Phosphine-Induced Alterations in Microsomal Enzymes of a Stored Grain Pest Trogoderma granarium Collected from Godowns of Punjab, Pakistan

Tanzeela Riaz1, Farah Rauf Shakoori2,* and Syed Shahid Ali3

1Faculty of Life Sciences, University of Central Punjab, Lahore, Pakistan

2Department of Zoology, University of the Punjab, Lahore, Pakistan

3Institute of Molecular Biology and Biotechnology, University of Lahore, Lahore-54590, Pakistan

ABSTRACT

The present study was aimed to determine the toxic effect of phosphine on microsomal enzymes (NADPH-Cytochrome P450 reductase (NADPH-CPR), ethylmorphine-N demethylase and aniline 4-hydroxylase) and soluble protein contents of a wheat grain pest, Trogoderma granarium collected from godowns of Punjab, Pakistan. Six populations of khpara beetle with different levels of susceptibility to phosphine were used in this study. Based on LC50, five populations (previously exposed to phosphine for 15 years) viz., Mandi Bahauddin-I (MBDIN-I), Mandi Bahauddin-II (MBDIN-II), Gujrat, Gujranwala and Sargodha were labeled as phosphine-tolerant populations and one population never exposed to any insecticide/fumigant for 13 years was termed as phosphine-susceptible population. Percent change in the activities of above mentioned microsomal enzymes and soluble protein contents in 4th and 6th instar larvae and adult beetles of phosphine-tolerant populations were evaluated with reference to phosphine-susceptible population as a control. The activities of NADPH-CPR, ethylmorphine-N demethylase, aniline 4-hydroxylase and soluble protein contents were significantly increased in all field collected phosphine-tolerant populations with reference to phosphine-susceptible population. Among developmental stages, the 4th instar larvae possessed higher microsomal enzyme activities than 6th instar larvae and adult beetles in all populations. The increased level of microsomal enzymes in phosphine-tolerant populations as compared to susceptible population has pointed some correlation between microsomal enzymes and phosphine tolerance.

Article Information

Received 05 May 2017

Revised 20 June 2017

Accepted 24 July 2017

Available online 12 January 2018

Authors’ Contribution

FRS and SSA designed the research project. TR conducted the experimental work. TR, FRS and ASS analyzed the data and wrote the article.

Key words

Trogoderma granarium, Wheat, Phosphine, Microsomal enzymes, Tolerance.

DOI: http://dx.doi.org/10.17582/journal.pjz/2018.50.1.291.297

* Corresponding author: [email protected]

0030-9923/2018/0001-0291 $ 9.00/0

Copyright 2018 Zoological Society of Pakistan

INTRODUCTION

 

Wheat (Triticum aestivum L.) is a staple diet in Pakistan and are produced in more quantity as per need (Anon, 2005-2006). Its storage is done in the houses as well as in the large government storage facilities but without any proper arrangement resulting into huge losses. The post-harvest losses of wheat grain have been reported to be 10-15% in Pakistan. Among various contributing factors to these losses, stored grain pest Trogoderma granarium (Everts) is considered to be the most destructive pest of wheat (Burges, 2008; Castalanelli et al., 2010). The agriculture sector of the economy is facing persistent challenges. By 2020, world demand for wheat is expected to be 40% higher than that of its level in the latter half of the 1990s (Mahroof et al., 2005; Fedina and Lewis, 2007). Various techniques have been applied to reduce the damage caused by these insect pests. Insecticidal approach was the most significant to keep the pests below economic loss level. Organochlorines, organophosphates, carbamates, pyrethroids were used to overcome the problem of pest infestation. Due to impaired ability of these pesticides to control these stored grain pests, the fumigation technique with methyl bromide and phosphine as fumigant is being widely used in godowns (Walter, 2006).

