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1 June 2017 Bioassay of Plant Extracts Against Aleurodicus dispersus (Hemiptera: Aleyrodidae)
Md. Abdul Alim, Janghoon Song, Un Taek Lim, Jang Jeon Choi, Md. Alamgir Hossain
Author Affiliations +

The spiraling whitefly, Aleurodicus dispersus Russell (Hemiptera: Aleyrodidae), is a destructive invasive pest in many parts of the world. Topical spray and dry film contact assays were conducted to measure the toxicity of 8 plant extracts and their mixtures traditionally used as insecticides in South Asian countries such as Bangladesh, India, and Nepal. The highest mortality (100%) of adults was recorded for neem (Azadirachta indica A. Juss.; Meliaceae) (ethanol) extract (500 mg/L) at 6 h after topical spray. This was followed by 5-leaved chaste tree (Vitex negundo L.; Lamiaceae) (ethanol), sweet sop (Annona squamosa L.; Annonaceae) (acetone), water pepper (Polygonum hydropiper L.; Polygonaceae) (acetone), banyan (Ficus benghalensis L.; Moraceae) (ethanol), banyan (acetone), and crown flower (Calotropis gigantea [L.] W. T. Aiton; Apocynaceae) (ethanol) extracts at 500 mg/L at 12 h after the spray. For the dry film method, the highest mortality (100%) of adults was also recorded for neem (ethanol) extract (500 mg/L) at 18 h after the treatment. Bioassay results indicate that neem (ethanol) extract mixed with crown flower (acetone), oleander (Nerium indicum Mill.; Apocynaceae) (acetone), or sweet sop (ethanol) (in the ratio of 1:1, 1:2, and 1:3 for each plant extract) showed synergism. Neem (ethanol) extract also showed the highest mean repellency rate (93%). In conclusion, neem, 5-leaved chaste tree, sweet sop, water pepper, banyan, and crown flower extracts showed good potential to control A. dispersus, and the mixtures of these plant extracts showed synergistic activity against A. dispersus.

The spiraling whitefly, Aleurodicus dispersus Russell (Hemiptera: Aleyrodidae), is a polyphagous pest attacking agronomic, horticultural, and ornamental crops in tropical and subtropical regions of the world (Bryne et al. 1990; Aiswariaya et al. 2007). Recently, A. dispersus has become the most serious pest of guava, Psidium guajava (Myrtales), orchards in Bangladesh and India (Kajita & Alam 1996; Aiswariaya et al. 2007), having been introduced through the movement of plant materials from other countries (Kajita & Alam 1996). The pest has also been reported in Brazil, Ecuador, Peru, the Philippines, Fiji, Indonesia, the Maldives, the Mariana Islands, and the Canary Islands on a variety of hosts (Waterhouse & Norris 1989; Nasruddin & Stocks 2014).

Severe infestations of this pest are a serious threat to guava production directly damaging the plant by removing sap from leaves, which reduces growth, weakens plants, and reduces crop yield (Nasruddin & Stocks 2014). Whiteflies also reduce the photosynthetic area of the leaves and lower the market value of fruit due to cosmetic damage from sooty mold (Bryne et al. 1990; Liu et al. 2007). Sooty mold may increase thermal absorption and raise leaf temperature, reducing leaf efficiency and causing premature tissue death (Bryne et al. 1990). Serious infestations of A. dispersus have been found on important ornamental plants, including poinsettia (Euphorbia pulcherrima Willd. ex Klotzsch; Euphorbiaceae) and madhobilota (Hiptage benghalensis [L.] Kurz; Malpighiaceae) in Bangladesh (Alim et al. 2014).

Chemical insecticides are partially effective against spiraling whitefly (Liu et al. 2007) but do not always provide effective control due to the presence of wax covering immature stages (James 2003). Because both nymphs and adults of A. dispersus feed on the lower surfaces of leaves, it is difficult to achieve effective coverage by spraying contact insecticides. Furthermore, the use of chemical pesticides may promote resistance in the pest and pollute the environment (Amjad et al. 2009). Thus, there is a need for alternative approaches to replace or supplement the current chemical-based pest management practices in guava orchards (Dubey & Sundararaj 2004).

