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    List of Odonata in Upland Paddy From Northern SumateraAmeilia Zuliyanti Siregar1, Che Salmah Md. Rawi2, and Zulkifli Nasution3

    1Postgraduate Student in School of Biological Sciences University Science Malaysia2School of Biological Sciences University Science Malaysia

    3Dept. Agrotechnology Universitas Sumatera Utara

    [email protected], [email protected]

    ABSTRACT

    Odonata community are considered effective predators to control pests organisms in

    rice fields. In the upland ricefields Manik Rambung Village in Northern Sumatera

    (Simalungun District) during 2008-2009, 19 species, 3 families, and 2 sub-orders of

    Odonata were collected and evaluated. The higher composition recovered 2 seasons

    (dry and wet) showed in Zone A (518 individuals), then followed by zone B (376

    individuals), and the lower score recorded from zone C (298 individuals). Sub-orderZygoptera separate in family Coenagrionidae (4 species), such as Pseudagrion

    microcephalum, Ischnura senegalensis, Agriocnemis femina, A. pygmaea; then

    family Gomphidae (2 species), consist of Ictinogomphus acutus and Gomphidia

    abbotti; while Anisoptera devided family Libellulidae (8 species) such as

    Potamarcha congener, Orthetrum sabina, Diplacodes trivialis, Crocothemis servilia,

    N. terminata, N. ramburii, Tholymis tillarga, and Pantala flavescens. However,

    distribution of Odonata were fluctuated in 3 plots (lowland, terrace, and control).

    Keywords: List, Odonata, Upland, Rice Field, North Sumatera.

    ABSTRAK

    Komunitas Capung termasuk pemangsa efektif untuk mengontrol organisme hama

    tanaman padi. Pada padi dataran tinggi di Desa Manik Rambung, Sumatera Utara

    (Kabupaten Simalungun) selama tahun 2008-2009, 19 spesies, 3 famili, dan 2 sub-

    ordo Capung dikoleksi dan dievaluasi. Komposisi tertinggi dalam 2 musim (panas dan

    hujan) menunjukkan ditunjukkan di zona A (518 individu), diikuti oleh zona B (376

    individu), dan terendah tercatat pada zona C (298 individu). Sub-ordo Zygoptera

    terbagi atas famili Coenagrionidae (4 spesies), yaitu Pseudagrion microcephalum,

    Ischnura senegalensis, Agriocnemis femina, A. pygmaea; kemudian famili

    Gomphidae (2 spesies), terdiri atas Ictinogomphus acutus dan Gomphidia abbotti;

    sedangkan Anisoptera terbagi atas famili Libellulidae (8 spesies) seperti Potamarcha

    congener, Orthetrum sabina, Diplacodes trivialis, Crocothemis servilia, N. terminata,

    N. ramburii, Tholymis tillarga, dan Pantala flavescens. Bagaimanapun, distribusi

    capung berfluktuasi pada 3 plot (dataran rendah, berteras, dan kontrol).

    Kata Kunci: Daftar, capung, dataran tinggi, sawah padi, Sumatera Utara.

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    INTRODUCTION

    Rice is one of the three major cereal crops, the others are wheat and corn. Unlike

    these latter, rice is grown largely in seasonally flooded fields. Rice is grown

    predominantly in the tropics and subtropics. De dutta (1987) describes the increase

    has been achieved largely by greater mechanization of farming, higher yielding

    varietes of rice, high levels of fertilizer use and widespread use of pesticides and

    herbicides.

    Tropical rice field usually have a particulary diverse insect fauna which serve as an

    important food source for fishes (Fernando, 1993). Based on the latest finding by Orr

    et al (2004), the Indonesian odonates fauna comprises about 750 species. They

    include zygopterans and anisopterans. Libellulidae is the most dominant family found

    in various ecosystems in Indonesia and Malaysia (Che Salmah et al., 1998). In

    Cambodia, 24 species of Odonata were recorded day trips to the Siem Reap area in

    lowland areas of Cambodia (Orr, 2005). There were at least 14 species of rice field

    Libellulidae (Odonate) in Northern Peninsular Malaysia (Che Salmah, 1996),

    Gunnathilagaraj et al (1999) recorded 16 species of Odonata in rice fields of Tamil

    Nadu, India. Barrion & Litsinger (1994) listed 14 species of Odonata in rice fields ofAsia and Africa, and 19 species of dragonflies (Odonata) in Thailand (Asahina, 1976),

    one of important group of freshwater invertebrates in the rice fields. The carnivorous

    and voracious odonate larvae occupy at te apex of food chain of invertebrate life.

