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Article

The Influence of Calcium Sulfate and Different Doses of Potassium on the Soil Enzyme Activity and the Yield of the Sward with a Mixture of Alfalfa and Grasses

by
Waldemar Zielewicz
1,*,
Dorota Swędrzyńska
2,
Arkadiusz Swędrzyński
1,
Witold Grzebisz
3 and
Piotr Goliński
1
1
Department of Grassland and Natural Landscape Sciences, Poznan University of Life Sciences, Wojska Polskiego 28, 60-637 Poznan, Poland
2
Department of General and Environmental Microbiology, Poznan University of Life Sciences, Wojska Polskiego 28, 60-637 Poznan, Poland
3
Department of Agricultural Chemistry and Environmental Biogeochemistry, Poznan University of Life Sciences, Wojska Polskiego 28, 60-637 Poznan, Poland
*
Author to whom correspondence should be addressed.
Agriculture 2022, 12(4), 475; https://doi.org/10.3390/agriculture12040475
Submission received: 23 February 2022 / Revised: 22 March 2022 / Accepted: 25 March 2022 / Published: 28 March 2022
(This article belongs to the Special Issue Legumes: Advances in Breeding, Productivity and Quality)
Browse Figure
Versions Notes

Abstract

:
Between 2012 and 2015, a field experiment was conducted at the Brody Experimental Farm, Poznan University of Life Sciences, Poland. The following two experimental factors were used in duplicate: calcium sulfate (CaSO4) fertilization—two levels (0 and 500 kg ha−1); and potassium (K) fertilization—four levels (0, 30, 60, and 120 kg ha−1). The soil pH (in H2O) and enzyme activity (dehydrogenase, acid phosphatase, alkaline phosphatase) were determined. The potassium fertilizer had a significant influence only on the dehydrogenase activity, which increased with the dose of potassium. The research showed that the fertilization of the sward mixture of alfalfa and grasses with potassium doses of 60 and 120 kg ha−1 in the K 60 and K 120 combinations resulted in higher yields of fresh matter than in the combination without the potassium fertilizer (K 0). In the last year of the research, the additional CaSO4 fertilization resulted in the highest increase in the yield of the mixture of alfalfa and grasses, as compared with the variant without this fertilizer. The application of this fertilizer in the first years of the research also increased the yield of fresh matter.

1. Introduction

The negative influence of agriculture on the natural environment, and even on the climate, is increasingly often emphasized. One of the most important current challenges is to limit this influence [1,2]. The cultivation of grass and legume mixtures based on natural biological processes is a relatively small burden for the environment. These mixtures help to maintain soil fertility and biological potential, also in the context of carbon sequestration. They have minimal requirements for nitrogen fertilization, because they form efficient symbiotic systems with diazotrophic bacteria [3,4,5,6,7]. The optimization of the fertilization of grass and legume mixtures with other macroelements, including potassium, calcium, and sulfur, remains an important problem.
Potassium is one of the most important macroelements in plant production due to the multifunctional effect of this nutrient on the physiological processes occurring in plants, and in consequence, on their yield. Potassium not only controls the water management, but also the nitrogen management in the plant, and it significantly minimizes abiotic and biotic stresses [8,9,10,11]. If the amount of potassium fertilizer exceeds the metabolic capacity of plants, their yield will not increase. Instead, the yield quality may be adversely affected, including the uptake of other macronutrients such as calcium and magnesium [12], which are particularly important for forage crops.
Sulfur is a nutrient with important structural and metabolic functions in plants. It is a component of proteins, fats, and amino acids, and it participates in their synthesis. Sulfur can be found in such amino acids as methionine, cysteine, and cystine, and in ferredoxin and vitamins (biotin, thiamine) [13]. Additionally, sulfur is involved in redox processes and stabilizes the protein structure [14]. If there is sulfur deficiency, the yield volume and quality decrease, e.g., the content of non-protein nitrogen in plants increases [15]. Soil sulfur deficiency reduces the yield-generating efficiency of nitrogen [16]. Sulfur deficiency disrupts the growth of root nodules and the process of atmospheric nitrogen fixation in alfalfa and other legumes due to lower nitrogenase activity [17]. Sulfur affects the process of atmospheric nitrogen fixation and thus determines the yield-generating effect in legumes [18]. Moderate doses of sulfur are the best for plants because then they exhibit the highest photosynthetic activity [19].
Currently, agricultural soils tend to be increasingly deficient in sulfur. One of the reasons for this situation is the effective desulfurization of flue gases from coal combustion. Some forms of sulfur deposited in soil are difficult to access for plants. Most of the agricultural soils in Poland have a low content of sulfate sulfur [20]. The decreasing content of sulfur in soils is a major problem of modern agriculture [21,22]. The issue of fertilization of crops with sulfur has been discussed in various studies (e.g., [23,24,25]). In order to optimize sulfur fertilization, it is necessary to select the right chemical formula and the time of application [26,27].
The metabolic functions of calcium are also important for the normal function of plants [28]. This element is essential for the division of cells in the growth buds of the roots and shoots. Calcium deficiency inhibits plant growth [29]. Alfalfa is a plant species with a high demand for calcium [30].
Calcium sulfate (CaSO4) is a calcium fertilizer used in agriculture. It is natural gypsum or a product of SO2 neutralization in combined heat and power plants [31]. When calcium sulfate is applied to soil, Ca2+ ions in the form of chemically neutral salt are available to plants, especially to the species with a high demand for calcium, such as clover and alfalfa [32,33]. Calcium sulfate is also a rich source of sulfur that plants can easily access. It has positive influence on the volume and quality of the yield of plants with a high demand for this element, e.g., rape and alfalfa [34].
Calcium sulfate affects plant growth and yield quality [35,36,37,38,39]. When used as a fertilizer, it directly supplies sulfur and calcium to plants. Calcium sulfate introduced into soil as a chemically neutral salt does not form concentrated solutions and its pH is almost neutral. As a result, it does not damage leaves and it can be safely used for top dressing, even as a dust fertilizer [30]. Calcium sulfate fertilization has positive effects on heavy clay soils because it increases the rate of water infiltration and reduces the crust on the surface of these soils [40,41].
The content of aluminum, which is toxic to plants, increases in acidic soils and disturbs the growth of plants’ roots [36,42]. Calcium sulfate only slightly modifies the soil pH, but it limits the toxic effect of aluminum in soil [43,44]. When calcium sulfate is applied in the soil solution, complex AlSO4 ions or molecular Al(OH)SO4 compounds are formed, which reduce the harmful effect of aluminum on plants [45,46].
The soil bioactivity is also manifested by the activity soil enzymes, which is a derivative of the metabolism of plants and soil organisms, especially the soil microbiome. The enzymatic activity of soil is an image and indicator of its biological condition and fertility [47,48]. Dehydrogenases, and acid and alkaline phosphatases, are considered the best indicators of the general population of soil microorganisms and soil microbial activity [49,50,51].
Dehydrogenases can be found in all living microbial cells, where they reflect the redox processes. They do not accumulate in the extracellular space, which prevents, for example, plant dehydrogenases from entering the soil. Therefore, the activity of soil dehydrogenases is almost exclusively related with the abundance and activity of soil microorganisms [52]. The activity of acid and alkaline phosphatases, which can be observed in living and dead plant cells and soil microorganisms, reflects the activity of enzymes related with soil colloids and humic substances [53,54]. Researchers studying the soil environment usually assess the activity of phosphomonoesterases (phosphoric monoester hydrolases), which are largely responsible for the decomposition of organic phosphorus compounds into inorganic forms—they catalyze the decomposition of organic phosphorus ester and phosphoric acid anhydrides [55,56]. Their activity plays an important role in the phosphorus cycle in nature. By participating in the hydrolysis of various phosphate compounds they stimulate the transformation of organic phosphorus compounds into inorganic phosphates, which are directly available to plants and soil microorganisms [57,58,59].
The soil enzyme activity is influenced by various general environmental factors (humidity, temperature, oxygen availability, pH, the presence of soil organic matter) and factors specific to a particular habitat (pesticides, heavy metals, farming methods, etc.). Organic and mineral fertilization is one of the most important factors in agrocenoses [60,61,62].
The aim of this study was to assess how different doses of potassium and calcium sulfate fertilizers applied to a mixture of alfalfa and grasses influenced the yield of the sward and changes in the soil enzyme activity.