Plant extracts are potential alternatives due to their high toxicity to insects, low development cost, and general safety to people (Isman 2000).To promote the use of such materials, we examined the toxicity of 8 plant extracts, neem (Azadirachta indica A. Juss; Meliaceae), 5-leaved chaste tree (Vitex negundo L.; Lamiaceae), sweet sop (Annona squamosa L.; Annonaceae), oleander (Nerium indicum L.; Apocynaceae), China box (Buxus sinica [Rehder & E.H. Wilson] M. Cheng; Buxaceae), water pepper (Polygonum hydropiper L.; Polygonaceae), banyan (Ficus benghalensis L.; Moraceae), and crown flower (Calotropis gigantea [L.] W. T. Aiton; Apocynaceae), and mixtures of these that traditionally have been used in Bangladesh and India (Rajashekar et al. 2012; Ahad et al. 2015) to suppress A. dispersus.

Table 1.

Toxicity of extracts from 8 plant species against Aleurodicus dispersus adults by topical spray.


Materials and Methods


The adults of A. dispersus used in assays were obtained from guava trees where they were managed without use of insecticides in guava orchards. Aleurodicus dispersus used in our bioassays were adults at least 24 h old collected randomly from a population of several hundred individuals maintained on guava branches (temperature 26.2 °C and RH 84%).To produce insects for tests, infested guava branches were combined with whitefly-free guava twigs for 24 h. The new twigs infested with whitefly eggs were then covered with mosquito netting (22 cm L × 15 cm D) and held for whitefly development. Branches were observed daily for whitefly pupation, and new adults were collected as they emerged and used in subsequent bioassays.


Eight plant species from Bangladesh and India that are known to have insecticidal activity (Rajashekar et al. 2012) were identified from their natural habitats from Dinajpur District, Bangladesh, and their leaves were used in our bioassays (Table 1). The identity of each plant species was verified and confirmed by plant morphology (Karim & Kabir 1995).


Fresh leaves for extraction were collected from mature plants (after the fruiting stage), cut into pieces, and ground in a mortar with a pestle. Ten grams of ground leaves of a particular species were mixed with 100 mL distilled water at room temperature (27.7 ± 0.2 °C; 75 ± 10% RH), and the mixture was passed through filter paper (Whatman ® No. 1, Sigma-Aldrich, Inc. Germany). Twenty-five mL of this filtrate were mixed with 100 mL of 1 of 2 solvents (ethanol or acetone) (Abe & Matsuda 2000). Each mixture was shaken for 30 min and left to separate in a funnel (V × L: 250 mL × 345 mm) with a conical flask (200 mL). After collection of the relevant fraction from the separating funnel, the extract was transferred to a flask and condensed by evaporating the solvent in a rotary evaporator (D 79219, Ika Werke Gmbh and Co., Staufen, Germany) at 78 °C or 56 °C, for ethanol and acetone extracts, respectively. The crude extract was then transferred quantitatively to a clean, weighed vial and kept in a refrigerator (3.0 ± 0.2 °C) until used for assays.


Topical Method

Test solutions from each of the 32 plant extracts were prepared in 10 mL batches (400 and 500 mg/L with 50% acetone in water). To prepare a test arena, a guava leaf petiole was inserted into moistened cotton and placed in a Petri dish (15 cm D × 3 cm H) with the ventral surface facing upward. Adults of A. dispersus (24 h old) from the rearing colony were collected in a group and placed on ice to allow counting. Batches of 20 cold-immobilized adults were placed on test leaves in Petri dishes with a fine brush and allowed to warm and regain mobility. When 15 insects had recovered from cold-immobilization and resumed activity, 1 mL of the 400 mg/L test solution was sprayed onto the leaf with a spray tower (Potter, Burkard Company, Oxbridge, United Kingdom). After air-drying, each Petri dish was closed with a lid and sealed with Parafilm®. Control Petri dishes were treated with an acetone (50% in water) solution. Each test was replicated 3 times. Treated adult whiteflies were examined for mortality at 6 h intervals after the treatment for 3 d. Adults that did not respond to probing with a small brush were considered dead. These procedures were conducted for the 8 acetone extracts and for the 8 ethanol extracts at concentrations of 400 and 500 mg/L.

