Next Article in Journal
Genotype by Location Effects on Yield and Seed Nutrient Composition of Common Bean
Next Article in Special Issue
RETRACTED: Effects of the Application of Biochar in Four Typical Agricultural Soils in China
Previous Article in Journal
Application of Anti-Transpirant to Control Sugar Accumulation in Grape Berries and Alcohol Degree in Wines Obtained from Thinned and Unthinned Vines of cv. Falanghina (Vitis vinifera L.)
 
 
Search for Articles:
Title / Keyword
Author / Affiliation / Email
Journal
Article Type
 
 
Advanced Search
 
Section
Special Issue
Volume
Issue
Number
Page
 
Journals
Agronomy
Volume 10
Issue 3
10.3390/agronomy10030346
agronomy-logo
Submit to this Journal Review for this Journal Propose a Special Issue
► Article Menu

Article Menu

share Share announcement Help format_quote Cite question_answer Discuss in SciProfiles thumb_up
...
Endorse textsms
...
Comment
first_page
settings
Order Article Reprints
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Biochar, Vermicompost, and Compost as Soil Organic Amendments: Influence on Growth Parameters, Nitrate and Chlorophyll Content of Swiss Chard (Beta vulgaris L. var. cycla)

by
Angela Libutti
1,*,
Vincenzo Trotta
2 and
Anna Rita Rivelli
3
1
Department of Science of Agriculture, Food and Environment, University of Foggia, Via Napoli, 25, 71122 Foggia, Italy
2
Department of Science, University of Basilicata, Via dell’Ateneo Lucano, 10, 85100 Potenza, Italy
3
School of Agricultural, Forest, Food and Environmental Sciences, University of Basilicata, Via dell’Ateneo Lucano, 10, 85100 Potenza, Italy
*
Author to whom correspondence should be addressed.
Agronomy 2020, 10(3), 346; https://doi.org/10.3390/agronomy10030346
Submission received: 7 February 2020 / Revised: 28 February 2020 / Accepted: 28 February 2020 / Published: 3 March 2020
(This article belongs to the Special Issue Applications of Biochar and Other Organic Amendments within a Sustainable Agriculture and Circular Economy)
Browse Figures
Review Reports Versions Notes

Abstract

:
Soil addition with organic amendments is an issue that receives growing attention in the agricultural sector. However, the effects of such materials on plant growth and crop yield are highly variable in the literature. This study aims to evaluate the influence of soil addition with biochar (from vine pruning residues), vermicompost (from cattle manure), and three different composts (from olive pomace or cattle anaerobic digestate), on the quali-quantitative response of Swiss chard (Beta vulgaris L. var. cycla) grown in pots. The organic amendments were applied to the soil in two doses to provide 140 and 280 kg N ha−1, respectively. Two growth cycles were considered, and, at each leaf cut, plants were analyzed for growth parameters (height, fresh weight, leaf number, and leaf area) and qualitative characteristics (nitrogen, nitrate, and pigment leaf content). Swiss chard responded positively to organic amendment and, particularly when the soil was treated with compost from animal wastes, higher plant growth and pigment leaf content were observed. Nitrate leaf content was always well below the NO3− thresholds established by the European Commission Regulations. Biochar application did not show a positive effect on the quali-quantitative characteristics of Swiss chard, likely due to benefits that may be achieved over time.

