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O A
2208
Advances in Environmental Biology, 6(7): 2208-2212, 2012
ISSN 1995-0756
This is a refereed journal and all articles are professionally screened and reviewed
ORIGINAL ARTICLE
Response Of Seven Populations Of The Two-Spotted Spider Mite (Tetranychus Urticae
Koch) For Chlorfenapyr Acaricide On Cucumber In Jordan
1
Tawfiq M.Al-Antary, 2Mohammad Raed Kame l Al- lALA, And 3Marwan I. Abdel-Wali
1
Plant Protection Dept, Faculty of Agriculture, University of Jordan, Amman, Jordan.
Ph.D student
3
Plant Protection Dept, Head, National Center of Agriculture Research and Extension, Ministry of Agriculture,
Amman, Jordan.
2
Tawfiq M.Al-Antary, Mohammad Raed Kame l Al- lALA, And Marwan I. Abdel-Wali: Response Of
Seven Populations Of The Two-Spotted Spider Mite (Tetranychus Urticae Koch) For Chlorfenapyr
Acaricide On Cucumber In Jordan
ABSTRACT
Laboratory bioassays were conducted during the period from June 2009 till August 2010 to evaluate the
toxicities of chlorfenapyr acaricide against adult females of seven populations of the two-spotted spider mite
(Tetranychus. urticae Koch). Six of the seven tested populations were collected from Al-Ramtha, Baq`a, Zyza,
Krimeh, Deir-Alla and Karamah covering the main regions devoted to cucumber cultivation in Jordan. The
seventh population was brought from Syria and was considered as a susceptible strain (SSS). Chlorfenapyr was
very effective against all the tested populations, with the highest estimated LC50 OF CHLORFENAPYR WAS
135.76 ppm against Deir-Alla population while the lowest LC50 was 49 ppm against the SSS strain. The
resistance factors against chlorfenapyr were ranged between 1.14 to 2.77 for all the tested populations. The
toxicity persisted for 9 days against adult mite females when they were applied at of the highest recommended
field dose. In general chlorfenapyr induced 70% mortality to all populations. These results indicated obviously
that most of the local TSSM populations displayed different level, of resistance to chlorfenapyr.
Key words: Acaricide,Toxicity,Chlorfenapyr,Spider-mite,Cucumber ,Jordan
Introduction
Two-spotted spider mite (TSSM), Tetranychus
urticae Koch (Acari: Tetranychidae), is a
polyphagous mite.It is a major pest on field crops,
and plastic-houses crops, [21,20,2]. It has recently
become a serious problem because of the extensive
use of acaricides, resulting in resistance among the
mite populations [6,18]. The development of the
resistance is also known to be accelerated under
confined environmental conditions such as plastichouses [24] particularly the mite has a very short life
cycle. In addition, the mite’s resistance to certain
acaricides has been shown to have cross resistance to
other acaricides. Thus, most commercial acaricides
have been often proved to be ineffective to control
the field mite populations [16,3,9].
From field screening of various acaricides, it
was speculated that TSSM has developed resistance
to the most conventional acaricides, but toxicological
data were very scarce and poorly documented [10]. It
is quite possible that TSSM susceptibility to
acaricides would differ from one location to another
of cucumber cultivation in Jordan. Therefore, it was
important to monitor the acaricide susceptibilities of
T. urticae populations that were collected from
cucumber cultivation in Jordan and to evaluate the
efficacy of testing acaricides. This study showed the
results of laboratory-based tests that determined the
response of six field populations (Al-Ramtha, Baq'a,
Zyzya, Krimeh, Deir-Alla, and Karamah) and one
susceptible strain of T. urticae to chlorfenapyr.
In 2009, the total number of plastic-houses in
Jordan, which were planted with vegetables, was
about 66,000. More than fifty percent of them were
planted with cucumber (36,000). [12]. The Jordanian
farmers rely heavily on acaricides to control the twospotted spider mite. Therefore, they have increased
the rate of application, applied a mixture of
acaricides and applied acaricides more frequently
than they should. They have complained about
unsatisfactory results in controlling T. urticae
[13,14]. The total quantity of acaricides imported to
Jordan in 2009 was 120,000 liters and / or kilograms.
