Introduction

 

The tobacco/silver leaf whitefly, Bemisia tabaci Gennadius (Hemiptera: Aleyrodidae) occurs in most parts of the world; is an important agricultural pest, and causing economic damage to crops (Palumbo et al. 2001). It has been listed as one of the world’s 100 worst invasive alien species (Lowe et al. 2000) and infesting more than 600 host plant species (DeBarro et al. 2011; Li et al. 2011) including cassava, cotton, sweet potatoes, tobacco, tomatoes (https://www.cabi.org/isc/datasheet/8927), and cucurbits (Dennehy et al. 2010; Cameron et al. 2014) . Adults and nymphs of B. tabaci damage plants by sucking nutrients and through the excretion of honeydew which reduces plant growth and yield by interfering photosynthesis (Jones 2003). B. tabaci also transmits more than 100 different plant viruses during feeding (Hogenhout et al. 2008) including Tomato Yellow Leaf Curl Virus (TYLCV) in tomato (Berlinger 1986).

B. tabaci was reported as a serious pest of tomato in 1997 from Oman (Azam et al. 1997) and was also recorded from eggplant, cucumber and melon (Kaakeh et al. 2007). The TYLCV was isolated from tomato in 2008 (Khan et al. 2008). The infected plants my show vein/inter-vein or leaf yellowing, yellow blotching or mosaic of leaves, leaf curling or crumpling, leaf vein thickening, leaf enations, leaf cupping, stem twisting and plant stunting (https://www.cabi.org/isc/datasheet/8927). B. tabaci is a cryptic species complex with more than 40 morphologically indistinguishable species (Hu et al. 2017). Within B. tabaci species complex, the Mediterranean (MED or biotype Q) and Middle East-Asia Minor 1 (MEAM1 or biotype B) species are highly invasive and cause substantial economic damage to crops (Luo et al. 2002; Chu et al. 2006; Vassiliou et al. 2011).

B. tabaci has been usually controlled with carbamates, OPs and pyrethroids representing 50 conventional insecticides (Horowitz et al. 2011). Resistance in B. tabaci to insecticide has developed due to the repeated applications of the same active ingredients and their use in larger quantities (Denholm et al. 1998; Horowitz et al. 2007). Repeated applications of insecticides exert high selection pressure which increases the rate of resistance development and also crop production cost (Naranjo and Ellsworth 2009). B. tabaci has tremendous potential to develop resistance to different insecticides (Horowitz et al. 2007) and has been reported to develop resistance to 64 active ingredients of different groups of insecticides (https://www.pesticideresistance.org/).

Deltamethrin (pyrethroid), thiamethoxam (neonicotinoid) and pyriproxyfen (juvenile hormone analog) have been used to control several insect pests including B. tabaci (Dennehy and Williams 1997; Li et al. 2000; Dennehy et al. 2008; Tsagkarakou et al. 2009). These insecticides have different modes of action. The pyrethroids target voltage-gated sodium channels (VGSCs), neonicotinoids work on acetylcholine receptors in the insect nervous system and insect juvenile hormone (JH) analog controls metamorphosis and development (Ishaaya and Horowitz 1992; Cahill et al. 1995; Dhadialla et al. 1998; Tomizawa and Casida 2005). Both neonicotinoids and insect growth regulators (IGRs) have been successful in controlling B. tabaci, which also resulted in their excessive use. In a survey conducted in Oman, majority (95%) of the farmers used insecticides consisting of 29 different active ingredients (Kaakeh et al. 2007). Deltamethrin and esfenvalerate (pyrethroids) have been extensively used in Oman mostly in aerial sprays against dubas bug (550 tons from 1993 to 2010) (Thacker et al. 2003; MAF 2014).

Resistance to deltamethrin, thiamethoxam and pyriproxyfen in B. tabaci has been reported from other regions (Toscano et al. 2001; Horowitz et al. 2002; Nauen et al. 2002; Nauen and Denholm 2005). In Oman, B. tabaci resistance has been reported to malathion and diazinon (organophosphates) (Talukder et al. 2008). However, no baseline data on susceptibility to deltamethrin, thiamethoxam and pyriproxyfen are available for B. tabaci populations in Oman. This study was conducted to generate baseline data on susceptibility of B. tabaci eggs, nymphs and adults to deltamethrin, thiamethoxam and pyriproxyfen which are commonly used on vegetables in Oman.

