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Effect of Manures and Amorphous Aluminosilicates on Amount and Stability of Adsorbed Humus on Coarse and Fine Clay of Different Soils from Long-term Fertilizer Experiment

机译:植物和无定形硅胶对长期肥料实验不同土壤粗粘土吸附腐殖质的浓度和稳定性的影响

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The present investigation was carried out to study the amount and stability of adsorbed humus against thermal and microbial decomposition in relation to nature and source of humus as well as amorphous aluminosilicate (AAS) content in coarse and fine clay. Three different organic manures namely farmyard manure (FYM), biogas slurry (BGS) and a decomposed green manure Daincha (Susana aculeata) compost (GMC) were taken for extraction offulvic and humic acid from them. Clay samples separated from four soils of long term fertilizer experiment belonging to the orders of Inceptisol, Mollisol, Vertisol and Alfisol were fractionated into coarse clay (0.2-2mm)(CC) and fine clay (< 0.2 mm) (FC) each of which was again subdivided into two fractions one with amorphous aluminosilicates (AAS) and another without AAS. Humic acid (HA) andfulvic acid (FA) from different sources were mixed with different clay samples and shaken for 24 hours. The prepared clay-humus complexes were incubated for stability studies against microbial decomposition using mixed fungus culture of Trichoderma receeii and Aspergillous awamori Thermal stability of clay-humus complexes were studied by incubating at 55 °C and determining organic carbon content at 10 days interval. Statistical analysis with respect of the amount of humus adsorbed followed the sequences: a) Vertisol- clay> Inceptisol- clay> Mollisol- clay = Alfisol- clay, b) FC >CC >CC minus AAS > FC minus AAS ; c) BGS-humus > FYM-humus > GMC-humus and d) HA > FA. With respect to stability against both microbial and thermal decomposition the common sequences of stability observed were a) FC >CC >CC minus AAS > FC minus AAS, b) BGS-humus > FYM -humus > GMC-humus and c) HA > FA.
机译:本研究进行了研究吸附腐殖质对腐殖质的性质和来源的热和微生物分解的量和稳定性以及粗糙和细粘土中的无定形铝硅酸盐(AAS)含量的稳定性。三种不同的有机粪便即养殖粪肥(FYM),沼气浆料(BGS)和分解的绿色粪便Daincha(Susana Aculeata)堆肥(GMC)来自它们的提取过度和腐殖酸。从属于Inceptisol,Mollisol,Vertisol和Alfisol的令的长期肥料实验中分离的粘土样品分离成粗粘土(0.2-2mm)(Cc)和细粘土(<0.2mm)(Fc)再次被细分为两个分数,其中无定形硅硅酸盐(AAS)和另一个没有AAS。将来自不同来源的腐殖酸(HA)腐殖酸(HA)和CARFIC酸(FA)与不同的粘土样品混合并摇动24小时。将制备的粘土 - 腐殖质复合物培养,用于使用Crichoderma Receeii的混合真菌培养和在55℃下孵育并在10天间隔内测定有机碳含量来研究粘性真菌培养物的微生物分解的稳定性研究。关于吸附的腐殖量的统计分析序列:a)转溶胶 - 粘土>粘土>胶粘粘土= alfisol-clay,b)Fc> Cc> Cc减去AAS> Fc减去Aas; c)BGS-HUMUS> FYM-HUMUS> GMC-HUMUS和D)HA> FA。关于对微生物和热分解的稳定性观察到的稳定性常见序列是a)fc> cc> cc minus aas> fc minus aas,b)bgs-humus> fym-humus> gmc-humus和c)ha> fa 。

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