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[biodiv] New notification from Biodiversitas Journal of Biological Diversity

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Ayu Astuti <[email protected]> Sun, Aug 8, 11:06 PM to me

You have a new notification from Biodiversitas Journal of Biological Diversity:

You have been added to a discussion titled "Pre-review" regarding the submission "A manuscript Incidence of banana leaf roller and diversity of it is parasitoids in Central Sulawesi, Indonesia".

Link: https://smujo.id/biodiv/authorDashboard/submission/9155 Ahmad Dwi Setyawan

Shahabuddin Saleh <[email protected]> Thu, Aug 12, 1:55 PM to Ahmad

Dear Editor Biodiversitas,

Attached is the revised version of our manuscript. It has been improved and formatted according to the GFA Biodiversitas and sending also through the above link. We hope it has met the journal requirements.

Best regards

~~~~~~~~~~~~~

Shahabuddin Saleh

Entomologist,

Department of Agrotechnology

Faculty of Agriculture, University of Tadulako

Jl. Soekarno Hatta KM 9 Palu, Sulawesi Tengah, Indonesia 94118.

Email: [email protected]; [email protected]

Website: http://stafsite.untad.ac.id/shahabuddin/; https://untad.academia.edu/shahabuddinsaleh

 

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Incidence of banana leaf roller and diversity of it is parasitoids in

1

Central Sulawesi, Indonesia

2

FLORA PASARU1, MOHAMMAD YUNUS1, MOH. HIBBAN TOANA1, NUR EDY1, SHAHABUDDIN SALEH1♥

3 1Plant Pests and Diseases Department, Agriculture Faculty, Tadulako University, 4

Jl. Soekarno Hatta Km. 9 Palu 94118, Sulawesi Tengah, Indonesia 5

Tel. +62 813-4124-9244, Fax.: +62-451-429738, email: [email protected] 6

7 xxx

Abstract. Indonesia is still facing banana losses due to the leaf roller (Erionoata thrax). As a native insect of Southeast Asia, this pest 8

actively destroys the Musa spp.ecies in a specific favorable environmental situation. Therefore, aA survey was done to measure the 9

incidence of banana leaf roller (BLR), diversity and performance of it is parasitoids, and analyze their relationship with the 10

environmental factors as well. The pra imago stages of BLR were collected at different altitudes and banana varieties in Central 11

Sulawesi, Indonesia, and transported to the laboratory for rearing and parasitism observation. The study revealed that the incidence of E.

12

thrax in the surveyed locations varied from 28.6 % to 85.8 %, whereas the parasitism level of the BLR parasitoids was in the range of 13

0.0 to 22.1 %. A total of nine parasitoids of BLR dominated by Hymenoptera were recorded, i.e., Agiommatus sumatraensis, Pediobius 14

erionoataea, Ooencyirtus pallidipes, Brachymeria lasus, Brachymeria thracis, Cotesia erionatae, Xanthopimpla gampsura, Palexorista 15

solennis, and Casinaria sp. Among them, B. lasus was the most abundant, widely distributed, and had the highest parasitism rate. Of all 16

environmental factors assessed by using the Generalized Linear Model (GLM), rainfall, altitudes, and banana variety showed correlation 17

and significantly affected the incidence of BLR. Our study figured out that BLR infestation is a major problem in Central Sulawesi.

18

Nevertheless, the presence of parasitoids recorded in this study may potentially be used as the biological control.

