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Pak. Entomol. Vol. 26, No.1, 2004<br />

BIODIVERSITY OF INSECTS ASSOCIATED WITH<br />

SUGARCANE CROP IN FAISALABAD<br />

Adnan Ahmed, Anjum Suhail, Za<strong>in</strong>-ul-Abd<strong>in</strong>, Sohaib Iftikhar and Kashif Zahoor<br />

Department <strong>of</strong> Agri. Entomology, University <strong>of</strong> Agriculture, Faisalabad<br />

ABSTRACT<br />

Studies were carried out <strong>in</strong> three localities (Shahbaz pur, Agriculture University<br />

Faisalabad and Makkuana) on the farmers’ fields. Data were collected on fortnightly basis by<br />

us<strong>in</strong>g hand net, light traps, malaise traps and pit fall traps and were analyzed statistically,<br />

us<strong>in</strong>g Shannon-We<strong>in</strong>er <strong>in</strong>dex <strong>of</strong> diversity. Species richness provides an extremely useful<br />

measurement <strong>of</strong> diversity when a complete catalogue <strong>of</strong> species <strong>in</strong> the community is<br />

obta<strong>in</strong>ed. A total <strong>of</strong> 11720 specimens belong<strong>in</strong>g to different <strong>in</strong>sect orders were captured <strong>in</strong><br />

three localities. About 117 species <strong>associated</strong> <strong>with</strong> <strong>sugarcane</strong> were identified. The diversity.,<br />

maximum diversity, species richness and species evenness <strong>in</strong> three localities were 1.55, 2.0,<br />

0.22 & 0.77 and 1.66, 2.0, 0.17 & 0.83 and 1.75, 2.0, 0.13 & 0.87, respectively.<br />

INTRODUCTION<br />

Species richness provides an extremely useful<br />

measurement <strong>of</strong> diversity where a complete<br />

catalogue <strong>of</strong> species <strong>in</strong> the community is obta<strong>in</strong>ed<br />

(Magurran, 1988).<br />

Biodiversity entails all form <strong>of</strong> biological<br />

entities <strong>in</strong>habit<strong>in</strong>g the Earth-<strong>in</strong>clud<strong>in</strong>g prokaryotes<br />

and eukaryotes, wild plants & animals and<br />

cultivated plants and even genetic material like<br />

seeds and germplasm (Kothari, 1992)<br />

Insects have great potential for understand<strong>in</strong>g<br />

ecosystem as measures <strong>of</strong> ecosystem health, but the<br />

<strong>in</strong>completeness <strong>of</strong> knowledge and the limitation <strong>of</strong><br />

resources <strong>in</strong>crease the difficulty <strong>of</strong> work on <strong>in</strong>sect<br />

<strong>biodiversity</strong>. The formal treatment <strong>of</strong> <strong>biodiversity</strong><br />

and its measures is complex. Despite considerable<br />

<strong>in</strong>terest <strong>in</strong> this subject, the use and application <strong>of</strong><br />

measurement <strong>in</strong>dices is heterogeneous (Williamson,<br />

1995)<br />

About 103 <strong><strong>in</strong>sects</strong> species <strong>associated</strong> <strong>with</strong><br />

<strong>sugarcane</strong> compris<strong>in</strong>g <strong>of</strong> Coleopteran (31 spp),<br />

Dictyoptera (2spp), Diptera (5spp), Hemiptera<br />

(12spp), Homoptera (18spp), Hymenoptera (7spp),<br />

Isoptera (3spp), Lepidoptera (13spp), Orthoptera (9<br />

spp) and one species <strong>of</strong> each <strong>of</strong> Thysanoptera,<br />

Neuroptera and Trichoptera (Kumaras<strong>in</strong>ghe, 1999).<br />

Sugar cane is a highly important cash <strong>crop</strong> and<br />

sugar production <strong>in</strong> the country mostly depends on<br />

this <strong>crop</strong>. It shares <strong>in</strong> value added <strong>in</strong> Agri and GDP<br />

are 6.2% and 1.5% respectively (Annonymous,<br />

2003).<br />

The number <strong>of</strong> eggs, nymphs and adults <strong>of</strong><br />

Pyrilla perpusilla were high <strong>in</strong> July, August and<br />

October (Fernando and Ganehiarachchi, 2000).<br />

Pest activity <strong>of</strong> pest (Root borer) was observed<br />

from January to December, and the population peak<br />

dur<strong>in</strong>g the second fortnight <strong>of</strong> September (Pandya<br />

and Patels, 1998).<br />

The activity <strong>of</strong> the pest (Top borer) was found<br />

spread over the months <strong>of</strong> January to December<br />

<strong>with</strong> a peak population level <strong>in</strong> the second fortnight<br />

