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Journal articles on the topic 'Soil plant interactions'

Author: Grafiati

Published: 10 December 2022

Last updated: 31 July 2025

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1

Krumins, Jennifer Adams, Nina M. Goodey, and Frank Gallagher. "Plant–soil interactions in metal contaminated soils." Soil Biology and Biochemistry 80 (January 2015): 224–31. http://dx.doi.org/10.1016/j.soilbio.2014.10.011.

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2

Fernando, Denise R. "Plant–Metal Interactions in the Context of Climate Change." Stresses 2, no. 1 (2022): 79–89. http://dx.doi.org/10.3390/stresses2010007.

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Expanding fundamental understanding of the complex and far-reaching impacts of anthropogenic climate change is essential for formulating mitigation strategies. There is abundant evidence of ongoing damage and threat to plant health across both natural and cultivated ecosystems, with potentially immeasurable cost to humanity and the health of the planet. Plant–soil systems are multi-faceted, incorporating key variables that are individually and interactively affected by climatic factors such as rainfall, solar radiation, air temperature, atmospheric CO2, and pollution. This synthesis focuses on

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3

Fox, R. L., N. V. Hue, R. C. Jones, and R. S. Yost. "Plant-soil interactions associated with acid, weathered soils." Plant and Soil 134, no. 1 (1991): 65–72. http://dx.doi.org/10.1007/bf00010718.

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4

Soto, B., and F. Diaz-Fierros. "Interactions Between Plant Ash Leachates and Soil." International Journal of Wildland Fire 3, no. 4 (1993): 207. http://dx.doi.org/10.1071/wf9930207.

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We studied a) leaching of Ulex, Pinus and Eucalyptus ashes; b) leaching from the surface layer (0 - 5 cm) of 6 types of soil subjected to thermal shock at a range of temperatures equivalent to those reached in a wildfire (25-degrees-C to 700-degrees-C); and c) leaching of Ulex, Pinus and Eucalyptus ashes through a subsurface soil layer not subjected to thermal shock. Element release from plant ashes and heat-treated soils was highly dependent on the solubility of the principal chemical forms in which that element occurred. The monovalent cations Na and K, largely present as chlorides and carbo

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5

M, Meena. "Tomato: A Model Plant to Study Plant-Pathogen Interactions." Food Science & Nutrition Technology 4, no. 1 (2019): 1–6. http://dx.doi.org/10.23880/fsnt-16000171.

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Tomato (Solanum lycopersicum) is a very important vegetable plant in the worldwide because of its importance as food, quality of fruit, improves productivity, and resistance to biotic and abiotic stresses. Tomato has been extensively used not just for food however conjointly as a research (plant-pathogen interactions) material. Generally, most of the tomato traits are agronomically imperative and cannot be studied using other model plant systems. It belongs to family Solanaceae and intimately associated with several commercially important plants like potato, tobacco, peppers, eggplant, and pet

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6

Lazarus, Brynne E., James H. Richards, Victor P. Claassen, Ryan E. O’Dell, and Molly A. Ferrell. "Species specific plant-soil interactions influence plant distribution on serpentine soils." Plant and Soil 342, no. 1-2 (2011): 327–44. http://dx.doi.org/10.1007/s11104-010-0698-2.

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7

Zhang, Hao, and Wei Zhang. "Plant–Soil Interactions in Karst Regions." Forests 14, no. 5 (2023): 922. http://dx.doi.org/10.3390/f14050922.

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8

Defossez, Emmanuel, Benoît Courbaud, Benoît Marcais, Wilfried Thuiller, Elena Granda, and Georges Kunstler. "Do interactions between plant and soil biota change with elevation? A study on Fagus sylvatica." Biology Letters 7, no. 5 (2011): 699–701. http://dx.doi.org/10.1098/rsbl.2011.0236.

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Theoretical models predict weakening of negative biotic interactions and strengthening of positive interactions with increasing abiotic stress. However, most empirical tests have been restricted to plant–plant interactions. No empirical study has examined theoretical predictions of interactions between plants and below-ground micro-organisms, although soil biota strongly regulates plant community composition and dynamics. We examined variability in soil biota effects on tree regeneration across an abiotic gradient. Our candidate tree species was European beech ( Fagus sylvatica L.), whose rege

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9

Pissolito, Clara, Irene A. Garibotti, Santiago A. Varela, et al. "Water-mediated changes in plant–plant and biological soil crust–plant interactions in a temperate forest ecosystem." Web Ecology 19, no. 1 (2019): 27–38. http://dx.doi.org/10.5194/we-19-27-2019.

