6.

Crop

Table 6. Total amount of nitrogen, phosphorous and potassium (kg/ha) applied to sweet potato, corn, soybean, tomato and cabbage.

Fertilizer (kg/ha)

Nitrogen Phosphorous Potass i um (N) (P2Os) (KP)

----------------------------------------------------------------Sweet potato 90 JO 240

Corn 120 45 25

Soybean 45 90 50

Tomato 100 150 50

Cabbage 90 60 0

The first application took place immediately after planting,

and t for mos t cr0p, the second app 1 i cat ion occu red 30 days a fter

planting (DAP).

For sweet pota to, ha 1 f of the fert il i zer was app 1 i ed as a spot

application at planting time, and the other half at 30 DAP. For

corn t two-third of the nitrogen was applied at planting, the

remaining one third at 30 DAP. The complete dose of phosphorous

and potassium was applied at the time of planting.

Soybean fertilizer was applied once at planting time as a

cont in uous band 7 to 10 cm to one si de of the row. Tomato and

cabbage were fert il i zed once by means of spot and ri ng

applications, respectively, at 21 DAP.

46

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3.5. Crop maintenance

Crops maintenance included watering, replanting, weeding and

hi11ing up of the soil, staking of tomato plants, lifting of vines,

and pruning of the old leaves.

Wa teri ng was provi ded, es peci a 11 y for cabbage and toma to,

du ri ng the fi rs t two weeks before the plants were we 11 es tab 1 i shed.

Sweet potato was al so watered ea r l yin the growi ng season, when the

weather was dry. All dead and missing plants were replaced ~ithin

7 to 10 DAP.

Hand weeding, especially of nutsedge, Cyperus roton~, which

domi nated the experi menta 1 a rea, was underta ken twi ce. Weed i ng was

done 14 and 28 DAP. Hi 11 i ng up of the soi 1 was done i mmedi a te 1 y

after weeding to support the crops.

Tomato plants were staked with 75 cm long sticks, 21 DAP.

Lifting of sweet potato vines to prevent the growth of adventious

roots took place twice, at 28 and 56 DAP. Pruning of old sweet

potato leaves was carried out as necessary.

3.6. Observations

3.6.1. Colonization by SPW

Observation of colonization of the sweet potato crop by SPW

was carried out at 56 DAP on 10 randomly selected plants from each

plot. A plant was considered to have been co1onized if a SPW was

present or if damage by SPW was evident. Percentage colonlzation

data was calculated as follows:

47

III

"

where:

N c = -------------- x 100 % T

C = percentage colonizat-jon of the sweet potato plant in a plot

N = number of samples colonized T = total number of samples per plot

Percentage of co 1 oni zati on data were tabul ated and transformed

w i t han arc sin t ra n s f 0 rm a t ion p rio r t 0 a n a lys i S 0 f var i an ce, as

recommended by Gomez & Gomez (1976, 1984 ), when data are in

proport ions.

3.6.2. Population density of SPW and percentage of damaged tuber

Ten samp l i ng un i ts (p 1 ants) were taken random 1 y from each

experimental unit to determine the size of the SPW population.

The tubers and vines (15 cm above the crown) of each plant were

dis sected direct 1 y a t ha rves t; and the number of weevi 1 1 arvae,

pupae and adul ts were total ed for each sampl; ng un; ts (pl ant) per

experimental unit.

The percentdge of infested (damaged) tubers WdS calcul ated as

fo 11 ows.

a l = ---------- x 100 %

a + b

Ivhere: l = percentage of i nfected tubers a = i nfected tubers b = hea l thy tubers

48

, ,

Data for thl~ number of i nsects, and the percentage of i nfected

tubers, were tabulated and transformed with a square root + 0.5,

and arcsin transformation, respectively, prior to analysis. The

square root + 0.5 and arcsin transformation are used when data

record rare events and relate to proportions, respectively (Gomez

& Gomez 1976, 1984).

3.6.3. Number and fresh weight of tubers

Number of tubers from ten plants from each plot were counted

and their fresh weight was recorded.

3.6.4. Marketable yield

Ma rketab le yi el d of sweet pot a to, corn and soybean were

wei ghed from each plot pri or to bel ng ma rketed. Prof; t obta; ned

from marketing the yield of a particular cropping system, without

ta king in to account the cos t of product ion, was recorded as i ts

economi c value. The value of each of the crops was based on the

market priees in the Manokwari market in December 1989.

3.6.5. Monetary index

Monetary index (Gomez & Gomez 1983) was used to evaluate the

yield advantage of each treatment. This was obtained by

substracting the total cost of production from total economic value

of the oroduce from each cropping system.

Total cost of production included operational cost and

materi al s. Operational cost consisted of land preparation,

49

planting, fertilizing, maintaning, harvesting, washing of the

tubers, drying and seeding of corn and soybean; while materials

included cost of sweet potato cuttings, corn and soybean seeds, and

fert il i zers (Urea, TPS, and Kel).

3.6.6. Insect diversity

Insects from the monoculture and the intercropped sweet potato

were sampled using a sweep net and pitfall traps as described

below.

a. Sweep net sampling

Sweep net sampling was done as described by Risch (1979) in

Costa Rica. One sampling unit (30 sweeps) was replicated four

tlmes in each experimental unit (plot). Thus, 120 sweeps were

taken from each experimental unit and a total of 360 sweeps were

taken from each tredtment. Sweeping w~s done in straight lines and

the vegeta t ion was never swept tw; ce duri ng a samp 1 i ng date.

Sweeping was carried out on four sampling dates, 35 DAP, 42 DAP, 49

DAP and 56 DAP, always between 08.00 a.m and Il.00 a.m.

1 nsec t s co 11 ected from each s amp 1 i ng un i t (30 sweeps) were

placed in a sma" plastic bag, killed with chloroform, separated

fram the vegetation, and stored in vials in 75 % methyl alcohol.

The insects were then separated into families under a stereoscopie

mi c roscope, accord i ng to the cl ass; fi cati on scheme ; n Borror et

ILL. (1989).

50

1 b. Pitfall traps

Five pitfall traps per plot were used to capture ground

inhabiting arthropods. The traps (12 cm diam. x 15 cm high

plastie containers), were p1aced diagonally at five points in each

plot 35 DAP (Fi g. 8). They were buri ed in the soil 50 tha t the

edge of the container was flush with the soil surface.

To prevent escape, the t raps were ha l f fi 11 ed wi th a near

saturated solution of water, salt and detergent.

51

10 !IL

o o

o

o o

Figure 8. Arrangement of pitfall traps in each cxperimental unit

15 zn.

52

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, ,

3.7. Analysis of data

3.7.1. Effects of intercropping on populations of SPW and on sweet potato production

For testing the significance of the effects of intercropping

on the populations of SPW (number of SPW and percentage of damage)

and on sweet potato production (number of tubers and fresh weight

of tubers), these data were subjected to analysis of variance.

Fisher's Least Significant Difference (LSD) test was used to locate

differences among means.

The relationship between numbers of SPW, and percentage of

damaged tubers were analyzed by means of regression analysis.

Marketable yield was tabulated to compare yield advantage.

Comparison of yield advantage among treatments using Land

Equivalent Ratio (LER) could not be carried out, because in the

present study corn and soybean were not planted in monoculture. As

a result, the yield advantage is expressed as a Monetary Index

(MI). This index can be obtained by using the following formula:

where

n MI = E (a

1X

1 - b) (Gomez & Gomez 1983).

