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E-SURVEILLANCE AND MANAGEMENT OF CONGRESS
GRASS, Parthenium hysterophorus L. THROUGH MEXICAN
BEETLE, Zygogramma bicolorata P. AND RECORD OF
NATURAL ENEMIES OF FEW COMMONLY
ASSOCIATED WEEDS
Ph.D. (Ag.) Thesis
by
Hemkant Chandravanshi
DEPARTMENT OF ENTOMOLOGY
COLLEGE OF AGRICULTURE
FACULTY OF AGRICULTURE
INDIRA GANDHI KRISHI VISHWAVIDYALAYA
RAIPUR (Chhattisgarh)
2018
E-SURVEILLANCE AND MANAGEMENT OF CONGRESS
GRASS, Parthenium hysterophorus L. THROUGH MEXICAN
BEETLE, Zygogramma bicolorata P. AND RECORD OF
NATURAL ENEMIES OF FEW COMMONLY
ASSOCIATED WEEDS
Thesis
Submitted to
Indira Gandhi KrishiVishwavidyalaya, Raipur
by
Hemkant Chandravanshi
IN PARTIAL FULFILMENT OF THE REQUIREMENTS FOR
THE DEGREE OF
Doctor
of
Philosophy
in
Agriculture
(Entomology)
Roll No.130115028 ID.No. 20131418499
January, 2018
i
ACKNOWLEDGEMENT
I feel whole hearted to thank my beloved chairman, Dr. (Smt.) Jayalaxmi Ganguli,
Associate Professor, Department of Entomology for her incessant and stead fast
inspiration, laudable counseling and surpassing guidance who conceived, shaped the
problem and provided insightful and indomitable lead with much care and affection
during the period of study.
I express my sincere and profound gratitude to Dr. V. K. Dubey, Head
department of Entomology. College of Agriculture, Raipur, for his inspiring
suggestions and providing me all the necessary facilities, during my study.
With extreme pleasure I thank my whole hearted sense of appreciation for the
other members of my Advisory Committee, Dr. Sanjay Sharma, Principal scientist
(Rice), Department of Entomology, Dr. Nitish Tiwari, Scientist, Department of
Agronomy and Dr. Ravi R. Saxena, Professor, Department of Agricultural Statistics
& Social Science, for providing proper guidance and encouragement throughout the
research work. Without their kind cooperation, it would not have been easy for me to
complete this manuscript.
I am highly obliged to Hon’ble Vice- Chancellor Dr. S.K. Patil, Dr. O.P.
Kashyap, Dean, College of Agriculture and Dr. S.S. Shaw, Director of Instructions,
IGKV, Raipur for providing necessary facilities to conduct the investigation.
I do express my heartiest thanks to the teachers of my department Dr. A. K.
Dubey, Dr. V. K. Koshta, Dr. R. N. Ganguli, Dr. Rajeev Gupta, Dr. H. K.
Chandrakar, Dr. S.K. Shrivastava, Dr. Y. K. Yadu, Dr. GajendraChandrakar, Dr.
NavneetRana, Dr. B. P. Katalam, Dr. Sonali Deole for their constant co-operative
suggestion, encouragement and help during my investigation.
I am thankful to Dr. Randeep Kushwaha, RAEO, Department of Agriculture,
Govt. of Chhattisgarh, for his kind support.
As, dearest is the friends love who have volunteered help at the time of need
for achieving my cherished goal paves me to offer loveable and debted thanks to Payal
iii
TABLE OF CONTENTS
Chapter Title Page
ACKNOWLEDGEMENT
I
TABLE OF CONTENTS Iii
LIST OF TABLES Vi
LIST OF FIGURES Viii
LIST OF NOTATIONS Xi
ABSTRACT xii
I INTRODUCTION 1
II REVIEW OF LITERATURE 4
2.1: To record the natural enemies of congress grass,
Parthenium hysterophorus L. with special reference to
its management with Mexican beetle, Zygogramma
bicolorata Pallister
4
2.2: To study the e-surveillance of parthenium and other
associated weeds in Kharif and Rabi season
6
2.3: To work out the feeding potential of Mexican beetle,
Zygogramma bicolorata P. under laboratory conditions
9
2.4: To study the bionomics of Mexican beetle, Zygogramma
bicolorata P.under laboratory conditions
10
III MATERIALS AND METHODS 16
3.1: To record the natural enemies of congress grass,
Parthenium hysterophorus L. with special reference to
its management with Mexican beetle, Zygogramma
bicolorata Pallister
16
3.1.1: Location of study 16
3.1.2: Geographical situation& climate 18
3.1.3: Details of study 18
3.2: To study the e-surveillance of parthenium and other
associated weeds in Kharif and Rabi season
18
3.2.1: Location of study: 18
3.2.2: Geographical situation& climate 18
3.2.3: Selection of villages 20
3.2.4: Details of study: 20
3.3: To work out the feeding potential of Mexican beetle,
Zygogramma bicolorata P. under laboratory conditions
20
3.3.1: Location of study: 20
3.3.2: Experimental details 20
iv
3.3.2.1: Feeding potential of Mexican beetle 20
3.3.2.2: Food consumption by adult & grubs
Mexican beetle within 24hrs
21
3.4: To study the bionomics of Mexican beetle, Zygogramma
bicolorata P. under laboratory
25
3.4.1: Location of study: 25
3.4.2: Details of study: 25
3.5: Statistical Analysis 25
IV RESULT AND DISCUSSION 29
4.1: To record the natural enemies of congress grass,
Parthenium hysterophorus L. with special reference to
its management with Mexican beetle, Zygogramma
bicolorata Pallister
29
4.1.1: Agro-forestry area 30
4.1.2: Cropped field area 31
4.1.3: Road side area 33
4.2: To study the e-surveillance of parthenium and other
associated weeds in Kharif and Rabi season
50
4.2.1: Upland 50
4.2.1.1: Arang block 50
4.2.1.2: Dharsiwa block 50
4.2.1.3: Tilda block 51
4.2.1.4: Abhanpur block 51
4.2.2: Midland 51
4.2.2.1: Arang block 51
4.2.2.2: Dharsiwa block 52
4.2.2.3: Tilda block 52
4.2.2.4: Abhanpur block 52
4.2.3: Lowland 52
4.2.3.1: Arang block 53
4.2.3.2: Dharsiwa block 53
4.2.3.3: Tilda block 53
4.2.3.4: Abhanpur block 53
4.2.4: Associated weeds with Porthanium and their
insect pest recorded during 2016-17 at Raipur
64
4.3: To work out the feeding potential of Mexican beetle,
Zygogramma bicolorata P. under laboratory conditions
54
4.3.1: Feeding potential of Mexican beetle 67
4.3.1.1: Early stage 67
4.3.1.2: Pre-reproductive 67
4.3.1.3: Reproductive 67
4.3.2: Food consumption by adult & grubs Mexican
beetle within 24hrs
71
4.4: To study the bionomics of Mexican beetle, Zygogramma 74
v
bicolorata P. under laboratory conditions
VI SUMMARY AND CONCLUSION 80
REFERENCES 88
RESUME 95
vi
LIST OF TABLES
Table Title Page
3.2 The e-surveillance programme conducted through GPS machine at
five villages of four each block of Raipur District
19
4.1aa Mean data of the associated insects with congress grass, P.
hysterophorus recorded under agro-forestry field area of IGKV
campus, Raipur during
35
4.1ab Mean data of the associated insects with congress grass recorded under
field cropped area of IGKV campus, Raipur during 2016
36
4.1ac Mean data of the associated insects with congress grass recorded under
road side area of IGKV campus, Raipur during 2016
37
4.1ba Mean data of the associated insects with congress grass under agro-
forestry area of IGKV campus, Raipur during 2017
40
4.1bb Mean data of the associated insects with congress grass under field
cropped area of IGKV campus, Raipur during 2017
41
4.1bc Mean data of the associated insects with congress grass under road
side area of IGKV campus, Raipur during 2017
42
4.1ca Pooled mean data of the associated insects with congress grass under
agro-forestry field area of IGKV campus, Raipur during 2016 &17
45
4.1cb Pooled mean data of the associated insects with congress grass under
field cropped area of IGKV campus, Raipur during 2016 &17
46
4.1cc Pooled mean data of the associated insects with congress grass under
road side area of IGKV campus, Raipur during 2016 &17
46
4.2a e-surveillance of parthenium and associated insects at Raipur District
in Kharif – Rabi season during 2016
55
4.2b e-surveillance of parthenium and associated insects at Raipur
Districtin Kharif – Rabi season during 2017
58
4.2c Pooled mean of e-surveillance of parthenium and associated insects at
Raipur District in Kharif – Rabiseason during 2016 and 2017
61
4.2d Insect-pest reported on other associated weeds with parthenium at
different block of Raipur District in Kharif – Rabi season during 2016-
17
66
4.3.1a Time taken (days) by Mexican beetle, Zygogramma bicolorata P. for
complete defoliation by different number of beetles releases per plant
under laboratory conditionsduring 2016&2017
68
4.3.1b The mean height and number of leaves per Parthenium plant at 68
vii
different plant stages
4.3.2a Food consumption by different stages of Mexican beetle, Zygogramma
bicolorata P. within 24hrs (in mg) under laboratory conditionsduring
2016&2017
72
4.4a Details of egg related of Mexican beetle, Zygogramma bicolorata
P.under laboratory conditionsduring 2016&2017
76
4.4b Bionomics of the different life stages of Mexican beetle, Z. bicolorata
under laboratory conditions during 2016&2017
78
viii
LIST OF FIGURES
Figure Title Page
3.1 Recording observations on insect pest of Parthenium at IGKV
campus, Raipur, C.G.
17
3.2 Recording observations on insect pest of Parthenium at Arang
block, Raipur, C.G.
17
3.3.1 Mass multiplication of Mexican beetle, Z. bicolorata, reared in cut
plastic tanks covered with nylone net using low cost technology
22
3.3.2 Mass multiplication of Mexican beetle, Z. bicolorata in cages under
laboratory conditions
22
3.3.3 Experiment conducted for testing complete defoliation of different
ages of Parthenium plants by releasing different number of pair
beetles, Z. bicolorata
23
3.3.4 Recording observations on the feeding efficiency of Z. bicolorata at
different stage of Parthenium plants
23
3.3.5 Eggs of Z. bicolorata on leaf of Parthenium 24
3.3.6 Food consumption by grubs and adult Mexican beetle, Z. bicolorata
P. under laboratory condition
24
3.4.1 Recording observations on bionomics of Z. bicolorata in Bio-
control laboratory, Department of Entomology, CoA, IGKV.
27
3.4.2 Bionomics observations of Z. bicolorata with microscope in Bio-
control laboratory, Department of Entomology, CoA, IGKV
27
3.4.3 Eggs of Mexican beetle, Z. bicolorata 28
3.4.4 Grub of Z. bicolorata under microscopic measurement 28
3.4.5 Grub of Mexican beetle, Z. bicolorata 28
3.4.6 Pupa of Mexican beetle, Z. bicolorata 28
3.4.7 Adult of Mexican beetle, Z. bicolorata 28
3.4.8 Male and female of Mexican beetle, Z. bicolorata 28
4.1aa Mean data showing the natural enemies of congress grass under
agro-forestry area of IGKV campus of Raipur during 2016
38
4.1ab Mean data showing the natural enemies of congress grass under
field croppedarea of IGKV campus of Raipur during 2016
38
4.1ac Mean data showing the natural enemies of congress grass under
road side area of IGKV campus of Raipur during 2016
39
4.1ad Mean data showing the natural enemies of congress grass under
agroforestry, field cropped and road side area of IGKV campus of
Raipur during 2016.
39
ix
4.1ba Mean data showing he natural enemies of congress grass under
agro-forestry area of IGKV campus of Raipur during 2017
43
4.1bb Mean data showing the natural enemies of congress grass under
field cropped area of IGKV campus of Raipur during 2017
43
4.1bc Mean data showing the natural enemies of congress grass under
road side area of IGKV campus of Raipur during 2017
44
4.1bd Mean data showing the natural enemies of congress grass under
agroforestry, field cropped and road side area of IGKV campus of
Raipur during 2017.
44
4.1ca Mean data showing the natural enemies of congress grass under
agro-forestry area of IGKV campus of Raipur during 2016 &2017
48
4.1cb Mean data showing the natural enemies of congress grass under
field cropped area of IGKV campus of Raipur during 2016 &2017
48
4.1cc Mean data showing the natural enemies of congress grass under
road side area of IGKV campus of Raipur during 2016 &2017
49
4.1cd Mean data showing the natural enemies of congress grass under
agroforestry, field cropped and road side area of IGKV campus of
Raipur during 2016 &2017.
49
4.2aa The data sowing different block of e-surveillance of UL, ML & LL
of enemies on parthenium and other associated weedsduringKharif –
Rabi season during 2016
56
4.2ab The data sowing e-surveillance on parthenium and other associated
weeds at Raipur District in Kharif – Rabi season during 2016
57
4.2ac The data sowing e-surveillance of different enemies of on
parthenium and other associated weeds at Raipur District
duringKharif – Rabi season during 2016
57
4.2ba The data sowing different block of e-surveillance of UL, ML & LL
of enemies on parthenium and other associated weeds duringKharif
– Rabi season during 2017
59
4.2bb The data sowing e-surveillance on parthenium and other associated
weeds at Raipur District in Kharif – Rabi season during 2017
66
4.2bc The data sowing e-surveillance of different enemies of on
parthenium and other associated weeds at Raipur District
duringKharif – Rabi season during 2017
66
4.2ca The pooled data sowing different block of e-surveillance of UL, ML
& LL of enemies on parthenium and other associated weeds during
Kharif – Rabi season during 2016& 17
62
4.2cb The pooled data sowing e-surveillance on parthenium and other 63
x
associated weeds at Raipur District in Kharif – Rabi season during
2016&17
4.2cc The pooled data sowing e-surveillance of different enemies of on
parthenium and other associated weeds at Raipur District
duringKharif – Rabi season during 2016&17
63
4.3.1a The mean day’s data sowing feeding potential of Mexican beetle,
Zygogramma bicolorata P. under laboratory conditionsduring
2016&2017
69
4.3.1b The pooled mean of the feeding potential of different number of
Mexican beetle on different age of Parthenium weeds during
2016&2017
70
4.3.2a The data sowing food consumption by Mexican beetle, Zygogramma bicolorata
P. within 24hrs (in mg) under laboratory conditionsduring
2016&2017
73
4.4a The figure showing average number of eggs, incubation period,
hatching number and hatching percentage of Mexican beetle,
Zygogramma bicolorata P.under laboratory conditions during
2016&2017
77
4.4b The figure showing different life stages of Mexican beetle under
laboratory conditions during 2016&2017
79
xi
LIST OF NOTATIONS/SYMBOLS
Notation Description
cm - Centimeter
mm - Millimeter
% - Per cent
oC - degree celsius
ml - milliliters
gm - grams
hrs - hours
/ - Per
Av - Average
sqm - Square meter
χ2 - chi square
RH - relative humidity
Temp - temperature
ha - hectares
i.e - that is
p - probability
@ - At the rate
Fig - figure
Viz; - namely
xiii
Canthocona bugs (0.02). In case of cropped field and road side area along with
highway also, similar trend was observed with highest number of ants (1.74 and 1.43)
and minimum number of Canthocona bugs (0.09). Descending order of the Mexican
beetle population/ten plants in agro-forestry, cropped field and road side area along
with highwaywas observed in different months as August<July<September<October.
The e-surveillance of parthenium and other associated weeds conducted at four
different blocks (Arang, Dharsiwa, Tilda and Abhanpur) of Raipur District, showed
that the overall mean population of associated insects at upland, midland and lowland
ranged from 0.06 to 2.57/sqm. The data indicated that the maximum population was
exhibited of ants (2.57/m2) and minimum (0.06/m
2) of Canthocona bugs while in case
of the Mexican beetle, Z. bicolorata was highest (2.46/m2) in low land situation. On
the basis of data, it can be concluded that the maximum natural enemies were
observed against Parthenium at Arang block, followed by Dharsiwa with minimum in
Tilda block of Raipur District.
Studies conducted to record associated weeds of Parthenium in Kharif and
Rabi 2016-17 depicted thirty seven weed species. Among the insect pests associated
on them, revealed domination by sucking pests viz; aphids, hoppers and mealy bugs.
Ants were recorded in large number associated with them. Few species of
semiloopers, caterpillars and mites/spiders were also noticed. Two predators namely
Coccinellid beetles and Canthocona bugs were also recorded.
The feeding potential of Mexican beetle on, Z. bicolorata at three age stages
i.e. early, pre-reproductive and reproductive stage of Parthenium grass on the basis of
overall mean data of two years indicated that it differed significantly. The lowest time
taken was (5.17 days) for complete defoliation by five pairs of Mexican beetles
followed by four pairs (9.00 days) and highest in two pairs (14.83 days). Therefore, in
early stage the damage inflicted by Z. bicolorata was more pronounced when it was
applied at early growth stages of the weed. Food consumption by adult and grubs of
Mexican beetle within 24hrs at different stages i.e. first, second, third, fourth instars
xiv
and adults indicated that maximum (11.03mg) foliage was consumed by third instar
grubs followed by fourth instars (7.94mg) and minimum in adults stage (0.74mg).
Among grubs and adult stages of the beetle, the third and fourth instars ingested
maximum.
The fecundity of a single female of Z. bicolorata P. was recorded to be 226.17
eggs. The incubation period ranged between 4.00 to 6.00 days with an average of 5.08
days, whereas, number of hatched eggs ranged from 5.33 to 27.33 with an average of
17.36 and the average per cent egg hatchability was 73.71%. There were four instars
of larval stages (grub) ranging from 3.00, 4.67, 5.17 and 6.00 days of first, second,
third and fourth instar respectively. The overall average larval duration was 18.83 days
while pupation period lasted for 8.67 days and the average adult longevity was found
to be of 81.7 days. The mean duration of life cycle was computed to be of 114.28 days
at 25±2 oc.
xvi
gh U;wure dSaFkksdksuk eRdq.k ¼0-02½ esa ns[kh xbZA Qly ç{ks= vkSj jktekxZ ds lkFk lM+d
fdukjs {ks= ds ekeys esa] leku ço`fÙk, lcls T;knk Øe'k% phafV;ks esa ¼1-74 vkSj 1-43½ vkSj
de ls de dSaFkksdksuk eRdq.k ¼0-09½ ds lkFk ns[kk x;kA eSfDldu chVy vkcknh dk ?kVrs
vkns'k&Øe] —f"k okfudh] Qly ç{ks= vkSj jktekxZ ds lkFk lM+d ds fdukjs ds {ks= esa
fofHkUu eghuksa ds nkSjku] vxLr < tqykbZ < vDVwcj eghus esa ns[kk x;kA
jk;iqj ftys ds pkj vyx&vyx fodkl&[kaMks ¼vkjax] /kjlhok] frYnk vkSj vHkuiqj½
ij vk;ksftr xktj ?kkl vkSj vU; lacaf/kr [kjirokj dh bZ&fuxjkuh us n'kkZ;k fd Åijh]
e/; vkSj fupyh Hkwfe dh lrg dk lEiw.kZr;k vkSlr dhVla[;k dk jsat 0-06 ls 2-57 çfr
oxZehVj FkhA vkadM+ksa us ladsr fn;k fd vf/kdre la[;k ¼2-57½ çfr oxZehVj phfV;ksa esa vkSj
de ls de ¼0-06½ dSaFkksdksuk eRdq.k esa fn[kkA tcfd eSfDldu chVy ds ekeys esa lcls
T;knk ¼2-46½ çfr oxZehVj FkkA vkadM+ksa ds vk/kkj ij] ;g fu"d"kZ fudkyk tk ldrk gS fd
vf/kdre çk—frd nq'euksa dk xktj ?kkl vkSj vU; lacaf/kr [kjirokj ds f[kykQ vkjax
fodkl&[kaM esa blds ckn /kjlhok fodkl&[kaM esa blds lkFk gh U;wure frYnk
fodkl&[kaM] jk;iqj ftys esa ns[kk x;k FkkA
[kjhQ vkSj jch 2016&17 esa xktj ?kkl ds lkFk tqM+s [kjirokjksa dks fjd‚MZ djus ds
fy, fd, x, v/;;uksa esa lSarhl [kjirokj çtkfr;ksa dks n'kkZ;kA mu ij ik, x, dhVksa esa]
jl pwlus okys dhVks dk opZLo irk pyk ftlesa eSuh] Qqndk vkSj pw.khZ eRdq.k ik, x,A
phafV;ksa dh cM+h la[;k muds lkFk tqM+s gq, ntZ fd;k x;A lkFk gh v/kZdq.Myd dhV]
bfYy;k ] lw{e edM+h] ijHk{kh edfM+;ksa dh Hkh dqN çtkfr;ka ns[kh x;hA nks ijHk{kh dhVks
dks Hkh ukfer fd;k x;k tSls dksfDlusfyM Hk`ax rFkk dSaFkksdksuk eRdq.M tks fd de la[;k esa
ntZ fd;s x,A
eSfDldu chVy] tk. ckbdksyksjkVk ih- dk nks lky ds vkSlr vkadM+ksa ds vk/kkj ij
xktj ?kkl ds rhu vk;q voLFkk tSls dh f'k'kq voLFkk] iwoZ&çtuu vkSj çtuu voLFkk ij]
egRoiw.kZ :i ls fHkUu n'kkZ;kA iw.kZr;k fu"i=.k ds fy, lcls de le; ¼5-17 fnu½
eSfDldu chVy ds ikap tksM+s ds ç;ksx ls blds ckn pkj tksM+s ¼9-00½ vkSj lcls vf/kd
le; nks tksM+s ¼14-83 fnu½ esa ns[kk x;kA vr,o] tc bls xktj ?kkl ds çkjafHkd fodkl
xvii
voLFkk esa NksM+k x;k Fkk] rks esfDldu chVy }kjk dh xbZ {kfr dks lcls de le; esa rFkk
vf/kd Li"V :i ls n'kkZ;kA eSfDldu chVy ds fofHkUu vk;q voLFkk vFkkZr~ çFke] f}rh;]
rr̀h;] prqFkZ voLFkkvks vkSj o;Ldksa }kjk Hkkstu xzg.k djus dh {kerk dks çfr 24 ?kaVksa ds
Hkhrj vkadus ij ;g ik;k x;k fd vf/kdre ¼11-03 feyhxzke½ Hk{k.k r`rh; Hk`axd voLFkk
}kjk blds mijkar prqFkZ Hk`axd voLFkk ¼7-94 feyhxzke½ vkSj U;wure esa o;Ld voLFkk ¼0-74
feyhxzke½ esa FkkA
esfDldu chVy dh ,d eknk }kjk dqy vaMk mRiknu 226.17 vkSj 4-00 ls 6-00
fnuksa dh vkSlr Å"ek;u vof/k FkkA tcfd vaMs QwVus dk jsat 5-33 ls 27-33 rd rFkk
vkSlr 17-36 FkkA vaMs QwVus dk çfr'kr 73-71% FkkA Hk`axd ds pkjksa voLFkk;s çFke] f}rh;]
rr̀h; ,oa prqFkZ voLFkk dh le;kof/ks Øe'k% 3.00] 4-67] 5-17 vkSj 6-00 fnu FksA lexz
vkSlr Hk`axd dh vof/k 18-83 fnu Fkh] tcfd 'ka[khdj.k dh vof/k 8-67 fnuksa dh ikbZ xbZ
Fkh rFkk vkSj vkSlr o;Ld vk;q 81-7 fnu dh ns[kh xbZA
CHAPTER I
INTRODUCTION
Congress grass, Parthenium hysterophorus L. belonging to family
Asteraceae commonly known as carrot weed and gajar ghans in hindi is an
invasive weed species in Africa, Australia and Asia. It is a native of tropical and
sub-tropical South and North America. The lightness of the seed, prolific seed
production, adaptability to wide range of habitats, drought tolerance, its ability to
release toxic chemicals against other plants, and its high growth rate allows it to
colonize new areas quickly and extensively.