Residual Assay Method

A guava leaf petiole was inserted into moistened cotton and placed into a Petri dish (15 cm D × 3 cm H) with the underside of the leaf facing upward. Test solutions (1 mL of the 400 or 500 mg/L solutions of either ethanol or acetone extracts) of each plant species were sprayed separately onto leaves using the spray tower as in the previous experiment, and the leaves were allowed to air-dry for 1 h. Twenty adults of A. dispersus (24 h old) were immobilized on ice as described for the previous experiment and gently placed on the treated leaves in the Petri dishes. Control Petri dishes were treated with acetone (50% in water). Each test was replicated 3 times. The treated adults were examined for mortality at 6 h intervals for 72 h after the treatment. Adults that did not show any responses when probed with a small brush were considered dead.

Tests with Mixed Extracts

The synergistic effect of mixtures of neem (ethanol) plus crown flower (acetone), neem (ethanol) plus oleander (acetone), and neem (ethanol) plus sweet sop (ethanol) extracts on A. dispersus adults was determined by the co-toxicity coefficient (CTC) method in the laboratory (Sun & Johnson 1960; Zhang et al. 2008). The concentration of 500 mg/L of 3 different mixtures at 3 ratios (1:1, 1:2, and 1:3) was applied using the spray tower to 20 A. dispersus adults, which were incubated in Petri dishes as described for the previous experiments. A control was sprayed with distilled water. Each treatment was replicated 3 times. Mortality was recorded at 6 h intervals up to 72 h after treatment.

The co-toxicity coefficient (CTC) was calculated as: (LD50 of toxicant alone / LD50 of toxicant in the mixture) × 100. When CTC is 100, it indicates a probability of similar action. When CTC > 100, a synergistic action can be assumed whereas CTC < 100 indicates antagonism.

Repellency Tests

Two fully expanded guava leaves were placed in a Petri dish (15 cm D × 3 cm H) with the ventral surface facing upward. One leaf was dipped in the tested plant extract (500 mg/L) and another was dipped in acetone (50% in water). Twenty adults of A. dispersus (24 h old) were immobilized on ice and gently introduced between the 2 treated leaves in the Petri dish (5 cm D × 1 cm H). Numbers of adults resting on each leaf were recorded after 3, 6, and 24 h. Each test was replicated 3 times.

Data were expressed as percentage of repulsion (PR) as PR (%) = (Nc - 50) × 2, where Nc = the percentage of insects present in the control. Positive (+) values indicate repellency and negative (−) values indicate attraction. Repellency class was categorized as class 0 ≤ 0.1, class I = 0.1 to 20.0, class II = 20.1 to 40.0, class III = 40.1 to 60.0, class IV = 60.1 to 80.0, and class V = 80.1 to 100.0% repellency (McGovern et al. 1977).


Differences in mortality among treatments were analyzed by univariate comparison testing (ANOVA) with SPSS® software version 16.0 (SPSS Inc., Chicago, IL). Post-hoc analyses were done by the Tukey test (Zar 2010). Data on lethal effects, Chi-squared values, and LT50 values were obtained from probit analysis (Robertson et al. 2007). Significant differences among the extracts in each assay were recorded when 95% confidence intervals (CI) did not overlap. LD50 values of the tested plant extracts and confidence limits were calculated for A. dispersus with log dosage-mortality probit regression equations. Co-toxicity coefficients were calculated according to Sun & Johnson (1960).



