Journal of Threatened
Taxa | www.threatenedtaxa.org | 26 August 2025 | 17(8): 27371–27377
ISSN 0974-7907 (Online) | ISSN 0974-7893 (Print)
https://doi.org/10.11609/jott.9668.17.8.27371-27377
#9668 | Received 06 February 2025 | Final received 22 June 2025 | Finally
accepted 04 August 2025
Spider (Araneae)
fauna in paddy ecosystem of Kangra Valley, Himachal
Pradesh, India
Manoj Bhaurao
Salunkhe 1, Muthusamy Sampathkumar
2 & Ajay Kumar Sood 3
1,3 Department of Entomology, College
of Agriculture, CSK Himachal Pradesh Agricultural University, Palampur, Himachal
Pradesh 176062, India.
2 ICAR-National Bureau of
Agricultural Insect Resources Bengaluru, Karnataka 560024, India.
1 manojbpatil1119@gmail.com
(corresponding author), 2 ento_sam@yahoo.co.in, 3 sood_hpau@yahoo.co.in
Editor: John T.D. Caleb,
SIMATS, Saveetha University, Chennai, India. Date of publication: 26 August 2025 (online & print)
Citation: Salunkhe, M.B., M. Sampathkumar
& A.K. Sood (2025). Spider (Araneae) fauna in paddy ecosystem of Kangra
Valley, Himachal Pradesh, India. Journal of
Threatened Taxa 17(8):
27371–27377. https://doi.org/10.11609/jott.9668.17.8.27371-27377
Copyright: © Salunkhe et al. 2025. Creative Commons Attribution 4.0
International License. JoTT allows unrestricted use,
reproduction, and distribution of this article in any medium by providing
adequate credit to the author(s) and the source of publication.
Funding: None.
Competing interests: The authors declare no competing interests.
Author details: Manoj Salunkhe is a PhD scholar at the Crop Protection Division, IARI–CICR, Nagpur Hub. He shall be undertaking research on insect pest management in the cotton ecosystem. Dr. M. Sampath Kumar is a senior scientist at ICAR–NBAIR, Bengaluru; part of his research is on spider taxonomy. Dr. A.K. Sood is working as a professor in the Department of Entomology, CSKHPKV. His research focuses on the management of insect and mite pests in crops grown in the hill ecosystem.
Author contributions: MBS did extensive spider collections from the study locations, photography, data analysis, and manuscript preparation and writing. MSK conceptualization, methodology, and spider identification. AKS supervision and guidance.
Acknowledgments: The authors sincerely acknowledge the support and facilities provided by CSK Himachal Pradesh Krishi Vishwavidyalaya (CSKHPKV), Palampur, executing the study. We also extend our deep gratitude to director the ICAR-NBAIR for extending facilities.
Abstract: Spiders are considered
biological indicators of ecosystem health. The present study documents the
diversity and abundance of predatory spiders in the paddy ecosystem of Kangra District, Himachal Pradesh, India, during the
cropping period from July 2023 to October 2023. A total of 543 specimens were
collected, representing 15 species across six families and nine genera. Oxyopidae was the most abundant family accounting for 44%
of specimens, followed by Tetragnathidae (24%), Salticidae (10%), and Araneidae (10%);
Lycosidae and Pisauridae
were sparsely represented. The most abundant species was Oxyopes
javanus, while Peucetia
viridana was the least recorded. The abundance of
spider populations exhibited temporal fluctuations throughout the study period,
with the highest numbers recorded during the second fortnight of August. Among
the three study localities, Shahpur exhibited the
highest diversity, with a Shannon-Wiener Index (H) of 1.95 and a Simpson Index
(D) of 0.84, indicating a well-balanced spider community, while Nagrota Bagwan had the highest
evenness (J’ = 0.93), suggesting a more uniform species distribution.
Keywords: Agroecosystem, biodiversity,
biological control, community, conservation, insect-pest suppression, predatory
spiders.