;=1

MI = monetary index a = species of crops bl = economic value of crops in a cropping system X: = yield of a species of crop

53

3.7.2. Insect diversity

AnalYS1S of the diversity of insects and spiders within the

four different sweet potato agroecosystems was determined by using

the Kruskal-Wallis non-parametric analysis of variance (Daniel

1990). This analysis is based on Kruskal-Wallis test statistic

(H) .

12 R ? 1

H = -------- E -----N(N + 1) n

1

3(N + 1) (Daniel 1990)

where: N = the total number of insect and spider families w;thin the four sweet potato cropping systems.

Rl = the sum of the ranks assigned to the number of insect and spider families within the four sweet potato cropping systems.

ThlS analysis was used to test the fo1lowing hypotheses:

1. Nu 11 hypot hes i s (Ho): The number of i nsect and s pi der famil i es

within each of the four sweet potato cropping systems are

sim; lare

2. Alterna t ive hypothes i s (HA): The number of ; nsect and spi der

fami 1 i es w; thi n each of the four sweet potato croppi ng systems

are no t sim i l a r .

The null hypothesis is rejected if the value of H in Kruskal-

Wa Il is non-parametric ana1ysis of variance is greater th an X23

. 0 05.

54

1

CHAPT ER IV

RESULTS

,.

Dald VIere collected from the four intercropped treatments:

rJw:(; t pota to mon ocu ltu re, sweet pota to + corn, sweet pota to +

soybean, and sweet potato + corn + soybean (Figs. 10,11,12 & 13

respectlvely) . A fi fth treatment (sweet potato + tomato +

cahbage), was abandoned because the cabbage and tomato crops were

hr~vlly damaged by the diamond-back moth, Plutella xylostel1a, and

fWJdriulll wl1t, L!"·t~.~trlum oxysporum, respectively (Fig. 9).

F l g. 9. Heav i l Y damaged tomato and cabbage i nter-cropped with sweet potato (treatment E).

56

1

1

1

Fig.IO. Sweet potata monoculture (treatment A).

Fig. Il. Sweet potato intercropped with corn (treatment B).

57 ,

1

_J

Fig. 12. Sweet patata intercropped with soybean (treatment C).

Flg. 13. Sweet patata intercropped with corn and soybean (treatment 0).

58

l 4.1. Effects of intercropping on the population of sweet potato

weevil (SPW) and on sweet potato yield.

4.1.1. Colonization of the sweet potato by SPW in four cropping systems

Colonization by the SPW at 56 DAP was significantly lower for

intercropped sweet potato compared with the sweet potato

monoculture (Table 7). ~here was, however, no significant

difference in colonization among the three intercropped treatments,

even though the level of colonization in the sweet potato + corn

(11 %) was only half of that in the sweet potato + soybean (23 X).

Table 7. Colonization of sweet potata by the sweet potato weevil (SPW) at 56 DAP.

Colonization by SPW (%) Sweet potato agroecosystem

Original Transformed Ratio data datai

------------------------------------------------------------------Sweet potato monoculture (A) 70 70.0 a?

Sweet potato + soybean (C) 23 23.2 b

Sweet potato + corn + soybean (D) 20 20.0 b

Sweet potato + corn (B) 10 10.8 b

Coefficient of variance (CV) 31.4

1) Arc sine transformation was used for transforming original percentage data.

2) Any two means in one column followed by different letters differ significantly at P < 0.05 using Fisher's Least Significant Different (LSD) test.

6.5

2.2

1.9

1.0

59

4.1.2. Population density of SPW and percentage of damaged tubers

Population density of SPW and percentage of damaged tubers

were significantly lower on the intercropped sweet potato

(treatments B, C, and D) compared with the sweet potato monoculture

(treatment A; Table 8). These rneasures were also significantly

lower in mixtures containing corn (treatment B & C) than in those

wlthout this crop (treatment C; Table 8). Thus, among the

interc~ops tested, corn was most able to reduce the population of

SPW and of damaged tubers.

Table 8. Number of sweet potato weevils (SPW) per kllogram of damaged tubers, and percentage of damaged tubers.

Swcet potato agroecosystem SPW Damaged tubers

No.jkg damaged Ratio tubers

% Ratio

------------------ -------------------------------------------------------Sweet potato monoculture (A) 37.0 al 16.0 21.9

Sweet potato + soybean (C) 21.0 b 9.1 14.7

SW(let potato + corn + soybean (0) 7.7 c 3.3

Swcet potato + corn (B) 2.3 c 1.0

Coffecient of Variance (CV) 20.9

1) Any two mean~ in one column followed by different letters differ significantly at P < 0.05 using Fisher's Least Significant Different (LSD) test.

6.6

2.6

al 8.4

b 5.7

c 2.5

c 1.0

60

1 Al though the i ncl us i on of soybean in the i ntercroppi ng mi xture

appeared to reduce this effect of the corn, the differences between

the mixture with and without soybean were not statistically

significant.

A high population of SPW is more likely to result ln a high

percentage of damaged tubers (Table 8). ThlS relationship is

depicted by the regression line of Y = 2.00 + 0.55 X (Fig. 14),

which indicates that there is a significant positive correlation

between population density of SPW and number of damaged tubers

(rca1 = 0,98 > ro 05 = 0.87).

4.1.3. Number and fresh weight of sweet potato tubers

Even though sweet potato intercropped with corn (treatments B

and D) significantly reduced the population density of SPW and

number of damaged tubers, the 1 eve l of product ion wi th corn,

measured as number of tubers per plant and as weight of fresh

tubers per 10 plants, was significantly lower th an in the cropping

systems without corn (Table 9).

Interestingly, the weight of fresh tubers in the sweet potata

+ corn + soybean mixture (treatment D) was half that in the sweet

potato + corn mixture (treatment B), although this difference was

not statistically significant. Furthermore, it appears that

whereas the i ncl us i on of soybean may have reduced sweet potato

yield, it did not affect sweet patata number, which was identical

in the two corn mixtures.

61

.' '\

.30 r y = 2.05 + 0.55 X r = 0.98

25 -A

,.r-....

n} ~'J --'-

IJI .-'IJ il ::J

.. ..J 1!J ", 'V U' r_, ~: L

r.J lU L-l

~I

o 5 10 15 20 ':0 .35 40

Fly. 14. Relationship betweEn number of sweet patata w~evl1s (SPW) and damaged tubers. A = ~weet potato monoculture, B = sweet potato + corn, C = sweet potato + soybean, 0 = sweet patalo + corn + soybean.

62

, A

-

Table 9. Effects of intercropping sweet potato on number of tubers per plant and on fresh weight of tubers per 10 plants.

Sweet patata agroecosystem Number of Ratio tubers per

Weight of Ratio fresh tubers

Sweet potato monoculture (A)

Sweet potato + soybean (C)

Sweet potato + corn (B)

per plant l

2.3 a

1.1 b

Sweet potato + corn + soybean (0) 1.1 b

Coefficient of variance (CV)

2.5

2.1

1.0

1.0

pet' 10 pl ants!

488.1 al

440.2 a

143.3 b

75.2 b

28.8

1) Any two means in one column followed by different letters differ significantly at P < 0.05 using Fisher's Least Significant Different (LSD) test.

6.6

5.9

1.9

1.0

4.1.4. Marketable yield and economic value of sweet potato and intercropped plants

Marketable yield and economic value of sweet potato, corn and

soybean from the four di fferent sweet potato agroecosystems are

presented in Table 10. The economic value of the marketable yield

was hi ghest for the sweet potato monocul ture and lowest for the

sweet potato + corn + soybean mi xture. Yi el d advantages in the

present study was calculated by using the monetary index (MI; Table

10) .