1. Introduction

Swiss chard (Beta vulgaris L. var. cycla) has been grown in Europe since antiquity and is now widely cultivated in many temperate regions of the world for its edible leaves and stalks. The leaves can be used in salads or cooked like spinach, while the stalks are usually chopped and cooked like celery. This vegetable represents a cheap and rich source of nutrients, available all year round. Both the leaves and stalks contain considerable nutritionally concentrations of vitamins (A, K, E, C, B3, B5, B9) and minerals (iron, potassium, calcium, phosphorus, and magnesium), dietary fibers and proteins, phytopigments such as chlorophyll and carotenoids, flavonoids and phenolic compounds including several phenolic acids with high free-radical scavenging capacity and antioxidant activity [1,2,3,4]. These properties make Swiss chard attractive for numerous health benefits and for reducing the risk of neurodegenerative and chronic diseases. However, the leaves of the species can also contain a considerable concentration of anti-nutritional factors such as oxalates and particularly nitrates [3,5]. According to Santamaria et al. [5], Swiss chard tends to accumulate more nitrates than other species, with over 60% of total nitrate content in the petioles. The authors also report that the mean daily vegetable nitrate intake (approximately 71 mg in Italy) come from lettuce, Swiss chard, and beetroot, which together accounted for 47% of daily intake. Acceptable nitrate daily intake, risks for human health, and limits to maximum levels of nitrate in vegetables are discussed in Santamaria [6]. According to the author, several factors affect the uptake and accumulation of nitrate in vegetables, as genetic factors (species and cultivar), environmental factors (temperature, light intensity, and photoperiod, soil nitrogen content), and agriculture practices (primarily nitrogen doses and chemical forms). As reported by Pokluda and Kuben [7], the nutritional value of Swiss chard is generally dependent on cultivars and varieties, but to a much greater extent on leaf portion (blades and petioles) and growing season (spring and autumn) [8]. Besides climate and environmental conditions, Ivanović et al. [1] reported that the nutritional and phytochemicals content, as well as the yield of Swiss chard, also depends on irrigation and fertilization. About this latter, the quality and yield of Swiss chard are strongly influenced by the amount, frequency, type, and method of fertilization. In addition to water pollution problems, intensive application of nitrogen fertilizers, particularly in the form of nitrates, may determine an excess of nitrogen in fresh-cut leafy vegetables, causing serious risks for human health and the environment [9]. Several studies focused on the effects of different forms and rates of mineral nitrogen fertilizers on Swiss chard quality [2,8,10,11], showing that high levels of N fertilizer, although they increase the production, compromise the quality of fresh-cut yield. The range between 100 and 150 kg N ha−1 is recommended for the species to meet yield level, production cost, and leaf quality, allowing to keep low nitrate content below safe limits and avoid a negative impact on leaf nutritional value. In a survey study on nitrate content of 22 vegetable species produced in Tunisia under organic and conventional farming systems [12], significant differences were observed in Swiss chard nitrate content (1176 vs. 2243 mg kg−1 fresh weight—Fw, respectively).
As an alternative to mineral fertilization, there is currently a growing interest in exploring the benefits and opportunities as well as the limitations in the use of organic amendments, as compost and biochar, to enhance plant nutrition, crop yield and quality, protect soil fertility, and ensure environmental sustainability of crop production [13,14,15,16,17]. Compost is the product of organic waste stabilization and sanitation through aerobic decomposition process, under controlled conditions [13]. Biochar is a carbon-rich, solid material obtained by biomass (manure, sewage sludge, wood biomass and crop residues) pyrolysis in an oxygen-limited environment [18,19,20,21]. The effects of their addition to agricultural soils depend on a number of factors, including feedstock properties and processing conditions, application rate, soil type, environmental conditions, and crop species [22,23]. About the latter, the yield response to compost or biochar applications are often contrasting; generally, either positive or negative and sometimes also neutral effects on crop yield and quality have been reported [13,24]. In Swiss chard, Paredes et al. [25] found no significant differences on plant growth and yield comparing inorganic fertilizer and two doses of compost from olive mill wastewater; while other authors using a vermicompost mixed with coir for container-grown plants [26] or compost from organic domestic wastes and crop residues [27] observed higher growth and yield increases. As to biochar, Trupiano et al. [28] found that this amendment stimulated leaves number and total biomass of lettuce in soil poor in nutrients. In a comparison of the efficacy of peanut shell biochar and biochar-based compost on crown daisy and lettuce productivity, biochar had little effect on crop growth and mass yield [29]. In a pot experiment [30], the addition of rice-husk biochar to soil with and without fertilizers (a mixture of compost, liquid compost, and lake sediments) increased the final biomass, root biomass, plant height and leaves number of lettuce and Chinese cabbage.
In this context, we report an experimental study aimed at assessing whether soil addition with different types of organic amendments can affect quantitative and qualitative characteristics of Swiss chard (Beta vulgaris L. var. cycla), a fresh-cut vegetable largely consumed in Italy as “erbetta da taglio”. For this purpose, a pot short-term experiment, where Swiss chard plants were grown on soil amended with a biochar (from vine pruning residues), a vermicompost (from cattle manure), and three different composts (from olive pomace and cattle anaerobic digestate), was carried out in order to evaluate plant growth, nitrogen, nitrate, and leaf pigment content.