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Abstract. In the quest to understand how biotic interactions respond to climate change, one area that remains poorly explored is how interactions involving organisms other than vascular plants will respond. However the interactions between plants and biological soil crusts (BSCs) are relevant in many ecosystems and they will likely respond uniquely to climate change. Simultaneous considerations of both plant–plant and plant–BSC interactions may substantially improve our understanding of this topic. The aim of this study is to assess whether water availability differentially affects the biotic

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10

Prisa, Domenico. "Soil Microbiota and Its Plant Interactions." International Journal of Current Research and Review 14, no. 08 (2022): 40–46. http://dx.doi.org/10.31782/ijcrr.2022.14807.

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Microbial biodiversity comprises microorganisms belonging to all kingdoms: from prokaryotes (archaea and bacteria) to eukaryotes (fungi, microalgae, moulds, yeasts and protists). Microorganisms make up a large part of the earth’s biomass, are extraordinarily diverse and are widespread in all habitats. More than two thirds of the total biodiversity consists of bacteria, while archaea and eukaryotes occupy less than one third. Microorganisms interact with each other and with the biotic and abiotic components of their environment, creating ecosystems in which there is a dynamic balance between th

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11

Etherington, J. R., R. J. Wright, V. C. Baligar, and R. P. Murrmann. "Plant--Soil Interactions at Low pH." Journal of Ecology 81, no. 1 (1993): 204. http://dx.doi.org/10.2307/2261248.

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12

REDDY, M. R. "Plant and Soil Interfaces and Interactions." Soil Science 147, no. 4 (1989): 308. http://dx.doi.org/10.1097/00010694-198904000-00011.

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&NA;. "Plant-Soil Interactions at Low pH." Soil Science 154, no. 1 (1992): 84. http://dx.doi.org/10.1097/00010694-199207000-00013.

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14

Szott, Lawrence T., Erick C. M. Fernandes, and Pedro A. Sanchez. "Soil-plant interactions in agroforestry systems." Forest Ecology and Management 45, no. 1-4 (1991): 127–52. http://dx.doi.org/10.1016/0378-1127(91)90212-e.

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15

Uren, N. C. "Plant-soil interactions at low pH." Soil Biology and Biochemistry 25, no. 7 (1993): 971. http://dx.doi.org/10.1016/0038-0717(93)90101-g.

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16

Horel, Ágota. "Soil–Plant–Water Systems and Interactions." Plants 13, no. 3 (2024): 358. http://dx.doi.org/10.3390/plants13030358.

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17

Aaronson, Julia K., Andrew Kulmatiski, Leslie E. Forero, Josephine Grenzer, and Jeanette M. Norton. "Are Plant–Soil Feedbacks Caused by Many Weak Microbial Interactions?" Biology 12, no. 11 (2023): 1374. http://dx.doi.org/10.3390/biology12111374.

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We used high-throughput sequencing and multivariate analyses to describe soil microbial community composition in two four-year field plant–soil feedback (PSF) experiments in Minnesota, USA and Jena, Germany. In descending order of variation explained, microbial community composition differed between the two study sites, among years, between bulk and rhizosphere soils, and among rhizosphere soils cultivated by different plant species. To try to identify soil organisms or communities that may cause PSF, we correlated plant growth responses with the microbial community composition associated with

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18

Moore, Amber, Steve Hines, Bradford Brown, et al. "Soil–Plant Nutrient Interactions on Manure‐Enriched Calcareous Soils." Agronomy Journal 106, no. 1 (2014): 73–80. http://dx.doi.org/10.2134/agronj2013.0345.

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19

Hackett, Sean C., Alison J. Karley, and Alison E. Bennett. "Unpredicted impacts of insect endosymbionts on interactions between soil organisms, plants and aphids." Proceedings of the Royal Society B: Biological Sciences 280, no. 1768 (2013): 20131275. http://dx.doi.org/10.1098/rspb.2013.1275.