63

L

Table 10. Marketable yield, economic values, cast of production and monetary index of sweet patata and intercrapped plants in intercrapped sweet patata with carn and soybean.

Cropping Yield Economie value Total Cast of system (t/ha) (Can. $/ha/season)* economic production

------------------------ ------------------------ value Ratio (Can. $/ha)** sweet corn soy- sweet corn soy-patata bean patata bean ($)

Monetary index

----------------------------------------------------------------------------------------------------------------Al 7.0 2808 2808

B 0.9 1.6 344 822 1226

C 2.9 0.5 1157 400 1558

0 0.8 0.6 0.3 30Q 324 256 890

*) Marketable price of sweet patato, corn, and soybean were 0.40, 0.54 and 0.77 dollars per kllogram, respectively.

**) Cast of production is presented in Appendix 3. 1) A= sweet potato monoculture

B= sweet potato + corn C~ sweet patata T soybean 0= sweet patata + corn + soybean

1.0 1539 1269

0.4 1268 -42

0.6 1484 74

0.3 1158 -256

64

4.2. Number of insect and spider families, and number of individuals of each family associated with sweet potato agroecosys tems

The number of i nsect and spi der fanlll i es, and number of

individuals of each family (Tables Il,12, 13, 14), were obtained

from sweep net samples; the pitfal1 traps did not generate data as

they proved to be i nope rat ; ve in the cond it i ons of the present

study. Detailed information on individuals collected from each

family i5 reported in Appendix 4.

fable 11. Insect and spider families (fam.) and individuals (ind.) of each family ca 11 ected at 35 DAP.

Order of B C i nsects & spi ders

fam. ind. fam. ind. fam. ind.

Coleoptera 1 8 3 31 5 27 Hymenoptera 3 3 3 3 7 18 Homoptera 2 9 4 9 Hemiptera 1 2 Orthoptera 3 25 3 16 4 15 l epi doptera 3 17 3 7 3 15 Di ptera 2 4 4 12 13 96 Araneae (spiders) l 1 1 10 1 56 ------------- ----------------------------------------------------Total 13 58

Ratio (fam.) 1.0

Ratio (ind.) 1.0

1) A = Sweet potata monocu lture B = Sweet potata + corn C = Sweet potata + soybean o = Sweet potata + corn + soybean

19 88 38 238

1.46 2.92

1. 52 4.10

D

fam. ind.

4 40 6 9 4 21 1 2 4 44 4 10

14 183 1 51

-----------38 360

2.92

6.21

65

rdblr~ 12. In'J(!ct and spider families (fam.) and individuals (ind.) of (!ach family collected at 42 DAP.

Order of insecls & spiders

B c D

fam. ind. fam. ind. fam. i nd. fam. i nd.

Co l coptera 2 29 4 72 4 64 4 Hymenoptera 1 2 4 12 6 20 5 lIomoptera 1 2 2 17 2 23 3 Il('m i ptera 2 15 2 344 5 200 6 Orlhoplera 4 28 4 26 4 26 4 1 Pp Idopter'a 2 5 3 7 4 [)Iptpra 3 14 8 102 12 325 14 r~dr" odea 1 4 1 BlattdrJd 1 2 Ardneae (spIders) 1 38 1 48 1 137 1

lot al 17 135 25 621 38 806 42

Ratio (fam.) 1.0 1. 47 2.24 2.47

I<alio (lnd.) 1.0 4.60 5.97

1) seeTabJe]l.

lable ]3. Insect and spider families (fam.) and individuals (ind.) of each family collected at 49 DAP.

215 16 26

543 75 12

277 3

247

1414

10.47

-------- ------------------------------------------------------ ---------------Order of AI B C 0

ln~('cts & spiders ----- ------------------------------------------------------fam. ind. fam. ind. fam. inde fam. inde

----------- -----------------------------------------------------------------Lo J coptera 3 29 4 56 3 122 3 89 IIYlllenopt era 3 23 4 23 7 40 7 35 lIol11optera 2 16 4 29 5 70 6 77 Ilellliptera 2 19 4 69 6 287 5 327 Ort hoptera 3 67 4 142 4 259 4 124 Lepidoptera 3 13 1 1 3 7 3 9 Di ptera 3 54 10 247 10 247 14 283 Mantodea 1 4 1 6 At'anea~ (spider) 1 72 l 79 1 246 1 343 ------ ___________________________________ a ____________ ________________________

Total 20 293 32 646 40 1282 44 1293

Rat io (fam.) 1.0 1. 60 2.0 2.20

Ratio (ind.) 1.0 2.20 4.38 4.41

1) see Table Il.

66

Table 14. Insect and spider families (fam.) and individuals (ind.) of each fami l y co 11 ected a t 56 DAP.

Order of insects & spiders

B C D

fam. ind. fam. ind. fam. ind. fam. ind.

Coleoptera Hymenoptera Homoptera Hemirtera OrUloptera Lepldoptera Neuroptera Diptera Mantodea Bl attari a Areneae (spiders)

Total

Ratio (fam.)

Ra t ion (i nd . )

1) see Table 11.

3 2 1 4 3 1

7 1

1

23

1.0

76 16 15

172 72 8

83 2

57

501

1.0

3 5 3 5 4

14 1

1

36

l. 57

47 Il 23

118 29

58 1

41

328

0.65

6 6 S 5 4 3 1

14

1 l

46

2.0

372 47 33

2418 342

5 1

120

4 171

3513

7.01

6 8 5 5 4 3 1

15 1 l 1

50

2.17

414 34 36

2320 238

2 2

215 1 3

161

3426

6.84

The i ntercropped systems supported more fami lies of i nsects

and spiders than did the monoculture (Tables 11,12, 13 and 14).

Wi th one except ion (sweet potato + corn at 56 DAP, t rea tmen t B,

Table 14) the intercropped systems also supported higher numbers of

arthropods, even up to 10 times the population density.

Compared with the monoculture, number of insect and spider

fami 1 ies in treatments B, C, and D are 46 %, 192 % and 192 % higher

at 35 DAP, 47 %, 124 ~~ and 147 % high:r at 42 DAP, 60 %,100 %, and

120 % higher at 49 DAP, and 57 %,100 % and 117 % higher at 56 DAP.

The i ncreases in number of i nsect and spi der fami lies over 100 %

occurred in the treatments that inclLded soybean: C (sweet potato

+ soybean) and B (sweet potato + corn + soybean). Cumulative data

for the entire sampling periods is shown in Figure 15.

67

The hi gh number of i nsect and spi der fami lies in the

i ntercroppi ng systems suggest that these systems provided a greater

diversity of habitats. A reason of the diversity of insect and

splder families within the different sweet potato cropping systems

was obtained by subjecting the data to Kruskal-Wallis non­

paramctrlc analysis of varlance. The analysis tested whether the

null hypothesis (the number of lnsect and spider families within

each of the four sweet potato croppi ng systems are simi l ar) or

alternative hypotheses (the number of insect and spider families

within at least one of the four sweet potato cropping systems is

not simllar) would be acceptable based on the H value of the

Kruskal-Wallis test.

The H val ue, 12.88, exceeded X23 . 0 05 (7.815), therefore the null

l hypothes 1 sis rej ected: hence, the numbers of i nsect and spi der

families for the four sweet potato cropping systems are diverse.

The average rank in diversity was higher in sweet potato

intercropped with corn and soybean (53.0), followed by sweet potato

intercropped with soybean (47.0), sweet potato intercropped with

corn (26.0), and sweet potato monoculture (10.0).

