1. Introduction
In recent years, there has been a rapid decline in biodiversity caused by the human demographic success. The rapid growth of the human population leads to e.g., massive exploitation of natural resources, global warming, soil degradation, species extinction, and an unprecedented ecosystem decline [
1,
2]. One of the instruments for biodiversity protection is livestock grazing [
3,
4]. Besides its low costs, free-range grazing contributes to limitation of the expansion of forest and scrub communities, which otherwise leads to retreat and disappearance of ecosystems with their valuable fauna and flora species. Grazing also contributes to optimization of economic and protection-related activities. Many studies have confirmed the positive effect of farmed animal grazing, i.e., sheep [
5,
6,
7,
8], cattle [
7,
9], or horses [
5,
8,
10,
11] on preservation of the biodiversity of areas covered by various forms of protection. In another research grazing has been found to have negative effects on ecosystem [
12,
13]. Farmed animal grazing can soil degraded [
14], reduced the density and biomass of plant and animal species and limited biodiversity [
15].
Cervid species can similarly be used for protection of habitats through extensive grazing. The scientific literature does not provide information on the role of these ruminants in the protection of biodiversity. Deer farms are present nowadays on a large scale in New Zealand and, to a lesser extent, in Europe, North America, Australia and even in tropical regions, such as Mauritius and New Caledonia, and deer are farmed under a variety of conditions, ranging from extensive to intensive systems [
16,
17]. The most widespread deer species in modern deer farms are red deer (
Cervus elaphus), and fallow deer (
Dama dama) [
16,
18]. The impact of these animal species on the soil environment may be of interest to nature managers.
The acreage of pastures in Europe has decreased considerably during the last several decades as a result of changes in land use, including the abandonment of farmed animal grazing, secondary succession, or the reforestation of land on poor soils [
7,
10]. This changes have exert an impact on of the soil, which plays a major role in maintaining ecosystem biodiversity. Consequently, unfavorable changes occur in the soil cover, e.g., reduction of biological activity, lower content of soil humus, and impoverishment of biological diversity. Habitats and their natural plant communities are dependent on soil properties and prevailing climatic conditions. In turn, soil quality and health depend on the course of organic matter transformations related mainly to microorganisms and released enzymes as well as the rate of biogeochemical alterations in the circulation of elements [
19,
20,
21]. The activity of soil enzymes is regarded as one of the most sensitive indicators of ecosystem functioning. It reflects both the trends and nature of biogeochemical processes and changes in the biological and physicochemical properties of soils [
22,
23]. Assessment of the environment condition based on enzymatic assays helps to express numerically the effect of numerous factors and to determine parameters that cannot be evaluated otherwise, e.g., elements of cellular metabolism. An unquestionable advantage is also the possibility of conducting series of analyses [
24,
25].
Since cervid farming is regarded as an ecological activity [
18,
26], it has been hypothesized that grazing of these species may have a beneficial effect on the biochemical properties of soil and ecosystem biodiversity. The strategic goal of the present study was to identify the trends and dynamics of changes in the chemical and biochemical properties of soil induced by rotational grazing of farmed deer. Assessment of the impact of extensive grazing of farmed animals on the biological status of soils facilitated measurement of the activity of a number of soil enzymes: dehydrogenases, neutral phosphatase, and urease. These enzymes are directly involved in the transformation of soil organic matter and react markedly to the effects of stress factors. The practical aim was to use enzyme assays for rapid assessment of the ecobiochemical status of soils.
3. Results
The physicochemical and biochemical properties of the soils in the research objects varied depending on the mode of land use, the duration of animal grazing, and the term of soil material sampling. The monitored soils were slightly acidic and neutral, with pH in 1 mol KCl·dm
−3 ranging from 6.37 to 7.03 (
Table 3). The soils of the experimental pasture pens exhibited higher pH values than the soil from the control plot (Co-beyond the grazing range). The highest pH values were detected in the soil where the grass was supplemented with the mixture of grasses. The pH values were lower in autumn than in spring (
Table 3).