The imported acaricides belong to 18 active
ingredients. The most active ingridient was
chlorfenapyr [12].
Corresponding Author
Tawfiq M.Al-Antary, Plant Protection Dept, Faculty of Agriculture, University of Jordan, Amman,
Jordan.
E-mail: [email protected]
2209
Adv. Environ. Biol., 6(7): 2208-2212, 2012
In addition to imported acaricides, there were
more than 15 local agrochemical factories that
produce different formulations of active ingredients.
Although TSSM represents a real threat to cucumber
plantation under plastic-houses in Jordan, few
toxicological studies on this pest have been
conducted. Therefore, this study aimed to evaluate
the susceptibilities of TSSM collected from
cucumber cultivation in Jordan to the studied
chlortenapyr and to find the resistance factors to the
tested among the (TSSM) populations.
between 27 -+ 5 C and 57-+8% and a photoperiod of
L16:D8. plants were irrigated and replaced as
needed.
Materials And Methods
The Tested acaricide:
Populations of the mite:
Chlorfenapyr 24% W/V,SC(pirate). Produced by
American Cyanamid Co(now BASF AG) in
1998,with higher recommended rate of 120 mg/L
H2O. Its Molecular formula is C15H11BrCIF3N2O
[19].
Seven T. urticae populations of different origin
were used in this study. Six of these populations
were collected from cucumber plants grown under
plastic houses conditions in different regions of
Jordan. These geographical regions include AlRamtha (100 Km North West of Amman), Baq'a (20
Km north west of Amman), Zyzya (30 Km South of
Amman), Krimeh (South of Jordan Valley), DeirAlla (Central of Jordan Valley) and Karamah (South
of Jordan Valley). These regions are considered the
main area for cucumber production in the country.
Other T. urticae was strain was obtained from
Lattakia Center for Rearing and Production of
Biological Agents (LCRPBA) in Syria. This strain
was reared there for 5 years and they did not spray it
by acaricides at all.
Production of bean plants:
Bean (Phaseolus vulgaris L. cv. Bronco) was
chosen for rearing and for the toxicological tests of
the (TSSM) because it is one of the mite’s favorite
host, and for its ease of producing transplants. Seeds
of bean (Bronco, Asgrow, USA) were directly sowed
inside 10 cm. pots. Potting media used was Peatmoss and Perlite with 3:1 ratio. Plants were infested
with SSS T. urticae when they reached the true leaf
stage. These plants were irrigated and replaced as
needed. No pesticides were applied on the plants
except for later the tested acaricides. These plants
were grown under greenhouse conditions at a
temperature of 25-35C, relative humidity of 45% to
60% and a photoperiod of L16:D8.
For use in the toxicological tests, polystyrene
trays of 84 cells were filled by Peat-moss and Perlite
(3:1 ratio). Then, these trays were sown by 1-2 bean
seeds for each cell, after complete germination the
cotyledon leaves were used in the toxicological tests.
Rearing of the Syrian susceptible strain:
Syrian T.urticae strain(SSS) was reared and
maintained on Phaseolus vulgaris at the Faculty of
Agriculture, University of Jordan, at temperature
Plant materials:
P. vulgaris seeds were sowed in 84 polystyrene
trays filled with Peat-moss and Perlite at ratio of 3:1.
Each cell was sowed with one or two seeds. Prior to
germination, cotyledon leaves of seedling were used
for all experimental sets.
Preparing of stock solution:
For each test, fresh stock solution was prepared
by dissolving a calculated quantity of the acaricide
enough to run the whole concentrations needed. The
acaricide were used as its commercial formulation.
Bioassay of the acaricide toxicity:
Toxicological bioassays were conducted
according to the procedures described by IRAC [7].