68

.-

No. of famille. ~~-----------------------------

60~---------------------------------------

~O~---------------

301----1

20~--f

10

o 36 4f2 ~9 66

DI~' aller planllng

- T,..IMenI Il œ 1'r..IIMftI a t;;;;ll'rNJa.nl C _ T""-.nl D

Figure 15. Number of insect and spider families associated with sweet potato cropping systems

59

4.3. AsQj domorpha sp. (Col eoptera: Chrysome li dae) and lycosa sp. lAraneae): two populations of arthropod species within the monoculture and intercropping systems.

The popu 1 a t i on of the spot ted tortoi se beet le, Asp i domorpha

sp., a 1 eaf-feedi ng i nsect assoc; ated wi th the sweet potato pl ant

and other J~omoea species (Simon Thomas 1961, 1964, Kalshoven

1983), wa s lower ln the i ntercropped sweet pota ta th a n in the sweet

potato monoculture (Fig. 16). The effect of the intercropped sweet

potata on the populatlons of this beetle was more evident and

statistically significant at 56 DAP, although not for all intercrop

trcatmcnts (Table 15). At 56 DAP, lntercropped sweet potato + corn

(trcatment B) had the lowest number of beetles (1.0), followed by

bot h i nte rcropped sweet pota to + soyhean (t rea tment C; 2.0), sweet

potato + corn + soybean (treatment 0; 2.0) with the sweet potato

monoculture having the highest number of beetles (treatment A;

4.0) .

The appos i te was obs erved wi th the popu 1 a t i on of the

predaceous spider, ~cosÀ sp. (Table 15, Fig. 17). The spider

populations were signicantly higher in intercropped sweet potato

whcre soybean was used as an intercropped plant (treatments C and

D; Table 15) and this was so throughout the cropping season, except

at 56 DAP, I"hen sweet potato + corn (treatrnent B) had less spiders

than the monoculture, though not significantly so.

70

Table 15. Number of spotted tortoise beetles colleeted at 56 DAP and spiders eolleeted at 35 DAP, 42 DAP, 49 DAP and 56 DAP. in four sweet potato cropping systems.

Croppi ng system·

A

B

C

D

Number of spotted tortoise beetles1

56 DAP

3.7 a

1.0 c

2.0 b

2.0 b

Number of the spiders l

35 DAP

0.3 b

3.3 b

18.7 a

17.0 a

42 DAP 49 DAP 56 DAP

12.7 b 24.0 b 19.0 be

16.0 b 26.3 b 13.7 b

45.7 a 82.0 a 57.0 a

82.3 a 114.3 a 53. 7 ab

1) Any two means in one column followed by different letters are differ signifieantly at P < 0.05 using fisher's Least Signi fi cant Di fferent (LSD) test.

*) A:.. sweet potato monoculture B = sweet potato + corn C = sweet potato , soybean D = sweet potato + corn + soybean

71

No. of bootloe 12~~-----------------------------------------'

101------------------------

o 1---------------

6f--------

4.--------

2

oLJli~~---<42 <49 01)'1 Iller plantlng

66

mrI TnJatmont A ~ Tr.unenl B D Tre&tlhlnl C • Tr •• llnOnl 0

Fi qure 16. Number 0 f spotted torto i se beetles t Aspidomorpha sp. {Co 1 eopterae: Cassididae} collected from four sweet potato cropping systems at 35, 42, 49 and 56 DAP. .

72

• "

1

No. of epldere 400

360

300

250

200

160

100

60

0 36 042 ~9 &6

Day. aUer plantlng

III Tre.lment A • Trwatlntnt B D Treatnent C _ Tr .. lrnenl 0

Figure 17. Number of spiders, Lycosa sp. (Areneae: Lycosidae)" coll ected from four sweet patata croppJ ng SYS tems a t 35, 42, 49 and 56 DAP.

73

l

CHAPTER V

DISCUSSION

5.1. Effects of intercrop~ing on the population density of the sweet potato weevil (SPW)

5. 1. 1. Effects of i ntercroppi ng on number of SPW and on percentage of damaged tubers

The low percentage of S PW co 1 oni z i ng sweet pota ta i ntercropped

with corn and/or soybean (Table 7) suggests that intercropping may

have affected its host searching behaviour. For example,

percentage colonization by SPW, number of SPW per plant, and

percentage of damaged tubers in the sweet pota to monocu ltu re was 7,

16, and 8 times that in the sweet potato + corn mixture,

respectively (Table 7 & 8). Similar high levels of damage in sweet

pota to monocu 1 tu res were al so reported in Papua New Gu i nea

(Sutherl and 1986b). Howpver, number of tubers per pl ant, weight of

fresh tubers per 10 plants, and total value of the marketable yield

in the monoculture were 3, 7 and 3 times that in the sweet potato

+ corn + soybean mixture and 3, 3 and 2 times that in the sweet

potato + corn mixture, respectively (Table 9 & 10). For farmers

who grow sweet potato primarily for home consumption, the

monoculture would be attractive, because of the higher produ·:tion

of tubers which may give them a marketable surplus. The monei..ary

index (MI) used to determi ne yi el d advantage of the di fferen t

treatments (Table 10), i11 ustrates that the greatest profit was

obtained by growing sweet potato as a monocul ture (treatment A),

and then vJhen i ntercropped wi th soybean (t reatment C), res u 1 t l ng in

a net gain of Cano $ 1269/ha and Cano $ 74/ha, respectively.

75

1

Thus, although the mixtures, particularly those including

corn, were effect ive in reduci ng numbers of SPW, they were

uneconomlC, especially when they included both corn and soybean.

The low percentage of colonization and low number of SPW in

1 nterc ropped sweet pota to i s probab l y a resu 1 t of phys i ca 1 and

biological effects of the intercropped plants on the weevils'

activi ty, growth and development (Perrin 1977, Altieri 1987). The

taller corn and soybean plants may act as physical barriers against

SPW invasion of the sweet potato crop. Presumably, the SPW either

moved away from the intercropped sweet potato to a more sui table

l oca t ion 0 r had to spend ext ra t i me and energy to fi nd the crop

(Kareiva 1983). In a corn + bean mixture, Parfait & Jarry (1987)

found that corn made the mi crocl imate unfavorable for the bean

weevil and modified the bean's phenology. Similar effects may be

partly responsible for the reduced of SPW population in the corn +

sweet potato mixture in the present study.

Furthermore, it is suspected that during the extended period

of hos t sea rch i ng in the i ntercropped sys tems, S PW wou l d have been

exposed to various environmental pressures, including higher

popu lat ion dens i ty of n atura 1 enem i es (Ka rei va 1983, van Emden

1990). Al though, in the present study the natura l enemi es were not

stud i ed quantitat i vely, they were recorded in both the sweet potato

agroecosystems and the surrounding area. For example, preying

Illant id s, wh i ch are genera l feeders (Ho 11 i ngswort h & l doi ne 1992),

\'Jcrr often seen searchi ng for prey on the sweet potato fol i age,

although their effects on SPWs were not evaluated. Also, chickens

76

.,

...

from a nearby village were commonly seen searching for insects in

the area surrounding the plots. Thus, the SPW would have been

vulnerable to attack by these and other natural enemies while

searching for a suitable hast.

Preda tors and pa ras i tes are usua 11 y more abundant with in

mixtures than in monocultures (Perrin 1977, Altieri 1987). This

may accou n t for much of the reduct i on of the popu lat ions 0 f SPW

within the mixtures.