In large stores, pesticides and fumigants are being used from last several years but their doses are not calculated as per resistivity of pest against the pesticides resulting into no control over the pest. The development of tolerance/resistance after exposure to sub-lethal doses of insecticides/fumigants has become universal phenomenon in stored grain pests. The increased tolerance/resistance may be due to the elevated levels of various insecticide hydrolyzing enzymes and other metabolites. This up-regulation is usually attributed to a genetic change in the activities of insecticides degrading enzymes (Riaz et al., 2017). There is variety of enzyme systems that could be affected by chronic doses of insecticides. The important among these resistance indicators are microsomal mixed-function oxygenase, cytochrome P-450 dependent mono-oxygenase and esterase systems (Vontas et al., 2002). This study was aimed to evaluate the direct/indirect effect of phosphine on various microsomal enzymes in T. granarium collected from different godowns of Punjab province having regular long exposure to phosphine and to evaluate their role in the development of tolerance against phosphine in T. granarium. There is no report on toxic effects of phosphine on microsomal enzymes of T. granarium.

 

Materials and methods

Rearing and maintenance of pest culture

A notorious stored grain pest, T. granarium (Everts) with common name khapra beetle was used in current investigation. Master cultures of five populations of khapra beetle tolerant to phosphine were collected from different godowns of Punjab province viz., Gujrat, Mandi Bahauddin-I (MBDIN-I), Gujranwala, Mandi Bahauddin-II (MBDIN-II), and Sargodha. These godowns have more than 15 year history of phosphine fumigation to wheat. The wheat samples containing T. granarium were collected in sterilized plastic bags and brought to laboratory for study. A phosphine-susceptible (population never exposed to phosphine previously) were taken from thirteen years old culture maintained in the culture room of department of Zoology, University of the Punjab, Lahore. The master cultures of T. granarium (six populations) were reared and maintained in temperature and humidity controlled room at 30±1°C and 65±5% RH. The culture was fed on sterilized broken wheat and flour in 300 ml glass jar tightened with rubber band (Riaz et al., 2014; Shakoori et al., 2016). Adult beetles (24 h old) were kept in the medium for 5-6 days for egg laying and then dead beetles were discarded form the jars. Eggs in the floor medium were allowed to develop into next adult beetles through various larval and pula stages and it was repeated for 4-5 generations to collect age wise homogenous stock of each population. The larvae were separated on the basis of size, the 4th instar larvae were about 3 mm in length and 6th instar larvae measured 5 mm.

Generation and administration of phosphine

Gaseous Phosphine was generated from commercially available aluminum phosphide (AlP) pellets comprising (approximately 0.2g) in the laboratory fume hood. Different doses of phosphine were calculated according to the formula given in FAO plant protection bulletin (FAO, 1975). Twenty insects of each 4th, 6th instar larvae and adult beetles (24 h old) were introduced for fumigation in each vial with three replicates for each dose. The insect containing vials were placed in vacuumed desiccators and calculated volume of phosphine for each dose was injected through sterilized Hamilton syringe in their respective desiccator. These desiccators were placed in temperature and humidity controlled room for 20 h exposure period. The LC50 of phosphine for each developmental stage was calculated according to Riaz et al. (2016).

Biochemical parameters (NADPH-CPR, ethylmorphine-N demethylase, aniline 4-hydroxylase and soluble protein contents) of five tolerant populations (Gujrat, MBDIN-I, Gujranwala, MBDIN-II and Sargodha) collected from godowns of Punjab were compared with biochemical parameters of phosphine-susceptible population.

