Interspecific larvae competence and mandible shape disparity in cutworm pest complex (Lepidoptera: Noctuidae)

Interspecific larvae competence and mandible shape disparity in cutworm pest complex (Lepidoptera: Noctuidae)

Journal Pre-proof Interspecific larvae competence and mandible shape disparity in cutworm pest complex (Lepidoptera: Noctuidae) Selene Niveyro, Hugo A...

5MB Sizes 0 Downloads 10 Views

Journal Pre-proof Interspecific larvae competence and mandible shape disparity in cutworm pest complex (Lepidoptera: Noctuidae) Selene Niveyro, Hugo A. Benítez PII:

S0044-5231(19)30117-2

DOI:

https://doi.org/10.1016/j.jcz.2019.10.004

Reference:

JCZ 25678

To appear in:

Zoologischer Anzeiger

Received Date: 10 July 2019 Revised Date:

28 September 2019

Accepted Date: 14 October 2019

Please cite this article as: Niveyro, S., Benítez, H.A., Interspecific larvae competence and mandible shape disparity in cutworm pest complex (Lepidoptera: Noctuidae), Zoologischer Anzeiger, https:// doi.org/10.1016/j.jcz.2019.10.004. This is a PDF file of an article that has undergone enhancements after acceptance, such as the addition of a cover page and metadata, and formatting for readability, but it is not yet the definitive version of record. This version will undergo additional copyediting, typesetting and review before it is published in its final form, but we are providing this version to give early visibility of the article. Please note that, during the production process, errors may be discovered which could affect the content, and all legal disclaimers that apply to the journal pertain. © 2019 Published by Elsevier GmbH.

1

Interspecific larvae competence and mandible shape disparity in cutworm pest

2

complex (Lepidoptera: Noctuidae).

3 4

Selene Niveyro1 & Hugo A. Benítez2

5 6

1

7

Pampa, Ruta 35 Km 334, Santa Rosa 6300, La Pampa, Argentina.

8

2

9

Velásquez #1775 Arica, Chile.

Cátedra de Zoología Agrícola, Facultad de Agronomía, Universidad Nacional de La

Departamento de Biología, Facultad de Ciencias, Universidad de Tarapacá, General

10 11

ABSTRACT

12

Cutworm pest complex (Lepidoptera: Noctuidae) varies globally in terms of regional

13

dominance, crops attacked and feeding behaviour. In the Pampean region, extensive

14

extensions of farming lands are affected by at least five cutworm species belonging to

15

the genus Agrotis, Feltia and Peridroma. Due to the competitive environment that

16

exposes these insects to stressors, certain individual features such as morphology could

17

provide useful insights about functional diversity related to its dispersion and

18

dominance. In this study, we analyze whether the shape of the mandibles is a

19

contrasting trait between seven cutworm species, and we discuss whether this

20

morphological trait can be an influential factor in the abundance and predominance of

21

species within the complex between the southern and northern part of the Pampean

22

region. Using geometric morphometrics tools, the results evidenced that cutworms

23

complex differs in this functional trait. Closer phylogenetically species of Agrotis were

24

widely different between them, while species phylogenetically distant belonging to

25

Feltia and Peridroma were lightly similar. These results showed that functional traits

26

have a fundamental importance to develop a predictive framework linking the herbivory

27

damage with the herbivore functional diversity.

28 29

Keywords: Noctuoidea; Agrotis; functional diversity; morphological trait; ecomorphology;

30

cutworms.

31

32

1. INTRODUCTION

33

Noctuoidea is the largest and most diverse superfamily of Lepidoptera with more than

34

40,000 recognized species (Wagner, 2001). Among them, numerous species are

35

important pests, including the cutworm species. Cutworm is the common name given to

36

the larvae of noctuid moth species feeds on roots, offspring of crop plants and grasses.