Parthenium hysterophorus L. is a highly invasive plant of global
significance. It is an herb of geotropical origin which now has spread too many
parts of the world (Adkins and Shabbir, 2014). The weed was accidentally
introduced to India in 1955 through imported food grains and at present has
invaded throughout India in about 35 million hactares of land (Sushil kumar and
Varshney 2007, Sushil kumar 2014).
It is notorious for causing allergic reactions (Kologi et al. 1997) besides a
threat to biodiversity and loss of crop productivity (Adkins and Shabbir 2014,
Sushil kumar, 2014). Management of Parthenium through manual and chemical
methods are effective strategies to control the weed in agricultural fields, but these
are not economical in pastures and large natural areas or wastelands
(Krishnamurthy et al. 1977).
The Mexican beetle, Zygogramma bicolorata Pallister (Coleoptera:
Chrysomelidae) was imported into India in 1983 for the biological control of the
noxious parthenium weed, P. hysterophorus L. Grubs and adult beetles feed
voraciously on the foliage and inflorescence and were mostly confined to congress
weed (Annadurai 1990; Jayanth and Nagarkatti 1997). The bio-ecology (Dhiman
and Bhargava 2005) and in vitro rearing of the beetle on parthenium has been well
documented (Jayanth et al. 1996; Kulkarni et al. 2000). Although the beetle is
known to occur throughout the year, the insect diapauses over an extended period
1
of time in nature (Jayanth et al. 1997) resulting in extensive proliferation of the
weed in its absence.
Classical biological control started with the introduction of a host-specific
leaf-feeding beetle, Z. bicolorata P. from Mexico (Jayanth 1987). In spite of good
information available on Parthenium about insects, fungi and plants infesting it,
countable efforts were made in the past to review all such information at one place.
The paper gives the thin scenario of different groups of bioagents and their status
in controlling Parthenium in India along with the important work carried out in the
world.
Biological control of Parthenium weed is considered to be the most cost
effective, environmentally safe and ecologically viable method (Dhileepan et al.
2000a). It was documented to control Parthenium worth of Rs 10 million in terms
of herbicide cost after initial release of bioagent, Z. bicolorata P. at Jabalpur, India
(Sushil kumar 2006) and it was estimated that this bioagent had checked the spread
of Parthenium in about eight million hectares of land since its release in India.
Omkar and pandey (2009) studied the effect of different temperatures on
reproductive attributes of Z bicolorata. They found that pre-oviposition and
postoviposition period declined with increasing temperature. Oviposition period
decreased from 92.9 to 27.5 days with temperature increment after 27 °C.
The weed suppresses growth of local vegetation and has been reported as a
health hazard for farm laborers causing dermatitis, eczema and asthma (NavBahar
2000). The weed is also a reservoir of tobacco leaf curl virus, mung yellow mosaic
and okra yellow vein mosaic virus (Singh and Singh 1999), groundnut and
sunflower bud necrosis (Chakravarthy 2002), tobacco streak virus (Rao et al. 2003)
and tomato leaf curl virus (Ansari et al. 2004).
In Chhattisgarh also, the congress grass, P. hysterophorus L. is omnipresent
in agricultural/horticultural fields, road side avenues, uncultivated lands and has
become a menace. So far, details of its presence in Raipur district have not been
documented; neither entomological aspects of other associated insect pests has
been studied.
2
Hence, looking to the above aspects, the present piece of work was
formulated entitled “E-surveillance and management of congress grass,
Parthenium hysterophorus L. through Mexican beetle, Zygogramma bicolorata
P. and record of natural enemies of few commonly associated weeds” under the
following objectives:
1. To record the natural enemies of congress grass, Parthenium hysterophorus
L. with special reference to its management with Mexican beetle,
Zygogramma bicolorata Pallister.
2. To study the e-surveillance of parthenium and other associated weeds in
Kharif and Rabi season.
3. To work out the feeding potential of Mexican beetle, Zygogramma
bicolorata P. under laboratory conditions.
4. To study the bionomics of Mexican beetle, Zygogramma bicolorata
P.under laboratory conditions.
3
CHAPTER II
REVIEW OF LITERATURE
This chapter deals with the brief account of research work done on the related
aspects by various workers from the state, country and abroad. The literature
pertaining to the present investigation entitled, “E-surveillance and management
of congress grass, Parthenium hysterophorus L. through Mexican beetle,
Zygogramma bicolorata P. and record of natural enemies of few commonly
associated weeds” was conducted in the Bio-control laboratory, Department of
Entomology, CoA, IGKV, Raipur including four blocks of Raipur district during
2016 & 2017 were collected and grouped under the following headings.
2.1: To record the natural enemies of congress grass, Parthenium hysterophorus L.
with special reference to its management with Mexican beetle, Zygogramma
bicolorata Pallister,
2.2: To study the e-surveillance of Parthenium and other associated weeds in
Kharif and Rabi season,
2.3: To work out the feeding potential of Mexican beetle, Zygogramma bicolorata
P. under laboratory conditions,
2.4: To study the bionomics of Mexican beetle, Zygogramma bicolorata P.under
laboratory conditions.
2.1: To record the natural enemies of congress grass, Parthenium
hysterophorus L. with special reference to its management with Mexican
beetle, Zygogramma bicolorata Pallister.
Kumari et al. (2014) reported that the invasion of Parthenium
hysterophorus L. and its impact on agriculture fields in different cultivated crops in
Bilaspur. A total number of 28 species under 27 genera and 16 families was
distributed in three study sites (Koni, Sakri & Kota) of cultivated fields in Bilaspur
C.G. These study sites were located in different altitudinal zones responding
different conditions in the this study. The number of species per sites ranged from
13 to 24. In the Sakri, number of species was ranged from 17 to 27, and the relative
4
density of plant species ranged between 0.77 with Heteropogon contortus,
Solanum surratense, Vernonia cinneria and Leucas aspera and 22.92 (Parthenium
hysterophorus). In the Kota, number of species was ranged from 14 to 28, and the
relative density of plant species ranged between 0.85 including Ageratum
conyzoides, Heteropogon contortus, Triticum aestivum and 29.06 (Zea mays) and
30.91 (Parthenium hysterophorus). In the Agriculture field, number of species was
ranged from 15 to 28, and the relative density of plant species ranged between 0.58
(Leucas aspera) and 26.23 (Triticum aestivum). The above work gives information
about the weeds harmful to herbs, crops and medicinal plants. Parthenium weed
can suppress and crowd out other weed species, and could form a single dominant
population in the invasion area, causing serious threat to plant community
biological diversity.
Jayanth and Nagarkatti (1987) started the biological control of Parthenium
with the introduction of a hostspecific leaf-feeding beetle, Zygogramma bicolorata
Pallister from Mexico. It was introduced by the Indian Institute of Horticultural
Research (IIHR), Bangalore for the management of Parthenium. It became
abundant within three years after introduction, resulting in a significant reduction
in Parthenium density in local areas (Jayanth and Bali, 1994a; Jayanth and
Visalakshy, 1996). Since then, the beetle dispersed over an area of more than 9000
km2 (Gupta, 2008) and weed suppression was evident in many parts of the state
(Gupta et al., 2004).
Singh (1997) considered use of biological control agents and exploitation
of competitive plants or the most economic and practical way of managing
Parthenium. During last few years much emphasis has been given to control
Parthenium through various biological agents like insects, pathogens and
competitive plants. In past, attempts were made to review work on biological
control of Parthenium in context to India, Australia and global situations as
reported by Singh, 1989&1997, Sushilkumar 1993, Sushilkumar and Bhan 1995,
McFadyan 1992, Dhileepan and McFadyen, 1997, Evans 1997 and Dhileepan and
Senaratne (2009).
5
Shenhmar et al. (1998) studied on the release of Z. bicolorata near Phillaur,
Jalandhar district, Indian Punjab, for the biological control of
the Parthenium weed. The areas were surveyed during 1994-97, and on 4
September 1996 the beetle was observed on Parthenium weeds in Morinda and
Ropar districts. Adults of Z. bicolorata were observed on 40-day-old sunflower
plants in an isolated field near Nawanshahr district in May 1997. A total of 5
beetles/plant were observed over a 10-day period. Z. bicolorata feeding was
observed on the leaves of some Parthenium hybrid plants. Egg-laying was not
observed.
Visalakshy et al. (1998) experimented field releases of Z. bicolorata for
biological control trials against P. hysterophorus which resulted in successful
control of the weed in different parts of India. Adults underwent diapause in the
soil from October to May, emerging with the onset of the monsoon rains. A survey
was carried out to determine whether delay in rainfall could affect emergence of
diapause adults. It was found that a delay of rainfall for more than 45 days could
reduce the emergence of adults significantly. In such areas, new releases may have
to be carried out for effective control of the weed.
Srikanth et al. (1988) surveyed the natural enemies of congress weed
(Parthenium hysterophorus) in Karnataka, India, during February 1987 which
revealed that a large number of plants were attacked by Orthezia insignis. Nymphs
and adults occurred on all parts of the plant and black sooty mould was seen on
severely infested plants.
2.2: To study the e-surveillance of Parthenium and other associated weeds in
Kharif and Rabi season.
Char et al. (1975) reported the common tailed mealy bug Ferrisia virgata,
mites Tetranychus cucurbitaeand Tetranychus sp. (Puttaswamy et al., 1976, Rajulu
et al., 1976) aphid, Aphis fabae and mealy bug, Pseudococcussp on Parthenium.
(Rajulu et al., 1976)
6
Kumar et al. (1979) in a survey in Tamil Nadu at 104 places during
October 1975 to October 1979 recorded many insects, a mite and few diseases on
Parthenium. They further reported that the Cerembycid borer, Obereasp. was also
found to kill this weed significantly. Earias sp. used Parthenium as an alternate
host (Thontadarya and Hiremath, 1978).
Thangavelu (1980) and Srikant et al. (1988) reported severe attack of a bug
Leptocentrustaurusand a scale insect, Orthezia insignis in Mysore and Bangalore
respectively.
Shenhmar et al. (1998) carried out a survey of Zygogramma bicolorata on
Parthenium spp. in Indian Punjab and adjoining states. The Chrysomelid was
generally found in small numbers and its populations were unable to suppress the
weeds.
McClay et al. (1995) surveyed North America was from bases at
Monterrey and Cuernavaca, Mexico, and Temple, Texas. A total of 262
phytophagous arthropod species was collected on P. hysterophorous by various
methods including hand picking, dissection, rearing and sweeping; 144 of these
species were found to feed on the plant at some stage of their life cycle. The orders
represented most abundantly were Coleoptera (33.2%), Homoptera
(22.95), Lepidoptera (20.2%) and Hemiptera (18.3%). Two fungal
pathogens, Puccinia abrupta var. partheniicola and P. melampodii, were also
observed. An index of similarity was used to make pair wise comparisons between
the phytophagous arthropod communities on different plant taxa. These
comparisons showed that the fauna of P. hysterophorus was most similar to that of
ragweeds (Ambrosia spp.). Six insect species that were shown to be stenophagous
were shipped to Australia for further testing and possible field release.
Bennett (1977) studied the biology of P. hysterophorus and its
associated insects and pathogens together with the results of field surveys carried
out in Mexico and the USA. Insects recorded from P. hysterophorus in Mexico and
the USA as well as the West Indies and South America
7
Mc Fadyen (1979) conducted a preliminary survey of the natural enemies
of P. hysterophorus in Brazil and Argentina to determine if suitable insects were
available for the biological control of the plant in Australia, where it was a serious
rangeland weed. The insects found are listed and their host specificity and damage
caused is discussed.
Cock, M. J. W. (1981) had surveyed and assessed natural enemies of
Mikania spp. in the Neotropics. The evidence of an eriophyiid mite, Acalitus sp.,
the curculionid, Pseudoderelomus baridiiformis, a thrips, perhaps Liothrips
mikaniae, and a cassid, Omoplata marginata was noted. The feeding preferences
of L. mikaniae were studied in the laboratory at Curepe. Substantial adult feeding
occurred only on Mikania micrantha . But very minor feeding occurred on P.
hysterophorus and Piper marginatum. Oviposition occurred on M. micrantha and
larvae developed normally only on M. micrantha and M. vitifolia. L. mikaniae is
therefore, considered suitable for introduction to SE Asia. Tests were also made on
the flower feeding species, Apionluteirostre. The results suggested a narrow host
range, possibly restricted to M. micranthaand M. vitifolia.
Kumar et al.(1979) conducted a survey in Tamil Nadu from October 1975
to October 1976 on the natural enemies of the weed, larvae and adults of the stem-
boring scolytid, Hypothenemus eruditus (Westw.) caused widespread wilting of the
weed, leading to good natural control; however, this beetle is known to attack
several crops in different parts of the world. A cerambycid borer, Oberea sp. was
also found to kill the plant. The other natural enemies found
including Parasaissetia nigra (Nietn.), (Saissetia nigra), S. coffeae (Wlk.), Coccus
longulus (Dgl.), Ceroplastes sp., Ferrisia virgata (Ckll.) (Ferrisia
navirgata), Nipaecoccus viridis (Newst.) (Pseudococcus corymbatus Green, Icerya
seychellarum(Westw.), Aphis gossypii Glov., Oxyrhachis tarandus (F.), Telingana
campbelli Dist., Coccosterphus minutus (F.), Chrysocoris stollii (Wolff), Dolycoris
indicus Stal, Ptochusovulum Faust, Monolepta signata (Ol.), Neorthacris
simulans (Bol.) (Orthacris simulans), Tetranychus cinnabarinus (Boisd.) and
several diseases. Unidentified natural enemies included a cerambycid and a
8
dipteran stem-borer. Most of the natural enemies were known to attack crops;
hence, the weed may serve as an alternative food-plant for many of them.
Kulshretha and Kumar (2013) surveyed different areas of Agra region for
three consecutive years (2008, 2009 and 2010) to record per cent incidence by
Chrysomelid beetles in randomly selected areas of gajar-ghas growing plants.The
data was taken week wise and pooled on monthly basis.
Dhiman and Bhargava (2005) reported that the incidence was maximum
(87.09% and 76.19%) in August months at it was observed to start March months
of 2009 and2010.
2.3: To work out the feeding potential of Mexican beetle, Zygogramma
bicolorata P. under laboratory conditions.
Aguirre-Uribe and Corrales (1992) carried out a survey was of
the insects feeding on wild and cultivated guayule (Parthenium argentatum)
in Mexico during 1979-80. A total of 40 insects were found, with the following
being potentially important: 4 species from the Curculionid genus Smicronyx,
damaging seeds; Pityophthorus sp., damaging stems of 26% of wild plants; the
mirid Lygus mexicanus and Polymerus sp., attacking seeds and leaves; 4 species of
the Cicadellid genus Empoasca attacking seeds and leaves; and a species from the
lyonetiid genus Bucculatrix, which fed on buds and young leaves, affecting 52% of
plants. A total of 32 species which attacked the plants occasionally are also listed.
Gupta and Sood (2002) conducted a survey during August 2001 in 5
districts of Himachal Pradesh, India, to determine the ecology of Zygogramma
bicolorata, a potential biological control agent against parthenium weed. The
beetle was best established in the Kangra district, where an average 72.8% (43.5-
100%) of Parthenium were infested and the insect population per infested plant
was also high (mean 8.5, 1.3-18.3) with similar in Hamirpur district. The impact
of defoliation on plant growth was evident at Hamirpur and Kangra, where 89-
100% of the plants were infested and the population of damaging stages (larvae
and adults) was high (73.5 and 58.6%, respectively).
9
Sanghmitra and Basu (2004) noticed during the survey of insect and fungal
infestation in P. hysterophorus plants from July to September 2003, it was
observed that a large number of insects were feeding on P. hysterophorus leaves
and flowers. The percentage of damage was very high (up to 90%). The insect was
identified as Listronotus setosipennis. This is thought to be the first report of L.
setosipennis from India.
Aherkar et al., (2014) surveyed on the activity of Z. bicolorata in Akola
District of Maharashtra, India, indicated that grubs and adults were feeding on X.
strumarium were recorded at five different spots on top, middle and
bottom leaves of five plants at each location. The observed on the plant compared
to the Parthenium, indicating that X. strumarium was less preferred for egg laying.
An average of 1.6 eggs per plant was noticed egg laying mostly on old leaves. An
average of 4.4 grubs per leaf was found feeding on old leaves of X. stumarium and
adults were also seen feeding on the leaf, with an average of 7.4 adults per plant.
Sushillkumarand Bhan (1997b) studied the effect of defoliation of
Parthenium by the Mexican beetle and mechanical damage in terms of changes in
total phenol (TP) and carbohydrate content. Total phenol and carbohydrate content
when quantitated in relation to 30 and 50% of local damage of leaves by beetles
revealed that amount of phenols decreased by 4.03 and 4.95 fold at 30 and 50%
defoliation of parthenium, respectively.
Singh (1997) reported, three insects namely defoliating beetle, Z.
bicolorata P. (Coleoptera: Chrysomelidae), the flower feeding weevil Smicronyx
lutulentus Dietz (Coleoptera: Curculionidiae) and the stem boring moth Epiblema
strenuana (Walker) (Lepidoptera: Tortricidae) based on the success in Australia,
were imported in India from 1983 to 1985.
Sushilkumar and Varshney (2007) reported in Madhya Pradesh that heavily
infested Parthenium sites were replaced at many places by deliberate broadcasting
of seeds of Charota, Cassia tora during March- April.
McClay (1980) surveyed for three years in Monterrey (Mexico) and
recorded a total 159 species of phytophagous insects on Parthenium besides many
10
unidentified species. Based on this survey, about nine insect species were
introduced in Australia for biological control of Parthenium.
Javaid et al., (2006) during field surveys of different Parthenium growing
areas in the province of Punjab from 2003-05, we found severe attacks of a mealy
bug species in an undisturbed area in Punjab University, Quaid-e-Azam Campus
Lahore. The mealy bugs were found feeding on leaves, stems and flower heads
of Parthenium. Five other weed species namely Boerhavia diffusa, Achyranthes
aspera, Malvestrum tricuspidatum, Sidaspinosa and Xanthium strumarium were
attacked by the mealy bug.
Chakravarthy (2002) reported from Tumkur, Karnataka, India, during
August-November 2002 on the feeding behaviour of Zygogramma beetles
on Parthenium and sunflower.
Kulkarni and Kulkarni (2000) studied on P. hysterophorus plants in 20
locations in north Karnataka, India, for the presence of Z. bicolorata during August
1999. The densest population of beetles was observed in Dharwad (10.4
beetles/plant), followed by Bijapur (5.6 beetles/plant) and Raichur (3.2
beetles/plant).
Kumar and Bhan (1998) released a biological control agent, the
chrysomelid beetle, Zygogramma bicolorata to suppress Parthenium, Parthenium
hysterophorus using was released following host specificity tests in
Bangalore,India, in 1984. Adults were collected from Bangalore and released in
1991 at Vindhyanagar, Madhya Pradesh. Although few insects were observed three
years after the initial release in and around Vindhyanagar, a 1996 survey revealed
that Z. bicolorata has spread up to 28 km from the release site, which confirms the
dispersal and establishment of the bio-logical control agent in relation to ecological
factors and the role of Z. bicolorata in integrated parthenium management.
11
2.4: To study the bionomics of Mexican beetle, Zygogramma bicolorata
P.under laboratory conditions.
Omkar and Pandey (2008) worked on development and survival of
different stages of Z. bicolorata at constant temperatures (20º, 25º, 27º, 30º and
35ºC) and revealed that development was fastest with maximum surviving
individuals at 27°C. They concluded that 27ºC was the most suitable for mass
rearing of Z. bicolorata.
Dhiman and Bhargawa (2005) suggested Z. bicolorata Pallister
(Coleoptera: Chrysomelidae) as an important biocontrol agent of Partheniurn
weed. Male Z. bicolorata measured 5.20 to 7.12 mm with an average of 6.67 mm
and female 6.0 to 8.0 mm in length with an average of 7.36 mm. Female laid eggs
either singly or in groups, in an average 40 eggs on leaves, flower, stem and buds
of Parthenium plants. Hatching percentage was highest in April and July, there
were four larval stages of creamy white colour. Larval duration extended from 3-5
days for 1st instar, 3-3.5 days for 2nd instar, 2-3 days for 3rd instar and 4-8 days
for 4th instar, larvae and adult were voracious feeders for Parthenium weed. 4th
instar larvae after growth dropped down on the soil near food plant root for
pupation upto a depth of 10 crns. Pupation period normally lasted for 10 to 12
days. Maximum population of adult Z. bicolorata and larvae were recorded in July
to mid September. and May. However, during the year peak population of weed
was recorded in April, May and July to September and minimum in the month of
December and January. During winter in last week of November. most of the adult
prepare to hibernate and pupae proceed for diapause, overwintering in adult and
diapause in pupae last upto mid February. taking a duration of about 2.5 to 3
months in district Saharanpur and adjacent area. Thus, the beetle has been well
established in the locality and naturaly control the weed upto good extent.
McClay (1983) during surveys in Mexico found potential biological
control agents of the Neotropical annual P. hysterophorus , which had become a
serious problem in Australia following its accidental introduction there. The
delphacid Stobaeraconcinna (Stǻl) was found comparatively rare at sites in Nuevo
León, Tamaulipas and San Luis Potosıacute˜; it was not found on plants other
12
than P. hysterophorus. Laboratory studies on its biology showed that the eggs were
laid in the stems, there were 5 nymphal instars and development from egg to adult
lasted 30-56 days. It could only reproduce on P. hysterophorus and Ambrosia
confertiflora of the 11 species of Compositae tested. At high population densities,
it caused yellowing of the leaves and spindly growth.
Bennett and McClay (1979) carried out surveys in the southern USA
and Mexico in 1976 for natural enemies of the noxious weed P. hysterophorus to
assess the possibility of its biological control in Australia, a more extensive
programme of research on those natural enemies found in Mexico was begun in
1978. It is based in Monterrey, Nuevo Leon. The arthropods found in Mexico and
thought sufficiently promising for further study are listed, as are species of
Compositae at present being used in initial (mainly multiple-choice) tests on food-
plant ranges. The most promising insect appears to be the weevil Smicronyx
lutulentus Dietz, adults of which were very common on P. hysterophorus in Nuevo
Leon and Tamaulipas up to November 1978, being found on the stems, finer
branches, flowers and buds. The related species P. confertum is the only other
plant on which the weevil has so far been found. The eggs are laid in the young
flower heads, and the larvae feed in the seeds. They pupate in the soil. Other
promising arthropods include a species of Ophraella that is possibly O. sexvittata
(Lec.), Aceria parthenii Keifer (Eriophyes parthenii) and an unidentified red aphid.
Henderson and Albrecht (1988) suggested that females were more tolerant
of extremes of temperatures than males, resulting in female-biased sex ratios.
However, percentage life span spent by immature stages of Z. bicolorata was
similar across all five temperatures (20º, 25º, 27º, 30º and 35ºC), indicating an
isomorphic development rate (Jarosik et al., 2002; Omkar et al., 2008). Decrease in
the incubation period of Z. bicolorata with increase in temperature probably results
from accelerated embryogenesis, causing early hatching of neonates (Ivanovic and
Nenadovic, 1999).
