We report on the correlation between reduced ALP protein, activity, and mALP expression levels in strains of three species in the Noctuidae Family with diverse resistance phenotypes against Cry toxins. Currently,
H. virescens is efficiently controlled by transgenic Bt cotton
[38], but numerous reports highlight the potential for the development of field resistance to Bt crops in
H. armigera [39],
[40],
[41], while field-evolved resistance to Bt toxins and Bt corn has already been reported for
S. frugiperda [3],
[27]. Considering that the
H. virescens resistant strains in this study present unique alterations in toxin binding
[21],
[22], processing of toxin
[24], or midgut regeneration
[42],
[43], our data suggest that reduced mALP expression is a potential biomarker for resistance to diverse Cry toxins and is independent of the resistance mechanism. Furthermore, our data with Cry-resistant Noctuidae suggests that reduced mALP is a common phenomenon in Bt-resistant lepidopteran larvae.
Even though no correlation between ALP activity levels and resistance to insecticides has been reported in the literature to date, reduced ALP activity levels in insects have been reported to occur after intoxication with lectins
[44], infection with cytoplasmic polyhedrosis virus (CPV) or
B. thuringiensis in
B. mori [45], and microsporidia in
Barathra brassicae [46]. However, decreased ALP activity appears to be specific to only certain pathologies, since it was not observed after infection of
B. mori with nuclear polyhedrosis virus (NPV) or
Serratia marcescens [45]. These observations suggest that although monitoring methods based on reduction in ALP activity levels would allow detection of resistance to Bt toxins, it may need to be combined with additional biomarkers to assure accurate detection of resistance. Another limitation of using reduced ALP levels in monitoring for resistance to Cry toxins is that, considering that in most cases Bt resistance is recessive, heterozygote larvae present similar levels of HvmALP and ALP activity as susceptible parents
[31]. To overcome these limitations, we expect that further characterization of the molecular mechanism involved in reduction of ALP levels in Bt-resistant larvae would result in identification of specific alleles to target in designing DNA probes for real time RT-PCR capable of discriminating heterozygotes and ALP reduction due to Bt resistance or infection by entomopathogens.
Previous reports have suggested that direct interaction between
B. thuringiensis Cry toxins and lepidopteran midgut ALP results in decreased ALP activity
[47],
[48]. However, our data on the reduction in ALP activity in resistant insects was independent of feeding on Cry-contaminated diet, or on diet composition, as larvae used in our work were reared on diverse diets (including fresh corn leaf tissue) and were not exposed to Cry toxins before dissection. This observation may suggest that a method based on detection of mALP down-regulation would detect Cry-resistant larvae regardless of larvae feeding on transgenic Bt crops or non-Bt refugia.
Considering that mALP has been proposed as receptor for Cry toxins in
M. sexta [49],
H. virescens [30],
H. armigera [50],
[51],
Aedes aegypti [52],
Anopheles gambiae [53], and
Anthonomus grandis [54], down-regulation of mALP expression may result in reduced Cry toxin binding to the brush border membrane in resistant insects. However, we detected HvmALP down-regulation in CXC and KCBhyb larvae, while Cry1Ac binding in BBMV from these larvae was not altered when compared to vesicles form susceptible insects
[21]. Since Cry1Ac has multiple binding sites in
H. virescens BBMV
[55], and Cry1Ac binding to HvmALP has not been quantified to date, it is possible that changes in Cry1Ac binding due to reduced HvmALP levels are masked by binding to alternative receptors in the BBMV. However, CXC and KCBhyb larvae are cross-resistant to Cry2Aa toxin, which does not share binding sites with Cry1Ac
[56].
Mammalian ALP transcript expression is modulated by members of the mitogen-activated protein kinase (MAPK) family. For example, the p38 kinase-dependent pathway modulates changes in ALP activity levels during development or stress in human osteoblast-like
[57],
[58] and intestinal cells
[59]. The homologous p38 pathway in
Caenorhabditis elegans [60],
[61], in
Manduca sexta, and
A. aegypti [62] controls the gut defense response against Cry intoxication. Considering this information, it is possible that reduced ALP levels in Cry-resistant insects reflect a constitutively expressed enhanced defensive response to intoxication, as previously suggested for
Ephestia kuehniella [63] or some of the
H. virescens resistant strains tested in our work
[42],
[43]. Based on reported functions for insect ALP enzymes
[64], we expect the gut ALP isoforms down-regulated in the tested Bt-resistant larvae are involved in digestion and gut development. However, down-regulation of these enzymes seems not to affect insect development or survival in the field, as larvae from the 456 and 512 strains of
S. frugiperda used in this paper were generated from field-collected eggs
[27] and do not present affected development when reared on corn leaf tissue compared to susceptible insects (data not shown). Lack of a direct correlation between reduced HvmALP levels and levels of resistance in the tested
H. virescens strains does not support a direct role for HvmALP in resistance, although multiple resistance mechanisms are present in these insects
[21],
[22],
[65]. Further research is needed to determine whether correlation between reduced levels of mALP expression and resistance represents a direct decrease in functional Cry toxin receptors and/or compensatory alterations in resistant larvae.
Development of insect resistance is one of the most crucial issues related to increased adoption rates for transgenic Bt crops. As with other insect pest groups, monitoring for heliothine resistance to Bt is currently performed using the F1 or F2 screening test
[38],
[66], which are lengthy and labor intensive. As a monitoring alternative, DNA-based methods would greatly increase sensitivity and speed of detection of resistance alleles, but their development is dependent on the identification of resistance alleles. Cadherins that serve as high affinity Bt toxin receptors have been proposed as optimal targets for the development of DNA-based strategies to detect resistance to Cry toxins in field pest populations
[17],
[67]. However, cadherin resistance alleles have not been detected in field populations of
P. gossypiella and
H. virescens [18],
[68], possibly due to the low frequency of Bt resistance alleles in field populations. In the case of
P. gossypiella screening, extensive parallel bioassay evidence indicated that cadherin alleles linked to resistance were rare or absent in
P. gossypiella populations screened by PCR
[69]. Recent reports suggest that the existence of multiple cadherin resistance alleles in field populations of
H. armigera may hinder successful screening when using DNA-based methods to detect specific cadherin resistant alleles
[70]. More recently, lack of expression of an ABC transporter protein in
H. virescens has been demonstrated to result in lack of Cry1Ac binding and resistance to this toxin, supporting a potential role for this protein during Cry1Ac intoxication
[65]. However, monitoring for alterations in Cry toxin receptors, as in the case of cadherin or ABC transporter-based monitoring methods, would only be effective in detecting resistance to Cry toxins binding to these receptors. The introduction of pyramided Bt crops represents increased levels of selection for resistance mechanisms to diverse Cry toxins that do not share receptors. In addition, other mechanisms not involving cadherin modifications are associated with resistance phenotypes
[5]. Based on our data, reduced ALP expression represents a biomarker that would detect resistant insects independently of the resistance mechanism or cross-resistance phenotype. Therefore, a biomarker not based on individual DNA sequence but rather diagnostic of a phenotype associated with resistance to Cry toxins, such as the one identified in this study, would be desirable in the development of monitoring methods. Future work aimed at developing effective and sensitive Bt-resistance monitoring methods will include characterization of the molecular mechanism resulting in ALP down-regulation, testing the range of mALP expression in natural field populations, and optimizing biochemical detection of ALP activity associated with resistance alleles in field populations.