 

Materials and Methods

 

Whiteflies collection and rearing

 

Two separate colonies of B. tabaci adults (MEAM1) were collected from Agricultural Experiment Station (AES) at the Sultan Qaboos University (SQU), Seeb (23.5910° N, 58.1730° E) and the ‘Pairidaeza’ organic farm at Barka (Al-Batinah governorate) (23.668854° N, 57.852961° E), Oman during March and April 2018. More than 100 adults were collected from infested tomato plants at each site using an aspirator. The collected adults were transported in cool box with ice. At the AES, different pesticides have been used in past while ‘Pairidaeza’ is a certified organic farm and pesticides have not been used for last three years. The SQU-1 (resistant) and Pairidaeza (susceptible) strains of B. tabaci colonies were reared separately inside two walk-in glass cages (3 m × 4 m × 3 m with a mesh door) in a secluded section of the glasshouse at AES. The colonies were maintained on potted eggplants in a 48 cm3 cage which was placed inside each walk-in glass cage with temperature and relative humidity (RH) set at 28 ± 2°C and 65 ± 5%, respectively. Inside individual cages, three pots with 23 plants were placed in 40 × 40 cm2 metal containers with 10 cm high edges. Pots were replaced every two weeks. Plants were irrigated with a programmed automatic drip system. Eggplant seedlings were grown in a growth chamber (25 ± 2°C and 65 ± 5% RH) at the SQU and fresh plants at 34 leaf stage were regularly provided to maintain the colonies.

 

Insecticides and concentrations tested

 

The formulated insecticides used in bioassays were bought from local market and included: deltamethrin 25 g L-1 (Delta 2.5 EC from Arab Pesticides and Veterinary Drugs Mfg. Co., Jordan), thiamethoxam 240 g L-1 (Actara 240 SC from Syngenta, India) and pyriproxyfen 100 g L-1 (Admiral 10 EC from Sumitomo Chemicals Co., Japan). Concentrations of each formulated insecticide were prepared with deionized water, by 3X serial dilutions, and 1–2 concentrations above the field recommended rates. The concentrations for deltamethrin were 0.74, 2.2, 6.7, 20, 60 and 180 µg/mL, for thiamethoxam were 0.2, 0.56, 1.70, 5, 15, 45 and 135 µg/mL, and for pyriproxyfen were 0.4, 1.2, 3.7, 11.1, 33.3 and 100 µg/mL.

 

Leaf-dip bioassay for adults

 

Six to seven concentrations of each insecticide that gave 15 to 85% mortality were selected for the bioassays (Heong et al. 2013). A leaf-dip bioassay method was adopted from Nauen et al. (2008). Leaf discs (45 mm) from eggplant leaves were dipped for 15 s in an insecticide solution separately for each concentration. Deionized water was used for control. Leaf discs were air dried for 60 min on paper towel and placed upside down on a 1.5% agar already poured in Petri dishes (55 mm). Petri-dish lids were ventilated with two rows of small holes and lids were covered with fine mesh using glue to prevent escaping of adults. B. tabaci adults were collected from the colonies with an aspirator into small plastic vials and immobilized by immersing the vials in the ice for 24 min. Working on a chilling pad, 20 B. tabaci adults (mixed sex) were transferred gently onto each treated leaf disc. Each concentration was replicated three times and a total of 360 adults were used for deltamethrin and pyriproxyfen, and 480 adults for thiamethoxam. Petri dishes were then covered with the already prepared lids and sealed with parafilm. Petri dishes were placed upside down and kept at 24 ± 2°C temperature, 60 ± 5% RH and a 12:12 h photoperiod in laboratory.

Leaf-dip (3-leaf whole plant) bioassay for eggs and nymphs

 

A leaf-dip (3-leaf whole plant) bioassay method was adopted from Bielza et al. (2019). An eggplant with three leaves each trimmed into a small rectangle (4 cm × 6 cm) were placed in the SQU-1 and Pairidaeza rearing cages for 24 h for egg laying to allow synchronization of each developing stage. For eggs and nymphs, separate bioassays were done. In egg-bioassay, after 24 h each leaf (with ~50 eggs) was completely merged in the insecticide solution for 20 sec. A single plant was used for each concentration, with each of the three infested leaves counted as three replicates. In bioassay for nymphs, the 3-leaf plants were inspected for the presence of 2nd instar nymphs 15 days after egg laying, and then treated by dipping individual leaves. Eggs and the immobile 2nd instar nymphs were counted on each leaf under stereomicroscope and a total of 9001400 eggs and 6001050 nymphs were used in these bioassays.

