1. Introduction
One of the main challenges of the 20th-21st centuries is to produce enough food for humanity, preserve the environmental quality, and maintain the economic well-being of the rural community [
1,
2]. Intensive agro-technologies has led to climate change, degradation of soil and water quality, the environment for humans and animals, and threats to human health [
3,
4]. The list of negative consequences related to the use of intensive farming technologies is growing [
5]. Soil tillage intensity influences on the soil chemical, physical and mechanical properties, gas flows, as well as development of faba bean cultivation, production and quality [
6,
7,
8,
9]. Conservation tillage makes an appropriate soil environment for growing of crop mainly through the reduction in the intensity of tillage and retention of plant residues [
10].
In European Union (EU) and other countries, different cropping systems were planned and new Greening programmes were developed to reduce the negative environmental impacts [
2]. In Lithuania since 2015, farms must comply with the requirements of the Greening programme [
5]. One of the requirements of the Greening programme is crop diversification [
11]. Therefore, it is mandatory to grow 2–3 crops on farms. The second important requirement is the identification of ecologically important areas. Perhaps the most acceptable way to implement this requirement is to include at least 7% of the area of nitrogen-fixing plants in the composition of farm crops. Besides, Lithuania is favourable for growing of faba bean [
11].
Today, faba bean is the second widely-grown grain legume in EU. The Faba bean is grown in climates ranging from temperate to semi-arid, using different cultivars and relatively different crop-management techniques [
12]. The faba bean (
Vicia faba L.) contains valuable human nutrients [
13], provide protein to human diets and animal feed and also has medicinal value [
14,
15]. Faba bean is also very important in crop rotations [
11,
16,
17,
18]. The introduction of legumes in the crop rotation becomes the main tool to maintain an acceptable soil fertility level [
19], reduce the incidence of weeds, diseases and pests [
20]. Faba bean bio-accumulates atmospheric nitrogen and is therefore classified as one of the most efficient sources of nitrogen [
14,
21,
22]. In Southern Europe, faba bean have shown the highest N yields [
23,
24]. This ecological service is usually using in intercropping of corn, potato and rapeseed cultivations [
25]. In addition, faba beans generally improve the productivity of the following crops [
26]. According to Unkovic et al. [
27] N
2 fixation of legumes can be influenced by the previous cropping sequence, periods of fallow, cropping intensity, and reduced tillage.
Plant roots perform many functions, they influence the developing processes of the ecosystem [
28,
29]. Root function is very important to plant health and yield. Quantifications of root growth and root distributions are necessary to understand plant-soil interactions. The depth and distribution of roots are important parameters governing water and nutrient uptake by faba bean plants [
30]. Faba bean (
Vicia faba L.) is a crop with a shallow root system with little osmoregulation and is very sensitive to high temperatures and water stress [
31,
32]. Husain et al. [
33] reported that faba beans have a potentially advantageous adaptation to water deficit that makes it change its root and aboveground biomass according to the soil moisture conditions. Depending on the nodule bacteria and the leguminous plant and the soil and climatic conditions, an effective symbiosis can accumulate nitrogen up to 400 kg ha
-1 and more during the growing season [
34].
According to the index of chlorophyll content, it is possible to determine the condition of plants, conditions of nitrogen nutrition and partially predict plant productivity. When there is a lack of nutrients, the amount of chlorophyll in young plants begins to decrease, and under favourable conditions, it increases [
35].
Lithuanian and foreign researchers do not yet have a precise and comprehensive answer to the question of how faba bean cultivation under different tillage and meteorological conditions intensities could develop. Complex detailed research is required to answer these questions. Research tasks: 1) to determine the impact of tillage intensity and vegetative conditions on faba bean canopy height, biomass and photosynthetic parameters; b) to establish the effect on faba bean root biomass and nodulation; c) to find the interactions between faba bean development parameters and meteorological conditions.