2. Materials and Methods

2.1. Research Site

The field experiment was conducted at the Brody Experimental Farm, Poznań University of Life Sciences, Poland (52°44′ N, 16°28′ E) on soil belonging to the typical lessive subtype, the glacial till type, and the type of light and strong loamy sands. The humus depth was greater than 30 cm. The soil was classified as Albic Luvisols according to the WRB, and as Typic Hapludalfs according to Soil Taxonomy. In terms of the grain size, it was classified as loamy sand underlined by loam [63]. The soil was characterized by the following physicochemical parameters: humus content—1.28%, slightly acidic soil pH (pHKCl = 6.5), content of macronutrients: P—82 mg, K—124 mg, and Mg—56 mg kg−1 soil.

2.2. Experimental Design

The split-plot field experiment was started in the autumn of 2011. A mixture of alfalfa and DSV Country 2056 grasses (alfalfa—80%, meadow fescue—15%, timothy—5%) was sown in plots sized 5.4 m × 5.0 m (27.0 m2) at an amount of 25 kg of seeds per 1 ha. Winter oilseed rape was used as a forecrop.
The following two experimental factors were used in 2 duplicates:
  • calcium sulfate fertilization—2 levels (0 and 500 kg ha−1 of CaSO4),
  • potassium fertilization—4 levels (0, 30, 60, and 120 kg ha−1 of K).
These fertilizer combinations are hereinafter referred to as: CaSO4 0 and CaSO4 500, and K 0, K 30, K 60, and K 120, respectively.
Calcium sulfate in the form of REA-gypsum (CaSO4∙2H2O) with 21.3% Ca and 17% sulfur content was applied in early spring. Potassium, in the form of potassium salt containing 60% K2O, was applied before the beginning of the growing season. Additionally, in spring, before the beginning of the growing season, two weeks after the application of calcium sulfate, uniform phosphorus fertilization at a dose of 60 kg ha−1 of P (triple superphosphate 46% P2O5) was applied in all combinations. At the beginning of the experiment, nitrogen fertilizer in the form of 34% ammonium nitrate was applied once at a starting dose of 40 kg ha−1 N in all experimental combinations.

2.3. Field and Laboratory Analyses

All analyses were conducted between 2012 and 2015. The sward was harvested three times at the full budding phase of alfalfa. The sward harvested from each plot in the fertilizer combinations was weighed and the yield of fresh weight per hectare was calculated. The total yield from the three harvests was analyzed.
Each time immediately before harvesting, the sward soil samples were collected with a soil sampling probe from the soil profile layer of 0–15 cm. Two pooled samples (10 soil punctures in each) were collected from each experimental combination. The soil pH (in H2O) and enzyme activity (dehydrogenase, acid phosphatase, alkaline phosphatase) were determined. The dehydrogenase activity (EC 1.1.1. DHA) was determined spectrophotometrically with 1% TTC (2,3,5-triphenyl tetrazolium chloride) as a substrate, after 24 h incubation at 30 °C, pH 7.4. Triphenylformazan (TPF) was produced, extracted with 96% ethanol, and measured spectrophotometrically at 485 nm. The enzyme activity was expressed as µmol TPF kg−1 DM of soil 24 h−1 [64]. The activity of alkaline phosphatase (AlP) (EC3.1.3.1) and acid phosphatase (AcP) (EC 3.1.3.2) was determined with the method developed by Tabatabei et al. [65], with para-nitrophenyl phosphate (pNPP) used as a substrate, after a one-hour incubation at 37 °C, at a wavelength of 400 nm. It was expressed as µmol pNP kg−1 h−1 DM of soil.

2.4. Statistical Analysis

The three-way ANOVA was used, in which Year, CaSO4, and K fertilization were the main factors (all the factors were considered fixed). This analysis was carried out according to the linear model given by the formula:
yijkl = µ + αi + βj + γk + (αβ)ij + (αγ)ik + (βγ)jk + (αβγ)ijk + eijkl
where: µ is the general mean; αi is the year effect; βj is the CaSO4 fertilization effect; γk is the K fertilization effect; (αβ)ij is the second order effect; (αγ)ik is the second order effect; (βγ)jk is the second order effect; (αβγ)ijk is the third order effect; eijkl is a random error.
The confidence intervals for the means were determined and the differences between the means were verified with Tukey’s HSD test at a significance of p = 0.05. Statistica and MS Excel software were used for calculations and graphical presentation of the results.

2.5. Weather Conditions

The course of weather conditions in the growing seasons between 2012 and 2015 is shown in Table 1. In 2012 there were favorable weather conditions for the growth and development of plants in the mixture of alfalfa with grasses. The average annual air temperature was moderate, i.e., 8.9 °C. The rainfall was fairly high for the Wielkopolska region, i.e., 811.5 mm. In 2013, the annual rainfall was 295 mm lower than in the previous year. July was a particularly dry month, with a total rainfall of 67.3 mm. In 2014, the total rainfall was 632.5 mm. The rainfall in May was similar to that in previous years, but in June there was a significant water shortage and an unfavorable distribution of rainfall, which negatively influenced the development of the plants. In the last year of the experiment, the total rainfall was the lowest, i.e., only 471.0 mm (Table 1). Rainfall deficits, which occurred during the growing season in the second and last years of the study, had quite often been observed in this part of the Wielkopolska region before [66].