SPW orients to its hosts by means of chemical eues produced

and re l eased by the sweet potato l ea ves a nd tuber sk in (Not th i ngham

et il. 1988). In intercropped sweet patata fields, however, such

chem; cal s may be masked by other chem; cal s from the i ntercrop

plants, thereby making it more difficult for the SPW to locate and

recogn i ze ; ts hos t.

5.1.2. Level of attack by SPW in relation to tuber formation.

l nterc rop plants maya ffect the growth and deve l opment of the

sweet pota to crop, thereby maki ng ; t 1 es s attractive ta SPW.

The sweet potato that attracts SPW is released chemical

dur; ng the forma tian of new tubers, wh; ch accu rs between 28 and 56

DAP (Wi 1 son & Lowe 1973, Wi 1 son 1982). Because i ntercropped sweet

potato probab 1 y recei ves l ess li ght than in monocul ture, the

resultant delayed tuber formation would also delay release of the

att ractant, and therefore effect the movement of SPW towa rds i ts

hos t .

77

l

The low number of tubers per pl ant, and the low wei ght of

fres Il tubers pe r 10 plants in sweet pota to i ntercropped wi th corn

were most 1ikely caused by the lack of light that resulted from

shading by the corn plants. Hahn (1977) found that a lack of light

caused a decrease in the net assimilation rate and dry matter

production, esp(lcially in the form of tubers. Moreno (1982), found

that intercropping sweet potato with corn in Guatemala reduced

sweet pota to yi el d by 63 percent; whereas Roberts et iÜ. ( 1983) ,

found that in Trinidad the reduction ranged from 10 % to 44 ~,.

Variations in yield were related to rainfall, the sweet potato

cultivar, planting date and crop spacing (Roberts et al. 1983).

In the present study, yield was lower when sweet potato was

i ntercropped wi th corn than wi th soybean (Table 9), pres umab 1 y

1 a rge 1 y because of the greater shad i ng effect 0 f corn. Soybean may

also have provided additional nitrogen to the sweet potato. This

possible benefit, however, was not evident when sweet potato was

intercropped with corn and soybean (treatment D; Table 9), probably

because of competi ti on from the corn for l imi ted resources,

particulélrly light, nutrients, water, and space; and under these

cond i t i ons the sweet potato plants produced on l y a few and mos t l Y

sma 11 tubers. Therefore , al though i ntercroppi ng reduced the number

of both pest i nsects and damaged tubers, it al so resul ted in a

greater reduction in marketable yield.

Because of the lower numbers of SPW in the corn + sweet potato

mixture, intercropping with corn seems to be the most promising

strategy for control of SPW, and should be investigated further,

78

,

~---~-~~--_ ..

but the 60 % reduction in economic value of marketable yield

1'1"0'1 i des a cons i derab le cha 11 enge to be overcome.

Unti 1 i ntercroppi ng systems are found that both reduce pest

damage, and produce higher or comparable yields and levels of

prof i t to monocu l ture, the 1 a tter i s li ke l y to be preferred by

farmers in Irian Jaya.

Among the in tercroppi ng systems exami ned in the present s tudy,

the sweet potato + soybean mi xture (t reatment C) i s the best choi ce

for i ncreas i ng in come and meet i ng n ut rit i ona l requi rements of the

indigenous people in both the lowland and highland regions of Irian

Jaya.

The in t roduct i on of soybean in to an i ndi genous sweet potato

cropping system in Irian Jaya presents several advantages. (1)

Because soybean roots are i nfected wi th the nitrogen fi xing

bacteri a, Rh i zobi um, thei r presence can i ncrease the amount of

nitrogen in the soil available to the sweet potato. (2) Protein­

rich soybeans would also enhance the nutritional quality of the

i nd i genous di et. The nu t rit; ona l va l ue of soybean has not yet been

recog ni zed, however, by l ri an Jaya' sind i genous sweet potato

farmers (La Ahmady 1988), who still primari ly regard ~oybean as a

cash crop. (3) The soybean crop by provi di ng the farmers wi th a

second marketable commodity would help them to diversify their

production base (Kass 1978). (4) The failure of one crOD within an

; ntercroppi ng sys tem as a resu l t of adverse env i ronmenta l

cond i t ions, s uch as drought, pests, or di sease, can be compensated

for the other trops (K(!ss 1978, Beets 198?). Th us, i ntercroppi ng

79

mdy provide yield stability, because an alternative crop may be a

cri ti ca l asset when the ma in crop i s compromi sed by poor weather or

other environmental stre5ses. (5). Soybean and sweet potato

i ntercropped together appear to harbour fewer inseet pests,

diseases and weeds than when bath crops are grown in pure stands.

5.2. Number of insect and spider families associated with sweet potato agroecosystems

The number of insect and spider families in the intercropped

sweet potato systems were generally higher tnan in the sweet potato

monocul ture. Results indicate that the insect and spider

popu lat ion i s more diverse in i ntercropped sweet potato than in a

sweet potato monocu 1 ture and tha t th i 5 di vers i ty changes wi th e rop

phenology.

This inerease in arthropod diversity in intercropping sweet

potato plots may s imp l y represent the addit i on of the faunas of the

eomponent crops An individllal crop and its associated

phytoph agous fauna (usually speeialized insects) in an

intercropping system may directly or indirectly provide chemical

eues attract i ng natura l enemi es (Pri ce 1986). Predators and

parasitoids, for example, may search and attack their Ilost in the

i ntercroppi ng systems, based on the a -t: tract i ve body odor rel ea sed

by phytophagous i nsects. A l sa, they may fi nd the phytophagous

i nsects i nd i rect l y th roug h chemi ca 15 re l eased by the hos t plan t on

which their potential prey or host is feeding

Therefore, an i ndi vi dual crop and its assoei ated

(Priee 1986).

80

fauna in sweet potata crappi ng systems may resul t ; n a hi gher

n umber of in sect s pee; es in in tercropped sys tems (Ri s ch et al.

1983).

There are numeraus parasitoids and predators associated with

i nsect pests of sweet patato and the other i ntercrops. For

examp1e, trichagrammids are known to parasitize the sweet potato

horn worm, Herse conva1vu1 i, L., and the Asian corn borer, Ostrinia

furnacalis_ Guinee (Nafus & Schreiner 1986). The latter ;s also

attacked by braconids, ichneumonids, chôlcidids, eu1ophids,

tachinids and by predators such as Orius spp.(Hemiptera:

Anthocori dae), Che l i soches spp. (Dermaptera: Che 1 i soch i dae), and

other i nsects and spi ders (Nafus & Schrei ner 1991). Many

parasitoids ènd predators associated with each species of insect

pest, wi 11 have contributed ta the higher insect diversity found in

, the i ntercropped sweet potato systems.

Even though the divers i ty of the a rthropod fauna in an

intercropped system is generally higher, the population density of

each species of herbivore, however, is generally lower (Risch et

al. 1983, Letourneau 1990). This is i1lustrated in the present

study, where a smaller population of the spotted tortoise bettle,

A~Qidoll1o~ha sp., a leaf-feeding insect exclusively associated with

sweet potato, tended to be lower in the intercropped systems than

in the monoculture (Fig. 17). Even though reasons for the lower

popu1 at i on of the beet lei Il the i ntercropped sweet potato were not

determi ned, prev; ous research has shown that i ntercroppi ng

frequently causes dramatic decrease in a pest population (Pimentel

8l

1961, Root 1973, Dempster & Coaker 1974, Perrin 1977, Karel ~ ~l.