19

Keywords: banana skipper, BLR parasitoid diversity, parasitism, environmental factorsweathers effect 20

Running title: Banana skipper and it is parasitoids 21

INTRODUCTION 22

Bananas mostly have mostly been planted in tropical countries. In Indonesia, it is not only developed by a big 23

plantation company but alsoand as a garden plant. Banana occupiesying first place among other fruits in terms of 24

distribution, area of planting, production, and as the most desirable fruits (Suyamto et al. 2005). However, there are some 25

limiting production factors of the banana, including pest infestation. One of the main pests of bananas is the banana 26

skipper, also known as the banana leaf roller (BLR). There are two species of skippers of the genus Erionota Mabille 27

(Lepidoptera: Hesperiidae) that feed on banana leaves recorded in Southeast and South Asia that isnamely E.thrax L. and 28

E. torus Evans (Cock 2015;, Irulandi et al. 2018). The imago oaf these two species can usually be distinguished by the 29

wing variations where the forewing of E. thrax has a straight outer margin and acute apex. In contrast, while the forewing 30

of E. torus is more convex in the outer margin and rounded apex (Poorani et al. 2020). The taxonomy, distribution, food 31

plants, and natural enemies of the BLR have been decisively reviewed by Cock (2015).

32

BLR is a slightly important pest in Asia. However, during the last two decades, the outbreak of BLR expanded and 33

caused serious defoliators (Cock 2015, Poorani et al. 2020). The feeding activity of the BLR larva causes considerable 34

damage to the banana's foliage by rolling the leaf while feeding on it. Although banana plants can tolerate up to 20%

35

defoliation, a heavy infestation can damage the whole banana leaf, leaving only the midrib intact. At 50 %, defoliation by 36

BLR larva will cause about 28 % of yield losses (Cock 2015). The lower yields of infested banana by BLR is due to the 37

delayed fruit maturity and reduced the bunch size (Abdul and Gosh 2020).

38

The infestation area of E.thrax In Indonesia tends to increase. In Central Sulawesi, a new infestation area of this banana 39

pest ranged from 35 to 108 ha from 2014 to 2018 (Ditlin Horti 2019). Several studies in Indonesia reported the parasitic 40

wasps and flies that potentially control the banana skipper (e.g., Hasyim et al. 1994; Hasyim et al. 1999; Erniwati and 41

Ubaidillah 2011; Rahmawati et al. 2018). Nevertheless, most of those studies were conducted in Sumatera and Java Island 42

and did not analyze the weather parameters' and the effect of banana variety effect on the BLR infestation. The 43

environmental factors, including weather, topography, natural enemies, and the banana cultivars influencing the population 44

and infestation of BLR (Sharanabasappa et al. 2016; Irulandi et al. 2018).

45

Therefore, information about the infestation of BLR, their parasitoid, and weather effects in Central Sulawesi known as 46

one of the biodiversity hotspots in the Wallacea region, is urgent to be conducted. This study provides baseline data of 47

Formatted: Font: Italic

Formatted: Font: Italic

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BLR incidences on different banana cultivars in this region as well as the diversity and parasitism of the BLR parasitoid 48

and their relation with environmental factors.

49

MATERIALS AND METHODS 50

Study area 51

The research was carried out in the banana plantation in the four villages of three regencies in Central Sulawesi, 52

Indonesia (Fig.ure 1). The mMajority of bananas are grown in the home garden. They are cultivated as a sole crop, border 53

crop, or intercrop in coconut and cacao plantations and several other crops.

54

55

Figure 1. Location of the study sites (indicated by blue circles) In Central Sulawesi, Indonesia 56

The study sites in each regency were selected purposively based on some environmental factors, including elevation, 57

climates, and variety of bananas (Table 1). Altitudes, win speed, temperature, and moisture were measured at one meter 58

from the ground by using a digital environment meter (MASTECH MS 6300, Mastech Indonesia), while rainfall data was 59

taken from the Meteorology, Climatology, and Geophysical Agency of Central Sulawesi.

