Background

The mealy bug ladybird, Cryptolaemus montrouzieri (Mulsant) (Coleoptera: Coccinellidae), is one of the most important biological control agents that preys upon a wide range of mealy bug species in many parts of the world (Simmonds et al. 2000). Both larvae and adults feed on all stages of mealy bugs, (Jayaraman et al., 1988). The first introduction of this ladybird for biological control dates back to 1891 when Albert Koebele brought it into California for control of Planococcus citri Risso (Bartlett 1974). Since then, the beetle has been introduced into several countries in biological control programs with varied success (Dixon 2000). The predator was introduced to Turkey from the USA in 1965 to control P. citri on citrus trees (Oncuer and Bayhan 1982), and it was introduced to Syria from Turkey in 1995; since then, it is reared at the Lattakia Center for Rearing Natural Enemies, Tartous Research Center and Biological Control Studies and Research Center. Rearing program of the predator in Syria aims to mass rear and release it periodically during the season to control citrus mealy bug in the western coast of Syria (Al-Khateeb and Asslan 2007; Al-Khateeb et al. 2012; Al-Khateeb and Raie 2002).

Population ecology is an essential component in the practical application of natural enemies in controlling pests, but the importance of genetics and adaptive evolution in biological control remains a controversial topic (Hufbauer and Roderick 2005; Phillips et al. 2008). The genetically improved natural enemies (predators, parasitoids and pathogens) might be the next level biological weapons against the pest populations in agricultural systems (Routray et al. 2016). Therefore, genetics research on insect natural enemies is rare and basically limited to parasitoid wasps and a few predators. The understanding of inbreeding is one of these genetic bases because traits may deteriorate rapidly through inbreeding (Jervis 2007). During the production phase of insects in the laboratory, some individuals can contribute randomly to the next generation more than others and this sampling effect can lead to a random loss of some alleles in each generation. This process is called a genetic drift and can lead to a substantial reduction in the genetic variability within the reared population. Therefore, inbreeding program is necessary as the first step to begin the genetic improvement programs because it is the most effective in increasing the levels of homozygosity and increasing the frequency of wanted and unwanted alleles and to increase the effectiveness of genetic selection (Jervis 2007). Estimation of genetics parameters of quantitative traits of the target species is necessary to create an artificial selection and expressed in values. The phenotypic value of an individual can be measured relative to the population mean, and the genetic structure of a population refers to the amount and distribution of genetic variations within and between populations (McDonald 1997). If the variation in a quantitative trait is, at least in part, genetically determined, then offspring should resemble their parents.

The heritability (h2) (the broad-sense heritability) is the most important genetic value. It is the ratio between the genetic variance and the total phenotypic. The general effect of the environment may seriously bias estimates of genetic variances and heritability. The estimation of h2 is necessary to establish an artificial selection or selection index. Artificial selection has been suggested as a method of improving the effectiveness of the natural enemies during mass-rearing (Rutledge and Wiedenmann 2003). Hazel (1943) introduced the analytical method for calculating a selection index. Creating an artificial selection contributes to estimate the relative economic values of the economically important traits, where the selection is based on the final outcome of the important traits and allows an excellent trait to cover the defects in another lower quality trait. Literature shows that the selected index is one of the helpful tools in this process, because it allows multiple traits to be selected simultaneously.

Due to the rarity of genetic studies related to C. montrouzieri and no selection index of it was reported before, this study was carried out to create an artificial selection of the most important economic characteristics: fecundity, preying potential of the 3rd larval instar, and larval developmental period which may contribute to raising the indicators of the biological efficacy of the predator.

