Long-Term Monitoring of Arthropod
Community
in Paddy Fields in Korea
Joon-Ho Lee and Hong-Hyun Park
Entomology Program, School of Agricultural Biotechnology,
Seoul National University, Suwon 441-744, Korea
Abstract
Long-term monitoring study has been conducted
to understand structure of arthropod community, find the effect of conventional
practices on arthropod community and enhance rice IPM in paddy fields. The arthropod community was analyzed
using guild categories. The arthropods were found in the order of
non-pests>natural enemies>pests in their density in unsprayed site in
Baran, Kyonggi Province, 1996. But the order could be changed dependent upon
immigration rates of pests, regional characteristics, cultural practices, and
sampling methods. The pest were mainly Homoptera and dominated by Delphacidae(Nilaparvata lugens Stål, Sogatella furcifera Horvath and Laodelphax striatellus Fallen) and
Cicadelidae (Nephotettix cincticeps
Uhler). They constituted>80% of pest abundance. Spiders were the most dominant
group in the natural enemy and constituted >90% of natural enemy abundance.
Non-pests group was mainly chironomids and occurred abundantly in early growing
season and gradually decreased as rice development proceeded. Pests and natural
enemies groups all occurred abundantly in mid and late growing season.
The results of
irrigating water quality study showed the densities of spiders were 2 or 3
times higher in the clean water field than in the other fields (life sewage and
animal sewage). The difference was apparent in webbing spiders. Through all the
growth stage of rice plants, the density of spider population in clean water
field increased as rice plants grew, however the other two sites didn¡¯t.
Arthropod community patterns in small rice fields associated with different
planting methods (transplanting, water seeding, and drill seeding) in Suwon
showed that differences in pest abundance were not found among rice fields
associated with different planting methods. No difference was found in species
richness and diversity in spider community among rice fields associated with
different planting methods. Different cultural methods (Conventional and Low
Input Sustainable Agriculture (LISA)) showed no differences in arthropod
abundance and species composition between two differently practiced fields.
Introduction
Pesticides centered pest control have caused
problems such as insecticide resistant, secondary pests, pesticide residue in
environment, and water and soil pollution. These problems also have occurred in
Korea without exception. Even though there have been many studies to reduce
insecticide overuse or abuse (Uhm et al. 1991), most of the studies were
focused on timely treatment of insecticides or establishing pest control
strategy using pesticides. Therefore, There have not been many studies trying
to develop comprehensive pest management strategy based on insect community
characteristics in paddy fields (Lee et al. 1997). These approaches might have
achieved partial success in controlling individual pest species, but have
exhibited several limits in solving pest problems with comprehensive
understanding of ecological structure in paddy fields. Occurrence of rice
insect pests is closely related to cultural methods such as cropping system,
sanitation and rotation and biological and environmental factors such as
natural enemies, rice variety, weather, and morphological structure of rice
plants. Therefore, to maintain stable rice ecosystem and to manage insect
pests, the management strategy should be developed based on comprehensive
understanding of characteristics of arthropod community structure in paddy
fields.
Studies presented in this
paper have been conducted to understand arthropod community structures in
various rice paddy fields located in Kyunggi province. Effects of different
cultural methods, irrigating water quality, pesticide application, and
conventional and low input practice on arthropod community have been studied
(Lee et al. 1997, Park et al 1997, Park and Lee 1997, Lee et al. 1998). A
common objective of these studies was to understand the arthropod community in
paddy fields and reveal the strength of interactions among pest, natural enemy
and non-pest groups. Based on these understandings, our aims are to develop
integrated pest management strategies harmonized with environment.
Materials
and Methods
This study was conducted in the rice paddy
fields located in upstream and downstream paddy fields neighboring Baran
reservoir, Kyunggi province in 1996. On May 20, rice seedlings were
transplanted to the experimental plots. Insecticides were treated twice to the
sprayed plot. To control rice water weevil (Lissorhoptrus
oryzophilus Kuschel) pyrethroid insecticide was applied (1kg/10a) 10 days
after transplanting and carbamate group insecticide was treated (150l/10a) 75 days after transplanting.
Electric powered sucking device was used to sample arthropods in the rice paddy
fields. Rectangular -shape acrylic cage (0.5 x 0.5 x 0.7m) was covered to
prevent arthropods from escaping from the sampling rice plants while sampling
was conducted. Each experimental plot was replicated 10 times and sampling was
conducted 13 times through rice growth periods with one week interval between
each sampling.