INTRODUCTION
Spiders are abundant invertebrate
predators in many terrestrial, natural, and agricultural ecosystems (Reshma
& Manju 2020). The updated checklist by Caleb & Sankaran (2025)
documents 1,976 spider species in India from 511 genera comprising 63 families,
representing approximately 3.7% of global spider diversity. Spiders play a
pivotal role in agricultural pest control by regulating insect populations (Sudhikumar et al. 2005; Reshma & Manju 2020); and they
are highly sensitive to habitat loss, climate change, and environmental
disturbances (Thirukonda et al. 2022). Paddy Oryza
sativa L. is a significant staple and cash crop in India, and spiders in
paddy fields can play an important role in controlling populations of
planthoppers, and leafhoppers (Samal & Misra 1975). Spider diversity documentation is a necessary
aspect of conservation strategies involving integrated pest management,
especially where paddy is an important crop as in Kangra
Valley of Himachal Pradesh. A preliminary investigation of spider fauna by Chhavi et al. (2021) reported nine spider families, of
which four: Araneidae, Oxyopidae,
Salticidae, and Tetragnathidae
were also recorded in the present study. Detailed information on species
diversity and community composition remains limited, and the present
investigation was undertaken to comprehensively assess spider communities in
the paddy ecosystem of Kangra Valley.
MATERIAL AND METHODS
Study Area
The study was conducted across
three localities in the Kangra District of Himachal
Pradesh: Nagrota Bagwan,
Palampur, and Shahpur. In Nagrota
Bagwan, the surveyed locations were Jalbimbi (32.105° N, 76.369 °E), Tharu
(32.105° N, 76.369° E), and Tarandi (32.103° N,
76.368° E). In Palampur locality, the locations included Banuri
(32.082° N, 76.534° E), Holta (32.105° N, 76.545 °E),
and Rajpura (32.105° N, 76.544° E). Whereas, in Shahpur,
spider collections were carried from Chandaran
(32.211° N, 76.118° E), Jhaghi (32.2086° N, 76.1803°
E), and Manjhiar (32.202 °N, 76.189 °E) (Figure 1).
Field data were recorded during
the cropping period from July to October 2023. Thirty days after
transplantation fortnightly sampling was undertaken using quadrates. Spiders
were collected from three quadrates (1 × 1 m) placed at each selected location
using direct hand collection method. In addition to that, five sweeps were
performed at the same location. Observations and collections were carried out
during the morning (0700–0800 h) and evening (1700–1800 h). Each of the three
quadrates were observed for a one-hour duration. The collected spider specimens
were preserved in 70% ethyl alcohol. The adult spider specimens were identified
based on taxonomic literature (Tikader 1970; Tikader & Malhotra 1980; Tikader
& Biswas 1981; Gajbe 2008; Yoshida 2009; Jäger 2011; Caleb 2020; Sankaran & Caleb 2023; World
Spider Catalog 2025).
Specimens have been deposited in
the National Insect Museum (NIM) of Indian Council of Agricultural
Research–National Bureau of Agricultural Insect Resources, Bengaluru for
further studies. The diversity indices of spider communities were calculated
using the following indices:
Margalef’s Index of Richness (MI): Measures
species richness using the formula:
MI = (S - 1) / ln (N)
Where S is the number of species,
and N is the total number of individuals. A higher MI value indicates greater
richness.
Shannon-Wiener Diversity Index
(H): Calculates species diversity based on abundance and evenness:
H = Σ {Pi × ln (Pi)}
Where Pi is the proportion of
individuals of a species. Higher H values represent more diverse and evenly
distributed communities.
Simpson’s
Index (D): Measures dominance of species: D = Σ (Pi ²)
The complement (1-D) indicates
diversity, values closer to 1 signifying greater diversity.
Pielou’s Evenness Index (J): Analyse the evenness of species distribution: J = H / Hmax
Where Hmax
= ln (S). The index ranges from 0–1, 1 indicating maximum evenness.
Statistical calculations were
performed in Microsoft Excel program.
RESULTS
A total of 15 species belonging
to nine genera under six families were recorded from the paddy ecosystem of Kangra Valley of Himachal Pradesh (Table 1). Oxyopidae was the dominant family, constituting six species
under two genera, followed by Araneidae (3 species), Tetragnathidae, Pisauridae, Lycosidae, and Salticidae,
recording one species each (Table 1, Figures 2 & 4). Analysis of
spider population data from the three study sites—Nagrota
Bagwan, Palampur, and Shahpur—revealed
notable variation in species composition and family-level abundance, indicating
distinct assemblage structures across the locations. Perusal of the data
contained in Figure 2 revealed that based on 543 collected individuals, Oxyopidae was the most abundant family, comprising 44%
individuals, followed by Tetragnathidae (24%), Salticidae (10%), and Araneidae
(10%). The remaining families, Pisauridae, and Lycosidae were sparsely represented. Oxyopes
javanus was the most dominant species across all
sites, contributing to 30.02% of the total species abundance, followed by Leucauge fastigata (16.02%),
and Plexippus paykulli
(9.76%). The spiders present in the paddy ecosystem were categorized
into the four guilds based on their foraging behaviour.