2. Materials and Methods

2.1. Experimental Layout

A greenhouse experiment was carried out during 2017 in Potenza (Southern Italy) at the University of Basilicata (PZ, 40°38′ N 15°48′ E, 819 m a.s.l.) on Swiss chard (Beta vulgaris L. var. cycla), grown in pots containing soil treated with different types of organic amendments. More specifically, the experimental design included: Non-treated soil or control (NT); soil treated with biochar produced by pyrolysis of vine pruning residues (B); soil treated with compost obtained from olive pomace (COP); soil treated with vermicompost obtained from cattle manure (CW); soil treated with composts obtained from 90% cattle anaerobic digestate with 10% wheat straw addition (CD1); soil treated with compost obtained from 79% cattle anaerobic digestate with 11% crop residues and 10% wheat straw addition (CD2). Each organic amendment was applied to the soil in 2 different doses, in order to provide 140 and 280 kg N ha−1, respectively (single and double dose). Considering the total nitrogen content of each amendment, an amendment application within the 0.15 m soil depth and a soil bulk density of 1.3 Mg m−3, the single and double doses corresponded to: 10–20, 9.5–19, 12–24, 13–26, and 10–20 Mg ha−1 as fresh matter for B, COP, CW, CD1, and CD2, respectively.
The soil used in the experiment was collected from an agricultural field located in the Potenza district (Southern Italy), whose characteristics are detailed below (Table 1). About the amendments, the biochar was obtained from vine pruning residues, through a pyrolysis process carried out in a pilot-scale fixed bed reactor, at the STAR*Facility Centre of Foggia University (Foggia, Southern Italy). Pruning biomass was pyrolyzed in a tubular reactor (30 L capacity), at a reaction temperature of 650 °C for eight hours. Vermicompost and composts were purchased from two industrial plants, which process organic residues from olive mills, crops, and livestock to produce high-quality soil amendments, respectively, located at Eboli (Salerno district, Italy) and Montescaglioso (Matera district, Italy).
Two months after the application of the organic amendments to the soil, seedlings of Swiss chard, cultivar “Eolo”, were transplanted singly into 13 × 13 × 24 cm pots, containing a 2 cm layer of expanded clay on the bottom to improve water drainage and 2 kg of non-treated or treated soil. The soil surface was covered with a 3 cm layer of polythene beads to prevent water losses by evaporation. In the course of the trial, pots were watered every 2–3 days, given approximately 120 mL of water. The experiment was laid out in a randomized complete block design with the six soil treatments and the 2 amendment doses each replicated 4 times.

2.2. Characterization of Soil and Organic Amendments

Before starting the experiment, a soil physico-chemical characterization was performed. The soil particle-size distribution was determined using the pipette-gravimetric method. The pH and electrical conductivity (EC) were measured on 1:2.5 (w/v) aqueous soil extracts and the saturated soil paste extracts, by a GLP 22+ pH-meter and a GLP 31+ EC-meter (Crison Instruments, Barcelona), respectively. The available phosphorus was determined by the sodium bicarbonate method [31], and the total organic carbon by the Walkley-Black acid dichromate digestion technique [32]. The organic matter was appraised by multiplying the percentage of the organic carbon by the factor 1.724. The Na+, Ca2+, Mg2+, and K+ were determined in soil saturated paste extracts and analyzed by using Atomic Absorption Spectroscopy—AAS (Perkin-Elmer Atomic Absorption Spectrophotometer—model 2380). The total nitrogen was obtained according to the Kjeldahl method [33] and the nitrate (NO3−) content was determined by soil extraction with 2 M KCl, followed by spectrophotometric analysis of the extract [34].
The information about the main physico-chemical characteristics detected on the soil are reported in Table 1.
Biochar, vermicompost, and composts were analyzed for a set of chemical properties. The pH and electrical conductivity were determined in deionized water (1:20 w/v), followed by shaking and waiting an equilibrium time of 90 min before measurement by a GLP 22+ pH-meter and a GLP 31+ EC-meter (Crison Instruments, Barcelona), respectively. The proximate analysis determined the relative content in fixed carbon, volatile solids, ash, and moisture, using a TGA analyzer unit (LECO-TGA701) according to the ASTM D7582 method. The ultimate analysis determined the C, N, and H content by dry combustion, using a CHN Elemental Analyser (CHN LECO 680) according to the method LECO-ASTM D5373. In the case of Corg, combustion was carried out after the complete removal of inorganic C with acid. For biochar, from hydrogen (H) and carbon (C) content, the molar ratios of hydrogen to organic carbon (H/Corg) was obtained.
Chemical properties of biochar, vermicompost, and composts are summarized in Table 2. The biochar showed a pH within the range of alkalinity, which is the typical value for the majority of biochar [35], and an EC value higher than that of the receiving soil. The total carbon (C) and the organic carbon (Corg) contents were well within the thresholds of the European Biochar Certificate [36] and according to the Class 1 of IBI-Standard [37], respectively. In addition, H/Corg molar ratio was found to meet the EBC and IBI-Standard requirements (H/Corg ≤ 0.7). Lower H/Corg ratios provided indications of long-term stability and persistence of biochar in the soil, contributing to carbon sequestration [38]; on the contrary, H/Corg values exceeding 0.7 were an indication of non-pyrolytic chars or pyrolysis deficiencies [39]. Vermicompost and composts proven to be mature and stable in terms of chemical characteristics, as reported in Table 2. Differently from biochar, they were neutral or slightly alkaline and resulted in a higher total N content. In addition, vermicompost and composts had a higher EC than the soil. Composts both from olive pomace (COP) and from cattle digestate (CD1 and CD2) showed a higher total N content than vermicompost (CW). Moreover, COP contained more Corg, which was very similar to Corg detected on biochar and more than double of Corg detected on CW, CD1, and CD2.