    Arai (1996) has discussed the cycling of organic and inorganic materials in modern

    rice farming in Japan, which treats it as an industry, as a threat to ecological stability

    and contrary to the long-term goals of human welfare. Succesion of the insect

    community structures in rice fields follows the patterns of water availabilty and

    phrases of rice growth (Heckman, 1974). While Benke (1978) noted that predation by

    invertebrates was one of the primary determinants of community structure and

    production of aquatic insects. Odonates are striking aquatic and aerial component of

    wetland environment, in term of both biomass and their influence as predators.

    Two major factors threaten the existence of dragonflies in their natural environments

    in Indonesia especially in North of Sumatra. Firstly, the intensive use of pesticides in

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    rice fields had tremendously reduced the diversity of dragonfly fauna as well as other

    rice pest predators (Heckman, 1979; Barrion & Litsinger, 1994). Secondly, the

    destruction of fresh water habitats due to industrializations and urban development

    destroyed numerous dragonfly breeding habitats. Despite these many species

    occurring in this country, very little information has been published on biological and

    ecological aspects of Indonesia fauna.

    MATERIALS AND METHODS

    Odonata were sampled from a ten ha rice field plot in Manik Rambung village in the

    Simalungun district, North of Sumatera. The area is located at 253 52.8N and 99

    0024.4E, about 90 km from Medan City at 594 - 602 meter above sea level (asl)

    (Figure 1). Thetemperature in this place ranged between 23 and 37C. This area is

    loated in a dry zone with a rainfall of 10.7 to 16. 4 mm in a year. The rice fields

    received water for rice planting mainly from the Siborna dam, about 75 km North of

    Simalungun. The area which borded by main road in the west and mini forest in the

    southeast. Scattered human settlements are found in the area. Usually two rice crops

    were grown in a year. The District Office of Agriculture Simalungun advises the

    farmers in this district on rice cultivation schedules. Rice cultivation in this field was

    partly mechanized and pesticides were minimally used.

    Rice Field Phases

    Rice Field Phases

    The six phases was defined according to shaded water areas and physical conditions

    of the field adopted from Mogi & Miyagi (1990). A fallow field phase (FI),

    uncultivated and filled with short but dense hygrophilous weeds, such as Eleocharis

    tetraquera. The plough field phase (PII) which is slightly undulated due to the

    ploughing process, and tyre tracts left by the tractors. Transplantation phase (TIII)

    with transplanted approximately 30 cm high. The water level could reach up to 5-40

    cm. A middle field = tiller phase (TIV), the rice plants have completed tillering but

    yet to eared. A mature field phase (MV) has rice plants which completly shade the

    water surface. It starts when the plants ear, produce flower panicles, develop grains

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    until the yellowing of the grains. A Preharvest phase (PVI) is usually drained to

    hasten ripening of grains to facilitate harvesting of rice.

    Collection of Odonata Larvae

    Sampling commenced in August 2008 until to August 2009. The areas studied were

    devided into 3 rice fields (plots), consisting of lowland (A), terrace (B), and control

    (C) in the rice fields. Thirty Odonata samples were collected every two weekly from

    each field along it leeves. Combine technique sampler (Core and Sweeping net) were

    used sampling of Odonata. A mesh size of 30-45 cm, depth 80 cm were suitable to

    sample odonate and was used throughout the study. The Odonata were identified

    using keys of Kumar (1973a, 1973b), Asahina (1976), Chowdury & Akhteruzzaman

    (1981), Shanti (1998), and Orr (2004). In this study, we are compare composition in 2

    seasons rice culture practice (dry and wet). The insecticide using Matador and Mipsin,

    then herbicide were Rhodiamin and Ally. The farmers given fertilizer NPK twice in

    every season planting paddy, exception plot C is one time.

    RESULTS AND DISCUSSIONS

    RESULTS

    Compositions of adults Odonata are shown in the Table 1 and Table 2 calculated

    biological diversity indices of odonate in upland rice fields, Manik Rambung.

    Table 1 Compositions of Odonata in rice fields (average number from 2 season),

    Manik Rambung, North Sumatera.A=lowland rice plots; B=terrace rice

    plots, C=control rice plots.

