Effect of digestate on soil organic matter content

Soil OM decreases in crop soils in Europe and in other continents therefore using amendments for increasing the soil OM content has a particular interest.

Digestate contains high amount of volatile fatty acid (C2-C5) which could be decomposed within few days in the soil (Kirchmann & Lundwall, 1993). The greatest rate of decomposition were observed in the first day after the treatment (Marcato et al., 2009) but the mineralization rate were high during the first 30 days (Plaza et al., 2007). Moreover, the C-mineralization values from the soil incubation assay showed that the results of raw slurry were similar to the effect of compost being in the start of composting process while the digested slurry had similar C-mineralization rate in the soil samples than that of the matured compost (Marcato et al., 2009).

1.3 Effect of digestate on the microbiological activity of soil

Soil microbial community has an important role in the fertility of soil and its alteration after intervention to the soil (e. g. manuring, soil improving, soil pollution) could be indicate more sensitive these changes than changes in the soil physical and chemical properties.

Among the different organic wastes like compost, biogas residue, sewage sludge and different manures with and without mineral N, the biogas residue was more efficient for promoting the soil microbiological activity. The high amount of easy-degradable carbon increased the substrate induced respiration (SIR), which was enhanced by the higher carbon content resulted from the higher litter and root exudates of higher plant growth. In accordance with these results, the largest proportion of active microorganisms was found in the digestate treated samples (Odlare et al., 2008; Kirchmann, 1991). Similarly, the activity of invertase was significantly higher in the digestate treated samples than that in control ones (Makadi et al., 2006).

Besides the macro — and micronutrient content of digestate which are important not for the crops but for soil microorganisms too, it contains growth promoters and hormones, also. Therefore it could be used for stubble remains to facilitate their decomposing. Makadi et al. (2007) compared the effect of digestate and Phylazonit MC bacterial manure on the growth of silage maize (Zea mays L. ‘Coralba’) as a second crop after winter wheat and on the enzyme activities of soil. Digestate was used at the rate of 50% of the total N demand of silage maize while the Phylazonit MC was used at 5 L ha-1 dose. Their results of the changes in enzyme activities are summarized in Table 6.

Treatments

Enzyme activity (mean±S. D.)

16/08/2006.

27/09/2006

Invertase activity (mg glucose 1 g-1soil 4 h-1)

a) Control

5,618+1,392“

3,767+2,030b

b) Phylazonit MC

7,437+1,945“

4,095+0,901b

c) Phylazonit MC+digestate

6,613±2,230a

1,584+0,748“

d) Digestate

6,024+1,486“

6,206+0,997c

Catalase activity (mg O2 1 g-1 dry soil 1 h-1)

a) Control

1,468+0,118b

1,797+0,289b

b) Phylazonit MC

1,160+0,144“b

1,410+0,050“

c) Phylazonit MC+digestate

0,983+0,275“

1,205+0,117“

d) Digestate

1,961+0,395“

1,288+0,063“

Table 6. Invertase and catalase activities of soil on the 3rd and 9th week after digestate and Phylazonit MC treatment (Data from Makadi et al., 2007). a, b, c indexes mean the different statistical groups according to Tukey’s test (p<0.05).

The maximum of the degradation of disaccharides, indicated by the invertase activity, was found in the 3rd week after Phylazonit MC treatment, while it was found only after the 9th week in the digestate treated soil samples. The Phylazonit MC contains only bacteria and promoting agents of bacterial activity for degrading the soil OM. Contrarily, in the digestate treated samples the degradation of disaccharides takes place at similar rate through 9 weeks because of the OM content of digestate used. Changes in catalase activity indicate the effect of nutrient content of digestate to the increasing microbial metabolism.