<strong>of</strong> May (Pandya and Patels, 1998).<br />

Intensive studies on the population dynamics <strong>of</strong><br />

the scarab pests have sought to understand the cause<br />

<strong>of</strong> outbreaks (Robertson, 1999).<br />

65


Pak. Entomol. Vol. 26, No.1, 2004<br />

Previously no work has been done on the<br />

<strong>biodiversity</strong> <strong>of</strong> <strong><strong>in</strong>sects</strong> <strong>associated</strong> <strong>with</strong> <strong>sugarcane</strong><br />

<strong>crop</strong> <strong>in</strong> Faisalabad. So, it is the need <strong>of</strong> the time to<br />

estimate to what extent man’s exploitation <strong>of</strong> natural<br />

resources has imparted adverse impact on the<br />

<strong>biodiversity</strong> <strong>of</strong> <strong><strong>in</strong>sects</strong>. The present research was<br />

conducted to estimate the <strong>biodiversity</strong> <strong>of</strong> <strong><strong>in</strong>sects</strong><br />

<strong>associated</strong> <strong>with</strong> <strong>sugarcane</strong> <strong>crop</strong> <strong>in</strong> Faisalabad.<br />

MATERIALS AND METHODS<br />

Three localities were selected for the study <strong>of</strong><br />

<strong>biodiversity</strong> <strong>of</strong> <strong><strong>in</strong>sects</strong> <strong>associated</strong> <strong>with</strong> <strong>sugarcane</strong><br />

<strong>crop</strong> <strong>in</strong> Faisalabad. These localities were Shahbaz<br />

pur, Makkuana, University <strong>of</strong> Agriculture.<br />

Collection was done on the farmers fields.<br />

Collection was made randomly by nett<strong>in</strong>g, hand<br />

pick<strong>in</strong>g, pitfall traps, malaise and light traps (one<br />

light trap <strong>in</strong> each locality). Pitfall traps were set<br />

diagonally <strong>in</strong> middle and sides <strong>of</strong> the field after<br />

every 10 foot steps <strong>in</strong> every acre which were<br />

selected randomly. Pitfall traps were “dustb<strong>in</strong>s” <strong>of</strong> 6<br />

<strong>in</strong>ch diameter and 10 <strong>in</strong>ch height, buried <strong>in</strong> the soil.<br />

Each trap was laid <strong>in</strong> such a way that the tips <strong>of</strong> the<br />

trap was flush <strong>with</strong> the surface <strong>of</strong> the ground. A<br />

plastic lid was suspended approximately 4 cm above<br />

the ground level to protect aga<strong>in</strong>st <strong>in</strong>undation dur<strong>in</strong>g<br />

the period <strong>of</strong> heavy ra<strong>in</strong>fall and evaporation <strong>in</strong> direct<br />

sunlight (Kle<strong>in</strong>, 1989). 10 per cent formal<strong>in</strong>e<br />

solution was used <strong>in</strong> these pitfall traps. A total <strong>of</strong> 15<br />

for each census <strong>in</strong> <strong>crop</strong> area were left up to 24 hr.<br />

Sampl<strong>in</strong>g was done for 2 consecutive days <strong>in</strong><br />

each fortnight and total population per month was<br />

counted. The specimens for each and every<br />

collection day were treated separately and were put<br />

<strong>in</strong>to vials for <strong>biodiversity</strong> count.<br />

Identification <strong>of</strong> <strong>in</strong>sect’s species<br />

The collected specimens were stored <strong>in</strong> vials<br />

conta<strong>in</strong><strong>in</strong>g formal<strong>in</strong>e solution and identified to<br />

species level. The identification <strong>of</strong> specimens was<br />

done <strong>in</strong> “Insect Biodiversity and Biosystematics<br />

Research Lab.” Department <strong>of</strong> Agri.Entomology,<br />

University <strong>of</strong> Agriculture, Faisalabad (Pakistan),<br />

<strong>with</strong> the help <strong>of</strong> related taxonomic material. Some<br />

<strong>of</strong> the specimens were identified by compar<strong>in</strong>g<br />

specimens aga<strong>in</strong>st collection <strong>in</strong> Museum <strong>of</strong> CABI<br />