1982, Altieri & LetournealJ 1982, 1984, Cromatie 1983, Altieri &

Liebman 1986, Tingey & Lamont 1988, van Emden 1990). For example

the popu lat ion dens i t i es of EmRoasca f abae (Ha rri s) and Mh~ fj!Jli\~

Scopol~, were significantly less in plot~ intercropped with winter

wheat th an in those grown in monocu l t rure (Ti ngey & Lamont 1988).

Simi1ary the reduction of the popu1dtion of the diamond-back moth,

Plu tell a x y los te 11 â ( L), w a s sig TI i fic an t l Y les 5 i n plo t s wh e re

cabbages were intercropped with tomatoes (Buranday & Raros 1975).

These authors a1so noted that int~rcrop plants acted as effective

physical and biological bal~riers to insect pest infestation.

However, the mechani sms in wh i ch i ntercropped plants prevent

infestations are not always similar for all species of insects.

In the case of the spotted tortoise beet1e, two hypotheses as

suggested by Root (1973), may be used two exp 1 ai n the beet le' s

lower popu 1 at ion dens i ty in i ntercropped sweet pota to: the resou rce

concentration hypothesis and the natural enemies hypothesis. The

first hypothesis predicts that specialized insect pests will be

1 ess abundant in i ntercropped systems when the mi xtures are

composed of both host and non-host crops (Sheehan 1986, Altieri

1987) . Therefore, in the present s tudy, the s potted torto i se

beetle, a specialist pest of the sweet potato crop, may have had a

difficult time locating, remaining on, and reproducing on the sweet

potato crop; the corn and soybean plants may have acted as physica1

barriers limiting movement of the beetle into or within the sweet

potato plants. The beetle a1so may not have recognized the sweet

82

potato plants because of chemicals produced by the other

intercropped plants m-lsking those of the sweet potato (Altieri

1987) .

The second hypothes i 5 states that hi gh veceta t ion divers i ty

improves conditions for natural enemies by providing a variety of

habitats, and abundar,t food and shelter, resulting in increasing

their numbers and efficiency in intercropping plots. For example,

i ntercroppi ng systems can provi de more pollen and nectar sources

that attract natural enemies and increase their reproductive

potent i al (Sheeh an 1986, Al t i eri 1987). Interc roppi ng sys tems can

also increase ground coyer which fa vors certain predators such as

carabid and staphylinid beetles, centipede and various arachanids,

and can increase diversity of herbivorous insects, which can serve

as alternative foud sources for natural enemies, making them less

likely to leave when the main pest species are rare (Altier; 1987).

1 n t he present s tudy, the s potted torto i se beet le may have

been regu l ated by an i ncreased number of natural enemi es in the

i ntercropped systems as compared wi th the monocul ture. For

cxample, chalcid wasps and encyrti:1îd hymenopterans that

parasitize the oothecae and larva, respectively (Simon Thomas 1964,

Ka l s hoven 1981), may be more abundant in the i ntercropped sweet

potato, which provides a more enriched microenvironment for their

development, than in the monculture.

The spi der, Lycos a sp., was more abu ndant in the i ntercropped

sys tems th an in the monocu l ture, and numbers i ncred sed over t ime ,

reaching a peak at 56 DAP. Spiders are considered as pioneer

83

-

arthropod species readily colonizing new habitélts (Bishop &

Riechert 1990). ïheir role in the present sweet potato cropping

sys tems was not cl ea rl y defi ned, but 5 pi ders are cornillon ly known as

effective natural enemies (Bishop & Riehert 1990).

The l arger spi der popul at ion in the i ntercropped t reatments

may be, in pa rt, accounted for by a more abündant and di verse

popul at i on of i nsect prey found in these ag roecosys tems, and th i s

would be favorable to the generalist spiders (Riehert & Lockley

1984) .

84

CHAPTER VI

CONCLUSIONS AND RECOMMENDATIONS FOR FURTHER RESEARCH

T

In the present s tudy, i ntercroppi ng sweet pota to wi th either

corn and/or soybean was found to reduce the SPW popul ation, rate of

colonization by SPW, and the associated level of damage to the

sweet potato tubers. Number of tubers and yield were higher,

however, in the sweet potato monoculture.

1 ntercropp i ng w loh corn was mos t eff ect ive from a pes t

man agement poi nt of vi ew, probab l y beeause i t prov i ded a more

significant physical barrier to the movement of the SPW than did

the soybean pla n ts. Moreover f by de 1 ayi ng tuber formé't ion. it may

have made the sweet potato plants less attractlve to the SPW.

Un for t u n a tel y, h 0 w ev e r, th i s r e t a rd a t l 0 n 0 f tub e r f 0 rm a t l 0 n

a1so signi ficantly reduced sweet potato yield, making it unlikely

to be accepted as an acceptable agronomie prnctice by sweet potato

farmers in IriRn Jaya.

Sweet pota to in tercropped wi th soybean yi el ded the second

hi 9 hes t i ncome a fter the sweet potato monocu lture, even thoug h

colonization and number of SPW's were higher than in the corn

mixtures. Thus, further work with soybean may be warranted to find

an appropiate crop ratio and spacing that is both effective in

controlling the SPW and economical1y acceptab1e to the sweet potato

farmers. Such development should take into account the indigenous

knowledge and traditional methods of the sweet potato farmers.

More insect and spider families, and therefore possibly a

grea ter divers i ty of s peci es, occu rred in i nterc ropped sweet pota to

than in sweet potato monocul ture. Popul ations of the phytophagous

spotted tortoise beet1e , Aspidomorpha sp., were lower in the

86

1 ntercropped systems than in the monoculture, but the oppùsi te was

found \'lÎth the predacious spider, Lycosa sp. The lower population

of ASPJ.Qo_mgTJ2hg sp. may be associated w-ith a higher number of

parasites and predators found in the inteï"cropped systems. If

Aspidomorph~ sp. is a threat to sweet patato, it may be controlled

by planting sweet potato with another crop that is not

taxonomically related, and is a non-host plant for this insect.

The larger population of the generalist spider may be related to

the larger number of prey species found in intercropped systems.

The present study is a first attempt to investigate

lntercropping as a potential cultural control strategy for SPW, or

for any other insect pest in Irian Jaya. Although the results are

prellminary, they indicate important directions for further

research. Four topics, in particular, are suggested for further

investigation.

1. Evaluation of thè contribution of the different mechanisms by

wh i ch corn red uces damage by the SPW, e. g., phys i ca 1 barri er,

chemical repellent, retardation of tuber formation, and

provision of a suitable habitat for natural control organisms.

ThlS might lead to further intercroppi ng experiments with

shorter cultivars of corn, shade tolerant sweet potato

cultivars, and different spacing between rows and times of

planting.

? ,- . Effects of the sweet potato crop on the productivity of the

intercrop(s). Again, experimentation with different cultivars

is called for to identify compatibility, and to avoid

87

competitlon and antagonism.

3. Such studies should also take into account both the

nutritional and economic implications of intercropping systems

for local farmers.

4. To increase the chances of adoption by the indigenous people,

it will also be necessary to find cropping patterns that build

on their indigenous knowledge and customs, and that are

compat i b le wi th the; r trad; t i ona l methods of product; on.

88

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105

, Â

APPENDICES

Appendix 1.

Fiel d layout of the experiment

10 Cil.

A c B

c D D

D A

B. c

E A E

~·------------------------_I l III

107

r , j,

1

,

A.

I.

II.

Appendi x 2.