The different habitat conditions generated by the mode of land use and the duration of animal grazing differentiated the content of organic carbon (TOC) and total nitrogen (TN) in the analyzed soils. The contents of TOC and TN in the monitored soils were in the range of 9.42–19.37 g·kg
−1 and 1.13–2.24 g·kg
−1, respectively (
Table 3). The free-range grazing of the cervids had a beneficial effect on the total organic carbon and nitrogen contents in the soils of the S and W pasture pens. This effect was most evident in pasture W, where the content of these components in the grazed soil was significantly higher than in the Co soil (
Table 3). This was caused by the supply of fresh organic matter to the soil environment with animal excrements and the full cover of the pen surface with grassy vegetation. No such tendency was observed in the case of pasture SG, which required supplementation with the mixture of grasses. The contents of TOC and TN in the soil from this pen were significantly lower than in the soil from the Co pen. In terms of the analysis dates, a statistically significant decrease in the content of these components in the S, SG, and Co soils was observed in autumn. An opposite trend was determined in the case of pen W (
Table 3). The values of the TOC:NT ratio in the analyzed soils ranged from 8.2 to 9.9 (
Table 3). The values of the TOC:NT ratio in the soil from pen SG were significantly higher than in the soils from the other experimental pens.
The content of mineral nitrogen forms (N-NH
4+ and N-NO
3−) in the analyzed soils varied depending on the mode of land use and the term of analyses. The contents of N-NH
4+ and N-NO
3− in the soils of the monitored objects were in the range of 1.34–7.08 mg·kg
−1 and 102.8–619.5 mg·kg
−1, respectively (
Table 3). The highest mean level of N-NH
4+ was determined in the soil from pasture S. In turn, the content of this component in the soils from pastures W and SG was significantly lower than that in the control soil. The mean levels of nitrate nitrogen (N-NO
3−) in the pasture soils were lower than that in the mown soil (Co), with the lowest content of this component determined in the pen S soil. Significantly higher amounts of mineral nitrogen forms in the analyzed soils were determined in spring than in autumn. A reverse tendency was found only in the case of the ammonium nitrogen content in the SG and Co soils (
Table 3).
The content of available phosphorus, potassium, and magnesium forms during the research period was 36–320 mg·kg
−1; 42–553 mg·kg
−1, and 48–136 mg·kg
−1, respectively (
Table 4). The soils from the pastures were characterized by a higher level of available phosphorus, potassium, and magnesium forms than the mown soil (Co). The highest content of these components was determined in the winter pasture (
Table 4). As in the case of nitrate nitrogen (N-NO
3−), the content of available P, K, and Mg forms was lower in autumn than in spring (
Table 4).
The enzymatic activity of the analyzed soils varied significantly between the pastures. The trend and intensity of biochemical processes depended on the individual properties of the enzyme, the term of analyses, and the mode of land use in the object (
Table 5). The following levels of the activity of dehydrogenases, neutral phosphatase, and urease were determined: 2.38–17.59 mg TPF kg
−1 24 h
−1, 30.72–235.87 mmol PNP kg
−1 h
−1, and 3.57–16.70 mg N-NH
4+ kg
−1 h
−1, respectively (
Table 5). In the deer grazing areas, the activity of all enzymes was clearly higher than in the soil from the Co plot. The highest enzyme activity was determined in the soil from pasture S (
Table 5). In turn, the SG soil exhibited the lowest enzymatic activity, which was significantly lower than that in the control. This was probably associated with the significantly lower content of organic carbon and total nitrogen than that in the soils from the other study plots (
Table 3). The present study demonstrated a close relationship between the dehydrogenases and phosphatase activity and the organic C and total N content in soil (
Table 6). The analysis of the seasonal changes revealed lower activity of most enzymes in autumn than in spring. An increase in urease activity was recorded in the second analysis term only in the SG and Co soils (
Table 5). A similar tendency was observed for the N-NH4
+ content (
Table 3).
The present study indicated a significant relationship between the urease activity and the N-NH
4+ content in soil (
Table 6). In turn, the activity of dehydrogenases and phosphatase exhibited a significant positive correlation with the levels of TOC, TN, and available P and Mg forms (
Table 6). This proves that the supply of biogenic substances significantly stimulates the activity of soil enzymes.