 

Data recording and analysis

 

Mortality of adults was assessed after 48 h for deltamethrin and after 72 h for thiamethoxam and pyriproxyfen. Adults not moving after gentle touch by a needle were considered dead. Number of eggs and hatched alive nymphs were recorded 7 days after treatment in the egg bioassay. In the bioassays for nymph, the number of dead nymphs and pupae were recorded 5 days after treatment. Percent mortality was computed following Abbott (1925). Lethal concentration values of each of the insecticide for the eggs, nymphs and adult stages were calculated separately using Polo Plus Version 2.0 (LeOra 1987). Resistance factors (RF) were calculated by dividing LC50 of SQU-1 strain (resistant) by LC50 of Pairidaeza strain (susceptible). An RF of <2 means no resistance while 2–10 is considered as very low, 11–20 as low, 21–50 as moderate, 51–100 as high and >100 as very high resistance (Saleem et al. 2008). Percent corrected mortality caused by the three insecticides applied at label recommended rate against eggs, nymphs and adults of B. tabaci were analyzed by single factor ANOVA (analysis of variance) using S.P.S.S. V19.0 and means were separated at LSD0.05.

 

Results

 

Susceptibility of adults to insecticides

 

The acute contact LC50 for deltamethrin was 55.09 µg/mL and 12.69 µg/mL for adults of SQU-1 and Pairidaeza strains, respectively. A low level of resistance (RF = 4.3) to deltamethrin was detected in SQU-1 adults compared to Pairidaeza. SQU-1 and Pairidaeza populations LC50s for thiamethoxam were 4.10 and 1.85 µg/mL, respectively. The SQU-1 population was 2.2-and 1.3-fold resistant to thiamethoxam and pyriproxyfen, respectively suggesting very low to no resistance against these insecticides (Table 1).

Susceptibility of nymphs and eggs to insecticides

 

LC50 of deltamethrin for nymphs of SQU-1 and Pairidaeza strains were 28.73 µg/mL and 8.37 µg/mL, respectively and nymphs of SQU-1 strain exhibited RF value 2.7-fold as compared to Pairidaeza strain. A very high LC50 of 7837 µg/mL was determined for SQU-1 strain while LC50 for Pairidaeza strain could not be determined because of the concentration range used. Therefore, RF for eggs against deltamethrin could not be calculated. LC50 for thiamethoxam was 7.21 and 2.59 µg/mL for nymphs of SQU-1 and Pairidaeza strains with RF of 2.7 for former strain while RF for eggs was 2.3-fold. LC50 for pyriproxyfen was 5.29 and 4.67 µg/mL against nymphs of SQU-1 and Pairidaeza strains with RF 1.1. LC50 for pyriproxyfen was 3.39 and 2.18 µg/mL for eggs of SQU-1 and Pairidaeza strains, respectively. The RF for eggs against pyriproxyfen was 1.6 (Table 2).

 

Mortality by field application rate

 

The field application rate of deltamethrin caused 47.0 ± 6.3 and 59.6 ± 6.5% mortality in adults and nymphs of SQU-1 strain, respectively, at dose of 20 µg a.i/mL, however, egg mortality was only 14.0 ± 3.1% (Table 3). Thiamethoxam caused 82.0 ± 9.4, 86.7 ± 8.5 and 17.3 ± 4.2% mortality in adults, nymphs and eggs of SQU-1 strain, respectively, at dose of 100 µg a.i/mL. Pyriproxyfen the field application rate at the dose of 75 µg a.i/mL caused 82.3 ± 9.8, 92.3 ± 10.5 and 82.0 ± 9.9% mortality in adults, nymphs and eggs, respectively.  Pyriproxyfen in SQU-1 strain which was not significantly different than the Pairidaeza strain. Mortality in adults and nymphs caused by thiamethoxam and pyriproxyfen in both strains was significantly higher (F= 109, df = 2, P < 0.001; F = 54, df = 2, P < 0.001) than deltamethrin. Mortality in eggs of both strains caused by pyriproxyfen was significantly higher (F= 247, df = 2, P < 0.001) than deltamethrin and thiamethoxam. There was no significant difference in adult (F= 1.3, df = 1, P=0.27), nymph (F = 0.33, df = 1, P=0.57) and eggs (F = 0.89, df, 1, P = 0.1) mortality between the SQU-1 and Pairidaeza strains.