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Ecologically significant symbiotic associations are frequently studied in isolation, but such studies of two-way interactions cannot always predict the responses of organisms in a community setting. To explore this issue, we adopt a community approach to examine the role of plant–microbial and insect–microbial symbioses in modulating a plant–herbivore interaction. Potato plants were grown under glass in controlled conditions and subjected to feeding from the potato aphid Macrosiphum euphorbiae . By comparing plant growth in sterile, uncultivated and cultivated soils and the performance of M. e

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20

Dodd, J. C. "The Role of Arbuscular Mycorrhizal Fungi in Agro- and Natural Ecosystems." Outlook on Agriculture 29, no. 1 (2000): 55–62. http://dx.doi.org/10.5367/000000000101293059.

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Symbionts called ‘mycorrhizal fungi’ occur in most biomes on earth, and are a fundamental reason for plant growth and development on the planet. The most common group of mycorrhizal fungi is that of the arbuscular mycorrhizal fungi (AMF), which colonize the roots of over 80% of land plant families, but they cannot as yet be cultured away from the host plant. AMF are primarily responsible for nutrient transfer from soil to plant, but have other roles such as soil aggregation, protection of plants against drought stress and soil pathogens, and increasing plant diversity. This is achieved by the

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21

Głuszek, Sławomir, Lidia Sas-Paszt, Beata Sumorok, and Ryszard Kozera. "Biochar-Rhizosphere Interactions – a Review." Polish Journal of Microbiology 66, no. 2 (2017): 151–61. http://dx.doi.org/10.5604/01.3001.0010.6288.

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Biochar is a solid material of biological origin obtained from biomass carbonization, designed as a mean to reduce greenhouse gases emission and carbon sequestration in soils for a long time. Biochar has a wide spectrum of practical utilization and is applied as a promising soil improver or fertilizer in agriculture, or as a medium for soil or water remediation. Preparations of biochar increase plant growth and yielding when applied into soil and also improve plant growth conditions, mainly bio, physical and chemical properties of soil. Its physical and chemical properties have an influence on

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22

Ajibade, Sinazo, Barbara Simon, Anita Takács, and Miklós Gulyás. "Effects of Cigarette Butt Leachate on the Growth of White Mustard (Sinapis alba L.) and Soil Properties: A Preliminary Study." Pollutants 4, no. 4 (2024): 515–36. https://doi.org/10.3390/pollutants4040035.

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Cigarette butts (CBs) are emerging soil contaminants, releasing chemicals upon contact with moisture. This study examined heavy metal concentrations leached from smoked and unsmoked CBs (Pall Mall, Philip Morris, and Marlboro) into OECD artificial soil and Vertisol soil and their accumulation in white mustard (Sinapis alba L.). Key physiological parameters, including germination rate, plant height, fresh weight, and dry weight, were analyzed, along with the uptake of heavy metals (Al, Fe, Mn, Zn, Ba, Ti, and Cu) and essential elements (Ca, Mg, Na, and K). Results showed that Mn had the highest

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23

Vinale, Francesco, Krishnapillai Sivasithamparam, Emilio L. Ghisalberti, Roberta Marra, Sheridan L. Woo, and Matteo Lorito. "Trichoderma–plant–pathogen interactions." Soil Biology and Biochemistry 40, no. 1 (2008): 1–10. http://dx.doi.org/10.1016/j.soilbio.2007.07.002.

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24

Tusar, Hachib Mohammad, Md Kamal Uddin, Shamim Mia, et al. "Biochar-Acid Soil Interactions—A Review." Sustainability 15, no. 18 (2023): 13366. http://dx.doi.org/10.3390/su151813366.

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Soil acidity is a major problem of agriculture in many parts of the world. Soil acidity causes multiple problems such as nutrient deficiency, elemental toxicity and adverse effects on biological characteristics of soil, resulting in decreased crop yields and productivity. Although a number of conventional strategies including liming and use of organic and inorganic fertilizers are suggested for managing soil acidity but cost-effective and sustainable amendments are not available to address this problem. Currently, there is increasing interest in using biochar, a form of biomass derived pyrogen

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25

Diaz, Anita, Iain Green, and Damian Evans. "Heathland Restoration Techniques: Ecological Consequences for Plant-Soil and Plant-Animal Interactions." ISRN Ecology 2011 (November 10, 2011): 1–8. http://dx.doi.org/10.5402/2011/961807.

