R. Čepulienė, A. Marcinkevičienė, R. Velička, R. Kosteckas, R. Pupalienė
{"title":"Effect of Spring Oilseed Rape Crop Density on Plant Root Biomass and Soil Enzymes activity/Suvirapsi Taimiku Tiheduse Moju Taimejuurte Biomassile Ja Mulla Ensuumide Aktiivsusele","authors":"R. Čepulienė, A. Marcinkevičienė, R. Velička, R. Kosteckas, R. Pupalienė","doi":"10.3176/ECO.2013.1.06","DOIUrl":null,"url":null,"abstract":"INTRODUCTION Soil health is the capacity of soil to function as a vital living system within ecosystem and land-use boundaries, to sustain plant and animal productivity and water and air quality, and to promote plant and animal health. To evaluate sustainability of agricultural practices, assessment of soil health using various indicators of soil quality is needed (Doran & Zeiss, 2000). Soil enzyme activity can be used as an indicator of soil quality for assessing the sustainability of agricultural ecosystems (Gianfreda et al., 2005; Roldan et al., 2005). Soil enzymes are important in catalysing innumerable reactions involved in the decomposition of organic matter, cycling of nutrients, and formation of organic matter structure (Bandick & Dick, 1999; Kandeler et al., 1999; Liu et al., 2008; Melero et al., 2008). Enzyme activity is closely related to other important indicators of biological activity: respiration intensity, nitrification ability, total amount of microorganisms, and even more strongly to soil organic carbon content, content of available [P.sub.2][O.sub.5] and [K.sub.2]O, soil acidity, and crop yield (Schimner & Sonnleitner, 1996; Bandick & Dick, 1999; Svirskiene, 1999; Liu et al., 2008). Enzymes that catalyse a wide range of soil biological processes offer a useful assessment of soil 'function', and common enzymes, such as urease and saccharase, fit into this category (Burns & Dick, 2005). Urease catalyses the hydrolysis of urea to C[O.sub.2] and N[H.sub.3], which is of particular interest because urea is an important nitrogen fertilizer. Urease is released from living and disintegrated microbial cells, and in the soil it can exist as an extracellular enzyme absorbed on clay particles or encapsulated in humic complexes (Nannipieri, 1994; Schimner & Sonnleitner, 1996). Saccharase catalyses the hydrolysis of saccharose into glucose and fructose and characterizes change processes of organic carbon compounds (Schimner & Sonnleitner, 1996). Several studies show that enzyme activities can be used as early indicators of changes in soil properties originated by soil and crop management practices such as tillage, crop rotation, residue management, and fertilization (Bandick & Dick, 1999; Kandeler et al., 1999; Acosta-Martinez et al., 2003; Roldan et al., 2005; Melero et al., 2008; Zakarauskaite et al., 2008; Wang et al., 2011). Acosta-Martinez et al. (2003) reported that the trends of the enzyme activities as affected by management depend on the soil, but in general crop rotation and conservation tillage increase enzyme activities. According to Bandick & Dick (1999), enzyme activities are generally higher in continuous grass fields than in cultivated fields. In cultivated systems, enzyme activity is higher where organic residues have been added as compared to treatments without organic amendments. Zakarauskaite et al. (2005) found higher urease activity in the soil where cereals were grown and higher saccharase and dehydrogenase activity where perennial grasses were grown. Marcinkeviciene et al. (2011) established that with increasing spring rape crop density from 100 to 450 plants [m.sup.