60

Table 1. Description of study sites 61

Environmental parameters

Parigi Moutong regency Sigi regency Poso regency

Sausu Maku Kawende Makmur

Coordinates -1.065816 S,

120.526795 E -1.0519472 S,

119,8880582 E -1.230886 S,

120.561421 E -1.137919 S, 120.058479 E

Altitude (m asl) 58 m 56 m 13 m 543 m

Wind Speed (m/s) 0.0 - 1.0 0.1 - 0.4 0.0 - 0.6 0.0 - 0.1

Temperature (oC) 31.9 - 33.8 33.1 - 35.0 31.2 - 32.2 32.7 - 33.4

Relative humidity (%) 60.9 - 72.3 60.6 - 63.0 64.5 - 73.0 58.7 - 65.0

Rainfall (mm/year) 146.21 66.44 126.32 160.38

Banana variety Raja, Mas Kepok Raja, Mas Raja

Insect sampling and identification 62

The incidence of BLR was observed on each study site from April to August 2019. Plant with at least one leaf roll in a 63

leaf was considered infested. For identification and parasitism observation, tThree eggs group and twenty leaf rolls per site 64

were collected randomly and reared at the Plant Pest Laboratory, Faculty of Agriculture, Tadulako University for 65

identification, and parasitism observation. The BLR and parasitoids were identified by using several determination keys 66

(Goulet and Huber 1993; Zhang et al. 2005; O’hara et al. 2009; Erniwati and Ubaidillah 2011). Species identification was 67

then verified by the taxonomist of Museum Zoologium Bogorienze (MZB) of the Indonesian Institute of Sciences (LIPI) 68

National Research and Innovation Agency (BRIN).

69

Data analysis 70

Descriptive and inferential statistics were used for the data analysis. The level of incidence or infestation of BLR was 71

calculated as:

72

Percent incidence = × 100%

73 74

Commented [R1]: Please provide higher resolution of the  map than give the source of the map. 

 

Commented [R2]:  How many banana trees did you use in  this study at each study site? 

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Parasitism level was calculated as:

75

Percent parasitism = × 100%

76 77

Data were checked for the normal distribution by Shapiro-Wilk’s W-test and normalized using the Arc-sin 78

transformation. Differences inof pest incidence and total parasitism among sStudy sites were tested by ANOVA followed 79

by Honestly Significant differences (HSD). The generalized linear models (GLMs) without interaction (Zuur et al. 2009), 80

with a quasi Poisson to account for overdispersion, wereas applied to gain a possible effect explanation of the 81

environmental factors on the incidence of BLR. Explanatory variables included wind, temperature, relative humidity, 82

altitude, and variety. All analyses were done by using R 3.6.2 (R Core Team 2019).

83

RESULTS AND DISCUSSION 84

The incidence of E. thrax and parasitism 85

The study recorded E.thrax as the BLR in our study area. The infestation of E. thrax at the banana plantation was 86

varied from low to heavy levels. The lowest incidence of BLR was recorded at Maku, Sigi districts, where the banana 87

population is dominated by Kepok variety, while the highest incidence was at Kawende, Poso district. In a low infestation, 88

the banana loses only a minor part of the leaf, whereas, in a high infestation, most parts of the leaves are defoliated 89

(Figs.ure 2a, and 2b). The pra imago stages inside the leaf rolls were found at both levels of infestation (Figs.ure 2 c, e, f).

90

91

Figure 2. Erionata thrax : a-b Symptoms of damages on banana; c-g: Life stages of E. thrax; c.Eggs; d.Early instar larva; e. Mature 92

larva; f. Pupa; g. Adult 93

TWhile the BLR incidence at the study sites was quite high and ranged from 28.6 % to 85.8 %, the total parasitism of 94

the BLR parasitoids also varied among sites, and it was between 15.1 % andto 36.4 %. BLR incidence was significantly 95

different among sites; F(3,12) = 77.321, p < 0.000 but total parasitism was not; F(3,12) = 2.010, p = 0.1663. Interestingly, 96

parasitism levels tended to increase following the incidence of BLR (Fig.ure 3).

97

Commented [R3]: How do you classify the level of  infection rates? 

Please add in the materials and methods 

Commented [R4]: Also for this. 