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We compare the soil and plant community development during heathland restoration on improved farmland when achieved through soil stripping with that achieved through soil acidification. We also test the potential for toxic metals to be made more available to plant and animal species as a result of these treatments. Acidification with elemental sulphur was found to be more effective than soil stripping for establishing an ericaceous sward despite the high levels of phosphate still present within the soil. However, both soil acidification and soil stripping were found to have the potential to in

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26

Schweitzer, Jennifer A., Joseph K. Bailey, Dylan G. Fischer, et al. "PLANT–SOIL–MICROORGANISM INTERACTIONS: HERITABLE RELATIONSHIP BETWEEN PLANT GENOTYPE AND ASSOCIATED SOIL MICROORGANISMS." Ecology 89, no. 3 (2008): 773–81. http://dx.doi.org/10.1890/07-0337.1.

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27

Waring, Bonnie G., Maria G. Gei, Lisa Rosenthal, and Jennifer S. Powers. "Plant–microbe interactions along a gradient of soil fertility in tropical dry forest." Journal of Tropical Ecology 32, no. 4 (2016): 314–23. http://dx.doi.org/10.1017/s0266467416000286.

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Abstract:Theoretical models predict that plant interactions with free-living soil microbes, pathogens and fungal symbionts are regulated by nutrient availability. Working along a steep natural gradient of soil fertility in a Costa Rican tropical dry forest, we examined how soil nutrients affect plant–microbe interactions using two complementary approaches. First, we measured mycorrhizal colonization of roots and soil P availability in 18 permanent plots spanning the soil fertility gradient. We measured root production, root colonization by mycorrhizal fungi, phosphatase activity and Bray P in

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28

Medyńska-Juraszek, Agnieszka, Pierre-Adrien Rivier, Daniel Rasse, and Erik J. Joner. "Biochar Affects Heavy Metal Uptake in Plants through Interactions in the Rhizosphere." Applied Sciences 10, no. 15 (2020): 5105. http://dx.doi.org/10.3390/app10155105.

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Heavy metals in soil pose a constant risk for animals and humans when entering their food chains, and limited means are available to reduce plant accumulation from more or less polluted soils. Biochar, which is made by pyrolysis of organic residues and sees increasing use as a soil amendment to mitigate anthropogenic C emissions and improve agronomic soil properties, has also been shown to reduce plant availability of heavy metals in soils. The cause for the reduction of metal uptake in plants when grown in soils enriched with biochar has generally been researched in terms of increased pH and

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29

Chauhan, Poonam, Neha Sharma, Ashwani Tapwal, et al. "Soil Microbiome: Diversity, Benefits and Interactions with Plants." Sustainability 15, no. 19 (2023): 14643. http://dx.doi.org/10.3390/su151914643.

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Plant roots aid the growth and functions of several kinds of microorganisms such as plant growth-promoting rhizobacteria, mycorrhizal fungi, endophytic bacteria, actinomycetes, nematodes, protozoans which may impart significant impacts on plant health and growth. Plant soil–microbe interaction is an intricate, continuous, and dynamic process that occurs in a distinct zone known as the rhizosphere. Plants interact with these soil microbes in a variety of ways, including competitive, exploitative, neutral, commensal, and symbiotic relationships. Both plant and soil types were found to have an im

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30

Ievinsh, Gederts. "Disentangling the Belowground Web of Biotic Interactions in Temperate Coastal Grasslands: From Fundamental Knowledge to Novel Applications." Land 12, no. 6 (2023): 1209. http://dx.doi.org/10.3390/land12061209.

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Grasslands represent an essential part of terrestrial ecosystems. In particular, coastal grasslands are dominated by the influence of environmental factors resulting from sea–land interaction. Therefore, coastal grasslands are extremely heterogeneous both spatially and temporally. In this review, recent knowledge in the field of biotic interactions in coastal grassland soil is summarized. A detailed analysis of arbuscular mycorrhiza symbiosis, rhizobial symbiosis, plant–parasitic plant interactions, and plant–plant interactions is performed. The role of particular biotic interactions in the fu

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31

Singh, Manya, and Wallace M. Meyer. "Plant-Soil Feedback Effects on Germination and Growth of Native and Non-Native Species Common across Southern California." Diversity 12, no. 6 (2020): 217. http://dx.doi.org/10.3390/d12060217.