Pandey et al (2001) reported male’s length as 6.00 mm and female 6.80
mm. Female lays eggs either singly or in groups ranging from 2 to 80 eggs on
13
leaves flower, stem and buds of Parthenium plants with an average of 40
eggs.Above said authors mentioned 60-65 eggs per day while Jayanth and Bali
(1993 a) recorded 45 eggs per day. Eggs are yellow or orange in colour which
hatch in 6-7 days in July and August and in 8-10 days in October and March with
an average of 7 days.This variation in egg number laid per day may be due to
climatic factors or due to single or multi time copulation. Maximum number of
damaged eggs in natural condition was recorded in June, perhaps due to
dehydration. Hatching percentage is highest in the month of April and July. A
group of 5 male and 5 female can lay 1500 eggs or more in 15 days. This indicates
the magnitude of reproductive power, which is a positive point for the control of
the weed.
Overwintering in adult and diapause in pupae lasted upto mid-February for
2.5 to 3 months in district Saharanpur and adjacent area. Few adults and larvae
have been observed upto December feeding on Parthenium,This duration is
variable according to ecoclimatic zones of the country. Mahadevappa (1997)
recorded 6-8 months period of summers and winter in Dharwad (Karnataka),
Visalakshy et al. (1998) recorded diapause from October to May and the
adult emergence with the onset of monsoon rains.The beetle is well established in
this locality and naturally controls the weed upto good extent. However, there is a
need of mass multiplication of the beetle so that these may be available to the
farmers and environmentalis at low cost for release in field to eradicate weed
completely.
Many workers in India representing different climatological conditions
have studied the biology of the beetle and reported variation in the various
biological parameters viz.,egg period (5 days), grub period (11-13 days), pupal
period (10-12 days), egg to adul temergence (27-29 days), eggs per female (1695-
3360), per cent hatching (30-53), preoviposition period (10-70 days), sex ratio
(female %) 1:0.40, male longevity (122-271days), female longevity (109-198
days), oviposition period (89-138 days) and postoviposition period (1-21 days)
(Jayanth and Bali, 1992).
14
Aherkaret al. (1992) from Prabhani reported egg period (2-6 days), grub
period (15-20 days), pupal period (10-12 days), egg to adult emergence (27-38
days), eggs per female (551), male longevity (30 days), female longevity (38
days)).
The whole life cycle took about 6-8 weeks and there may be up to 4
generations/year, depending on rainfall and food availability (McFadyen, 1992). In
autumn due to shorter days and cooler temperatures, adult beetles diapause in the
soil. The dipausing adults emerge in spring in response to rainfall, increased
temperature and longer days. Adult beetles can live up to 2 years and usually spend
around 6 months diapausing in the soil during autumn and winter (McFadyen,
1993).
Gautam et al. (2006) studied the biology of Z bicolorata adults collected
from Delhi (semi-tropical), Jammu (Jammu and Kashmir; temperate), Jabalpur
(Madhya Pradesh; semi-tropical) and Haridwar (Uttaranchal; foothills), India,
under laboratory conditions (26 ± 1°C and 60±5% relative humidity). The pre-
oviposition period lasted for 5-10, 7-10, 3-7 and 7-8 days for the Delhi, Jammu,
Jabalpur and Haridwar populations, respectively. The incubation period was 3-5
days in all populations. The larval period was longest (16-20 days) for the Jammu
population. The pupal period required 7-11 days for theDelhi population, and 6-10
days for the other populations. The total developmental period lasted for about 19-
28, 22-30, 18-27 and 18-26 days for the Delhi, Jammu, Jabalpur and Haridwar
populations, respectively. Fecundity (903 eggs per female), egg hatchability
(75.60%), and female/male ratio (1.63) were greatest for the Jammu population.
Adult longevity for this population (65.8 days for male and 62.4 days for the
female) was only slightly inferior to that recorded for the Jabalpur population (74.6
and 66.7 days, respectively). The peak ovulation period occurred on the second
week after emergence except in the Jabalpur population (fourth week after
emergence). Larval survival was highest for the Delhi population (53.35%),
followed by the Jabalpur (46.67%), Jammu (40.07%) and Haridwar(33.36%)
populations.
15
CHAPTER III
MATERIAL AND METHODS
This chapter deals with the material and methods used under different
objectives of the experiment entitled, “E-surveillance and management of
congress grass, Parthenium hysterophorus L. through Mexican beetle,
Zygogramma bicolorata P. and record of natural enemies of few commonly
associated weeds” was conducted at the Department of Entomology, IGKV,
Raipur, during 2016 & 2017. The material and methods are presented here with
the following sub headings:
3.1: To record the natural enemies of congress grass, Parthenium hysterophorus L.
with special reference to its management with Mexican beetle, Zygogramma
bicolorata Pallister,
3.2: To study the e-surveillance of parthenium and other associated weeds in
Kharif and Rabi season,
3.3: To work out the feeding potential of Mexican beetle, Zygogramma bicolorata
P. under laboratory conditions,
3.4: To study the bionomics of Mexican beetle, Zygogramma bicolorata P.under
laboratory conditions.
3.1: To record the natural enemies of congress grass, Parthenium
hysterophorus L. with special reference to its management with Mexican
beetle, Zygogramma bicolorata Pallister
3.1.1: Location of study:
Population of Mexican beetle, Z. bicolorata was recorded at three locations
of IGKV campus namely research field area of agricultural and horticultural crops,
agro-forestry field area and road side along NH-6 from administrative building to
College of Agriculture, Raipur.
16
Fig. 3.1: Recording observations on insect pest of Parthenium at IGKV campus, Raipur, C.G.
Fig. 3.2: Recording observations on insect pest of Parthenium at Arang block, Raipur, C.G.
17
3.1.2: Geographical situation& climate:
Raipur is situated in the central part of the Chhattisgarh state and lies at
21.16 N latitude and 81.36 E longitude at an altitude of 298 metres above the
mean sea level.Raipur district comes under dry sub-humid agro-climatic region.
3.1.3: Details of study:
Ten plants from each of these three locations were selected randomly and
the number of eggs, grubs and adult beetles were recorded throughout the study
period in both years. Other insect pests associated with parthenium were also
recorded along with their numbers.
3.2: To study the e-surveillance of parthenium and other associated weeds in
Kharif and Rabi season
3.2.1: Location of study:
The e-surveillance programme of parthenium and other associated weeds
was conducted at four different Blocks (Arang, Dharsiwa, Tilda and Abhanpur) of
Raipur district in Chhattisgarh. The study was conducted at the prone areas of
different villages in Raipur districts. Five villages from each block were identified
and five respondents from each village were selected for the study during kharif-
rabi cultivation in the year 2016 and 2017.
3.2.2: Geographical situation& climate
Raipur is situated in the central part of the Chhattisgarh state and lies at
21.16 N latitude and 81.36E longitude at an altitude of 298 metres above the
mean sea level.
Arang lies at N-21o 11’41.46”, E-81
o 58’11.44”,
Dharsiwa- N-21o 24’29.46”, E-81
o 40’19.16”,
Tilda- N-21o 33’04.88”, E-81
o 47’51.72” and
Abhanpur- N-21o 03’14.98”, E-81
o 45’04.87”
with dry sub-humid agro-climatic conditions.
18
Table-3.2: The e-surveillance programme conducted through GPS machine at five
villages of four each block of Raipur District
S.No
.
Block/village
name
Latitude (N) Longitude (E)
Degree
(0)
Minute
(')
Second
(")
Degree
(0)
Minute
(')
Second
(")
A Arang N 210 11’ 41” E 81
0 58’ 11”
1 Palaud N 210 10’ 59” E 81
0 50’ 60”
2 Parshada N 210 11’ 45” E 81
0 49’ 17”
3 Rico N 210 11’ 46” E 81
0 47’ 39”
4 Umariya N 210 13’ 17” E 81
0 49’ 54”
5 Sendh N 210 11’ 52” E 81
0 48’ 13”
B Dharsiwa N 210 24’ 29” E 81
0 40’ 19”
1 Serikheri N 210 14’ 38” E 81
0 44’ 21”
2 Jora N 210 14’ 31” E 81
0 42’ 40”
3 Temri N 210 12’ 12” E 81
0 42’ 23”
4 Dharampura N 210 12’ 54” E 81
0 42’ 56”
5 Banrasi N 210 11’ 29” E 81
0 43’ 18”
C Tilda N 210 33’ 04” E 81
0 47’ 51”
1 Neora N 210 33’ 46” E 81
0 48’ 42”
2 Dondekala N 210 20’ 24” E 81
0 45’ 42”
3 Murra N 210 27’ 41” E 81
0 38’ 76”
4 Tulsi N 210 31’ 55” E 81
0 48’ 33”
5 Dondekhurd N 210 19’ 29” E 81
0 45’ 59”
D Abhanpur N 210 03’ 14” E 81
0 45’ 04”
1 Rakhi N 210 01’ 42” E 81
0 39’ 18”
2 Nardaha N 210 30’ 31” E 81
0 76’ 22”
3 Tekari N 210 05’ 37” E 81
0 39’ 51”
4 Rakhi-2 N 210 01’ 48” E 81
0 39’ 53”
5 Kurud N 210 18’ 74” E 81
0 70’ 31”
19
3.2.3: Selection of villages
The following five villages were selected from each block as mentioned
below:
i. Arang block: Palaud, Parshada, Rico, Umariya and Sendh,
ii. Dharsiwa block: Serikheri, Jora, Temri, Dharampura and Banrasi,
iii. Tilda block: Neora, Dondekala, Murra, Tulsi and Dondekhurd,
iv. Abhanpur block: Rakhi, Nardaha, Tekari, Rakhi-2 and Kurud.
In each village, five respondents were selected randomly in potential growing
area during kharif-rabi cultivation in the year of 2016 and 2017.
3.2.4: Details of study:
For this investigation, the observations of weeds were recorded though GPS
machine on the basis of visual/magnifying glass from upland, midland and lowland
in one sqm at five locations i.e. five farmers from each selected villages during
Kharif and Rabi season. Parthenium and different associated weeds like annual/
perennial were observed to find out the population of insect pests associated at
different critical plant stages.
3.3: To work out the feeding potential of Mexican beetle, Zygogramma
bicolorata P. under laboratory conditions
3.3.1: Location of study
The feeding potential of Mexican beetle, Zygogramma bicolorata P. was
conducted in the Bio-control laboratory, Department of Entomology, IGKV,
Raipur, Chhattisgarh.
3.3.2: Experimental details
3.3.2.1: Feeding potential of Mexican beetle, Z. bicolorata P.
The Mexican beetles and leaves of Parthenium food were collected from
the IGKV fields and maintained in the Bio-control laboratory and used for testing
the feeding potential at different growth stages of Parthenium. For this, experiment
was set up under completely randomized design (CRD) comprising of three
different age groups of Parthenium plants i.e. early stage (Av.19.33cm and Av.
20
7.33 leaves), pre-reproductive (non-flowering, Av. 34.66cm and Av. 18.66 leaves)
and reproductive (flowering, Av. 54.70cm and Av. 32.33 leaves) and replicated
thrice. On each potted plant four treatments comprising of beetles of 2, 3, 4 and 5
pairs were released. Observations were recorded on alternate days for the number
of insects established and time taken (number of days) for complete defoliation of
plants at each stage. The data obtained from the experiment was transformed
accordingly and analyzed statistically.
3.3.2.2: Food consumption by adult and grubs of Mexican beetle, Z. bicolorata
P.
For determining the food consumption of Mexican beetle, Z. bicolorata P.
experiment was conducted in the Bio-control laboratory, Department of
Entomology, IGKV, Raipur, Chhattisgarh at 25-30°C and 60 ± 5% RH,. Newly
hatched different instars of grubs were taken for food utilization study. Grubs from
different instars maintained separately as stock culture were used for the study. The
newly emerged different stages of beetles i.e. first, second, third, fourth instars and
adults were released on to previously weighed leaf of host plant in different petri
dishes (10 cm. dia.) provided with moist filter paper and allowed to food for 24
hrs. The experiment was replicated thrice. At the end of each day of the
experiment, the filter paper was cleaned with a fine camel hair brush to collect the
excrement. After consumption of host plant leaves were measured on weight basis.
The amount of food consumption was estimated by the formula given
below:-
Food consumption = total food given to grubs & adult (wt) – Left over food by grubs & adult (wt)
21
Fig. 3.3.1: Mass multiplication of Mexican beetle, Z. bicolorata, reared in cut plastic tanks covered with nylon net using low cost technology
Fig. 3.3.2: Mass multiplication of Mexican beetle, Z. bicolorata in plastic basins covered with plastic net under laboratory conditions
22
Fig. 3.3.4: Recording observations on the feeding efficiency of Z. bicolorata at different stage of Parthenium plants
Fig. 3.3.3: Experiment conducted for testing complete defoliation of different ages of Parthenium plants by releasing different number of paired beetles, Z. bicolorata
23
Fig. 3.3.5: Eggs of Z. bicolorata on leaf of Parthenium leaves.
Fig. 3.3.6: Food consumption by grubs and adults of Mexican beetle, Z. bicolorata P. under laboratory condition.
24
3.4: To study the bionomics of Mexican beetle, Z. bicolorata P.under
laboratoryconditions
3.4.1: Location of study:
The bionomics of the Mexican beetle, Z. bicolorata P. was studied under
laboratory conditions in the Bio-control laboratory, Department of Entomology,
IGKV, Raipur, Chhattisgarh.
3.4.2: Details of study:
In this experiment fresh leaves of parthenium were provided in petridishes
on which single pair of newly emerged Z. bicolorata beetles was released. The
observations were recorded on fecundity, incubation period and duration of larval
(grub) instars, pupal and longevity of male and female beetles.
3.5: Statistical Analysis
The data obtained under various experiments were tabulated and subjected
to statistical analysis as per requirement. Data in percentage were subjected to
angular transformation whereas numerical data were transformed to square root
transformation before subjected to statistical analysis (Gomez and Gomez, 2010).
The data recorded on all the traits related to bionomics of Mexican beetle
contributing characters under all the season were statistically analyzed as follows.
Mean
Mean is the value of observation of genotypes of a series. It represents the
standard average value over fluctuations in the environment. Mean was calculated
by the following formula:
X̅ = Σ Xi/n
Where, Σ Xi = summation of all the observations
n = total number of observations
Range
Range is the difference between the highest and the lowest value of a series
of observations and thus provides the information about the extent of variability
present in the treatments.
25
Range = Highest value – Lowest value
Analysis of variance
The mean data of each replication was used to analysis of variance using
CRD design. The model for experimental design used i.e., Completely
Randomized Design can be expressed as follows: Yi = µ + vi + ei
Where,
µ = General mean
ti = Effect of ith
treatments
ei = Error component
The skeleton of the analysis of variance are as follows:
Table: ANOVA table for CRBD design
Sources of
variation
Degree of
freedom
Sum of
squares
Mean sum
of squares
Computed F Tabular F
5% 1%
Treatments t-1 SSt MSSt Fcal
Fd.f.
(e, v)
Fd.f.
(e, v) Error t(r-1) SSe MSSe
The following formulae were used for the estimation of standard error,
critical difference and coefficient of variance:
a. SEm±= 𝐸𝑀𝑆
𝑟
b. C. D. = 2𝐸𝑀𝑆
𝑟× t at error d. f. (5%)
c. C. V. % = EMS
GM × 100
Where,
r = Number of replications, d.f. = Degree of freedom
v = Number of treatment, S.S. = Sum of square
C.D. = Critical difference, C.V. = Coefficient of variance
M.S.S = Mean sum of squares, E.M.S. = Error mean square
S.Em± = Standard error of mean, G.M. = Grand mean
26
Fig. 3.4.1: Recording observations on bionomics of Z. bicolorata in Bio-control laboratory, Department of Entomology, CoA, IGKV.
Fig. 3.4.2: Recording observations on bionomics of Z. bicolorata under trinocular digital microscope in Bio-control laboratory, Department of Entomology, CoA, IGKV.
27
Fig. 3.4.3: Eggs of Mexican beetle, Z. bicolorata Fig. 3.4.4: Grub of Z. bicolorata under microscopic measurement.
Fig. 3.4.5: Grub of Mexican beetle, Z. bicolorata Fig. 3.4.6: Pupa of Mexican beetle, Z. bicolorata
Fig. 3.4.7: Adult of Mexican beetle, Z. bicolorata Fig. 3.4.8: Male and female of Mexican beetle, Z. bicolorata
28
CHAPTER IV
RESULTS AND DISCUSSION
This chapter deals with the result and discussions obtained under different
objectives of the experiment entitled, “E-surveillance and management of
congress grass, Parthenium hysterophorus L. through Mexican beetle,
Zygogramma bicolorata P. and record of natural enemies of few commonly
associated weeds” conducted at the Department of Entomology, IGKV, Raipur
during 2016 & 2017. The result and discussions are presented here with under the
following sub headings:
4.1: To record the natural enemies of congress grass, Parthenium hysterophorus L.
with special reference to its management with Mexican beetle, Zygogramma
bicolorata Pallister,
4.2: To study the e-surveillance of Parthenium and other associated weeds in
Kharif and Rabi season,
4.3: To work out the feeding potential of Mexican beetle, Zygogramma bicolorata
P. under laboratory conditions,
4.4: To study the bionomics of Mexican beetle, Zygogramma bicolorata P.under
laboratory conditions.
4.1: To record the natural enemies of congress grass, Parthenium
hysterophorus L. with special reference to its management with Mexican
beetle, Zygogramma bicolorata Pallister
Population of Mexican beetle, Z. bicolorata was recorded at three locations
of IGKV campus namely research field area of agricultural and horticultural crops,
agro-forestry field area and road side along NH-6 from administrative building to
College of Agriculture, Raipur. Observations were recorded on the number of
adults, grubs and other insect pests associated with Parthenium at three selected
locations on ten randomly selected plants throughout the study period are presented
in table- 4.1aa, 4.1ab, 4.1ac, 4.1ba, 4.1bb, 4.1bc, 4.1ca, 4.1cb & 4.1cc and fig.-
4.1aa, 4.1ab, 4.1ac, 4.1ad, 4.1ba, 4.1bb, 4.1bc, 4.1bd, 4.1ca, 4.1cb, 4.1cc & 4.1cd
follows:
29
4.1.1: Agro-forestry field area
In the survey of agro-forestry field area, the average population of
Mexican beetle (egg, grubs and adults) on ten randomly selected plants in agro-
forestry field area ranged from (0.00 to 1.50, 0.00 to 0.30 and 0.00 to 0.50),
respectively. The highest number of eggs (1.50/plant) of Mexican beetle was
observed during July followed by August i.e. (0.40/plant) while grubs (0.30/plant)
and adults (0.50/ plant) were recorded in August followed by (0.20/plant) and
(0.33/ plant) in July respectively.
As far as other insect pests associated with Parthenium was concerned
maximum population of ants (2.60/plant) was recorded in December followed by
aphids (2.50/plant) in January. Semilooper and Canthocona bugs with 0.01/plant
on January-May, March and July, respectively during 2016.
The overall months average of Mexican beetle, Z. bicolorata P. (egg, grubs
and adults) population was noticed as 0.16, 0.04 and 0.07/plant, respectively while
average of other insect pest associated with Parthenium was observed to be
maximum (1.17/ten plants) in aphids followed by ants (1.02/ten plants) and
minimum in Canthocona bugs ( 0.02/plant) during 2016.
In second year i.e. in 2017 the average population of Mexican beetle (egg,
grubs and adults) on ten plants in agro-forestry area ranged from (0.00 to 0.95,
0.00 to 0.20 and 0.00 to 0.30), respectively. Maximum eggs (0.95/plant) of
Mexican beetle was observed in July followed by August (0.30/plant), the grubs
(0.20/plant) and adults (0.30/plant) was observed maximum in August and
minimum (0.10/plant) and (0.23/plant) in July, respectively. Whereas, other insect
pest associated with Parthenium ranged from 0.00 to 2.60/plant. The highest
population of ants (2.60/plant) was recorded in December followed by (1.60/ten
plants) in March and lowest (0.01/plant) in semilooper in March, spider and
Canthocona bug in July. The overall months average of Mexican beetle (egg, grubs
and adults) population was observed as 0.10, 0.03 and 0.04/plant, respectively
while average of other insect pests associated with Parthenium was observed to be
maximum (0.87/plant) in ants followed by aphids (0.71/plant) and minimum in
Canthocona bugs and cow bugs (0.02/plant).
30
The pooled analysis of two years data of Mexican beetle (egg, grubs and
adults) on ten plants in agro-forestry area ranged from (0.00 to 1.23, 0.00 to 0.25
and 0.00 to 0.40), respectively. The highest number of eggs (1.23/plant) of
Mexican beetle was observed in July followed by August i.e. 0.35/plant while
grubs (0.25/plant) and adults (0.40/plant) was exhibited maximum in August
followed by (0.15/plant) and (0.28/plant) in July, respectively.
As far as, other insect pests associated with Parthenium was concerned it
ranged from 0.00 to 2.60/plant. Maximum population of ants (2.60/plant) was
recorded in December followed by aphids (2.50/plant) in December and January.
Whereas minimum in semilooper in March and Canthocona bugs in July
i.e.0.01/plant, respectively during 2016 and 2017
The overall pooled data of two years depicted the mean population of
Mexican beetle (egg, grubs and adults) as 0.13, 0.03 and 0.06/ plant, respectively
while other insect pest associated with Parthenium was observed maximum (0.94/
plant) in aphids and ants, respectively followed by mealy bugs (0.45/plant) and
minimum in Canthocona bug (0.02/plant)
4.1.2: Cropped field area
The average population of Mexican beetle (egg, grubs and adults) on ten
plants in cropped field area ranged from (0.00 to 2.90, 0.00 to 2.30 and 0.00 to
2.30), respectively. The highest number of eggs (2.90/plant) of Mexican beetle was
observed during of August the followed by July i.e. 2.50/plant while grubs
(2.30/plant) and adults (0.80/plant) was recorded maximum in August and
September months followed by (2.20/plants) and (0.60/plants) during July and
October, respectively.
Other insect pests associated with Parthenium ranged from 0.00 to
6.20/plant. Maximum population of aphids (6.20/plant) was recorded in October
followed by (6.10/plant) in September and minimum of semilooper in March,
Canthocona bugs in July, ladybird beetle in June, August and Spittle bug in August
i.e. 0.01/plant, respectively during 2016.
The overall months average of Mexican beetle (egg, grubs and adults)
population was found to be 0.61, 0.48 and 0.19/plant, respectively while average
of other insect pests associated with Parthenium was observed maximum
31
(2.03/plant) of ants followed by aphids (1.88/plant) and minimum of Canthocona
bug ( 0.12/plant) during 2016.
In the second year, average population of Mexican beetle (egg, grubs and
adults) on ten plants in cropped field area ranged from (0.00 to 1.90, 0.00 to 1.30
and 0.00 to 0.80), respectively. Maximum eggs (1.90/plant) of Mexican beetle was
observed in August followed by September (1.20/plant), grubs (1.30/plant) and
adults (0.80/plant) was observed maximum in August and September months and
minimum (0.50/plant) and (0.33/plant) in October and July, respectively. In case of
other insect pest associated with Parthenium was concerned it ranged from 0.00 to
4.10/plant. The highest population of aphids (4.10/plant) was recorded in
September and lowest (0.01/plant) in leaf miner in March, Spittlle bugs in August,
lady bird beetle in June, July, August and Canthocona bugs in July.