37

Cutworms have great potential for spring damage in the Pampean region (Argentina),

38

where they cut lucerne sprouts, seedlings of corn, sorghum, soybeans, and sunflowers

39

(Aragón, 1985). In severe cases, the damage by the cutworms forces the reseed of the

40

crop. Therefore, the economic thresholds for cutworm complex are very low, in summer

41

crops it is estimated at 1 caterpillar per m2 (Aragón, 1985) and in lucerne 1-2 caterpillars

42

per crown (Villata, 1993).

43

Cutworm pest complex varies globally in terms of regional dominance, life cycle and

44

feeding behaviour (Ayre & Lamb, 1990; Wang et al., 2015). In the Pampean region,

45

vast extensions of farming lands are affected by at least five cutworm species: Agrotis

46

ipsilon (Hufnagel), Agrotis robusta (Blanchard), Feltia deprivata (Walker), Feltia

47

gypaetina (Guenée), Feltia lutescens (Blanchard), Feltia irritans (Köhler) and

48

Peridroma saucia (Hubner) (Aragón, 1985). The composition of the complex and the

49

dominance of species vary greatly in the region. Until the 90s, the damages by

50

cutworms were mainly caused by Agrotis ipsilon (Aragón, 1985), while by the middle

51

of the decade this situation has been modified by presenting prolonged and severe attack

52

by the species Agrotis robusta and Feltia gypaetina (Aragón, 1995). In the north part of

53

the region, Agrotis ipsilon is still the dominant species, while Agrotis robusta is

54

registered as the main species in the southern and drier part of the region (Corró Molas

55

et al., 2017). Samples taken in recent years (2014-2018) also indicated fluctuations

56

among summer seasons in the proportion of the rest of the cutworm species that make

57

up the complex e.g. Feltia lutescens and especially Feltia deprivata and Peridroma

58

saucia (Niveyro data unpublished). However, the density of these species in the

59

complex always remains low when compared to Agrotis genus. Regardless of the higher

60

abundance of one or another species, the five species coexist sympatrically around the

61

whole region and generally share, compete or exploit alternative resources to survive

62

and reproduce (Corró Molas et al., 2017; Matley et al., 2017).

63

It is a practice in agroecosystem to reduce the pest influence incorporating different

64

resource pools or partitioning them to reduce herbivory, similar species can co-exist

65

within distinct ecological niches (Chesson, 2000). For cutworms, the ecological niche is

66

mainly driven by competition for resources and feeding interactions among organisms,

67

although other factors such as morphological, functional and physiological constraints

68

may contribute (Frankie & Ehler, 1978; Worner & Gervey, 2006). Since a competitive

69

environment exposes these insects to stressors, certain organismal aspects such as

70

morphology could provide useful insights about the expression of the phenotype-

71

environment interaction (Benítez et al., 2014) and functional diversity related to

72

dispersion and dominance (Mikac et al., 2016). Different rearing environments may

73

produce dissimilar stress level in insects, which could be reflected on their multiples

74

morphological diversity where the organism development modulates their own shape

75

variation in response to changes in the environment (Chazot et al., 2016) There are

76

several issues for which morphological analyses play an important role in

77

agroecosystem. For instance, ecomorphological studies have revealed constraints and

78

selective factors affecting the fitness response to certain environments of particular

79

phenotypes (Bower & Piller, 2015, Sherratt et al., 2018). Besides, morphological

80

diversity can reflect functional diversity in a community (Deraison et al., 2015). In

81

cutworm complex, morphological variation, particularly in functional structures such as

82

mandible, can influence the herbivory affecting crops, as well as, reflect an adaptive

83

capacity of the species to expand and colonize other regions with the consequent

84

economic damage. In all these cases, morphology reveals certain organismal aspects

85

that relate an individual to its environment, hence its importance. Indeed, the

86

relationship between morphology and ecology could provide useful insights about the

87

expression of the phenotype-environment interaction and the related evolutionary

88

history (Piersma & Drent, 2003).