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Changes in plant assemblages can influence biotic and abiotic soil conditions. These changes can cause plant–soil feedbacks that can inhibit or facilitate plant germination and growth. Here, we contribute to a growing literature examining plant–soil feedbacks in the endangered sage scrub ecosystem by examining the germination and growth of Artemisia californica, the dominant native shrub species in the ecosystem, in soil conditioned by two widespread plant invaders (Brassica nigra, Bromus madritensis ssp. rubens), and the germination and growth of these invasive species in conspecific and hete

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32

He, Lei, Lulu Cheng, Liangliang Hu, Jianjun Tang, and Xin Chen. "Deviation from niche optima affects the nature of plant–plant interactions along a soil acidity gradient." Biology Letters 12, no. 1 (2016): 20150925. http://dx.doi.org/10.1098/rsbl.2015.0925.

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There is increasing recognition of the importance of niche optima in the shift of plant–plant interactions along environmental stress gradients. Here, we investigate whether deviation from niche optima would affect the outcome of plant–plant interactions along a soil acidity gradient (pH = 3.1, 4.1, 5.5 and 6.1) in a pot experiment. We used the acid-tolerant species Lespedeza formosa Koehne as the neighbouring plant and the acid-tolerant species Indigofera pseudotinctoria Mats. or acid-sensitive species Medicago sativa L. as the target plants. Biomass was used to determine the optimal pH and t

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33

Soliveres, Santiago, and Pablo García Palacios. "Secondary succession, biotic interactions and the functioning of roadside communities: plant-soil interactions matter more than plant-plant interactions." Ecosistemas 28, no. 2 (2019): 50–60. http://dx.doi.org/10.7818/ecos.1718.

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34

Bardgett, Richard D., Gerlinde B. De Deyn, and Nicholas J. Ostle. "Plant-soil interactions and the carbon cycle." Journal of Ecology 97, no. 5 (2009): 838–39. http://dx.doi.org/10.1111/j.1365-2745.2009.01545.x.

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35

Piazzolla, P., A. Buondonno, F. Palmieri, and A. Stradis. "Studies on Plant Viruses-soil Colloids Interactions." Journal of Phytopathology 138, no. 2 (1993): 111–17. http://dx.doi.org/10.1111/j.1439-0434.1993.tb01367.x.

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36

Bech, Jaume. "Potentially harmful elements in soil–plant interactions." Journal of Soils and Sediments 14, no. 4 (2014): 651–54. http://dx.doi.org/10.1007/s11368-014-0877-5.

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37

Wang, Cong, Bojie Fu, Lu Zhang, and Zhihong Xu. "Soil moisture–plant interactions: an ecohydrological review." Journal of Soils and Sediments 19, no. 1 (2018): 1–9. http://dx.doi.org/10.1007/s11368-018-2167-0.

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38

van der Ent, Antony, and Hans Lambers. "Plant-soil interactions in global biodiversity hotspots." Plant and Soil 403, no. 1-2 (2016): 1–5. http://dx.doi.org/10.1007/s11104-016-2919-9.

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39

Blank, Robert, Robert Qualls, and James Young. "Lepidium latifolium : plant nutrient competition-soil interactions." Biology and Fertility of Soils 35, no. 6 (2002): 458–64. http://dx.doi.org/10.1007/s00374-002-0494-0.

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40

Hadas, A., W. E. Larson, and R. R. Allmaras. "Advances in modeling machine-soil-plant interactions." Soil and Tillage Research 11, no. 3-4 (1988): 349–72. http://dx.doi.org/10.1016/0167-1987(88)90006-2.

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41

Edmeades, Gregory O. "Plant-environment interactions." Field Crops Research 42, no. 2-3 (1995): 144–45. http://dx.doi.org/10.1016/0378-4290(95)90041-1.

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42

Kong, Chui-Hua, Zheng Li, Feng-Li Li, Xin-Xin Xia, and Peng Wang. "Chemically Mediated Plant–Plant Interactions: Allelopathy and Allelobiosis." Plants 13, no. 5 (2024): 626. http://dx.doi.org/10.3390/plants13050626.

