Изменение противоэрозионной стойкости орошаемых серо-коричневых почв сухой субтропической зоны Азербайджана в зависимости от давности их орошения

Э. А. Гурбанов, Ф. М. Рамазанова, С. М. Гусейнова, З.Р. Гурбанова
{"title":"Изменение противоэрозионной стойкости орошаемых серо-коричневых почв сухой субтропической зоны Азербайджана в зависимости от давности их орошения","authors":"Э. А. Гурбанов, Ф. М. Рамазанова, С. М. Гусейнова, З.Р. Гурбанова","doi":"10.17223/19988591/56/2","DOIUrl":null,"url":null,"abstract":"The dry subtropical zone of Azerbaijan is located in an erosion-hazardous zone, and irrigation erosion manifests itself on an area of more than 255 thousand hectares. The damage caused by irrigation erosion to the agriculture of the republic is manifested not only in the destruction of the soil structure, but also in the removal of nutrients from the soil. At the same time, the patterns of change in the anti-erosion resistance of grey Cinnomanic soils /Luvic Calcisols /Luvic-Calcic Kastanozems (according to the classification of the USSR), grey Cinnamonic soils (according to the classification of Azerbaijan), (on WRB (2014)-Haplic Kastanozems / Haplic Calcisols) in the dry subtropical zone of Azerbaijan, depending on the age of irrigation, are diverse and not fully studied. Therefore, conducting research in this direction and assessing the antierosion resistance of grey Cinnamonic soils is relevant for Azerbaijan. The aim of this research is to study the changing of the anti-erosion resistance of irrigated grey Cinnomanic soils in the foothill and plain areas of the dry subtropical zone of the republic, depending on the age of irrigation. Based on the results obtained, the place of grey Cinnomanic soils in the international classification system WRB (2014) was determined. The research was carried out on grey Cinnomanic soils of heavy loamy and light clayey granulometric composition of the foothills and plains of the dry subtropical zone of different irrigation periods, in the territories: Grey Cinnomanic (virgin soils) – Beylagan (39°46'02.2''N, 47°36'13.3''E) and Yevlakh region (40°60'67.75''N, 47°17'02.71''E); Newly Irrigated Grey Cinnamonic (20-25 years old) – Agdash region (40°63'24.62''N, 47°49'11.92''E) and Geokchay region (40°37'10.5''N, 47°44'29.5''E); Irrigated Grey Cinnamonic (about 100 years old) – Bilasuvar (39°48'36.49''N, 48°43'35.24''E), Yevlakh (40°44I 34.18''N, 46°96'51.13''E), kshu (40°55'39.53''N, 48°35'04.18''E), and Aghstafa region (41°06'11.17''N, 45°28'07.32''E); For a Long Time-Irrigated Grey Cinnamonic (about 300 years old) – Bilasuvar (39°44'25.56''N, 48°42'52.72''E) and Beylagan region (39°76'45.13''N, 47°59'13.50''E). The research methods are comparative-geographical (geographical patterns of distribution of these soils according to the granulometric competition and humus content of the arable horizon) and comparative-analytical. On the plots, soil sections were laid, a morphological description was carried out, soil samples were taken from the genetic horizons (Field guide of soils in Russia (2008), FAO. Guidelines for soil description (2006), IUSS Working Group WRB. World Reference Base of Soil Resources 2014, update 2015, Kallas and Tanzybayev (2001)). The anti-erosion resistance of soils was determined by the bottom erosion flow rate-according to Kuznetsov MS. (1981), the water resistance of the aggregates – by methods of dry and “wet” aggregate analysis according to Savvinov, the specific gravity of the solid phase – by the pycnometric method, the granulometric compotition – by the pipette method, soil density – with a drill according to the generally accepted method (Arinushkina, 1970; Vadyunina and Korchagina, 1986]. The value of the protrusions of soil roughness was determined by the ratio ∆ = 0.7 dw, where dw is the weighted average diameter of the water-resistant aggregates. The value dw was calculated based on the results of the structural analysis of the soil by the Savvinov method at the initial moisture content W (Grigoryev and Makkaveev, 1979), the content of total humus – according to Tyurin, modified bu Nikitin, cellulolytic activity – by application method for the decomposition of cotton canvases (Kazeev, Kolesnikov and Valkov, 2003). Depending on the age of irrigation, we