89

In recent years, the development of a morphological quantitative toolkit used in multiple

90

studies in ecomorphology known as geometric morphometrics (GM) has made it

91

possible to detect small shape variations that used to be difficult to distinguish with

92

traditional linear morphometrics (Adams & Rohlf, 2000). GM is a coordinate-based

93

method, which means that its primary data are cartesian coordinates of anatomically

94

distinguishable landmarks (i.e. discrete anatomical points that are arguably homologous

95

among all the individuals under analysis) (Adams et al., 2013).

96

GM techniques have never been applied on the mandible of Lepidoptera`s larvae.

97

Nevertheless, the only published approximation to this topic has been done in an

98

agronomic system and it is a study on beetle larvae (Benítez et al., 2014).

99

In this study, the mandibular shape belonging to the cutworm complex present in the

100

Pampean region was analysed. Taking regional dominance of species into

101

consideration, the hypotheses stated is that mandibular shape is a contrasting trait

102

among the species within the cutworm complex.

103 104

2. MATERIALS AND METHODS

105

2.1. Laboratory mass rearing of cutworms

106

Five gravid female moths of seven cutworm species: Agrotis ipsilon (Hufnagel), Agrotis

107

robusta (Blanchard), Feltia deprivata (Walker), Feltia lutescens (Blanchard), F.

108

gypaetina (Guenée), Feltia irritans (Köhler) and Peridroma saucia (Hubner), were

109

collected using a light trap located in the campus of the Faculty of Agronomy,

110

UNLPam, La Pampa, Argentina (36° 33'9 '' S; 64° 18'8'' W, 220 masl). Moths collected

111

come from fields where larvae are exposed to natural competitive environments. Each

112

moth collected was placed individually in plastic cups of 165 cc and fed a sugar solution

113

of 10% honey and distilled water. Tissue paper was placed inside the plastic cup to

114

facilitate the oviposition. Newly emerged larvae were separated in individual plastic

115

cups of 120 cc to avoid cannibalism and reared with artificial diet based on bean meal,

116

yeast extract, wheat-germ, sorbic acid, ascorbic acid and formaldehyde (following the

117

methodology of Niveyro et al., 2015) until the fifth instar larvae was achieved. The

118

temperature of the laboratory was 25 ± 2 ºC, with 65 ± 10% relative humidity and the

119

photoperiod was 16:8 h Light–dark cycle. Five male specimens of each species were

120

also collected in the light trap to confirm species identification by genitalia dissection

121

(Aragón, 1985; Lafontaine, 2004). Left and right mandibles of each species (N = 194

122

mandibles) were dissected and preserved in 70% ethyl alcohol: A. ipsilon (n = 14), A.

123

robusta (n = 38), F. deprivata (n= 60), F. lutescens (n = 34), F. gypaetina (n = 12), F.

124

irritans (n = 6) and P. saucia (n = 30). Larvae were not sexed for morphometrics

125

analysis.

126

2.2. Shape analysis

127

The concave surface of left and right mandibles of each species was photographed using

128

a Leica digital camera on a binocular of Leica EZ4 stereo-microscope and saved in

129

JPEG format using the Leica Application Suite version 1.7 (Leica Microsystems

130

Limited, Switzerland). Photographs were digitized with tpsUtil version 1.58 and

131

tpsDig2 version 2.17 (Rohlf, 2013). Twelve anatomical landmarks (LM) were digitized

132

to capture the shape of the mandibles (Fig. 1, Table 1). The first tooth of the mandible,

133

hereinafter named as lobe, was not considered in the analysis for being an inner lobe

134

and impractical to locate in all samples. A generalized Procrustes analysis was applied

135

to the landmark to remove the information of size, position and orientation from the

136

shape variables (Rohlf & Slice, 1990; Dryden & Mardia, 1998). Left and right mandible

137

were digitized twice and a Procrustes ANOVA was calculated to compare the influence

138

of the digitizing error (Klingenberg & McIntyre, 1998) Both sides were analysed

139

(matching symmetry) independently and the for graphical reasons the left side was used.

