The initial characteristics of soil parameters are presented in Table 1.
The pH and EC of soil were 7.65 and 0.27 dSm
-1, respectively. The organic carbon content of experimental soil was 0.31 per cent. The soil had nutrient content
viz available nitrogen, available phosphorus and available potassium of 224, 12.5 and 540 kg ha
-1, respectively. The soil microbial populations namely bacteria (x106 cfu g
-1 of soil), fungi (x104 cfu g
-1 of soil) and actinomycetes (x 103 cfu g
-1 of soil) was 32.2, 16.5 and 21.4, respectively. The major nutrients content of organic manures used in the experiment
viz nitrogen, phosphorus and potassium of vermicompost was 2.90, 0.90 and 1.30 per cent and farm yard manure was 0.50, 0.25 and 0.40 per cent, respectively (Table 2).
The post-harvest soil chemical and biological properties are presented in Table 3,4 and 5.
The highest soil pH value of 7.62 was recorded in T
1 (Control) and lowest soil pH value of 7.44 was observed in, T
6 (Soil + Vermicompost 50%). There was no significant effect of treatments observed on soil pH. However, the treatment which received organic manures showed very slight decrease in soil pH could be ascribed to the acidifying effects due to the organic acid produced during the course of decomposition of organic amendments. Similar to the above findings,
Guidi and Hal (1998) also observed that the application of various organic materials decreased the soil pH value due to the organic and inorganic acids produced during decomposition of organic matter in soil. The highest soil EC value of 0.41 dSm
-1 was recorded in T
2 (Soil+RDF) and lowest soil EC value of 0.25 dSm-1 was observed in, T
6 (Soil + Vermicompost 50%). The electrical conductivity (EC) of soil was significantly influenced by both organic and inorganic manures. The highest value of soil EC was recorded by the application of 100 per cent RDF. These results are in line with the findings of
Tiwari et al., (1995), who observed that the soil EC was increased due to the application of recommended dose of fertilizers through inorganic sources. The highest soil organic carbon content of 0.45 per cent was recorded in T
6 (Soil + Vermicompost 50%), followed by T
5 (Soil + Vermicompost 25%) and T
4 (Soil + FYM 50%). The lowest soil organic carbon content of 0.28 per cent was observed in control (T
1). The soil organic carbon content was differed significantly among the treatments. The treatment receiving organic manures was recorded highest value of organic carbon content in soil, which might be due to the increase in organic carbon content by the application of organic manure compared to application of RDF through fertilizers.
Badale and More (2000) also reported the application of organic manures increased the organic carbon content over inorganics.
Natarajan (2003) also reported, increase in organic carbon content due to the addition of organic manures through poultry manures, compost and oil cakes.
The highest available nitrogen, available phosphorus and available potassium content of 241, 13.5 and 548 kg ha
-1 were recorded in T
6 (Soil + Vermicompost 50%), followed by T
5 (Soil + Vermicompost 25%) and T
4 (Soil + FYM 50%). The lowest available nitrogen, available phosphorus and available potassium content of 214, 10.8 and 528 kg ha
-1 were observed in control (T
1), respectively. The soil nutrient content
viz available nitrogen, available phosphorus and available potassium were differing significantly among the treatments. Generally, the available nutrient content of soil was more in organic manure received treatment. It might be due to the availability of higher macro and micro nutrients from higher quantities of organic manures. Similarly,
Canali et al., (2000) also reported that organic manure application through compost, poultry manure and oil cakes enhance the availability of nitrogen in soil. These results are in line with the findings of
Warncke and Srigar (1992), who reported that the application of organic manures through oil cakes increased the soil available phosphorus in soil.
Mathan et al., (2000) also reported the organic manure amendments (FYM, poultry manure, oil cakes and cotton waste) increased the higher potassium availability in soil than inorganic amendments. Application of different organic manures like vermicompost and FYM was significantly increase the soil available nutrient contents
(Deepa Joshi et al., 2016). (Sharma et al., 2016) also reported, soil nutrients status was improved by the addtition of different organic manures.
The highest total bacteria, total fungi and total actinomycetes population of 35.1 (x 106 cfu g
-1 of soil), 18.0 (x 104 cfu g
-1 of soil) and 23.8 (x 103 cfu g
-1 of soil) were recorded in T
6 (Soil +Vermicompost 50%), followed by T
5 (Soil + Vermicompost 25%) and T
4 (Soil + FYM 50%). The lowest total bacteria, total fungi and total actinomycetes population of 20.8 (x 106 cfu g
-1 of soil), 13.7 (x 104 cfu g
-1 of soil) and 16.4 (x 103 cfu g
-1 of soil) were observed in control (T
1), respectively. The treatments received organic manure particularly vermicompost recorded highest population of bacteria, fungi and actinomycetes after harvest of the crop as compared to other treatments. It might be due to the availability of nutrients obtained from the organic manures.
Somasundaram and Sankaran (2004) also reported that the soil applied with organic manures recorded the maximum microbial population and enzyme activity than compared to recommended dose of inorganic fertilizers. Population of microbes under organic treatments acted as an index of soil fertility because it serves as a temporary sink of nutrient flux as reported by
Hassink et al., (1991). The lowest soil microbial load was registered under control, which might be due to low availability of nutrients and organic carbon content of soil.