It is observed from the data regarding morphological characteristics (Table 1) that in general all the soils were characterized by brown colour mixed with shades of grey and yellow. Majority of the soils either have silty loam (Balh, Gaggal, Dhangu, Baggi and Behna) or silty clay loam (Dhangu and Chachyot) texture. The variations in the texture of soils obtained here in the present study evinced the general statement of
Robinson (1949) that in case the parent material is the dominant factor in soil formation, the most obvious way in which it affects the soils is through similarity in colour and texture. Similar results had already been obtained by
Kaistha and Gupta (1992) while studying the soil genesis in Himalayas. However, very dark brown colour in the surface (0.0-0.15 m depth) soils of vegetable growing areas could be attributed to the presence of more content of organic carbon in these soils. Another important morphological characteristic of these soils is the presence of gravels in the lower layers of these soils (Table 1) which might be explained due to the prevailing alluvial conditions earlier in the area as the river Suketi still flows into its eastern and western parts. Black brown concretions were noticed in few of the horizons of paddy growing soils only (Table 1). The presence of very dark brown to dark reddish brown mottles (mostly 10YR 5/6 to 7.5 YR 5/8) was the common phenomenon in the rice growing soils (Table 1).
Silty loam was the dominant texture of the soils irrespective of soil depth. Generally silt was the dominant fraction (25.7 to 49.2%) followed by that of sand (coarse and fine sand). The content of coarse sand fraction was in the range of 12.1 to 48.1 per cent (Table 1). More content of coarse sand in all the soils under study could be explained due to presence of sandy type of rocks
viz., sandstones, silt stones, granites etc. prevailed in the area. In none of the profiles except Dhangu, illuviation of clay had been observed indicating, thereby, less development of soil profiles. However, in Dhangu profile, there was an accumulation of clay at 0.60 to 0.75 and 0.75-0.90 m depth. The higher content of organic carbon in these soils which had resulted in bringing about low bulk density from the average value (1.33 mg m-3). The bulk density of surface and sub-surface soils in vegetable, paddy and maize growing soils was found lower as compared to paddy and maize growing soils which might be attributed to the role of intensive management (tillage operations, frequent applications of higher amount of organic manures and fertilizers) and consequently better microbial activities. Particle density increased with depth of the soil in almost all the profiles. Its value in vegetable growing soils was higher in comparison to paddy and maize growing soils. However, this increased trend was not significant which might be due to the dominance of light minerals in these soils as reported by
Gupta (1992). The per cent soil porosity in vegetable soils was higher in comparison to paddy and maize soils, which could be due to the presence of higher organic matter in the former groups of soils (Table 1). In general, the per cent soil porosity decreased with the depth
(Singh et al., 2000).
The overall pH values of the studied soils ranged from 6.4 to 7.1, indicating slightly acidic to neutral in reaction (Table 2).
(Kaistha and Gupta, 1993) also found that soils of Central Himalayas of Himachal Pradesh had pH of 6.7-7.7. There is no specific trend in pH values of different crop growing areas except Naulakha paddy soils where pH values were found to increase with depth possibly due to leaching of bases.
EC of soil in vegetable, paddy and maize growing areas varies from 0.31-0.78 dS/ m, electrical conductivity was found almost safe limit in all the growing areas studied, though a decreasing trend was observed in the subsurface. Comparatively a little higher salt accumulation, as evidenced by EC values, under vegetable growing areas was observed, might be the consequence of frequent applications of fertilizers, composted animal manures. Similar findings for soil electrical conductivity under the system of vegetable production were reported by
Ammari et al., (2015). Organic carbon content in vegetable growing soils was higher in comparison to paddy and maize growing soils, which was due to the addition of FYM in vegetable soils (Table 2).
The surface horizons of vegetable growing soils had more available N in comparison to paddy and maize growing soils, and their contents decreased with the increase in depth (Table 2). As discussed earlier, the organic carbon content of the soil profile samples also showed a similar distribution. Higher amount of organic carbon in the surface layer of vegetable growing soils was responsible for higher amount of available N. The available N bore a close positive relationship with organic carbon which was also reported by
Ramesh et al., (1994). The available P content in vegetable growing soils was higher in comparison to paddy and maize growing soils and decreased with increase in depth (Table 2). Among soil properties, organic carbon and DTPA-extractable micronutrients possessed significant positive related with available P. The available K content was higher in vegetable growing soils than paddy and maize growing soils (Table 2). The available K content decreased with the depth in all the soils. The higher available K content in vegetable soils which could be ascribed to more organic matter in these soils. However, addition of potassic fertilizers by the farmers while cultivating vegetables which eventually increased K content in these soils could not be ruled out.
As such, the soils under study were low to medium with respect to available nitrogen, phosphorus and potassium status.
The soils of paddy growing area were high in DTPA-extractable Fe content as compared to vegetable and maize growing areas (Table 2) which might be due to suitable moisture regimes that accelerate the reduction process causing more availability of Fe. DTPA-extractable Fe content decreased with increased depth might be due to regular addition of Fe through plant residues on the surface. These results were in conformity with the findings of
Jalali et al., (1998). The DTPA-extractable Zn content in vegetable growing soils was slightly more in comparison to paddy and maize growing soils and it also decreased with the depth (Table 2). The higher available Zn content in vegetable soils might be due to the release of organic acids from added FYM and thus converting insoluble Zn into chelating or soluble Zn. Similar results had been reported by
Jalali et al., (1998). The DTPA-extractable Cu content was found to decrease with the increase in depth, but in the soils of paddy growing area, it did not follow any definite trend which might be due to stratification of soils (Table 2). The DTPA-extractable Fe, Zn, Cu and Mn were also high in these soils. Similar results were by
(Vadivelu and Bandyopadhyay, 1995).