4. Discussion
Soil is an important component serving a variety of functions in the ecosystem. It is responsible for e.g., the ecochemical status of the environment as a natural buffer degrading xenobiotic compounds. Most importantly for animal welfare, it is a medium for plant growth and development [
43]. Appropriate content of macro- and microelements in soil partly affects their content in green fodder [
44,
45]. The present results demonstrated differences in the physicochemical and biochemical parameters of the soils from the research plots associated with the mode of land use, the duration of animal grazing, and the analysis term. The increase in the value of pH of the pasture soils was related to microbial decomposition of uric acid excreted by animals. Ammonia, which forms NH
4OH in the soil solution, is the main end product of the conversion of uric acid and its salts [
46]. Additionally, animal feces are rich in alkaline elements [
47,
48]. The upward trend in the pH value in the livestock grazed soil has also been confirmed by other authors, e.g., Futa et al. [
5] and Hao and He [
9]. Grazing also influences the amount and composition of soil organic matter (SOM) through its effects on litter accumulation and decomposition [
49]. The present study showed a beneficial effect of free-range grazing of cervids on the contents of organic carbon and total nitrogen. The effect has been confirmed by other investigators of free-range grazing of farm animals, e.g., Liu et al. [
49], Li et al. [
50], Bielińska et al. [
51] and Galindo et al. [
52]. The seasonal changes in the TOC and NT content in the analyzed soils may have been related to the rate of the decomposition of fresh organic matter supplied to the soil environment. The fluctuations in the content of organic carbon and total nitrogen in the soils may have been associated with the meteorological conditions as well. Elevated air temperature and soil desiccation are known to contribute to a faster increase in the amount of organic matter, whereas rainfalls and temperature drops reduce its levels [
51]. Uric acid excreted by animals with feces is a source of heterogeneous nitrogen in grazed soils, regardless of the grazing system, soil type, and climate conditions [
53,
54,
55,
56]. In a urine patch, significant amounts of urinary N are rapidly converted into ammonium N in the soil and a substantial portion of the urine-derived ammonium N is gradually converted into nitrate N [
57]. The content of nitrogen nitrate in the soils analyzed in the present study was several times higher than that of the ammonium form. The pH value of the soil environment is an important determinant of the relationships between both forms of mineral nitrogen in soils. The slightly acidic or neutral pH of the analyzed soils may have contributed to intensification of the rate of microbial oxidation of ammonium ions. The reduction of the content of these components in autumn was associated with the uptake thereof by plants during the growing season, leaching from the top layer of the soil profile caused by rainwater, and ease of diffusion migration. N-NO
3− is especially susceptible to migration with water [
57]. The increase in the content of macroelements in the deer pasture soils was induced by the supply of fresh organic matter to the soil environment with animal feces. The results of investigations conducted by Li at al. [
50] in an alpine meadow on the Tibetan Plateau demonstrated that grazing had a significant positive effect on soil properties, i.e., the soil moisture content, soil organic carbon concentration, soil total nitrogen concentration, soil available nitrogen, soil total phosphorus, and soil available phosphorus. Similarly, Galindo et al. [
52] found that cattle grazing had a significant effect on soil properties, i.e., it increased the amount of available nutrients (K, Ca, Mg) and TOC. The lower content of the available forms of P, K, and Mg observed in autumn in the present study may have been associated with the intensive uptake of these components by plants during the growing season [
5].