revealed changes in the morphological profile of soil and qualitative indicators of physical-chemical properties of grey Cinnamonic soils during cultivation. İn newly irrigated grey Cinnamonic soils, the cultivated layer (25-30 cm thick) is not fully formed, new arable (A1-22-27 cm) and subsurface horizons (A2-15-16 cm) have been formed and are somewhat compacted, the structure is deteriorated, the level of carbonate and gypsum horizons is lowered. The profile of irrigated soils differs sharply from virgin and newly irrigated soils, has a clear colour differentation; a cultivated layer is formed (thickness - 52-56 cm), the arable horizon is A1-25-28 cm, subsoil - A2-24-26 cm, the illuvial-carbonate horizon is poorly expressed, down to 96-101 cm. Long time-irrigated (irrigation-accumulative) soils under the influence of long-term irrigation with turbid waters and constant cultivation have lost the signs of zonal primary soils and acquired a special type of soil profile – a monotonous grayish-brownish colour, uniformity of profile and composition, a fully formed cultivated layer with a thickness of 65-70 cm; burried horizons are found at a depth of 61-83 cm. A distinctive feature of the irrigated and irrigation-accumulative (long-irrigated) variants of grey Cinnamonic soils – an increase in the microaggregates content, a high content of physical clay (60.8-64.3%), which, when compared with the non-flush type of water regime (virgin), causes not very high humus content of the upper (0-25 and 25-50 cm of soil) horizons (2.29 and 1.78% humus), their weak resistance to the destructive action of water (See Tables 2 and 3). The content of waterresisant aggregates >0.25 mm in layers (0.25 cm) of the soil in comparison with virgin (54.08%) decreases to 35.83% in newly irrigated, in irrigated - to 38.23 % and in irrigation-accumulative (long-irrigated) - up to 40.40% (See Table 4); the highest values of the coefficient of variation of density (CV = 13.54), with a standard deviation (SD = 0.161) are observed in newly irrigated soils (See Table 5). A high bottom erosive flow rate was noted in virgin soils is 0.070-0.072 m/s, somewhat less - in irrigated (0.050–0.063 m/s), in long-irrigated (irrigation-accumulative) (0.048–0.050 m/s) and in newly irrigated soils - 0.048-0.049 m/s (See Table 6). The highest value of porosity, with a solid phase density of 2.65-2.67 g/cm3 , is noted on non-irrigated (virgin) soils (49-55%), in long-irrigated (irrigation-accumulative) soils, it decreases to 47-49%, and on irrigated at a solid phase density of 2.66-2.77 g/cm3 corresponded within the permissible values (51-52%) (See Table 6). The values of the weighted average diameter of water-resistant aggregates decreased from virgin to newly irrigated and to long-irrigated (irrigation-accumulative) soils (from 0.67- 0.74 mm to 0.27-0.31 mm) (See Fig. 1). The highest value of the ratio of anti-erosion resistance to erosion flow velocity was observed for virgin grey Cinnamonic soils (0,0710±0,102 m/s). The maximum average height of roughness protrusions was noted in long-irrigated (irrigation-accumulative) soils (0.27 mm), then irrigated (0.25 mm), and the smallest - in newly irrigated (0.19 mm) soils (See Table 7). We revealed that depending on the age of their irrigation, the anti-erosion resistance of grey Cinnamonic soils, as the bottom erosion flow rate and anti-erosion resistance decrease, can be arranged in the following row: virgin soils → irrigated → longirrigated → newly irrigated. Based on the results obtained, we determined the place of grey Cinnamonic soils in the international classification system WRB (2014): Virgin soils - Saturated gley calcareous heavy loamy - Duric Gleyic Calcic Kastanozems (Loamic); Newly irrigated Grey Cinnamonic (20-25 years old) - Powerful new irrigated calcareous heavy loamy Grey Cinnamonic - Someric Calcic Kastanozems (Loamic); Irrigated Grey Cinnamonic (about 100 years old) - Powerful cultivated irrigated calcareous heavy loamy - Someric Kastanozems (Anthric, Loamic); For a long time-irrigated Grey Cinnamonic (over 300 years old) - Powerful gley cultivated for a long time irrigated calcareous heavy loamy Grey Cinnamonic - Gleyic Petrocalcic Kastanozems (Anthric, Loamic). The paper contains 1 Figures, 7 Tables, and 46 References.","PeriodicalId":37153,"journal":{"name":"Vestnik Tomskogo Gosudarstvennogo Universiteta-Biologiya","volume":null,"pages":null},"PeriodicalIF":0.4000,"publicationDate":"2021-01-01","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Vestnik Tomskogo Gosudarstvennogo Universiteta-Biologiya","FirstCategoryId":"1085","ListUrlMain":"https://doi.org/10.17223/19988591/56/2","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"Q4","JCRName":"BIOLOGY","Score":null,"Total":0}