    Species A B C

    Dry Wet Dry Wet Dry Wet

    Zygopteran

    Coenagrionidae

    Argiocnemis rubescens

    Agriocnemis femina

    A.pygmaea

    Ischmura senegalensis

    Pseudagrion microcephalum

    P.pruinosum

    P. rubriceps

    3

    61

    26

    16

    0

    2

    2

    4

    78

    38

    20

    5

    2

    0

    2

    54

    19

    21

    3

    2

    0

    4

    80

    33

    15

    6

    3

    0

    1

    25

    22

    11

    1

    2

    0

    3

    31

    17

    3

    1

    1

    0

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    Anisopteran

    Gomphidae

    Ictinogomphus acutus 2 0 1 2 0 0

    Libellulidae

    Acisoma panarpoides

    Crocothemis serviliaLibellulidae

    Diplacodes trivialis

    Neurothemis fluctuans

    N.terminata

    Orthetrum sabina

    O.testaceum

    Pantala flavescens

    Potomarcha congener

    Tholymisaurora

    T. tillarga

    4

    5

    3

    7

    1

    76

    7

    30

    1

    3

    5

    0

    5

    4

    2

    1

    71

    0

    33

    0

    0

    1

    3

    2

    2

    4

    1

    33

    1

    23

    4

    3

    6

    0

    5

    1

    1

    1

    67

    2

    23

    1

    0

    0

    0

    2

    1

    8

    3

    54

    5

    22

    2

    0

    3

    0

    0

    1

    3

    0

    57

    1

    18

    0

    0

    0

    Total Zygoptera 110 147 101 141 62 56

    Total Anisoptera 144 117 83 51 100 80

    Total number of odonata 254 264 184 192 162 136

    Total number of potential

    preys

    629 429 183 1064 813 186

    Description of Odonata

    They were divided two orders, such as Zygoptera and Anisoptera. Zygoptera separte

    in family Coenagrionidae (4), such as Pseudagrion microcephalum, Ischnura

    senegalensis, Agriocnemis femina, A. pygmaea; then family Gomphidae (2), consist

    of Ictinogomphus acutus,Gomphidia abbotti; while Anisoptera devided family

    Libellulidae (8) such as Potamarcha congener, Orthetrum sabina, Diplacodes

    trivialis, Crocothemis servilia, N. terminata, N. ramburii, Tholymis tillarga, and

    Pantala flavescens.

    Fluctuations suborder Odonata consist of Zygoptera and Anisoptera in rice field

    shown in figure 1 (lowland), figure 2 (terrace), and figure 3 (control).

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    0

    200

    400

    600

    800

    1000

    1200

    Ag Sp Oc No De Ja Fe Ma Ap Ma Jn Jl Ag

    2008 Month 2009

    Numberin

    di

    Zygoptera Anisoptera

    Figure 1. Fluctuations sub-order Odonata (Zygoptera and Anisoptera) in lowland

    0

    100

    200

    300

    400

    500

    600

    700

    800

    900

    Aug Sep Oct Nov Dec Jan Feb Mar Apr May Jun Jul Aug

    2008 Month 2009

    Individuals/2

    Zygoptera Anisoptera

    Figure 2. Fluctuations sub-order Odonata (Zygoptera and Anisoptera) in terrace

    0

    100

    200

    300

    400

    500

    600

    700

    Aug Sep Oct Nov Dec Jan Feb Mar Apr May Jun Jul Aug

    2008 Month 2009

    Numberindiv

    idu

    2

    Zygoptera Anisoptera

    Figure 3. Fluctuations sub-order Odonata (Zygoptera and Anisoptera) in control

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    DISCUSSIONS

    The Odonate in rice field of Manik Rambung, North of Sumatra were quite diverse,

    consist of 3 families, 14 genera, and 19 species. Ghahari et al (2009) recorded 30

    species from 19 genera and 8 families of Odonata were collected and evaluated.Meanwhile Kandibane et al (2007) revealed the inventory of 12 Odonata with 9

    species dragonflies and 3 species damselflies. Then Ansori (2006) recorded 4 species

    (Ortetrum sabina, Crocothemis servilea, Neurothemis terimata, and Anaciaeshna

    jaspidea) in some fields in Bandung, Indonesia. However, the densities of family

    Gomphidae Ichtinogomphus acutus was much lower which recorded in this study.

    Minimum pesticide application as used in this rice field plots had proven no harmful

    effect on the odonates.