Cost of production for monoculture and intercropped sweet potato

SWEET POTATD MONOCULTURE

OPERATIONAL COST

1. Land preparati on 1.1. Clearing and cutting of grasses and

bushes of 10.000 W @ Rp. 35 ......... 1.2. Ploughing, 10.000 W, Rp ...•.....•... 1.3. Plotting and leveling ................ 1.4. Mounding . . . . . . . . . . . . . . . . . . . .........

2. Planting and fertilizing 2.1. Planting ............................ 2.2. Ferti1izing .........................

3. Maintaining 3.1. Rep1anting . . . . . . . . . . . . . . . . . ......... 3.2. Weeding ............................. 3.3. Hi 11 i ng u~ the soi l •................ 3.4. Lifting t e vines ...................

4. Harvesting ........... Il •••••••••••••••••• 5. C1eaning and washing of tubers ...........

MATERIALS

Rp. 350.000 Rp. 200.000 Rp. 100.000 Rp. 167.500

Rp. 75.000 Rp. 75.000

Rp. 30.000 Rp. 80.400 Rp. 40.200 Rp. 20.000 Rp. 100.000 Rp. 40.000

1. Sweet potato cutting ..................... Rp. 619.750 2. Fertilizer .......••.. ...•• ............... Rp. 101.919

---------------------------TOTA!_ Rp. 2.000.569

B. SWEET POTATD + CDRN

1. OPERATIONAL COST

1. Land prepa rat ion 1. 1. Clearing and cutting of grasses and

bushes, 10.000 M2, @ Rp.35 .......... Rp. 350.000

1. 2. Ploughing, 10.000 W, Rp. 20 ....... Rp. 200.000 1.3. Plotting and leveling . . . . . . ........ Rp. 100.000

2. Planting and fertilizing 2.1. Planting . . . . . . . . . . . . . . . . . . . ........ Rp. 75.000 2.2. Fertilizing . . . . . . . . . . . . . . . . . . . . . . . . Rp. 75.000

108

3. Maintai ning 3. 1. Rep l ant i ng .... . . . . . . . . . . . . . . . . . . . . . Rp. 3.2. Weeding ............................ Rp. 3.3. Hilling up the soil ........... ..... Rp. 3.4. Lifting the vine ........ ........... Rp.

4. Harvesting .............................. Rp. 5. Cleaning and washing of the tubers ...... Rp. 6. Dryi ng and seedi ng of corn .............. Rp.

II. MATERIALS

1. Sweet potato 2. Corn seeds 3. Fertilizer

cuttings .................. . Rp. Rp. Rp.

30. 000 80.400 40.200 20.100

100.500 40.200 75.000

371.850 5.000

85.246

TOTAL Rp. 1.648.496

C. SWEET POTATO + SOYBEAN

1. OPERATIONAL COST

1. Land preparation

2. 3. 4. 5. 6.

Planting and fertilazing .............. . Maintaining ............•............... Harvesting ............................ . Cleaning and washing of the tubers .... . Drying and seeding of the soybean ..... .

II. MATERIALS

1. Sweet potato cuttings .................. . 2. Soybean seeds ...........•....•......... 3. Fertilizer ............................ .

TOTAL

D. SWEET POTATO + CORN + SOYBEAN

1. OPERATIONAL COST

1. Land preparat ion ..................... . 2. Planting and fertilizing ............. . 3. Maintaining .......................•... 4. Harvesting ........................... . 3. Cleaning and washing of the tubers ... . 4. Drying and seeding of soybean and corn.

Rp.

Rp. Rp. Rp. Rp. Rp.

Rp. Rp. Rp.

650. 000

150. 000 170.700 100.500 40.000 75. 000

619.750 5.000

118.125

Rp. 1.924.275

RP. Rp. Rp. Rp. Rp. Rp.

650. 000 150. 000 170.700 100.500 40.200 75. 000

109

II. MATERIALS

1. Sweet potato cuttings ................. Rp. 247.900 2. Corn seeds ............................ Rp. 2.500 3. Soybean seeds ... ........ ...... ........ Rp. 2.500 4. Fertilizer ............................ Rp. 66.088

------------------------TOTAL Rp. 1.505.3ll6

SUMMARY OF THE SWEET POTATO INTERCROPPING PRODUCTION COSTS

Type of sweet potato intercropping system

Production cast

Sweet pûtato monoculture

Sweet potato + Corn

Sweet potato + Soybean

Indonesi an Rupi ah (Rp)

2.000.569

1. 648.496

1.924.275

Canadian dollar (Can. $)'

1,538.89

1,268.07

1,480.21

~ Sweet potata + Carn + Soybean 1.505.388 1,157.99 ---------~---------------------------------------------------------

* In 1989 Cano $ 1 was equal ta Rp.1300,-

110

t

Appendi x 3 . •

Insect and spider families associated with sweet potato croppi fig systems a t 35. 42. 49 and 56 DAP.

A. Insect and spider families associated with the sweet potato cropping systems sampled at 35 DAP.

-----------------------------------------------------------------Order & Familiy of Sweet potato agroecosystem insects & spiders -------------------------------------------

A B C D -----------------------------------------------------------------COLEOPTERA F-:-Chrysome li dae 5 27 18 34 F. Cocci ne 11 i dae 1 4 3 F. Curculionidae 2 1 F. Cassidae 3 1 F. Nitidulidae 2 1 F. Carabidae 2 2 F. Buprestidae HYMENOPTERA r. Argidae 1 2 F. F ormi cac i dae l. 1 8 1

l F. Braconidae 3 4 F. Chalcididae 1 1 3 2 F. Eurytomi dae 1 1 F. Au 1 aei dae 1 1 F. Andrenidae 1 -F. Scelionidae 2 2 HOMOPTERA F. Cicadelidae 8 2 13 F. Delhpacidae 1 1 2 F. Cercopi dae 1 3 F. A~ididae 5 3 HEM! TERA r~-Mi ri dae 2 2 ORTHOPTERA F~---~yrgomorph i dae 2 3 4 F. Acrididae - Acridinae 8 3 3 2 - Cyrtacanthaerinae 13 10 4 7 F. Tetrogi ni idae - Pseudophyll i dae 2 8 - Phaneropterinae 4 14 F. Gryll i dae - Nemobunae 2 1 1 9

111

LEPIDOPTERA F. Pyra 1 i dae 12 2 10 4 F. Sphi ngi dae 2 2 2 2 F. Nymph a li dae 3 3 3 1 F. Noctu i dae 6 DI PTERA F. Phori dae 1 2 F. Lonchopteri dae 4 2 1 F. Asilidae 1 7 F. Bombyl i dae 1 2 F. Empididae 2 2 F. Cono~i dae 2 1 3 2 F. Syrp i dae 4 3 2 1 F. Agromyzi dae 4 73 159 F. Musci dae 2 3 F. Anthomyi i dae 3 1 F. Otti dae 2 3 F. 00 l i ch 0 p 0 d i d a e 2 4 F. Strat i orny; i dae 2 2 F. Tepth ri dae 2 ARANEAE F. Lycos i dae 1 10 56 51

-----------------------------------------------------------------

1 B. Insect and spi der associ ated wi th sweet potato 1. cropping systems at 42 DAP.

.,

Order & Family of i nsects & spi ders

A

Sweet potato agroecosystem

B c o ------------------------------------------------------------------COLEOPTERA F. Chrysome li dae 22 59 37 180 F. Cocci nel idae 1 3 15 25 F. Curcu li oni dae 2 1 2 F. Cassididae 6 3 2 5 F. Carabi dae 5 9 3 HYMENOPT ERA F. Formi caci dae 2 3 2 3 F. Bracon i dae 3 3 F. Chalcididae 7 Il 7 F. Scelionidae 1 2 1 F. Cephi dae 1 2 2 HOMOPTERA F. Ci dade 1; dae 14 19 20 F. De l ph a cid a e 2 3 3 2 F . Acana 1 oni i dae 4 4