This study was conducted in three different
rice paddy fields irrigated with three different water quality types (clean
water, life sewage and animal sewage) from 1994 to 1996. The experimental
fields were located in Banwol, Kyunggi province. The quality of water irrigated
to clean water rice field and two other sites was classified as acceptable and
slightly polluted, respectively, according to the water quality classification
test. To collect arthropods on a rice plant, mesh cloth cage (1 x 0.5 m) was
covered on a sampling rice plant then bottom of the plant was cut with a large
scissors. The experimental plots were replicated 10 times and sampling was
conducted with two weeks interval.
This study was conducted in rice paddy fields
in the experimental station of Seoul national university located in Suwon,
Kyunggi province in 1994. Each plot (18.5 m x 18 m) was planted with three
different methods (transplanting, water seeding and drill seeding). Electric
powered sucking device was used to sample arthropods in the rice paddy fields.
Rectangular -shape acrylic cage (0.5 x 0.5 x 0.7m) was covered to prevent
arthropods from escaping while sampling was conducted. There were 10
replications of the experimental plots and sampling was conducted with 15 days
interval.
This experiment was conducted in 1995 and
1996. The experimental plots were located in Top-dong, Suwon, Kyunggi province.
Two rice paddy fields that were cultivated by two farmers were selected and one
rice field was designated to conventional cultural practice plot and the other
was designated to low input practice plot (LISA). Each plot was treated with
pesticides and fertilizers as shown in table 1. To sample arthropods on a rice
plant, mesh cloth cage (1 x 0.5 m) was covered on a sampling rice plant then
bottom of the plant was cut with a scissors. Each experimental plot was
replicated 10 times and sampling was conducted with 2 weeks interval.
Table. 1. Fertilizer and
pesticides applications for conventional and LISA plots
|
Item |
Conventional |
LISA |
|
Fertilizer application(kg/10a) |
11.8 : 5.3 : 5.3 (N: P: K) |
5.3 : 2.5 : 2.5 (N: P: K) |
|
Pesticide applications(no.) |
|
|
|
Herbicides |
1 |
1 |
|
Insecticide & Fungicide |
5 |
2 |
Results
and Discussion
Table 2 showed the mean density of arthropods
by taxa in guilds sampled in control plots in Baran, Kyonggi province. The
occupancy pattern of each guild appeared in the order of non-pests > natural
enemies > pests. The mean density of non-pests was much higher than that of
other guilds and there was little difference between the mean densities of the
natural enemies and the pests. This occupancy pattern is different from other
previous studies. The pattern appeared in the order of pests > non-pests
> natural enemies in Jinju (Song and Choi 1993) and natural enemies >
pests > non-pests in Ichon (Lee et al. 1997). It is suspected that these
differences were resulted from the differences of immigration rates of pests,
regional characteristics, cultural practices, and sampling methods.
Dominant species of the pests were brown
planthopper (Nilaparvata lugens Stål),
white-backed planthopper (Sogatella
furcifera Horvath), and small brown planthopper (Laodelphax striatellus Fallen) in Delphacidae, and Nephotettix cincticeps Uhler in
Cicadelidae. These dominant species were over 80 % of total pest species. In
natural enemy guild, spiders were dominant group occupied over 90 %. Parasitic
wasps and heteropterans were two distinctive minor groups in this guild. In
non-pests group, chironomids and flies in Diptera, and collembolans were
dominant groups. Chironomids and flies appeared in high density level during
early rice growing season while collembolans reached high density level late in
the season. Lavae and adults of chironomids and flies, as well as collembolans
were preys of generalist predators like spiders (Settle et al. 1996).
