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Evaluation of select biochars and clays as supports for phytase to increase the fertilizer potential of animal wastes

机译:选择Biochars和粘土的评估作为植物酶的支持,以增加动物废物的肥料潜力

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Manures may contain considerable amounts of organophosphates (org-P) that must be enzymatically converted to inorganic phosphate (i.e., PO_4-P) to be plant available. Although adding enzymes into manures can facilitate mineralization of org-P to PO_4-P, enzymes that are not immobilized are easily lost through leaching, degradation, or denaturation. In this study, the immobilization of enzymes onto nine different biochar surfaces was explored. Phytase. which mineralizes a main class of org-P, was used as the model enzyme. Immobilization methods included covalent grafting accomplished by the carbodiimide crosslinker method and physical sorption. The results showed that physisorption was as effective as grafting for loading phytase to the biochars. Phytase loading after mixing 0.1 g biochar and 2 mg phytase correlated positively with biochar C:H ratio (an indicator of aromatic content) suggesting the importance of the hydrophobic effect. An increase in pH led to a decrease in phytase loading consistent with repulsion between negatively charged sites on phytase and the increasing negative charge on biochar. Less than 4% of the immobilized phytase leached after sequential extractions over seven days using manure dissolve organic matter solutions. However, the activity of immobilized phytase decreased markedly compared to the free state phytase. The specific activity of immobilized phytase was two orders of magnitude lower than that of free phytase at pH 5 and 7. Nevertheless, results showed that deactivation of phytase by biochars were reversible once the phytase was detached from the surfaces. Compared to the biochars, clay minerals (montmorillonite, kaolinite and hematite) tended to have greater loading rates and higher phytase activity. Composting manures with coamendments of biochar and minerals may enhance both short- and long-term P mineralization potential.
机译:粪肥可含有相当大量的有机磷酸(ORG-P),必须酶促转化为无机磷酸盐(即,PO_4-P)是可用的植物。尽管将酶添加到粪便中可以促进ORG-P的矿化,但是通过浸出,降解或变性容易损失未固定的矿化。在这项研究中,探讨了酶的固定到九种不同的生物炭表面上。植酸酶。将主要类ORG-P矿物融为一体,作为模型酶。固定化方法包括通过碳二亚胺交联剂方法和物理吸附完成的共价接枝。结果表明,物理吸收与将植酸酶加载到生物藻酶的接枝一样有效。植酸酶加载在混合0.1g生物炭和2mg植酸酶与Biochar C:H比(芳族含量的指示器)相关,表明疏水效果的重要性。 pH的增加导致植酸酶负载的减少一致,其植酸酶上带负电荷的位点与生物炭的负电荷增加。使用粪肥溶解有机物质溶液在六天内持续七天后少于4%的固定植酸酶浸出。然而,与自由态植酸酶相比,固定的植酸酶的活性显着降低。固定化植酸酶的比活性比pH5和7的游离植酸酶低两个数量级。然而,一旦植物酶从表面脱离,就会通过生物谱去激活植酸酶。与Biochars相比,粘土矿物质(蒙脱石,高岭石和赤铁矿)往往具有更大的加载率和更高的植酸酶活性。堆肥粪便具有生物炭和矿物质的共同,可以增强短期和长期的P矿化潜力。

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