RU2359444C2 - Phyto-remedy method of purification of soil from heavy metals - Google Patents

Phyto-remedy method of purification of soil from heavy metals Download PDF

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RU2359444C2
RU2359444C2 RU2007119743/12A RU2007119743A RU2359444C2 RU 2359444 C2 RU2359444 C2 RU 2359444C2 RU 2007119743/12 A RU2007119743/12 A RU 2007119743/12A RU 2007119743 A RU2007119743 A RU 2007119743A RU 2359444 C2 RU2359444 C2 RU 2359444C2
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glycyrrhiza
mass
soil
licorice
plants
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RU2007119743/12A
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RU2007119743A (en
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Екатерина Константиновна Батовская (RU)
Екатерина Константиновна Батовская
Вячеслав Петрович Зволинский (RU)
Вячеслав Петрович Зволинский
Александр Макарович Салдаев (RU)
Александр Макарович Салдаев
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Государственное научное учреждение Прикаспийский научно-исследовательский институт аридного земледелия Российской академии сельскохозяйственных наук
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Abstract

FIELD: agriculture.
SUBSTANCE: invention refers to biological purification of soil polluted with heavy metals. The method consists in growing plants on deactivated area; through their root system plants accumulate radio-nuclides and heavy metals contained in soil; further the method consists in removing growth and in its successive utilisation. As remedy for soil deactivation from heavy metals there are used plants of Glycyrrhiza giabra L. Glycyrrhiza uralensis Fisch. and amaranthus purple; four-five years old cuttings from roots of Glycyrrhiza are planted on deactivated area and plantations of Glycyrrhiza are grown; also cuttings are of 0.20-0.25 m length, diametre of 8-20 mm with four-six accessory buds and they are planted at depth of 0.16-0.22 m with row-spacing of 2.1-2.8 m in two mutually perpendicular directions with seeding rate 21500-28600 pieces per hectare. In first two years of plant vegetation there is performed drop watering along rows of plants at rate of dropper consumption from 2 to 4 l/h with interval of their placement 0.3-0.4 m in a cavity of flexible watering pipelines. During September-October by the end of vegetation of the third year growth of Glycyrrhiza and associated grass on the deactivated area vegetation mass is low-cut mowed and piled into silo pits. Each year at beginning of the fourth, fifth and sixth year of plant growths there is carried out sowing of seeds of amaranthus; sowing is direct without cultivation of soil with row spacing 0.7-1.4 m at depth 0.5-1.5 cm and at seeding rate of 8x106-12x106 pieces/hectare. Vegetation mass of Glycyrrhiza and amaranthus is mowed and chopped in August of each year, and chopped mass in form of cutting is piled into the same silo pit. Brine of natural mineral bischofite of 1.1-1.3 t/m at rate of 200-400 l per ton of raw silo mass is introduced between layers of silo mass of thickness 0.3-0.6 m. Starting from the eighth year of plants growing in the plantation there is performed extraction of Glycyrrhiza root at depth of 0.4…0.6 m with exposing roots and rhizomes of Glycyrrhiza to day surface leaving stripes of virgin zone of 0.6-0.8 m width as zone of reservation. Root mass of Glycyrrhiza is subject to extraction with successive production of thick and dry Glycyrrhiza extract for industrial application. Freak parts of the roots and rhizomes of Glycyrrhiza and wastes of extract production are mixed with silo above-soil mass of Glycyrrhiza and amaranthus in pits. Late in autumn produced organic fertiliser saturated with microelements from bischofite brine is strewn on surface of cultivated stripes at extraction of root mass. The upper layer of soil in each stripe is milled with a rotary tiller at depth of 0.10-0.16 m till obtaining agronomic valuable soil aggregate; further the upper layer is compacted with a water-filled roller at pressure of 0.16…0.32 MPa. In a year repeated extraction of root mass of Glycyrrhiza is performed in another direction of cutting planting. There is facilitated phyto-deactivation of root inhabited layer of soil, ground and upstream water.
EFFECT: facilitating phyto-deactivation of root-inhabited layer of soil, ground and upstream water.
24 dwg, 21 tbl

Description

Текст описания приведен в факсимильном виде.

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Claims (1)