Table. 2. Mean density
of arthropods by taxa in guilds sampled at paddy fields in Baran, Kyonggi
Province, 1996 (Sample unit = 6 hills (0.5 x 0.5m)).
|
Guilds |
Order |
Common name |
Mean density |
|
Pests |
Homoptera |
Aphids |
1.61 |
|
|
|
Leafhopper |
0.59 |
|
|
|
Planthopper |
5.40 |
|
|
Hemiptera |
Phytophagous bug |
0.84 |
|
|
Lepidoptera |
Rice stem borer |
0.02 |
|
|
|
Rice leaf roller |
0.01 |
|
|
|
Others |
0.02 |
|
|
Coleoptera |
Rice water weevil |
0.11 |
|
|
|
Rice leaf beetles |
0.05 |
|
|
Subtotal
|
|
8.72 |
|
Natural Enemies |
Araneae |
Spiders |
8.50 |
|
|
Coleoptera |
Carabids |
0.47 |
|
|
Hemiptera |
Predatory bug |
0.51 |
|
|
Others |
|
0.21 |
|
|
Subtotal
|
|
9.72 |
|
Non-pests |
Collembola |
Collembola |
0.85 |
|
|
Diptera |
Chironomides |
24.84 |
|
|
|
Flies |
3.6 |
|
|
Subtotal
|
|
29.36 |
|
|
Total
|
|
47.80 |
Figure 1 showed the changes of occupancy rate
of each guild during the rice growing season. In early growing season,
non-pests guild showed over 90 % occupancy rate in both experimental plots, and
pests and natural enemy guild showed low occupancy rate. However, in the middle
of the season the occupancy rate of the natural enemies gradually increased and
at the late in the season, natural enemies showed highest occupancy rate among
three guilds. These patterns which were well coincided with results of previous
studies (Song and Choi 1993, Yun 1997) were assumed to be a general trend of
arthropod community structure in paddy fields in Korea. And no differences were
found in changes of percentage of each guild between unsprayed plot and sprayed
plot (fig. 1)
Figure 1. Proportion(%) of three guilds (pests(¡¤), natural enemies(¡Û),
non-pests(¡å)) in two paddy fields, Baran,
Kyonggi province, 1996. (a) Unsprayed field, (b) Sprayed field.
Figure 2 shows the changes in the densities
of arthropods with rice developmental stages (early, middle and late growing
stages) with three irrigating water qualities. . The same fluctuation patterns
in total arthropod density didn¡¯t repeat annually. In 1994, the density levels
were almost the same thought out the developmental stages of rice in all three
plots. The density level in life sewage irrigating fields was higher in early
season in 1995 and, the density level increased as time passed in rice fields
irrigated with three different water qualities in 1996. Without the outbreak of
immigrating pests such as brown planthopper, occurrences of arthropods in
normal year had high variances in densities among samples at the early season
but the variances decreased at the late (Park and Lee 1997). But life sewage
irrigated fields showed the density variance increased with time in 1996.

Figure
2. Changes in the density (no. / hill) of
arthropods in the rice fields with different irrigating water quality at
Banwol, Kyonggi province, 1994 –1996.
Table 3 showed the mean densities of spiders
classified by their life strategy in rice paddy fields with different
irrigating water qualities. The density level of spiders was 2 – 3 times higher
in clean water irrigating field than in life sewage or in animal sewage
irrigating fields. The density levels of hunting spiders showed no differences
among all three types of fields. However orb webbing spiders and space webbing
spiders showed higher density levels in clean water irrigating fields than in
the other two types of fields.
Table. 3. Densities
(No./hill) of spiders in rice paddy fields with different irrigating water
quality at Banwol, Kyonggi Province, 1995
|
Type |
Clean water |
Life sewage |
Animal sewage |
|
Hunting spiders |
2.50 |
2.56 |
2.11 |
|
Orb webbing spiders |
2.72 |
0.28 |
0.50 |
|
Space webbing spiders |
4.61 |
2.06 |
1.11 |
Total
|
9.83 |
4.89 |
3.72 |
Figure 3 showed the changes of the densities
of spider in three different qualities of water irrigating rice fields with
three rice developmental stages. During the early rice developmental stage, the
density levels were the same in all three water qualities irrigating fields.
However, the density level difference between the clean water irrigating rice
fields and the life sewage and animal sewage irrigating fields increased with
rice developmental stages. The density of spider was low at the early stage and
increased in the mid-stage, then maintained in high level until the late
developmental stage (Okuma et al 1978, Park and Lee 1997). In this study, there
was no rapid increase of the density at the middle of the rice developmental
stage in the life sewage and the animal sewage irrigating fields. This result
might be resulted from the negative effect of low water quality on spider
community.

Figure 3. Changes in the
densities (No. / hill) of spider in the rice fields with different irrigating
water quality at Banwol, Kyonggi province, 1995.
