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Basic bio-ecological parameters of the invasive Red Palm Weevil, Rhynchophorus ferrugineus (Coleoptera: Curculionidae), in Phoenix canariensis under Mediterranean climate

Published online by Cambridge University Press:  08 September 2010

Ó. Dembilio
Affiliation:
Institut Valencià d'Investigacions Agràries (IVIA), Unitat Associada d'Entomologia UJI-IVIA, Centre de Protecció Vegetal i Biotecnologia, Ctra Montcada-Nàquera km 4.5, E-46113-Montcada, Spain
J.A. Jacas*
Affiliation:
Universitat Jaume I (UJI), Unitat Associada d'Entomologia UJI-IVIA, Departament de Ciències Agràries i del Medi Natural, Campus del Riu Sec, E-12071-Castelló de la Plana, Spain
*
*Author for correspondence Fax: +34 964728216 E-mail: jacas@camn.uji.es
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Abstract

The invasive red palm weevil, Rhynchophorus ferrugineus Olivier (Coleoptera, Curculionidae), is one of the most destructive pests of palms in the world. Since its detection in the Mediterranean Basin, the ornamental Phoenix canariensis Hort. ex Chabaud has become its main host. This study was aimed at determining the life cycle of R. ferrugineus in live P. canariensis palms. Egg lethal temperature threshold and thermal constant were determined in the laboratory and resulted in 13.1°C and 40.4 degree days (DD), respectively. A semi field assay was carried out in a mesh enclosure where living P. canariensis palms were artificially infested with neonate larvae at one-month intervals from June 2008 to May 2009 under natural conditions. Infested palms were dissected at different time intervals. Maximum mortality rates for R. ferrugineus were observed for palms infested either in December or January (100%), whereas those infested from April through September showed maximum survival rates. Mean monthly temperatures below 10.3°C were lethal for neonate larvae, as 4.5°C were for older immature stages. All recovered larvae could be classed according to one of 13 instars. A thermal constant of 666.5 DD was estimated for complete larval development. Pupal develoment required an additional 282.5 DD. Based on these results and on the temperatures from 46 climatic stations selected in the Iberian Peninsula, less than one generation per year can be expected in areas with mean annual temperature below 15°C and more than two where mean annual temperature is above 19°C.

Information

Type
Research Paper
Copyright
Copyright © Cambridge University Press 2010
Figure 0

Table 1. Development time and number of instars reported by different authors for R. ferrugineus feeding on different substrates.

Figure 1

Fig. 1. Development rate (line) and egg hatching (bars) of R. ferrugineus eggs exposed to different temperatures. The line represents the linear regression used to estimate LTT (y=0.0269×x–0.3512; LTT=13.1°C). Each bar is the mean of three groups of ten eggs less than two hours old.

Figure 2

Fig. 2. Survivorship of R. ferrugineus neonate larvae artificially introduced into P. canariensis palms. Each bar is the mean of 12 palms infested with 16 neonate larvae per month. Bars with the same letter are not statistically different (Kruskal-Wallis K=165.913; P<0.0001).

Figure 3

Fig. 3. Survivorship of R. ferrugineus immature stages in P. canariensis palms. Each bar is the mean of 7–25 palms (see number in parenthesis below each month) dissected each month. Palms were originally infested with 16 neonate larvae. Bars with the same letter are not statistically different (Kruskal-Wallis K=70.266; P<0.0001).

Figure 4

Fig. 4. Mean, maximum and minimum temperatures registered in the mesh enclosure where infestations took place. , Mean; ; Min.

Figure 5

Table 2. Relationship between mean monthly mortality of R. ferrugineus larvae (y) and mean monthly temperatures (x=maximum, Tmax; minimum, Tmin; and mean, Tmean) registered during the assay (2008–2009). 2a. Mortality of neonate larvae (see Fig. 2). 2b. Mortality of immature stages (see fig. 3).a. Neonate mortality

Figure 6

* b. Immature mortality

Figure 7

Fig. 5. Head capsule width distribution of R. ferrugineus larvae reared in P. canariensis. The lines are the individual instar distributions. Graphs produced by Hcap (Logan et al., 1998).

Figure 8

Fig. 6. Linear regression between the natural logarithm (loge) of mean larval head capsule width (y) and instar number (x) of R. ferrugineus larvae reared in P. canariensis.

Figure 9

Fig. 7. Linear regression between head capsule width and larval weight of R. ferrugineus larvae reared in P. canariensis.

Figure 10

Table 3. Number of instars of R. ferrugineus, including the mean, size and probability of misclassifying of head capsule width generated by Hcap program (Logan et al., 1998).

Figure 11

Table 4. Mean values and standard deviation of lengths and widths of head capsule, labrum and clypeus and mandible length (mm) of R. ferrugineus larvae reared in P. canariensis.

Figure 12

Table 5. Relationship between larval head capsule width and other larval head measurements of R. ferrugineus larvae reared in P. canariensis.

Figure 13

Fig. 8. Relationship between mean head capsule width per instar and cumulated heat units (DD) above lower temperature threshold (15°: Martín & Cabello, 2006) for R. ferrugineus larvae reared in P. canariensis.

Figure 14

Fig. 9. Map of the Iberian Peninsula showing mean annual temperatures (MAT) (Ninyerola et al., 2005). Dots represent the 46 climatic stations where the number of generations of R. ferrugineus per year was estimated based on the regression shown in table 6, which uses MAT as independent variable.

Figure 15

Table 6. Linear relationships between the number of annual generations of R. ferrugineus estimated in 46 climatic stations in the Iberian Peninsula (see fig. 9) and mean annual temperatures (MAT), mean maximum temperatures (MMT) and mean minimum temperatures (MmT).