Biochemical analysis of microsomal enzyme activities

The microsomal fraction was prepared by the method of Schenkman et al. (1981) described in steps as follow:

Preparation of microsomal fraction

For the preparation of whole homogenate, homogenizing medium, homogenizing tubes, cylinders and centrifuge tubes were kept in ice. Beetles (1g) were homogenized in 3ml of homogenizing medium (0.154M KCl) with five return stroke of motor driven Teflon glass homogenizer with constant cooling in crushed ice. The homogenate was diluted 25% i.e., 0.25 g homogenate/ml so, 3 ml of homogenate was diluted with 1ml of homogenizing medium (0.154M KCl). The 4 ml homogenate was covered with parafilm and mixed by gentle inversion. The homogenate was centrifuged at 10,000 g for 20 min at 4ºC. A thin layer of floating lipids were removed with pasture pipette. The supernatant was transferred to other precooled tube and were ultra-centrifuged at 105,000 g for 1 h at 2-4ºC. The cytosol fraction and lipid layer were removed by pasture pipette. Pellet was washed with homogenizing medium (0.154M KCl) and followed by ultra-centrifugation. Supernatants were discarded and microsomal pellet was diluted further and used for biochemical analysis of various enzymes.

Determination of microsomal enzymes activities

The activity of NADPH-CPR was determined spectrophotometrically by the method of Peterson et al. (1978) using cytochrome, potassium cyanide and NADPH.

The N-demethylation of ethylmorphine results in the formation of formaldehyde which is trapped in the incubation medium by the presence of semicarbazide and estimated spectrophotometrically by means of Hantysch reaction (Nash, 1953) and modified procedure of Alvares and Mannering (1970).

The 4-hydroxylation of aniline hydrochloride results in the formation of 4-aminophenol, which is determined spectorphotometrically by indophenol reaction. Aniline 4-hydroxylase was determined by method of Nakanishi et al. (1971) with a modification that NADPH is added directly into the incubation medium instead of generating NADPH from NADP, isocitric acid, isocitric dehydrogenase and magnesium ions.

The total soluble proteins were estimated according to Lowry et al. (1951). Soluble protein contents were calculated as µg/mg of tissue from standard curve prepared by using bovine serum albumin (BSA).

Analysis of variance (ANOVA) followed by tukey’s Post Hoc test was applied to all the data of biochemical parameters to compare pair wise means of various populations to determine the significant difference at P<0.05 using SPSS software.

 

Results

 

The activity of three microsomal enzymes (NADPH-CPR, ethylmorphine N-demethylase and aniline 4-hydroxylase) in three different developmental stages of phosphine-susceptible and tolerant populations (Gujrat, MBDIN-I, Gujranwala, MBDIN-II and Sargodha) of T. granarium was described in Table I.

NADPH-CPR, ethylmorphine N-demethylase and aniline 4-hydroxylase activities were significantly increased in all phosphine-tolerant populations when compared to susceptible population at P<0.05. In 4th instar larvae NADPH-CPR activity was significantly different from each other in all tolerant populations likewise in adult beetles significant difference among tolerant populations was observed, whereas in 6th instar larvae, MBDIN-II and Gujranwala had non-significant difference in NADPH-CPR activity at P<0.05. Percent increase in NADPH-CPR activity of tolerant populations in comparison with susceptible population is shown in Figure 1. Based on increased level of NADPH-CPR activity, tolerant populations can be graded as: MBDIN-II ˃ Gujranwala ˃ MBDIN-I ˃ Sargodha ˃ Gujrat. Adult and 6th instar larvae possessed less NADPH-CPR activity than 4th instar larvae in all populations.

 

Table I.- Activities of various microsomal enzymes (nmol/min/ml)) and soluble protein contents (mg/mg of body weight) of 4th instar larvae, 6th instar larvae and adult beetles of susceptible and five tolerant populations of T. granarium.