Cotyledon leaves from untreated bean plants were
placed, lower side up, in Petri-dishes lined with
water-saturated cotton wool. 25 adult females of T.
urticae were introduced into each cotyledon leaf by
using a binocular microscope and a fine paintbrush.
24 hours after mite release, each Petri-dish was
sprayed with a constant amount of the acaricide
solutions for 2 seconds using a hand sprayer. The
sprayed Petri-dishes were left to dry for 30 minutes,
then they were placed under room temperature. Mites
condition was assessed by gentle probing with a fine
paintbrush. Mites were classed as dead when they
didn’t move or displayed some movement not
exceeding their body length. Mites which were able
to move were considered alive. This assessment of
mites conditions were recorded 48 hours after
acaricide application. The LC50, and LC90 values
and their 95% confidence limits were calculated from
probit regressions using the SPSS13 program
[17,23].
The application of the acaricide was done with
four replicates per each concentration, and with
seven concentrations for the acaricide. These
concentrations were chosen based on preliminary
studies and they were different for each T. urticae
population. Tap water was sprayed as control.
These experiments were carried out in the Pesticide
laboratory at temperature between 25,5 C and 57,8%
relative humidity.
2210
Adv. Environ. Biol., 6(7): 2208-2212, 2012
Statistical analysis:
Data were subject to probit analysis [4] which
incorporated Abbott's correction for natural mortality
[1]. The SPSS (version 13 USA) computer program
was used for data analysis to estimate LC50 and
LC90 values, regression coefficient (slope) and its
standard error, intercept and its standard error,
Pearson goodness of fit chi-square, expected
mortality, and 95% confidence limits (95%CL) for
effective level of concentrations. This programmed
used normal equivalent deviate (NED) instead of
probit numbers. However, NED numbers can be
readily adjusted to probit by adding 5 to each NED
number (Finney, 1971). Y value for each line
estimated by probit regression was equal to 0.0 and
1.28 when LC50 and LC90 (X) value was converted
to log base 10, respectively.
LC50 and LC90 values were considered
significant when (95% CL) did not overlap. To
determine the resistance factor (RF) for each
population, the LC50 of each acaricide of the field
population was divided by the corresponding LC50
for the susceptible strain. The resistance factors were
categorized according to Fukami (1983) as follows:
low. RF<10, moderate 10<RF≤ 40, high 40-60 and
very high resistance >60. LC90 values in ppm
divided by the higher recommended field rate in ppm
were calculated and tabulated for each TSSM strain
(Ratio value). Goodness of line fitting was checked
by Chi-square test X2. According to Finney (1971),
the value of X2 at 0.05 level of probability equals to
14.1 at 5 degree of freedom (df). Results obtained in
this study revealed that (X2) Goodness of fit chisquare were less than that tabulated for each
regression line indicating goodness of fit at 0.05 level
of probability.
Results:
Susceptibility of seven populations of T.urticae
collected from different locations of cucumber
production are illustrated in Table (1).Bioassay tests
showed that chlorfenapyr pronounced significantly
the lowest LC50 values for mite populations
originated from Syria and Al-Ramtha, whereas
populations collected from Deir-Alla and Karamah
displayed considerably the greatest LC50
values(Table1). However, there were no significant
differences between LC50 values for the populations
from Deir-Alla,and Karamah,as well as LC50 values
were not significantly different for the populations
from Zyzya and Krimeh. Also there were no
significant differences between Al-Ramtha and the
SSS strain while LC50 value for Baqa population
was significantly different from all the other
populations(Table1).The estimated LC50 values of
chlorfenapyr against tested T.urticae field
populations were (350.64) for Karamah,(350.02) for
Deir-Alla,(278.92ppm) for Zyzya,(213.33ppm) for
Baqa(177.34ppm) for Krimeh, and (143.6ppm) for
Al-Ramtha population. From the LC90 values it was
noted that there were no significant differences
among Karamah,Deir-Alla and Zyzya populations.