(5)

Figure 3. Incidence of banana leaf roller (E. thrax) and total parasitism in the study sites. Different letters indicate significant 98

differences (HSD Test, p < 0.01) 99

Diversity and parasitism of BLR parasitoids 100

The study determined nine species of parasitoids of E. thrax. Eight of them, i.e., Agiommatus sumatraensis 101

Crawford, Pediobius erionotaeataea Kerrich, Ooencyirtus pallidipes (Ashmead), Brachymeria lasus (Walker), 102

Brachymeria thracis (Crawford), Cotesia (Apanteles) erionatae Wilkinson, Xanthopimpla gampsura 103

Krieger, and Casinaria sp. belonged to Hymenoptera, and only one Dipteran parasitoid was found, i.e., Palexorista 104

solennis (Walker) (Fig.ure 4).

105 106

107

Figure 4. Parasitoids of BLR in Central Sulawesi, Indonesia; (a). A. sumatraensis, (b). P. erionatae, (c). O. pallidipes, (d). P.

108

solennis (e). B. thracis, (f). B. lasus, (g) C. erionoatae, (h). X. gampsura, (i). Casinaria sp.

109

The parasitoid size was in the range of 1.2 to 14.9 mm with X. gampsura, showed the bigger size was X. gampsura 110

than followed by B. lasus , and P. solennis. The host stage infested by parasitoids wasere varied, i.e., egg, larva, and pupa 111

of the BLR. They were also different concerning the numbers of immatures per individual host. Three parasitoid species 112

were solitary (one parasitoid per host), and the rest were gregarious (more than one parasitoid per host). The parasitoid B.

113

lasus was the most gregarious parasitoids where the number of adult parasitoids that emerged from one host wasere about 114

7 to 15 individuals.

115

Commented [R5]: Please pay attention to the parentheses  in the author's name. If the author's name is in the  parentheses, it means that the species' name has been  revised. 

 

Commented [R6]: Sub genus should be in the parentheses  

Commented [R7]: Please add scale bar to each photo 

(6)

The number of parasitoids species was different between locations. There were six species found in Maku, five species 116

in Kawende, four species in Makmur, and two species in Sausu. Of nine recorded parasitoids, only B. lasus were 117

distributed in all sStudy sites, while other species were only present at a particular location. The parasitism level of 118

different parasitoid species ranged from 0.0 to 22.1 %. The higher parasitism was recorded by B.lasus (15.9 ± 2.2 119

%), followed by A. sumatraensis (9.4 ± 2.9 %) and P. erionotae (8.8 ± 2.1 %), while the lowest parasitism was C.

120

erionatae and X. gampsura (0.5 ± 0.1 %) (Table 2).

121

Table 2. Parasitoids of E. thrax, parasitism, and their distributions in the Study sites.

122

Ordo/Family/Species Size

(mm)1 Host

stadia Type of parasitoids

Parasitism of each species at a different location

(Regency/ District)2 Average

Sausu,

Parimo Maku,

Sigi Kawende,

Poso Makmur, Poso Hymenoptera/ Chalcididae

Brachymeria lasus Walker 5.4 ± 0.2 Pupa Gregarious 13.3 ± 1.4 17.5 ± 0.3 11.3 ± 2.5 21.5 ± 4.5 15.9 ± 2.2 Brachymeria thracis

Crawford 5.0 ± 0.3 Pupa Gregarious 3.3 ± 1.4 0 5.0 ± 2.5 0 2.1 ± 0.9

Hymenoptera/ Braconidae Cotesia (Apanteles)

erionotae Wilkinson 3.8 ± 0.2 Larva Gregarious 0 2.5 ± 0.5 3.3 ±1.4 0 0.5 ± 0.1

Hymenoptera/ Ichneumodidae Xanthopimpla gampsura

Krieger 14.9 ± 0.2 Pupa Soliter 0 2.5 ± 0.5 0 0 0.5 ± 0.1

Casinaria sp. 1.2 ± 0.2 Larva Soliter 0 0 3.3 ± 1.4 0 0.8 ± 0.4

Hymenoptera/ Pteromalidae Agiommatus sumatraensis

Crawford 2.6 ± 0.3 Egg Soliter 0 22.1 ± 8.7 0 15.3 ± 3.2 9.4 ± 2.9

Hymenoptera/ Eulophidae Pediobius erionotae

Kerrich 1.9 ± 0.5 Egg Soliter 0 15.0 ± 3.9 0 20.0 ± 4.4 8.8 ± 2.1

Hymenoptera/ Encyrtidae Ooencyrtus pallidippes

Ashmead 1.5 ± 0.3 Egg Gregarious 0 3.3 ± 1.7 0 9.0 ± 1.4 2.3 ± 0.8

Diptera : Tachinidae Palexorista solennis

(Walker) 6.9 ± 0.3 Larva Gregarious 0 0 5.0± 2.5 0 1.3 ± 0.6

1 an average size of three individual of imago, 2 an average of four times observation. Data shown are mean ± standard error 123

The relationship between BLR incidence and environmental factors 124

The environmental factors and banana cultivars were varied among the study sites, particularly the altitude, rainfall, 125

and banana varieties. A GLM analysis showed that of six environmental variables measured, the rainfall, altitude, and 126

banana varieties showed correlation and significantly affected the BLR incidence of BLR (Table 3).