140

Principal component analysis (PCA) based on the covariance matrix of individual

141

mandible shape was performed in order to graphically visualize the mandible shape

142

variation related to cutworm species in multidimensional space.

143

A Canonical variate analysis (CVA) was performed in order to find the shape features

144

that best distinguish among the groups based on the mandible shape changes and to

145

quantify the morphological distance between different species. The results were

146

reported as the p-values of Mahalanobis distances and Procrustes distances

147

(Klingenberg & Monteiro, 2005). To evaluate the effect of size on the shape (allometry)

148

a multivariate regression analysis was computed using the centroid size as an

149

independent variable and the Procrustes coordinates as the dependent variable

150

(Monteiro, 1999). All the morphometric analyses were performed using the software

151

MorphoJ 1.06d (Klingenberg, 2011).

152 153

3. RESULTS

154

The Procrustes ANOVA to assess the measurement error showed that the mean square

155

of digitalization error was much smaller than the Individual discarding measurement

156

error of the landmarking process (Table 2). The first three components of the PCA

157

accounted for 77.8% of the total variation (PC1: 38.52%, PC2: 25.06%, PC3: 14.24%).

158

In general, the largest difference in mandible shape was explained by the distance

159

between landmark 3 and 4, and from the landmarks in the apical end of the lobes (i.e.

160

landmark 1, 7, 9, 11) to the landmark in the intersection (i.e. landmark 8, 10 and 12).

161

In the genus Agrotis, differences in the mandible shape showed that A. ipsilon has a

162

wider mandible with elongated and pointed incisor lobes than A. robusta. Conversely,

163

A. robusta has the narrowest mandible among all the species tested and its incisor lobes

164

have a broad shape with sharper crests (Fig. 2). Furthermore, regarding the genus

165

Agrotis, the scatterplot of the PCA showed that A. robusta samples was more

166

homogeneous group than A. ipsilon samples. In contrast, A. ipsilon samples shared the

167

morphological space with all the remaining species (Fig. 3. a).

168

In the genus Feltia, there were also differences, but they were not as noticeable as in the

169

genus Agrotis. F. deprivata and F. lutescens have the widest mandible, F. irritans the

170

narrowest one, and F. gypaetina presents intermediate width values. Moreover,

171

differences in landmark 1, 7, 9 and 11 among species indicate that F. irritans has the 3rd

172

and 4th incisor lobes less prominent than the rest of the samples. Comparisons among all

173

genera and species showed that P. saucia shares characteristics with F. deprivata but it

174

differs from A. robusta and A. ispilon by its wider mandible shape and less protuberant

175

incisor and molar lobes.

176

After maximizing the variance, the scatterplot of the CVA showed clusters between the

177

cutworm species and the permutation between them was statistically significant (P

178

<0.05) (Table 3). The CVA analysis showed that A. ipsilon is a completely separated

179

group from other species and with the maximum variation in its mandible shape. Even

180

though it was observed some samples of F. deprivata, F. lutescens and P. saucia share

181

the morphospace, these species tended to be rather separated (Fig. 3.b).

182

Multivariate regression analysis in Fig. 4 showed that there was a 10% of allometry

183

influenced by the mandible shape on the centroid size, whereas the effect can be noticed

184

on the specimens of A. robusta, which could have affected the morpho-space of the

185

shape. After analysing a PCA from the residual of the regression (data without size

186

influence) can be clearly evidence that the shape of A. robusta influenced by allometry

187

(Supplementary Fig. 1).

188 189

4. DISCUSSION

190

The results of this study indicated a wide range of mandibular shape within the cutworm

191

complex. Phylogenetically closest species of Agrotis were widely different, while other

192

species phylogenetically distant such as Feltia and Peridroma were lightly similar.