Populations	NADPH-CPR	Ethylmorphine N-demethylase	Aniline 4-hydroxylase	Total soluble protein contents
4th instar larvae
Susceptible	428.57 ± 0.218a*	982.5 ±0.290a	39.48 ± 0.144a*	199.61 ± 4. 26ad*
MBDIN-I	517.85 ± 0.248a	1095.01 ±0.350a	45.36 ± 0.197a	213.64 ± 2.21ad
MBDIN-II	535.70 ± 0.244a	1310.21 ±0.290a	47.04 ± 0.375a	210.12 ± 3.13a
Gujrat	494.04 ± 0.234a	1280.13 ±0.283a	42.56 ± 0.233a	229.35 ± 2.39ad
Gujranwala	523.80 ± 0.203a	1350.34 ±0.401a	49.84 ± 0.291a	231.1 ± 3.44ad
Sargodha	470.23 ± 0.272a	1120.47 ±0.266a	43.63 ± 0.175a	211. 34 ± 4.31a
6th instar larvae
Susceptible	410.70 ± 0.206bd	967.5 ±0.31a	38.92 ± 0.117b	195.21 ± 3.79b
MBDIN-I	499.99 ± 0.123bd	1050.11 ±0.364a	44.24 ± 0.277b	209.69 ± 3.24b
MBDIN-II	511.89 ± 0.169b	1290.04 ±0.306a	46.2 ± 0.145b	207.01 ± 3.93
Gujrat	476.18 ± 0.353bd	1220.39 ±0.277a	42.01 ± 0.116b	225.78 ± 3.41b
Gujranwala	510.89 ± 0.334b	1320.14 ±0.285a	47.88 ± 0.189b	227.35 ± 3.71b
Sargodha	452.37 ± 0.244bd	1100.42±0.321a	43.12 ± 0.177b	226.15 ± 3.06b
Adult beetles
Susceptible	374.99 ± 0.282c	938.03±0.254a	37.8 ± 0.163cd	189.42 ± 3.51c
MBDIN-I	464.27 ± 0.301c	1020.16 ±0.347a	43.4 ± 0.228cd	206.37 ± 3.86c
MBDIN-II	505.94 ± 0.245c	1207.14 ±0.276a	44.8 ± 0.317cd	205.61 ± 2.91c
Gujrat	434.51 ± 0.227c	1200.26 ±0.258a	40.6 ± 0.239c	221.98 ± 3.20c
Gujranwala	488.08 ± 0.212c	1300.19 ±0.307a	47.32 ± 0.273cd	224.54 ± 3.75c
Sargodha	446.42 ± 0.362c	1070.13 ±0.317a	41.44 ± 0.190c	222.11 ± 3.38c

 

Percent increase in ethylmorphine N-demethylase activity of tolerant populations in comparison with susceptible is shown in Figure 2. Based on increased level of ethylmorphine N-demethylase activity, tolerant populations can be graded as: Gujranwala ˃ MBDIN-II ˃ Gujrat ˃ Sargodha ˃ MBDIN-I. Ethylmorphine N-demethylase activity of adult is found less than that of 6th instar larvae and likewise ethylmorphine N-demethylase activity of 6th instar larvae is also less compared to 4th instar larvae in all populations.

 

 

Aniline 4-hydroxylase activity was significantly different in 4th instar larvae of all tolerant populations likewise 6th instar larvae also possessed significant difference among all tolerant populations, whereas adult beetle of Gujrat and Sargodha population had non-significant difference in aniline 4-hydroxylase activity at P<0.05. Percent increase in aniline 4-hydroxylase activity of tolerant populations in comparison with susceptible population is shown in Figure 3. Based on increased level of aniline 4-hydroxylase activity, tolerant populations can be graded as: Gujranwala ˃ MBDIN-II ˃ MBDIN-I ˃ Sargodha ˃ Gujrat. Adult beetles and 6th instar larvae possessed less aniline 4-hydroxylase activity compared to 4th instar larvae in all populations.

 

 

Total soluble proteins of adult is less than that of 6th instar larvae and likewise total soluble proteins of 6th instar larvae is less compared to 4th instar larvae in all populations except for Sargodha population. In Sargodha population 6th instar larvae exhibited higher total soluble proteins activity compared to 4th instar larvae. Percent increase in total soluble proteins of tolerant populations in comparison with susceptible is shown in Figure 4.