引用次数: 0

Abstract

The dry subtropical zone of Azerbaijan is located in an erosion-hazardous zone, and irrigation erosion manifests itself on an area of more than 255 thousand hectares. The damage caused by irrigation erosion to the agriculture of the republic is manifested not only in the destruction of the soil structure, but also in the removal of nutrients from the soil. At the same time, the patterns of change in the anti-erosion resistance of grey Cinnomanic soils /Luvic Calcisols /Luvic-Calcic Kastanozems (according to the classification of the USSR), grey Cinnamonic soils (according to the classification of Azerbaijan), (on WRB (2014)-Haplic Kastanozems / Haplic Calcisols) in the dry subtropical zone of Azerbaijan, depending on the age of irrigation, are diverse and not fully studied. Therefore, conducting research in this direction and assessing the antierosion resistance of grey Cinnamonic soils is relevant for Azerbaijan. The aim of this research is to study the changing of the anti-erosion resistance of irrigated grey Cinnomanic soils in the foothill and plain areas of the dry subtropical zone of the republic, depending on the age of irrigation. Based on the results obtained, the place of grey Cinnomanic soils in the international classification system WRB (2014) was determined. The research was carried out on grey Cinnomanic soils of heavy loamy and light clayey granulometric composition of the foothills and plains of the dry subtropical zone of different irrigation periods, in the territories: Grey Cinnomanic (virgin soils) – Beylagan (39°46'02.2''N, 47°36'13.3''E) and Yevlakh region (40°60'67.75''N, 47°17'02.71''E); Newly Irrigated Grey Cinnamonic (20-25 years old) – Agdash region (40°63'24.62''N, 47°49'11.92''E) and Geokchay region (40°37'10.5''N, 47°44'29.5''E); Irrigated Grey Cinnamonic (about 100 years old) – Bilasuvar (39°48'36.49''N, 48°43'35.24''E), Yevlakh (40°44I 34.18''N, 46°96'51.13''E), kshu (40°55'39.53''N, 48°35'04.18''E), and Aghstafa region (41°06'11.17''N, 45°28'07.32''E); For a Long Time-Irrigated Grey Cinnamonic (about 300 years old) – Bilasuvar (39°44'25.56''N, 48°42'52.72''E) and Beylagan region (39°76'45.13''N, 47°59'13.50''E). The research methods are comparative-geographical (geographical patterns of distribution of these soils according to the granulometric competition and humus content of the arable horizon) and comparative-analytical. On the plots, soil sections were laid, a morphological description was carried out, soil samples were taken from the genetic horizons (Field guide of soils in Russia (2008), FAO. Guidelines for soil description (2006), IUSS Working Group WRB. World Reference Base of Soil Resources 2014, update 2015, Kallas and Tanzybayev (2001)). The anti-erosion resistance of soils was determined by the bottom erosion flow rate-according to Kuznetsov MS. (1981), the water resistance of the aggregates – by methods of dry and “wet” aggregate analysis according to Savvinov, the specific gravity of the solid phase – by the pycnometric method, the granulometric compotition – by the pipette method, soil density – with a drill according to the generally accepted method (Arinushkina, 1970; Vadyunina and Korchagina, 1986]. The value of the protrusions of soil roughness was determined by the ratio ∆ = 0.7 dw, where dw is the weighted average diameter of the water-resistant aggregates. The value dw was calculated based on the results of the structural analysis of the soil by the Savvinov method at the initial moisture content W (Grigoryev and Makkaveev, 1979), the content of total humus – according to Tyurin, modified bu Nikitin, cellulolytic activity – by application method for the decomposition of cotton canvases (Kazeev, Kolesnikov and Valkov, 2003). Depending on the age of irrigation, we revealed