127

Table 3. Generalized linear models relating the incidence of BLR with the wind, temperature, relative humidity, altitude, and banana 128

variety 129

Variable Estimate SE P

(Intercept) 4.175682 2.218066 0.05976 ns

Wind speed -0.068239 0.299170 0.81957 ns

Temperature -0.033590 0.060304 0.57751 ns

RH Rainfall

-0.004889 -0.020428

0.005599 0.008971

0.38256 ns 0.02279 *

Altitude 0.006129 0.001891 0.00119 **

Banana variety 1.443106 0.369379 9.358e-05 ***

Significant codes: *** < 0; ** < 0.01; * < 0.05; ns = non significant 130

Discussion 131

In this study, we investigated the incidence and parasitism of BLR and its relationship to environmental factors.

132

Previous studies have been reported the BLR attack on bananas in Indonesia and other tropical countries (Hasyim et 133

al. 1994; Hasyim et al. 1999; Erniwati and Ubaidillah 2011; Irulandi et al. 2018). It is generally known that BLR attacks 134

do not significantly reduce banana production except in high attack rates (Okolle et al. 2006). The population and 135

infestation of this pest are influenced by various abiotic and biotic factors such as elevation, weather, wind, natural 136

enemies, and banana varieties (Okolle et al. 2010; Irulandi et al. 2018).

137

For the first time, this study uncovers the incidence of BLR and diversity of it is parasitoids at different altitudes and 138

banana varieties andas well as its relation to the environmental factors in Central Sulawesi, situated in the Wallacea region.

139

Commented [R8]:  

Temperature 

The range of temperature among each study site is almost  the same, so the non significant result of the statistical  analysis is not because the temperature has no correlation  with the BLR incidence.  

Commented [R9]: What is the implication of the location  study that is situated in Wallacea region to the result of this  study? 

(7)

The study noted that BLR attacked all banana varieties at the studied sites with a high incidence rate. Interestingly, the 140

lowest incidence was recorded at Maku, Sigi district, where the banana population was dominated by Kapok variety., and 141

Tthe highest was found at Kawende (Poso regency), where three banana varieties were planted (Raja, Kapok, and Mas). A 142

study conducted in West Java, Indonesia, noteds differences in BLR infestation between banana varieties where Raja 143

variety had the highest (Novianti 2008). It also has been reported that in India, it has also been reported that BLR preferred 144

a particular banana variety, and it might be related to the leaf character, such as the thickness of leaf lamina 145

(Sharanabasappa et al. 2016; Irulandi et al. 2018). It suggests that further investigation might distinguish the resistance of 146

banana varieties against BLR.

147

The population of the skipper generally tended to be abundant at a higher elevation (Hasyim et al. 1994). Surprisingly, 148

the current study recorded a dissimilar pattern where the BLR incidence tended to be higher in the banana planted at lower 149

altitudes (Sausu and Kawende). Nevertheless, the results presented in the current study would support the hypothesis that 150

weather parameters, including temperature, moisture, and altitude, together with banana cultivars, affecting the incidence 151

of BLR (Okolle et al. 2010; Kalshoven 1981; Sharanabasappa et al. 2016). It is noteworthy that E.thrax may have a 152

favorable condition to establish in banana leaves as long the host is present. Weather conditions may directly influence the 153

larval development or mortality of E.thrax or indirectly the fitness of banana as the host plant of E.thrax (Okolle et al.