3. Results

The analysis of variance (Table 2) indicated a significant effect of CaSO4 fertilization on the yield of the sward, the soil pH, and the activity of dehydrogenases and alkaline phosphatase. The potassium fertilizer significantly influenced the yield of the fresh matter of the alfalfa and grass mixture and the dehydrogenase activity. The interaction between the CaSO4 and K fertilization was observed only for the yield. The main effect of the year was significant for all five variables (fresh matter yield, soil pH, dehydrogenase, acid phosphatase, and alkaline phosphatase activities). The year × CaSO4 fertilization interaction was statistically significant for the yield and alkaline phosphatase activity.
During the experiment, the average yield of the mixture of alfalfa and grasses (Table 3) ranged from 30.26 to 67.92 t of fresh matter per hectare in the combination without the CaSO4 fertilizer, and from 36.48 to 70.82 t per hectare in the combinations with the CaSO4 fertilizer. The highest yields of fresh matter were noted in 2013, although it was a rather dry year. The yield of the sward in the combination with the CaSO4 fertilizer and the full dose of potassium (120 kg ha−1) was over 70 t of fresh matter (FM) per ha. The lowest yields were noted in the last year of the experiment.
The analysis of the effect of the applied doses of the potassium fertilizer on the average yield of the sward mixture in individual combinations and years of the study showed that, in the variant without the CaSO4 fertilizer, the difference in the total yields between the K 0 and K 120 combinations was 27.52 t of fresh matter per hectare (14.93%). In the variant with the CaSO4 fertilizer, the difference between these combinations in the total yield obtained during the years of the study amounted to 31.83 t of fresh matter per hectare (15.91%) (Table 3).
The analysis of the effect of the CaSO4 fertilization showed that, in the subsequent years of the study, the yields increased in all the K combinations. In comparison with the K 0 combination, the application of potassium at the doses of 30, 60, and 120 kg ha−1 in the variants without CaSO4 increased the yield of fresh matter by 8.36 t ha−1 (4.5%), 19.53 t ha−1 (10.6%), and 27.52 t ha−1 (14.9%), respectively. In comparison with the K 0 combination, the application of potassium at the doses of 30, 60, and 120 kg ha−1 in the variants with CaSO4 increased the yield of fresh matter by 6.22 t ha−1 (3.11%), 23.7 t ha−1 (11.8%), and 31.93 t ha−1 (15.9%), respectively.
The statistical analysis of the yields revealed a significant difference between the variants with and without the CaSO4 fertilizer. The potassium fertilizer also significantly increased the yields. The fertilization levels of 60 and 120 kg K ha−1 increased the yields considerably, both in the variants with and without CaSO4. It turned out that the dose of 60 kg K ha−1 was as effective as the full dose of 120 kg K ha−1, despite the lower amount of potassium applied to the soil.
The effect of CaSO4 application on the efficiency of potassium fertilization in relation to sward yield increase is shown in Figure 1. In each year, the application of CaSO4 significantly increased the yields of fresh matter.
The assessment of the effect of the applied fertilizer combinations on the soil pH was the starting point for the interpretation of the soil enzyme activity (Table 2 and Table 4). The CaSO4 fertilization decreased the soil pH. The effect was minimal but unambiguous. It exhibited an upward trend in the following years and it was statistically significant. The effect of different doses of potassium fertilization on soil pH was statistically insignificant (Table 4).
All the analyzed factors clearly influenced the activity of dehydrogenases (Table 5). Only the main effects Year, CaSO4 and K fertilization, separately, were significant. The CaSO4 fertilizer reduced the dyhydrogenase activity, whereas the potassium fertilizer clearly increased the activity of this enzyme as the dose of potassium increased. There was no interaction between the independent variables (Table 2).
The significant differences in acid phosphatase activity were only obtained for Year (Table 2 and Table 6). The influence of the experimental variants on the acid phosphatase activity was minimal, inconclusive, and statistically insignificant.
Unlike acid phosphatase, alkaline phosphatase is mainly of microbial origin. The significant differences in alkaline phosphatase activity were only obtained for Year, CaSO4 and the interaction Year × CaSO4 (Table 2 and Table 7). CaSO4 fertilization significantly reduced the activity of this enzyme.
In order to assess the correlations between the variables, the Pearson correlation coefficient was used for analysis (Table 8). The strongest correlations were found between the activity of both phosphatases, the activity of phosphatases and the yield, and between the dehydrogenase activity and the soil pH. The analysis did not reveal any correlation between the dehydrogenase activity and the yield. These correlations confirmed the aforementioned explanations of the research results and observed phenomena.