193

Mandibular shape was mainly defined by its width (distance between landmarks 3 and

194

4) and the shape of their incisor lobes (landmarks 1, 7, 9, 11). In noctuid larvae, the

195

incisor process or lobes in the mandible are generally considered to have been used for

196

biting while the molar lobes are mostly for crushing (Das, 1937). The differences

197

observed in the lobes of the mandible may generate a functional change on how the

198

larvae can cut and crush or macerate the plant tissues. Considering this functional

199

difference, it is likely that species with stronger molar and incisor lobes may have

200

biological advantages in grassland areas where vegetation is dominated by grass plants

201

with high lignin and fiber contents. Consequently, it was notorious in most of the

202

samples tested here, a greater sign of wear in the molar lobes than in the incisor lobes of

203

the mandible. This suggests that once the molar lobes are worn, the feeding of the larva

204

may depend mostly on the incisor lobes. According to the CVA, the dominant species,

205

A. robusta, differs from the rest of the cutworm species by its narrow mandible and the

206

shape of its incisor lobes. In consequence, the argument stated in this study is that in A.

207

robusta the lower depth in the notches of the incisors lobes generates a more compact

208

structure and stronger than in the remaining species.

209

It is well known that A. ipsilon is considered one of the biggest pests worldwide; these

210

results showed the contrary for the semi-arid areas of the Pampean Region, being

211

another species of Agrotis better represented and more competitive among them. The

212

geometric morphometric analysis showed that A. robusta besides being noticeable

213

different from all the examined species, it has the longest life cycle in comparison to all

214

the species tested (insect-rearing data not shown), and the mandible shape variance it

215

could allow this species to occupy all the different nutritional spaces around the

216

southern and semi-arid areas of the Pampean region.

217

Because of that and due to the higher competence pressures, lower population density is

218

noticeable for A. ipsilon in the semi-arid areas of the Pampean region, compared to the

219

different locations worldwide. Some tools in geometric morphometrics can be used to

220

detect developmental instability between populations as a consequence of fitness

221

competence (Klingenberg, 2015), being fluctuating asymmetry the most commonly

222

used. Preliminary shape asymmetries were calculated (results not showed) finding that

223

A. ipsilon has higher values of fluctuating asymmetry than A. robusta. Analyzing the

224

level of developmental instability product of competence would be the next steps to

225

follow, in order to detect the fitness behaviours related to the competition between

226

larvae in the agricultural environment. Besides, it should be borne in mind the presence

227

of biological control and climatic conditions could influence the abundance and

228

predominance of cutworm dispersion. Also, new experimental designs are necessary to

229

assess how the competitive environment drives the morphological diversity we report in

230

this study.

231

Considering that these species are agricultural pests, the results achieved here also have

232

implications for pest management practice. In this sense, the simultaneous occurrences

233

of cutworm species in the same ecological niche and the results obtained here raise

234

questions about how changes in the proportion of the species within the complex may

235

influence the herbivory levels on the crops. According to literature, herbivory level on a

236

plant community increases as the functional diversity within the associated insect

237

community increases (Shoener, 1974, Duffy et al., 2007). Hence the impact of the

238

cutworm complex on crop plant biomass may not only depend on the number of species

239

per se, but also on the particular traits of the species present (Deraison et al., 2015).

240

Changes in functional diversity of mandibular traits within the cutworm complex could

241

modify the cut of sprouts and seedlings of summer crops. The results of this study

242

evidenced that cutworm’s complex differs in functional traits, mandibular shape, and

243

this functional characteristic in species is of fundamental importance to determine the

244

degree of damage that can be expected and to develop a predictive framework linking

245

the herbivory damage with the herbivore functional diversity. Broadening knowledge of

246

functional traits in insect pest can help to establish accurate values of economic damage

247

thresholds in order to reduce the indiscriminate use of pesticide.

248 249

ACKNOWLEDGMENT

250

This work was supported in part by grant Pfort CyT-2017 Nº 140/2018 UNLPam and

251

Research Project No I-144/17 FA-UNLPam. HB Thanks to the Universidad de

252

Tarapacá, UTA Mayor 9719-17 and CONICYT Redes de Investigación REDI170182.