Materials and methods

Rearing of Planococcus citri (Risso)

The potato was used as a host for P. citri. Successful rearing required using a suitable variety of potato; Sponta has proved to be one of the best varieties for rearing P. citri, due to its ability to withstand the conditions of storage, speed to break dormancy stage at a temperature of 4 ± 1 °C and speed giving branches in a short period. The potatoes were kept under a dark condition, at a temperature of 10–12 °C and 60 ± 10% RH inside plastic containers until branches reach 10–15 cm. P. citri was a preferable insect prey species because of its short life cycle and its fecundity under the conditions of 25 ± 2 °C, 60 ± 10% RH, and 16:8 light to dark (L:D), using the same plastic containers. Potato stems (10–15 cm long) were prepared to be infested with P. citri, using slices of smooth, clean papers, and placed on P. citri. The leaves were transferred to darkness to obtain new growths. Repetition of this process was undertaken twice a day to get a pure infestation. Thirty to 45 days were needed to reach the complete infestation and obtaining different instars of P. citri.

Rearing of Cryptolaemus montrouzieri Mulsant

The techniques of Smith and Armitage (1931) and Whitcomb and Bell (1964) for rearing C. montrouzieri were followed. Adults of the predator were released on the branches of infested potatoes with P. citri, under the conditions of 25 ± 2 °C temperature, 60 ± 10% RH, and 16:8 light to dark (L:D), inside the same plastic containers.

First parental laboratory generation (Po)

The experiments were carried out (with 30 replicates), using a glass cage (2/l), covered with a soft cloth. Each cage had 2 tubers of potato, infested with P. citri and one pair (1♂+1♀) of C. montrouzieri, isolated from the stock culture, to establish the first parent generation (Po). The cages were placed in an incubator under the conditions of 25 ± 2 °C, 60 ± 10% RH, and 16:8 light to dark (L:D); after hatching of C. montrouzieri newly larvae in the containers, 30 newly hatched larvae were isolated from each replicate and then transferred to Petri dishes with the branches of potatoes infested with P. citri to develop to C. montrouzieri adults in order to study the morphobiological parameters of the predator.

Genetic improvement lines of the predator

  1. 1.

    The control line. The paternal pair was chosen randomly for each replicate at the beginning of each generation, from the previous generation, through the inbreeding 12 generation program.

  2. 2.

    The first quantitative trait (fecundity). The selection was based on one quantitative trait assumed to be polygenic (female fecundity (Fec.)). The parent pair was selected according to the highest fecundity of female.

  3. 3.

    The second quantitative trait (preying potential of the 3rd larval instar). The selection was based on the quantitative trait (preying potential, potential of the 3rd larval instar (PPLI)). The parent pair was selected for the next generation, according to the highest preying potential of the 3rd larval instar.

  4. 4.

    The third quantitative trait (larval developmental period). The selection was based on the quantitative trait (larval developmental period (LdP)). The parent pair was selected for the next generation, according to the highest (larval developmental period).

All traits + the control consisted of 30 replicates/each, and the selection was conducted in order to improve and increase this trait through the 12 inbreeding generations and to calculate its economic value to be included in the selection index. Morphobiological indicators in all lines were calculated at the end of Po, F1, F3, F6, and F12.

  1. 1.

    Genetic parameters were calculated at the end of F12.

  2. 2.

    Correlation relationships were calculated in Po and F12 in the control.

Calculated morphobiological parameters

  1. 1.

    Length of female: by using millimeter lens.

  2. 2.

    Fecundity: calculation based on the number of the newly hatched larvae.

  3. 3.

    Reproduction: number of adults produced by one female.

  4. 4.

    Survival rate: reproduction/fecundity × 100.

  5. 5.

    Preying potential of adults for female (P. citri nymphs/day). One hundred nymphs/3rd nymphal instars of P. citri were kept in Petri dishes (9-mm diameter), 30 replicates for females, for each generation and for each line. The Petri dishes were checked daily, and the number of nymphs consumed by C. montrouzieri individual was recorded in 3 days, and then the average daily predation rate was recorded.

  6. 6.

    Preying potential of 3rd larval instar: by the same way was recorded.

  7. 7.