Seeding methods have greatest effect on the
development of arthropod community in rice paddy fields at the early in the
season. Seeding methods also influence the cultural practice applied in early
rice growing season and this could result in changes in early rice ecosystem.
These changes will affect the development and the density of arthropod
community on rice plants. Figure 4 shows the temporal density fluctuation of
three arthropod guilds in rice paddy fields seeded with 3 different methods.
Delphacidae and Cicadelidae in Homoptera constituted over 90 % of the pest
guild. There was almost no occurrence of brown planthoper and white- backed
planthopper. Green rice leafhopper started to occur in early August, and then
at the end of August the density of Green rice leafhopper reached the highest
level. However, the highest density level was only 2 ind. /6 hills. The density
level of spiders that constituted over 90 % of natural enemy guild rapidly
increased since August.

Figure 4. Temporal
fluctuation of main pest and natural enemy in differently planted rice paddy
fields in Suwon , 1994.
On the other hand the seasonal patterns that
the density of major pests, brown planthopper and white-backed planthopper
occurred at low density in early growing season and thereafter showed slightly
increase could be explained by huge decreases of migration of these pests from
China recently. Green rice leafhoppers are not migration pest from China, they
also showed same population dynamics patterns as planthoppers. At early growing
season non-pest group including chironomids and flies showed higher density in
drill seeding plot than transplanting plot (Lee et al. 1997). And since mid
rice growing season the structural difference of arthropod community by seeding
method didn¡¯t appear in our study, so we assumed that these different methods
could not cause occurrence of arthropod in paddy field.
Table 4 shows the result of analysis of
spider community in rice paddy fields seeded with different methods. There was
no difference in the number of spider species sampled (16 – 7 species) and in
diversity indices among different seeding methods.
Table. 4. Diversity indices
of spider community in small rice paddy field in 1994
|
Indices |
Water Seeding |
Drill Seeding |
Transplanting |
|
No. of species |
16 |
16 |
17 |
|
No. of individuals |
178 |
183 |
376 |
|
Shannon index (H¡¯) |
2.435 |
2.363 |
2.389 |
|
Dominance index (D) |
0.123 |
0.129 |
0.127 |
|
Evenness index (J¡¯) |
0.878 |
0.852 |
0.843 |
Figure 5 shows the occurrence of arthropods
in guilds in rice paddy fields cultivated with two different cultural
practices. There was no significant difference in the occurrence of arthropods
between the two differently cultivated rice fields. Chironomids were the
dominant species in the early season and decreased in density after July. Then,
the density of pest guild consisted mainly of Delphacidae and Cicadelidae and
natural enemy guild consisted mainly of spiders increased. The density of
natural enemy and pest guild started to increase in mid-July. It is thought
that increased fitness and reproductive capacity of arthropods of the guilds
resulted from increased humidity, temperature and canopy and increased prey
populations in rice paddy fields could be the reason. This result agreed with
previous studies (Song and Choi 1993, Yun 1997, and Lee et al. 1997).

Figure 5. Temperal abundance of arthropods of
three guilds(pest, natural enemy and non-pest) in rice fields managed by
different cultural methods, Suwon, 1995 and 1996.
Only 51.3 % of pesticides and fertilizers
were applied in low input plots in this study compared to conventionally
cultivated plots (Table 5). However, no difference was found in the community
structures and the density of arthropods in the rice paddy fields regardless
the cultivating practice used. This result showed that even though conventional
cultural practice inputs more energy into the field than low input practice,
rice development might not be affected by higher energy inputs in conventional
practice. Therefore, it is possible that with conventional cultural practice
more energy was input into the rice fields than necessary.
Table. 5. Total energy of
fertilizer and pesticides applied in rice fields
|
Source |
|
Energy Equivalents |
Input energy(kcal/10a) |
|
|
|
|
Conventional |
LISAa |
|
|
Fertilizer |
Nitrogen |
14,700 kcal/kg |
161,700 |
88,200 |
|
|
Phosphate |
14,700 kcal/kg |
24,000 |
24,000 |
|
|
Potash |
14,700 kcal/kg |
12,800 |
12,800 |
|
Herbicides |
|
14,700 kcal/kg |
12,990 |
13,828 |
|
Other pesticides |
|
14,700 kcal/kg |
86,665 |
14,501 |
|
|
|
|
|
|
|
Total |
|
|
298,155 (100%) |
152,829 (51.3%) |
a Low input
sustainable agriculture.
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