A total of 956 individuals of ground beetles belonging to 28 species, 19 genera under of 11 subfamilies of Carabidae family were observed during the study period. On the basis of total number of species, Harpalinae and Trechinae were the most dominant subfamily with 7 species each followed by Brachininae (3 species), Scaritinae (3 species), Lebiinae (2 species), Paussinae (1 species), Anthiinae (1 species), Carabinae (1 species), Pterostichinae (1 species), Platyninae (1 species), Cicindelinae (1 species), respectively (Table 1 and Fig 3). Similar results were also reported by Kumar and Rajagopal (1997) who documented a total of 74 species of carabid beetles belonging to 37 genera of subfamily Harpalinae from Karnataka;
Mili et al., (2018) reported a total of 8 species of carabid beetles belonging to 4 genera
viz.
Clivina,
Harpalus,
Scarites and
Sparostes in
Gerbera and
Gladiolus crops of Jorhat, Assam;
Ali et al., (2015) collected a total of 281 carabid beetles and the species were noted as
Carabus hemprichi,
Harpalus sp. 1,
Harplaus sp. 2
, Calathus sp. and
Pseudoophonus rufipes which of them dominant species was
C. hemprichi in loquat orchard, while
Harpalus sp. 1 was the predominat species in guava orchard in the agro-ecosystem of the Syrian coast. The observations made in the present study are in favour of
Kazmi and Ramamurthy (2004) who reported three species of Carabidae family
viz.
Carabus orientalis,
Anthia sexmaculata and
Calosoma maderae from the Indian Thar Desert, Rajasthan.
Trigunayat and Sharma (2020) reported three species of carabid beetles
viz.
Carabus orientalis,
Scarites terricola and
Anthia sexmaculata and two species of Cicindellidae family from Keoladeo National Park, Bharatpur, Rajasthan.
Thakare and Zade (2012) recorded three species of Carabid beetles
viz.
Calosoma orientale,
Chaenius sp. and
Scarites sp. from the vicinity of Samadohmakhala road, Melghat Tiger Reserve, Maharashtra. Similiarly,
Thakare et al., (2013) collected and examined 10 species of carabid beetles belonging to six subfamilies
viz. Harpalinae, Anthiinae, Paussinae, Scaritinae, Carabinae and Siagoninae from Melghat Tiger Reserve, Maharashtra, India.
Kushwaha et al., (2015) collected 21 species under 18 genera of ground beetles from five districts of Chhattisgarh, India.
Thakkar and Parikh (2016) studied on diversity and abundance of coleopterans and reported 24 species of ground beetles from Gujarat, India.
Deshmukh and Gajbhiye (2017) recorded 12 species of carabid beetles belonging to 7 subfamilies
viz. Paussinae, Licininae, Harpalinae, Scaritinae, Siagoninae, Anthiinae and Panagaeinae from Pench Tiger Reserve (East) Maharashtra, India.
Shirbhate and Shirbhate (2020) documented 34 species of ground beetles from forest areas and agricultural areas of Akola district, Maharashtra, India.
In terms of total number of individuals Harpalinae was the most dominant subfamily with 25.83% of the total collected beetles. Trechinae was the second most dominant subfamily which constituted 24.58% of the total recorded beetles. Lebiinae, Cicindelinae, Pterostichinae, Brachininae, Scaritinae, Platinae, Anthiinae, Carabinae and Paussinae subfamilies were subsequently constituted 21.75%, 6.80%, 4.71%, 4.60%, 3.87%, 2.71%, 2.51%, 2.30%, 0.31% of the total collected beetles (Fig 2). These results were similar of findings of
Kustasi and Marko, 2007;
Igondova and Majzlan, 2015;
Nagahata et al., 2002, Kadar and Lovei, 1992. About 4.05% abundance of Carabidae family was reported from agri-biodiversity park of Agricultural University, Hyderabad, Telangana
(Sahoo et al., 2020). Kutasi et al., (2004) reported the species richness and composition of carabids in Hungary.
Diversity indices of carabid beetles in all four sites are shown in Table 2. The Shannon-Wiener index of carabidae family is same in both Site-A (agriculture land) and Site-B (Plains) recorded highest diversity value as 2.72 followed by Site-C (Rocky area) as 2.52 and Site-D (banks of water bodies) as 2.25. Species Richness Index is recorded high in Site-B as 4.43 followed by Site-A as 4.08, Site-C as 3.48 and low in Site-D as 2.25. However, the evenness index (Jx) was greatest in Site-C as 0.90, moderate in Site-D as 0.87 and least in both Site-A and Site-B as 0.83 (Table 2). The lowest evenness index at both the Site A and B were probably due to greatest abundance of the major species (125 individuals of
Dromius quadrimaculatus, 49 individuals of
Chaenius bimaculatus and 47 individuals of
Lophyra differens). Altogether, when the diversity indices were compared for selected four sites (Table 2), it was found that both Sites A (agriculture land) and Site B (Plains are dominated by grasses, herbs and shrubs) have the highest and similar species diversity and species richness. This implies that the availability of different herbs, shrubs, plants and crop cultivars were providing suitable microhabitats for flourished to the diversity and abundance of carabid species. In the previous studies by
Gaston, 1991 and
Cheng et al., 2007 revealed that plants and insects interrelate by way of mutualism and phytophagy and the structural intricacy of habitat and diversity of vegetation forms showed correlation with insect species diversity
(Alarape et al., 2015). Beetles are found where there is a favourable environment for their survival (
Samways, 2007;
Adeduntan and Olusola, 2013). Site-C (rocky areas) has moderate species diversity and species richness which is due to low availability of vegetation forms, increased soil erosion, sedimentation, water run-off and low moisture content in rocky area
(Lacey et al., 1989). Site-D (banks of water bodies) also has low species diversity and species richness because of low forging sites and little availability of microhabitats for carabid beetles. The pattern of species diversity and composition indicated habitats related with assemblage structure of vicinity area of water bodies
(Kubo et al., 2013).