The overall months of average Mexican beetle (egg, grubs and adults)
population was observed as 0.43, 0.30 and 0.19/plant, respectively while other
insect pest associated with Parthenium showed maximum (1.45/plant) in ants
followed by aphids (1.22/plant) and minimum in semilooper ( 0.14/plant).
The pooled analysis of two years data of Mexican beetle, Z. bicolorata P.
(egg, grubs and adults) on ten plants in cropped field area ranged from (0.00 to
2.40, 0.00 to 1.80 and 0.00 to 0.80), respectively. The highest number of eggs
(2.40/plant) of Z. bicolorata was observed in August followed by July i.e.
2.00/plant while grubs (1.80/plant) and adults (0.80/plant) was exhibited maximum
on August and September followed by (1.70/plant ) and (0.60/plant) in July and
October, respectively.
Other insect pests associated with Parthenium ranged from 0.00 to
4.70/plant, in which maximum population of aphids (4.70/plant) was recorded in
October followed by (3.00/plant) in November and minimum number of spiders,
lady bird beetles and Canthocona bugs of 0.01 in March, July, July, August and
July, respectively.
The overall pooled data of two years, mean population of Mexican beetle
(egg, grubs and adults) was recorded as 0.52, 0.39 and 0.19/plant, respectively
while other insect pest associated with Parthenium was observed to be maximum
32
(1.74/plant) of ants followed aphids (1.55/plant) and minimum in Canthocona bugs
(0.09/plant).
4.1.3: Road side area
The average population of Z. bicolorata (egg, grubs and adults) on ten plants in
road side area ranged from (0.00 to 7.40, 0.00 to 5.30 and 0.00 to 8.50),
respectively. The highest eggs (7.40/plant) of Mexican beetle was observed in
August followed by July i.e. 6.50/plant while grubs (5.30/plant) and adults
(8.50/plant) was exhibited maximum in August followed by (0.20/plant) and
(1.00/plant) in July and September, respectively. Other insect pest associated with
Parthenium ranged from 0.00 to 2.80/plant. Maximum population of mealy bugs
(2.80/plant) was recorded in September followed by (1.80/plant) in October and
minimum population of semilooper was noticed in March and Canthocona bugs
was observed in July as 0.01/plant, respectively during 2016.
The overall months of average of Mexican beetle (egg, grubs and adults)
population was recorded as 1.84, 0.46 and 0.90/plant, respectively while other
insect pest associated with Parthenium observed was maximum (0.98/plant) of
mealy bugs followed by ants (0.70/plant) and minimum of Canthocona bugs
(0.02/plant) during 2016.
In second year, average population of Mexican beetle (egg, grubs and
adults) on ten plants in road side area ranged from (0.00 to 5.70, 0.00 to 4.30 and
0.00 to 7.50), respectively. Maximum eggs (5.70/plant) of Mexican beetle was
observed in August followed by September (5.40/plant), the grubs (4.30/plant) and
adults (7.50/plant) was observed maximum in August and minimum (0.20/plant)
and (0.33/plant) on July, respectively. Other insect pest associated with Parthenium
ranged from 0.00 to 2.80/plant. The highest population of mealy bugs (2.80/plant)
was recorded in September and lowest (0.01/plant) of semilooper in March and
Canthocona bugs in July.
The overall mean population of Mexican beetle (egg, grubs and adults)
population was observed to be of 1.43, 0.38 and 0.82/plant, respectively while
other insect pest associated with Parthenium was observed as maximum
(0.94/plant) of mealy bugs followed by ants (0.70/plant) and minimum of
Canthocona bugs (0.02/plant).
33
The pooled analysis of two years data of Mexican beetle (egg, grubs and
adults) on ten plants in road side area ranged from (0.00 to 2.40, 0.00 to 1.80 and
0.00 to 0.80), respectively. The highest eggs (2.40/plant) of Mexican beetle was
observed on August followed by July i.e. 2.00/plant while grubs (1.80/plant) and
adults (0.80/plant) was exhibited maximum in August and September followed by
(1.70/plant) and (0.60/plant) in July and October, respectively. As far as other
insect pests associated with Parthenium was concerned; it ranged from 0.00 to
5.10/plants. The maximum population of aphids (4.70/plant) was recorded in
September followed by (4.70/plant) in October and minimum in case of semilooper
during March, lady bird beetle from June to August and Canthocona bugs in July
i.e. 0.01/plant, respectively during 2016 and 2017.
The overall pooled data of two years, showed that the mean population of
Mexican beetle (egg, grubs and adults) was recorded to be 0.48, 0.36 and
0.17/plant, respectively while other insect pests associated with Parthenium was
observed to be maximum (1.62/plant) in ants followed by aphids (1.43/plant) and
minimum in spittle bugs (0.14/plant).
Gupta and Sood (2002) who conducted survey in August 2001 in 5 districts
of Himachal Pradesh, India, to determine the ecology of Zygogramma bicolorata, a
potential biological control agent against parthenium weed also reported mean
maximum infestation in the month of August with 8.50/plant, which is in
agreement with the present finding.
Similarly Dhiman and Bhargava (2005) also reported that the incidence of
Z.bicororata was maximum (87.09% and 76.19%) in August months which is in
accordance with the present studies.
34
4.1
aa:
Mea
n d
ata
of
the
ass
oci
ate
d i
nse
cts
wit
h c
on
gre
ss g
rass
, P
. h
yste
roph
oru
s re
cord
ed u
nd
er a
gro
-fore
stry
fie
ld a
rea o
f IG
KV
cam
pu
s, R
aip
ur
du
rin
g 2
016
S.
No.
Bio
-ag
ents
/Mo
nth
Agro
fore
stry
Ja
n
Feb
M
ar
Ap
r M
ay
Ju
n
Ju
l A
ug
Sep
O
ct
No
v
Dec
M
ean
1
Zy
go
gra
mm
a (
Eg
g)
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
1.5
0
0.4
0
0.0
0
0.0
0
0.0
0
0.0
0
0.1
6
2
Zy
go
gra
mm
a (
Gru
bs)
0
.00
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.2
0
0.3
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
4
3
Zy
go
gra
mm
a A
du
lts
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.3
3
0.5
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
7
4
Mea
ly b
ug
0
.70
0.4
0
0.9
0
0.7
0
0.0
0
0.7
0
0.2
0
0.7
0
0.7
0
0.8
0
0.7
0
0.7
0
0.6
0
5
Ap
hid
2
.50
1.3
0
1.5
0
0.5
0
0.0
0
0.0
0
0.0
0
1.5
0
1.5
0
1.2
0
1.5
0
2.5
0
1.1
7
6
An
t (s
mal
l/la
rge)
0
.60
1.5
0
1.6
0
0.9
0
0.8
0
0.6
0
1.2
0
0.6
0
0.6
0
0.6
0
0.6
0
2.6
0
1.0
2
7
Sp
ital
bu
g
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
8
Lea
fhop
per
0
.00
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
1.0
1
1.0
3
0.0
0
0.0
0
0.0
0
0.0
0
0.1
7
9
Lea
f m
iner
0
.50
0.6
0
0.7
0
0.8
0
0.7
0
0.4
0
0.0
0
0.0
0
0.4
0
0.2
0
0.3
0
0.7
0
0.4
4
10
Sem
ilo
op
er
0.2
0
0.1
0
0.0
1
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.1
0
0.0
0
0.2
0
0.3
0
0.0
8
11
Lad
y b
ird
bee
tle
0.1
0
0.2
0
0.3
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.3
0
0.0
8
12
Red
uvid
bu
g
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
13
Sp
ider
0
.40
0.5
0
0.6
0
0.4
0
0.3
9
0.3
0
1.0
1
0.4
0
0.4
0
0.4
0
0.4
0
0.4
0
0.4
7
14
Can
tho
con
a bu
g
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
1
0.0
0
0.0
0
0.0
0
0.0
0
0.1
9
0.0
2
15
Co
w b
ug
1
.30
1.2
0
1.3
0
0.2
0
0.0
0
0.0
0
0.0
0
0.0
0
0.3
0
0.2
0
0.3
2
0.3
0
0.4
3
To
tal
6.4
0
5.8
1
6.9
3
3.5
0
1.9
0
2.0
0
5.4
8
5.6
3
4.1
0
3.5
0
4.1
3
8.1
1
4.7
9
*T
he
dat
a sh
ow
s A
v. o
f fo
rtnig
htl
y i
nte
rval
35
4.1
ab
: M
ean
data
of
the
ass
oci
ate
d i
nse
cts
wit
h c
on
gre
ss g
rass
rec
ord
ed
un
der
fie
ld c
rop
ped
are
a o
f IG
KV
ca
mp
us,
Raip
ur
du
rin
g
2016
S.
No.
Bio
-ag
ents
/Mo
nth
Fie
ld c
rop
ped
are
a
Ja
n
Feb
M
ar
Ap
r M
ay
Ju
n
Ju
l A
ug
Sep
O
ct
No
v
Dec
M
ean
1
Zy
go
gra
mm
a (
Eg
g)
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
2.5
0
2.9
0
1.4
0
0.5
0
0.0
0
0.0
0
0.6
1
2
Zy
go
gra
mm
a (
Gru
bs)
0
.00
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
2.2
0
2.3
0
0.6
0
0.5
0
0.2
0
0.0
0
0.4
8
3
Zy
go
gra
mm
a A
du
lts
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.3
3
0.5
0
0.8
0
0.6
0
0.0
0
0.0
0
0.1
9
4
Mea
ly b
ug
0
.70
0.4
0
0.9
0
0.7
0
0.0
0
0.7
0
0.2
0
0.7
0
0.0
0
0.8
0
0.7
0
0.7
0
0.5
4
5
Ap
hid
1
.50
0.3
0
0.5
0
0.5
0
0.0
0
0.0
0
0.0
0
1.5
0
6.1
0
6.2
0
3.5
0
2.5
0
1.8
8
6
An
t (s
mal
l/la
rge)
1
.60
2.5
0
2.6
0
1.9
0
1.8
0
1.6
0
2.2
0
2.6
0
1.8
0
1.6
0
1.6
0
2.6
0
2.0
3
7
Sp
ital
bu
g
0.1
0
0.0
9
0.0
8
0.0
4
0.4
9
0.3
4
0.3
0
0.0
1
0.0
0
0.0
0
0.0
0
0.0
0
0.1
2
8
Lea
fhop
per
0
.00
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
9
Lea
f m
iner
0
.70
0.6
0
1.7
2
0.8
2
0.7
5
0.8
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.4
5
10
Sem
ilo
op
er
0.8
0
0.9
0
0.0
1
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.1
4
11
Lad
y b
ird
bee
tle
1.1
0
1.2
0
1.3
0
0.2
0
0.1
0
0.0
1
0.0
1
0.0
1
0.2
0
0.1
0
0.0
0
0.0
0
0.3
5
12
Red
uvid
bu
g
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
13
Sp
ider
1
.40
1.5
0
1.6
0
1.4
0
1.3
9
1.3
0
1.1
0
1.4
0
0.1
0
0.0
0
0.0
0
0.0
0
0.9
3
14
Can
tho
con
a bu
g
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
1
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
15
Co
w b
ug
2
.30
2.2
0
2.3
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.5
7
To
tal
10
.20
9.6
9
11.0
1
5.5
6
4.5
4
4.7
5
8.8
7
11
.92
11
.00
10
.30
6.0
0
5.8
0
8.3
0
*T
he
dat
a sh
ow
s A
v. o
f fo
rtnig
ht
inte
rval
36
4.1
ac:
Mea
n d
ata
of
the
ass
oci
ate
d i
nse
cts
wit
h c
on
gre
ss g
rass
rec
ord
ed u
nd
er r
oad
sid
e are
a o
f IG
KV
ca
mp
us,
Raip
ur
du
rin
g
2016
S.
No.
Bio
-ag
ents
/Mo
nth
Road
sid
e
Ja
n
Feb
M
ar
Ap
r M
ay
Ju
n
Ju
l A
ug
Sep
O
ct
No
v
Dec
M
ean
1
Zy
go
gra
mm
a (
Eg
g)
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
6.5
0
7.4
0
5.7
0
2.5
0
0.0
0
0.0
0
1.8
4
2
Zy
go
gra
mm
a (
Gru
bs)
0
.00
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.2
0
5.3
0
0.0
0
0.0
0
0.0
0
0.0
0
0.4
6
3
Zy
go
gra
mm
a A
du
lts
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.3
3
8.5
0
1.0
0
0.5
0
0.4
6
0.0
0
0.9
0
4
Mea
ly b
ug
0
.10
0.3
0
0.4
0
0.2
0
0.0
0
1.7
0
1.2
0
1.7
0
2.8
0
1.8
0
0.7
0
0.8
0
0.9
8
5
Ap
hid
0
.00
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.6
0
1.8
0
1.2
0
1.5
0
2.5
0
0.6
3
6
An
t (s
mal
l/la
rge)
0
.20
0.5
0
0.6
0
0.9
0
0.6
0
0.6
5
0.2
0
0.8
0
1.1
0
1.6
0
0.6
0
0.6
0
0.7
0
7
Sp
ital
bu
g
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.4
0
0.0
0
0.0
0
0.0
0
0.0
3
8
Lea
fhop
per
0
.00
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
1.0
1
1.0
3
0.0
0
0.0
0
0.0
0
0.0
0
0.1
7
9
Lea
f m
iner
0
.50
0.6
0
0.7
0
0.8
0
0.7
0
0.4
0
0.0
0
0.0
0
0.0
0
0.2
0
0.3
0
0.7
0
0.4
1
10
Sem
ilo
op
er
0.2
0
0.1
0
0.0
1
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.2
0
0.3
0
0.0
7
11
Lad
y b
ird
bee
tle
0.1
0
0.2
0
0.3
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.3
0
0.0
8
12
Red
uvid
bu
g
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
13
Sp
ider
0
.40
0.5
0
0.6
0
0.4
0
0.3
9
0.3
0
1.0
1
0.4
0
1.7
0
0.4
0
0.4
0
0.4
0
0.5
8
14
Can
tho
con
a bu
g
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
1
0.0
0
0.0
0
0.0
0
0.0
0
0.1
9
0.0
2
15
Co
w b
ug
0
.30
0.2
0
0.3
0
0.2
0
0.0
0
0.0
0
0.0
0
0.0
0
0.2
0
0.1
0
0.3
0
0.2
0
0.1
5
To
tal
1.8
0
2.4
0
2.9
3
2.5
0
1.6
9
3.0
5
10.4
6
25
.73
14
.70
8.3
0
4.4
6
5.9
9
7.0
0
*T
he
dat
a sh
ow
s A
v. o
f fo
rtnig
ht
inte
rval
37
Fig-
4.1a
a: M
ean
data
showingt
he n
atur
al e
nem
ies o
f con
gres
s gra
ss u
nder
agr
o-fo
rest
ry a
rea
of IG
KV
cam
pus o
f Rai
pur
duri
ng 2
016
Fig-
4.1ab:
Mea
n da
ta showingt
he n
atur
al e
nem
ies o
f con
gres
s gra
ss u
nder
fiel
d cr
oppe
dare
a of
IGK
V c
ampu
s of R
aipu
r du
ring
201
6
0123456789
Jan
Feb
Mar
Apr
May
Jun
Jul
Aug
Sep
Oct
Nov
Dec
Av populn of enemies
Mon
ths
Zyg
ogra
mm
a ( G
rubs
)Z
ygog
ram
ma
Adu
ltsM
ealy
bug
Aph
idA
nt (s
mal
l/lar
ge)
Spita
l bug
Lea
fhop
per
Lea
f min
erSe
milo
oper
Lad
y bi
rd b
eetle
Red
uvid
bug
Spid
erC
anth
ocon
a bu
gC
ow b
ug
02468101214
Jan
Feb
Mar
Apr
May
Jun
Jul
Aug
Sep
Oct
Nov
Dec
Av populn of enemies
Mon
ths
Zyg
ogra
mm
a ( G
rubs
)Z
ygog
ram
ma
Adu
ltsM
ealy
bug
Aph
idA
nt (s
mal
l/lar
ge)
Spita
l bug
Lea
fhop
per
Lea
f min
erSe
milo
oper
Lad
y bi
rd b
eetle
Red
uvid
bug
Spid
erC
anth
ocon
a bu
gC
ow b
ug
38
Fig-
4.1ac:
Mea
n da
ta showingt
he n
atur
al e
nem
ies o
f con
gres
s gra
ss u
nder
roa
d si
de a
rea
of IG
KV
cam
pus o
f Rai
pur
duri
ng 2
016
Fig-
4.1a
d: M
ean
data
showingt
he n
atur
al e
nem
ies o
f con
gres
s gra
ss u
nder
agr
ofor
estr
y, fi
eld
crop
ped
and
road
side
are
a of
IGK
V c
ampu
s of
Rai
pur
duri
ng 2
016.
051015202530
Jan
Feb
Mar
Apr
May
Jun
Jul
Aug
Sep
Oct
Nov
Dec
Av populn of enemies
Mon
ths
Zyg
ogra
mm
a ( G
rubs
)Z
ygog
ram
ma
Adu
ltsM
ealy
bug
Aph
idA
nt (s
mal
l/lar
ge)
Spita
l bug
Lea
fhop
per
Lea
f min
erSe
milo
oper
Lad
y bi
rd b
eetle
Red
uvid
bug
Spid
erC
anth
ocon
a bu
gC
ow b
ug
0
0.51
1.52
2.5
Agro
-fore
stry
Fiel
d cr
oppe
dRo
ad si
de
Av populn of enemies
Area
Zygo
gram
ma
( Egg
)Zy
gogr
amm
a ( G
rubs
)Zy
gogr
amm
a Ad
ults
Mea
ly b
ugAp
hid
Ant (
smal
l/lar
ge)
Spita
l bug
Leaf
hopp
erLe
af m
iner
Sem
iloop
erLa
dy b
ird b
eetle
Redu
vid
bug
Spid
erCa
ntho
cona
bug
Cow
bug
39
Tab
le 4
.1b
a:
Mea
n d
ata
of
the
ass
oci
ate
d i
nse
cts
wit
h c
on
gre
ss g
rass
un
der
ag
ro-f
ore
stry
area
of
IGK
V c
am
pu
s, R
aip
ur
du
rin
g
2017
S.
No.
Bio
-ag
ents
/Mo
nth
Agro
fore
stry
Jan
F
eb
Mar
Ap
r M
ay
Ju
n
Ju
l A
ug
Sep
O
ct
No
v
Dec
M
ean
1
Zy
go
gra
mm
a (
Eg
g)
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.9
5
0.3
0
0.0
0
0.0
0
0.0
0
0.0
0
0.1
0
2
Zy
go
gra
mm
a (
Gru
bs)
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.1
0
0.2
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
3
3
Zy
go
gra
mm
a A
du
lts
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.2
3
0.3
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
4
4
Mea
ly b
ug
0.5
0
0.3
0
0.3
0
0.5
0
0.0
0
0.4
0
0.2
0
0.5
0
0.3
0
0.2
0
0.2
0
0.1
0
0.2
9
5
Ap
hid
1.5
0
1.0
1
1.2
0
0.0
0
0.0
0
0.0
0
0.0
0
0.5
0
0.5
0
1.1
0
1.2
0
1.5
0
0.7
1
6
An
t (s
mal
l/la
rge)
0.6
0
0.5
0
1.6
0
0.9
0
0.8
0
0.6
0
0.2
0
0.6
0
0.6
0
0.6
0
0.8
0
2.6
0
0.8
7
7
Sp
ital
bu
g
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
8
Lea
fhop
per
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
1.0
2
0.0
0
0.0
0
0.0
0
0.0
0
0.0
9
9
Lea
f m
iner
0.0
0
0.0
0
0.0
0
0.6
0
0.6
0
0.4
0
0.0
0
0.0
0
0.2
0
0.2
0
0.2
0
0.6
0
0.2
3
10
S
emil
oo
per
0.0
0
0.0
0
0.0
1
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.3
0
0.0
3
11
L
ady b
ird
bee
tle
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.3
0
0.0
3
12
R
edu
vid
bu
g
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
13
S
pid
er
0.4
0
0.5
0
0.6
0
0.4
0
0.3
9
0.3
0
0.0
1
0.4
0
0.3
0
0.4
2
0.4
0
0.4
5
0.3
8
14
C
anth
oco
na
bu
g
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
1
0.0
0
0.0
0
0.0
0
0.0
0
0.1
9
0.0
2
15
C
ow
bu
g
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.3
0
0.4
2
0.3
2
0.4
2
0.1
2
To
tal
3.0
0
2.3
1
3.7
1
2.4
0
1.8
0
1.7
0
1.7
2
3.8
3
2.2
1
3.0
4
3.1
3
6.5
8
2.9
5
*T
he
dat
a sh
ow
s A
v. o
f fo
rtnig
ht
inte
rval
40
Tab
le 4
.1b
b:
Mea
n d
ata
of
the
ass
oci
ate
d i
nse
cts
wit
h c
on
gre
ss g
rass
un
der
fie
ld c
rop
ped
are
a o
f IG
KV
ca
mp
us,
Raip
ur
du
rin
g
2017
S.
No.
Bio
-ag
ents
/Mo
nth
Fie
ld c
rop
ped
are
a
Ja
n
Feb
M
ar
Ap
r M
ay
Ju
n
Ju
l A
ug
Sep
O
ct
No
v
Dec
M
ean
1
Zy
go
gra
mm
a (
Eg
g)
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
1.5
0
1.9
0
1.2
0
0.5
0
0.0
0
0.0
0
0.4
3
2
Zy
go
gra
mm
a (
Gru
bs)
0
.00
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
1.2
0
1.3
0
0.6
0
0.5
0
0.0
0
0.0
0
0.3
0
3
Zy
go
gra
mm
a A
du
lts
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.3
3
0.5
0
0.8
0
0.6
0
0.0
0
0.0
0
0.1
9
4
Mea
ly b
ug
0
.40
0.2
0
0.5
0
0.7
0
0.0
0
0.7
0
0.2
0
0.7
0
0.0
0
0.4
0
0.2
0
0.5
0
0.3
8
5
Ap
hid
0
.50
0.3
0
0.5
0
0.5
0
0.0
0
0.0
0
0.0
0
1.5
0
4.1
0
3.2
0
2.5
0
1.5
0
1.2
2
6
An
t (s
mal
l/la
rge)
1
.60
1.5
0
1.6
0
0.9
0
0.8
0
1.6
0
1.2
0
2.6
0
1.8
0
1.6
0
0.6
0
1.6
0
1.4
5
7
Sp
ital
bu
g
0.1
0
0.0
9
0.3
0
0.5
0
0.5
0
0.3
4
0.3
0
0.0
1
0.0
0
0.0
0
0.0
0
0.0
0
0.1
8
8
Lea
fhop
per
0
.00
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
9
Lea
f m
iner
0
.34
0.3
0
0.0
1
0.8
2
0.7
5
0.8
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.2
5
10
Sem
ilo
op
er
0.8
0
0.9
0
0.0
1
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.1
4
11
Lad
y b
ird
bee
tle
0.5
0
0.7
0
0.0
0
0.7
0
0.2
0
0.0
1
0.0
1
0.0
1
0.2
0
0.1
0
0.0
0
0.0
0
0.2
0
12
Red
uvid
bu
g
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
13
Sp
ider
1
.40
1.5
0
0.5
0
0.7
0
0.0
0
0.7
0
0.2
0
1.4
0
0.1
0
0.0
0
0.0
0
0.0
0
0.5
4
14
Can
tho
con
a bu
g
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
1
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
15
Co
w b
ug
2
.30
2.2
0
2.3
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.5
7
To
tal
7.9
4
7.6
9
6.2
2
5.5
2
2.2
5
4.8
5
5.1
5
9.9
2
8.8
0
6.9
0
3.3
0
3.6
0
6.0
1
*T
he
dat
a sh
ow
s A
v. o
f fo
rtnig
ht
inte
rval
41
Tab
le 4
.1b
c: M
ean
data
of
the
ass
oci
ate
d i
nse
cts
wit
h c
on
gre
ss g
rass
un
der
road
sid
e are
a o
f IG
KV
ca
mp
us,
Raip
ur
du
rin
g 2
017
S.