Specialist/Stalkers (Oxyopidae, Salticidae) were the most dominant guild in the selected
localities, encompassing 53.4%, followed by orb web weavers (34.6%), ambushers
(8.1%), and ground hunters (3.9%) (Table 2).
The spider diversity indices
showed disparities across the localities of Nagrota Bagwan, Palampur, and Shahpur. Nagrota Bagwan had the
Shannon-Wiener index of 1.94 and Pielou evenness
index of 0.93, indicating a highly diverse, and evenly distributed spider
community (Table 3). This indicates that distribution of spider species in Nagrota Bagwan was more uniform.
In contrast, Palampur had the lowest Pielou’s
Evenness index (0.88), supporting a relatively more uneven distribution of
spiders, although the Shannon-Wiener index (1.93) remained high, indicating
relatively high diversity but less balanced. The Margalef
index was the highest in Palampur (1.55), indicating a slightly greater variety
of species with regard to the other two localities, while Nagrota
Bagwan had the lowest MI (1.34), indicating moderate
species richness. The Shannon-Wiener diversity index (H) was calculated for
three localities namely Nagrota Bagwan,
Palampur, and Shahpur. The obtained values were 1.94,
1.93, and 1.95, respectively. These values indicate that species diversity is
relatively consistent across the three localities, with minor variations
suggesting a relatively stable ecological balance. Shahpur
had the highest Simpson index (0.84), followed by Nagrota
Bagwan (0.83), suggesting a more balanced spider
community in these areas compared to Palampur (0.81), where the community was more
dominated by spider species namely, Oxyopes
javanus, Oxyopes
shweta, and Argiope
aemula.
DISCUSSION
In the present study, six spider
families, namely, Araneidae, Lycosidae,
Oxyopidae, Pisauridae, Salticidae, and Tetragnathidae,
were recorded across three localities of paddy ecosystem of Kangra
Valley. The majority of spider species belonged to the families Oxyopidae, Tetragnathidae, and Araneidae. Earlier studies have also identified Oxyopidae, Tetragnathidae and Araneidae as dominant spider families in paddy ecosystem
from various parts of India (Sebastian et al. 2005; Premila
2003; Moses et al.2023).
Foraging guild classification was
done by Uetz et al. (1999). The data on different
foraging guilds of spiders are presented in Table 2. The dominance of
specialists/stalkers (53.4%) over web builders in the paddy ecosystem may be
attributed to frequent agricultural disturbances, such as worker movement
during the cropping season, and heavy rains. These disturbances often damage
webs, making it difficult for web-building spiders to thrive. Consequently,
stalker spiders, which do not rely on webs, are more successful in such
disturbed environments. Data on seasonal abundance of spider shows that spider
populations fluctuated throughout paddy cropping period (July 2023 to October
2023), including peak of 125 individuals in the second fortnight of August
(Figure 2). The population was higher from the second fortnight of July to the
first fortnight of September. Our results demonstrated that spider diversity
was significantly higher in locations exhibiting greater habitat complexity,
characterized by intense pest (prey) buildup smothered with intensive coverage
of weedy vegetation in the field bunds. These findings are in line with Uetz (1991), who documented that structurally complex
habitats offer a broader range of ecological niches, and resources, thereby
facilitating higher spider species richness. Spiders are sensitive to habitat
structure and more complex habitats, such as complex vegetation, inclined to
propel more diverse spider population. Adjoining habitats also play a role in
determining spider composition by affecting prey and predator movements (Polis
et al. 1998). These observations are supported by the findings of Sudhikumar et al. (2005), who emphasized the need for
further studies on adjoining habitats and bunds to understand their impact on
spider populations in paddy fields.
Although all collections were
made in paddy fields, variation in spider species abundance across the
locations may be attributed to differences in plant density, growth stages,
water levels, pesticide use, surrounding vegetation, prey availability, and
microhabitat conditions. These local factors play a significant role in
supporting spider communities. Overall, complexity of habitat, and availability
of prey are determining factors in buildup of spider populations and their ecological
role in pest regulation in paddy ecosystems.
Richness and abundance of spider
recorded in the current investigation highlight the pivotal role of habitat
structure, and vegetation complexity in impacting the prevalence of spider
species. The physical structure and complexity of crop plants provide favourable conditions for spiders by facilitating web
construction, prey availability, shelter, and favourable
microclimatic factors, viz., temperature and humidity, which also support
mating and predatory activities. These findings are in line with the
observations of Young & Edwards (1990), who documented variations in the
habitat structure, including plant density, and vegetation cover, significantly
affect the diversity, distribution, and ecological distribution of spider
species. In a nutshell, we encountered six spider families, with Oxyopidae as the most abundant family. Oxyopes
javanus was the most numerically prominent,
followed by Leucauge fastigata.