    Developmental period: the period (days) from eggs to adults.

  8. 8.

    Larval developmental period: the period (days) from hatching 1st larval instar to the pupation.

Experimental design and statistical analysis

Experiments were carried out using the Randomized Complete Block Design. Obtained data were subjected to ANOVA test, using the computer software package SPSS V.18 to determine Duncan’s multiple range tests at probability 1%. Parameter response for each line of genetic improvement of the predator at the end of the 12th generation was calculated as follows:

Inbreeding depression/parameter response = [(F12-P0)/F12] × 100 (Oupadissakoon and Wersman 1977).

Estimation of genetic parameters

  • Genetic, phenotypic, and environmental variances were calculated according to the following formulas:

$$ \mathrm{VP}\kern0.5em =\kern0.5em \mathrm{VG}+\mathrm{VE} $$
(1)
$$ \mathrm{VE}\kern0.5em =\kern0.5em \mathrm{MSE} $$
(2)
$$ \mathrm{VG}\kern0.5em =\kern0.5em \left(\mathrm{MST}\hbox{-} \mathrm{MSE}\right)/\mathrm{r} $$
(3)

where VP is the phenotypic variance, VG is the genetic variance, VE is the environmental variance, R is the number of replications for each generation, MST are the mean squares between groups (between generations), and MSE are the mean squares within groups (error).

  • Broad sense heritability h2bs = VG/VP × 100 (4). Formulas (1), (2), (3), and (4) were estimated according to (Falconer 1989).

  • To compare the variations among traits, phenotypic coefficient of variation (PCV), genotypic coefficient of variation (GCV), and environmental coefficient of variation (ECV) were computed, according to the method suggested by Singh and Chaudhary (1985) (5, 6, 7): PCV = (√Vp/X) 100 (5), GCV = (√Vg/X) 100 (6), and ECV = (√Ve/X) 100 (7)

Where X is the grand mean for each of the studied traits.

  • Artificial selection (selection index) was calculated according to the following formulas: I = b1x1 + b2x2 + b3x3 (Hazel 1943)

where I is the index value and b1, b2, and b3 are economic values (index weights) of the quantitative traits (fecundity, preying potential of the 3rd larval instar, larval developmental period), respectively. x1, x2, and x3 are phenotypic information sources and refer to the same quantitative traits.

  • Economic value (b) was calculated according to the following formula:

b = P−1Gv

where P−1 is the inverse of the phenotypic variance, G is a matrix of the genetic variance, and v is the relative economic values of objective traits. Relative economic values were calculated according to fecundity trait as the primary trait.

Results and discussion

Changes in morphobiological parameters of C. montrouzieri for 12 inbreeding generations

Results in Table 1 and Figs. 1, 2 and 3 showed that there were significant decreases in all quantitative traits under control line, the numerical value of the female length decreased from 4.58 mm in Po to 4.13 mm in F3, and insignificant decrease between F3 and F6, F9, and F12, which confirms that three generations of inbreeding were sufficient to reflect the values depression of this trait due to increased expression of recessive alleles and the inbreeding depression recorded (− 16.81%).

Table 1 Changes in morphobiological parameters (mean ± SD) of the predator C. montrouzieri for 12 inbreeding generations using three genetic improved lines
Fig. 1
figure 1

Changes in the fecundity according to the change of genetic improved lines

Fig. 2
figure 2

Changes in the preying potential of 3rd larval instar (P. citri nymphs/day) according to the change of genetic improved lines

Fig. 3
figure 3

Changes in the developmental period according to the change of genetic improved lines

Fecundity was more affected by the control line (Fig. 1), decreased significantly from 134.97 in Po to 107.83 in F3, and continued a significant depression to F9. It was 87.90 less than the insignificant decrease at F12. Thus, fecundity trait required nine inbreeding generations to express its response to the pattern of inbreeding recording (− 42.28%) at the end of F12.