2.3. Analysis of Plant Growth Parameters

Starting from 10 days after transplanting (DAT), the growth of the seedlings was monitored through an accurate counting of the leaf number, carried out twice per week.
As foreseen by the production specifications of Swiss chard, the cuts of the marketable leaves were scheduled at the end of two growth cycles, each lasting about 4 weeks. The first cut was made at 34 DAT, taking care to not blind the plant, thus allowing the subsequent development of the newly formed basal leaflets; the second cut was made at 60 DAT.
At the end of each growth cycle, before leaf cutting, the height of the plant (H) from the soil line to the top of the longest leaf was measured. Then, leaves were cut, cleaned with tap water, dried with paper towels, counted, weighed to determine the fresh weight (FW), and scanned to measure the leaf area (LA) by using an LI-COR leaf area meter (Model 3100, Inc., Lincoln, NE, USA). Finally, leaves were dried in a ventilated oven at 70 °C until a steady weight to determine the dry weight (DW).

2.4. Analysis of Nitrogen, Nitrate, and Pigment Leaf Content

Dried leaf tissue was analyzed for nitrogen and nitrate content. The nitrogen (total N) content was determined by the Kjeldahl method [33]. Nitrate (NO3−) content was measured by the colorimetric method on leaf water extract added to salicylic acid in concentrated sulfuric acid, as performed by Cataldo et al. [40]. The complex formed by nitration of salicylic acid under highly acidic conditions absorbs maximally at 410 nm in basic (pH > 12) solutions. The absorbance of the chromophore was directly proportional to the amount of nitrate present in the sample.
Before the first cut of the leaves, chlorophyll leaf content was estimated using a hand-held SPAD 502 m (Konica-Minolta corporation, Ltd., Osaka, Japan). Average SPAD chlorophyll readings were calculated from 3 measurements from the tip to the base of the youngest fully expanded leaf (SPADleaf) and of all the leaves per plant (SPADplant). Subsequently, a sample of fresh tissue from each of the 4 plants per treatment was collected to measure the leaf content of the following pigments: Chlorophyll a (CHL a), chlorophyll b (CHL b), and carotenoids (CA). Briefly, fresh leaf tissues were ground with a glass homogenizer in 2 mL 80% acetone (v/v). The homogenate was centrifuged at 2300 g for 2 min, and CHL a, CHL b, and CA contents were, respectively, calculated from absorbances at 646.6, 663.6 [41], and 480 nm [42]. Total chlorophyll (CHL) was determined as the sum of CHL a and CHL b. CHL values correlated well (R2 = 0.88) with SPAD readings (data not shown). Therefore, the SPAD chlorophyll readings were used to give an accurate and rapid estimate of total chlorophyll leaf content during the second growth cycle.