154

2010). However, modifying the environmental conditions related to management practices almost possible to deal with the 155

cost of spending. Therefore, the presence of parasitoids E. thrax parasitoids is promising for biological control.

156

Parasitoid insects are natural enemies that play an essential role in BLR population control (Hasyim et al. 2003; Okolle 157

et al. 2010). This study found nine species of parasitoids associated with banana skipper pests, which is quite higher than 158

those reported previously in Indonesia (see Hasyim et al. 2003; Erniwati and Ubaidillah 2011; Wibowo et al. 2015;

159

Rahmawati et al. 2018). The presence of P. solennis in Central Sulawesi is firstly reported by this study.

160

The study noted the different levels of parasitism. Of nine parasitoids found, B. lasus was the most distributed species, 161

found in all studied sites. This species also had the highest parasitism rate (13.3 – 21.5 %) and was the most gregarious.

162

Additionally, the size of B. lasus was the third larger among recorded parasitoids. All of these characteristics support B.

163

lasus as the enormous potential biological agent of BLR. According to the “adult size–fitness hypothesis” particularly in 164

hymenopteran parasitoids, larger size individuals haves several advantages, such as has a high capacity to find high-quality 165

hosts, lifetime fecundity, longevity, and mating success than smaller parasitoids (Gao et al. 2016). The body size positively 166

affects the parasitoids’ distances travelled (Fischbein et al. (2018), and theseis advantages are most likely related towith 167

their higher searching efficiency (Iranipour et al. 2020). Furthermore, the gregarious parasitoids haves several advantages 168

compared with the solitary parasitoids (Iranipour et al. 2020;, Samkova et al. 2021). For examples, Cotesia erionotae 169

(Wilkinson), a gregarious larval parasitoid, has been successfully used toin controlling Erionota spp.in some parts of the 170

world (Kalshoven 1981;, Cock 2015).

171

Other prospective parasitoids for control BLR recorded at the low and high altitudes in this study were A.

172

sumatraensis and P. erionotae. The parasitism levels were 9.6 – 21.3 % and 16.7 – 33.3 %, respectively. The previous 173

study in Central Sulawesi reported about 1.2% and 3.7 % parasitism for B.lasus and C. erionotae (Rahmawati et al. 2018).

174

Hasyim et al. (1994) recorded a 10-14 % parasitism of eggs by O.erionatae and P. erionatae, 1–-80 % of larvae killed 175

by Casinaria sp., and 50% of larvae attacked by C. erionotae.

176

Parasitoid, P. solennis that recorded in this study is also potentially to control the BLT. The parasitism level of this 177

parasitoid was quite low. This is in line with Hasyim et al. (1994) and Poorani et al. (2020) highlighted the minor 178

importance of the Tachinid flies of Tachinid flies (P. solennis). It has been reviewed that parasitizing of the leafroller 179

caterpillar by Tachinid flies was lower than Hymenoptera flies (O’hara et al. 2009). Nevertheless, Sharanabasappa et al.

180

(2018) encountered two important tachinid parasitoids of E.torus in India.

181

Besides reported as the most common and effective biological control agency of banana skippers (Okolle et al. 2010), 182

hymenopteran parasitoids were also important for another group of pests (Wang et al. 2019). However, the effectiveness of 183

parasitoids to manage the banana skipper will increase by combining it with cultural or chemical controls in the scheme of 184

integrated pest management (Okolle et al. 2010; Irulandi et al. 2018). Release the BLR parasitoids could be useful when 185

the BLR population in the fields is low, while chemical control only needs if the population of this pest is high (Okolle et 186

al. 2006).

187

The present study detected that a higher infestation of E.thrax tended to follow by higher parasitism at all studied sites.