changes in the morphological profile of soil and qualitative indicators of physical-chemical properties of grey Cinnamonic soils during cultivation. İn newly irrigated grey Cinnamonic soils, the cultivated layer (25-30 cm thick) is not fully formed, new arable (A1-22-27 cm) and subsurface horizons (A2-15-16 cm) have been formed and are somewhat compacted, the structure is deteriorated, the level of carbonate and gypsum horizons is lowered. The profile of irrigated soils differs sharply from virgin and newly irrigated soils, has a clear colour differentation; a cultivated layer is formed (thickness - 52-56 cm), the arable horizon is A1-25-28 cm, subsoil - A2-24-26 cm, the illuvial-carbonate horizon is poorly expressed, down to 96-101 cm. Long time-irrigated (irrigation-accumulative) soils under the influence of long-term irrigation with turbid waters and constant cultivation have lost the signs of zonal primary soils and acquired a special type of soil profile – a monotonous grayish-brownish colour, uniformity of profile and composition, a fully formed cultivated layer with a thickness of 65-70 cm; burried horizons are found at a depth of 61-83 cm. A distinctive feature of the irrigated and irrigation-accumulative (long-irrigated) variants of grey Cinnamonic soils – an increase in the microaggregates content, a high content of physical clay (60.8-64.3%), which, when compared with the non-flush type of water regime (virgin), causes not very high humus content of the upper (0-25 and 25-50 cm of soil) horizons (2.29 and 1.78% humus), their weak resistance to the destructive action of water (See Tables 2 and 3). The content of waterresisant aggregates >0.25 mm in layers (0.25 cm) of the soil in comparison with virgin (54.08%) decreases to 35.83% in newly irrigated, in irrigated - to 38.23 % and in irrigation-accumulative (long-irrigated) - up to 40.40% (See Table 4); the highest values of the coefficient of variation of density (CV = 13.54), with a standard deviation (SD = 0.161) are observed in newly irrigated soils (See Table 5). A high bottom erosive flow rate was noted in virgin soils is 0.070-0.072 m/s, somewhat less - in irrigated (0.050–0.063 m/s), in long-irrigated (irrigation-accumulative) (0.048–0.050 m/s) and in newly irrigated soils - 0.048-0.049 m/s (See Table 6). The highest value of porosity, with a solid phase density of 2.65-2.67 g/cm3 , is noted on non-irrigated (virgin) soils (49-55%), in long-irrigated (irrigation-accumulative) soils, it decreases to 47-49%, and on irrigated at a solid phase density of 2.66-2.77 g/cm3 corresponded within the permissible values (51-52%) (See Table 6). The values of the weighted average diameter of water-resistant aggregates decreased from virgin to newly irrigated and to long-irrigated (irrigation-accumulative) soils (from 0.67- 0.74 mm to 0.27-0.31 mm) (See Fig. 1). The highest value of the ratio of anti-erosion resistance to erosion flow velocity was observed for virgin grey Cinnamonic soils (0,0710±0,102 m/s). The maximum average height of roughness protrusions was noted in long-irrigated (irrigation-accumulative) soils (0.27 mm), then irrigated (0.25 mm), and the smallest - in newly irrigated (0.19 mm) soils (See Table 7). We revealed that depending on the age of their irrigation, the anti-erosion resistance of grey Cinnamonic soils, as the bottom erosion flow rate and anti-erosion resistance decrease, can be arranged in the following row: virgin soils → irrigated → longirrigated → newly irrigated. Based on the results obtained, we determined the place of grey Cinnamonic soils in the international classification system WRB (2014): Virgin soils - Saturated gley calcareous heavy loamy - Duric Gleyic Calcic Kastanozems (Loamic); Newly irrigated Grey Cinnamonic (20-25 years old) - Powerful new irrigated calcareous heavy loamy Grey Cinnamonic - Someric Calcic Kastanozems (Loamic); Irrigated Grey Cinnamonic (about 100 years old) - Powerful cultivated irrigated calcareous heavy loamy - Someric Kastanozems (Anthric, Loamic); For a long time-irrigated Grey Cinnamonic (over 300 years old) - Powerful gley cultivated for a long time irrigated calcareous heavy loamy Grey Cinnamonic - Gleyic Petrocalcic Kastanozems (Anthric, Loamic). The paper contains 1 Figures, 7 Tables, and 46 References.
