S. littoralis male antennae expressed a great diversity of esterases
[17] complicating the identification of putative PDEs. The 20 antennal esterases identified to date are distributed among the three choline/carboxylesterase classes described in
[20]. We have focused on
SlCXE7, which belongs to the second class containing mostly extracellular and secreted enzymes.
SlCXE7 clustered within the Lepidoptera-specific clade #001
[21], containing enzymes mostly expressed in larval midgut
[22]. SlCXE7 is notably very close to an
Helicoverpa armigera esterase involved in insecticide resistance, HaCCE001a (accession number FJ997290; 74% of amino acid identity)
[22].
SlCXE7 expression is however clearly restricted to the antennae of adults and larvae, a specific pattern suggesting a specific function in olfaction rather than in xenobiotics detoxication. SlCXE7 is also overexpressed in males, which are specialized in sex pheromone perception, suggesting a possible role in pheromone processing as PDE.
Recombinant SlCXE7 enzyme was indeed able to efficiently hydrolyze the two female sex pheromone components. SlCXE7 affinity for the two pheromone components was high, as revealed by low K
m values comprised between that of ApolPDE
[10] and PjapPDE
[11]. SlCXE7
in vitro turnover numbers (k
cat) were around 0.4 s
−1 with the two pheromone compounds and specific activities were also of the same order (7.6×10
3 M
−1 s
−1 for Z9E11-14:Ac and 10.8×10
3 M
−1 s
−1 for Z9E12-14:Ac). These specific activities are lower than that of ApolPDE from
A. polyphemus (1×10
8 M
−1 s
−1) or of insect juvenile-hormone esterases (between 6×10
6 to 501×10
6 M
−1 s
−1,
[23]) but higher than that of PjapPDE from
P. japonica (2×10
3 M
−1 s
−1, calculated from
[11]). The similar stereochemistry of the two
S. littoralis pheromone components, which only differ by the position of an unsaturation, could possibly account for this close kinetics. In
P. japonica, PjapPDE has been however shown to degrade (R)-japonilure more rapidly than its enantiomer (S)-japonilure, an inhibitor of male attraction
[11].
SlCXE7 expression and regulation in males are consistent with a possible function of this enzyme as a PDE. During development,
SlCXE7 expression level increased rapidly after emergence and reached a maximum in 3-day-old adults. This profile is similar to that of ApolPDE
[10] and other olfactory genes, such as Pheromone-Binding Proteins. These expression patterns were also concomitant with the electrophysiological responsiveness to odorant components
[24],
[25]. Maximum levels of
SlCXE7 expression were also consistent with male reproductive behaviour and short adult lifespan. In our rearing conditions,
S. littoralis males were indeed able to mate rapidly after emergence and they died in 5 to 6 days. We have also observed variations in
SlCXE7 expression level during the scotophase. The highest level was observed during the latter part of the scotophase, in time with maximum male behavioural responsiveness to the sex pheromone
[26]. In addition, in male antennae,
in situ hybridization suggested that
SlCXE7 transcripts were located in olfactory sensilla, including the long trichoid sensilla. These sensilla are mostly tuned to the major pheromone component Z9E11-14:Ac but some lateral long trichoids specifically respond to the minor component Z9E12-14:Ac
[18]. Finally,
SlCXE7 expression level in adult male antennae is induced
in vivo by exposure of males to high dose of Z9E11-14:Ac (50 female/equivalent). As many studies showed that the enzyme substrates are capable of inducing the expression of those enzymes, this suggested that Z9E11-14:Ac might be a physiological substrate for SlCXE7 in adult males. Induction of various xenobiotics-metabolizing enzymes, including CCEs, by xenobiotics or plant allelochemicals from the diet has been well documented in insects (reviewed in
[27],
[28]). Induction of these enzymes by volatiles has been less studied but has been shown recently
[12]. Overexpression of a PDE at the time of maximum responsiveness of males to the sex pheromone and/or when males were subjected to high dose of pheromone, may increase pheromone degradation and thus minimize signal saturation. This mechanism could reduce the adaptation/habituation of ORNs to the pheromone signals, thus maintaining the sensitivity of the pheromone communication system.
Contrary to ApolPDE or PjapPDE, which were only expressed in males
[5],
[10],
[11], SlCXE7 expression was also faintly observed in adult female and in larval antennae.
S. littoralis females are able to detect their own sex pheromone
[18] but their antennae are mostly specialized in plant volatile detection
[29],
[30], because these components play a crucial role for host plant selection before egg laying.
S. littoralis larvae are also known to detect green-leaf volatiles
[31].
In situ hybridization on male antennae suggested that
SlCXE7 transcripts were located in long but also in short trichoid sensilla responding to plant's odorants. These data suggested that SlCXE7 could putatively hydrolyze other odorants than sex pheromones, in larvae and adults of both sexes.
SlCXE7 was indeed able to efficiently hydrolyze
Z3-6:Ac, a green leaf volatile emitted by host plants, especially when they are damaged, and which induced clear antennal responses in both
S. littoralis females
[30] and males
[12]. The k
cat and specific activity of SlCXE7 towards Z3-6:Ac were of 36 s
−1 and 2.4×10
4 M
−1 s
−1, respectively. This turn-over number ranged between the k
cat values obtained for ApolPDE (127 s
−1 [10]) and PjapPDE (1.36 s
−1, calculated from
[11]) with the corresponding pheromones. Another antennal esterase from
S. littoralis, SlCXE10, has been shown to hydrolyze Z3-6:Ac with close kinetics, but contrary to SlCXE7, it was not able to degrade the sex pheromone components
[12]. Moreover, its intracellular location was not in favour of an involvement in signal termination but rather in odorant clearance
[12]. This enzyme belongs to another class of carboxylesterases, suggesting that the structural diversity of antennal esterases could partially reflect their substrate specificities.
SlCXE7 kinetics parameters for the two sex pheromone compounds and the plant volatile were thus different in our
in vitro conditions. Because of a high V
max, SlCXE7 showed higher k
cat for Z3-6:Ac than for the two pheromone components, but because of a high K
m, SlCXE7 affinity for Z3-6:Ac is clearly weaker. In their natural environment, the male search for female sex pheromones occurs in a plant odour rich background. The emission rate of pheromone by a female
S. littoralis is indeed in the order of a few ng/h
[32], whereas the emission rates for a single volatile by a plant are in the range of mg/h, as measured for Z3-6:Ac emission by damaged cotton-plant
[33]. A high affinity for the pheromone components present in minute amounts in the air may be critical for their efficient degradation, whereas a high velocity may be more crucial to degrade a substrate present in high concentrations.
The present study suggests that a same ODE could play a dual role in the degradation of both sex pheromone and plant volatile components. We could presume that rapid degradation of plant volatiles within the pheromone-sensitive sensilla could participate to reduce the background noise. Highly specialized pheromone sensilla from male moths have to face to a variety of odorants during insect life: the ability of a same enzyme to efficiently degrade pheromone components and plant volatiles constitutes an economical system that could participate to maintain the high sensitivity of the sex pheromone detection system.