For the reproduction, the value of this trait decreased significantly from 121.97 in Po to 93.57 in F3 and continued this regression to 80.03 in F6. F6 was an equilibrium point because the differences were insignificant between F6 and each of F3, F9, and F12 and six inbreeding generations were sufficient to express its response to the control line, recording (− 46.93%) at the end of F12.

As well, the survival rate decreased significantly from 89.74% in Po to 86.41% in F3, with insignificant differences between F3 and each of F9 and F12 and inbreeding depression recording (− 7.66%) at the end of F12.

The results showed that the preying potential of the 3rd larval instar (Fig. 2) recorded significant differences during the studied generations. It decreased significantly from 27.06 larvae/day in Po to 21.42 larva/day at F12 with a response − 20.84%. As for the preying potential of female, six generations of inbreeding were sufficient to express their response to the inbreeding line, recording (− 21.71%) at the end of F12. The larval developmental period (Fig. 3) decreased significantly from 14.87 day in Po to 12.63 day at F12 and the response was − 15.06%. Developmental period was characterized by equilibrium and stability from Po to F12 with insignificant differences during the studied generations. The response recorded (− 1.31%).

Changes in morphobiological parameters of C. montrouzieri for the first genetic improved line/the first quantitative trait (fecundity), through inbreeding in 12 generations

Results in Table 1 and Figs. 1, 2 and 3, for fecundity improvement in lines within inbreeding program of the predator, showed that the length of female increased significantly from 4.51 mm in Po to 4.90 mm in F3, while its height was stabilized until the end of F12, with insignificant differences. This increase in the value of this indicator was offset by the depression in the control line and for three generations, which confirms that the female length needed three generations of successive breeding to reflect the alleles isolation of this trait, the female length response for this improvement line in F12 was (+ 9.53%), with significant differences from the control line (− 16.81%). Which confirms that the improvement of fecundity had led to improve the length female due to the positive correlation between them (r = 0.81 in Po and r = 0.63 in F12) (Tables 1 and 2).

Table 2 Correlation relationships between quantitative traits of C. montrouzieri during Po and F12 in the control line

For the fecundity, it responded to the line of recurrent selection from the first isolation generation F1 to F12. The fecundity increased significantly from 138.20 in Po to 157.83 at F1 to 171.90 at F3 (Table 1). In F6, fecundity recorded 182.90 with insignificant differences with F9 and significant differences with F12. Response recorded + 40.96%. It was almost equal to the inbreeding depression in the control line with significant differences in all studied generations.

The value of reproduction increased significantly from 126.43 in Po to 174.20 at F12; the response for this selection line recorded + 37.78 to approach the inbreeding depression of this indicator in the control line.

This significant increase in reproduction indicator was a result of the positive correlation between the fecundity and reproductive indicator (0.99 and + 0.76, respectively) (Table 2).

As for the survival rate trait, this genetic improvement line did not affect significantly the numerical changes of its values during the studied generations. The response was − 2.09% at the end of F12, despite the positive correlation between fecundity and survival rate at 0.01% were + 0.73 and 0.56 at Po and F12 in the control line, respectively (Tables 1 and 2). This correlation contributed to maintain the values of this indicator from depression compared with the control line and response was (− 7.66%) at F12.

Statistical analysis showed that this improvement line could not raise the values of other traits (preying potential of 3rd larval instar, preying potential of female, and larval developmental period). In addition, it could not even keep this trait from depression and was close to control line, and their response of this line were − 15.84, − 27.81, and − 11.10%, respectively, compared with control line − 20.84, − 21.71, and − 15.06%, respectively.

For the development period trait, despite the positive increase achieved by this improved line and response recording (2.64%), compared to the control line (− 1.31%) and insignificant differences through studied generations, but this increase was in favor of an increase in the eggs and pupal stages, which are non-predatory and non-economic stages.