253

We thank two anonymous reviewers for their valuable suggestions.

254 255

REFERENCES

256 257

Adams D.C. & Rohlf F.J. (2000). Ecological character displacement in Plethodon:

258

biomechanical differences found from a geometric morphometric study. Proceedings

259

of the National Academy of Sciences 97: 4106-4111.

260 261

Adams D.C., Rohlf F.J., Slice D.E. (2013). A field comes of age: geometric morphometrics in the 21st century. Hystrix 24: 7.

262

Aragón J. (1985). Bioecología, sistemas de alarma y control de orugas cortadoras en

263

cultivo de girasol, maíz y soja. Inf. Para extensión. EEA Marcos Juárez INTA: 12p.

264

Aragón J. (1995). Plagas de la alfalfa. En: La Alfalfa en la Argentina. INTA Centro

265

Regional Cuyo. Edit. Editar, San Juan.280 pp.

266

Ayre G. L. & Lamb R. J. (1990). Life histories, flight patterns, and relative abundance

267

of nine cutworms (Lepidoptera: Noctuidae) in Manitoba. The Canadian Entomologist

268

122: 1059-1070.

269

Benítez H. A., Püschel T., Lemic D., Čačija M., Kozina A. & Bažok R. (2014).

270

Ecomorphological variation of the wireworm cephalic capsule: studying the

271

interaction of environment and geometric shape. PloS one, 9(7), e102059.

272 273

Bower L. M. & Piller K. R. (2015). Shaping up: a geometric morphometric approach to assemblage ecomorphology. Journal of fish biology 87: 691-714.

274

Chazot N., Panara S., Zilbermann N., Blandin P., Le Poul Y., Cornette R., Elias M. &

275

Debat V. (2016). Morpho morphometrics: shared ancestry and selection drive the

276

evolution of wing size and shape in Morpho butterflies. Evolution 70: 181–194.

277 278

Chesson P. (2000) Mechanisms of maintenance of species diversity. Annual Review of Ecology Systematics 31: 343–366.

279

Corró-Molas A., Baudino E., Vilches J., Guillot-Giraudo W., Babinec F., Vergara G.,

280

Niveyro S., Ghironi E. & Ferrero C. (2017). Estudio comparativo de la densidad del

281

complejo de orugas cortadoras (Lepidoptera: Noctuidae) en diferentes ambientes y

282

cultivos antecesores en la región subhúmeda pampeana central. Semiárida Revista de

283

la FA -UNLPam 27: 29-35.

284 285

Das G. M. (1937). Memoirs: The musculature of the mouth-parts of insect larvae. Journal of Cell Science 2: 39-77.

286

Deraison H., Badenhausser I., Loeuille N., Scherber C. & Gross N. (2015). Functional

287

trait diversity across trophic levels determines herbivore impact on plant community

288

biomass. Ecology letters 18: 1346-1355.

289

Dryden I.L. & Mardia K.V. (1998). Statistical shape analysis. Wiley Chichester.

290

Duffy J. E., Cardinale B. J., France K. E., McIntyre P. B., Thébault E., & Loreau M.

291

(2007). The functional role of biodiversity in ecosystems: incorporating trophic

292

complexity. Ecology letters 10: 522-538.

293 294 295 296

Frankie G. W. & Ehler L. (1978). "Ecology of insects in urban environments." Annual Review of Entomology 23: 367-387. Klingenberg

C.

(2015).

Analyzing

fluctuating

asymmetry

with

geometric

morphometrics: concepts, methods, and applications. Symmetry 7: 843-934.

297

Klingenberg C. P. & McIntyre G. S. (1998). Geometric morphometrics of

298

developmental instability: analyzing patterns of fluctuating asymmetry with

299

Procrustes methods. Evolution 52: 1363-1375.

300

Klingenberg C. P. & Monteiro L.R., (2005). Distances and directions in

301

multidimensional shape spaces: Implications for morphometric applications.