2.5. Statistical Analysis

Data were analyzed using a mixed linear model ANOVA in which “amendment” (fixed effect, six levels: NT, B, COP, CW, CD1, and CD2) and “dose” (random effect, two levels: 140 and 280 kg N ha−1) were the main effects, followed by Duncan test at p ≤ 0.05. This analysis was used to test for amendment (A) and dose (D) differences, as well as for their interaction (A × D). Significant levels were expressed as * p ≤ 0.05, ** p ≤ 0.01 and *** p ≤ 0.001.

3. Results

3.1. Plant Growth Parameters

Figure 1 shows the number of leaves produced by Swiss chard plants during the two considered growth cycles, respectively, completed at 34 and 60 DAT. The total leaf number detected at 34 and 60 DAT (at the first and second cut, respectively) statistically differed between cuts (p ≤ 0.001), amendments (p ≤ 0.05), doses (p ≤ 0.05), and cuts x doses interaction (p ≤ 0.05). During the two growth cycles, leaf number increased over time, reaching, on average, a higher value at the first (17.7 ± 0.4) than the second cut (9.8 ± 0.3). Among amendments, CW showed the highest leaf number both at the first and at the second cut (21.5 ± 2.4 and 13.3 ± 1.6, respectively). The plants treated with B produced a lower number of leaves than the plants treated with the other organic amendments (on average 17.5 and 8.6, respectively at the first and the second cut) that did not differ from the non-treated plants (NT). Except for B, the number of leaves in each treatment was generally higher when the double dose (280 kg N ha−1) was applied compared to the single one (140 kg N ha−1). Considering the two cuts and the two amendment application doses as a whole, the number of leaves produced by Swiss chard plants ranged, on average, from a minimum value of 26.3 in NT and B to a maximum value of 32.2 in CW (29.5 and 34.8, single and double dose, respectively).
Figure 2 reports the height (H), leaf area (LA), and fresh weight (FW) values recorded at the first and second cut of Swiss chard. Considering the first cut, H and LA (Figure 2a,c, respectively) were significantly influenced by organic amendments (p ≤ 0.001). Higher H and LA values were measured on plants treated with amendments from animal wastes (13.5 cm, and 175 cm2, respectively, as average of CW, CD1, and CD2), followed by compost from olive pomace (COP) (12.3 cm, and 140 cm2, respectively) and then biochar (B) (10.0 cm, and 103 cm2, respectively) that did not differ from non-treated plants (NT) (10.6 cm, and 120 cm2, respectively). The plant height was significantly influenced by organic amendments x doses interaction (p ≤ 0.05). Particularly, the highest value of H (15.7 cm) was detected in plants treated with a double dose of CD2. Considering the plant weight, the FW values (Figure 2e) were always statistically different among the organic amendments (p ≤ 0.001) and between the two doses (p ≤ 0.05) applied to the soil. When the soil was treated with the double dose of CW, CD1, and CD2, significantly higher values of FW (10.1, 8.0, and 11.1 g, respectively) were observed. On average, by adding amendments from animal wastes (CW, CD1, CD2) and olive pomace (COP) increases of 41.6% and 12.5% of FW were, respectively, observed in comparison to non-treated plants (NT), while a decrease of 16% was detected in plants treated with biochar (B). Furthermore, again in plants treated with CW, CD1, and CD2, FW increased by 25% on average when the double dose of amendments was applied. On the contrary, FW did not statistically differ between plants treated with COP and B, respectively. Considering both LA and FW values, the interaction between type and dose of organic amendments applied to the soil was not statistically significant.
At the second cut, H, LA, and FW (Figure 2b,d,f, respectively) significantly differed among organic amendments (p ≤ 0.001). Except for H, LA, and FW also differed between the applied doses (p ≤ 0.05 and p ≤ 0.01 for LA and FW, respectively). As already reported for the first leaf cut, H, LA, and FW values were higher in CD2, CD1, and CW (10.2 cm, 76.5 cm2, and 4.3 g, respectively, as the average of the three treatments) than COP and B. This latter was found to be not statistically different from the non-treated control (NT). LA and FW resulted generally higher when the plants were treated with the double dose of CD2, CD1, and CW (84.4 cm2 and 4.8 g, respectively, as an average of the three treatments) compared to the single one.