Changes in morphobiological parameters of C. montrouzieri for the second quantitative trait (preying potential of the 3rd larval instar) through inbreeding in 12 generations

Results in Table 1 and Figs. 1, 2 and 3 showed that the recurrent selection of this trait for 12 inbreeding generations contributed to the increase of the values of preying potential of the 3rd larval instar with significant differences from 24.20 nymphs/day in Po to 27.03 at F3 and to 28.18 at F9 and with insignificant differences between F9 and F12. The preying potential of the 3rd larval instar response to selection recorded + 22.81% at the end of F12 and was almost equal to the inbreeding depression in control line, recording − 20.84%.

Despite the positive correlation between preying potential of the 3rd larval instar and preying potential of female, recording + 0.44 and + 0.32 in Po and F12 in control line, respectively (Table 2). This did not affect the improvement of the numerical values of this indicator, and the differences remained insignificant through the studied generations. The positive effect of this selection was to maintain the values of this indicator of depression when compared with the control line.

For the other traits (female length, fecundity, reproduction, survival rate, larval developmental period), their values were decreased significantly from Po to F12, similar to the control line.

For developmental period, despite its height and significant differences from Po to F12, this increase was not real and unimportant, because the developmental period increased, while the larval developmental period decreased. The increase was in favor of resting stages and non-predatory.

Changes in morphobiological parameters of C. montrouzieri in the third quantitative trait (larval developmental period) through inbreeding in 12 generations

Results in Table 1 and Figs. 1 and 3 showed that the recurrent selection of this trait for 12 inbreeding generations was contributed to the increase of the value of larval developmental period with significant differences. The value of this trait increased from 12.17 days in Po to 13.77 days at F1 and to 14.80 days at F3. The differences remained insignificant between F3 and F9 and increased to 15.07 days at F12 with significant differences. The first segregation generation was the most important generation in showing the value of this attribute and its response to the line of selection and was + 23.83% at F12.

The significant increase in the value of the development period was from 29.63 days in Po to 31.43 days at F12 due to the positive correlation between these two indicators and was + 0.37 and + 0.30 in Po and F12, respectively (Table 2).

For the other traits (female length, fecundity, reproduction, survival rate, preying potential of the 3rd larval instar, preying potential of female), the values of these indicators decreased significantly from Po to F12, similar to the control line.

The genetic effect in raising predator indicator values appeared either directly in cases where the indicator was used within its own genetic improved line (fecundity, preying potential of the 3rd larval instar, and larval developmental period) or indirectly through positive correlation (between indicators) within the same improvement line, while every genetic improved line did not affect to the raising of other indicators when compared to control and other improved lines (Table 1) and Figs. 1, 2 and 3).

The inbreeding can have a number of negative effects in many quantitative traits and is related to loss of heterozygosity or to increase the expression of recessive alleles (Charlesworth and Charlesworth 1999). Obtained results agree with several researchers about inbreeding depression that has been demonstrated to negative affection in many quantitative traits of insect, female fecundity (Henter 1993; Tanaka 1993; Roff and DeRose 2001; Van Oosterhout et al. 2000), adult size (e.g., Armbruster et al. 2000; Reale and Roff 2003) and larval development time (Morjan et al. 1999; Roff 1998). Fox and Scheibly (2006) reported that the seed beetle Stator limbatus exhibited substantial inbreeding depression at all stages of development. Eggs from sib mating were less likely to develop and hatch, and larval mortality was higher and development time longer for offspring of sib mating. Nakamura (1996) stated that decreases in adult emergence and host mortality were observed after two generations of inbreeding in the fly Exorista japonica, and Al-Khateeb et al. (2012) reported that the most morphobiological parameters of C. montrouzieri were significantly reduced after six generations of inbreeding but inbreeding is not always disadvantageous, because it leads to greater genetic variance among progenies and may increase the expected genetic gain with selection (Falconer 1989; Jervis 2007; Paterniani and Miranda Filho 1987).