302

Systematic Biology 54: 678-688.

303 304

Klingenberg C. P. (2011). MorphoJ: an integrated software package for geometric morphometrics. Molecular Ecology Resources 11: 353-357.

305

Lafontaine J. D., Dominick R. B., Ferguson D. C., Franclemont J. G., Hodges R. W. &

306

Munroe E. G. (2004). The moths of North America. Noctuoidea: Noctuidae (part).

307

Noctuinae (part—Agrotini). Fasc. 27.1. The moths of North America. Wedge

308

Entomological Research Foundation, Washington, DC.

309

Matley, J. K., Heupel, M. R., Fisk, A. T., Simpfendorfer, C. A., & Tobin, A. J. (2017).

310

Measuring niche overlap between co-occurring Plectropomus spp. using acoustic

311

telemetry and stable isotopes. Marine and Freshwater Research 68: 1468-1478.

312

Mikac K.M., Lemic D., Bažok R., Benítez H.A. (2016). Wing shape changes: a

313

morphological view of the Diabrotica virgifera virgifera European invasion.

314

Biological Invasion 18: 3401–3407.

315

Monteiro L. R. (1999). Multivariate regression models and geometric morphometrics:

316

the search for causal factors in the analysis of shape. Systematic Biology 48: 192-

317

199.

318

Niveyro S.L. (2015). Herbivory by insects in Amaranthus and its relationship with

319

morphological, phenological and chemical features in different cultivars. PhD

320

Thesis. Universidad Nacional de Córdoba, Argentina.

321 322 323 324

Piersma T. & Drent J. (2003). Phenotypic flexibility and the evolution of organismal design. Trends in Ecology & Evolution 18: 228-233. Rohlf F. J. & Slice D. (1990). Extensions of the Procrustes method for the optimal superimposition of landmarks. Systematic Biology 39: 40-59.

325

Rohlf F.J. (2013) TPSdig, v. 2.17. NY State University at Stony Brook.

326

Schoener T.W. (1974). Resource partitioning in ecological communities. Science 185:

327 328 329 330 331 332 333

27-39. Sherratt E., Anstis M. & Keogh J. S. (2018). Ecomorphological diversity of Australian tadpoles. Ecology and evolution 8: 12929-12939. Villata C. (1993). Bioecología y control de plagas: 34-80. En: Alfalfa. Protección de la pastura. Subprograma Alfalfa. Agro de Cuyo. Manuales. 4. Wagner D.L. (2001) Moths. Encyclopedia of Biodiversity, Vol. 4 (ed. by S. A. Levin), pp. 249–270. Academic Press, San Diego.

334

Wang R. L., Li J., Staehelin, C., Xin X. W., Su Y. J. & Zeng R. S. (2015). Expression

335

analysis of two P450 monooxygenase genes of the tobacco cutworm moth

336

(Spodoptera litura) at different developmental stages and in response to plant

337

allelochemicals. Journal of Chemical Ecology 41: 111-119.

338 339

Worner S. & Gevrey M. (2006). Modelling global insect pest species assemblages to determine risk of invasion. Journal of Applied Ecology 43: 858-867.

340 341

FIGURE AND TABLE LEGENDS

342 343

Table 1. Location of the 12 landmarks to capture the cutworm mandible shape.

344

Landmarks

Location

1

Apical end of the 2nd incisor lobe

2

Beginning of the mandibular condyle

3

Middle of the mandibular condyle

4

Opposite to mandibular condyle

5

Apical end of the 2nd molar lobe

6

Intersection between the 1st and 2nd molar lobe

7

Apical end of the 1st molar lobe

8

Intersection between the 3rd incisor lobe and the 1st molar lobe

9

Apical end of the 4th incisor lobe

10

Intersection between the 3rd incisor and 4th incisor lobe

11

Apical end of the 3rd incisor lobe

12

Intersection between the 2nd and 3rd incisor lobe

345 346

Table 2. Procustes ANOVA results to assess the measurement error for shape change in

347

the cutworm samples.