4. Discussion

There are several reasons why the year of the experiment and its interactions influenced the variables under analysis. The most important of these are the differences in the weather conditions in individual years of the experiment, and especially the differences in the amount and distribution of rainfall during the growing season, which determined the supply of water available to plants. It is a well-known fact that water is one of the main factors determining the growth and development of plants, because it influences their ability to take up soil minerals. Although alfalfa, which was the dominant plant in the sward, is relatively resistant to periodic droughts [67,68], it is not indifferent to the influence of drought stress. Grasses react very strongly to periodic water shortages in the soil profile [69]. During the growing seasons in 2012 and 2014, there was a sufficient amount of rainfall for the development of the mixture of alfalfa and grasses (Table 1), but 2013, and especially 2015, were dry. The significant differences between the variables in individual years of the experiment were also caused by changes in the viability of the plants, which resulted from the specificity of their development in the subsequent years. In the first year, the plants fully developed and achieved their full yield potential. In the last years of the experiment this potential decreased due to the plants’ ageing [70]. In consequence, the sward became less dense and low weeds appeared.
The doses of potassium fertilizer applied in individual experimental combinations during the years of the study had a significant influence on the plants, both in the variants with and without the CaSO4 fertilizer. Robin et al. [71] conducted a study on white clover and observed that when the plants had a higher supply of potassium during a water deficit, the water potential and stomatal resistance in the leaves decreased, which reduced the loss in the growth of the biomass of this species. This observation was also confirmed by the yields of the plants analyzed in our experiment. In 2015, there was a very interesting reaction of the mixture of alfalfa and grasses to the CaSO4 fertilizer. The last year of the experiment was characterized by a rainfall deficit, which resulted in the lowest yields (Table 3). However, under such unfavorable soil moisture conditions there was an interaction between CaSO4 and potassium applied at the doses of 60 and 120 kg ha−1. The yield of fresh matter from the sward in the K 120 combination increased by 8.46 t ha−1. It was 23.16% higher than the yield from the same combination but without the CaSO4 fertilizer. The dose of potassium reduced by half, i.e., the K 60 combined with the CaSO4 fertilizer had an even better effect. The yield of fresh matter from the sward increased by 9.55 t ha−1, i.e., by 29.3%.
The accumulation of the effects of fertilization in the subsequent years of the experiment was undoubtedly another important reason for the changes in the variables under analysis. This particularly applied to the slow changes in the physicochemical properties of the soil, such as pH. Although the analysis did not reveal any significant effect of the potassium fertilization on the soil pH, the interaction between the year of the experiment, CaSO4 fertilization, and K fertilization had a statistically significant influence on this parameter.
The research conducted by Tirado-Corbalá et al. [72] showed that the application of CaSO4 stimulated the growth of the root system of alfalfa in soils with limited content of water and minerals. It also improved soil fertility and the growth of alfalfa. The application of CaSO4 did not have a measurable effect on the yield of alfalfa, nor did it have a major effect on the content of macronutrients, except for the plants’ increased uptake of sulfur. CaSO4 is an excellent source of sulfur, so the fertilization of the soils where the availability of this element is limited improves the production of alfalfa biomass.
Most authors indicate that CaSO4 has either no or a very poor deacidification effect [73,74]. However, there have also been reports, including our study, which documented the slightly acidifying effect of this fertilizer on the soil [75,76]. The effect is caused by the sulfate ions formed after the decomposition of the salt (CaSO4), which react with water to produce sulfuric acid. Potassium fertilization may also reduce the soil pH [73,77].
The experimental combinations had a diversified influence on the biological properties of soil in individual years of the study, which was manifested by the differences between the mean values and their significance. In some cases, the lack of statistical significance of the differences was caused by the considerable difference in the results between individual dates of analyses. However, the same trends were observed in each year, as can be seen in the charts (Table 4, Table 5, Table 6 and Table 7).
It is most likely that the lower soil pH reduced the dehydrogenase activity in the combinations fertilized with CaSO4. According to Swędrzyńska et al. [78], even slight changes in pH may strongly modify the qualitative and quantitative composition of the soil microbiome, and thus affect the activity of soil enzymes. The negative effect of CaSO4 on the dehydrogenase activity should not be attributed to sulfur alone, because the experiments conducted by Niewiadomska et al. [79] clearly showed that the dehydrogenase activity increased after the application of both elemental sulfur fertilizer and potassium fertilizer.
The lack of the effect of the applied experimental factors on the acid phosphatase activity may be explained by the fact that the activity of this enzyme is largely the plant’s response to phosphorus deficiency in soil [80]. In our experiment, the amount of phosphorus in the fertilizer met the nutritional demand of alfalfa and grasses in the sward. The usefulness of acid phosphatase as an indicator of soil bioactivity was also limited by the high pH of the soil in our experiment.
It is noteworthy that the course of the alkaline phosphatase activity, which is mostly affected by the activity of soil microorganisms, was similar to the course of the dehydrogenase activity—it was reduced by the CaSO4 fertilizer. Also in this case, it is most likely that the decreased activity of this enzyme was caused by the lower pH of the soil in the combinations fertilized with CaSO4. Other authors observed a similar dependence between the soil pH and the alkaline phosphatase activity in their studies [76].
Symanowicz et al. [81] conducted a study on barley and observed that balanced nitrogen and potassium fertilization should be applied both to the forecrop and the succeeding crop in order to maintain the optimal activity of soil enzymes. Higher doses of potassium improved the dehydrogenase activity, whereas lower doses improved the activity of acid and alkaline phosphatases. The same authors observed that the fertilization of pea plants with nitrogen at a dose of 20 kg ha−1 and potassium at a dose of 166 kg ha−1 increased the urease and dehydrogenase activity in the soil [82]. Swędrzyńska et al. [78] found that soil bioconditioners based on calcium carbonate stimulated the activity of dehydrogenases, phosphatases, and urease. As shown in most studies discussing fluctuations in the soil enzyme activity during the growing season, it is most likely that they are influenced by variable weather conditions, which consequently affect the soil temperature and moisture [83].

5. Conclusions

The results of this experiment showed that all the factors under analysis, i.e., potassium fertilization, CaSO4 fertilization, and the weather conditions, significantly influenced the yield of the sward with the mixture of alfalfa and grasses, in addition to the variables determining the soil bioactivity.
  • The calcium sulfate (CaSO4) fertilizer significantly decreased the activity of dehydrogenases and alkaline phosphatase. It is most likely that this effect was caused indirectly by the decrease in the soil pH as a result of the calcium sulfate fertilization. The potassium fertilizer had a significant influence only on the dehydrogenase activity, which increased with the dose of potassium.
  • The research showed that the fertilization of the sward mixture of alfalfa and grasses with potassium doses of 60 and 120 kg ha−1 in the K 60 and K 120 combinations resulted in higher yields of fresh matter than in the combination without the potassium fertilizer (K 0).
  • In the last year of the research, the additional CaSO4 fertilization resulted in the highest increase in the yield of the mixture of alfalfa and grasses, compared with the variant without this fertilizer. The application of this fertilizer in the first years of the research also increased the yield of fresh matter.

Author Contributions

Conceptualization, W.Z., D.S., W.G.; methodology, W.Z., D.S., W.G.; software, A.S. validation, W.G. and P.G.; formal analysis, W.Z., D.S.; investigation, W.Z., D.S.; resources, W.Z.; data curation, W.Z., A.S.; writing—original draft preparation, W.Z., D.S., A.S., W.G., P.G.; writing—review and editing, W.Z., D.S., A.S., W.G., P.G. visualization, W.Z., A.S.; supervision, W.Z.; project administration, W.Z.; funding acquisition, W.Z. All authors have read and agreed to the published version of the manuscript.

Funding

Publication was co-financed within the framework of the Polish Ministry of Science and Higher Education’s program: “Regional Initiative Excellence” in the years 2019–2022 (No. 005/RID/2018/19).

