Termite mound soil properties in West Bengal, India
Introduction
Termite mounds, a micro landform feature generally found in the lateritic landscapes of the tropical and subtropical regions (Dangerfield et al., 1998; Levick et al., 2010). Termite mounds have distinct morphology compared with the surrounding topsoil (de BRUYN and Conacher, 1990; Abe et al., 2009). Generally, termite mounds are stable, erosion resistant, (Léonard and Rajot, 2001; Jouquet et al., 2004; Ackerman et al., 2007), and increase nutrient concentration and mineral reserves (Kebede, 2004). Diets of termites are based on wood, grasses, litter, and nutrient-rich soil, so most of the termite's nest grows on wood soil interface and high biomass regions (Eggleton et al., 1996; Mora et al., 2006). Termite mound's growth, abundance and volume vary regionally due to variation in climate, vegetation cover, soil properties, biomass abundance, slope and groundwater depth etc. (Gathorne-Hardy and Eggleton, 2001; Cancello et al., 2014; Davies et al., 2014; Jamilu Bala Ahmed et al., 2019). Biological agents like termites are important for pedological processes hence are termed as bioengineers (Holt and Lepage, 2000); Millogo et al., 2011; Whitford and Eldridge, 2013; Jouquet et al., 2016). Termites have great impact on soil properties including redistribution of soil particles with nutrient and minerals, nest building, repacking and cementing, feeding activity, interaction with the organism, organic matter (OM) decomposition, nutrient recycling, foraging behaviour and decaying (Holt and Lepage, 2000). They also effects on soil properties by their chemical secretions (Prestwich, 1979; Hanus et al., 2010) and by bringing up subsoil to the soil surface for construction of mounds (Lee and Wood, 1971; Holt and Lepage, 2000; Jouquet et al., 2011; Mujinya et al., 2014). Termites are the most important soil fauna which help to modify physicochemical properties of soil (de BRUYN and Conacher, 1990; Lee and Foster, 1991; Holt and Lepage, 2000; Millogo et al., 2011; Jouquet et al., 2011; Rückamp et al., 2012; Jouquet et al., 2016; Lavelle et al., 2016), and built stable, microstructural and morphological features which are distinct from surrounding soil (Lee and Wood, 1971; Eschenbrenner, 1986; Lal et al., 1992; Dangerfield et al., 1998; Jungerius et al., 1999; Turner, 2000; Sarcinelli et al., 2009). The effects of termites are not limited to their living area, they also effect inside the mound and surrounding foraging area (Rückamp et al., 2012). Quantifying the distribution of termite mounds, regeneration, volume and mass of mound provide useful information on nutrient and minerals, the good productive capacity of the soil and groundwater resource (Turner, 2000; Kaschuk et al., 2006; Ackerman et al., 2007; Mège and Rango, 2010). Research on termite mounds historically concentrated on physicochemical and geomorphological properties (Lee and Wood, 1971; Wood et al., 1983; Abe et al., 2009; Dowuona et al., 2012), and their stability, erodibility, runoff, infiltration rate (Léonard and Rajot, 2001; Jouquet et al., 2012) and physicochemical properties of termite's mound (as a whole) in relation to adjacent topsoil (Hesse, 1955; Brian, 1978; Asawalam et al., 1999; López-Hernández, 2001; Jouquet et al., 2005; Ackerman et al., 2007; Kawaguchi and Nishi, 2007; Asawalam and Johnson, 2007; Jiménez et al., 2008; Okullo and Moe, 2012). As termites bring up soil not only from topsoil but also from subsoil (Jouquet et al., 2002),mound soils are affected by rainfall and thus eroded materials may also affect associated surface soils surrounding the mounds (Arshad, 1982; Lal et al., 1992).This study emphasizes the effect of the mound soil properties on the surrounding surface soil properties and makes a comparison between physicochemical properties of mound soil (at different depth) and surrounding surface soil (non-mound affected soil at different depth). The hypothesis was whether there is significant difference between mound soil properties and surrounding surface soil properties and the mound soil properties that may affect the surrounding surface soil properties. Therefore, the aims of this study were 1) to assess the effects of the mound soil properties on the surrounding surface soil properties, 2) to find out the difference between termite mound and surrounding surface soil properties in the study area and 3) to analyse the characteristics of mounds with their abundance, mass of materials (mass of termite mounds) and rate of regeneration.
Section snippets
Location of the study area
The study sites were situated in the lateritic soils of Paschim Medinipur district. Which is located in the southwestern part of West Bengal, India. The locational extent of this area is 22°25′40″ N to 22°26′4″ N and 87°17′40″ E to 87°18′14″ E (Fig. 1). Samples were collected from 20 termite mounds and 20 surrounding surface soils from different position of the study area at random and at different depth (Table 1). Average distance between sampling mound and the surface soil is 4 m. Ten mounds
Characteristics of mound
Termite mounds (as a whole) were approximately conical shaped with a height range from 33.22 cm to 241.30 cm and diameter range from 111.76 cm to 314.96 cm. The average height of termite mound was 252 cm, 184 cm and 161 cm in dense vegetation, dispersed vegetation and grassland area, respectively. In the study area, most of the mounds are conical in shape but few others cathedral configuration. Most of the termite mounds were compact and sealed with trees and bushes (Fig. 4) and some internal
Conclusion
After the study, it is found that most of the termite mounds have developed on the trees and bushes, where canopy cover is dense. Mound height, the mass of material, abundance and regeneration rate are high in dense vegetation (dense vegetation < dispersed vegetation < grassland). Soil properties of termite mounds positivly correlated with the surrounding surface soil properties except porosity and dispersion ratio. But soil properties of termite mounds have no significant effects on all
Declaration of competing interest
None.
Acknowledgements
The authors are grateful to Vidyasagar University Science Instrument Centre (USIC) especially, Dipankar Sir and Anindita Madam for their valuable guidance with soil testing and for technical assistance in laboratory analysis. Finally, the authors would like to thank to all the researcher of our lab for their encouragement, and valuable suggestion for undertaking this study.
Funding
This research did not receive any specific grant from funding agencies in the public, commercial, or not-for-profit sectors.
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2022, Ecotoxicology and Environmental SafetyCitation Excerpt :This study has revealed a linear positive relationship with the percentage of carbon (T1 mound: y (Soil) = 0.729x (T1) + 1.08, R2 = 0.93, F value = 16.35, P < 0.05; T2 mound: y (Soil) = 0.942x (T2) + 1.16, R2 = 0.96, F value = 12.32, P < 0.05) and nitrogen (T1 mound: y (Soil) = 1.2x (T1) – 0.03, R2 = 0.97, F value = 18.23, P < 0.05; T2 mound: y (Soil) = 1.12x (T2) – 0.02, R2 = 0.93, F value = 17.24, P < 0.05) in mounds along with their respective contents in the surrounding soil. However, less C and N percentages of termite mounds have attributed to the mound construction strategy of Odontotermes longignathus in which the termites excavate the soil from the deeper layers having poor organic matter content (Bera et al., 2020). Contour-Ansel et al. (2000) have demonstrated such low C and N content due to feeding behaviour of termites which release only salivary secretions (instead of feeding as other soil feeding termites) during the building of mounds (Contour-Ansel et al., 2000).