2. Materials and Methods
2.1. Site description
The long-term stationary field experiment has been started in 1988 at the Experimental Station (54°52`N, 23°49` E) of Vytautas Magnus University, Agriculture Academy, Lithuania. In this study, the experimental data from 2016–2019 is analysed. The Lithuanian climate is surplus humid, average annual precipitation rate is 600–650 mm. The vegetative season lasts up to 150–180 days. The soil at the experimental site is a silty loam (45.6% sand, 41.7% silt, 12.7% clay) Planosol
(Eutric Endogleyic Drainic) [
36]. The soil of an experiment is approx. neutral, rich of available phosphorus (up to 384.0 mg kg
-1), consist average amount of available potassium (up to 201.0 mg kg
-1), rich of available magnesium (up to 634.0 mg kg
–1), and consist average amount of total nitrogen (1.20–1.73 g kg
-1).
2.2. Meteorological conditions
Last two decades Lithuanian climate became more ustable in the case of temperatures and precipitation rates. As you can see in
Figure 1, all experimental sesons were different. If the beginning of vegetative period was arid, the meadle or end of vegetation could be sulplus humid. The same with air temperatures. The most warm was 2018 vegetative season, the most cold was 2017 season. The highest precipitation rates were in 2016, cops extremally felt lack of moisture in 2019.
2.3. Experimental treatments and agronomic practices
In autumn, after the harvesting of pre-crop (winter wheat), the soil of an experiment was differently tilled: deeply and shallowly ploughed with mouldboard plough, chiselled, disked and not tilled (
Table 1).
Faba bean was cultivated according to the conventional technology, which well described by Kimbirauskiene et al. [
9]. Faba bean was sown at the end of April or beginning of May (
Table 2). Local fertilization (NPK 7:16:32, 300 kg ha
-1) was done during sowing operation.
The distance between rows was 25 cm, sowing depth was approx. 5–6 cm. Variety ‘Fuego’ was sown at the rate 200–220 kg of grain per ha (40–45 seeds per m
2). Before sowing, the seeds were inoculated with a
Rhizobium leguminosarum bacterial preparation (approximately 200 ml of preparation per 100 kg of seeds). A single application of the herbicide (a.i.
aclonifen 600 g l
-1) was done just after the sowing of faba bean. Insecticide (a.i.
lambda-cyhalothrin, 0.15 l ha
-1) was applied at the middle of May up to beginning of June. Fungicide (26.7% a.i.
boscalid and 6.7% a.i.
pyraclostrobin, 1 l ha
-1) was applied in June [
37].
2.4. Methods and analysis
Faba bean development parameters were determined at the beginning of faba bean flowering (BBCH 60–63). 10 faba bean plants were pick-upped in each experimental plot for this study. The height of each plant was measured and weighed to determine its green biomass. There were weighted roots of faba beans. Number of symbiotic nodules also were calculated. The biomass samples were dried in a thermostat at 105 °C to constant weight. The dry biomass of the plants was thus determined. The assimilation area of bean leaves (cm2) was measured with a leaf area measuring device Win Dias (Delta–T Devices Ltd., UK). The leaf chlorophyll index was also measured with a chlorophyll content meter CCM–200 plus (Opti–Sciences).
All experimental data were processed using two-factor analysis of variance (ANOVA) from the statistical software package SYSTAT, version 10 [
38]. The significance of differences among the treatments was estimated by the least significant difference (LSD) test. The method of correlation regression analysis was applied to evaluate the causality of the studied traits. We used the program STAT ENG from the package ANOVA [
39,
40,
41].
3. Results and Discussion
3.1. Height of faba bean canopy
After performing the statistical analysis of the results of two factors, it became clear that the height of faba beans in differently cultivated soil (factor A) differed significantly (
Table 3).