112

------ -- ~

HErH PTERA ~ .... r~-PenTatomi dae 13 271

F. Thyreoco r i dae 119 123 F. Lygaei dae 1 2 2 1 F. Mi ri dae 14 342 63 144 F. Coreidae 2 1 F. Reduvi dae 3 3 ORTHOPTERA r-~ Pyr~omorph i dae 5 7 1 1 F. Acndidae - Acrididae 9 3 3 36 - Cyrtacan t hacri da 1 6 8 F. Tetriginidae - Pseudophyll i dae 7 3 7 10 - Phaneropteri nae 1 12 F. Gryll i dae - Oecanthi nae 1 3 - Nemobunae 5 7 6 13 LEPIDOPTERA r.-P-yra 1 i dae 3 1 5 F. Spingidae 2 3 1 F. Nymphal i dae 3 3 F. Noctui dae 3 DIPTERA F. As i 1 i dae 8 3 37 18 F. Bombyl i dae 5 3

l F. Stratiomydae 4 2 F. Rhagi on; dae 2 F. Phori dae 3 5 F. Lonchopteri dae 12 4 F. Therevi dae 4 4 F. Empi di dae 1 8 F. Conohi dae 39 3 9 F. Syrp idae 2 2 1 4 F. Dolichopodidae - 3 1 F. Tephriti dae 6 2 6 F. Agromyzi dae 32 265 211 F.Ottidae F. Muscidae 4 1 4 F. Anthomyi i dae 2 2 MANTODEA 4 3 BLATTARIA 2 ARANEAE r-:-Lycos i dae 38 48 137 247 ----------------------------------------------------------------

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C. Insect and spider associated with sweet potato cropping .. systems collected at 49 DAP .

-----------------------------------------------------------------Order & Fami ly of Sweet potato agroecosystem insects & spiders --------------------------------------------

A B C D ------------------------------------------------------------------COLEOPTERA F. Chrysomel idae 8 47 86 58 F. Cocc;nel idae 4 2 27 24 F. Curcul i oni dae 6 1 5 F. Cassididae 11 5 4 2 F. Bupresti dae 1 F. Carabi dae 5 HYMENOPTERA F. Formi cac i dae 15 9 21 Il F. Braconi dae 4 2 5 F. Chalcididae 3 8 16 4 F. Scelionidae 2 2 3 F. Ichneumon i dae 4 F. Megachi 1 i dae 5 4 6 F. Spheci dae 1 6 HOMOPTERA F. Ci dadell i dae 12 21 45 48 F. Del phaci dae 4 6 5 14

1 F. Acanaloni idae 14 6 F. Ci cadi dae 1 3 5 F. Cercopod i dae 1 - 3 F. Aphididae HEMI PTERA

3 1

F. Pentatomi dae 2 19 133 F. Thyreocori dae 5 - 125 92 F. Lygaei dae 2 4 4 F. Mi ri dae 14 62 131 93 F. Corei dae 6 9 F. Tinfidae 3 2 ORTHOP ERA F. Pyr~omorphi dae 2 28 15 F. Acrl di dae - Acri di dae 39 67 56 44 - Cyrtacanthacri da 6 6 80 23 F. Tetriginiidae

Pseudophyll i dae 4 12 Il - Phaneropteri nae 14 55 27 5 F. Gryll i dae - Oecanth i dae 4 - Nemobunae 4 12 52 26 LEPIDOPTERA F. Plutellidae 5 1 3 3 F. Sphi ngi dae 3 1 1 F. Nympha 1 i dae 5 3 5

~ ,. 114

NEUROPTERA 1 DIP-rERA -r~ As lTdae 7 15 19 22 F. Tipulidae F. Mydi dae F. Stratipmydae 3 1 F. Phori dae 31 9 F. Locho~teridae 2 8 F. Bomby i dae 8 13 7 F. fmpididae 30 16 13 F. Conohi dae 3 F. Syrp i dae 8 26 17 8 F. Pi)unculidae -F. 00 ichopodidae 46 17 7 F. Tephritidae 9 7 2 F. Agromyzidae 52 112 191 F. Se)t i dae 2 F. He epmyz i dae F. Musc; dae 22 28 43 9 F. Anthom~i idae 2 1 1 F. Sa rcop agae

6 MANTODEA 4 ARANEAE f~--Lycos i dae 72 79 246 343 -----------------------------------------------------------------

:1 D. Insect and spider associated with sweet potat croppi ng sys tems at 56 DAP.

------------------------------------------------------------------Order & Family of Sweet potato agroecosys tem insects & spiders --------------------------------------------

A B C D ------------------------------------------------------------------COLEOPTERA F. Chrysomelidae 45 31 313 339 F. Coccinelidae 12 Il 44 52 F. Curculionidae 7 2 2 12 F. Cassididae Il 3 6 6 F. Bupresti dae 1 1 2 F. Carabi dae 2 2 F. Nitidulidae 4 3 HYMENOPTERA F~--Formi caci dae 3 19 14 F. Braconi dae 3 4 8 5 F. Cha 1 ci di dae 2 2 15 5 F. Au 1 aci dae 1 1 1 F. Scelionidae 1 2 5 F. Ichneumonidae 2 1 F. Cyn i pi dae 1 F . Andreni dae 2 . -

115

HOMOPTERA F. Ci cadell i dae 6 17 14 29 • F. De l phaci dae 2 3 7 F. Acana10ni idae 4 14 2 F. Cicadidae 1 3 F. Cocci dae 1 4 HEMI PTERA F. Pentatomi dae 48 24 1693 1276 F. Thryreocoridae 27 12 468 624 F. lygaei dae 3 4 2 2 F. Mi ri dae 86 75 209 396 F. Corei dae 8 3 46 22 ORTHOPTERA F. PyrQomorphidae 3 23 10 F. Acr,didae - Acri di dae 4 9 30 65 - Cyrtacanthacaridae 6 2 125 46 F. Tetriginiidae

Pseudoph; 11 i dae 10 1 14 19 - Phaneropteri dae 19 9 56 45 F. Gry11 i dae - Oecanthi nae 5 32 30 - Nemobunae 27 5 62 23 lEPIDOPTERA F. Sphingidae 3 1 F. Nymphal·: dae 3

1 F. Noctui dae 2 NEUROPTERA 1 DIPTERA F. As il i dae 6 3 4 1 F. Bomby1 i dae 6 5 12 24 F. St rat i omy; da e 4 6 4 F. Rhagionidae 1 F. Phori dae 10 5 27 12 F. lochopteri dae 12 7 23 1 F. Therevi dae 1 1 F. Empididae 7 5 12 4 F. Cono~i dae - - 1 F. Syrp i dae 3 5 5 6 F. Pi ~uncul i dae 1 1 F. Do ;chopodidae 1 4 6 F. Tephritidae 1 4 5 F. Agromyzi dae 4 4 F. Sepsidae 2 F. Muscidae 20 14 15 146 F. Anthomyi i dae 2 1 1 F. Api oceri dae 2 MANTODFA 2 1 BLATTARIA 4 ARANEAE F. lycos i dae 57 12 371 161 -----------------------------------------------------------,.

116