No.
Bio
-ag
ents
/Mo
nth
Road
sid
e
Ja
n
Feb
M
ar
Ap
r M
ay
Ju
n
Ju
l A
ug
Sep
O
ct
No
v
Dec
M
ean
1
Zy
go
gra
mm
a (
Eg
g)
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
4.5
0
5.7
0
5.4
0
1.5
0
0.0
0
0.0
0
1.4
3
2
Zy
go
gra
mm
a (
Gru
bs)
0
.00
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.2
0
4.3
0
0.0
0
0.0
0
0.0
0
0.0
0
0.3
8
3
Zy
go
gra
mm
a A
du
lts
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.3
3
7.5
0
1.0
0
0.5
0
0.4
6
0.0
0
0.8
2
4
Mea
ly b
ug
0
.10
0.3
0
0.4
0
0.2
0
0.0
0
1.7
0
1.2
0
1.7
0
2.8
0
0.0
0
1.7
0
1.2
0
0.9
4
5
Ap
hid
0
.00
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.6
0
1.8
0
1.2
0
1.5
0
2.5
0
0.6
3
6
An
t (s
mal
l/la
rge)
0
.20
0.5
0
0.6
0
0.9
0
0.6
0
0.6
5
0.2
0
0.8
0
1.1
0
1.6
0
0.6
0
0.6
0
0.7
0
7
Sp
ital
bu
g
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.4
0
0.0
0
0.0
0
0.0
0
0.0
3
8
Lea
fhop
per
0
.00
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
1.0
1
1.0
3
0.0
0
0.0
0
0.0
0
0.0
0
0.1
7
9
Lea
f m
iner
0
.20
0.5
0
0.6
0
0.9
0
0.6
0
0.4
0
0.0
0
0.0
0
0.0
0
0.2
0
0.3
0
0.7
0
0.3
7
10
Sem
ilo
op
er
0.2
0
0.1
0
0.0
1
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.2
0
0.3
0
0.0
7
11
Lad
y b
ird
bee
tle
0.1
0
0.2
0
0.3
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.3
0
0.0
8
12
Red
uvid
bu
g
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
13
Sp
ider
0
.40
0.5
0
0.2
0
0.5
0
0.6
0
0.9
0
0.6
0
0.4
0
1.7
0
0.4
0
0.4
0
0.4
0
0.5
8
14
Can
tho
con
a bu
g
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
1
0.0
0
0.0
0
0.0
0
0.0
0
0.1
9
0.0
2
15
Co
w b
ug
0
.30
0.2
0
0.5
0
0.6
0
0.9
0
0.6
0
0.0
0
0.0
0
0.2
0
0.1
0
0.3
0
0.2
0
0.3
3
To
tal
1.5
0
2.3
0
2.6
3
3.1
0
2.7
0
4.2
5
8.0
5
22
.03
14
.40
5.5
0
5.4
6
6.3
9
6.5
3
*T
he
dat
a sh
ow
s A
v. o
f fo
rtnig
ht
inte
rval
42
Fig-
4.1b
a: M
ean
data
showingt
he n
atur
al e
nem
ies o
f con
gres
s gra
ss u
nder
agr
o-fo
rest
ry a
rea
of IG
KV
cam
pus o
f Rai
pur
duri
ng 2
017
Fig-
4.1bb:
Mea
n da
ta showingt
he n
atur
al e
nem
ies o
f con
gres
s gra
ss u
nder
fiel
d cr
oppe
d ar
ea o
f IG
KV
cam
pus o
f Rai
pur
duri
ng 2
017
01234567
Jan
Feb
Mar
Apr
May
Jun
Jul
Aug
Sep
Oct
Nov
Dec
Av populn of enemies
Mon
ths
Zyg
ogra
mm
a ( G
rubs
)Z
ygog
ram
ma
Adu
ltsM
ealy
bug
Aph
id
Ant
(sm
all/l
arge
)Sp
ital b
ugL
eafh
oppe
rL
eaf m
iner
Sem
iloop
erL
ady
bird
bee
tleR
eduv
id b
ugSp
ider
Can
thoc
ona
bug
Cow
bug
024681012
Jan
Feb
Mar
Apr
May
Jun
Jul
Aug
Sep
Oct
Nov
Dec
Av populn of enemies
Mon
ths
Zyg
ogra
mm
a ( G
rubs
)Z
ygog
ram
ma
Adu
ltsM
ealy
bug
Aph
idA
nt (s
mal
l/lar
ge)
Spita
l bug
Lea
fhop
per
Lea
f min
erSe
milo
oper
Lad
y bi
rd b
eetle
Red
uvid
bug
Spid
erC
anth
ocon
a bu
gC
ow b
ug
43
Fig-
4.1bc:
Mea
n da
ta showingt
he n
atur
al e
nem
ies o
f con
gres
s gra
ss u
nder
roa
d si
de a
rea
of IG
KV
cam
pus o
f Rai
pur
duri
ng 2
017
Fig-
4.1b
d: M
ean
data
showingt
he n
atur
al e
nem
ies o
f con
gres
s gra
ss u
nder
agr
ofor
estr
y, fi
eld
crop
ped
and
road
side
are
a of
IG
KV
cam
pus
of R
aipu
r du
ring
201
7.
0510152025
Jan
Feb
Mar
Apr
May
Jun
Jul
Aug
Sep
Oct
Nov
Dec
Av populn of enemies
Mon
ths
Zyg
ogra
mm
a ( G
rubs
)Z
ygog
ram
ma
Adu
ltsM
ealy
bug
Aph
idA
nt (s
mal
l/lar
ge)
Spita
l bug
Lea
fhop
per
Lea
f min
erSe
milo
oper
Lad
y bi
rd b
eetle
Red
uvid
bug
Spid
erC
anth
ocon
a bu
gC
ow b
ug
0
0.2
0.4
0.6
0.81
1.2
1.4
1.6
Agro
-fore
stry
Fiel
d cr
oppe
dRo
ad si
de
Av populn of enemies
Area
Zygo
gram
ma
( Egg
)Zy
gogr
amm
a ( G
rubs
)Zy
gogr
amm
a Ad
ults
Mea
ly b
ugAp
hid
Ant (
smal
l/lar
ge)
Spita
l bug
Leaf
hopp
erLe
af m
iner
Sem
iloop
erLa
dy b
ird b
eetle
Redu
vid
bug
Spid
erCa
ntho
cona
bug
Cow
bug
44
4.1
ca:
Poole
d m
ean
data
of
the
ass
oci
ate
d i
nse
cts
wit
h c
on
gre
ss g
rass
un
der
agro
-fore
stry
fie
ld
area
of
IGK
V c
am
pu
s, R
aip
ur
du
rin
g 2
016 &
17
S.
No.
Bio
-ag
ents
/Mo
nth
Agro
fore
stry
Jan
F
eb
Mar
Ap
r M
ay
Ju
n
Ju
l A
ug
Sep
O
ct
No
v
Dec
M
ean
1
Zy
go
gra
mm
a (
Eg
g)
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
1.2
3
0.3
5
0.0
0
0.0
0
0.0
0
0.0
0
0.1
3
2
Zy
go
gra
mm
a (
Gru
bs)
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.1
5
0.2
5
0.0
0
0.0
0
0.0
0
0.0
0
0.0
3
3
Zy
go
gra
mm
a A
du
lts
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.2
8
0.4
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
6
4
Mea
ly b
ug
0.6
0
0.3
5
0.6
0
0.6
0
0.0
0
0.5
5
0.2
0
0.6
0
0.5
0
0.5
0
0.4
5
0.4
0
0.4
5
5
Ap
hid
2.0
0
1.1
6
1.3
5
0.2
5
0.0
0
0.0
0
0.0
0
1.0
0
1.0
0
1.1
5
1.3
5
2.0
0
0.9
4
6
An
t (s
mal
l/la
rge)
0.6
0
1.0
0
1.6
0
0.9
0
0.8
0
0.6
0
0.7
0
0.6
0
0.6
0
0.6
0
0.7
0
2.6
0
0.9
4
7
Sp
ital
bu
g
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
8
Lea
fhop
per
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.5
1
1.0
3
0.0
0
0.0
0
0.0
0
0.0
0
0.1
3
9
Lea
f m
iner
0.2
5
0.3
0
0.3
5
0.7
0
0.6
5
0.4
0
0.0
0
0.0
0
0.3
0
0.2
0
0.2
5
0.6
5
0.3
4
10
Sem
ilo
op
er
0.1
0
0.0
5
0.0
1
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
5
0.0
0
0.1
0
0.3
0
0.0
5
11
Lad
y b
ird
bee
tle
0.0
5
0.1
0
0.1
5
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.3
0
0.0
5
12
Red
uvid
bu
g
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
13
Sp
ider
0.4
0
0.5
0
0.6
0
0.4
0
0.3
9
0.3
0
0.5
1
0.4
0
0.3
5
0.4
1
0.4
0
0.4
3
0.4
2
14
Can
tho
con
a bu
g
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
1
0.0
0
0.0
0
0.0
0
0.0
0
0.1
9
0.0
2
15
Co
w b
ug
0.6
5
0.6
0
0.6
5
0.1
0
0.0
0
0.0
0
0.0
0
0.0
0
0.3
0
0.3
1
0.3
2
0.3
6
0.2
7
To
tal
4.7
0
4.0
6
5.3
2
2.9
5
1.8
5
1.8
5
3.6
0
4.7
3
3.1
6
3.2
7
3.6
3
7.3
5
3.8
7
*T
he
dat
a sh
ow
s A
v. o
f fo
rtnig
ht
inte
rval
45
4.1
cb:
Poole
d m
ean
data
of
the
ass
oci
ate
d i
nse
cts
wit
h c
on
gre
ss g
rass
un
der
fie
ld c
rop
ped
are
a o
f IG
KV
ca
mp
us,
Raip
ur
du
rin
g
2016 &
17
S.
No.
Bio
-ag
ents
/Mo
nth
Fie
ld c
rop
ped
are
a
Jan
F
eb
Mar
Ap
r M
ay
Ju
n
Ju
l A
ug
Sep
O
ct
No
v
Dec
M
ean
1
Zy
go
gra
mm
a (
Eg
g)
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
2.0
0
2.4
0
1.3
0
0.5
0
0.0
0
0.0
0
0.5
2
2
Zy
go
gra
mm
a (
Gru
bs)
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
1.7
0
1.8
0
0.6
0
0.5
0
0.1
0
0.0
0
0.3
9
3
Zy
go
gra
mm
a A
du
lts
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.3
3
0.5
0
0.8
0
0.6
0
0.0
0
0.0
0
0.1
9
4
Mea
ly b
ug
0.5
5
0.3
0
0.7
0
0.7
0
0.0
0
0.7
0
0.2
0
0.7
0
0.0
0
0.6
0
0.4
5
0.6
0
0.4
6
5
Ap
hid
1.0
0
0.3
0
0.5
0
0.5
0
0.0
0
0.0
0
0.0
0
1.5
0
5.1
0
4.7
0
3.0
0
2.0
0
1.5
5
6
An
t (s
mal
l/la
rge)
1.6
0
2.0
0
2.1
0
1.4
0
1.3
0
1.6
0
1.7
0
2.6
0
1.8
0
1.6
0
1.1
0
2.1
0
1.7
4
7
Sp
ital
bu
g
0.1
0
0.0
9
0.1
9
0.2
7
0.5
0
0.3
4
0.3
0
0.0
1
0.0
0
0.0
0
0.0
0
0.0
0
0.1
5
8
Lea
fhop
per
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
9
Lea
f m
iner
0.5
2
0.4
5
0.8
7
0.8
2
0.7
5
0.8
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.3
5
10
S
emil
oo
per
0.8
0
0.9
0
0.0
1
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.1
4
11
L
ady b
ird
bee
tle
0.8
0
0.9
5
0.6
5
0.4
5
0.1
5
0.0
1
0.0
1
0.0
1
0.2
0
0.1
0
0.0
0
0.0
0
0.2
8
12
R
edu
vid
bu
g
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
13
S
pid
er
1.4
0
1.5
0
1.0
5
1.0
5
0.7
0
1.0
0
0.6
5
1.4
0
0.1
0
0.0
0
0.0
0
0.0
0
0.7
4
14
C
anth
oco
na
bu
g
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
1
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
15
C
ow
bu
g
2.3
0
2.2
0
2.3
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.5
7
To
tal
9.0
7
8.6
9
8.6
2
5.5
4
3.4
0
4.8
0
7.0
1
10
.92
9.9
0
8.6
0
4.6
5
4.7
0
7.1
6
*T
he
dat
a sh
ow
s A
v. o
f fo
rtnig
ht
inte
rval
46
4.1
cc:
Poole
d m
ean
data
of
the
ass
oci
ate
d i
nse
cts
wit
h c
on
gre
ss g
rass
un
der
road
sid
e are
a o
f IG
KV
ca
mp
us,
Raip
ur
du
rin
g 2
016
&17
S.
No.
Bio
-ag
ents
/Mo
nth
Road
sid
e
Jan
F
eb
Mar
Ap
r M
ay
Ju
n
Ju
l A
ug
Sep
O
ct
No
v
Dec
M
ean
1
Zy
go
gra
mm
a (
Eg
g)
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
2.0
0
2.4
0
1.3
0
0.5
0
0.0
0
0.0
0
0.4
8
2
Zy
go
gra
mm
a (
Gru
bs)
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
1.7
0
1.8
0
0.6
0
0.5
0
0.1
0
0.0
0
0.3
6
3
Zy
go
gra
mm
a A
du
lts
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.3
3
0.5
0
0.8
0
0.6
0
0.0
0
0.0
0
0.1
7
4
Mea
ly b
ug
0.5
5
0.3
0
0.7
0
0.7
0
0.0
0
0.7
0
0.2
0
0.7
0
0.0
0
0.6
0
0.3
5
0.4
5
0.4
3
5
Ap
hid
1.0
0
0.3
0
0.5
0
0.5
0
0.0
0
0.0
0
0.0
0
1.5
0
5.1
0
4.7
0
3.1
5
2.3
0
1.4
3
6
An
t (s
mal
l/la
rge)
1.6
0
2.0
0
2.1
0
1.4
0
1.3
0
1.6
0
1.7
0
2.6
0
1.8
0
1.6
0
1.1
5
2.6
0
1.6
2
7
Sp
ital
bu
g
0.1
0
0.0
9
0.1
9
0.2
7
0.5
0
0.3
4
0.3
0
0.0
1
0.0
0
0.0
0
0.0
0
0.0
0
0.1
4
8
Lea
fhop
per
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
9
Lea
f m
iner
0.5
2
0.4
5
0.8
7
0.8
2
0.7
5
0.8
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.3
5
10
S
emil
oo
per
0.8
0
0.9
0
0.0
1
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.1
5
11
L
ady b
ird
bee
tle
0.8
0
0.9
5
0.6
5
0.4
5
0.1
5
0.0
1
0.0
1
0.0
1
0.2
0
0.1
0
0.0
0
0.0
0
0.2
6
12
R
edu
vid
bu
g
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
13
S
pid
er
1.4
0
1.5
0
1.0
5
1.0
5
0.7
0
1.0
0
0.6
5
1.4
0
0.1
0
0.0
0
0.0
0
0.0
0
0.7
1
14
C
anth
oco
na
bu
g
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
1
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
15
C
ow
bu
g
2.3
0
2.2
0
2.3
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.0
0
0.5
5
To
tal
9.0
7
8.6
9
8.6
2
5.5
4
3.4
0
4.8
0
7.0
1
10
.92
9.9
0
8.6
0
4.7
5
5.3
5
6.7
4
*T
he
dat
a sh
ow
s A
v. o
f fo
rtnig
ht
inte
rval
47
Fig-
4.1c
a: M
ean
data
showingt
he n
atur
al e
nem
ies o
f con
gres
s gra
ss u
nder
agr
o-fo
rest
ry a
rea
of IG
KV
cam
pus o
f Rai
pur
duri
ng 2
016
&20
17
Fig-
4.1cb:
Mea
n da
ta showingt
he n
atur
al e
nem
ies o
f con
gres
s gra
ss u
nder
fiel
d cr
oppe
d ar
ea o
f IG
KV
cam
pus o
f Rai
pur
duri
ng 2
016
&20
17
012345678
Jan
Feb
Mar
Apr
May
Jun
Jul
Aug
Sep
Oct
Nov
Dec
Av populn of enemies
Mon
ths
Zyg
ogra
mm
a ( G
rubs
)Z
ygog
ram
ma
Adu
ltsM
ealy
bug
Aph
idA
nt (s
mal
l/lar
ge)
Spita
l bug
Lea
fhop
per
Lea
f min
erSe
milo
oper
Lad
y bi
rd b
eetle
Red
uvid
bug
Spid
erC
anth
ocon
a bu
gC
ow b
ug
024681012
Jan
Feb
Mar
Apr
May
Jun
Jul
Aug
Sep
Oct
Nov
Dec
Av populn of enemies
Mon
ths
Zyg
ogra
mm
a ( G
rubs
)Z
ygog
ram
ma
Adu
ltsM
ealy
bug
Aph
idA
nt (s
mal
l/lar
ge)
Spita
l bug
Lea
fhop
per
Lea
f min
erSe
milo
oper
Lad
y bi
rd b
eetle
Red
uvid
bug
Spid
erC
anth
ocon
a bu
gC
ow b
ug
48
Fig-
4.1cc:
Mea
n da
ta showingt
he n
atur
al e
nem
ies o
f con
gres
s gra
ss u
nder
roa
d si
de a
rea
of IG
KV
cam
pus o
f Rai
pur
duri
ng 2
016
&20
17
Fig-
4.1c
d: M
ean
data
showingt
he n
atur
al e
nem
ies o
f con
gres
s gra
ss u
nder
agr
ofor
estr
y, fi
eld
crop
ped
and
road
side
are
a of
IGK
V c
ampu
s of
Rai
pur
duri
ng 2
016
&20
17.
024681012
Jan
Feb
Mar
Apr
May
Jun
Jul
Aug
Sep
Oct
Nov
Dec
Av populn of enemies
Mon
ths
Zyg
ogra
mm
a ( G
rubs
)Z
ygog
ram
ma
Adu
ltsM
ealy
bug
Aph
idA
nt (s
mal
l/lar
ge)
Spita
l bug
Lea
fhop
per
Lea
f min
erSe
milo
oper
Lad
y bi
rd b
eetle
Red
uvid
bug
Spid
erC
anth
ocon
a bu
gC
ow b
ug
0
0.2
0.4
0.6
0.81
1.2
1.4
1.6
1.82
Agro
-fore
stry
Fiel
d cr
oppe
dRo
ad si
de
Av populn of enemies
Area
Zygo
gram
ma
( Egg
)Zy
gogr
amm
a ( G
rubs
)Zy
gogr
amm
a Ad
ults
Mea
ly b
ugAp
hid
Ant (
smal
l/lar
ge)
Spita
l bug
Leaf
hopp
erLe
af m
iner
Sem
iloop
erLa
dy b
ird b
eetle
Redu
vid
bug
Spid
erCa
ntho
cona
bug
Cow
bug
49
4.2: To study the e-surveillance of Parthenium and other associated weeds in
Kharif and Rabi season
The e-surveillance programme of Parthenium and other associated weeds
was conducted at four different Blocks (Arang, Dharsiwa, Tilda and Abhanpur) of
Raipur, Chhattisgarh. For this investigation, the observations of weeds were
recorded though GPS machine on the basis of visual/magnifying glass from
upland, midland and lowland in one sqm area of five locations i.e. five farmers
field under each selected village during Kharif and Rabi season were included.
Parthenium and other associated weeds like annual/perennial were observed to find
out the population of insect pests associated at the different critical plant stages.
The observations were recorded at periodical intervals and presented in table-4.2a,
4.2b &4.2c and fig.-4.2aa, 4.2ab, 4.2ac, 4.2ba, 4.2bb, 4.2bc, 4.2ca, 4.2cb & 4.2cc
as follows:
4.2.1: Upland
4.2.1.1: Arang block
During first year i.e. in 2016 the maximum average population (3.87) /sqm
of ants was noticed followed by spider (0.89) whereas minimum (0.01)/sqm of
caterpillars compared with the population of Mexican beetle was recorded of
(0.80) /sqm at Arang block.
During second year also highest population (2.87) /sqm was recorded in
case of ants followed by spider whereas minimum (0.79)/sqm of caterpillars and
(0.76)/sqm of Mexican beetle, while lowest (0.04) in case of Canthocona bugs
were recorded at Arang block.
Pooled analysis of two years data scored maximum (3.37) /sqm of ants
followed by Mexican beetle (0.78/sqm) while minimum population was recorded
of Canthocona bugs i.e. 0.04 at Arang block.
4.2.1.2: Dharsiwa block
During first year, the maximum average population (2.87)/sqm were
noticed of ants and minimum (0.04)/sqm in case of mealy bugs as compared with
the population of Mexican beetle (0.82) /sqm was recorded.
50
During second year also the highest population (1.87) /sqm was recorded in
ants and minimum (0.01)/sqm of Canthocona bugs while (0.86)/sqm of Mexican
beetles were recorded at Dharsiwa block.
Pooled analysis of two years data scored maximum (2.37) /sqm of ants
followed by Mexican beetle (0.84/sqm) and minimum of Canthocona bugs i.e.
(0.01) /sqm.
4.2.1.3: Tilda block
During the first year, maximum average population (3.87) /sqm was
noticed in case of ants and minimum (0.01)/sqm of Canthocona bugs as compared
with the population of (0.65)/sqm Mexican beetle was recorded.
During second year also, similar trend of highest population (2.87) /sqm
was recorded in ants and minimum (0.06)/sqm in cow bugs while (0.61)/sqm of
Mexican beetle was observed at Tilda block.
Pooled analysis of two years data scored maximum (3.37) /sqm in ants,
(0.84)/sqm Mexican beetle and minimum of Canthocona bugs i.e. (0.01) /sqm.
4.2.1.4: Abhanpur block
During the first year, maximum average population of (3.88) /sqm was
noticed in case of ants and minimum (0.01)/sqm of Canthocona bugs as compared
with the population (1.85)/sqm of Mexican beetle.
During the second year, highest population (2.88) /sqm was also recorded
in case of ants and minimum (0.02)/sqm in lady bird beetle while (1.61)/sqm of
Mexican beetle at Abhanpur block.
Pooled analysis of two years data scored maximum (3.38) /sqm in ants
followed by Mexican beetle (1.73/sqm) and minimum of Canthocona bugs i.e.
(0.01)/sqm.
4.2.2: Midland
4.2.2.1: Arang block
During the first year, maximum average population of (2.86) /sqm was
noticed of ants and minimum (0.02)/sqm of cow bugs, semilooper and lady bird
beetles. The population of Mexican beetles was recorded to be (1.42)/sqm.
51
During the second year also highest population (1.86) /sqm was recorded in
case of ants and minimum (0.02)/sqm of semilooper while Mexican beetle was
observed to be (1.32)/sqm at Arang block.