On average, the tallest plants grew in the DC and SC plots. Vegetation conditions (factor B) influenced the average faba bean plant height significantly. The highest faba beans grew in 2017, when the average daily air temperature was usually lower than the long-term average, and the precipitation was more evenly distributed than in the other years of the experiment because faba bean is temperate climate crop. Precipitation rate and average air temperature weakly correlated with the average height of faba bean plant. According to Chaves et al. [
42] the most common environmental factors limiting plant productivity are drought and extreme temperatures. Research conducted by Šliogerytė [
43] also proved that the water deficit had a negative impact on the physiological indicators of plants. Faba beans have coping mechanisms that allow them to mitigate potential negative water stress effects. According to Husain et al. [
33], these mechanisms consist of reducing its rate of height increase, decreasing its rate of leaf-area expansion slightly, greatly increasing root growth, producing leaves of smaller specific area and shedding leaves. We found a significant interaction between both experimental factors. The highest average faba bean plant height (101 cm) was determined in 2017 in the SC plots, and the lowest was in 2016, in SC plots (51.2 cm) (
Table 3).
3.2. Faba bean leaves chlorophyll index
Tillage intensity (factor A) had no significant effect on faba bean leaves chlorophyll index. However, the vegetation conditions of the experimental years had a significant influence (factor B) (
Table 4).
The highest faba bean leaves chlorophyll index was determined in 2018 (43.7). In other research years, this indicator differed significantly from year to year. It was significantly the lowest in 2017 (26.3). The process of photosynthesis is influenced by key factors such as nutritional, tillage and meteorological conditions [
44,
45]. In our experiment, the meteorological conditions had significant impact, but interaction between factors A and B was non-significant. Chlorophyll index mainly correlated with average air temperature (r=0.437,
P> 0.05). In addition, the chlorophyll index also correlated to a greater extent on the amount of magnesium in the soil, the abundance of annual and perennial weeds at the beginning of the growing season (r = 0.570; -0.859; -0.776,
P> 0.05) (data are not presented).
3.3. Faba bean leaves assimilation area
Leaf assimilation area is important for photosynthetic productivity [
46,
47]. In our experiment, tillage treatments (factor A) had a lower influence on the assimilation area of faba bean plant leaves than the vegetation conditions of the research year (factor B) (
Table 5), but the largest assimilation area was determined in the DC plots. The year 2017 was the most favourable for the development of faba beans and the leaf area of the faba bean plant was the largest (1153.6 cm). No significant interaction was found between the two experimental factors.
Correlation analysis of the experimental data showed high correlation between leaves assimilation area and plant average height (r=0.937, P ≤ 0.010 > 0.001). Precipitation rate and average air temperature had weak correlation with leaves assimilation area.
3.3. Faba bean canopy dried biomass
The assimilation area of the leaves is important for photosynthesis productivity. The highest biomass of the dried canopy of the faba bean plant was found in the DC plots (
Table 6). In NT plots, the biomass was significantly lower only (1.2 times). Meteorological conditions of the experimental vegetation periods had a significant influence on the dry biomass of the faba bean canopy.
The highest dry biomass of the faba bean plant canopy was determined in 2019, although this year's vegetation period was dry enough, but warmer than in other research years. We found slight correlation between average air temperature and canopy dried biomass (r=0.337,
P> 0.05). No interaction between the two experimental factors was found. Robertson and Swinton [
1] found that the productivity of crops depended on chlorophyll concentration in the leaves. In our experiment, we also found average correlation between faba bean plant canopy dried biomass and leaves chlorophyll index (r=0.433,
P> 0.05) and assimilation area of leaves (r=0.404,
P> 0.05).
3.4. Faba bean roots dried biomass
According to the average data of factor A, the highest (8.0 g) average dry biomass of the roots of the bean plant was found in NT and DC plots (
Table 7). It was similar in the plots of ather treatments. According to the average data of factor B, just like the canopy of the plant, the roots also developed best in 2017. No significant interaction between the factors was found.