 

Discussion

 

Deltamethrin, thiamethoxam and pyriproxyfen are currently used in the management of B. tabaci in different horticultural crops in Oman. Resistance in B. tabaci has developed as a result of the intensive use of these insecticides (Li et al. 2000; Dennehy et al. 2008; Tsagkarakou et al. 2009). A very low resistance to deltamethrin Table 1: Toxicity of three insecticides against adults of two B. tabaci strains using leaf-dip bioassay

 

Insecticides

Strains

Total number tested

LC10 (µg/mL) (95% FL)

LC50 (µg/mL) (95% FL)

LC90 (µg/mL) (95% FL)

Slope (± SE)

heta

RFb

Deltamethrin

SQU-1

360

0.66 (0.15-1.62)

55.09 (24.92-112.18)

1256.9 (389.1-4226.9)

0.81 ± 0.17

0.47

4.3

 

Pairidaeza

360

0.46 (0.26-1.74)

12.69 (5.42-39.35)

526.7 (181.2-1229.5)

0.66 ± 0.15

0.15

 

Thiamethoxam

SQU-1

480

0.27 (0.01-1.41)

4.10 (0.98-15.30)

135.64 (42.3-7141.4)

0.95 ± 0.13

1.85

2.2

 

Pairidaeza

480

0.12 (0.09-1.62)

1.85 (0.08-5.20)

85.63 (22.3-1421.5)

0.64 ± 0.12

0.67

 

Pyriproxyfen

SQU-1

360

0.32 (0.07-0.76)

8.39 (5.28-12.86)

218.2 (100.5-811.9)

0.91 ± 0.13

0.41

1.3

 

Pairidaeza

360

0.27 (0.06-0.67)

6.59 (4.27-11.38)

182.4 (84.7-567.4)

0.84 ± 0.14

0.32

 

LC10, LC50 and LC90 are the concentrations (µg/mL) that will kill 10, 50 and 90% of the B. tabaci adults, respectively

60 adults used in control

aA value lower than 1 indicates that homogeneity and linearity of dose-mortality response were rejected

bResistance factor (RF) = LC50 of SQU-1 strain divided by LC50 of Pairidaeza strain

 

Table 2: Toxicity of insecticides against nymphs and eggs of two B. tabaci strains using leaf-dip (3-leaf whole plant) bioassays

 

Insecticides

Strains

Life stage

Total number tested

LC10 (µg/mL)

LC50 (µg/mL)

LC90 (µg/mL)

Slope (± SE)

heta

RFb

Deltamethrin

SQU-1

Nymphs

Eggs

600

900

0.82 (0.29-1.87)

15.87 (4.38-37.01)

28.73 (7.12-63.36)

7837 (3832-18936)

697.8 (283.2-1963.5)

--

1.08 ± 0.13

0.68 ± 0.13

1.30

0.07

2.7

--

Thiamethoxam

SQU-1

Nymphs

Eggs

1050

1400

0.91 (0.27-2.25)

11.62 (3.75-22.95)

7.21 (3.27-12.71)

3319.5 (889.4-54602.0)

157.89 (49.7-2210.9)

--

1.42 ± 0.19

0.52 ± 0.10

0.78

1.01

2.7

2.3

 

Pairidaeza

Nymphs

Eggs

1050

1400

0.63 (0.15-1.52)

3.56 (1.57-12.32)

2.59 (0.24-11.24)

1419.5 (693.4-21361.1)

102.8 (29.7-710.9)

--

1.51 ± 0.28

0.66 ± 0.19

0.27

0.58

 

Pyriproxyfen

SQU-1

Nymphs

Eggs

600

900

0.29 (0.06-0.74)

0.13 (0.04-0.28)

5.29 (2.59-8.38)

3.39 (2.29-4.98)

93.7 (49.6-267.1)

86.18 (42.5-262.3)

1.03 ± 0.16

0.91 ± 0.07

0.69

0.27

1.1

1.6

 

Pairidaeza

Nymphs

Eggs

600

900

0.33 (0.08-0.98)

0.11 (0.05-0.53)

4.67 (2.24-7.27)

2.18 (0.94-4.47)

87.6 (36.4-187.9)

68.58 (35.8-182.6)

1.11 ± 0.12

0.73 ± 0.09

0.36

0.14

 

LC10, LC50 and LC90 are the concentrations (µg/mL) that will kill 10, 50 and 90% of the B. tabaci nymphs or eggs, respectively

aA value lower than 1 indicates that homogeneity and linearity of dose-mortality response were rejected

bResistance factor (RF) = LC50 of SQU-1 strain divided by LC50 of Pairidaeza strain

 

Table 3: Efficacy of the three commonly used insecticides against B. tabaci applied at label recommended rate

 

Insecticides

Label rate

a.i. (µg/mL)

Strain

Percent corrected mortality

 

 

 

 

Adults

Nymphs

Eggs

Deltamethrin

80 mL per 100 L water

20

SQU-1

Pairidaeza

47.0 ± 6.3a

62.7 ± 4.3a

59.6 ±6.5a

67.4 ± 7.3a

14.0 ± 3.1a

16.1 ± 3.4a

Thiamethoxam

 