Фиторемедиационный способ очистки почв от тяжелых металлов, включающий выращивание на дезактивируемой местности растений, аккумулирующих через корневую систему радионуклиды и тяжелые металлы, содержащиеся в почве, удаление растительного покрова с дальнейшей его утилизацией, отличающийся тем, что в качестве средства дезактивации почв от тяжелых металлов используют растения солодки голой Glycyrrhiza glabra L., Glycyrrhiza uralensis Fisch. и амаранта сорта Багряный, на дезактивируемой местности посадкой черенков четырех-пятилетнего возраста из корневищ солодки длиной 0,20-0,25 м и диаметром 8-20 мм с четырьмя-шестью пазушными почками на глубину 0,16-0,22 м с широкими междурядьями 2,1-2,8 м в двух взаимно перпендикулярных направлениях с нормой высева 21500-28600 шт. на гектар создают плантации растений солодки, в первые два года жизни растений осуществляют капельный полив вдоль рядков растений с нормой расхода капельниц от 2 до 4 л/ч с шагом их размещения 0,3-0,4 м в полости гибких поливных трубопроводов, к концу вегетации третьего года жизни растений солодки и сопутствующих трав на дезактивируемой местности в период сентябрь-октябрь месяцы проводят скашивание вегетативной массы на низком срезе и ее закладку в силосные траншеи, ежегодно в начале четвертого, пятого и шестого годов жизни растений проводят прямой без обработки почвы посев семян растений амаранта с шириной междурядий 0,7-1,4 м на глубину 0,5-1,5 см с нормой высева семян 8·106-12·106 штук/га, а в августе месяце каждого года скашивают и измельчают вегетативную массу солодки и амаранта, измельченную массу в виде резки закладывают в ту же силосную траншею, при этом по слоям силосуемой массы 0,3-0,6 м в траншею вносят рассол природного минерала бишофит плотностью 1,1-1,3 т/м3 нормой 200-400 л на тонну сырой силосной массы, начиная с восьмого года жизни растений в плантации ведут добычу солодкового корня на глубину 0,4…0,6 м с извлечением корней и корневищ солодки на дневную поверхность полосами целинной зоны шириной 0,6-0,8 м в качестве зоны резервации, корневую массу солодки подвергают эксплуатации с получением густого и сухого экстракта солодки для технических целей, нетоварные части корня и корневищ солодки и отходы экстрактного производства перемешивают с силосной надземной массой солодки и амаранта в траншеях, полученное органическое удобрение, насыщенное микроэлементами из рассола бишофита, поздно осенью поверхностно вносят на обработанные полосы при извлечении корневой массы, верхний слой почвы в каждой полосе фрезеруют до агрономически ценных почвенных агрегатов почвенными фрезами на глубину 0,10-0,16 м и уплотняют верхний слой водоналивными катками давлением 0,16…0,32 МПа, а через год в другом направлении посадки черенков солодки производят повторную выемку корневой массы солодки. A phytoremediation method for cleaning soils from heavy metals, including growing plants on deactivated areas that accumulate radionuclides and heavy metals contained in the soil through the root system, removing vegetation cover with its further utilization, characterized in that plants are used as a means of soil decontamination from heavy metals licorice Glycyrrhiza glabra L., Glycyrrhiza uralensis Fisch. and amaranth of the Bagryany variety, on a decontaminated area, planting cuttings of four to five years of age from licorice rhizomes 0.20-0.25 m long and 8-20 mm in diameter with four to six axillary buds to a depth of 0.16-0.22 m with wide between rows 2.1-2.8 m in two mutually perpendicular directions with a seeding rate of 21500-28600 pcs. per hectare plantations of licorice plants are created; in the first two years of plant life, drip irrigation is carried out along rows of plants with a dropper flow rate of 2 to 4 l / h with a step of their placement of 0.3-0.4 m in the cavity of flexible irrigation pipelines, by the end vegetation of the third year of life of licorice plants and associated herbs on decontaminated areas in the period from September to October, mow the vegetative mass at a low cut and lay it in silo trenches, annually at the beginning of the fourth, fifth and sixth years of plant life direct sowing of seeds of amaranth plants without row cultivation with a row spacing of 0.7-1.4 m to a depth of 0.5-1.5 cm with a seed rate of 8 · 10 6 -12 · 10 6 units / ha, and in August of each year, the vegetative mass of licorice and amaranth is mowed and crushed, the crushed mass in the form of cutting is laid in the same silo trench, while brine of a natural mineral bischofite with a density of 1.1-1 is introduced into the trench in layers of a silage mass of 0.3-0.6 m , 3 t / m 3 with a norm of 200-400 l per tonne of raw silage, starting from the eighth year of life of plants in the plantation, they are producing licorice ny to a depth of 0.4 ... 0.6 m with the extraction of roots and rhizomes of licorice on the day surface with stripes of virgin zone 0.6-0.8 m wide as a reservation zone, the root mass of licorice is subjected to operation with obtaining a thick and dry licorice extract for technical purposes, non-marketable parts of the root and rhizomes of licorice and waste of extract production are mixed with a silo overhead mass of licorice and amaranth in trenches, the obtained organic fertilizer, saturated with trace elements from bischofite brine, is applied superficially in late autumn to the worked strips when extracting the root mass, the upper soil layer in each strip is milled to agronomically valuable soil aggregates by soil mills to a depth of 0.10-0.16 m and the upper layer is compacted with water filling rollers with a pressure of 0.16 ... 0.32 MPa, and after a year in the other direction of planting licorice cuttings, re-excavate the licorice root mass.
RU2007119743/12A 2007-05-28 2007-05-28 Phyto-remedy method of purification of soil from heavy metals RU2359444C2 (en)

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103858552A (en) * 2013-09-09 2014-06-18 轻工业环境保护研究所 Method for constructing soil of plough layer on coarse sand earth surface by heavy metal polluted sediment
RU2583696C2 (en) * 2014-09-24 2016-05-10 Федеральное государственное бюджетное образовательное учреждение высшего профессионального образования "Курский государственный университет" Method of cleaning soil of urbanised territories from zinc and copper
RU2618281C1 (en) * 2015-12-16 2017-05-03 Владимир Владимирович Чертов Method for extraction of metals from soil using biomass of plants

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111819942B (en) * 2020-07-14 2024-04-19 扬州市耕地质量保护站 Method for cultivating barren sandy backfill soil to supplement soil development level of cultivated land

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103858552A (en) * 2013-09-09 2014-06-18 轻工业环境保护研究所 Method for constructing soil of plough layer on coarse sand earth surface by heavy metal polluted sediment
CN103858552B (en) * 2013-09-09 2015-10-07 轻工业环境保护研究所 Build method and the application thereof of topsoil in coarse sand earth's surface with heavy metal polluted bed mud
RU2583696C2 (en) * 2014-09-24 2016-05-10 Федеральное государственное бюджетное образовательное учреждение высшего профессионального образования "Курский государственный университет" Method of cleaning soil of urbanised territories from zinc and copper
RU2618281C1 (en) * 2015-12-16 2017-05-03 Владимир Владимирович Чертов Method for extraction of metals from soil using biomass of plants

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