Pooled analysis of two years data scored maximum (2.36) /sqm of ants
and Mexican beetle (1.37/sqm) while minimum in cow bug i.e. (0.02) /sqm.
4.2.2.2: Dharsiwa block
During the first year, maximum average population of (2.86) /sqm was
noticed in ants and minimum (0.01)/sqm of semilooper, where as the population of
Mexican beetle was recorded to be (1.42)/sqm.
During the second year also ants dominated with highest population (1.86)
/sqm and minimum (0.02)/sqm of cow bugs while (1.32)/sqm of Mexican beetle
population was recorded at Dharsiwa block.
Pooled analysis of two years data scored maximum (2.36) /sqm in ants,
(1.37/sqm) of Mexican beetle and minimum of semilooper, spittle bugs and cow
bugs i.e. (0.02) /sqm, respectively.
4.2.2.3: Tilda block
During the first year i.e. in 2016 maximum average population of (1.95)
/sqm was noticed in case of ants and minimum (0.01)/sqm of Canthocona bugs
while the population of Mexican beetle was recorded as (0.40)/sqm.
During the second year, again ants recorded highest population (1.76) /sqm
and minimum (0.02)/sqm in cow bugs and semilooper, respectively while
(1.32)/sqm of Mexican beetle were observed at Tilda block.
Pooled analysis of two years data scored maximum (1.76) /sqm in ants,
(0.36/sqm) of Mexican beetle and minimum of cow bugs and semilooper i.e. (0.02)
/sqm, respectively.
4.2.2.4: Abhanpur block
During the first year, maximum average population of (3.76) /sqm was
noticed in ants and minimum (0.01)/sqm in Canthocona bugs where as the
population of Mexican beetle was recorded as (1.40)/sqm.
52
In the second year also ants recorded highest population (2.76) /sqm and
lowest (0.10)/sqm in Canthocona bugs while (1.32)/sqm of Mexican beetle were
recorded at Abhanpur block.
Pooled analysis of two years data scored maximum (3.26) /sqm in ants
and Mexican beetle (1.36/sqm) and minimum in Canthocona bugs i.e. (0.06) /sqm.
4.2.3: Lowland
4.2.3.1: Arang block
During the first year, maximum average population of (2.70) /sqm was
noticed in case of Mexican beetles and minimum (0.01)/sqm in cow bugs and
Canthocona bugs.
During second year, the highest population (2.76) /sqm was recorded in
ants and minimum (0.03)/sqm of semilooper while (1.70)/sqm the in case of
Mexican beetle were recorded at Arang block. Pooled analysis of two years data
scored maximum (2.33) /sqm in ants followed by Mexican beetle (2.20/sqm) and
minimum in Canthocona bugs i.e. (0.01) /sqm.
4.2.3.2: Dharsiwa block
During the first year, the maximum average population of (1.70) /sqm was
noticed in Mexican beetle and minimum (0.02) /sqm in mealy bugs and
semilooper.
During second year, the highest population (1.33) /sqm was recorded in
ants and minimum (0.02)/sqm in semilooper while (0.70)/sqm of Mexican beetle at
Dharsiwa block.
Pooled analysis of two years data scored maximum (1.28) /sqm of ants
followed by Mexican beetle (1.20/sqm) and minimum of Canthocona bugs and
semilooper i.e. (0.02) /sqm.
4.2.3.3: Tilda block
During the first year, maximum average population of (2.70) /sqm was
noticed in case of Mexican beetle and minimum (0.08)/sqm in caterpillar.
53
In the second year also similar highest population of (2.70) /sqm was
recorded in Mexican beetle and minimum (0.06)/sqm of lady bird beetle at
Dharsiwa block.
Pooled analysis of two years data scored maximum (2.20) /sqm in Mexican
beetle and minimum in cow bug i.e. (0.10) /sqm.
4.2.3.4: Abhanpur block
During the first year, maximum average population of (3.80) /sqm was
noticed in case of Mexican beetle and minimum (0.01)/sqm in Canthocona bugs.
In the second year also highest population of (3.70) /sqm was recorded in
Mexican beetle and minimum (0.10)/sqm in cow bugs at Abhanpur block.
Pooled analysis of two years data scored maximum (3.75) /sqm in Mexican
beetle and minimum in lady bird beetle i.e. (0.05) /sqm.
On the basis of overall block (Arang, Dharsiwa, Tilda and Abhanpur) on
upland, midland and lowland was ranged from 0.01 to 3.62, 0.01 to 2.81 and 0.10
to 2.73, respectively during 2016. The maximum population was exhibited
(3.62)/sqm in ants and minimum in (0.01)/sqm in Canthocona bugs on lowland and
midland was also noticed (02.81) /sqm highest in ants and lowest in (0.01)/sqm in
Canthocona bugs while maximum (3.80)/sqm was recorded in Mexican beetle and
minimum in (0.01)/sqm in Canthocona bugs.
On the basis of overall block (Arang, Dharsiwa, Tilda and Abhanpur) on
upland, midland and lowland was ranged from 0.01 to 3.62, 0.01 to 2.70 and 0.10
to 2.73, respectively during 2017. The maximum population was exhibited (2.62)
/sqm in ants and minimum in (0.01) /sqm in Canthocona bugs on lowland and
midland was also noticed (1.76) /sqm highest in ants and lowest in (0.02) /sqm in
cow bugs while maximum (3.70) /sqm was recorded in Mexican beetle and
minimum in (0.10) /sqm in Canthocona bugs and cow bugs.
On the basis of pooled data of two years overall block i.e. at Arang,
Dharsiwa, Tilda and Abhanpur on upland, midland and lowland was ranged from
0.01 to 3.62, 0.01 to 2.70 and 0.10 to 2.73, respectively. The maximum population
was exhibited (3.12) /sqm in ants and minimum in (0.01) /sqm of Canthocona bugs
on lowland and midland was also noticed (1.76) /sqm highest in ants and lowest in
54
Tab
le-4
.2a:
e-su
rvei
llan
ce o
f p
art
hen
ium
an
d a
ssoci
ate
d i
nse
cts
at
Raip
ur
Dis
tric
t in
Kh
ari
f – R
abi
seaso
n d
uri
ng 2
016
S.
No
. E
nem
ies/
Blo
ck
U
L
ML
L
L
GM
A
ran
g
Dh
ars
iwa
T
ild
a A
bh
an
pu
r
Mea
n A
ran
g
Dh
ars
iwa
T
ild
a A
bh
an
pu
r
Mea
n A
ran
g
Dh
ars
iwa
T
ild
a A
bh
an
pu
r
Mea
n
1
Mex
ican b
eetl
e 0
.80
0.8
2
0.6
5
1.8
5
1.0
3
1.4
2
1.4
2
0.4
0
1.4
0
1.1
6
2.7
0
1.7
0
2.7
0
3.8
0
2.7
3
1.4
1
2
Ap
hid
s 0
.09
0.9
0
0.1
0
0.1
0
0.3
0
0.0
0
0.0
0
0.1
0
0.1
0
0.0
5
0.0
0
0.1
0
0.7
0
0.6
0
0.3
5
0.1
5
3
Mea
ly b
ugs
0.1
9
0.0
4
0.0
7
0.6
6
0.2
4
0.1
0
0.2
0
0.2
0
0.3
0
0.2
0
0.0
7
0.0
2
0.2
0
0.4
0
0.1
7
0.2
7
4
Co
w b
ug
s 0
.06
0.0
6
0.0
5
0.3
1
0.1
2
0.0
2
0.0
3
0.0
2
0.2
0
0.0
7
0.0
1
0.0
0
0.1
0
0.1
1
0.0
6
0.1
0
5
Ho
pp
ers
0.4
0
0.2
1
0.2
1
0.6
1
0.3
6
0.5
0
0.3
0
0.2
0
0.4
0
0.3
5
0.5
7
0.2
7
0.2
7
0.4
7
0.4
0
0.3
4
6
Sem
ilo
op
er
0.4
0
0.3
3
0.1
4
0.1
0
0.2
4
0.0
2
0.0
1
0.0
2
0.1
0
0.0
4
0.0
4
0.0
2
0.1
0
0.7
0
0.2
2
0.2
1
7
Cat
erp
illa
r 0
.01
0.1
1
0.1
1
0.4
0
0.1
6
0.1
0
0.1
2
0.1
5
0.1
7
0.1
4
0.8
0
0.1
8
0.0
8
0.7
0
0.4
4
0.2
6
8
Sp
ittl
e b
ug
s 0
.21
0.0
9
0.0
1
0.9
0
0.3
0
0.0
8
0.0
2
0.1
0
0.3
0
0.1
2
0.0
7
0.0
4
0.1
8
0.2
8
0.1
4
0.2
2
9
Sp
ider
/mit
es
0.8
9
0.7
9
0.8
9
0.8
1
0.8
4
2.8
5
1.8
5
1.9
5
2.9
5
2.4
0
1.4
8
1.3
8
1.4
8
1.5
8
1.4
8
0.8
8
10
Ants
3
.87
2.8
7
3.8
7
3.8
8
3.6
2
2.8
6
2.8
6
1.7
6
3.7
6
2.8
1
2.3
3
1.2
3
1.8
3
3.7
3
2.2
8
2.2
4
11
Lad
y b
ird
bee
tle
0.2
0
0.0
9
0.0
8
0.2
0
0.1
4
0.0
2
0.1
0
0.3
0
0.7
0
0.2
8
0.0
8
0.6
0
0.6
0
0.1
0
0.3
5
0.1
3
12
Can
tho
cona
bu
gs
0.0
3
0.0
0
0.0
1
0.0
1
0.0
1
0.0
0
0.0
0
0.0
1
0.0
1
0.0
1
0.0
1
0.0
0
0.0
0
0.0
1
0.0
1
0.1
0
13
Oth
ers
0.6
0
0.2
1
0.7
0
1.2
0
0.6
8
0.5
9
0.5
9
0.3
5
2.0
0
0.8
8
0.3
6
0.2
7
0.1
6
1.2
0
0.5
0
0.5
5
*M
ean p
opula
tion =
Aver
age
popula
tion o
f eg
g, n
ym
ph/g
rubs/
larv
ae a
nd a
dult
s of
five
farm
er’s
fie
ld i
n f
ive
vil
lages
fro
m e
ach b
lock
55
Fig.
--4.
2aa:
The
dat
a so
win
g di
ffer
ent b
lock
of e
-sur
veill
ance
of U
L, M
L &
LL
of e
nem
ies o
n pa
rthe
nium
and
oth
er a
ssoc
iate
d w
eeds
duri
ngK
harif
– R
abi s
easo
n du
ring
201
6
0
0.51
1.52
2.53
3.54
4.5
UL
ML
LL
Av of enemies pol'n
Land
Ara
ng
Mex
ican
bee
tleAp
hids
Mea
ly b
ugCo
w b
ugHo
pper
sSe
milo
oper
Cate
rpill
ers
Spitt
al b
ugSp
ider
/mite
sAn
tsLa
dy b
ird b
eetle
Cant
hoco
na b
ugO
ther
s0
0.51
1.52
2.53
3.5
UL
ML
LL
Av of enemies pol'n
Land
Dha
rsiw
a M
exic
an b
eetle
Aphi
ds
Mea
ly b
ug
Cow
bug
Hopp
ers
Sem
iloop
er
Cate
rpill
ers
Spitt
al b
ug
Spid
er/m
ites
Ants
Lady
bird
bee
tle
Cant
hoco
na b
ug
Oth
ers
0
0.51
1.52
2.53
3.54
4.5
UL
ML
LL
Av of enemies pol'n
Land
Tild
a M
exic
an b
eetle
Aphi
ds
Mea
ly b
ug
Cow
bug
Hopp
ers
Sem
iloop
er
Cate
rpill
ers
Spitt
al b
ug
Spid
er/m
ites
Ants
Lady
bird
bee
tle
Cant
hoco
na b
ug
Oth
ers
0
0.51
1.52
2.53
3.54
UL
ML
LL
Av of enemies pol'n
Land
Abh
anpu
r M
exic
an b
eetle
Aphi
ds
Mea
ly b
ug
Cow
bug
Hopp
ers
Sem
iloop
er
Cate
rpill
ers
Spitt
al b
ug
Spid
er/m
ites
Ants
Lady
bird
bee
tle
Cant
hoco
na b
ug
Oth
ers
56
Fig.
--4.
2ab:
The
dat
a so
win
g e-
surv
eilla
nce
on p
arth
eniu
m a
nd o
ther
ass
ocia
ted
wee
ds a
t Rai
pur
Dis
tric
t in
Kha
rif –
Rab
i sea
son
duri
ng 2
016
Fig.
--4.
2ac:
The
dat
a so
win
g e-
surv
eilla
nce
of d
iffer
ent e
nem
ies o
f on
part
heni
um a
nd o
ther
ass
ocia
ted
wee
ds a
t Rai
pur
Dis
tric
t dur
ingK
harif
– R
abi s
easo
n du
ring
201
6
0
0.51
1.52
2.53
3.54
UL
ML
LL
Av of enemies pol'n
Land
Rai
pur
Mex
ican
bee
tleAp
hids
Mea
ly b
ugCo
w b
ugHo
pper
sSe
milo
oper
Cate
rpill
ers
Spitt
al b
ugSp
ider
/mite
sAn
tsLa
dy b
ird b
eetle
Cant
hoco
na b
ugO
ther
s
0
0.51
1.52
2.53
3.54
Av of enemies pol'n
Land
Rai
pur
UL
ML
LL
0
0.51
1.52
2.5
Raip
ur D
istr
ict
Av of enemies pol'n
Mex
ican
bee
tle
Aphi
ds
Mea
ly b
ug
Cow
bug
Hopp
ers
Sem
iloop
er
Cate
rpill
ers
Spitt
al b
ug
Spid
er/m
ites
Ants
Lady
bird
bee
tle
Cant
hoco
na b
ug
57
Ta
ble
-4.2
b:
e-s
urv
eill
an
ce o
f p
art
hen
ium
an
d a
sso
cia
ted
in
sects
at
Ra
ipu
r D
istr
icti
n K
ha
rif –
Ra
bi
sea
son
du
rin
g 2
01
7
S.
No
. E
nem
ies/
Blo
ck
U
L
ML
L
L
GM
A
ran
g
Dh
ars
iwa
T
ild
a
Ab
ha
np
ur
Mea
n A
ran
g
Dh
ars
iwa
T
ild
a
Ab
ha
np
ur
Mea
n A
ran
g
Dh
ars
iwa
T
ild
a
Ab
ha
np
ur
Mea
n
1
Mex
ican b
eetl
e 0
.76
0.8
6
0.6
1
1.6
1
0.9
6
1.3
2
1.3
2
0.3
2
1.3
2
1.0
7
1.7
0
0.7
0
2.7
0
3.7
0
2.2
0
1.4
1
2
Ap
hid
s 0
.20
0.3
0
0.2
0
0.2
0
0.2
3
0.0
0
0.0
0
0.1
0
0.1
0
0.0
5
0.0
0
0.1
0
0.0
0
0.6
0
0.1
8
0.1
5
3
Mea
lyb
ug
0
.13
0.0
7
0.0
7
0.6
7
0.2
3
0.4
0
0.3
0
0.3
0
0.4
0
0.3
5
0.0
8
0.0
3
0.3
0
0.5
0
0.2
3
0.2
7
4
Co
wb
ug
0
.06
0.0
6
0.0
6
0.6
1
0.2
0
0.0
2
0.0
2
0.0
2
0.2
0
0.0
7
0.0
0
0.0
0
0.1
0
0.1
0
0.0
5
0.1
0
5
Ho
pp
ers
0.5
2
0.2
0
0.1
1
0.5
1
0.3
4
0.6
0
0.3
0
0.3
0
0.3
0
0.3
8
0.4
7
0.1
7
0.2
7
0.3
7
0.3
2
0.3
4
6
Sem
ilo
op
er
0.4
4
0.3
4
0.2
4
0.1
4
0.2
9
0.0
2
0.0
2
0.0
2
0.2
0
0.0
7
0.0
3
0.0
2
0.2
0
0.9
0
0.2
9
0.2
1
7
Cat
erp
illa
r 0
.00
0.1
0
0.1
0
0.8
0
0.2
5
0.1
2
0.1
2
0.1
2
0.1
0
0.1
2
0.0
8
0.0
8
0.8
0
0.7
0
0.4
2
0.2
6
8
Sp
ittl
e b
ug
s 0
.21
0.0
8
0.0
9
1.0
9
0.3
7
0.0
4
0.0
2
0.0
0
0.3
0
0.0
9
0.0
8
0.0
4
0.3
8
0.3
8
0.2
2
0.2
2
9
Sp
ider
/mit
es
0.7
9
0.6
9
0.7
9
0.7
1
0.7
4
1.8
5
0.8
5
0.9
5
1.9
5
1.4
0
0.4
8
0.3
8
0.4
8
0.5
8
0.4
8
0.8
8
10
Ants
2
.87
1.8
7
2.8
7
2.8
8
2.6
2
1.8
6
1.8
6
1.7
6
2.7
6
2.0
6
2.3
3
1.3
3
1.7
3
2.7
3
2.0
3
2.2
4
11
Lad
y b
ird
bee
tle
0.1
0
0.1
0
0.0
9
0.0
2
0.0
8
0.2
0
0.1
0
0.0
0
0.7
0
0.2
5
0.0
8
0.0
6
0.0
6
0.0
0
0.0
5
0.1
3
12
Can
tho
cona
bu
gs
0.0
4
0.0
1
0.0
0
0.0
0
0.0
1
0.0
0
0.0
0
0.1
0
0.1
0
0.0
5
0.0
0
0.0
0
0.0
0
1.0
0
0.2
5
0.1
0
13
Oth
ers
0.5
8
0.0
8
0.8
0
1.0
0
0.6
2
0.4
6
0.3
6
0.3
5
1.0
0
0.5
4
0.2
6
0.2
7
0.2
6
1.2
0
0.5
0
0.5
5
To
tal
6.6
9
4.7
5
6.0
2
10
.23
6.9
2
6.8
9
5.2
7
4.3
4
9.4
3
6.4
8
5.5
9
3.1
8
7.2
8
12
.76
7.2
1
6.8
7
*M
ean p
opula
tion =
Aver
age
popula
tion o
f eg
g, n
ym
ph/g
rubs/
larv
ae a
nd a
dult
s of
five
farm
er’s
fie
ld i
n f
ive
vil
lages
fro
m e
ach b
lock
58
Fig.
--4.
2ba:
The
dat
a so
win
g di
ffer
ent b
lock
of e
-sur
veill
ance
of U
L, M
L &
LL
of e
nem
ies o
n pa
rthe
nium
and
oth
er a
ssoc
iate
d w
eeds
dur
ingK
harif
– R
abi s
easo
n du
ring
201
7
0
0.51
1.52
2.53
3.5
UL
ML
LL
Av of enemies pol'n
Land
Ara
ng
Mex
ican
bee
tleAp
hids
Mea
ly b
ugCo
w b
ugHo
pper
sSe
milo
oper
Cate
rpill
ers
Spitt
al b
ugSp
ider
/mite
sAn
tsLa
dy b
ird b
eetle
Cant
hoco
na b
ugO
ther
s0
0.2
0.4
0.6
0.81
1.2
1.4
1.6
1.82
UL
ML
LL
Av of enemies pol'n
Land
Dha
rsiw
a M
exic
an b
eetle
Aphi
ds
Mea
ly b
ug
Cow
bug
Hopp
ers
Sem
iloop
er
Cate
rpill
ers
Spitt
al b
ug
Spid
er/m
ites
Ants
Lady
bird
bee
tle
Cant
hoco
na b
ug
Oth
ers
0
0.51
1.52
2.53
3.5
UL
ML
LL
Av of enemies pol'n
Land
Tild
a M
exic
an b
eetle
Aphi
ds
Mea
ly b
ug
Cow
bug
Hopp
ers
Sem
iloop
er
Cate
rpill
ers
Spitt
al b
ug
Spid
er/m
ites
Ants
Lady
bird
bee
tle
Cant
hoco
na b
ug
Oth
ers
0
0.51
1.52
2.53
3.54
UL
ML
LL
Av of enemies pol'n
Land
Abh
anpu
r M
exic
an b
eetle
Aphi
ds
Mea
ly b
ug
Cow
bug
Hopp
ers
Sem
iloop
er
Cate
rpill
ers
Spitt
al b
ug
Spid
er/m
ites
Ants
Lady
bird
bee
tle
Cant
hoco
na b
ug
Oth
ers
59
Fig.
--4.
2bb:
The
dat
a so
win
g e-
surv
eilla
nce
on p
arth
eniu
m a
nd o
ther
ass
ocia
ted
wee
ds a
t Rai
pur
Dis
tric
t in
Kha
rif –
Rab
i sea
son
duri
ng 2
017
Fig.
--4.
2bc:
The
dat
a so
win
g e-
surv
eilla
nce
of d
iffer
ent e
nem
ies o
f on
part
heni
um a
nd o
ther
ass
ocia
ted
wee
ds a
t Rai
pur
Dis
tric
t dur
ingK
harif
– R
abi s
easo
n du
ring
201
7
0
0.51
1.52
2.53
UL
ML
LL
Av of enemies pol'n
Land
Rai
pur
Mex
ican
bee
tleAp
hids
Mea
ly b
ugCo
w b
ugHo
pper
sSe
milo
oper
Cate
rpill
ers
Spitt
al b
ugSp
ider
/mite
sAn
tsLa
dy b
ird b
eetle
Cant
hoco
na b
ugO
ther
s
0
0.51
1.52
2.53
3.5
Av of enemies pol'n
Land
Rai
pur
UL
ML
LL
0
0.51
1.52
2.53
Aran
gDh
arsiw
aTi
lda
Abha
npur
Av of enemies pol'n
Land
Rai
pur
Mex
ican
bee
tle
Aphi
ds
Mea
ly b
ug
Cow
bug
Hopp
ers
Sem
iloop
er
Cate
rpill
ers
Spitt
al b
ug
Spid
er/m
ites
Ants
Lady
bird
bee
tle
Cant
hoco
na b
ug
Oth
ers
60
Tab
le-4
.1c:
Po
ole
d m
ean
of
e-su
rvei
llan
ce o
f p
art
hen
ium
an
d a
ssoci
ate
d i
nse
cts
at
Raip
ur
Dis
tric
t in
Kh
ari
f –
Ra
bis
easo
n d
uri
ng
20
16
an
d 2
01
7
S.