Mortality of A. dispersus adults on guava leaves sprayed with different plant extracts under laboratory conditions varied significantly by extract (Table 1). All plant extracts had an adverse effect on A. dispersus at different times after the treatment in this assay (Fig. 1A). At 6 h after the topical application of neem (500 mg/L), 100% mortality was recorded for the ethanol extract and 51% for the acetone extract. The topical application of neem (500 mg/L) caused 74% mortality at 12 h after application for the acetone extract. Five-leaved chaste tree (ethanol), sweet sop (acetone), water pepper (acetone), banyan (ethanol), banyan (acetone), and crown flower (ethanol) extracts caused 100% mortality at 12 h after topical spray (Table 1; Fig. 1A). When applied at 400 mg/L (with 50% acetone as diluent), sweet sop (acetone), banyan (ethanol), and crown flower (ethanol) extracts caused 100% mortality at 18 h after topical spray (Table 1; Fig. 1B). Probit analysis showed that A. dispersus was most sensitive to neem ethanol extract and least sensitive to crown flower (acetone) extract (Table 2). The mortality response to dose among extracts is summarized in Table 2.


Neem (ethanol) extract at 500 mg/L (with 50% acetone as diluent) caused the highest mortality and killed 100% of A. dispersus 18 h after treatment when extracts were presented as dried residues (residual assay method) (Fig. 2A). Neem (acetone), 5-leaved chaste tree (acetone), China box (acetone), banyan (acetone), and crown flower (ethanol) extracts caused 100% mortality at 30 h after treatment with 500 mg/L (with 50% acetone as diluent). The other plant extracts were effective but caused significantly lower mortality. Based on probit analysis, neem (ethanol) extract was the most toxic to A. dispersus whereas crown flower (acetone) extract was the least toxic (Table 3; Fig. 2A). Neem (ethanol) extract caused the highest mortality of A. dispersus in the residual assay method within 24 h after treatments (Fig. 2B). Mortality responses to 500 mg/L and 400 mg/L (with 50% acetone as diluent) are summarized in Table 3.

Fig. 1.

Survival of Aleurodicus dispersus adults exposed to the plant extracts tested by topical spray: 500 mg/L (A), 400 mg/L (B).



The effects of 3 different mixtures, neem (ethanol) plus crown flower (acetone), neem (ethanol) plus oleander (acetone), and neem (ethanol) plus sweet sop (ethanol) extracts at 3 ratios (1:1, 1:2, and 1:3) on adults of A. dispersus were synergistic. Bioassay results revealed that the synergism was significant, and their cotoxicity coefficients were highest in neem (ethanol) plus crown flower (acetone) extracts (256.78) and lowest in neem (ethanol) plus oleander (acetone) extracts (102.02) at 1:3 and 1:1 ratios, respectively (Table 4).


The repellency of the tested plant extracts to A. dispersus adults varied (Table 5). Neem (ethanol) extract showed the highest mean repellency rate (93.3%) and belongs to repellency class V, followed by water pepper (ethanol), water pepper (acetone), and crown flower (ethanol) extracts in the same class. The 5-leaved chaste tree (acetone) and crown flower (acetone) extracts belong to repellency class IV, and the rest of the plant extracts belong to different repellency classes. Sweet sop (acetone) extract showed the lowest mean repellency rate (35.6%), belonging to repellency class II.

Fig. 2.

Survival of Aleurodicus dispersus adults exposed to the plant extracts tested by the dry film method: 500 mg/L (A), 400 mg/L (B).


Table 2.

Statistical comparison of LT50 values of plant extracts against Aleurodicus dispersus adults tested by topical spray (n = 45).


Table 3.

Statistical comparison of LT50 values of plant extracts against Aleurodicus dispersus adults tested by dry film (n = 45).



Chemicals derived from Dalmatian pyrethrum (Tanacetum cinerariifolium [Trevir.] Sch. Bip.; Asteraceae), neem, and other plant species are traditionally used to control various crop pests in Asia (Saminathan & Jayaraj 2001; Liang et al. 2003; Atkinson et al. 2004). Neem products, tobacco extracts, and rosin soap have been found to be effective against A. dispersus in several countries such as Bangladesh, India, and Pakistan (Dubey & Sundararaj 2004; Kambrekar & Awaknavar 2004; Sinha et al. 1992; Luo et al. 2002). Zhang et al. (2008) observed that ethanol extracts of Celosia argentea L. (Amaranthaceae) and Eupatorium odoratum L. (Asteraceae) had high activity against A. dispersus, with LC50 values of 753.4 and 999.8 mg/L, respectively.