It is known that tillage systems influence soil properties such as bulk density, aggregation and pore continuity, temperature, aeration and moisture levels, which can affect root growth [
48,
49]. In our experiment, we found negative correlation between air temperature and roots dried biomass (r=-0.505,
P> 0.05). Precipitation rate had positive effect (r=0.381,
P> 0.05). Research conducted by Šliogerytė et al. [
43] showed that moisture deficit disturbs the distribution of dry mass in the plant and more of it accumulates in the roots than in the above-ground part. Similarly, we found negative correlation between faba bean canopies dried biomass and roots dried biomass (r=-0.520,
P≤ 0.05>0.01). We also found correlations between roots dried biomass and plant canopy height (r=0.545,
P≤0.05>0.01), chlorophyll index (r=-0.726,
P≤0.010>0.001) and leaves assimilation area (r=0.565,
P≤ 0.05>0.01). In addition, the dry biomass of the roots of the faba bean at the time of flowering correlated with the volume of pre-crop residues on topsoil after faba bean sowing (r = 0.703,
P> 0.05), the density of the crop at the beginning of the growing season (r = -0.926,
P≤0.05>0.01), the total weediness of the crop at the beginning of the growing season (r = -0.928,
P≤0.05>0.01), magnesium amount in the soil in the 15-25 cm layer at the beginning of vegetative period (r = 0.980,
P≤0.010>0.001) (data are not presented).
3.5. Number of nodules on faba bean roots
In our experiment, in differently cultivated soil (factor A), the number of nodules on the roots of the faba bean plant differed insignificantly (
Table 8). Despite this, the most nodules were found in the SP and NT plots. López-Bellido et al. [
50] similarly concluded that number of nodules is also influenced by the chosen method of tillage and which plants we grow in the experiment.
Trinick et al. [
51] found that adequate supply and balance of photosynthetic products must be ensured to maintain the required number of nodules on the roots [
52]. In our experiment, leaves chlorophyll index slightly correlated with number of nodules (r=-0.327, P> 0.05) and canopy dried biomass (r=-0.610, P≤0.05>0.01). Also we found correlations between number of nodules and roots dried biomass (r=0.397, P> 0.05).
Examining the influence of factor B, it was found that the most favorable year for the development of bean symbiotic nodules was 2017, during which the average number of nodules on the roots of the bean plant was the highest (111.6 units) or from 1.4 to 1.8 times higher than in subsequent years of the experiment. According to the Amanuel et al. [
53] and Puschel et al. [
54], the roots of faba beans and other legumes with root nodules are very sensitive to nitrogen, phosphorus, potassium and water levels. In our experiment, between the number of symbiotic nodules and soil phosphorus content, potassium content, and nitrogen content in the 15-25 cm soil layer at the beginning of the growing season, a moderately strong positive relationship was established (r=0.681; 0.585; 0.523, P> 0.05). A positive relationship was also found between soil structural stability, number of earthworms and number of nodules (r=0.815 and 0.611, P>0.05) (data are not presented). In addition, precipitation rates and air temperatures weakly correlated with number of nodules. We did not find significant interactions between the experimental factors.
4. Conclusions
Different tillage methods (factor A) had less influence on faba bean development than vegetative conditions during the growing seasons (factor B). Despite this, DC generally showed better faba bean canopy development rates than other treatments. Faba bean roots developed somewhat better was in NT plots.
Vegetative conditions during vegetative seasons (factor B) had a significant influence on faba bean development indicators. In addition, in most cases, the effects of meteorological conditions in all four years of the experiment were significantly different from each other. This shows that, due to climate change, the conditions of each vegetative season become unique and require precise attention in agricultural practice.
Author Contributions
Conceptualization, K.R.; methodology, K.R. and R.K.; software, A.S., R.K, and K.R.; validation, R.K. and K.R.; formal analysis, R.K., A.S., R.J. and K.R.; investigation, R.K., A.S. and K.R.; resources, R.K., K.R., R.J. and A.S.; data curation, R.K., K.R., R.J. and A.S.; writing—original draft preparation, R.K., K.R. and A.S.; writing—review and editing, K.R., A.S., R.J. and R.K; visualization, A.S., R.K. and K.R.; supervision, K.R.; project administration, K.R. All authors have read and agreed to the published version of the manuscript.