-2], compared with the thinnest crop (50-100 plants [m.sup.-2]), the activity of urease in the soil does not change significantly, while the activity of saccharase significantly increases (by 31-53%). According to the data of Zakarauskaite et al. (2008), long-term application of mineral fertilizers inhibits the activity of urease and saccharase. Roots are the primary tools for the uptake of all mineral elements and water required for crop growth. Due to this fact, root growth and development are highly plastic (Neumann & Martinoia, 2002) and depend on climatic factors (Kjellstrom & Kirchmann, 1994), soil properties (Barraclough, 1989), crop density (Liakas et al., 2006), and fertilization (Govahi & Saffari, 2006). Roots store not only nutrients and carbohydrate reserves for plants, but they also host microbes (Chung et al. …","PeriodicalId":262667,"journal":{"name":"Estonian Journal of Ecology","volume":"1 1","pages":"0"},"PeriodicalIF":0.0000,"publicationDate":"2013-03-01","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"3","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Estonian Journal of Ecology","FirstCategoryId":"1085","ListUrlMain":"https://doi.org/10.3176/ECO.2013.1.06","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"","JCRName":"","Score":null,"Total":0}
引用次数: 3

摘要

土壤健康是指土壤在生态系统和土地利用边界内作为重要生命系统发挥作用,维持动植物生产力、水和空气质量以及促进动植物健康的能力。为了评估农业实践的可持续性,需要使用各种土壤质量指标来评估土壤健康(Doran & Zeiss, 2000)。土壤酶活性可作为评估农业生态系统可持续性的土壤质量指标(Gianfreda et al., 2005;Roldan et al., 2005)。土壤酶在催化有机质分解、养分循环和有机质结构形成的无数反应中起着重要作用(Bandick & Dick, 1999;Kandeler et al., 1999;Liu et al., 2008;Melero et al., 2008)。酶活性与其他重要的生物活性指标:呼吸强度、硝化能力、微生物总量密切相关,而与土壤有机碳含量、速效氮含量[P.sub.2][O.sub. 2]密切相关。[5]和[K.sub.][2]土壤酸度对作物产量的影响[j];Bandick & Dick, 1999;Svirskiene, 1999;刘等人,2008)。催化多种土壤生物过程的酶提供了对土壤“功能”的有用评估,而常见的酶,如脲酶和糖化酶,就属于这一类(Burns & Dick, 2005)。脲酶催化尿素水解成C[O.sub]。[2]和[H.sub.][3],这是特别有趣的,因为尿素是一种重要的氮肥。脲酶从活的和分解的微生物细胞中释放出来,在土壤中,它可以作为一种细胞外酶被粘土颗粒吸收或被包裹在腐殖质复合体中(Nannipieri, 1994;Schimner & Sonnleitner, 1996)。糖酶催化蔗糖水解成葡萄糖和果糖,表征有机碳化合物的变化过程(Schimner & Sonnleitner, 1996)。几项研究表明,酶活性可以作为土壤和作物管理措施(如耕作、作物轮作、残留物管理和施肥)引起的土壤性质变化的早期指标(Bandick & Dick, 1999;Kandeler et al., 1999;Acosta-Martinez et al., 2003;Roldan et al., 2005;Melero et al., 2008;Zakarauskaite et al., 2008;Wang et al., 2011)。Acosta-Martinez等人(2003)报道,受管理影响的酶活性趋势取决于土壤,但一般来说轮作和保护性耕作会增加酶活性。根据Bandick & Dick(1999)的研究,连续草地的酶活性通常高于耕地。在栽培系统中,与不添加有机添加剂的处理相比,添加有机残留物的处理酶活性更高。Zakarauskaite等人(2005)发现,种植谷物的土壤中脲酶活性较高,而种植多年生草的土壤中糖化酶和脱氢酶活性较高。Marcinkeviciene等人(2011)发现,随着春油菜种植密度从100株增加到450株[m.sup. 2011]。与最薄作物(50-100株[m.sup. 2])相比,土壤脲酶活性变化不显著,而蔗糖酶活性显著增加(提高31-53%)。Zakarauskaite et al.(2008)的数据表明,长期施用矿物肥会抑制脲酶和糖酶的活性。根是吸收作物生长所需的所有矿物元素和水分的主要工具。由于这一事实,根的生长和发育具有高度的可塑性(Neumann & Martinoia, 2002),并取决于气候因素(Kjellstrom & Kirchmann, 1994)、土壤特性(Barraclough, 1989)、作物密度(Liakas等人,2006)和施肥(Govahi & Saffari, 2006)。根不仅为植物储存营养和碳水化合物储备,还为微生物提供宿主(Chung et al. . ...)