Data Availability Statement

All data generated or analyzed during this study are included in this published article.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Głodowska, M.; Gałazka, A. Intensyfikacja rolnictwa a środowisko naturalne (Unsustainable agriculture and its environmental consequences). Zesz. Probl. Postęp. Nauk Rol. 2018, 592, 3–13. [Google Scholar]
  2. Scherr, S.J.; McNeely, J.A. Biodiversity conservation and agricultural sustainability: Towards a new paradigm of ‘ecoagriculture’ landscapes. Phil. Trans. R. Soc. B 2008, 363, 477–494. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  3. Chung, H.; Zak, D.R.; Reich, P.B.; Ellsworth, D.S. Plant species richness, elevated CO2, and atmospheric nitrogen deposition alter soil microbial community composition and function. Glob. Change Biol. 2007, 13, 980–989. [Google Scholar] [CrossRef] [Green Version]
  4. Fornara, D.A.; Tilman, D.; Hobbie, S.E. Linkages between plant functional composition, fine root processes and potential soil N mineralization rates. J. Ecol. 2009, 97, 48–56. [Google Scholar] [CrossRef]
  5. Bhattacharyya, R.; Prakash, V.; Kundu, S.; Srivastva, A.K.; Gupta, H.S.; Mitra, S. Long term effects of fertilization on carbon and nitrogen sequestration and aggregate associated carbon and nitrogen in the Indian sub-Himalayas. Nutr. Cycl. Agroecosyst. 2010, 86, 1–16. [Google Scholar] [CrossRef]
  6. Zak, D.R.; Holmes, W.E.; White, D.C.; Peacock, A.D.; Tilman, D. Plant diversity, soil microbial communities, and ecosystem function: Are there any links? Ecology 2003, 84, 2042–2050. [Google Scholar] [CrossRef] [Green Version]
  7. Yang, Y.; Tilman, D.; Furey, G.; Lehman, C. Soil carbon sequestration accelerated by restoration of grassland biodiversity. Nat. Commun. 2019, 10, 718. [Google Scholar] [CrossRef] [Green Version]
  8. Grzebisz, W.; Gransee, A.; Szczepaniak, W.; Diatta, J. The effects of K fertilization on water-use efficiency in crop plants. J. Plant Nutr. Soil Sci. 2013, 176, 355–374. [Google Scholar] [CrossRef]
  9. Sardans, J.; Peňuelas, J. Potassium: A neglected nutrient in global change. Glob. Ecol. Biogeogr. 2015, 24, 262–275. [Google Scholar] [CrossRef] [Green Version]
  10. White, P.H. Improving potassium acquisition and utilization by crop plants. J. Plant Nutr. Soil Sci. 2013, 176, 305–316. [Google Scholar] [CrossRef]
  11. Wood, S.; Sebastian, K.; Scherr, S.J. Soil resource condition. In Pilot Analysis of GLOBAL ECOSYSTEMS: Agroecosystems; World Resource: Washington, DC, USA, 2000; pp. 45–54. [Google Scholar]
  12. Whitehead, D.C. Nutrient Elements in Grasslands. Soil-Plant-Animal Relationships; CABI Publishing: New York, NY, USA, 2000. [Google Scholar]
  13. Saito, K. Regulation of sulfate transport and synthesis of sulfur-containing amino acids. Curr. Opin. Plant Biol. 2000, 3, 188–195. [Google Scholar] [CrossRef]
  14. De Kok, L.J.; Castro, A.; Durenkamp, M.; Stuiver, C.E.E.; Westerman, S.; Yang, L.; Stulen, I. Sulphur in plant physiology. Nawozy Nawoż. Fert. Fertiliz. 2003, 2, 55–80. [Google Scholar]
  15. Brodowska, M.S. Wpływ nawożenia siarką na zawartość azotu w roślinach w warunkach zróżnicowanego zaopatrzenia gleby w wapń i magnez. Ann. UMCS Sect. E Agric. 2004, 59, 1861–1869. [Google Scholar]
  16. Scherer, H.W. Sulphur in crop production-Invited paper. Eur. J. Agron. 2001, 14, 81–111. [Google Scholar] [CrossRef]
  17. Varin, S.; Cliquet, J.B.; Personeni, E.; Avice, J.C.; Lemauviel-Lavenant, S. How does sulphur availability modify N acquisition of white clover (Trifolium repens L.)? J. Exp. Bot. 2009, 61, 34–225. [Google Scholar] [CrossRef] [Green Version]
  18. Scherer, H.W. Impact of sulfur on N2 fixation of legumes. In Sulfur Assimilation and Abiotic Stress in Plants; Khan, N.A., Singh, S., Umar, S., Eds.; Springer: Berlin/Heidelberg, Germany, 2008. [Google Scholar]
  19. Scherer, H.W. Sulfur in soils. J. Plant Nutr. Soil Sci. 2009, 172, 326–335. [Google Scholar] [CrossRef]
  20. Siebielec, G.; Smreczak, B.; Klimkowicz-Pawlas, A.; Maliszewska-Kordybach, B.; Terelak, H.; Koza, P.; Hryńczuk, B.; Łysiak, M.; Miturski, T.; Gałązka, R.; et al. Monitoring Chemizmu Gleb Ornych w Polsce w Latach 2010–2012; IUNG-PIB: Puławy, Poland, 2012; p. 202. [Google Scholar]
  21. Grzebisz, W.; Przygocka-Cyna, K. Aktualne problemy gospodarowania siarką w rolnictwie polskim. Nawozy Nawoż. Fert. Fertiliz. 2003, 4, 64–77. [Google Scholar]
  22. Przygocka-Cyna, K.; Grzebisz, W. Sulphur balance in Poland–regional analysis. Fragm. Agron. 2017, 34, 60–75. [Google Scholar]
  23. Hoel, B.O. Effects of sulphur application on grain yield and quality, and assessment of sulphur status in winter wheat (Triticum aestivum L.). Acta Agric. Scand. Sect. B Soil Plant Sci. 2011, 61, 499–507. [Google Scholar]
  24. Järvan, M.; Edesi, L.; Adamson, A. Effect of sulphur fertilization on grain yield and yield components of winter wheat. Acta Agric. Scand. Sect. B Soil Plant Sci. 2012, 62, 401–409. [Google Scholar] [CrossRef]
  25. Karamanos, R.E.; Harapiak, J.T.; Flore, N.A. Sulphur application does not improve wheat yield and protein concentration. Can. J. Soil Sci. 2013, 93, 223–228. [Google Scholar] [CrossRef]
  26. Gallejones, P.; Castello’n, A.; del Prado, A.; Unamunzaga, O.; Aizpurua, A. Nitrogen and sulphur fertilization effect on leaching losses, nutrient balance and plant quality in a wheat–rapeseed rotation under a humid Mediterranean climate. Nutr. Cycl. Agroecosyst. 2012, 93, 337–355. [Google Scholar] [CrossRef]
  27. Hawkesford, M.J. Sulfate uptake and assimilation–whole plant regulation. In Sulfur Metabolism in Plants, Proceedings of the International Plant Sulfur Workshop 1; De Kok, L.J., Tausz, M., Hawkesford, M.J., Hoefgen, R., McManus, M.T., Norton, R.M., Rennenberg, H., Saito, K., Schnug, E., Tabe, L., Eds.; Springer Science + Business Media: Dordrecht, Germany, 2012; pp. 11–24. [Google Scholar]
  28. White, P.J.; Broadley, M.R. Calcium in plants. Ann. Bot. 2003, 92, 487–511. [Google Scholar] [CrossRef] [PubMed]