Correlation between the most important quantitative traits of the predator C. montrouzieri

Results in Table 2 showed that there were positive significant correlations between fecundity and each of length of female, reproduction, and survival rate during Po and F12 which were + 0.81, + 0.63, + 0.99, 0.76, 0.73, and 0.56, respectively, and negative correlation between fecundity and other indicators (preying potential of the 3rd larval instar, preying potential of female, larval development period and development period) during Po and F12 which were − 0.516, − 0.38, − 0.46, − 0.33, − 0.28, − 0.17, − 0.15, and − 0.19, respectively.

As shown in Table 2, the studied quantitative traits can be categorized into three groups:

  1. 1.

    The first group included the important indicators that have positive correlations among them (fecundity, female length, reproduction, and survival rate) and concerned with the expression of the fecundity.

  2. 2.

    The second group concerned with the expression of the feeding potential represented in the (preying potential of the 3rd larval instar and preying potential of female) with superiority to the preying potential of the 3rd larval instar. This is an important trait for predatory insects that are used in integrated pest management program.

  3. 3.

    The third group concerned with the expression of larval development period and development period traits. The larval development period showed a greater advantage in the extent to which it fluctuate values. It was the real predatory stage and represented the predation economic age, while the development period was moved away from the practical expression of this concept due to the existence of the resting, non-economic and non-predation phases (egg and pupal stage).

Fecundity is an important life history trait in understanding population dynamics, because it is one of the bases from which population changes are determined through the incidence of environmental factors (Honek 1993; Richerson et al. 1978). Therefore, fecundity was served as the primary trait in the research. The relationship between fecundity and adult body size in many insects has been studied (Honek 1993). Obtained results agree with Honek (1986) who reported that in insects, there is a strong positive correlation between female size and its fecundity, reproduction, and survival, and with Zheng et al. (1993) who stated that in predators, larger females have a shorter preoviposotional period than smaller ones and this may contribute to their higher fecundity.

Obtained results agree with the finding of Asslan et al. (2008) who stated that the fecundity of the predator Coccinella septempunctata was correlated positively with the female length, reproduction, and survival rate. The correlation coefficient between them was + 0.8, + 0.7, and 0.5, respectively, and Al-Khateeb (2013) reported that the fecundity of the predator C. montrouzieri was correlated positively with each of adult size, reproduction, and survival and the correlation coefficient between them was + 0.91, + 0.99, and + 0.63, respectively in the parent generation.

Results presented in Table 3 showed that the phenotypic variance was higher than the genotypic one in the control line for fecundity trait and was 1019.09 and 483.48, respectively. Similarly, the phenotypic variation coefficient was higher than the genetic variation coefficient and was 30.39 and 20.93%, respectively. The broad sense heritability (h2bs) was 47.43% which was a moderate percentage and that had an environmental impact.

Table 3 Estimation of the important genetic parameters of quantitative traits included in the artificial index of C. montrouzieri among 12 generations of inbreeding

When the fecundity was introduced in the genetic improved line within inbreeding program, the genetic variation coefficient (GCV) increased (12.16%) compared with the (PCV) (15.24%) and h2bs increased to 63.70% which was higher and was confirmed as the high genetic balance of this trait to determine the phenotypes of its individuals.

The positive significant correlation between fecundity and each of length of female, reproduction, and survival rate, during Po and F12, which were + 0.81, + 0.63; + 0.99+, 0.76; and + 0.73, + 0.56 (Table 2), respectively, increased the value of these traits together when subjecting them to breeding and selection programs (direct or multiple quantitative traits). Obtained results agree with the finding of Falconer and Mackay (1996) and Jervis (1997) who stated that the high values of the genetic variation coefficient of quantitative traits indicate that it can be used as a selection tool based on the phenotypic expression of these traits because the difference between the phenotypic variation coefficient and the genetic variation coefficient is low and thus increases the chances of selection and the possibility of genetic improvement. Jervis (2007) reported that the higher the GCV value, the higher the probability of the success of selection.