Institutional Review Board Statement
Not applicable.
Informed Consent Statement
Not applicable.
Data Availability Statement
Not applicable.
Conflicts of Interest
The authors declare no conflict of interest.
References
- Roberttson, G. P.; Swinton, S. M. Reconciling agricultural productivity and environmental integrity: a grand challenge for agriculture. Front Ecol Environ. 2005, 3, 38–46. [Google Scholar] [CrossRef]
- Foley, A. J.; Ramankutty, N.; Brauman, K. A.; Cassidy, E. S.; Gerber, J.; Johnston, M. S.; Mueller, N. D.; O’Connell, C.; Ray, D. K.; West, P. C.; Balzer, C.; Bennett, E. M.; Carpenter, S. R.; Sheehan, J.; Siebert, S.; Tilman, D.; David, P. M. Solutions for a cultivated planet. Nature. 2011, 478, 337–342. [Google Scholar] [CrossRef]
- Dubrocsky, N. M.; Burow, R.; Clark, G. M.; Gronber, J. M.; Hamilton, P. A. The quality of our nation`s waters: Nutrients in the natio`s streams and groundwater, 1992–2004. Geol Surv 2010, 1350, 162–174. [Google Scholar]
- Rohr, J. R.; McCoy, K. A. A qualitative meta–analysis reveals consistent effects of atrazine on freshwater fish and amphibians. Environ Health Persp. 2010, 118, 20–32. [Google Scholar] [CrossRef] [PubMed]
- Bogužas, V.; Kairytė, A.; Jodaugienė, D. Soil physical properties and earthworms as affected by soil tillage systems, straw and green manure management. Zemdirbyste 2010, 97(3), 3–14. [Google Scholar]
- Vetsch, J. A.; Gyles, W. R. Corn production as affected by tillage system and starter fertilizer. Agron J. 2002, 94(3), 532–540. [Google Scholar] [CrossRef]
- Kulig, B.; Lepiarczyk, A.; Oleksy, A.; Kolodziejczyk, M. The effect of tillage system and forecrop on the yield and values of LAI and SPAD indices of spring wheat. Eur J Agron. 2010, 33, 43–51. [Google Scholar] [CrossRef]
- Lu, X.; Cui, Y.; Liao, Y. Tillage and crop straw methods affect energy use efficiency, economics and greenhouse gas emissions in rainfed winter wheat field of Loess Plateau in China. Acta Agric Scand B Soil Plant Sci. 2018, 68(6), 562–574. [Google Scholar] [CrossRef]
- Kimbirauskienė, R.; Romaneckas, K.; Naujokienė, V.; Sinkeviečienė, A.; Šarauskis, E.; Buragienė, S.; Stanislaw, B. Plonosol CO2 respiration, chemical and physical properties of differently tilled faba bean cultivation. Land. 2020, 456(9), 1–13. [Google Scholar]
- Organisation for Co-operation and Economic Development (OECD), Environmental Indicators for Agriculture–Vol. 3: Methods and Results, OECD, Paris, France, 2013, pp. 389–391.
