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Chemical Soil-Biological Engineering Theoretical Foundations, Technical Means, and Technology for Safe Intrasoil Waste Recycling and Long-Term Higher Soil Productivity

机译:化学土壤 - 生物工程理论基础,技术手段和安全腹膜油废物回收和长期较高土壤生产率

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The amelioration and remediation technology was developed on the basis of research of phosphogypsum and utilization in the Haplic Chernozem of South-European facies (Rostov Region). Phosphogypsum was utilized via dispersed application into a soil layer of 20–45 cm with intrasoil milling of this layer. The phosphogypsum utilization doses were 0, 10, 20, and 40 t ha~(–1). The Pb analytical content in soil solution was studied in the model experiment. The soil solution Pb thermodynamic forms were calculated. The mathematical chemical–thermodynamic model ION-2 was developed to calculate the real soil solution (water extract) calcium-carbonate equilibrium (CCE) ion forms, considering the ion pair association. The associated ion pairs CaCO 3) 0), CaSO 4) 0), MgCO 3) 0), MgSO 4) 0), CaHCO_(3)~(+), MgHCO_(3)~(+), NaCO_(3)~(–), NaSO_(4)~(–), CaOH~(+), and MgOH~(+) were accounted for in soil solution equilibrium macroion form calculation. The procedure for the microelement ion [including heavy metals (HMs)] equilibrium concentration in the soil solution coefficient k _(as) calculation was proposed to account for the real soil solution CCE, macroions, and HM (including Pb) association. The Pb~(2+) ion in soil solution was mostly bound to associates PbOH~(+), Pb(OH) 2) 0), PbCO 3) 0), Pb(CO_(3))_(2)~(2–), and PbHCO_(3)~(+). The calculation of CCE and ion association in soil solution revealed 14.5–21.5 times HM passivation compared to HM water-soluble values. The calculated HM activity in the soil solution in the example of the Pb~(2+) ion was less than 4% after phosphogypsum application in the target amelioration layer of 20–45 cm. The studied phosphogypsum doses were substantiated as environmentally safe. This was because the real soil solution CCE provided HM ion form association and consequent passivation. The dry steppe soil remediation after phosphogypsum application was justified as highly probable. The intrasoil milling chemical soil-biological engineering technology was developed for simultaneous soil amelioration and remediation on the basis of the biogeosystem technique (BGT*) transcendental methodology. The BGT*-based technology was tested in the long-term field experiments and is capable of ensuring the priority geophysical micro- and macroaggregate structure via intrasoil milling and mixing of soil illuvial and transitional horizons. This helps synthesize soil multilevel architecture, providing intrasoil-dispersed environmentally safe recycling of wastes of different origin. Addressing the environment safety concerns, a new decision of the intrasoil milling device was proposed for phosphogypsum and other substance application to soil.
机译:改善和修复技术是基于磷酸缺口和利用在南欧面部(罗斯托夫地区)的磷化物显膜和利用率的基础上进行开发的。通过分散的应用将磷酸缺口与该层的intaInoil碾磨成20-45cm的土壤层。磷酸缺口使用剂量为0,10,20和40 t ha〜(-1)。在模型实验中研究了土壤溶液中的PB分析含量。计算土壤溶液PB热力学形式。考虑到离子对缔合的,开发了数学化学热力学模型离子2以计算真实土壤溶液(水提取物)碳酸钙平衡(CCE)离子形式。相关离子对Caco 3)0),Caso 4)0),MgCO 3)0),MgSO 4)0),CaHCO_(3)〜(+),MgHCO_(3)〜(+),Naco_(3) 〜( - ),NasO_(4)〜( - ),CaOH〜(+)和MgOH〜(+)被占土壤溶液平衡宏观形式计算。在土壤溶液系数 k _(AS)计算中,将微晶体离子[包括重金属(HMS)]平衡浓度的方法考虑了真实的土壤溶液CCE,宏观和HM(包括PB)协会。土壤溶液中的PB〜(2+)离子主要符合PBOH〜(+),PB(OH)2)0),PBCO 3)0),PB(CO_(3))_(2)〜( 2-)和PBHCO_(3)〜(+)。与HM水溶性值相比,土壤溶液中CCE和离子缔合的计算显示为HM钝化14.5-21.5倍。在磷酸缺口在20-45cm的靶改变层中磷酸缺口施用后,Pb〜(2+)离子的实施例中的土壤溶液中的计算的HM活性小于4%。所研究的磷酸缺口剂量是根据环境安全的。这是因为真实的土壤溶液CCE提供了HM离子形式关联和随之而来的钝化。磷酸缺口施用后的干草原土壤修复是高度可能的。基于生物盖系统技术(BGT *)超渡方法的同时土壤改善和修复,开发了introiloil铣削化学土壤生物工程技术。在长期现场实验中测试了BGT *基础的技术,能够通过interAly铣削和土壤光明和过渡视线的混合来确保优先地球物理微观和大型宏观格子结构。这有助于合成土壤多级架构,提供不同起源废物的intrasoil分散的环境安全回收。寻址环境安全问题,提出了一种新的磷酸杆菌和其他物质应用于土壤的新决定。

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