Furthermore, the LC90 values were not significantly
different for the SSS compared with the populations
from Al-Ramtha and Krimeh. Estimated Resistance
factors showed clearly that Deir-Alla (RF=2.77) and
Karamah (2.75) populations were more resistant to
chlorfenapyr toxicity, followed by
Zyzya
(2.26),Krimeh(2.2),Baqa(1.51),and Al-Ramtha(1,14).
Table 1: Susceptibilities of field-collected populations of T. urticae adult females to chlorfenapyr (Higher recommended field rate =120
mg/L).
LC50(mg/l)
LC90(mg/l)
L.E.P.R2
Ratio4
RF5
Population name
Slope±S.E3.
95%CL1
95%CL
Y=a+b(x)
LC90
LC50
55.87 d6
143.60 c6
Ar-Ramtha
Y=-5.46+3.13 (x)
50.41-61.01
126.71-169.23
3.13±0.26
1.2
1.14
74.17 c
213.33 b
Baq'a
Y=-5.22+2.79 (x)
65.86-81.97
186.15-255.07
2.79±0.24
1.78
1.51
110.97 b
278.92 ab
Zyzya
Y=-6.55+3.20 (x)
100.22.121.08
247.13-326.66
3.20±0.27
2.32
2.26
107.83 b
177.34 bc
Krimeh
Y=-12.06+5.93 (x)
102.50-112.90
165.49-199.18
5.93±0.48
1.48
2.2
135.76 a
350.02 a
Deir-Alla
Y=-6.65+3.12 (X)
122.31-148.43
309.32-411.97
3.12±0.26
2.92
2.77
134.85 a
350.64 a
Karamah
Y=-6.58+3.09 (x)
121.4-147.54
309.74-411.97
3.09±0.26
2.92
2.75
49.05 d
129.59 cd
_
SSS
Y=-5.14+3.04 (x)
43.82-53.95
114.74-151.56
3.04±0.25
1.1
95% Confidence limits for LC50 or LC90 in ppm.
L.E.P.R. = Line Estimated by Probit Regression.
S.E. = Standard error.
Ratio LC90 = LC90 / higher recommended field rate.
R.F. Resistance Factor= LC50 of field population / LC50 of susceptible population (SSS).
LC50 or LC90 values having different letters are significantly different (95% CL did not overlap).
2211
Adv. Environ. Biol., 6(7): 2208-2212, 2012
Discussion:
Monitoring
of
local
populations
for
susceptibility towards acaricides is the first step in
resistance management of T. urticae. It is essential to
carry out acaricide resistance tests regularly to avoid
resistance development in target mites. In addition,
control tactics must depend on the use of different
acaricides to avoid or delay resistance.
Chlorfenapyr was found to provide an excellent
control in controlling T.urticae adult females. The
resistance factors indicate that there was a moderate
resistance to chlorfenapyr (RF ranged from 1.14 to
2.77). Chlorfenapyr was produced in (1998) and it
was registered and introduced to Jordan in 2005, so
this acaricide is now out of patency which means that
the market will be saturated with generics and T.
urticae susceptibility will be negatively affected. The
present results agreed with results obtained by
several authors [9,8] from Korea. The authors
concluded that the RF values of chlorfenapyr were
low (RF ≤ 3). However, Lee et al [10] found that the
resistance factors of anther acaricide named
abamictin, varied between 0.3 to 90.5 towards
T.urticae eight populations collected from deferent
locations in Korea
(rf <3). However, lee et al., [10] found that the
resistance factors of anothen acaricide named
abamectin,varied between 6.3 to 19.5 towards T.
urticae eight populations collected from different
locations in korea. In Japan, Ochiai et al. [15].