- Šarauskis, E.; Romaneckas, K.; Jasinskas, A.; Kimbirauskienė, R.; Naujokienė, V. Improving energy efficiency and environmental mitigation through tillage management in faba bean production. Energy. 2020, 209, 1–10. [Google Scholar] [CrossRef]
- Trumper, K.; Ravilions, C.; Dickso, B. Carbon sequestration in dry land soils. Food and Agriculture Organization of the United Nations. World Soil Resources Reports. 2008, 102, 1–12. [Google Scholar]
- Gao, B.; Bian, X. C.; Yang, F.; Chen, M. X.; Das, D.; Zhu, X. R.; Jiang, Y.; Zhang, J.; Cao, Y. Y.; Wu, C. F. Comprehensive transcriptome analysis of faba bean in response to vernalization. Plant. 2020, 251(1), 10–22. [Google Scholar] [CrossRef] [PubMed]
- Etemadi, F.; Hashemi, M.; Barker, A. V.; Zandvakili, O. R.; Liu, X. Agronomy, nutritional value, and medicinal application of faba bean (Vicia faba L.). Hortic. Plant J 2019, 5, 170–182. [Google Scholar] [CrossRef]
- Guo, Z.; Dong, Y.; Dong, K.; Zhu, J.; Ma, L. Effects of nitrogen management and intercropping on faba bean chocolate spot disease development. J. Crop Prot. 2020, 127, 1–7. [Google Scholar] [CrossRef]
- Collison, E. J.; Riutta, T.; Slade E., M. Macrofauna assemblage composition and soil moisture interact to affect soil ecosystem functions. Acta Oecol. 2013, 47, 30–36. [Google Scholar] [CrossRef]
- Crumsey, J. M.; Le Moine, J. M.; Capowiez, Y.; Goodsitt, M. M.; Larson, S. C.; Kling, G. W.; Nadelhoffer, K. J. Community-specific impacts of exotic earthworm invasions on soil carbon dynamics in a sandy temperate forest. Ecology. 2013, 94, 2827–2837. [Google Scholar] [CrossRef]
- Eerd, L. V.; Congreves, K. A.; Hayes, A.; Verhallen, A.; Hooker, D. C. Long-term tillage and crop rotation effects on soil quality, organic carbon, and total nitrogen Canadian. J. Soil Sci. 2014, 94(3), 303–315. [Google Scholar]
- Boldrini, A.; Benincasa, P.; Tosti, G.; Tei, F.; Guiducci, M. The risk of N loss in an organic and a conventional farming system. Editorial Milenio, Lleida, Spain, 2007, pp. 315–317.
- Mwanamwenge, J.; Loss, S. P.; Siddique, K. H. M.; Cocks, P. S. Growth, seed yield and water use of faba bean (Vicia faba L.) in a short-season Mediterranean-type environment. Aust. J. Exp. Agric. 1998, 38, 171–180. [Google Scholar] [CrossRef]
- Karkanis, A.; Ntatsi, G.; Lepse, L.; Fernandez, J. A.; Vagen, I. M.; Rewald, B.; Alsina, I.; Kronberga, A.; Balliu, A.; Olle, M.; Bodner, G.; Dubova, L.; Rosa, E.; Savvas, D. Faba bean cultivation – revealing novel managing practices for a more sustainable and competitiveness European cropping systems. Front. Plant Sci. 2018, 9, 1115. [Google Scholar] [CrossRef]
- Etemadi, F.; Hashemi, M.; Zandvakili, O.; Dolatabadian, A.; Sadeghpour, A. Nitrogen contribution from winter–killed faba bean cover crop to spring–sown sweet corn in conventional and no–till systems. Agron J. 2018, 110(2), 455–462. [Google Scholar] [CrossRef]
- López-Bellido, L.; López-Bellido, R. J.; Castillo J., E.; López-Bellido F., J. Effects of tillage, crop rotation, and nitrogen fertilization on wheat under rainfed Mediterranean conditions. Agron J. 2000, 92, 1054–1063. [Google Scholar] [CrossRef]
- Alsalimm, H.A.A.; Abood, A.; Abbas, L.M.R. The ability of Rhizobium leguminosarum inoculum to improve fava faba beans (Vicia faba L.) growth and produce some hydrolytic enzymes. Iraqi J. Sci. 2018, 59, 1231–1236. [Google Scholar]
- Zhang, F.; Shen, J.; Li, L.; Liu, X. An overview of rhizosphere processes related with plant nutrition in major cropping systems in China. Plant Soil. 2004, 260, 89–99. [Google Scholar] [CrossRef]
- Peoples, M. B.; Hauggaard-Nielsen, H.; Jensen, E. S. The potential environmental benefits and risks derived from legumes in rotations. Agron. monogr. 2009, 52, 349–385. [Google Scholar]
- Unkovich, M. J.; Herridge, D.; Peoples, M.; Cadisch, G.; Boddey, B.; Giller, K.; Alves, B.; Chalk P. Measuring plant-associated nitrogen fixation in agricultural systems. ACIAR Monograph No. 136, Canberra, Australia, 2008, pp. 258.