    Fiften families insects were also recorded by Heckman (1974, 1979) in rice fields of

    Laos and Thailand that were completly free of pesticides. Similar number of taxa

    were collected in the Phillipines (Mogi & Miyagi, 1990). The existence of odonata in

    the rice field was totally dependent on the availability of water. Temporary drying

    especially in rain fed rice fields was a major factor that reduced the abundance of

    most insect communities (Mogi, 1993). However, odonata is the largest insect order,

    which is entirely predaceous in rice ecosystem. Both naiads and adults are the

    voracious predators on other insect (Krishnasamy et al., 1983).

    Fluctuation Odonata (zygoptera and anisoptera) quite similar in lowland (A) and

    terrace zones (B). Only in control zone (C), the farmers given fertilizer NPK one

    times in rice fiels and without using pesticide.We are assumption the lower population

    of Odonata related and depend to microhabitat, food source, and environment

    unsuitable for them. However, odonata is the largest insect order, which is entirely

    predaceous in rice ecosystem. Both naiads and adults are the voracious predators on

    other insect (Krishnasamy et al.,1983). Families Libellulidae and Coenagrionidae are

    predators. Many species of they are aggressive, eating on most of other insects.

    Cannibalistic libellulids consume all types of aquatic species of suitable sizes and

    textures (Pritchard, 1964; Thompson 1978; Folsom & Collins, 1984, Blois, 1985)

    such as corixids (Folsom, 1980) and Anopheles mosquitoes.

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    Minimum insecticide application using Matador and Mipsin, then herbicide used by

    Rhodiamin and Ally in manik Rambung for two zones, lowland and terrace. Arai

    (1996) has discussed the cycling of organic and inorganic materials in modern rice

    farming in Japan, which treats it as an industry, as a threat to ecological stability and

    contrary to the long-term goals of human welfare. Succesion of the insect community

    structures in rice fields follows the patterns of water availabilty and phrases of rice

    growth (Heckman, 1979). Odonata are striking aquatic and aerial component of

    wetland environment, in term of both biomass and their influence as predators. Then

    large amount of fertilizers and herbicides were applied to the actively growing rice

    plants. Nutrients availability coupled with high penetration of sunlight resulted in high

    production of phytoplankton (Ali, 1988). The abundance of food resulted in

    proliferation of prey species which eventually led to an increase in predator

    abundance, it has been reported that the mean total density of macroinvertebrates was

    positively correlated with the densities of predators such as odonates and predatory

    midges (Thorp & Cothran, 1984).

    The abundance of relatively diverse animal community in this rice field implied a

    continuous availability of preys in this habitat. Although factors such as prey

    availability and refugia determined the actual preys available to the predaotors,

    mortality due to starvation was presumably uncommon for most predator species.

    Families Libellulidae and Coenagrionidae are predators. Many soecies of them are

    aggressive, eating on most of other insects. Cannibalistic libellulids consume all types

    of aquatic species of suitable sizes and textures (Chutter 1961, Pritchard 1964;

    Thompson, 1978; Folsom & Collins, 1984; Blois 1985) such as corixids (Folsom,

    1980) and Anopheles mosquitoes.

    In this study libellulids appeared to be the most important predators due to their high

    population densities as compared to other predators. Neverheless dysticids, hydro-

    philids notonectids and damselfly larvae had caused 89% mortality of mosquito larvae

    in artificial ponds (McDonalds & Buchanan, 1981). Therefore the prey-predator

    interactions play an important role in regulating the community of aquatic insects in

    this rice field.

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    ACKNOWLEDGMENT

    This research was funded in National Strategic Donation by Ministry of Education

    Higher Republic of Indonesia. We thank some farmers, Mr. Silalhi, Mr. Napitupulu,

    Mr. Sinaga, and Mr. Boy Risman Silalahi for field assistance.

    REFERENCES

    Ali BA. 1988. Water quality in rice fields and swamp ponds and its relationship to

    phtoplankton growth in rice field fish culture system. Trop. Ecol. 29: 63-70.

    Arai Y. 1996. Adapatation of red dragonflies in Japanese paddy fields. Thre N. Insects 31 (8):23-26.

    Asahnia S 1979). An illustrated key to the dragonflies found in the padddy field of Thailand.

    IABCR-NEWS No.4.

    Barrion AT & JA Litsinger. 1994. Taxonomy of rice insect pests and their arthropods

    parasites and predators. In Heinrichs EA (Ed.). Biology and management of rice

    insects. Wiley Eastern Limited. New Age International Limited, New Delhi. Pp. 13-

    359.