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Effect of Spring Oilseed Rape Crop Density on Plant Root Biomass and Soil Enzymes activity/Suvirapsi Taimiku Tiheduse Moju Taimejuurte Biomassile Ja Mulla Ensuumide Aktiivsusele
INTRODUCTION Soil health is the capacity of soil to function as a vital living system within ecosystem and land-use boundaries, to sustain plant and animal productivity and water and air quality, and to promote plant and animal health. To evaluate sustainability of agricultural practices, assessment of soil health using various indicators of soil quality is needed (Doran & Zeiss, 2000). Soil enzyme activity can be used as an indicator of soil quality for assessing the sustainability of agricultural ecosystems (Gianfreda et al., 2005; Roldan et al., 2005). Soil enzymes are important in catalysing innumerable reactions involved in the decomposition of organic matter, cycling of nutrients, and formation of organic matter structure (Bandick & Dick, 1999; Kandeler et al., 1999; Liu et al., 2008; Melero et al., 2008). Enzyme activity is closely related to other important indicators of biological activity: respiration intensity, nitrification ability, total amount of microorganisms, and even more strongly to soil organic carbon content, content of available [P.sub.2][O.sub.5] and [K.sub.2]O, soil acidity, and crop yield (Schimner & Sonnleitner, 1996; Bandick & Dick, 1999; Svirskiene, 1999; Liu et al., 2008). Enzymes that catalyse a wide range of soil biological processes offer a useful assessment of soil 'function', and common enzymes, such as urease and saccharase, fit into this category (Burns & Dick, 2005). Urease catalyses the hydrolysis of urea to C[O.sub.2] and N[H.sub.3], which is of particular interest because urea is an important nitrogen fertilizer. Urease is released from living and disintegrated microbial cells, and in the soil it can exist as an extracellular enzyme absorbed on clay particles or encapsulated in humic complexes (Nannipieri, 1994; Schimner & Sonnleitner, 1996). Saccharase catalyses the hydrolysis of saccharose into glucose and fructose and characterizes change processes of organic carbon compounds (Schimner & Sonnleitner, 1996). Several studies show that enzyme activities can be used as early indicators of changes in soil properties originated by soil and crop management practices such as tillage, crop rotation, residue management, and fertilization (Bandick & Dick, 1999; Kandeler et al., 1999; Acosta-Martinez et al., 2003; Roldan et al., 2005; Melero et al., 2008; Zakarauskaite et al., 2008; Wang et al., 2011). Acosta-Martinez et al. (2003) reported that the trends of the enzyme activities as affected by management depend on the soil, but in general crop rotation and conservation tillage increase enzyme activities. According to Bandick & Dick (1999), enzyme activities are generally higher in continuous grass fields than in cultivated fields. In cultivated systems, enzyme activity is higher where organic residues have been added as compared to treatments without organic amendments. Zakarauskaite et al. (2005) found higher urease activity in the soil where cereals were grown and higher saccharase and dehydrogenase activity where perennial grasses were grown. Marcinkeviciene et al. (2011) established that with increasing spring rape crop density from 100 to 450 plants [m.sup.-2], compared with the thinnest crop (50-100 plants [m.sup.-2]), the activity of urease in the soil does not change significantly, while the activity of saccharase significantly increases (by 31-53%). According to the data of Zakarauskaite et al. (2008), long-term application of mineral fertilizers inhibits the activity of urease and saccharase. Roots are the primary tools for the uptake of all mineral elements and water required for crop growth. Due to this fact, root growth and development are highly plastic (Neumann & Martinoia, 2002) and depend on climatic factors (Kjellstrom & Kirchmann, 1994), soil properties (Barraclough, 1989), crop density (Liakas et al., 2006), and fertilization (Govahi & Saffari, 2006). Roots store not only nutrients and carbohydrate reserves for plants, but they also host microbes (Chung et al. …
求助全文
通过发布文献求助,成功后即可免费获取论文全文。 去求助
来源期刊
自引率
0.00%
发文量
0
×
引用
GB/T 7714-2015
复制
MLA
复制
APA
复制
导出至
BibTeX EndNote RefMan NoteFirst NoteExpress
×
提示
您的信息不完整,为了账户安全,请先补充。
现在去补充
×
提示
您因"违规操作"
具体请查看互助需知
我知道了
×
提示
确定
请完成安全验证×
copy
已复制链接
快去分享给好友吧!
我知道了
右上角分享
点击右上角分享
0
联系我们:info@booksci.cn Book学术提供免费学术资源搜索服务,方便国内外学者检索中英文文献。致力于提供最便捷和优质的服务体验。 Copyright © 2023 布克学术 All rights reserved.
京ICP备2023020795号-1
ghs 京公网安备 11010802042870号
Book学术文献互助
Book学术文献互助群
群 号:604180095
Book学术官方微信