 

Discussion

 

Khapra beetle, Trogoderma granarium is a serious pest of stored grains all over the world. In present study the increased activities of NADPH-CPR, ethylmorphine N-demethylase and aniline 4-hydroxylase were observed in all phosphine tolerant populations with reference to susceptible population. The MBDIN-II population has a significant percent increase 25, 24.63 and 35% NADPH-CPR activity, Gujranwala population has 37.43, 36.44 and 38.60% increase in ethylmorphine N-demethylase activity and 26.24, 23.02 and 25.18% increase in aniline 4-hydroxylase activity in 4th, 6th instar larvae and adult beetle respectively, with reference to susceptible population. Among developmental stages, the 4th instar larvae possessed higher NADPH-CPR, ethylmorphine N-demethylase and aniline 4-hydroxylase activities than 6th instar larvae and adult beetles revealing that microsomal activities started to decrease as development proceeds.

There was no data available on activities of NADPH-CPR, ethylmorphine N-demethylase and aniline 4-hydroxylase activities in T. granarium against phosphine. It was assumed that mortality after phosphine exposure occurred due to disruption of mitochondrial respiration which suggests that energy insufficiency was the cause of mortality after phosphine exposure. It was proposed that there is a relationship between energy metabolism and phosphine resistance and tolerance is associated with degree of oxygen uptake. Under hypoxic conditions, metabolic demand is suppressed and ultimately suppressed respiration occurs so insect remained insensitive to phosphine. Mitochondrial uncouplers, increase metabolic demand and increase toxicity (Valmas et al., 2008). The tolerance may be due to non-disruption of electron transport chain and phosphorylation for energy production. So insect survived and developed tolerance.

Mixed function oxidases are very important markers of resistance. High titers of MFOs are associated with resistance (Tomita et al., 1995). They are able to convert lipophilic compounds into polar metabolites that can be easily eliminated from the body; for that reason, they are mainly located in the digestive apparatus (Feyereisen, 2005). Cytochrome P-450 dependent mono oxygenases are a very diverse group of heme containing hydrophobic enzymes that involve in detoxification of various exogenous and endogenous compounds. The detoxification mechanism occurs as a substrate metabolism.

NADPH cytochrome P-450 reductase (EC 1.6.2.4) plays very important role in oxidative metabolism of many endogenous and exogenous compounds (Nelson, 2003). During oxidative metabolic reactions, NADPH cytochrome P-450 reductase accepts a hydride ion (one proton and two electrons) from NADPH and donates two electrons, one at a time to P-450. In this way cytochrome P-450 reductase is an enzyme with two substrates, NADPH and artificial electron acceptor cytochrome c (Gigon et al., 1969). Due to the large number of enzymes and their substrate specificity, P450s are able to catalyze different reactions like epoxidation, hydroxylation, N-dealkylation, O- dealkylation or desulfurization; for that reason they play an important role in the metabolism of many insecticide classes, including carbamates, organophosphates, pyrethroids and DDT (Simon, 2014). These monooxyganases are involved to oxidize phosphine to its oxons through phosphorus oxidation reaction (Dauterman and Hodgson, 1990).

Monooxygenase mediated resistance is the most prominent type of metabolism based insecticide resistance reported by Oppenoorth, (1984) and Brattsten et al. (1986). Vincent et al. (1985) reported that in house fly it was first time detected that P-450 reductase level was higher in insecticide resistant population and later on its higher level was also reported by Kotze and Wallbank (1996) in other insect species. Elevated levels of P-450 reductase associated with monooxygenase mediated resistance suggested that there was a change in proteins that could lead to tolerance (Oppenoorth, 1984) proposed that resistance was developed due to increased detoxification, which results from a change in the catalytic activity of the P-450 reductase and also due to change in the level of expression of the P-450.

 

Conclusion

 

The microsomal enzyme activities were significantly higher in phosphine-tolerant population collected from godowns as compared to phosphine-susceptible population. This increase in microsomal enzyme level is an indication of some indirect effects of phosphine on microsomal enzyme activities and tolerance is not developed at once but it is a gradual process after continuous exposure to sub lethal concentrations of fumigant. So it is recommended that the lethal concentration of phosphine for each population should be calculated periodically to avoid development of tolerance/resistance, so some control could be achieved to eliminate this pest in storage facilities of wheat.