Among the selected localities, species richness was highest in Shahpur (1.95) and Nagrota Bagwan (1.94) compared to Palampur (1.93). A higher
dominance of foraging guild specialists/stalkers was observed across all
localities. Considering all aspects, the spider community is influenced by
various factors, like habitat complexity, prey species type, adjacent fields,
and various abiotic factors (Padma & Sundararaj
2021; Dave & Trivedi 2024). The findings of this investigation provide
information on the spider diversity recorded in the paddy ecosystem of Kangra District, thereby strategies can be worked out for
conservation of these spiders in regulating insect pests, as farmers of this
region are in favour of biocontrol-based approaches
in pest management. Future research directions should prioritize on prey
preference, habitat selection, adaptability of climatic factors, and predatory
potential of dominant spider species.
Table 1.
The relative abundance of spider species associated with paddy ecosystems of Kangra Valley, Himachal Pradesh.
|
Family/ Species |
Collection based on quadrates
and sweeps nets July–October 2023
(number of individuals) |
Relative abundance (in %) |
|||
|
Nagrota Bagwan |
Palampur |
Shahpur |
Total |
||
|
Araneidae Clerck, 1757 |
|||||
|
Argiope aemula (Walckenaer, 1841) |
0 |
18 |
0 |
18 |
3.31 |
|
Neoscona theisi (Walckenaer, 1841) |
0 |
11 |
0 |
11 |
2.03 |
|
Neoscona vigilans
(Blackwall, 1865) |
0 |
0 |
27 |
27 |
4.97 |
|
Lycosidae Sundevall, 1833 |
|||||
|
Hippasa lycosina Pocock, 1900 |
21 |
0 |
0 |
21 |
3.87 |
|
Oxyopidae Thorell, 1869 |
|||||
|
Oxyopes hindostanicus (Pocock, 1901) |
12 |
14 |
0 |
26 |
4.79 |
|
Oxyopes javanus (Thorell, 1887) |
55 |
61 |
47 |
163 |
30.02 |
|
Oxyopes shweta (Tikader,
1970) |
0 |
18 |
0 |
18 |
3.31 |
|
Oxyopes sp. |
0 |
0 |
11 |
11 |
2.03 |
|
Peucetia sp. |
0 |
8 |
6 |
14 |
2.58 |
|
Peucetia viridana (Stoliczka, 1869) |
0 |
4 |
1 |
5 |
0.92 |
|
Pisauridae Simon, 1890 |
|||||
|
Nilus phipsoni (F.O. Pickard-Cambridge, 1898) |
19 |
0 |
25 |
44 |
8.10 |
|
Salticidae Blackwall, 1841 |
|||||
|
Plexippus paykulli (Audouin, 1826) |
15 |
16 |
22 |
53 |
9.76 |
|
Tetragnathidae Menge, 1866 |
|||||
|
Leucauge celebesiana (Walckenaer, 1841) |
20 |
0 |
0 |
20 |
3.68 |
|
Leucauge fastigata (Simon, 1877) |
31 |
22 |
34 |
87 |
16.02 |
|
Tetragnatha sp. |
12 |
0 |
13 |
25 |
4.60 |
|
Total |
185 |
172 |
186 |
543 |
100.00 |
Table 2. Different foraging guilds of spider groups recorded from Kangra Valley.
|
|
Foraging guild |
Family |
Proportion (in %) |
|
1 |
Ground hunters |
Lycosidae |
3.9 |
|
2 |
Orb web weavers |
Araneidae Tetragnathidae |
34.6 |
|
3 |
Ambushers |
Pisauridae |
8.1 |
|
4 |
Specialists/ stalkers |
Oxyopidae Salticidae |
53.4 |
Table 3. Diversity indices of spider fauna in different localities of Kangra Valley.
|
Parameters/ Diversity indices |
Localities |
||
|
Nagrota Bagwan |
Palampur |
Shahpur |
|
|
Species richness (S) |
8 |
9 |
9 |
|
Total individuals (N) |
185 |
172 |
186 |
|
Margalef index (MI) |
1.34 |
1.55 |
1.53 |
|
Shannon-Wiener index (H) |
1.94 |
1.93 |
1.95 |
|
Simpson index (D) |
0.83 |
0.81 |
0.84 |
|
Pielou evenness index
(J') |
0.93 |
0.88 |
0.89 |
For
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