  29. Marschner, P. Marschner’s Mineral Nutritions of Higher Plants; Elsevier Ltd.: Amsterdam, Netherlands, 2012; p. 651. [Google Scholar]
  30. Chen, L.; Dick, W.A. Gypsum as an Agricultural Amendment. General Use Guidelines; Ohio State University: Columbus, OH, USA, 2011; pp. 13–18. [Google Scholar]
  31. Kairies, C.L.; Schroeder, K.T.; Cardone, C.R. Mercury in gypsum produced from flue gas desulfurization. Fuel 2006, 85, 2530–2536. [Google Scholar] [CrossRef]
  32. Chen, L.; Dick, W.A.; Nelson, S. Flue gas desulfurization by-products as sulphur sources for alfalfa and soybean. Agron. J. 2005, 97, 265–271. [Google Scholar]
  33. Favaretto, N.; Norton, L.D.; Joern, B.C.; Brouder, S.M. Gypsum amendment and exchangeable Calcium and Magnesium affecting Phosphorous and Nitrogen Runoff. Soil Sci. Soc. Am. J. 2006, 70, 1788–1796. [Google Scholar] [CrossRef] [Green Version]
  34. Potarzycki, J.; Przygocka-Cyna, K.; Wendel, J.; Biniek, Ł.; Ridiger, B. The impact of sulphur fertilization on yield of winter wheat. Fragm Agron. 2015, 32, 63–72. [Google Scholar]
  35. Sumner, M.E. Gypsum and acid soils: The world scene. Adv. Agron. 1993, 51, 1–32. [Google Scholar]
  36. Toma, M.; Sumner, M.E.; Weeks, G.; Saigusa, M. Long-term Effects of Gypsum on Crop Yield and Subsoil Chemical Properties. Soil Sci. Soc. Am. J. 1999, 63, 891–895. [Google Scholar] [CrossRef]
  37. Alcordo, I.; Rechcigl, J.E. Phosphogypsum in agriculture: A review. Adv. Agron. 1993, 49, 55–119. [Google Scholar]
  38. Shainberg, J.; Summer, M.E.; Miller, W.P.; Farina, M.P.W.; Pavan, M.A.; Fey, M.V. Use of gypsum on soils: A review. Adv. Soil Sci. 1989, 9, 1–111. [Google Scholar]
  39. Smyth, T.J.; Cravo, S. Aluminum and calcium constraints to continuous crop produc-tion in a Brazilian Amazon soil. Agron. J. 1992, 84, 50–843. [Google Scholar] [CrossRef]
  40. Miller, W.P. Infiltration and soil loss of three gypsum amended Ultisols under simulated rainfall. Soil Sci. Soc. Am. J. 1987, 55, 783–787. [Google Scholar] [CrossRef]
  41. Norton, L.D.; Zhang, X.C. Liming to improve chemical and physical properties of soil. In Handbook of Soil Conditioners: Substances that Enhance Physical Properties of Soil; Wallace, A., Terry, R.E., Eds.; Marcel Dekker: New York, NY, USA, 1998; pp. 309–331. [Google Scholar]
  42. Carvalho, M.C.S.; van Raij, B. Calcium sulphate, phosphogypsum and calcium carbonate in the amelioration of acid subsoils for root growth. Plant Soil 1997, 192, 37–48. [Google Scholar] [CrossRef]
  43. Alva, A.K.; Sumner, M.E.; Miller, W.P. Reactions of gypsum or phosphogypsum in highly weathered acid subsoils. Soil Sci. Soc. Am. J. 1990, 54, 993–998. [Google Scholar] [CrossRef]
  44. Wright, R.J.; Hern, J.L.; Baligar, V.C.; Bennet, O.L. The effects of surface applied amendments on barley root growth in an acid subsoil. Commun. Soil Sci. Plant Anal. 1985, 16, 179–192. [Google Scholar] [CrossRef]
  45. Farina, M.P.W.; Channon, P. Acid-subsoil ameloriation: II. Gypsum effects on growth and subsoil chemical properties. Soil Sci. Soc. Am. J. 1988, 49, 175–180. [Google Scholar] [CrossRef]
  46. Dontsova, K.M.; Norton, L.D. Clay dispersion, infiltration and erosion as influenced by exchangeable Ca and Mg. Soil Sci. 2002, 163, 184–193. [Google Scholar] [CrossRef]
  47. Zuber, S.M.; Villamil, M.B. Meta-analysis approach to assess effect of tillage on microbial biomass and enzyme activities. Soil Biol. Biochem. 2016, 97, 176–187. [Google Scholar] [CrossRef] [Green Version]
  48. Zielewicz, W.; Swędrzyński, A.; Dobrzyński, J.; Swędrzyńska, D.; Kulkova, I.; Wierzchowski, P.S.; Wróbel, B. Effect of forage plant mixture and biostimulants application on the yield, changes of botanical composition, and microbiological soil activity. Agronomy 2021, 11, 1786. [Google Scholar] [CrossRef]
  49. García, C.; Hernández, M.T.; Costa, F. Potential use of dehydrogenase activity as an index of microbial activity in degraded soils. Commun. Soil Sci. Plant Anal. 1997, 28, 123–134. [Google Scholar] [CrossRef]
  50. Lemanowicz, J.; Bartkowiak, A.; Breza-Boruta, B. Changes in phosphorus content, phosphatase activity and some physicochemical and microbiological parameters of soil within the range of impact of illegal dumping sites in Bydgoszcz. Environ. Earth Sci. 2016, 75, 510. [Google Scholar] [CrossRef] [Green Version]
  51. Telesiński, A.; Krzyśko-Łupicka, T.; Cybulska, K.; Wróbel, J. Response of soil phosphatase activities to contamination with two types of tar oil. Environ. Sci. Pollut. Res. 2018, 25, 28642–28653. [Google Scholar] [CrossRef]
  52. Wolińska, A.; Stępniewska, Z. Dehydrogenase activity in the soil environment. In Dehydrogenases; Canuto, R.A., Ed.; InTech: London, UK, 2012; pp. 183–210. [Google Scholar]
  53. Banerjee, A.; Sanyal, S.; Sen, S. Soil phosphatase activity of agricultural land: A possible index of soil fertility. Agric. Sci. Res. J. 2012, 2, 9–412. [Google Scholar]
  54. Hu, C.; Cao, Z. Size and activity of the soil microbial biomass and soil enzyme activity in long-term field experiments. World J. Agric. Sci. 2007, 3, 63–70. [Google Scholar]
  55. Condron, L.M.; Turner, B.L.; Cade-Menun, B.J.; Sims, J.; Sharpley, A. Chemistry and dynamics of soil organic phosphorus. Phosphorus Agric. Environ. 2005, 46, 87–121. [Google Scholar]
  56. Garcia-Ruiz, R.; Ochoa, V.; Hinojosa, M.B.; Carreira, J.A. Suitability of enzyme activities for the monitoring soil quality improvement in organic agricultural system. Soil. Biol. Biochem. 2008, 40, 2137–2145. [Google Scholar] [CrossRef]
  57. Wyszkowska, J.; Wyszkowski, M. Activity of soil dehydrogenases, urease, and acid and alkaline phosphatases in soil polluted with petroleum. J. Toxicol. Environ. Health Part A 2010, 73, 1202–1210. [Google Scholar] [CrossRef] [PubMed]
  58. Salazar, S.; Sanchez, L.; Alvarez, J.; Valverde, A.; Galindo, P.; Igual, J.M.; Peix, A.; Santa-Regina, I. Correlation among soil enzyme activities under different forest system management practices. Ecol. Engin. 2011, 37, 1123–1131. [Google Scholar] [CrossRef]