Our results indicated that neem, 5-leaved chaste tree, sweet sop, oleander, China box, water pepper, banyan, and crown flower extracts at 500 mg/L all exhibited significant insecticidal action against A. dispersus in the topical spray assay. Among the 8 plant species, the highest adult mortality was found with neem (ethanol) extracts irrespective of assay method (Tables 1 and 2), although acute toxicity of neem extract was higher when it was extracted in ethanol than when extracted in acetone. Ethanol is a better solvent for extracting more of the toxic component from neem leaves (Sharma et al. 2010). The next most effective plant extracts were 5-leaved chaste tree (ethanol), sweet sop (acetone), water pepper (acetone), banyan (ethanol), banyan (acetone), and crown flower (ethanol) at 12 h after treatment at 500 mg/L. In the dry film assay, the highest mortality (100%) was also recorded from neem (ethanol) at 18 h after treatment at 500 mg/L. Dubey & Sundararaj (2004) reported that bi- and tri-weekly applications of neem effectively controlled nymphal populations of A. dispersus, causing 62.2% mortality even 21 d after treatment. In another study, Neemark® (West Coast Herbochem Ltd. Mumbai, India) retained its toxicity (from an initial mortality of 55% to 45% on day 15) better than NeemAzal® T/S (E.I.D. Parry, India, Ltd.) (45% to 25% mortality); Neemark® is neem leaf extract 2% w/w and NeemAzal® contains 10 g/L azadirachtin A in the form of an emulsifiable concentrate (Kambrekar & Awaknavar 2004). Thus, the different results of toxicity tests in this study might be caused by different toxic compounds being extracted.

Table 4.

Comparative toxicity of mixed plant extracts to Aleurodicus dispersus adults.


Table 5.

Repellency rates of tested plant extracts against Aleurodicus dispersus adults at different hours after treatment.


The synergistic effects of neem (ethanol) with crown flower (acetone), oleander (acetone), and sweet sop (ethanol) extracts to A. dispersus were significant (Table 4). Sakthivel et al. (2011) found a synergistic effect of dimethoate (0.05%) with neem oil (3%), with this combination providing mortality in eggs (81%) and nymphs and adults (94%) of A. dispersus. The plant extracts tested probably displayed different modes of action against A. dispersus. Azadirachtin (the major ingredient of neem insecticide) alone has been shown to have various modes of action including direct effects by inhibiting cell division and protein synthesis and indirect effects by blocking hormone release (Mordue [Luntz] & Nisbet 2000). Mixtures of plant extracts with different modes of action could enhance synergism and delay the development of resistance in A. dispersus. A mixture of different active compounds was suggested for Bemisia tabaci (Gennadius) (Hemiptera: Aleyrodidae) control to reduce the development of insecticide resistance (Isman 2000; Dubey & Sundararaj 2004). Myzus persicae (Sulzer) (Hemiptera: Aphididae) developed resistance to pure azadirachtin but not to neem seed extract; the different constituents in the seed extract (i.e., azadirachtin, salanin, nimbin, and their respective analogues) might have different modes of action or different target sites in the aphid (Feng & Isman 1995). Prakash & Rao (1997) did an extensive revision of plants containing secondary compounds active against insects. These authors reported 866 plant products with insecticidal, repellent, antifeedant, or insect growth regulator activity. Larew & Locke (1990) proposed that botanical insecticides may involve the removal of insects' cuticle wax, physical action, repellency, or cell membrane disruption. Valladares et al. (2003) examined the antifeeding activity of an extract of senescent leaves of Melia azadirachta L. (Meliaceae) on 9 insect species and found leaf extract strongly deterred feeding and increased mortality. Our results also show the highest repellency rate in neem (ethanol) plant extract (Table 5).

