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These results showed that the relative content of polysaccharide groups increased in the primary stage of incubation with maize straw, and the amide groups were stable.
For this reason, different mass flow combinations (e.g. in autumn, a combination with maize straw) and efficient process chains need to be investigated.
These results indicate that polysaccharide groups of Fe/Al-OC mainly contribute to the sequestration of Fe/Al-OC during the primary decomposition stage of maize straw, and the phenol group was stable in different genesis of paddy soils.
The composting pile were made up by a mixture (base matrix) of buffalo manure and cow dung (70%% w/w) with maize straw and poplar trimming as structuring woody part (30%% w/w).
Heating rate has significant effect on the pyrolysis of maize straw and U. pertusa.
The activation energy and lnA of maize straw and U. pertusa are listed in table 5.
Similar(48)
The experiment was arranged in a randomized block design with three replications for each treatment, including the unfertilized control (CK), chemical nitrogen (N) with phosphorus (P) and potassium (K) (NPK), NPK plus maize straw (NPKS), and NPK plus cattle manure (NPKM).
Pyrolysis of four different crop residues (wheat straw, maize straw, rice straw and rice husk) was carried out at 400 °C in a designed mobile bench-scale pyrolyser.
There was no significant difference at least on the basis of the C/N ratio between the grass (16, 7, 21.7 and 18).and the maize straw (24, 19.5 and 19.8) in the final compost mixtures.
Moreover, the proportions of amide-C of Fe/Al-OC extracted from soil TP, RP, PP, and MS with maize straw increased by 0.43 % and 0.13 % in soil TP and PP, but decreased by 0.06 and 0.30 % in soil RP and MS (Fig. 4; Table 4).
Grass composts started off at higher C/N ratios (26, 36 and 47) than the corresponding maize straw composts (26, 30 and 35).
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