    Benke AC. 1978. Interactions among cooexisting predators: a field experiment with dragonfly

    larvae.J. Anim. Ecol. 47: 335-350.

    Blois C. 1985. The larval diet of three anisopteran (Odonata) species. Freshwat. Biol. 15: 505-

    514.

    Che Salmah MR, Hasan STS, Abu Hassan A & Ali AB. 1998. Influence of physical and

    chemical factors on the larval abundance ofNeurothemis tullia (Drury) (Odonata:

    Libellulidae) in a rain fed rice field.Hydrobiologia 389: 193-202.

    Che Salmah MR. 1996. Some aspect of biology and ecology ofNeurothemis tullia (Drury)

    (Odonata: Libellulidae) in laboratory and rain fed rice field in Peninsular Malaysia.

    Ph.D thesis, Universiti Pertanian Malaysia, Serdang, Selangor.

    Corbet PS. 1962. A biology of Odonata. London. HF and Witherby Ltd.

    Corbet PS. 1980. A biology of Odonata.Ann.Rev.Entomol. 25: 187-217.

    Chutter FM. 1961. Certain aspects of the morphology and ecology of the nymphs of several

    species of Pseudagrion Selys (Odonata).Arch. Hydrobiol 57: 430-463.

    Fernando CH. 1993. Rice field ecology and fish culturean overview. Hydrobiologia 259: 91-

    113.

    Folsom TC. 1980. Predation ecology and food of the larval dragonfly Anax junius(Aeshenidae). Ph.D thesis, University of Toronto, Canada.

    9

  • 7/27/2019 Seminar PEI-UGM 2010

    10/10

    Folsom TC & Collins C. 1984. The diet and foraging behaviour of the larval dragonfly Anax

    junius (Aeshenidae) with assessment of the role of refuges and prey activity. Oikos

    42: 105-113.

    Gunathilagaraj K, RP Sounsarajan, N Chitra & M. Swamiappan. 1999. Odonata in thye rice

    fields of Coimbatore.Zoos Print J. 14: 43-44.

    Heckman CW. 1974. The seasonal succession of species in a rice paddy in Vientiane, Laos.

    Int.Revue ges.Hydrobiol. 59 (4): 489-507.

    Heckman CW. 1979. Rice field ecology in north-eastern Thailand. The Hague: Junk.

    Krishnasamy N, OP Chautian & RK das. 1983. As some common predators of rice insects

    pests in Assam, India. IRRN 9: 15-16.

    Kumar A & V. Khanna. 1983. A review of the taxonomy and ecology of Odonata larvae from

    India. Oriental Insects 17: 127-157.

    Mcdonal G & Buchanan A. 1981. The mosquito and predatory insect fauna inhabiting

    freshwater ponds, with particular reference to Culex annulitrostris Skuse (Diptera:

    Culicidae).Aust.J.Ecol. 6: 21-27.

    Merrit RW & Cummins KW. 1984. An introduction to the aquatic insects of North America.

    Dubuque, Iowa: Kendall/Hunt Publ.

    Mogi M. 1993. Effect of intermittent irrigation on mosquitoes (Diptera: Culicidae) and

    larvivarous predator in rice fields.J. Med. Ent. 30 (2): 309-319.

    Mogi M & Miyagi I. 1990. Colonization of rice fields mosquitoes (Diptera: Culicidae) andlarvivorous predators in asynchronous rice cultivation areas in the Phillipines. J.

    Med. Entomol. 27 (4): 530-536.

    Orr AG. 2005. Dragonflies of Peninsular Malaysia and Singapore. Natural History

    Publications (Borneo), Malaysia. Pp.1-125

    Pearson WD & DR Franklin. 1968. Some furher factors affecting drift rates of Bactis and

    Simulids in large river.Ecology 4: 75-81.

    Pritchard G. 1964. The prey of dragonfly larvae (Odonata: Anisoptera) in ponds in northern

    Alberta. Can. J.Zool.42: 785-800.

    Shanti Susanti. 1998. Mengenal Capung. Puslitbang Biologi-LIPI, Jakarta. Pp.1-81.

    Thompsons DJ. 1978. The natural prey of larvae of the damselfly, Ischnura elegans

    (Odonata).Freshwat.Biol. 8: 377-384.

    Thorp JH & Cothran ML. 1984. Regulation of freshwater community structure at multiple

    intensities of dargonfly predation. Ecol 65 (5); 1546-1555.

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