- Berg, G.; Smalla, K. Plant species and soil type cooperatively shape the structure and function of microbial communities in the rhizosphere. FEMS Microbiol. Ecol. 2009, 68, 1–13. [Google Scholar] [CrossRef]
- Birkhofer, K.; Schoning, I.; Alt, F.; Herold, N.; Klarner, B.; Maraun, M.; Marhan, S.; Oelmann, Y.; Wubet, T.; Yurkov, A.; et al. General relationships between abiotic soil properties and soil biota across spatial scales and different land-use types. Plos one. 2012, 7, 43292. [Google Scholar] [CrossRef] [PubMed]
- Manschadi, A. M.; Sauerborn, J.; Stützel, H.; Göbel, W.; Saxena, M. C. Simulation of faba bean (Vicia faba L.) root system development under Mediterranean conditions. Eur J Agron. 1998, 9, 259–272. [Google Scholar] [CrossRef]
- Bond, D. A.; Jellis, G. J.; Rowland, G. G.; Le Guen, J.; Robertson, L. D.; Khalil, S. A.; Li-Juan, L. Present status and future strategy in breeding faba beans (Vicia faba L.) for resistance to biotic and abiotic stresses. Euphytica. 1994, 73, 151–166. [Google Scholar] [CrossRef]
- Xia, M. Z. Effects of drought during the generative development phase of faba bean (Vicia faba L.) on photosynthetic characters and biomass production. J. Agric. Sci. 1994, 122, 67–72. [Google Scholar] [CrossRef]
- Husain, M. M.; Reid, J. B.; Othman, H.; Gallagher J., N. Growth and water use of Faba beans (Vicia faba) in a sub-humid climate. I. Root and shoot adaptations to drought stress. Field Crops Res. 1990, 23, 1–17. [Google Scholar] [CrossRef]
- Paul, E. A.; Clark, F. E. Soil microbiology and biochemistry. New York, 1989. 273.
- Jeon, M. W.; Ali, M. B.; Hahn, E. J.; Paek, K. Y. Photosynthetic pigments, morphology and leaf gas exchange during ex vitro acclimatization of micropropagated CAM Doritaenopsis plantlets under relative humidity and air temperature. Environ. Exp. Bot. 2006, 55, 183–194. [Google Scholar] [CrossRef]
- IUSS WORKING GROUP, W. R. B., et al. update 2015. World Reference Base for Soil Resources. International Soil Classification System for Naming Soils and Creating Legends for Soil Maps. Food and Agriculture Organization of the United Nations, Rome, 2014, 190.
- Romaneckas, K.; Kimbirauskienė, R.; Adamavičienė, A.; Buragienė, S.; Sinkevičienė, A.; Šarauskis, E.; Jasinskas, A.; Minajeva, A. Impact of sustainable tillage on biophysical properties of Planosol and on faba bean yield. Agric. Food Sci. 2019, 28, 101–111. [Google Scholar] [CrossRef]
- SPSS Instant 10. Statistics I; IBM: Armonk, NY, USA, 2000, 663.