 

Acknowledgement

 

This research article is a part of PhD thesis of first author. The 1st author is highly thankful to higher education commission of Pakistan (HEC) for providing funding to carry out research under its “indigenous 5000 PhD fellowship” program.

 

Ethical standard

This article does not contain any studies with human participants or animals performed by any of the authors.

 

Statement of conflict of interest

The authors stated no conflicts of interest.

 

References

 

Anonymous, 2005-2006. Year book. Government of Pakistan, Ministry of Food, Agriculture and Livestock, Islamabad, pp. 55.

Alvares, A.P. and Mannering, G.J., 1970. Two-substrate kinetics of drug-metabolizing enzyme systems of hepatic microsomes. Mol. Pharmacol., 6: 206–212.

Brattsten, L.B., Holyoke, C.W., Leeper, J.R. and Raffa, K.F., 1986. Insecticide resistance: challenge to pest management and basic research. Science, 231: 1255–1260. https://doi.org/10.1126/science.231.4743.1255

Burges, H.D., 2008. Development of the khapra beetle, Trogoderma granarium, in the lower part of its temperature range. J. Stored Prod. Res., 44: 32–35. https://doi.org/10.1016/j.jspr.2005.12.003

Castalanelli, M.A., Severtson, D.L., Brumley, C.J., Szito, A., Foottit, R.G., Grimm, M., Munyard, K. and Groth, D.M., 2010. A rapid non-destructive DNA extraction method for insects and other arthropods. J. Asia. Pac. Ent., 13: 243–248. https://doi.org/10.1016/j.aspen.2010.04.003

Dauterman, W.C. and Hodgson, E., 1990. Metabolism of xenobiotics. Safer Insect. Dev. Use, Basel, New York, pp. 19–55.

FAO, 1975. FAO plant protection bulletin, 23rd ed.

Fedina, T.Y. and Lewis, S.M., 2007. Effect of Tribolium castaneum (Coleoptera: Tenebrionidae) nutritional environment, sex, and mating status on response to commercial pheromone traps. J. econ. Ent., 100: 1924–1927. https://doi.org/10.1603/0022-0493(2007)100[1924:EOTCCT]2.0.CO;2

Feyereisen, R., 2005. Insect cytochrome P450. Comp. Mol. Insect Sci., 4: 1–77. https://doi.org/10.1016/B0-44-451924-6/00049-1

Gigon, P.L., Gram, T.E. and Gillette, J.R., 1969. Studies on the rate of reduction of hepatic microsomal cytochrome P-450 by reduced nicotinamide adenine dinucleotide phosphate: effect of drug substrates. Mol. Pharmacol., 5: 109–122.

Kotze, A.C. and Wallbank, B.E., 1996. Esterase and monooxygenase activities in organophosphate-resistant strains of Oryzaephilus surinamensis (Coleoptera: Cucujidae). J. econ. Ent., 89: 571–576. https://doi.org/10.1093/jee/89.3.571

Lowry, O.H., Rosebrough, N.J., Farr, A.L. and Randall, R.J., 1951. Protein measurement with the Folin phenol reagent. J. biol. Chem., 193: 265–275.

Mahroof, R., Subramanyam, B. and Flinn, P., 2005. Reproductive performance of Tribolium castaneum (Coleoptera: Tenebrionidae) exposed to the minimum heat treatment temperature as pupae and adults. J. econ. Ent., 98: 626–633. https://doi.org/10.1603/0022-0493-98.2.626

Nakanishi, S., Masamura, E., Tsukada, M. and Matsumura, R., 1971. Kinetic studies for aniline hydroxylase after prolonged ethanol treatment. Jpn. J. Pharmacol., 21: 303–309. https://doi.org/10.1254/jjp.21.303