In conclusion, this study indicates that neem (ethanol), 5-leaved chaste tree (ethanol), sweet sop (acetone), water pepper (acetone), banyan (ethanol), and crown flower (acetone) extracts were the most effective extracts tested against A. dispersus. All the plant extract mixtures tested showed synergism against A. dispersus. These results should promote the development of new products suitable for controlling A. dispersus in organic guava orchards. Future studies are needed to screen active components and develop effective formulations for use in the field.


The authors acknowledge the Ministry of Science and Technology, Government of the People's Republic of Bangladesh for financial support.

References Cited


Abe M, Matsuda K. 2000. Feeding deterrents from Momordica charantia leaves to cucurbitaceous feeding beetle species. Applied Entomology and Zoology 35: 143–149. Google Scholar


Ahad MA, Nahar MK, Amin MR, Suh SJ, Kwon YJ. 2015. Biological activities of five weed extracts against Callosobruchus chinensis L. (Coleoptera: Bruchidae). Korean Journal of Applied Entomology 54: 83–89. [In English] Google Scholar


Aiswariaya KK, Manjunatha M, Naik M. 2007. Biology and host range of spiraling whitefly. Karnataka Journal of Agricultural Science 20: 149–152. Google Scholar


Alim MA, Hossain AA, Rahman F. 2014. Population dynamics of spiraling whitefly on ornamental plants and its natural enemies in Bangladesh. Bangladesh Journal of Entomology 24: 47–55. Google Scholar


Amjad M, Bashir MH, Afzal M, Khan MA. 2009. Efficacy of some insecticides against whitefly (Bemisia tabaci Genn.) infesting cotton under field condition. Pakistan Journal of Life and Social Sciences 7: 140–143. Google Scholar


Atkinson BL, Blackman AJ, Faber H. 2004. The degradation of the natural pyrethrins in crop storage. Journal of Agricultural and Food Chemistry 52: 280–287. Google Scholar


Bryne DN, Bellows TS, Parella MP. 1990. Whiteflies in agricultural system, pp 227–226 .In Gerling D [ed.], Whiteflies: Their Bionomics, Pest Status and Management. Intercept Press, Andover, United Kingdom. Google Scholar


Dubey AK, Sundararaj R. 2004. Evaluation of neem products against Aleurodicus dispersus Russell (Aleyrodidae: Homoptera) on Bauhinia variegate and Michelia champaca. Indian Journal of Plant Protection 32: 126–128. Google Scholar


Feng R, Isman MB. 1995. Selection for resistance to azadirachtin in the green peach aphid, Myzus persicae. Experientia 51: 831–833. Google Scholar


Isman MB. 2000. Plant essential oils for pest and disease management. Crop Protection 19: 603–608. Google Scholar


James RR. 2003. Combining azadirachtin and Paecilomyces fumosoroseus (Deuteromycotina: Hyphomycetes) to control Bemisia argentifolii (Homoptera: Aleyrodidae). Journal of Economic Entomology 96: 25–30. Google Scholar


Kajita H, Alam MZ. 1996. Whiteflies on guava and vegetables in Bangladesh and their aphelinid parasitoids. Applied Entomology and Zoology 31: 159–162. [In English] Google Scholar


Kambrekar DN, Awaknavar JS. 2004. Field evaluation of insecticides and oil combinations against spiraling whitefly, Aleurodicus dispersus on guava. Karnataka Journal of Agricultural Science 17: 712–716. Google Scholar


Karim SM, Kabir SM [eds.]. 1995. An introduction to weeds of Bangladesh. Bangla Academy, Dhaka, Bangladesh, 25–68 pp. [In Bengali] Google Scholar


Larew HG, Locke JC. 1990. Repellency and toxicity of a horticultural oil against whiteflies on chrysanthemum. HortScience 25: 1406–1407. Google Scholar


Liang GM, Chen W, Liu TX. 2003. Effects of three neem-based insecticides on diamondback moth (Lepidoptera: Plutellidae). Crop Protection 22: 333–340. Google Scholar


Liu SS, De Barro PJ, Xu J, Luan JB, Zang LS, Ruan YM, Wan FH. 2007. Asymmetric mating interactions drive widespread invasion and displacement in a whitefly. Science 318: 1769–1772. Google Scholar