Regional Biosciences Centre, Daata Gunj Bukhsh<br />

Road, Rawalp<strong>in</strong>di.<br />

Diversity Index<br />

The <strong>biodiversity</strong> count was made to estimate<br />

species richness, species evenness and species<br />

diversity (Kikkawa, 1996) by us<strong>in</strong>g Shannon<br />

diversity <strong>in</strong>dex (Shannon, 1948) as follows.<br />

H =<br />

OR<br />

∑<br />

nlogn −<br />

H′<br />

=<br />

n<br />

H′<br />

max = logk<br />

H′<br />

J′<br />

=<br />

H′<br />

max<br />

D = 1−<br />

J′<br />

(pi − In(pi))<br />

k<br />

∑<br />

i<br />

filog fi<br />

H is the diversity; pi is the population <strong>of</strong> ith<br />

species <strong>in</strong> <strong>crop</strong> area. H’ is the diversity <strong>in</strong>dex <strong>of</strong><br />

total number <strong>of</strong> collected specimens, fi is the<br />

proportion <strong>of</strong> ith species, H’max is the maximum<br />

diversity, K is the total number <strong>of</strong> species <strong>in</strong> the<br />

entire <strong>crop</strong> area j’ is the evenness and D represents<br />

dom<strong>in</strong>ance <strong>of</strong> species<br />

RESULTS AND DISCUSSION<br />

The research studies were conducted dur<strong>in</strong>g<br />

March to August <strong>in</strong> 2004. A total <strong>of</strong> 11720<br />

specimens belong<strong>in</strong>g to different <strong><strong>in</strong>sects</strong> orders were<br />

captured represent<strong>in</strong>g 117 species. Diversity,<br />

species richness, species evenness were calculated<br />

by Shannon-We<strong>in</strong>er diversity <strong>in</strong>dex. The evenness<br />

value showed that the whole <strong>of</strong> the <strong>crop</strong> area was<br />

evenly distributed <strong>with</strong> only the dom<strong>in</strong>ance <strong>of</strong> few<br />

species <strong>of</strong> different orders namely Homoptera <strong>with</strong><br />

highest population <strong>of</strong> <strong>sugarcane</strong> plant hopper<br />

(Pyrilla perpusilla, Ot<strong>in</strong>otus oneratus, Perk<strong>in</strong>csiella<br />

sp, Alerolobus barodenesis). Lepidoptera<br />

(Svripophaga nivella, Chilo <strong>in</strong>fuscatellus,<br />

Emmalocera depressella, Acherontia atropos).<br />

Orthoptera (Atractomorpha acutipennis,<br />

Coenagrion puella, Gryllus bimaculatus,<br />

Trigonidium cic<strong>in</strong>deloides, Chrotogonus<br />

trachypterous, Oxya <strong>in</strong>tricata, Euconocephalus<br />

<strong>in</strong>certus, Hedotettix gracilis, Chlaenius quadricolor,<br />

66


Pak. Entomol. Vol. 26, No.1, 2004<br />

Orthrophagus atroplitus, Coleoptera (Calosoma<br />

maderae, Craspendophorus elegans, Orthrophagus<br />

atroplitus, Scrabaeus brahm<strong>in</strong>us, Heteroderes lenis,<br />

Aspidomorpha miliaris, Aulocophora foveicolis),<br />

Hymenoptera (Vespa orientalus, Rhyssa<br />

persuasoria, Formica Spp., Monomorium<br />

m<strong>in</strong>imum.<br />

Table 1: Result <strong>of</strong> Shannon-We<strong>in</strong>er<br />

diversity <strong>in</strong>dex.<br />

Biodiversity<br />

Components<br />

Shahbaz<br />

pur<br />

Makkuana Agriculture<br />

University<br />

Diversity (H) 1.55 1.66 1.75<br />

Max. Diversity 2.0 2.0 2.0<br />

Evenness (J’) 0.22 0.17 0.13<br />

Richness 0.77 0.83 0.87<br />

The value <strong>of</strong> Diversity (1.66) was maximum <strong>in</strong><br />

Makkuana and m<strong>in</strong>imum (1.55) <strong>in</strong> Shahbaz pur.<br />

Maximum Diversity (2.0) was same <strong>in</strong> all three<br />

localities. Evenness was maximum (0.22) <strong>in</strong><br />

Shahbaz pur and m<strong>in</strong>imum (0.13) <strong>in</strong> Agriculture<br />

University. Richness was maximum (0.87) <strong>in</strong><br />

Agriculture University and m<strong>in</strong>imum (0.77) <strong>in</strong><br />

Shahbaz pur.<br />

The temperature was recorded maximum (42.5<br />

o C) <strong>in</strong> the month <strong>of</strong> July and m<strong>in</strong>imum (38.4 o C) <strong>in</strong><br />

the month <strong>of</strong> March. Relative humidity was<br />

recorded maximum (66 %) <strong>in</strong> August and m<strong>in</strong>imum<br />