Nash, T., 1953. The colorimetric estimation of formaldehyde by means of the Hantzsch reaction. Biochem. J., 55: 416. https://doi.org/10.1042/bj0550416

Nelson, D.R., 2003. Comparison of P450s from human and fugu: 420 million years of vertebrate P450 evolution. Arch. Biochem. Biophys., 409: 18–24. https://doi.org/10.1016/S0003-9861(02)00553-2

Oppenoorth, F.J., 1984. Biochemistry of insecticide resistance. Pestic. Biochem. Physiol., 22: 187–193. https://doi.org/10.1016/0048-3575(84)90088-9

Peterson, J.A., Ebel, R.E. and O’Keefee, D.H., 1978. Dual-wavelength stopped-flow spectrophotometric measurement of NADPH-cytochrome P-450 reductase. Methods Enzymol., 52: 221–226. https://doi.org/10.1016/S0076-6879(78)52025-9

Riaz, T., Shakoori, F.R. and Ali, S.S., 2016. Toxicity of phosphine against tolerant and susceptible populations of. Punjab Uni. J. Zool., 31: 25–30.

Riaz, T., Shakoori, F.R. and Ali, S.S., 2014. Effect of temperature on the development, survival, fecundity and longevity of stored grain pest, Trogoderma granarium. Pakistan J. Zool., 46: 1485–1489.

Riaz, T., Shakoori, F.R. and Ali, S.S., 2017. Effect of phosphine on esterases of larvae and adult beetles of phosphine-exposed populations of stored grain pest, trogoderma granarium collected from different godowns of Punjab. Pakistan J. Zool., 49: 819-824.

Schenkman, J.B., Sligar, S.G. and Cinti, D.L., 1981. Substrate interaction with cytochrome P-450. Pharmacol. Ther., 12: 43–71. https://doi.org/10.1016/0163-7258(81)90075-9

Shakoori, F.R., Feroz, A., Riaz, T., 2016. Effect of sub-lethal doses of phosphine on macromolecular concentrations and metabolites of adult beetles of stored grain pest, Trogoderma granarium, Previously exposed to phosphine. Pakistan J. Zool., 48: 583–588.

Simon, J.Y., 2014. The toxicology and biochemistry of insecticides. CRC Press.

Tomita, T., Liu, N., Smith, F.F., Sridhar, P. and Scott, J.G., 1995. Molecular mechanisms involved in increased expression of a cytochrome P450 responsible for pyrethroid resistance in the housefly, Musca domestica. Insect Mol. Biol., 4: 135–140. https://doi.org/10.1111/j.1365-2583.1995.tb00018.x

Valmas, N., Zuryn, S. and Ebert, P.R., 2008. Mitochondrial uncouplers act synergistically with the fumigant phosphine to disrupt mitochondrial membrane potential and cause cell death. Toxicology, 252: 33–39. https://doi.org/10.1016/j.tox.2008.07.060

Vincent, D.R., Moldenke, A.F., Farnsworth, D.E. and Terriere, L.C., 1985. Cytochrome P-450 in insects. 6. Age dependency and phenobarbital induction of cytochrome P-450, P-450 reductase, and monooxygenase activities in susceptible and resistant strains of Musca domestica. Pestic. Biochem. Physiol., 23: 171–181. https://doi.org/10.1016/0048-3575(85)90005-7

Vontas, J.G., Hejazi, M.J., Hawkes, N.J., Cosmidis, N., Loukas, M. and Hemingway, J., 2002. Resistance-associated point mutations of organophosphate insensitive acetylcholinesterase, in the olive fruit fly Bactrocera oleae. Insect Mol. Biol., 11: 329–336. https://doi.org/10.1046/j.1365-2583.2002.00343.x

Walter, V., 2006. Commodity and space fumigations in the food industry. Insect Management Food Storage Process, Second ed. AACC Int. St. Paul, Minnesot, pp. 18. https://doi.org/10.1016/B978-1-891127-46-5.50021-0