- Leonavičienė, T. SPSS Programų Paketo Taikymas Statistiniuose Tyrimuose; Lithuanian University of Educational Sciences: Vilnius, Lithuanian, 2007; Volume 663. [Google Scholar]
- Raudonius, S. Application of statistics in plant and crop research: Important issues. Zemdirb. Agric. 2017, 104, 377–382. [Google Scholar] [CrossRef]
- Scott Long, J.; Ervin, L. Using Heteroscedasticity Consistent Standard Errors in the Linear Regression Model. Am. Stat. 2012, 54, 217–224. [Google Scholar]
- Chaves, M. M.; Maroko, J. P.; Pereira, J. S. Understanding plant responses to drought – from genes to the whole plant. Funct. Plant Biol. 2003, 30, 239–264. [Google Scholar] [CrossRef] [PubMed]
- Šliogerytė, K.; Sakalauskienė, S.; Brazaitytė, A.; Lazauskas, S.; Sakalauskaitė, J.; Sirtautas, R.; Duchovskis, P. Paprastojo kukurūzo (Zea mays L.), auginto skirtingomis drėgmės ir temperatūros sąlygomis, fotosintezės ir biometrinių rodiklių kitimas. Sodininkystė ir daržininkystė 2009, 28, 189–197. [Google Scholar]
- Janušauskaitė, D.; Auškalnienė, O.; Pšibišauskienė, G. Skirtingo tankumo vasarinių miežių chlorofilo indeksas ir jo ryšys su derliumi. Zemdirbyste 2009, 96(4), 124–138. [Google Scholar]
- Janušauskaitė, D.; Feizienė, D.; Feiza, V. The effect of tillage, fertilization and residue management on winter wheat and spring wheat physiological performance. Acta Physiol. Plant. 2022, 44, 1–13. [Google Scholar] [CrossRef]
- Fageria, N. K.; Baligar, V. C.; Clark, R. B. Physiology of crop production. The Harworth Press. New York, London, Oxford, USA, 2006, pp. 345.
- Murungu, F. S.; Chiduza, C.; Muchaonyerwa, P. Biomass accumulation, weed dynamics and nitrogen uptake by winter cover crops in a warm-temperate region of South Africa. Afr. J. Agric. Res. 2010, 5(13), 1632–1642. [Google Scholar]
- Probert, M. E.; Fergus, I. F.; Bridge, B. J.; McGarry, D.; Thompson, C. H.; Russel, J. S., The Properties and Management of Vertisols. C.A.B. International. 1987, Wallingford, Oksford, UK.
- Coulombe, C. E.; Wilding, L. P.; Dixon, J. B. Overview of Vertisols: characteristics and impacts on society. Adv. Agron. 1996, 57, 289–375. [Google Scholar]
- López-Bellido, R. J; López-Bellido, L.; Benitez-Vega, J.; Munoz-Romero, V.; López-Bellido, F. J.; Redondo, R. Chickpea and faba bean nitrogen fixation in a Mediterranean rainfed Vertisol: Effect of the tillage system. Eur J Agron. 2011, 34(4), 222–230. [Google Scholar] [CrossRef]
- Trinick, M. J.; Dilworth, M. J.; Grounds, M. Factors affecting the reduction of acetylene by root nodules of Lupinus species. New Phytol. 1976, 77, 359–370. [Google Scholar] [CrossRef]
- Zhou, Y.; Hagedorn, F.; Zhou, C.; Jiang, X.; Wang, X.; Li, M. H. Experimental warming of a mountas tundra increases soil CO2 effluxes and enhances CH4 and N2O uptake at Changbai mountain, China. Sci. Rep. 2016, 6, 1–8. [Google Scholar]
- Amanuel, G.; Kunne, R. F.; Tanner, D. G.; Vlek, P. L. G. Biological nitrogen fixation in faba bean (Vicia faba L.) in the Ethiopian highlands as affected by P fertilization and inoculation. Biol. Fertil. Soils 2000, 32, 353–359. [Google Scholar] [CrossRef]
- Puschel, D.; Janoušková, M.; Voříšková, A.; Gryndlerová, H.; Vosátka, M.; Jansa, J. Arbuscular mycorrhiza stimulates biological nitrogen fixation in two Medicago spp. through improved phosphorus acquisition. Front. Plant Sci. 2017, 8, 382–390. [Google Scholar] [CrossRef]
|
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content. |
© 2023 by the authors. Licensee MDPI, Basel, Switzerland. This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license (http://creativecommons.org/licenses/by/4.0/).