(27%) <strong>in</strong> May. Maximum ra<strong>in</strong> fall (130 mm) was<br />

recorded <strong>in</strong> the month <strong>of</strong> July and m<strong>in</strong>imum (4.6<br />

mm) <strong>in</strong> the month <strong>of</strong> June.<br />

Homoptera (2170), Hemiptera (939),<br />

Lepidoptera (2140), Coleoptera (1254), Isoptera<br />

(1248) and Orthoptera(1053) were <strong>in</strong> abundance <strong>in</strong><br />

<strong>sugarcane</strong> fields dur<strong>in</strong>g the collection periods<br />

followed by Neuropteran (318), Diptera (1132),<br />

Odonata (324) and Hymenoptera (884). The<br />

maximum <strong>in</strong>sect population was observed <strong>in</strong> the<br />

months <strong>of</strong> July and August because there was<br />

maximum relative humidity (64% & 66%<br />

respectively) and ra<strong>in</strong>fall (130 mm and 60.7 mm,<br />

respectively) <strong>in</strong> July and August.<br />

Table 2:<br />

Months<br />

Meterological data for six months.<br />

Temperature<br />

(C o ) Avg.<br />

Max.<br />

M<strong>in</strong>.<br />

Relative<br />

Humidity<br />

(%) Avg.<br />

Ra<strong>in</strong>fall<br />

(mm)<br />

March 38.4 24.7 31 19.0<br />

April 38.6 24.9 30 16.0<br />

May 40.2 26.4 27 16.4<br />

June 42.5 29.7 44 4.6<br />

July 39.8 28.6 64 130<br />

August 39.4 28.1 66 60.7<br />

The population <strong>of</strong> <strong>sugarcane</strong> leaf hopper<br />

<strong>in</strong>creased from March to April and the curve was<br />

dim<strong>in</strong>ish<strong>in</strong>g uptill June show<strong>in</strong>g that there was a<br />

marked decrease <strong>in</strong> population <strong>in</strong> the month <strong>of</strong> June<br />

at high temperature (42.5 o C) and low relative<br />

humidity (44%). Similarly the population <strong>of</strong><br />

<strong>sugarcane</strong> stem borer, <strong>sugarcane</strong> top borer,<br />

<strong>sugarcane</strong> root borer and <strong>sugarcane</strong> black bug<br />

<strong>in</strong>creased from March to April and there was a<br />

marked decrease <strong>in</strong> population <strong>of</strong> these pests <strong>in</strong> the<br />

month <strong>of</strong> June at high temperature (42.5 o C) and less<br />

relative humidity (44%). But the population <strong>of</strong><br />

<strong>sugarcane</strong> whitefly did not show a marked <strong>in</strong>crease<br />

<strong>in</strong> the months <strong>of</strong> July and August due to high<br />

relative humidity (66%). The population <strong>of</strong> whitefly<br />

showed a little <strong>in</strong>crease <strong>in</strong> the month <strong>of</strong> May<br />

because <strong>of</strong> low relative humidity (27%).<br />

The ETL <strong>of</strong> Pyrilla perpusilla is 2 adults or<br />

nymphs per leaf and the observed (5 per leaf)<br />

population which was much higher than the<br />

predeterm<strong>in</strong>ed ETL. So, Pyrilla perpusilla is the<br />

potential pest dur<strong>in</strong>g collection period and<br />

67


Pak. Entomol. Vol. 26, No.1, 2004<br />

maximum population dur<strong>in</strong>g July-August. The<br />

predeterm<strong>in</strong>ed ETL <strong>of</strong> borers is 10% attacked<br />

plants, the observed damaged plants were also 10%<br />

dur<strong>in</strong>g the collection period (April & May and July<br />

& August), maximum damage was dur<strong>in</strong>g the<br />

months <strong>of</strong> July & August.<br />

2500<br />

2000<br />

1500<br />

1000<br />

500<br />

0<br />

Collembola<br />

Odonata<br />

Orthoptera<br />

Dermapter<br />

a<br />

Neutoptera<br />

Isoptera<br />

Hemiptera<br />

Homoptera<br />

Coleoptera<br />

Lepidopter<br />

a<br />

Hymenopte<br />

ra<br />

Diptera<br />

CONCLUSION<br />

• March & April and July & August are the four<br />

critical months for the <strong>sugarcane</strong> <strong>crop</strong>.<br />

• All three types <strong>of</strong> borers (top borer, stem borer,<br />

root borer) are potential pests as their ETL are<br />

<strong>in</strong> accordance <strong>with</strong> the predeterm<strong>in</strong>ed ETL.<br />