estimated LC50 for another acaricide named
bifenazate against T. urticae was 0.63 ppm.. In
Belgium, Van Leeuwen et al., [22] reported that
bifenazate-resistant strain lacked cross resistance to
many different chemical classes and modes of action
of other acaricides This might be applied also on the
results of the present study of chlortenapyr In South
Korea, Lee et al. [10] concluded that all T. urticae
populations tested had low to moderate resistance to
bifenazate. Resistance factors ranged from 0.8 to
11.0. The same authors mentioned that the resistance
to other acaricides might result in the cross resistance
to bifenazate or other acaricide such as chlortenapyr
of this study ,However, Martinson et al., [11]
concluded that the reference susceptible population,
and the bioassay methods differ among researchers,
and it is therefore not easy to compare these
results.The present obtained results do not agree with
those obtained by Marcic (2007) in Serbia. These
conflicting results might be due to the bioassay test
used. In our present study, results were taken on
treated adult females of TSSM while Marcic(2007)
studied the toxicity of spiromesifen on fecundity and
fertility and population growth rates of TSSM.
In conclusions all the tested field populations
were susceptible to chlorfenapyr. The resistance
factor ranged from 1.14 to 2.77. At its high
recommented field rate chlorfenapyr effective in
controlling T.urticae.However , chlorfenapyr was
active in controlling adult females of TSSM when it
was used at its recommended rate, as well as it had
long residual effect. However, in order to gain safe
and high cucumber product and to manage resistance
development by T.urticae to acaricides the following
are recommended:
1. Regular monitoring should be carried out to
detect the extent of resistance to the pesticides used.
2. Restricting the use of acaricides to which
the magnitude of resistance is high.
3. Establishing of baseline LC50 to new
acaricide before widespread use which allow better
monitoring of changes in susceptibility over time.
4. Applying acaricides that have different
active ingredients and different mode of action.
5. Training growers on alteration of acaricides
based on mode of action to facilitate long term
sustainable spider mite management for agriculture
in Jordan.
6. Studying the mechanisms of resistance to
acaricides is very important to prevent cross
resistance between closely related groups.
Acknowledgments
Thanks are extended to the Dean ship of
Research at UNIVERSITY OF JORDAN and
Agriculture Materials company administration for
finance support. Thanks are also to the staff at
theLattakia (enter for Rearing and production of
biological Agents in Syria for providing us the
sensitive strain of the spider mite.
Refferences
1.
2.
3.
4.
5.
6.
7.
8.
Abbott, W., 1925. A method of computing the
effectiveness of an insecticide.J. Economic
Entomology, 18: 265-267.
Al-Mommany, A and T. Al-Antary, 2008. Pests
of Garden and Home, 2nd edition. Jordan
University Publications, Amman. pp: 518.
El kady, G.A., H.M. El-Sharabasy, M.F.
Mahmoud and I.M. Bahgat, 2007. Toxicity of
two potential bio-insecticides against moveable
stages of Tetranychus urticae Koch. Journal of
Applied Science Research, 3(11): 1315-1319.
Finney, D., 1971. Probit Analysis. Cambridge
University Press. London, pp: 333.
Fukami, J., Y. Uesugi and K. Ishizuka, 1983.
Pest Resistance to Pesticides. Soft Science
Inc.,Tokyo, Japan.
Gough, N., 1990. Evaluation of miticides for the
control of two- spotted spider mite Tetranychus
urticae Koch on field roses in southern
Queensland .Crop Protection, 9: 119-127.
IRAC, Insecticide Resistance Action Committee,
2004. Susceptibility test methods No 3 and 4a.
www.irac-online,org
Kim, Y.J., S.W. Lee, J.R. Cho, H.M. Park and
Y.J. Ahn, 2007. Multiple resistance and
2212
Adv. Environ. Biol., 6(7): 2208-2212, 2012
9.
10.
11.
12.
13.
14.
15.
16.
biochemical mechanisms of dicofol resistance in
Tetranyches urticae (Acari:Tetranychidae).
J.Asia Pacific Entomol., 10(2): 165-170.
Koh, S.H., Y.J. Ahn, J.S. Im, C. Jung, S.H. Lee
and J.H. Lee, 2009. Monitoring of acaricide
resistance
of
Tetranychus
urticae
(Acari:Tetranychidae) from Korean apple
orchards. J. of Asia-Pacific Entomology, 12: 1521.