The trend and intensity of the changes in the enzyme activity depended on the specific properties of each enzyme. This is associated with the content of specific substrates for enzymatic reactions in the soil and the individual sensitivity and resistance of enzymes to environmental and stress factors [
20]. Soil microbial biomass, i.e., the living part of soil organic matter, functions as a transient nutrient sink and is responsible for decomposition and transformation of organic materials, which are mostly derived from above- and below-ground plant residues, and release of nutrients from organic matter used by plants [
49]. The organic matter content in soil is closely associated with the level of soil enzyme activity, as confirmed by many authors [
57,
58]. The high amount of organic matter in soil can increase biological activity by providing microorganisms with appropriate substrates [
49,
52,
59], which in turn can stimulate the synthesis of soil enzymes. Soil enzymes are produced mainly by soil microorganisms, although they can also be contained in plant root secretions [
20,
60]. Soil enzymatic activity can be regarded as a potentially sensitive indicator of changes in the soil environment induced by transformation of nutrients in the soil [
60] and by livestock grazing [
5]. As suggested by Dick et al. [
61], the activity of soil enzymes should be the basic parameter for assessment of the quality of mineral soils, given their rapid response to environmental factors, compared to other soil properties. As shown by Ingram et al. [
62], it is important to gain understanding of microbial communities and related processes to elucidate the C and N cycling. Furthermore, analysis of several enzyme activities involved in C, N, and P cycling can provide information about soil metabolic or functional responses to changes in management practices [
63]. Herold et al. [
57] found that intensive land use, including livestock grazing, resulted in a significant increase in the activity of specific enzymes involved in the C cycle, regardless of the research region and soil properties, which may have exerted an effect on the decomposition of soil organic matter and the circulation of nutrients. However, these authors did not show an impact of livestock grazing on the activity of microorganisms and enzymes involved in the transformation of N and P compounds [
57].
The analysis of the seasonal changes revealed lower activity of most enzymes in autumn than in spring. This may be related to weather conditions and seasonal dynamics of soil nutrient content [
64,
65]. An increase in urease activity was detected only in the soils sown with a mixture of grasses and in the control plot in the second term of analyses. A similar tendency was observed in the content of N-NH4+. Nitrogen is taken up by plants and soil microorganisms in the ammonium form (N-NH4+). When large amounts of N-NH4+ are available, the utilization of alternative N sources, e.g., nitrates (N-NO
3−), is generally inhibited. In turn, at low availability of N-NH4+, enzymatic systems for utilization of alternative N sources are activated, and the presence of a substrate induces their synthesis [
66].
The present results confirm the idea that enzymatic activity is one of the most important parameters of the biological status of the soil environment, as it is a measure of soil fertility and quality as well as ecosystem biodiversity [
19,
20,
62,
67]. The cited authors highlight the close relationship of soil enzymes with many important physicochemical and biological parameters, e.g., reaction, organic matter content, biological activity, and microbial biomass content. Dehydrogenases are commonly found in organic matter-rich soils, and they are regarded as good indicators of the respiratory metabolism of microbes [
20,
62]. Nannipieri et al. [
68] have reported that phosphatases stimulate the conversion of organic phosphorus compounds into inorganic phosphates, while ureases are involved in ammonification, during which ammonia is released from urea, amino acids, and purine bases. Deer excrements in the soil environment are a source of organic matter, macro- and microelements, and enzymes, which are secreted by numerous species of bacteria and fungi present in urine and feces. Feces are also a unique food for hundreds of species of invertebrate coprophages. Animal excrements are also used by many species of e.g., flowering plants visited by many species of wasps, butterflies, and flies. Properly conducted grazing can improve the living conditions of deer and other species of wild fauna through promotion of plant species diversity. At a low level of grazing or postponed grazing, pastures may be dominated by seasonal perennials outcompeting species that are important for deer. Livestock grazing can improve the diversity of herbaceous plants by compaction of the soil and thinning dense tree stands or shrubs [
69]. The results reported by Santalahti et al. [
70] showed that reindeer grazing altered the fungal community structure and enhanced extracellular enzyme activities related to degradation of cellulose and hemicelluloses and nutrient acquisition from the needle litter in northern boreal forest soils. Reindeer grazing increased the estimated species richness but had no significant effect on soil fungal diversity [
70]. Li et al. [
50] reported that the vegetation height, coverage, and above-ground biomass significantly declined with increased grazing intensity, but the species richness reached the highest level in a moderate grazing intensity meadow. The species composition in the vegetation cover, in turn, has an impact on the accumulation of specific substrates for enzymatic reactions in the soil. The influence of higher plants on soil enzymes depends on the chemical composition of the plant, which may differ between different genera, species, and varieties, even in the case of root exudates [
51,
71]. In turn, as suggested by Herold et al. [
57], microbial biomass and its structure as well as enzyme activity are dependent on soil parameters to a greater extent than on the type of use of meadows.