No
. E
nem
ies/
Blo
ck
U
L
ML
L
L
GM
A
ran
g
Dh
ars
iwa
T
ild
a A
bh
an
pu
r
Mea
n A
ran
g D
ha
rsiw
a T
ild
a A
bh
an
pu
r
Mea
n A
ran
g D
ha
rsiw
a T
ild
a A
bh
an
pu
r
Mea
n
1
Mex
ican b
eetl
e 0
.78
0.8
4
0.6
3
1.7
3
1.0
0
1.3
7
1.3
7
0.3
6
1.3
6
1.1
1
2.2
0
1.2
0
2.7
0
3.7
5
2.4
6 1
.52
2
Ap
hid
s 0
.15
0.6
0
0.1
5
0.1
5
0.2
6
0.0
0
0.0
0
0.1
0
0.1
0
0.0
5
0.0
0
0.1
0
0.3
5
0.6
0
0.2
6 0
.19
3
Mea
ly b
ugs
0.1
6
0.0
5
0.0
7
0.6
6
0.2
4
0.2
5
0.2
5
0.2
5
0.3
5
0.2
8
0.0
8
0.0
2
0.2
5
0.4
5
0.2
0 0
.24
4
Co
w b
ug
s 0
.06
0.0
6
0.0
6
0.4
6
0.1
6
0.0
2
0.0
3
0.0
2
0.2
0
0.0
7
0.0
1
0.0
0
0.1
0
0.1
1
0.0
5 0
.09
5
Ho
pp
ers
0.4
6
0.2
1
0.1
6
0.5
6
0.3
5
0.5
5
0.3
0
0.2
5
0.3
5
0.3
6
0.5
2
0.2
2
0.2
7
0.4
2
0.3
6 0
.36
6
Sem
ilo
op
er
0.4
2
0.3
4
0.1
9
0.1
2
0.2
7
0.0
2
0.0
2
0.0
2
0.1
5
0.0
5
0.0
4
0.0
2
0.1
5
0.8
0
0.2
5 0
.19
7
Cat
erp
illa
r 0
.01
0.1
1
0.1
1
0.6
0
0.2
0
0.1
1
0.1
2
0.1
4
0.1
4
0.1
3
0.4
4
0.1
3
0.4
4
0.7
0
0.4
3 0
.25
8
Sp
ittl
e b
ug
s 0
.21
0.0
9
0.0
5
1.0
0
0.3
3
0.0
6
0.0
2
0.0
5
0.3
0
0.1
1
0.0
7
0.0
4
0.2
8
0.3
3
0.1
8 0
.21
9
Sp
ider
/mit
es
0.8
4
0.7
4
0.8
4
0.7
6
0.7
9
2.3
5
1.3
5
1.4
5
2.4
5
1.9
0
0.9
8
0.8
8
0.9
8
1.0
8
0.9
8 1
.23
10
Ants
3
.37
2.3
7
3.3
7
3.3
8
3.1
2
2.3
6
2.3
6
1.7
6
3.2
6
2.4
4
2.3
3
1.2
8
1.7
8
3.2
3
2.1
6 2
.57
11
Lad
y b
ird
bee
tle
0.1
5
0.1
0
0.0
9
0.1
1
0.1
1
0.1
1
0.1
0
0.1
5
0.7
0
0.2
7
0.0
8
0.3
3
0.3
3
0.0
5
0.2
0 0
.19
12
Can
tho
cona
bu
gs
0.0
4
0.0
1
0.0
1
0.0
1
0.0
1
0.0
0
0.0
0
0.0
6
0.0
6
0.0
3
0.0
1
0.0
0
0.0
0
0.5
1
0.1
3 0
.06
13
Oth
ers
0.5
9
0.1
5
0.7
5
6.5
0
2.0
0
0.5
2
0.4
7
0.3
5
1.5
0
0.7
1
0.3
1
0.2
7
0.2
1
1.2
0
0.5
0 1
.07
To
tal
6.6
9
7.2
2
5.6
4
6.4
6 1
6.0
3
8.8
4
7.7
3
6.3
8
4.9
5 1
0.9
1
7.4
9
7.0
6
4.5
0
7.8
4 1
3.2
2 8
.15
*M
ean p
opula
tion =
Aver
age
popula
tion o
f eg
g, n
ym
ph/g
rubs/
larv
ae a
nd a
dult
s of
five
farm
er’s
fie
ld i
n f
ive
vil
lages
fro
m e
ach b
lock
61
Fig.
--4.
2ca:
The
poo
led
data
sow
ing
diff
eren
t blo
ck o
f e-s
urve
illan
ce o
f UL
, ML
& L
L o
f ene
mie
s on
part
heni
um a
nd o
ther
ass
ocia
ted
wee
ds d
urin
g Kh
arif –
Rabi
seas
on d
urin
g 20
16&
17
0
0.51
1.52
2.53
3.54
UL
ML
LL
Av of enemies pol'n
Land
Ara
ng
Mex
ican
bee
tleAp
hids
Mea
ly b
ugCo
w b
ugHo
pper
sSe
milo
oper
Cate
rpill
ers
Spitt
al b
ugSp
ider
/mite
sAn
tsLa
dy b
ird b
eetle
Cant
hoco
na b
ugO
ther
s0
0.51
1.52
2.5
UL
ML
LL
Av of enemies pol'n
Land
Dha
rsiw
a M
exic
an b
eetle
Aphi
ds
Mea
ly b
ug
Cow
bug
Hopp
ers
Sem
iloop
er
Cate
rpill
ers
Spitt
al b
ug
Spid
er/m
ites
Ants
Lady
bird
bee
tle
Cant
hoco
na b
ug
Oth
ers
0
0.51
1.52
2.53
3.54
UL
ML
LL
Av of enemies pol'n
Land
Tild
a M
exic
an b
eetle
Aphi
ds
Mea
ly b
ug
Cow
bug
Hopp
ers
Sem
iloop
er
Cate
rpill
ers
Spitt
al b
ug
Spid
er/m
ites
Ants
Lady
bird
bee
tle
Cant
hoco
na b
ug
Oth
ers
01234567
UL
ML
LL
Av of enemies pol'n
Land
Abh
anpu
r M
exic
an b
eetle
Aphi
ds
Mea
ly b
ug
Cow
bug
Hopp
ers
Sem
iloop
er
Cate
rpill
ers
Spitt
al b
ug
Spid
er/m
ites
Ants
Lady
bird
bee
tle
Cant
hoco
na b
ug
Oth
ers
62
Fig.
--4.
2cb:
The
poo
led
data
sow
ing
e-su
rvei
llanc
e on
par
then
ium
and
oth
er a
ssoc
iate
d w
eeds
at R
aipu
r D
istr
ict i
n Kh
arif –
Rabi
seas
on d
urin
g 20
16&
17
Fig.
--4.
2cc:
The
poo
led
data
sow
ing
e-su
rvei
llanc
e of
diff
eren
t ene
mie
s of o
n pa
rthe
nium
and
oth
er a
ssoc
iate
d w
eeds
at R
aipu
r D
istr
ict d
urin
gKha
rif –
Rab
i sea
son
duri
ng 2
016&
17
0
0.51
1.52
2.53
3.5
UL
ML
LL
Av of enemies pol'n
Land
Rai
pur
Mex
ican
bee
tleAp
hids
Mea
ly b
ugCo
w b
ugHo
pper
sSe
milo
oper
Cate
rpill
ers
Spitt
al b
ugSp
ider
/mite
sAn
tsLa
dy b
ird b
eetle
Cant
hoco
na b
ugO
ther
s
0
0.51
1.52
2.53
3.5
Av of enemies pol'n
Land
Rai
pur
UL
ML
LL
0
0.51
1.52
2.53
Raip
ur D
istr
ict
Av of enemies popul'n
Mex
ican
bee
tle
Aphi
ds
Mea
ly b
ug
Cow
bug
Hopp
ers
Sem
iloop
er
Cate
rpill
ers
Spitt
al b
ug
Spid
er/m
ites
Ants
Lady
bird
bee
tle
63
(0.03) /sqm in cow bugs while maximum (2.46)/sqm was recorded in Mexican
beetle and minimum in (0.05)/sqm in cow bugs.
The data of overall Raipur District of upland, midland and lowland ranged
from 0.06 to 2.57. The maximum population was exhibited (2.57) /sqm in ants and
minimum in (0.06) /sqm in Canthocona bugs while compared with the Mexican
beetle was noticed maximum (2.46) /sqm.
Similar findings were reported by Kulkarni and Kulkarni (2000) who studied
on P. hysterophorus plants in 20 locations in north Karnataka, India, for the
presence of Z. bicolorata and found that the densest population of beetles was
observed in Dharwad (10.4 beetles/plant), followed by Bijapur (5.6 beetles/plant)
and Raichur (3.2 beetles/plant). The beetle population is in line with the population
recorded at Raichur,Karnataka.
Bennett (1977) and Kumar, et al., 1979 , reported larvae and adults of the
stem-boring scolytid, Hypothenemus eruditus (Westw.) causing widespread
wilting of the weed, leading to good natural control and also a cerambycid borer,
Oberea sp. was also found to kill the plant, however both were not recorded in the
present studies from Raipur district of Chhattisgarh.
4.2.4: Associated weeds with Parthenium and their insect-pests recorded
during 2016-17 at Raipur district
Studies conducted on associated weeds with Parthenium in different blocks
of Raipur district, resulted thirty seven weed species. Insect pests associated with
weeds recorded during Kharif and Rabi season of 2016 and 2017, revealed that
sucking pests such as aphids, hoppers dominated the weeds; followed by caterpillar
and mealy bugs. Maximum population of aphids were recorded on Latjira,
Achyranthe saspera L., Kantedarchauli, Amaranthus spinosus L., Choulai,
Amaranthus virdis L., Satyanashi, Argemone maxicana L., Aak/madar, Calotropis
gigantean L., Silyari, Celosia argentea L., Bathua, Chenopodium album L.,
Scorpion weed, Heliotropium indicum L., Gunima, Leucas aspera L., Chirpoti,
Physallis minima L. and Gokhru, Xanthium strumarium L.; Hoppers, were
recorded with nine weed species namely Sawa, Echinochloa colona L., T grass,
Paspalum conjugatum P., Baru, Sorghum halepense L., Motha, Cyperus difformis
L., Kantedarchauli, Amaranthus spinosus L., Aak/madar, Calotropis gigantean L.,
64
Charota, Cassia tora L. and Gokhru, Xanthium strumarium L.; Mealy bugs were
recorded on five weed species viz; Aak/madar, Calotropis gigantean L., Scorpion
weed, Heliotropium indicum L., Pignut, Hyptissu aveolens L., Ramphul/Barmsiya,
Lantana camara L., Gokhru, Xanthium strumarium L.; Ants were found associated
with the above sucking pests to consume the honey dew secreted by these insects.
Apart from these, few semiloopers and spiders were also observed. Among
predators, Coccinellid beetles and Canthocona bugs were also observed.
Exploiting insect pests for eco-friendly management of invasive and locally
associated weeds is being done all over the world (Heimpel and Mills, 2017) thus
reducing the need for pesticides including India. The present study recorded thirty
seven weed species, on which a number of insect pests were noticed viz; sucking
pests such as aphids, hoppers and mealy bugs, along with few caterpillars and
semiloopers. These insects can be studied in further details and can be useful tools
in weed management.
65
Tab
le-4
.2d
: In
sect
-pes
t re
port
ed o
n o
ther
ass
oci
ate
d w
eed
s w
ith
pa
rth
eniu
m a
t d
iffe
ren
t b
lock
of
Ra
ipu
r D
istr
ict
in K
ha
rif –
Ra
bi
sea
son
du
rin
g 2
016
-17
S.
No.
N
am
e of
ass
oci
ate
d w
eed
s In
sect
-pes
ts
Mex
ican
b
eetl
e
Ap
hid
s M
ealy
b
ug
C
ow
b
ug
H
op
per
s S
em
iloo
per
C
ate
rp
illa
r
Sp
ittl
e
bu
gs
Sp
ider/
m
ites
A
nts
L
ad
y b
ird
b
eetl
e
Can
thoco
na
bu
g
Oth
ers
Loca
l n
am
e
Bota
nic
al
na
me
1
2
3
4
5
6
7
8
9
10
11
12
13
1
Vip
er g
rass
D
ineb
rare
tro
fle
xa V
ahl.
x
x
x
x
x
x
x
x
x
x
x
2
S
aw
a
Ech
ino
chlo
a c
olo
na
L.
x
x
x
x
x
x
x
x
x
x
3
Bad
asaw
a
Ech
ino
chlo
a c
rusg
all
L.
x
x
x
x
x
x
x
x
x
4
Gan
tegaw
ta
Het
ero
po
go
n c
on
tort
us
L.
x
x
x
x
x
x
x
x
x
x
x
x
x
5
Bla
dy g
rass
Im
per
ata
cyl
ind
rica
L.
x
x
x
x
x
x
x
x
x
x
x
6
Bad
auri
Is
cha
emu
m r
ug
osu
m S
ali.
x
x
x
x
x
x
x
x
x
x
x
x
7
T g
rass
P
asp
alu
mco
nju
ga
tum
P.
x
x
x
x
x
x
x
x
x
x
x
8
Bea
rd g
rass
P
oly
po
go
n m
on
spel
ien
sis
L.
x
x
x
x
x
x
x
x
x
x
x
x
9
Bar
u
So
rgh
um
ha
lep
ense
L.
x
x
x
x
x
x
x
x
1
0
Chri
stm
as g
rass
T
hem
eda
arg
uen
s L
. x
x
x
x
x
x
x
x
x
x
x
x
x
11
Sw
eet
signal
gra
ss
Uro
chlo
a p
lati
gin
ea
x
x
x
x
x
x
x
x
x
x
x
12
Mo
tha
Cyp
eru
s d
iffo
rmis
L.
x
x
x
x
x
x
x
x
x
x
x
x
13
Lat
jira
A
chyr
an
thes
asp
era
L.
x
x
x
x
x
x
x
x
x
x
x
14
Mah
akw
a
Ag
era
tum
co
nyz
oid
es L
. x
x
x
x
x
x
x
x
x
x
x
1
5
Kan
ted
arch
auli
A
ma
ran
thu
s sp
ino
sus
L.
x
x
x
x
x
x
x
x
x
16
Cho
ula
i A
ma
ran
thu
s vi
rdis
L.
x
x
x
x
x
x
x
x
x
17
Sat
yanas
hi
Arg
emo
ne
ma
xica
na
L.
x
x
x
x
x
x
x
x
x
x
18
Ku
kurm
uta
B
lum
eala
cera
x
x
x
x
x
x
x
x
x
x
x
x
19
Aak/m
adar
C
alo
tro
pis
gig
an
tea
n L
. x
x
x
20
Phug
gab
ail
Ca
rdio
sper
mu
m h
ali
caca
bu
m L
. x
x
x
x
x
x
x
x
x
x
x
x
x
21
Char
ota
C
ass
ia t
ora
L.
x
x
x
x
x
x
x
x
x
2
2
Sil
yar
i C
elo
sia
a
rgen
tea
L.
x
x
x
x
x
x
x
x
2
3
Asi
atic
pen
ny
wo
rt
Cen
tell
a a
sia
tica
L.
x
x
x
x
x
x
x
x
x
x
2
4
Bat
hua
Ch
eno
po
diu
m a
lbu
m L
. x
x
x
x
x
x
x
x
x
x
x
25
Kan
kau
a/K
ena
Co
mm
elin
a b
eng
ha
len
sis
L.
x
x
x
x
x
x
x
x
x
x
x
x
x
26
Mac
hhar
ia
Co
rch
oru
s a
estu
an
s L
. x
x
x
x
x
x
x
x
x
x
x
x
x
27
Til
iace
ae
Co
rch
oru
s o
lito
riu
s L
. x
x
x
x
x
x
x
x
x
x
x
x
x
28
Am
arb
el
Cu
scu
ta c
hin
ensi
s Y
un.
x
x
x
x
x
x
x
x
x
x
x
x
x
29
Bad
idud
hi
Eu
ph
orb
ia g
enic
ula
ta O
rt
x
x
x
x
x
x
x
x
x
x
x
x
x
30
Cho
tid
ud
hi
Eu
ph
orb
ia h
irta
Ort
x
x
x
x
x
x
x
x
x
x
x
31
Sco
rpio
n w
eed
H
elio
tro
piu
m i
nd
icu
m L
. x
x
x
x
x
x
x
x
x
x
x
32
Pig
nut
Hyp
tis
sua
veo
len
s L
. x
x
x
x
x
x
x
x
x
x
33
Ram
phu
l/B
arm
siya L
an
tan
a c
am
ara
L.
x
x
x
x
x
x
x
x
x
3
4
Gu
nim
a
Leu
cas
asp
era
L.
x
x
x
x
x
x
x
x
x
x
35
Chir
po
ti
Ph
ysa
llis
min
ima
L.
x
x
x
x
x
x
x
x
x
x
x
36
Pat
har
-Chat
a
Tri
an
them
a p
ort
ula
cast
rum
L.
x
x
x
x
x
x
x
x
x
x
x
x
37
Go
khru
X
an
thiu
m s
tru
ma
riu
mL
. x
x
x
x
x
x
66
4.3: To work out the feeding potential of Mexican beetle, Zygogramma
bicolorata P. under laboratory conditions
4.3.1: Feeding potential of Mexican beetle, Z. bicolorata P.
To test the feeding potential of Mexican beetle, Z. bicolorata, different
numbers of beetles i.e. 2, 3, 4 and 5 pairs were released on three different stages of
host plant (early stage, pre-reproductive and reproductive) of Parthenium grass.
Observations were recorded on every alternate day for the number of insects
established, mortality and time taken (number of days) for complete defoliation of
plant at each stage are presented in table-4.3.1.a & 4.3.1.b and fig.-4.3.1.a &4.3.1.b
as follows:
4.3.1.1: Early stage
Results of the experiments conducted in the first year i.e. during 2016, all the
treatments showed significant differences between each other. Maximum time
taken for complete defoliation was (6.6 days) by two pairs followed by (5.66 days)
by three pairs while minimum time taken was (2.00 days) by five pairs.
During second year, the maximum time taken for complete defoliation was
(7.33 days) by two pairs followed by (4.33 days) three pairs whereas, minimum
time taken was (1.33 days) by five pairs.
4.3.1.2: Pre-reproductive
During 2016, testing of the feeding efficiency of Z. bicolorata at pre-
reproductive age of host plants revealed maximum time taken (11.00 days) for
complete defoliation by two pairs followed by (8.66) in three pairs while minimum
time taken was (3.33 days) by five pairs of beetles.
During 2017, the maximum time taken was (11.33 days) for complete
defoliation by two pairs followed by (10.33 days) in three pairs whereas, minimum
time taken was (4.66 days) by five pairs of beetles. The results of these
experiments were significantly superior with overall treatments.
4.3.1.3: Reproductive
During 2016, the feeding efficiency of Z. bicolorata at reproductive age of
host plants depicted maximum time taken (14.33 days) for complete defoliation by
67
4.3
.1a:
Tim
e ta
ken
(d
ays)
by
Mex
ican
bee
tle,
Zyg
ogra
mm
a b
icolo
rata
P. fo
r co
mp
lete
def
oli
ati
on
by d
iffe
ren
t n
um
ber
of
bee
tles
rele
ase
s p
er
pla
nt
un
der
lab
ora
tory
con
dit
ion
sdu
rin
g 2
016&
2017
S. N
o.
Tre
atm
ents
E
arl
y s
tage
Pre-
rep
rod
uct
ive
R
epro
du
ctiv
e
GT
2016
2017
Mea
n
2016
2017
Mea
n
2016
2017
Mea
n
1
Tw
o p
air
s 6.6
6
(2.6
8)
7.3
3
(2.8
0)
7.0
0
11.0
0
(3.3
9)
11.3
3
(3.4
4)
11.1
7
14.3
3
(3.8
5)
15.3
3
(2.9
8)
14.8
3
11.0
0
2
Th
ree
pair
s 5.6
6
(2.4
8)
4.3
3
(2.2
0)
5.0
0
8.6
6
(3.0
3)
10.3
3
(3.2
9)
9.5
0
12.3
3
(3.5
8)
13.6
6
(3.7
6)
13.0
0
9.1
7
3
Fou
r p
air
s 3.6
6
(2.0
4)
3.3
3
(1.9
6)
3.5
0
6.3
3
(2.6
1)
5.3
3
(2.4
1)
5.8
3
8.6
6
(3.0
3)
9.3
3
(3.1
4)
9.0
0
6.1
1
4
Fiv
e p
air
s 2.0
0
(1.5
8)
1.3
3
(1.3
5)
1.6
7
3.3
3
(1.9
6)
4.6
6
(2.2
7)
4.0
0
5.0
0
(2.3
5)
5.3
3
(2.4
1)
5.1
7
3.6
1
Tota
l 17.9
8
16.3
2
17.1
5
29.3
2
31.6
5
30.4
9
40.3
2
43.6
5
41.9
9
29.8
9
SE
M
CD
@ 5
%
CV
(%
)
0.4
08
0.7
43
15.7
13
0.3
33
0.6
06
13.8
56
0.6
45
1.1
74
15.2
46
0.5
27
0.9
59
11.5
31
0.5
00
0.9
10
8.5
89
0.5
27
0.9
59
8.3
62
*D
ata
in p
aren
thes
is s
ho
ws
squ
are
roo
t tr
ansf
orm
atio
n
*T
he
dat
a sh
ow
s A
v.
of
thre
e re
pli
cati
ons
4.3
.1b
: T
he
mea
n h
eigh
t an
d n
um
ber
of
leaves
per
Pa
rth
eniu
m p
lan
t at
dif
fere
nt
pla
nt
stages
.
* D
ata
sh
ow
s m
ean
of
two y
ears
S. N
o.
Pla
nt
stages
M
ean
pla
nt
hei
gh
t (c
m)
Mea
n n
um
ber
of
leaves
/pla
nt
1
Ear
ly s
tage
19.3
3
7.3
3
2
Pre
-rep
roduct
ive
34.6
6
18.6
6
3
Rep
roduct
ive
54.7
0
32.3
3
68
Fig.-4.3.1.a: The mean day’s data sowing feeding potential of Mexican beetle, Zygogramma bicolorata P. under laboratory conditionsduring 2016&2017
0
2
4
6
8
2016 2017 Mean
Early stage
Av o
f day
Two pairs Three pairs Four pairs Five pairs
0
2
4
6
8
10
12
2016 2017 Mean
Pre-reproductive
Av o
f day
Two pairs Three pairs Four pairs Five pairs
02468
10121416
2016 2017 Mean
Reproductive
Av o
f day
Two pairs Three pairs Four pairs Five pairs
69
Fig.
-4.3
.1.b
: T
he p
oole
d m
ean
of t
he f
eedi
ng p
oten
tial o
f di
ffer
ent
num
ber
of M
exic
an b
eetle
on
diff
eren
t ag
e of
Par
then
ium
w
eeds
dur
ing
2016
&20
17
0.00
2.00
4.00
6.00
8.00
10.0
0
12.0
0
Two
pairs
Thre
e pa
irsFo
ur p
airs
Five
pai
rs
Av of days
Mex
ican
bee
tles
70
two pairs followed by (12.33 days) in three pairs while minimum time taken was
(5.00 days) by five pairs.
During 2017, the maximum time taken (15.33 days) for complete defoliation
by two pairs followed by (13.66 days) in three pairs whereas, minimum time taken
(5.33 days) by five pairs. The results of these experiments significantly superior
to overall treatments.
On the basis of overall mean days of two years data indicated that feeding
efficiency of Z. bicolorata on different age of host plant i.e. early stage, pre-
reproductive and reproductive treatments were significantly superior. The highest
time taken (14.83 days) for complete defoliation by two pairs of beetles followed
by (13.00 days) by three pairs whereas, minimum time was taken by five pairs of
Mexican beetle (5.17 days) for complete defoliation.
4.3.2: Food consumption by adult & grubs Mexican beetle, Z. bicolorata P.
The different stages of beetles i.e. first, second, third, fourth instars and
adults were released on host plant in different petri dishes. Observations were
recorded on the quantity of food eaten by different life stages of Z. bicolorata
within 24hrs as per the data presented in table-4.3.2a and fig.-4.3.2a the all the
treatments showed significant differences among each other. In the first year, food
consumption of Z. bicolorata was maximum (11.01mg) by third instar grubs
followed by fourth instar (8.10mg) and minimum food was consumed by adult
stage (0.73mg); similar mode of feeding was observed during 2017, also in which
the highest amount of food consumed was by third instar grubs (11.04mg).
followed by fourth instar (7.77mg) and minimum by adults (0.75mg).
Overall two years data indicated that food consumption of Z. bicolorata was
maximum (11.03mg) by third instar grubs followed by fourth instar (7.94mg) and
minimum by adults (0.74mg).