Lee, Y.S., M.H. Song, K.S. Ahn, K.Y. Lee, J.W.
Kim and G.H. kim, 2003. Monitoring of
acaricide resistance in two-spotted spider mite
(Tetranychus urticae) populations from rose
greenhouses in korea . J.Asia-Pacific
Entomokogy, 6(1): 91-96.
Martinson, T.E., T.J. Dennehey, J.p. Nyrop and
W.H. Reissing, 1991. Field-measurements of
selection
for
two
spotted
spider-mite
(Tetranychus urticae) (Acari:Tetranychidae)
Resistance
to
dicofol
in
apple
orchards.J.Econ.Entomol., 84: 7-16.
Ministry of Agriculture, 2009. Annual
Agricultural Statistics. The Hashemite Kingdom
of Jordan. Amman, Jordan.
Nazer, I.K., 1982. Susceptibility of the spider
mite (Tetranychus urticae Koch.) to certain
acaricides.Dirasat, 9: 71-77.
Nazer, I.K., 1985. Response of the two-spotted
spider
mite(Tetranychus
urticae
Koch.),collected from the Jordan Valley, to
certain acaricides. Dirasat, 12: 143-150.
Ochiai, N., M. Mizuno, N.T. Miyake, M.
Dekeyser, L.J. Canlas and M. Takeda, 2007.
Toxicity of bifenazate and its principal active
metabolite,diazene,to Tetranychus urticae and
panonychus citri and their relative toxicity to the
predaceous mites,Phytoseiulus persimilis and
Neoseiulus californicus.Exp.Appl.Acarol., 43:
181-197.
Ramasubramanian, T., K. Ramaraju and A.
Regupathy, 2005. Acaricide resistance in
Tetranychus
urticae
Koch
(Acari:
17.
18.
19.
20.
21.
22.
23.
24.
Tetranychidae) Global Scenario. Journal of
Entomology, 2(1): 33-39.
Robertson, J.L., R.M. Russell, H.K. Preisler and
N.E. Savin, 2007. Bioassays With Arthropods.
CRC Press, Boca Raton., pp: 250.
Sokeli, E., R. Ay and I. Karaca, 2007.
Determination of the resistance level of twospotted spider mite (Tetranychus urticae Koch)
population in apple orchards in Isparta Province
against some pesticides. Ankara University
Ziraat Fakultesi., 13(4): 326-330.
Tomlin, C.D., 2005. The Electronic Pesticide
Manual, 13th edition. Crop Protection
Publications. British Crop Protection Council.
Farnham, Surrey, UK
Tsagkarakou, A., M. Navajas, J. Lagnel, J.
Gutierrez and N. Pasteur, 1996. Genetic
variability in Tetranychus urticae (Acari:
Tetranychidae) from Greece: insecticide
resistance and isozymes. Entomological Society
of America., 1345-1358.
Van den Boom, C.E.M., T.A. Van Beek and M.
Dicke, 2003. Differences among plant species in
acceptance by the spider mite Tetranychus
urticae Koch.Journal of Applied Entomology,
127: 177-183.
Van Leeuwen, T., L. Tirry and R. Nauen, 2006.
Complete maternal inheritance of bifenazate
resistance in Tetranychus urticae Koch (Acari:
Tetranychidae) and its implications in mode of
action considerations. Insect Biochemistry and
Molecular Biology, 36: 869-877.
Van Pottelberge, S., van T. Leeuwen, R. Nauen
and L. Tirry, 2009. Resistance mechanisms to
mitochondrial electron transport inhibitors in a
field-collected strain of Tetranychus urticae
Koch (Acari: Tetranychidae), Bulletin of
Entomological Research, 99: 23-31.
Zhang, Z.Q., 2003. Mites of Greenhouses:
Identification, Biology and Control. CABI
Publishing, Wallingford, UK, pp: xii+244.
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