  59. Alvarez, M.; Huygens, D.; Diaz, L.M.; Villanueva, C.A.; Heyser, W.; Boeckx, P. The spatial distribution of acid phosphatase activity in ectomycorrhizal tissues depends on soil fertility and morphotype and relates to host plant phosphorus uptake. Plant Cell Environ. 2012, 35, 126–135. [Google Scholar] [CrossRef]
  60. Huang, W.; Liu, J.; Zhou, G.; Zhang, D.; Deng, Q. Effects of precipitation on soil acid phosphatase activity in three successional forests in southern China. Biogeosciences 2011, 8, 1901–1910. [Google Scholar] [CrossRef] [Green Version]
  61. Kalembasa, S.; Symanowicz, B. Enzymatic activity of soil after applying various waste organic materials, ash, and mineral fertilizers. Pol. J. Environ. Stud. 2012, 21, 41–1635. [Google Scholar]
  62. Swędrzyńska, D.; Grześ, S. Impact of long-term tillage systems and different nitrogen fertilisation on chemical and biological properties of soil and sugar beet yield. Fragm. Agron. 2017, 34, 92–106. [Google Scholar]
  63. Marcinek, J.; Komisarek, J. Systematyka Gleb Polski. Rocz. Glebozn. 2011, 62, 193. [Google Scholar]
  64. Thalmann, A. Zur Methodik der Bestimmung der Dehydrogenase Aktivität in Boden Mittels Triphenyltetrazoliumchlorid (TTC). Landwirtsch. Forsch. 1968, 21, 249. [Google Scholar]
  65. Tabatabei, M.A.; Bremner, J. Use of p-nitrophenyl phosphate for assys of soil phosphatase activity. Soil Biol. Biochem. 1969, 1, 301. [Google Scholar] [CrossRef]
  66. Goliński, P.; Czerwiński, M.; Jřrgensen, M.; Mřlmann Jřrgen, A.B.; Golińska, B.; Taff, G. Relationship between climate trends and grassland yield across contrasting European locations. Open Life Sci. 2018, 13, 98–589. [Google Scholar] [CrossRef] [PubMed]
  67. Zhang, C.; Shi, S.; Liu, Z.; Yang, F.; Yin, G. Drought tolerance in alfalfa (Medicago sativa L.) varieties is associated with enhanced antioxidative protection and declined lipid peroxidation. J. Plant Physiol. 2019, 232, 226–240. [Google Scholar] [CrossRef] [PubMed]
  68. Luo, Y.Z.; Liu, H.; Yan, G.; Li, G.; Turner, N.C. Roots of Lucerne Seedlings are More Resilient to a Water Deficit than Leaves or Stems. Agronomy 2019, 9, 123. [Google Scholar] [CrossRef] [Green Version]
  69. Pornaro, C.; Serena, M.; Macolino, S.; Leinauer, B. Drought Stress Response of Turf-Type Perennial Ryegrass Genotypes in a Mediterranean Environment. Agronomy 2020, 10, 1810. [Google Scholar] [CrossRef]
  70. Coruh, I.; Tan, M. Lucerne persistence, yield and quality as influenced by stand aging. N. Z. J. Agric. Res. 2008, 51, 39–43. [Google Scholar] [CrossRef]
  71. Robin, C.; Shamsun-Noor, L.; Guckert, A. Effect of potassium on the tolerance to PEG-induced water stress of two white clover varieties (Trifolium repens L.). Plant Soil 1989, 120, 58–153. [Google Scholar] [CrossRef]
  72. Tirado-Corbalá, R.; Slater, B.K.; Dick, W.A.; Baker, D. Alfalfa Responses to Gypsum Application Measured Using Undisturbed Soil Columns. Plants 2017, 6, 29. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  73. Łabętowicz, J.; Szymańska, M.; Stępień, W. Przydatność gipsu do poprawy właściwości fizykochemicznych gleb lekkich (Usefulness of gypsum in the improvement of physicochemical properties of light soil). Rocz. Glebozn. 2010, 61, 154–158. [Google Scholar]
  74. Sosulski, T.; Szara, E.; Łabętowicz, J.; Domeradzka, K.; Felak, M. Wpływ węglanu wapnia, gipsu i fosfogipsu na plony oraz skład chemiczny roślin i roztworu glebowego. Zesz. Probl. Post. Nauk Rol. 2008, 533, 345–356. [Google Scholar]
  75. Graham, M.H.; Haynes, R.J. Organic matter accumulation and fertilizer–induced acidification interact to affect soil microbial and enzyme activity on a long–term sugarcane. Management experiment. Biol. Fert. Soils 2005, 41, 249–256. [Google Scholar] [CrossRef]
  76. Verdenelli, R.A.; Chavarria, D.N.; Dominchin, M.F.; Rovea, A.; Vargas Gil, S.; Meriles, J.M. Influence of 12-years of NPS fertilization on soil quality, microbial community profile and activity under conservation agricultural management. Cienc. Suelo 2018, 36, 99–109. [Google Scholar]
  77. Grzebisz, W. Potassium and biotic stress. Elements in the environment-potassium (red. Grzebisz, W.). J. Elem. 2004, 4, 49–56. [Google Scholar]
  78. Swędrzyńska, D.; Zielewicz, W.; Swędrzyński, A. Comparison of soil bioconditioners and standard fertilization in terms of the impact on yield and vitality of Lolium perenne and soil biological properties. Open Life Sci. 2019, 14, 666–680. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  79. Niewiadomska, A.; Barłóg, P.; Borowiak, K.; Wolna-Maruwka, A. The effect of sulphur and potassium fertilisation on the nitrogenase and microbial activity in soil under broad bean (Vicia faba L.) cultivation. Fresenius Environ. Bull. 2015, 24, 723–732. [Google Scholar]
  80. Niewiadomska, A.; Sulewska, H.; Wolna-Maruwka, A.; Ratajczak, K.; Waraczewska, Z.; Budka, A.; Głuchowska, K. The influence of biostimulants and foliar fertilisers on the process of biological nitrogen fixation and the level of soil biochemical activity in soybean (Glycine max L.) cultivation. Appl. Ecol. Environ. Res. 2019, 17, 12649–12666. [Google Scholar] [CrossRef]
  81. Symanowicz, B.; Kalembasa, S.; Toczko, M.; Skwarek, K. The effect of different potassium fertilization of forecrop on the enzymatic activity of soil in spring barley cultivation. Acta Agroph. 2018, 25, 85–94. [Google Scholar] [CrossRef]
  82. Symanowicz, B.; Kalembasa, S.; Niedbała, M.; Toczko, M.; Skwarek, K. Fertilisation of pea (Pisum sativum L.) with nitrogen and potassium and its effect on soil enzymatic activity. J. Elem. 2018, 23, 57–67. [Google Scholar] [CrossRef]
  83. Steinweg, J.M.; Dukes, J.S.; Wallenstein, M.D. Modeling the effects of temperature and moisture on soil enzyme activity: Linking laboratory assays to continuous field data. Soil Biol. Biochem. 2012, 55, 85–92. [Google Scholar] [CrossRef]
Agriculture 12 00475 g001 550
Figure 1. Increase sward yield in individual combinations of potassium fertilization under the influence of CaSO4 (t ha−1 FM).
Figure 1. Increase sward yield in individual combinations of potassium fertilization under the influence of CaSO4 (t ha−1 FM).
Agriculture 12 00475 g001