188

This result indicated that parasitoids of BLR performed well in the fields and most likely showed the density-dependent 189

nature of the parasitoids. However, environmental factors such as elevation, rainfall, temperature and humidity could also 190

be the determining factors directly or indirectly. Differences in topography can result in differences in climate factors and 191

plant phylogeny (Okolle et al. 2010).

192

It has been reported that incidence of E. torus was positively correlated with maximum temperature and sunshine 193

hours, but negatively correlated with minimum temperature, morning and evening relative humidity and rainfall 194

(Sharanabasappa et al., 2016). High infestation and parasitism of E.thrax usually occur during the rainy season and lower 195

wind speed (Kalshoven 1981; Okolle et al. 2006), but heavy rainfall may roll down the young instar larvae in leaf and 196

wind-torn leaves and interrupt the formation of leaf roll. Meanwhile, the larval period of the BLR was longer during lower 197

temperature and higher humidity (Okolle et al. 2010; Irulandi et al. 2018). This condition might favor their natural enemies 198

such as microbes or parasitoids to develop better.

199

Commented [R10]:  

Alititude  Makmur = 543 m  Maku = 56 m 

However BLR incidence of Makmur is higher than Maku   

See comment R8 

(8)

Future studies would be essential to explore the diversity of the natural enemies of BLR besides parasitoids. Several 200

predators such as a bug, Platynopus melacanthus, birds (particularly crows), ants, and spiders contributes to the mortality 201

of the pra imago of E. thrax (Okolle et al. 2010, Poorani et al. 2020). Another challenge is to explore the BLR-parasitoid 202

association by using a DNA barcoding approach to cope with the problem of the identification due to the incompleteness 203

collection of the BLR specimens (Cock et al. 2019).

204

In conclusion, this study provides insight into the current situation of BLR incidence in Central Sulawesi, Indonesia.

205

BLR infestation is a major problem with incidence rich up to 85%. In addition, this study also recorded nine species of 206

parasitoids for the pest E. thrax. These included eight species of insects in the wasp order and one in the fly order. They 207

were A. sumatraensis, P. erionataea, O. pallidipes, B. lasus, B. thracis, C. erionatae, X. gampsura, P.

208

solennis, and Casinaria sp. Parasitoid B. lasus was the most potential for controlling E.thrax followed by A.

209

sumatraensis dan P. erionotae. The rainfall, altitude, banana varieties, and parasitism were acting as a natural control of 210

the banana skipper.

211

ACKNOWLEDGMENTS 212

This research was financially supported by the professor's research and scientific publication program of the Tadulako 213

University of Indonesia in 2019. We thank taxonomists of MZB, LIPI, particularly Prof. Rosichon Ubaidillah, for the 214

parasitoid identification and Dicky Wahyudi for collecting of the banana skipper.

215

REFERENCES 216

Abdul JK, Gosh SM. 2020. Biology and damage of banana skipper Erionota torus (Evans) from Malabar region of Kerala. Indian Jj.

217

Eentomol. 82(3): 429-434. DoI No.: 10.5958/0974-8172.2020.00112.1.

218

Cock MJW. 2015. A critical review of the literature on the pest Erionota spp. (Lepidoptera, Hesperiidae): Ttaxonomy, distribution, food 219

plants, early stages, natural enemies and biological control. CAB reviews 10 (7): 1-30. DOI: 10.1079/PAVSNNR201510007.

220

Cock MJW, Buddie AG, Cafa G. 2019. Piloting the use of DNA barcoding in support of natural enemy surveys: New parasitoid records 221

for banana skippers (Erionota spp., Lepidoptera, Hesperiidae) in Malaysia. J Asia Pac Entomol. 22: 183-188.

222

DOI: 10.1016/j.aspen.2018.12.019.

223

Ditlin Horti, Direktorat Perlindungan Hortikultura. 2019. Statistik Iklim, OPT dan DPI. Pusat Data dan Informasi Pertanian.URL : 224

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