348

Source of variation

SS

MS

31.386625

0.333900

94

75.42

<0.0001

Side

0.621406

0.621406

1

140.36

<0.0001

Individual*Side

0.416154

0.004427

94

1.54

0.0066

Error 1

0.547017

0.002879

190

Individual

df

F

P

349 350

Table 3. Procrustes distance between species (upper right triangle) and Mahalanobis

351

distance between the centroids of the groups (lower left triangle) derived from canonical

352

variation analysis. P-values for the pairwise are marked with asterisk (*) to indicate

353

significantly different (P < 0.05), double asterisk (**) when they are highly significant

354

(P< 0.001), and ns non-significant. AI: A. ipsilon, AR: A. robusta, FD: F. deprivata, FG: F.

355

gypaetina, FI: F. irritans, FL: F. lutescens and PS: P. saucia.

356

AI

AR

FD

FG

FI

FL

PS

AI

-

0.0643**

0.0465*

0.0493ns

0.0600 ns

0.0513 *

0.0561**

AR

4.1726*

-

0.0878**

0.0441*

0.0654*

0.0711**

0.0895**

FD

4.3152*

3.7874**

-

0.0544**

0.0633*

0.0313**

0.0238 ns

-

0.0404 ns

0.0326 ns

0.0525 ns

FG 4.6071** 2.4330** 2.5317**

357 358 359 360 361 362 363 364

FI

5.0036** 3.2899** 3.8140**

3.2692*

-

0.0424 ns

0.0667 ns

FL

5.2135** 3.3537** 2.0239**

1.9227*

3.6539**

-

0.0315 *

PS

4.9945** 4.0220** 1.8175** 2.8999**

4.3700**

1.8417**

-

365

Fig. 1. Ventral view of the concave surface of a cutworm mandible indicating landmark

366

locations. ams: anterior mandible setae, pms: posterior mandible setae,

367 368

Fig. 2. Wireframe representation of the average mandible shape variation and their

369

corresponding landmarks for the ventral view. AI: A. ipsilon (red), AR: A. robusta

370

(black), FD: F. deprivata (green), FG: F. gypaetina (yellow), FL: F. lutescens (orange),

371

FI: F. irritans (blue), and PS: P. saucia (pink).

372 373

Fig. 3. a) Principal component analysis (PCA) and b) Canonical variate analysis (CVA)

374

comparing the left mandible shape from seven cutworm species. The figures show the

375

first two PCA and CVA axes and the wireframe visualization of the average shape for

376

the species. Different colours and letters indicate the species. AI: A. ipsilon (red), AR:

377

A. robusta (black), FD: F. deprivata (green), FG: F. gypaetina (yellow), FI: F. irritans

378

(blue), FL: F. lutescens (orange) and PS: P. saucia (pink).

379 380

Fig. 4. Regression analysis of Score 1 and the centroid size. Different colours indicate

381

the species testes. AI: A. ipsilon (red), AR: A. robusta (black), FD: F. deprivata (green),

382

FG: F. gypaetina (yellow), FI: F. irritans (blue), FL: F. lutescens (orange) and PS: P.

383

saucia (pink).

384 385

Supplementary Figure 1: Principal component analysis of the average mandible shape

386

(left and right) from seven cutworm species a) using the covariance matrix of the

387

individual shape variation and b) using the covariance matrix of the residual of the

388

multivariate regression after an allometry correction. AI: A. ipsilon (red), AR: A.

389

robusta (black), FD: F. deprivata (green), FG: F. gypaetina (yellow), FI: F. irritans

390

(blue), FL: F. lutescens (orange) and PS: P. saucia (pink).

391

Declaration of interests ☒ The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper. ☐The authors declare the following financial interests/personal relationships which may be considered as potential competing interests:

Author declaration We wish to confirm that there are no known conflicts of interest associated with this publication. All the sources of funding for the work described in this publication are acknowledged in the manuscript.