Table
Table 1. Weather conditions during the vegetation period in RGD Brody in the years 2012–2015.
Table 1. Weather conditions during the vegetation period in RGD Brody in the years 2012–2015.
MonthAverage Air Temperature (°C)Total Rainfall (mm)
20122013201420152012201320142015
IV8.88.010.510.422.915.446.346.4
V14.914.413.113.077.269.873.525.6
VI16.017.316.115.5163.0125.342.085.3
VII19.220.121.519.2197.667.383.184.9
VIII18.719.117.322.160.151.5137.215.1
IX14.312.915.414.730.033.764.840.6
X8.210.310.97.910.910.939.821.7
IV–X average temperature14.314.615.014.7----
IV–X rainfall----561.7373.9486.7319.6
Annual average temperature8.98.810.110.2----
Annual rainfall----811.5516.5632.5471.0
Table
Table 2. Three-way ANOVA for analyzed depended variables.
Table 2. Three-way ANOVA for analyzed depended variables.
Source of VariationYieldpHDehydrogenaseAcid PhosphataseAlkaline Phosphatase
dfSSFSSFSSFSSFSSF
Year37741.31066.30 ***1.11621.444 ***356.0444.105 ***0.0209610.743 ***0.071690.688 ***
CaS041180.474.54 ***0.81747.093 ***34.5912.854 ***0.000310.4700.008632.804 ***
K3684.794.32 ***0.0250.48674.609.241 ***0.000300.1560.00050.686
Year × CaS043145.320.02 ***0.0601.1516.820.8440.000530.2700.00394.890 **
Year × K9319.214.66 ***0.0670.43213.870.5730.000490.0830.00110.470
CaS04 × K376.810.57 ***0.0100.1961.360.1690.000190.0990.00010.109
Year × CaS04 × K9185.58.52 ***0.3272.095 *8.620.3560.000310.0520.00040.176
Error160 (32) 177.4 2.775 430.54 0.10403 0.0421
Total191 (63) 19410.7 5.198 926.43 0.12711 0.1283
* p < 0.05; ** p < 0.01; *** p < 0.001. 1—number of degrees of freedom for yield analysis.
Table
Table 3. Effect of CaSO4 application and varying doses of potassium fertilization on sward yields of alfalfa-grass mixtures (t ha−1 FM).
Table 3. Effect of CaSO4 application and varying doses of potassium fertilization on sward yields of alfalfa-grass mixtures (t ha−1 FM).
YearCaSO4 FertilizationPotassium Fertilization
K 0K 30K 60K 120
2012046.33 c52.35 bc53.19 b55.84 ab
50050.90 bc55.41 ab56.57 ab59.92 a
2013062.21 c63.83 bc67.70 abc67.92 abc
50065.34 abc67.75 abc69.94 ab70.82 a
2014045.49 b45.51 b50.37 ab51.53 ab
50047.26 ab46.07 b54.96 ab56.09 a
2015030.26 d30.96 cd32.56 cd36.52 bc
50036.48 bc36.87 abc42.11 ab44.98 a
Within each year, values followed by the same letter are not statistically different at p < 0.05.
Table
Table 4. Effect of analyzed factors on pH of soil.
Table 4. Effect of analyzed factors on pH of soil.
YearCaSO4 FertilizationPotassium Fertilization
K 0K 30K 60K 120
201206.61 ab6.52 ab6.63 a6.53 ab
5006.48 b6.50 ab6.47 b6.51 ab
201306.50 ab6.54 ab6.56 a6.55 a
5006.47 ab6.39 bc6.44 abc6.31 c
201406.50 a6.52 a6.47 a6.32 b
5006.28 b6.31 b6.32 b6.41 ab
201506.45 a6.43 ab6.35 abc6.46 a
5006.24 c6.28 bc6.23 c6.21 c
Within each year, values followed by the same letter are not statistically different at p < 0.05.
Table
Table 5. Effect of analyzed factors on dehydrogenases activity (µmol TPF kg−1 DM of soil 24 h−1).
Table 5. Effect of analyzed factors on dehydrogenases activity (µmol TPF kg−1 DM of soil 24 h−1).
Year2012201320142015
1.528 b4.128 a4.843 a2.125 b
CaSO4 fertilizationCaSO4 0CaSO4 500
3.570 a2.742 b
Potassium fertilizationK 0K 30K 60K 120
2.245 c2.952 bc3.452 ab3.974 a
Within each variable, values followed by the same letter are not statistically different at p < 0.05.
Table
Table 6. Effect of analyzed factors on acid phosphatase activity (µmol pNP g−1 DM of soil h−1).
Table 6. Effect of analyzed factors on acid phosphatase activity (µmol pNP g−1 DM of soil h−1).
Year2012201320142015
0.0762 b0.0987 a0.0728 b0.0751 b
CaSO4 fertilizationCaSO4 0CaSO4 500
0.0794 a0.0820 a
Potassium fertilizationK 0K 30K 60K 120
0.0801 a0.0790 a0.0817 a0.0821 a
Within each variable values followed by the same letter are not statistically different at p < 0.05.
Table
Table 7. Effect of year × CaSO4 fertilization interaction on alkaline phosphatase activity (µmol pNP g−1 DM of soil h−1).
Table 7. Effect of year × CaSO4 fertilization interaction on alkaline phosphatase activity (µmol pNP g−1 DM of soil h−1).
YearCaSO4 Fertilization
CaSO4 0CaSO4 500
20120.0618 a0.0497 b
20130.1141 a0.0885 b
20140.0811 a0.0657 b
20150.0529 a0.0525 a
Within each year, values followed by the same letter are not statistically different at p < 0.05.
Table
Table 8. The r-Pearson correlation coefficient between the parameters examined.
Table 8. The r-Pearson correlation coefficient between the parameters examined.
DehydrogenaseAcid PhosphataseAlkaline PhosphatasepH
Yield0.05600.5766 *0.4112 *0.0793
pH0.4434 *−0.15570.2932 *
Alkaline phosphatase0.3717 *0.5698 *
Acid phosphatase0.0905
* p < 0.01.
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Zielewicz, W.; Swędrzyńska, D.; Swędrzyński, A.; Grzebisz, W.; Goliński, P. The Influence of Calcium Sulfate and Different Doses of Potassium on the Soil Enzyme Activity and the Yield of the Sward with a Mixture of Alfalfa and Grasses. Agriculture 2022, 12, 475. https://doi.org/10.3390/agriculture12040475

AMA Style

Zielewicz W, Swędrzyńska D, Swędrzyński A, Grzebisz W, Goliński P. The Influence of Calcium Sulfate and Different Doses of Potassium on the Soil Enzyme Activity and the Yield of the Sward with a Mixture of Alfalfa and Grasses. Agriculture. 2022; 12(4):475. https://doi.org/10.3390/agriculture12040475

Chicago/Turabian Style

Zielewicz, Waldemar, Dorota Swędrzyńska, Arkadiusz Swędrzyński, Witold Grzebisz, and Piotr Goliński. 2022. "The Influence of Calcium Sulfate and Different Doses of Potassium on the Soil Enzyme Activity and the Yield of the Sward with a Mixture of Alfalfa and Grasses" Agriculture 12, no. 4: 475. https://doi.org/10.3390/agriculture12040475

APA Style

Zielewicz, W., Swędrzyńska, D., Swędrzyński, A., Grzebisz, W., & Goliński, P. (2022). The Influence of Calcium Sulfate and Different Doses of Potassium on the Soil Enzyme Activity and the Yield of the Sward with a Mixture of Alfalfa and Grasses. Agriculture, 12(4), 475. https://doi.org/10.3390/agriculture12040475

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