8 g per 20 L water

100

SQU-1

Pairidaeza

82.0 ± 9.4b

94.3 ± 11.6b

86.7 ± 8.5b

87.6 ± 8.3b

17.3 ± 4.2a

25.0 ± 4.6a

Pyriproxyfen

150 mL per 200 L water

75

SQU-1

Pairidaeza

82.3 ± 9.9b

93.7 ± 10.1b

92.3 ± 10.5b

94.4 ± 11.3b

82.0 ± 9.9b

87.6 ± 8.7b

Values sharing same letters in column don’t differ significantly (P > 0.05)

 

was detected in adults (4.3-fold) and nymphs (2.7-fold) of SQU-1 strain with reduced mortalities in both stages of the tested strains at field application rate. Houndete et al. (2010), while establishing baseline susceptibility, recorded a very low 1.64.7-fold resistance to deltamethrin in B. tabaci collected from cotton fields. The same populations, however, showed reduced susceptibility (RF = 44) to another pyrethroid, bifenthrin. Resistance factor for eggs treated with deltamethrin could not be calculated because LC50 was not determined for the susceptible strain. A very low level of resistance was observed for thiamethoxam in adults (2.2-fold) and nymphs (2.7-fold) of SQU-1 strain, while no resistance (<2 fold) was detected in egg stage. Adults of SQU-1 strain treated with thiamethoxam had slightly reduced but non-significant mortality at the field application rate. Pyriproxyfen treated eggs, nymphs and adults did not show any resistance. Eggs of SQU-1 strain treated with field application rate of pyriproxyfen did not show reduction in susceptibility.

Findings of very low resistance ratios to deltamethrin in the SQU-1 strain may be due to its cautious use at the experimental station. B. tabaci from other commercial farms where deltamethrin is repeatedly used may show reduced susceptibility levels. Very low resistance ratios to thiamethoxam and lack of resistance to pyriproxyfen show that B. tabaci has retained a general level of susceptibility to these insecticides. These two insecticides are relatively new to Oman. It is unlikely that they may cause any resistance problem and their effectiveness is expected to be maintained in near future. Another reason for the very levels of resistance is because of the presence of B biotype in Oman. One strain of B. tabaci representing the B biotype had resistance factors between 18 showing very low to no resistance to imidacloprid, thiamethoxam and acetamiprid (Qiong et al. 2012). The Q biotype of B. tabaci has shown stronger resistance to neonicotinoid insecticides than B biotype (Ma et al. 2007; Luo et al. 2010; Rao et al. 2011; Qiong et al. 2012).

Monitoring field populations for their susceptibility to the most used insecticide classes is crucial for early detection of resistance development (Roush and Miller 1986). While developing resistance management strategies for an insect pest, it is important to establish the baseline susceptibility levels (Prabhaker et al. 2008). Baseline susceptibility data provide a reference point to which subsequent susceptibility data can be compared with. Any shift in the susceptibility to a particular insecticide from the reference would detect resistance in its early stages.

The determined baseline susceptibility levels of B. tabaci adults, nymphs and eggs against deltamethrin, thiamethoxam and pyriproxyfen can be used for continuous monitoring of B. tabaci populations. Natural variations in responses to insecticides in populations collected from various geographic regions in Oman should be expected. B. tabaci populations should also be tested at different time of the year, for example September to December, that could help explain the causes of variability in insecticide susceptibility. Any change in the susceptibility levels indicates development of resistance in B. tabaci. Once resistance is detected, resistance management strategies must be initiated and implemented before control failures occur. An extensive survey and toxicological work with several strains collected from different regions in Oman, with different history of insecticide applications, is underway which will help in broadening the susceptibility baseline data of B. tabaci.

Our results provide a baseline for future comparisons of the sensitivity of B. tabaci to three insecticides that represent the primary classes being used to control this pest, each with a different mode of action. The range of concentrations across which these populations responded will allow baseline sensitivity studies in other governorates in Oman to test the active range of response for these insecticides. Insecticide resistance management (IRM) is a crucial component of a successful IPM program (Foster et al. 2002). Preventative approaches should be implemented instead of relying on only insecticides (Timmeren et al. 2018). IRM strategies should include rotation of insecticides (based on IRAC classification with different modes/site of action). Thiamethoxam and pyriproxyfen did not show any reduction in susceptibility and should be included in rotation. Use of insecticides should be integrated with cultural and biological pest management tools that will provide effective management of B. tabaci in Oman.

 

Acknowledgements

 

The authors acknowledge the financial support provided by Sultan Qaboos University, Oman through internal grant ‘IG/AGR/CROP/18/02’.

 

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