Also the ETL <strong>of</strong> <strong>sugarcane</strong> plant hopper (Pyrilla<br />

perpusilla) was higher than the predeterm<strong>in</strong>ed<br />

ETL. So Pyrilla is also a potential pest <strong>of</strong><br />

<strong>sugarcane</strong> <strong>crop</strong>.<br />

• Control strategies should be applied on the 1 st<br />

fortnight <strong>of</strong> March and last fortnight <strong>of</strong> April.<br />

Series1<br />

Insect Numbers<br />

Fig 1: Insect fauna <strong>of</strong> <strong>sugarcane</strong> <strong>in</strong><br />

Faisalabad<br />

6000<br />

5000<br />

4000<br />

3000<br />

2000<br />

1000<br />

0<br />

March<br />

April<br />

May<br />

June<br />

Months<br />

July<br />

August<br />

Series1<br />

Fig. 2: Insect population <strong>in</strong> different Months<br />

Population size<br />

1400<br />

1200<br />

1000<br />

800<br />

600<br />

400<br />

200<br />

0<br />

Pest population <strong>in</strong> different Months<br />

March<br />

April<br />

May<br />

June<br />

July<br />

August<br />

Months<br />

top borer<br />

stem borer<br />

root borer<br />

leaf hopper<br />

Fig.3: Pest population <strong>in</strong> different Months<br />

REFERENCES<br />

Andersen,A.N., J.A. Ludwig, L.M. Lowe and<br />

D.C.F. Rentz, 2001. Grasshoppers <strong>biodiversity</strong><br />

and bio<strong>in</strong>dicators <strong>in</strong> Australian tropical<br />

savannas. Austral. Ecol., 26(3): 213-222.<br />

Annonymus, 2003. Economic survey <strong>of</strong> Pakistan,<br />

2002-03.<br />

Gasm. G. and I.V.S. Fernando, 2000. Population<br />

dynamics <strong>of</strong> the <strong>sugarcane</strong> plant hopper (Pyrilla<br />

perpusilla) <strong>in</strong> the wet zone <strong>of</strong> Sri Lanka.<br />

Tropical. Sci., 40: 3, 144-153: 7 ref.<br />

Kothari, A., 1992. The Biodiversity Convension: an<br />

Indian viewpo<strong>in</strong>t. Santuary, 12 (3): 34-43.<br />

Kumaras<strong>in</strong>ghe, N.C., 1999. Insect fauna <strong>associated</strong><br />

<strong>with</strong> <strong>sugarcane</strong> plantations <strong>in</strong> Sri Lanka<br />

Division <strong>of</strong> Pest Management, Sugarcane<br />

Research Institute, Uda Walawe 70190, Sri<br />

Lanka.<br />

Kikkawa, J., 1996. Complexity, Diversity and<br />

Stability. In Community ecology: pattern and<br />

process. Blackwell Scientific Publication,<br />

Melbouren. Pp. 41-65.<br />

Kle<strong>in</strong>, B. C., 1989.Effect <strong>of</strong> forest fragmentation on<br />

dung and carrion beetle communities <strong>in</strong> central<br />

Amazonia. Ecol., 70 (6): 1715-1725.<br />

68


Pak. Entomol. Vol. 26, No.1, 2004<br />

Magurran, A. E., 1988. Ecological Diversity<br />

and Management. Pr<strong>in</strong>ceton University<br />

Press, Pr<strong>in</strong>ceton, NJ. In: Insect Ecology:<br />

An Ecosystem Approach. Academic<br />

Press. USA. pp.221-247.<br />

Robertson et al. 1999. Comparative review<br />

<strong>of</strong> population dynamics <strong>of</strong> scrab pests.<br />

Sugar Research and Development<br />

Corporation, P.O. Box 2151, Innisfail,<br />

old, 4860, Australia.<br />

Shannon, C.E. 1948. A mathematical theory<br />

<strong>of</strong> communication. Bell System tech. J.,<br />

27 : 37-423, 623-656.<br />

Williamson, M. 1995. Species diversity <strong>in</strong><br />

ecological communities. Pp. 325-336.<br />

In: Barlett, M. S. and R. W. Horns<br />

(eds.). The Mathematical theory <strong>of</strong> the<br />

dynamics <strong>of</strong> biological populations.<br />

Academic Press. London.<br />

Wilson, E.O., 1992. The diversity <strong>of</strong> life.<br />

Norton. New York, U.S.A.<br />

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