71
4.3
.2a:
Food
con
sum
pti
on
by d
iffe
ren
t st
ages
of
Mex
ican
bee
tle,
Zyg
ogra
mm
a b
icolo
rata
P. w
ith
in 2
4h
rs (
in m
g)
un
der
lab
ora
tory
con
dit
ion
sdu
rin
g 2
016&
2017
S. N
o.
Lif
e st
age
Food
con
sum
pti
on
by g
rub
s &
ad
ult
wit
hin
24h
rs (i
n m
g)
2016
2017
Mea
n
1
I-in
star
2.5
0
(1.7
3)
2.4
7
(1.7
2)
2.4
8
2
II-I
nst
ar
5.2
0
(2.3
9)
5.2
3
(2.3
9)
5.2
2
3
III-
Inst
ar
11.0
1
(3.3
9)
11.0
4
(3.4
0)
11.0
3
4
IV-I
nst
ar
8.1
0
(2.9
3)
7.7
7
(2.8
8)
7.9
4
5
Adult
s 0.7
3
(1.1
1)
0.7
5
(1.1
2)
0.7
4
Tota
l 27.5
4
27.2
6
27.4
0
SE
M
CD
@ 5
%
CV
(%
)
0.0
78
0.1
38
2.4
52
0.1
47
0
.26
0
4.6
78
* D
ata
in p
aren
thes
is s
ho
ws
squ
are
root
tran
sform
atio
n
*T
he
dat
a sh
ow
s A
v.
of
thre
e re
pli
cati
ons
72
Fig.
-4.3
.2:
The
dat
a so
win
g fo
od c
onsu
mpt
ion
by M
exic
an b
eetle
, Zyg
ogra
mm
a bi
colo
rata
P. w
ithin
24h
rs (
in m
g) u
nder
labo
rato
ry
cond
ition
sdur
ing
2016
&20
17
024681012
2016
2017
Mea
n
Food consumption (in mg)
Year
s
I-ins
tar
II-In
star
III-In
star
IV-In
star
Adul
ts
73
4.4: To study the bionomics of Mexican beetle, Zygogramma bicolorata P.
under laboratory conditions
Studies on the bionomics of the Mexican beetle, Z. bicolorata P.was
conducted under laboratory conditions in the Bio-control laboratory, Department
of entomology, CoA, IGKV, Raipur. In this experiment the fresh leaves of
Parthenium were provided in petridish along with single pair of newly emerged Z.
bicolorata beetles. Observations were recorded on fecundity, incubation period and
duration of larval (grub) instars, pupal and longevity of male and female beetles
are presented in table-4.4a & 4.4b and fig.- 4.4a & 4.4b the female Z. bicolorata
as recorded under laboratory conditions showed that it laid eggs either singly or in
groups ranging from 5.83 to 29.33 eggs on leaves, flower, stem and buds of
Parthenium with an average of 18.85 eggs. The eggs were yellowish orange in
colour. The incubation period was in between 4.00 to 6.00 days with an average of
5.08 days. Mean number of hatching eggs ranged from 5.33 to 27.33 with an
average of 17.36 while average per cent of egg hatching was 73.71%. There were
four larval instars (grubs) i.e. first, second, third and fourth instars with an average
larval duration extending from 3.00 to 6.00 days for different stages of grubs. The
duration of larval period was 3.00 days for first instar, 4.67 days for second instar,
5.17 days for third instar and 6.00 days for fourth instars with an overall average
larval duration of 18.83 days while pupation period lasted 8.67 days and the adult
longevity was observed to be of 81.7 days.
The results on the development of the beetle on Parthenium leaves were in
agreement with (Pandey et al., 2001) who reported grub, pupal and total
developmental period to be 13, 10 and 29 days, respectively, while Jayanth and
Geetha Bali (1997) observed the periods to be 4-6, 14-16, 8-10 and 28-30 days,
respectively. Adult longevity was 120 days and the fecundity was 65 eggs per day.
Bali (1993 a) recorded 45 eggs per day. Eggs were yellow or orange in colour
which hatched in 6-7 days in July and August and in 8-10 days in October and
March with an average of 7 days Pandey et al. (2001) recorded it as 4 days while
Jayanth and Bali (1993 a) reported it as 5 days. This variation in egg number laid
per day may be due to climatic factors or due to single or multi time copulation.
Maximum number of damaged eggs in natural condition was recorded in June,
74
perhaps due to dehydration. Hatching percentage is highest in the month of April
and July. A group of 5 male and 5 female can lay 1500 eggs or more in 15 days.
This indicates the magnitude of reproductive power, which is a positive point for
the control of the weed. According to Pandey et al. (2001) the pre pupae burried
themselves only upto 1-3 cms deep in soil, for pupation. Pupation period normally
lasts for 10-12 days but it may be increased to 15-20 days in summer (June) and
winter (November) This increased longevity may be attributed due to climatic
change.
75
4.4
a:
Det
ail
s of
egg r
ela
ted
to M
exic
an
bee
tle,
Zyg
ogra
mm
a b
icolo
rata
P.u
nd
er l
ab
ora
tory
con
dit
ion
sdu
rin
g 2
016&
2017
S. N
o.
Date
A
v e
gg
(No.)
D
ate
M
ean
in
cub
ati
on
per
iod
(days)
M
ean
nu
mb
er o
f eg
g h
atc
hin
g
Mea
n e
gg h
atc
hin
g (
%)
1
01-0
7-1
7
15.6
7
05-0
7-1
7
4.0
0
13.5
0
72.2
2
2
03-0
7-1
7
29.3
3
08-0
7-1
7
5.0
0
27.0
0
91.1
3
3
04-0
7-1
7
5.8
3
09-0
7-1
7
5.0
0
5.3
3
47.3
7
4
05-0
7-1
7
13.1
7
10-0
7-1
7
5.0
0
12.3
3
78.9
3
5
06-0
7-1
7
20.8
3
11-0
7-1
7
5.0
0
18.5
0
74.1
3
6
07-0
7-1
7
20.1
7
12/0
7/1
7
6.0
0
18.6
7
95.0
1
7
08-0
7-1
7
10.1
7
13/0
7/1
7
5.0
0
9.5
0
31.9
1
8
09-0
7-1
7
30.0
0
14/0
7/1
7
5.0
0
27.3
3
92.2
4
9
10-0
7-1
7
15.5
0
15/0
7/1
7
5.0
0
14.5
0
79.4
8
10
11-0
7-1
7
25.0
0
17/0
7/1
7
6.0
0
23.1
7
78.4
6
11
13-0
7-1
7
20.5
0
18/0
7/1
7
5.0
0
18.5
0
60.3
2
12
15-0
7-1
7
20.0
0
20/0
7/1
7
5.0
0
20.0
0
83.3
3
Av
18.8
5
Av 5
.08
17.3
6
73.7
1
*D
ata
sho
ws
mea
n o
f si
x r
epli
cati
ons
76
Fig.
-4.4
a: T
he f
igur
e sh
owin
g av
erag
e nu
mbe
r of
egg
s, in
cuba
tion
peri
od,
hatc
hing
num
ber
and
hatc
hing
per
cent
age
of M
exic
an b
eetle
,
Zygo
gram
ma
bico
lora
ta P
.und
er la
bora
tory
con
ditio
ns d
urin
g 20
16&
2017
0102030405060708090100
05101520253035
12
34
56
78
910
1112
Av per cent
No.of days
Av e
gg (N
o.)
Av in
cuba
tion
perio
d(da
ys)
Av e
gg h
atch
ing(
No.
)Av
egg
hat
chin
g (%
)
77
4.4
b:
Bio
nom
ics
of
the
dif
fere
nt
life
sta
ges
of
Mex
ican
bee
tle,
Z.
bic
olo
rata
un
der
lab
ora
tory
con
dit
ion
s d
uri
ng 2
016&
2017
S. N
o.
Inse
ct l
ife
stage
Av s
ize
(in
mm
) M
ean
(d
ays)
L
ength
W
idth
1
Fec
undit
y
- 226.1
7 e
ggs
2
Egg s
ize
1.5
0
0.5
8
-
3
Incu
bat
ion
per
iod
-
5.0
8
4
1st
inst
ar g
rub
1.6
2
0.5
8
3.0
0
5
2nd i
nst
ar g
rub
2.4
0
0.7
4
4.6
7
6
3rd
inst
ar g
rub
4.5
0
1.5
0
5.1
7
7
4th
inst
ar g
rub
5.8
0
2.0
0
6.0
0
8
Tota
l la
rval
dura
tion
-
18.8
3
9
pupal
per
iod
5.7
5
2.8
0
8.6
7
10
Adult
longev
ity
a.
Mal
e
b.
Fem
ale
6.5
0
7.2
0
3.5
0
3.6
0
81.7
*D
ata
sho
ws
mea
n o
f th
ree
rep
lica
tio
ns
78
Fig.
-4.4
b: T
he fi
gure
show
ing
diff
eren
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79
CHAPTER -V
SUMMARY AND CONCLUSION
The summary, conclusion and suggestions for future work of the experiment
entitled “E-surveillance and management of congress grass, Parthenium
hysterophorus L. through Mexican beetle, Zygogramma bicolorata P. and
record of natural enemies of few commonly associated weeds” conducted at the
Department of Entomology, IGKV, Raipur during 2016 & 2017, are mentioned
under the following objectives:
5.1: To record the natural enemies of congress grass, Parthenium hysterophorus L.
with special reference to its management with Mexican beetle, Zygogramma
bicolorata Pallister,
5.2: To study the e-surveillance of Parthenium and other associated weeds in
Kharif and Rabi season,
5.3: To work out the feeding potential of Mexican beetle, Zygogramma bicolorata
P. under laboratory conditions,
5.4: To study the bionomics of Mexican beetle, Zygogramma bicolorata P.under
laboratory conditions.
SUMMARY
5.1: To record the natural enemies of congress grass, Parthenium
hysterophorus L. with special reference to its management with Mexican
beetle, Zygogramma bicolorata Pallister
Population of Mexican beetle, Z. bicolorata was recorded at three locations
of IGKV campus namely research field area of agricultural and horticultural crops,
agro-forestry field area and road side along NH-6 from administrative building to
College of Agriculture, Raipur District.
To agro-forestry area, the overall months of average of Mexican beetle (egg,
grubs and adults) population was noticed 0.16, 0.04 and 0.07/plant, respectively
while average other insect pest associated with Parthenium was observed
maximum (1.17/plant) in aphids followed by ants (1.02 plant) and minimum in
canthocona bug ( 0.02/plant) during 2016. During 2017, the average Mexican
80
beetle (egg, grubs and adults) population was observed 0.10, 0.03 and 0.04/ten
plants, respectively while average of other insect pests associated with Parthenium
was observed as maximum (0.87/plant) in ants followed by aphids (0.71/plant)
and minimum in Canthocona bugs and cow bugs (0.02/plant).Whereas, The overall
pooled data of two years, showed the mean population of Mexican beetle (egg,
grubs and adults) as 0.13, 0.03 and 0.06/plant, respectively while other insect pest
associated with Parthenium was observed as 0.94, 0.45, and 0.02/plant of aphids,
mealy bugs and Canthocona bugs, respectly.
Incropped field area, the overall months of average of Mexican beetle (egg,
grubs and adults) population was noticed as 0.61, 0.48 and 0.19/plant, respectively
while average of other insect pest associated with Parthenium was observed as
maximum (2.03/plant) in ants followed by aphids (1.88/plant) and minimum in
Canthocona bugs (0.12/plant) during 2016. In the second year i.e. in 2017
Mexican beetle (egg, grubs and adults) population was observed 0.43, 0.30 and
0.19/plant, respectively while other insect pest associated with Parthenium was
observed as maximum (1.45/plant) in ants followed by aphids (1.22/plant) and
minimum in semilooper (0.14/plant). The overall pooled data of two years depicted
the mean population of Mexican beetle (egg, grubs and adults) as 0.52, 0.39 and
0.19/ten plants, respectively while other insect pest associated with Parthenium
was observed maximum (1.74/plant) in ants followed aphids (1.55/plant) and
minimum in Canthocona bugs (0.09/plant).
In road side area, the average Mexican beetle (egg, grubs and adults)
population was recorded as 1.84, 0.46 and 0.90/plant, respectively while other
insect pest associated with Parthenium was observed maximum (0.98/plant) in
mealy bug followed by ants (0.70/plant) and minimum in Canthocona bugs
(0.02/plant) during 2016. During 2017, the Mexican beetle (egg, grubs and adults)
population was observed as 1.43, 0.38 and 0.82/plant, respectively while other
insect pest associated with Parthenium was observed as maximum of (0.94/plant)
in mealy bugs followed by ants (0.70/plant) and minimum in Canthocona bugs
(0.02/plant). The overall pooled data of two years, the mean population of Mexican
beetle (egg, grubs and adults) was recorded 0.48, 0.36 and 0.17/plant, respectively
while other insect pest associated with Parthenium was observed maximum
81
(1.62/plant) in ants followed by aphids (1.43/plant) and minimum in spittle bugs
(0.14/plant).
Gupta and Sood (2002) who conducted survey in August 2001 in 5 districts
of Himachal Pradesh, India, to determine the ecology of Zygogramma bicolorata, a
potential biological control agent against parthenium weed also reported mean
maximum infestation in the month of August with 8.50/plant, which is in
agreement with the present finding.
Similarly Dhiman and Bhargava (2005) also reported that the incidence of
Z.bicororata was maximum (87.09% and 76.19%) in August months which is in
accordance with the present studies.
5.2: To study the e-surveillance of Parthenium and other associated weeds in
Kharif and Rabi season
The e-surveillance programme of Parthenium and other associated weeds
was conducted at four different Blocks (Arang, Dharsiwa, Tilda and Abhanpur) in
Raipur District of Chhattisgarh. On the basis of overall block (Arang, Dharsiwa,
Tilda and Abhanpur) on upland, midland and lowland ranged from 0.01 to 3.62,
0.01 to 2.81 and 0.10 to 2.73, respectively during 2016. The maximum population
was exhibited of (3.62)/sqm in ants and minimum in (0.01)/sqm in Canthocona
bugs on lowland. In midland also highest population of (02.81)/sqm in ants and
lowest of (0.01)/sqm in Canthocona bugs while maximum (3.80)/sqm was
recorded in Mexican beetle and minimum in (0.01)/sqm in Canthocona bugs.
In 2017, the overall block (Arang, Dharsiwa, Tilda and Abhanpur) on
upland, midland and lowland was ranged from 0.01 to 3.62, 0.01 to 2.70 and 0.10
to 2.73, respectively. The maximum population was exhibited by ants (2.62)/sqm
and minimum in (0.01)/sqm in case of Canthocona bugs. Similarly on lowland and
midland also highest population of ants (1.76)/sqm and lowest in (0.02)/sqm in
cow bugs were recorded. while maximum Mexican beetle (3.70)/sqm were
recorded.
On the basis of pooled data of two years overall block i.e. at Arang,
Dharsiwa, Tilda and Abhanpur on upland, midland and lowland ranged from 0.01
to 3.62, 0.01 to 2.70 and 0.10 to 2.73, respectively. The maximum population was
exhibited by ants (3.12)/sqm and minimum in (0.01)/sqm in canthocona bug on
82
lowland and midland was also noticed (1.76)/sqm highest in ants and lowest in
(0.03)/sqm in cow bug while maximum (2.46)/sqm was recorded in Mexican
beetle and minimum in(0.05)/sqm in cow bugs.
The data of overall Raipur District of lowland, midland and lowland was
ranged from 0.06 to 2.57. The maximum population was exhibited (2.57)/sqm in
ants and minimum in (0.06)/sqm in canthocona bug while compare with the
Mexican beetle was noticed maximum (2.46)/sqm.
Similar findings were reported by Kulkarni and Kulkarni (2000) who studied
on P. hysterophorus plants in 20 locations in north Karnataka, India, for the
presence of Z. bicolorata and found that the densest population of beetles was
observed in Dharwad (10.4 beetles/plant), followed by Bijapur (5.6 beetles/plant)
and Raichur (3.2 beetles/plant). The beetle population is in line with the population
recorded at Raichur,Karnataka.
Bennett (1977) and Kumar, et al., 1979 , reported larvae and adults of the
stem-boring scolytid, Hypothenemus eruditus (Westw.) causing widespread
wilting of the weed, leading to good natural control and also a cerambycid borer,
Oberea sp. was also found to kill the plant was not recorded in the present studies
from Raipur district of Chhattisgarh.
Studies conducted to record associated weeds of Parthenium in Kharif and
Rabi 2016-17 depicted thirty seven weed species. Among the insect pests
associated on them revealed, domination by sucking pests viz; aphids, hoppers and
mealy bugs. Ants were recorded in large numbers in association with them. Few
species of semiloopers, caterpillars and mites/spiders were also noticed. Two
predators namely Coccinellid beetles and Canthocona bugs were also recorded.
Exploiting insect pests for eco-friendly management of invasive and locally
associated weeds is being done all over the world (Heimpel and Mills, 2017) thus
reducing the need for pesticides including India. The present study recorded thirty
seven weed species, on which a number of insect pests were noticed viz; sucking
pests such as aphids, hoppers and mealy bugs, along with few caterpillars and
semiloopers. These insects can be studied in further details and can be useful tools
in weed management.
83
5.3: To work out the feeding potential of Mexican beetle, Zygogramma
bicolorata P. under laboratory conditions
The feeding potential of Mexican beetle, Z. bicolorata, on the basis of overall
mean of two years data indicated that the treatments were significantly superior
over each other. The highest time taken was (14.83 days) for complete defoliation
by two pairs of beetles followed by (13.00 days) three pairs whereas, minimum
time taken was by five pairs of Mexican beetles (5.17 days). Overall two years of
data indicated that food consumption of parthenium was maximum (11.03mg) by
third instar grubs followed by fourth instars (7.94mg) and minimum in adults stage
(0.74mg).
5.4: To study the bionomics of Mexican beetle, Zygogramma bicolorata
P.under laboratory conditions
The studies on the bionomics of Mexican beetle, Z. bicolorata P.was
conducted under laboratory conditions. Revealed that the female Z. bicolorata laid
eggs either singly and/or in group on ranging from 5.83 to 29.33eggs on leaves
flower, stem and buds of parthenium with an average of 18.85 eggs. The
incubation period was in between 4.00 to 6.00 days with an average of 5.80 days.
The number of hatched of eggs ranged from 5.33 to 27.33 with an average of
17.36 while per cent of egg hatching was 73.71%. There were four larval instars
(grubs) stages i.e. first, second, third and fourth instars with average larval duration
of 3.00 to 6.00 days. It was 3.00, 4.67, 5.17 and 6.00 days for first, second, third
and fourth instars respectively, with overall average larval duration of 18.83 days.
Pupal period was of 8.67 days and adult longevity was noticed to be of 81.7 days.
The results on the development of the beetle on parthenium leaves were in
agreement with Pandey, Joshi, and Tiwari (2001), who reported grub, pupal and
totaldevelopmental period to be 13, 10 and 29 days, respectively, while Jayanth
and Geetha Bali (1997) observed the periods to be 4-6, 14-16, 8-10 and 28-30
days, respectively.Adult longevity was 120 days and the fecundity was 65 eggs per
day. Provision of soil facilitated 75% pupation under in vitro conditions (Gautam,
2002).
84
Bali (1993 a) recorded 45 eggs per day. Eggs are yellow or orange in colour
which hatch in 6-7 days in July and August and in 8-10 days in October and March
with an average of 7 days Pandeyet al. (2001) recorded it as 4 days while
Jayanthand Bali (1993 a) reported it as 5 days. This variation in egg number laid
per day may be due to climatic factors or due to single or multi time copulation.
Maximum number of damaged eggs in naturel condition was recorded in June,
perhaps due to dehydration. Hatching percentage is highest in the month of April
and July. A group of 5 male and 5 female can lay 1500 eggs or more in 15 days.
This indicates the magnitude of reproductive power, which is a positive point for
the control of the weed.
CONCLUSION
A survey of natural enemies of congress grass with special reference to its
management with Mexican beetle /plant data in agro-forestry area indicated that
the mean of egg (0.13), grubs (0.03) and adults (0.06) population was exhibited
maximum in August month. It was followed by July and September. It was
similar to recorded in cropped fieldand road side area along with highway that
is (0.52, 0.39 & 0.19) and (0.48, 0.36 & 0.17), respectively Whereas, other
insect pest associated with Parthenium was observed on February to March
months that is maximum sown (0.94) in aphids and ants, respectively and
minimum in Canthocona bugs (0.02). In case of cropped field and road side
area along with highway was also similar observed highest (1.74&1.43) in ants
with minimum in Canthocona bugs (0.09). Descending order of the Mexican
beetle population/ten plants in agro-forestry, cropped fieldand road side area
along with highway observed with in different months were as August < July <
September < October.
The e-surveillance programme of Parthenium and other associated weeds was
conducted at four different Blocks (Arang, Dharsiwa, Tilda and Abhanpur) of
Raipur District, the overall mean population of lowland, midland and lowland
was ranging from 0.06 to 2.57/sqm. The data indicated that the maximum
population was exhibited (2.57)/sqm in ants and minimum in (0.06)/sqm in
Canthocona bugs while in case of the Mexican beetle was noticed highest
85
(2.46)/sqm. On the basis of data, it can said that the maximum enemies were
observed against Parthenium and other associated weeds at Arang block. It was
followed by Dharsiwa with minimum was sown in Tilda block of Raipur
District.
Record of associated weeds of Parthenium in Kharif and Rabi 2016-17 depicted
thirty seven weed species. Among the insect pests associated on them, revealed
domination by sucking pests viz; aphids, hoppers and mealy bugs. Ants were
recorded in large number in associated with them. Few species of semiloopers,
caterpillars and mites/spiders were also noticed. Two predators namely
Coccinellid beetles and Canthocona bugs were also recorded.
The feeding potential of Mexican beetleon three age stages: early stage, pre-
reproductive and reproductive of Parthenium grass on the basis of overall mean
day of two years the data indicated that feeding efficiency of Z. bicolorata on
different age of host plant i.e. early stage, pre-reproductive and reproductive
treatments were sown significantly superior. The lowest time taken (5.17 days)
for complete defoliation by five pairs of Mexican beetle followed by three pairs
(13.00) and highest in two pairs (14.83 days)).Whereas, food consumption by
adult & grubs Mexican beetle within 24hrs at different stages i.e. first, second,
third, four instars and adults were indicated that maximum (11.03mg) eaten by
third instar grubs followed by four instars (7.94mg) and minimum in adults
stage (0.74mg).
The fecundity of single female of Z. bicolorata ranged from 5.83 to 29.33eggs
with an average of 18.85 eggs. The incubation period varied between 4.00 to
6.00 days with an average of 5.80 days, whereas, number of hatching of eggs
ranged from 5.33 to 27.33 with an average of 17.36 while per cent of egg
hatching was found to be 73.71%. There were four instars (grubs) stages i.e.
first, second, third and fourth instars with an average larval duration extending
from 3.00 to 6.00 for different stages of grubs, i.e. 3.00, 4.67, 5.17 and 6.00
days for 1st, 2
nd, 3
rd and 4
th instars respectively, with average larval duration of
18.83 days, pupal period of 8.67 days and adult longevity was 81.7 days.
86
SUGGESTIONS FOR FURTHER WORK
1. Potential of other associated insect pests of Parthenium should be studied.
2. More studies on management aspects should be worked out.
3. Impact of Charota, Cassia tora as replacer of Parthenium weed should be
studied.
87
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