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阿塞拜疆干燥亚热带地区灌溉灰褐色土壤抗侵蚀强度的变化,取决于灌溉的时效
阿塞拜疆干燥的亚热带地区位于侵蚀危险区,灌溉侵蚀面积超过25.5万公顷。灌溉侵蚀对共和国农业造成的损害不仅表现在土壤结构的破坏上,而且表现在土壤养分的流失上。与此同时,阿塞拜疆干燥亚热带灰色肉桂土/Luvic calisols /Luvic- calcium Kastanozems(根据苏联的分类),灰色肉桂土(根据阿塞拜疆的分类),(WRB (2014)-Haplic Kastanozems / Haplic Calcisols)的抗侵蚀性变化模式是多种多样的,取决于灌溉年龄,尚未得到充分研究。因此,开展这一方向的研究和评价灰色褐土的抗侵蚀能力对阿塞拜疆具有重要意义。本研究的目的是研究在共和国干旱的亚热带丘陵和平原地区,灌溉后灰土的抗侵蚀能力随灌溉年限的变化。在此基础上,确定了灰色肉桂土在国际分类系统WRB(2014)中的位置。研究了亚热带干旱地区不同灌溉时期丘陵和平原的重壤土和轻粘土颗粒组成的灰色肉桂土,在以下地区进行了研究:灰色肉桂土(处女地)- Beylagan(39°46'02.2 " N, 47°36'13.3 " E)和Yevlakh地区(40°60'67.75 " N, 47°17'02.71 " E);新灌溉的灰肉桂(20-25岁)- Agdash地区(北纬40°63′24.62”,东经47°49′11.92”)和Geokchay地区(北纬40°37′10.5”,东经47°44′29.5”);灌溉灰桂树(约100年)- Bilasuvar(北纬39°48′36.49”,东经48°43′35.24”),Yevlakh(北纬40°44′34.18”,东经46°96′51.13”),kshu(北纬40°55′39.53”,东经48°35′04.18”)和Aghstafa地区(北纬41°06′11.17”,东经45°28′07.32”);长期灌溉的灰色肉桂树(约300岁)- Bilasuvar(39°44'25.56”N, 48°42'52.72”E)和Beylagan地区(39°76'45.13”N, 47°59'13.50”E)。研究方法有比较地理法(根据可耕层的粒度竞争和腐殖质含量确定这些土壤的地理分布模式)和比较分析法。在这些地块上铺设了土壤剖面,进行了形态描述,并从遗传层采集了土壤样本(《俄罗斯土壤现场指南》(2008),粮农组织)。土壤描述指南(2006),国际土壤研究所WRB工作组。世界土壤资源参考数据库2014,2015年更新,Kallas and Tanzybayev(2001))。根据库兹涅佐夫女士(1981)的说法,土壤的抗侵蚀性是由底部侵蚀流速率确定的;根据Savvinov的说法,通过干和“湿”团聚体分析方法确定团聚体的抗水能力;固体相的比重-通过比重法确定;颗粒组成-通过吸管法确定;土壤密度-根据普遍接受的方法(Arinushkina, 1970;Vadyunina and Korchagina, 1986]。土壤粗糙度凸出值由比值∆= 0.7 dw确定,其中dw为防水团聚体的加权平均直径。dw值是根据Savvinov方法对土壤结构分析的结果计算得出的,初始含水量W (Grigoryev和Makkaveev, 1979),总腐殖质含量-根据Tyurin,修改了Nikitin,纤维素水解活性-采用分解棉质帆布的应用方法(Kazeev, Kolesnikov和Valkov, 2003)。根据灌溉年限的不同,揭示了灰褐土在栽培过程中土壤形态特征和理化性质定性指标的变化。İn新灌溉灰色褐土,栽培层(25 ~ 30 cm厚)未完全形成,新的可耕层(a1 ~ 22 ~ 27 cm)和地下层(a2 ~ 15 ~ 16 cm)已形成并有些压实,结构恶化,碳酸盐层和石膏层水平降低。灌水土壤的剖面与未灌水土壤和新灌水土壤有明显的不同,具有明显的色差;形成耕地层(厚度- 52 ~ 56 cm),耕地层位a1 ~ 25 ~ 28 cm,底土层位a2 ~ 24 ~ 26 cm,地表—碳酸盐岩层位表现不明显,低至96 ~ 101 cm。长期灌水(灌积)土壤在混浊水长期灌溉和持续耕作的影响下,失去了地带性原生土壤的特征,形成了一种特殊类型的土壤剖面——单调的灰褐色,剖面和成分均匀,完全形成的栽培层厚度为65 ~ 70 cm;在61-83厘米的深度发现了致密层。
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