Luo C, Yao Y, Wang RJ, Yan FM, Hu DX, Zhang ZL. 2002. The use of mitochondrial cytochrome oxidase mtCOI gene sequences for the identification of biotypes of Bemisia tabaci (Gennadius) in China. Acta Entomologica Sinica 45: 759–763. Google Scholar


McGovern TP, Gillenwater HB, McDonald LL. 1977. Repellents for adult Tribolium confusum Mandelates. Journal of the Georgia Entomological Society 12: 79–84. Google Scholar


Mordue (Luntz) AJ, Nisbet AJ. 2000. Azadirachtin from the neem tree Azadirachta indica: its action against insects. Anais da Sociedade Entomológica do Brasil 29: 615–632. Google Scholar


Nasruddin A, Stocks IC. 2014. First report of economic injury due to the spiraling whitefly (Hemiptera: Aleyrodidae) on pepper in Indonesia. Florida Entomologist 97: 1255–1259. Google Scholar


Prakash A, Rao J. 1997. Botanical Pesticides in Agriculture. CRC Press, Boca Raton, Florida. Google Scholar


Rajashekar Y, Bakthavatsalam N, Shivanandappa T. 2012. Botanicals as grain protectants. Psyche 2012: article 646740. Google Scholar


Robertson JL, Preisler HK, Russell RM. 2007. PoloPlus: Probit and Logit Analysis User's Guide. LeOra Software, Petaluma, California. Google Scholar


Sakthivel N, Punithavathy G, Qadri SMH. 2011. Evaluation of different insecticides and botanicals against spiraling whitefly Aleurodicus dispersus (Russell) infesting mulberry. Indian Journal of Sericulture 50: 98–102. Google Scholar


Saminathan VR, Jayaraj S. 2001. Weeds as host of the spiralling whitefly, Aleurodicus dispersus Russell (Homoptera: Aleyrodidae) around Madurai, Tamil Nadu. Pest Management and Economic Zoology 9: 27–30. Google Scholar


Sharma T, Qamar A, Khan MA. 2010. Evaluation of neem (Azadirachta indica) extracts against the eggs and adults of Dysdercus cingulatus (Fabricius). World Applied Sciences Journal 9: 398–402. Google Scholar


Sinha SN, Chakrabarti AK, Agnihotri NP, Jain HK, Gajbhiye VT. 1992. Field evaluation of synthetic pyrethroids against thrips, Thrips tabaci (Lind.) on onion and their residues. Indian Journal of Entomology 54: 44–47. Google Scholar


Sun YP, Johnson ER. 1960. Analysis of joint action of insecticides against house flies. Journal of Economic Entomology 53: 887–892. Google Scholar


Valladares G, Garbin L, Defagó MT, Carpinella C, Palacio S. 2003. Antifeedant and insecticide activity of an extract from senescent leaves of Melia azedarachta (Meliaceae). Revista de la Sociedad Entomológica Argentina 62: 53–56. [In Spanish] Google Scholar


Waterhouse DF, Norris KR. 1989. Biological Control: Pacific Prospects. Supplement 1. Australian Centre for International Agricultural Research, Canberra, Australia. Google Scholar


Zar JH. 2010. Biostatistical Analysis, 5th Edition. Prentice Hall, Upper Saddle River, New Jersey. Google Scholar


Zhang ZX, Cheng DM, Hu S, Xu HH. 2008. It is unreasonable to use co-toxicity coefficient to evaluate the synergism of pesticides. Plant Protection 34: 34–36. [In Chinese] Google Scholar
Md. Abdul Alim, Janghoon Song, Un Taek Lim, Jang Jeon Choi, and Md. Alamgir Hossain "Bioassay of Plant Extracts Against Aleurodicus dispersus (Hemiptera: Aleyrodidae)," Florida Entomologist 100(2), 350-357, (1 June 2017).
Published: 1 June 2017
aspersiones directas
direct spray
efecto mutuo
extracto mixto
mixed extract
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