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Plant–plant interactions are a central driver for plant coexistence and community assembly. Chemically mediated plant–plant interactions are represented by allelopathy and allelobiosis. Both allelopathy and allelobiosis are achieved through specialized metabolites (allelochemicals or signaling chemicals) produced and released from neighboring plants. Allelopathy exerts mostly negative effects on the establishment and growth of neighboring plants by allelochemicals, while allelobiosis provides plant neighbor detection and identity recognition mediated by signaling chemicals. Therefore, plants c

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43

Siciliano, S. D., and J. J. Germida. "Mechanisms of phytoremediation: biochemical and ecological interactions between plants and bacteria." Environmental Reviews 6, no. 1 (1998): 65–79. http://dx.doi.org/10.1139/a98-005.

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The use of plants to reduce contaminant levels in soil is a cost-effective method of reducing the risk to human and ecosystem health posed by contaminated soil sites. This review concentrates on plant-bacteria interactions that increase the degradation of hazardous organic compounds in soil. Plants and bacteria can form specific associations in which the plant provides the bacteria with a specific carbon source that induces the bacteria to reduce the phytotoxicity of the contaminated soil. Alternatively, plants and bacteria can form nonspecific associations in which normal plant processes stim

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44

van de Voorde, Tess F. J., Wim H. van der Putten, and T. Martijn Bezemer. "Soil inoculation method determines the strength of plant–soil interactions." Soil Biology and Biochemistry 55 (December 2012): 1–6. http://dx.doi.org/10.1016/j.soilbio.2012.05.020.

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45

Salam, Nishant Kumar, A. Krishnamoorthi, Sneh Trivedi, et al. "Optimizing soil nutrient dynamics: Recent insights into soil-plant interactions." International Journal of Research in Agronomy 8, no. 5 (2025): 846–54. https://doi.org/10.33545/2618060x.2025.v8.i5g.2994.

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46

Sanon, A., Z. N. Andrianjaka, Y. Prin, et al. "Rhizosphere microbiota interfers with plant-plant interactions." Plant and Soil 321, no. 1-2 (2009): 259–78. http://dx.doi.org/10.1007/s11104-009-0010-5.

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47

Sanon, A., Z. N. Andrianjaka, Y. Prin, et al. "Rhizosphere microbiota interfers with plant-plant interactions." Plant and Soil 325, no. 1-2 (2009): 351–52. http://dx.doi.org/10.1007/s11104-009-0100-4.

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48

Sharma, Rama, Aditya Kumar, Amit Bagri, and Vikas Chandra. "ROLE OF SOIL MICROBES IN MODULATION OF PLANT DEFENSE AGAINST INSECT PESTS: A REVIEW." ANNALS OF ENTOMOLOGY 42, no. 01 (2024): 1. http://dx.doi.org/10.59467/ae.2024.42.1.

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A vital role of soil microbes is to keep plants healthy and productive. There is growing interest in the role of soil microbes in plant defense against insect pests. Soil microbes can influence plant resistance to insect pests by interacting with plants. They produce compounds that can degrade insect toxins and make plants resistant to pests. By understanding the complex interactions between soil microbes, plants, and insect pests, strategies could be developed to enhance crop resilience and reduce reliance on chemical inputs. They can improve plant defense by generating secondary metabolites,

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49

Naidu, R., and P. Rengasamy. "Ion interactions and constraints to plant nutrition in Australian sodic soils." Soil Research 31, no. 6 (1993): 801. http://dx.doi.org/10.1071/sr9930801.

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Many of the arable soils in Australia are affected by salinity and/or sodicity. Nutrient deficiency and ion toxicity may occur in both saline and sodic soils. Ho-ever, the mechanism for these constraints on plant growth in sodic soils differs from that of saline soils. Fertility of sodic soils with low nutrient reserves is compounded by the low supply of water and oxygen to roots in profiles with dispersive clays. Nutrient constraints in sodic soils are created by the electron and proton activities (pE and pH) in an environment of degraded soil structure. Australian sodic soils accumulate rela

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50

Riedel, R. M. "Interactions of plant-parasitic nematodes with soil-borne plant pathogens." Agriculture, Ecosystems & Environment 24, no. 1-3 (1988): 281–92. http://dx.doi.org/10.1016/0167-8809(88)90072-2.

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