Statistical analyses showed that the h2bs increased from (31.66%) in control line to (40.80%) in the second quantitative trait (preying potential of the 3rd larval instar) (Table 3). This reflected the medium genetic stock and the effect of the environmental factors controlling the expression of this trait. The positive significant correlation between preying potential of the 3rd larval instar and preying potential of the female will increase the value of this indicator when this trait included in genetic improvement programs.

As for the larval developmental period, there were differences between the value of genetic variance and phenotypic variation in the control line and were (0.65, 3.77), respectively. These differences were reflected in the values of the PCV %, GCV% and h2bs and were 14.45, 6.0, and 17.27%, respectively.

These differences remained significant in the artificial selection program (third line) through 12 inbreeding generations. Despite a slight improvement in h2bs, it remained low and was 33.50%. This indicates the significant impact of environmental factors on the expression of this trait and its genetic stock was low. In order to improve this trait, it must be used in the selection index/artificial selection. Estimate the level of heritability h2bs is the most important genetic value in order to include and represent it in the artificial selection: a low h2bs (less than 0.4), a moderate h2bs 0.4–0.6, and a high h2bs (greater than 0.6).

Constructing equation of selection index/artificial selection

The construction of the selection index included three quantitative traits (fecundity, preying potential of the 3rd larval instar, and the larval developmental period). Fecundity was served as the primary trait in the research.

$$ {\displaystyle \begin{array}{l}I=\mathrm{b}1\mathrm{x}1+\mathrm{b}2\mathrm{x}2+\mathrm{b}3\mathrm{x}3\\ {}\begin{array}{l}b={P}^{\hbox{-} 1} Gv\ \\ {}\mathrm{b}1={(688.85)}^{\hbox{-} 1}(438.71)\ (1)\\ {}\mathrm{b}1=0.637=0.64\\ {}\mathrm{b}2={(9.37)}^{\hbox{-} 1}(3.83)\ (8.58)\\ {}\mathrm{b}2=3.502=3.5\\ {}\mathrm{b}3={(3.42)}^{\hbox{-} 1}(1.15)\ (14.18)\\ {}\mathrm{b}3=4.751=4.75\end{array}\\ {}I=0.64\left(\mathrm{x}1\right)+3.50\left(\mathrm{x}2\right)+4.75\left(\mathrm{x}3\right)\end{array}} $$

Results in Table 4 showed that the relative economic values of the three quantitative traits (fecundity, preying potential of the 3rd larval instar, and the larval developmental period) were 1, 8.58, and 14.18, respectively.

Table 4 Economic values of the fecundity, between preying potential of the 3rd larval instar and the larval developmental period

After solving the system of normal equations, the selection index was termed:

\( \mathit{\mathsf{I}}=\mathsf{0.64}\left(\mathsf{x1}\right)+\mathsf{3.50}\left(\mathsf{x2}\right)+\mathsf{4.75}\left(\mathsf{x3}\right) \), while I was the index value and b1 = 0.64, b2 = 3.50, and b3 = 4.75 were the index weights and refer to the three studied quantitative traits (Table 4). x1, x2, and x3 are phenotypic information sources and also refer to the studied quantitative traits, respectively.

Conclusions

The created artificial selection can serve as a simple and fast way to rank the predator and can be applied it in the next genetic improvement programs of C. montrouzieri, according to its high value to be parents for consecutive generations. Based on the results of this research and the correlation relations that were organized, according to the three groups, the use of these traits in the artificial selection may allow the other traits to be raised and the fecundity trait, which was served as the primary trait in the research, leads to the removal and coverage of the defects of both traits (preying potential of the 3rd larval instar and the larval developmental period), and thus was the best way to raise the most important indicators of the bio-efficiency of the predator.