3.2. Total N and NO3− Leaf Content

Total N content of Swiss chard leaves was significantly influenced by organic amendments (p ≤ 0.001), doses (p ≤ 0.001) as well as their interaction (p ≤ 0.001), both at the first and second cut, as shown in Figure 3a,b, respectively.
At the first leaf cut (Figure 3a), the total N value was significantly higher in plants treated with CD2 (2.6% ± 0.4% dw) than B (2.0% ± 0.1% dw), CD1 (1.9% ± 0.2% dw), COP (1.7% ± 0.1% dw) and NT (1.1% ± 0.1% dw). CD2 did not differ from CW (2.3% ± 0.5% dw). On average, significantly higher values of total N were registered when the soil was treated with the double dose of amendments (2.3% ± 0.2% dw) than the single one (1.8% ± 0.1% dw). The highest total N content in leaf tissues was equal to 2.9% ± 0.1% dw for plants treated with CD2 at double dose, with an increase of 163% compared with NT. At the second cut of the leaves (Figure 3b), total N content was significantly higher in plants treated with amendments from animal wastes (1.7% ± 0.2% dw, as average of CD2, CD1 and CW) than non-treated soil (NT = 0.9% ± 0.1% dw), followed by compost from olive pomace (COP = 1.4% ± 0.3% dw) and biochar (B = 1.4% ± 0.2% dw) that did not differ between each other. Again, the soil addition with the double dose of organic amendments significantly increased nitrogen leaf content than the single one (1.9% ± 0.1% dw vs. 1.3% ± 0.1% dw). Total N reached the highest value (2.4% ± 0.1% dw) in plants treated with double dose of CD2, showing an increase of 176% in comparison with NT.
Figure 3c,d report the NO3− content measured on Swiss chard leaves at the first and second cut, respectively. NO3− content was always affected by organic amendments (p ≤ 0.001) and doses (p ≤ 0.001), as well as their interaction (p ≤ 0.001). At the first cut, plants treated with compost from olive pomace (COP) showed significantly higher NO3− content (333.2 ± 12.2 mg kg−1 Fw) than the other amendments (B = 242.5 ± 5.1; CW = 217.7 ± 8.5; CD1 = 212.7 ± 9.7; CD2 = 208.5 ± 21.6 mg kg−1 Fw) and non-treated control (NT = 163.1 ± 8.4 mg kg−1 Fw). Soil addition with the double dose of amendments always resulted in higher leaf NO3− content (on average, 268.6 ± 11.8 mg kg−1 Fw) than the single one (on average, 217.2 ± 11.8 mg kg−1 Fw). The highest NO3− leaf content, equal to 360.9 ± 10.3 mg kg−1 Fw, was observed in plants treated with the double dose of COP. A similar trend of NO3− leaf content was observed at the second leaf cut. NO3− was higher in plants treated with COP (330.7 ± 9.7 mg kg−1 Fw) than the other amendments (B = 249.1 ± 9.4; CW = 246.4 ± 5.9; CD1 = 244.9 ± 12.5; CD2 = 258.3 ± 19.4 mg kg−1 Fw) and non-treated control (NT 163.8 ± 9.7 mg kg−1 Fw). The average value of NO3− content was significantly higher when the plants were treated with the double amendment dose (291.9 ± 8.0 mg kg−1 Fw) than the single one (239.9 ± 9.3 mg kg−1 Fw). The highest NO3− content was detected in plants treated with COP at double dose (347.6 ± 6.2 mg kg−1 Fw).

3.3. Pigment Leaf Content

The leaf CA, CHL a, CHL b, and total CHL content (Figure 4) measured at the first cut of Swiss chard leaves resulted statistically different only among the amendments (p ≤ 0.05). A significantly higher CA content (Figure 4a), equal to 21.9 mg 100 g Fw−1, was measured in plants treated with compost from animal wastes (CD2). Values of CA ranging from 17.3 to 19.2 mg 100 g Fw−1 were observed in plants treated with compost from olive pomace (COP) and the two amendments from animal wastes (CW and CD1). The lowest CA content was equal to 14.7 mg 100 g Fw−1, as measured in plants treated with biochar (B) that did not differ from non-treated control (NT). As CA, also the leaf CHL a content (Figure 4b) was significantly higher in plants treated with CD2 (91.3 mg 100 g Fw−1), followed by CD1 (80.1 mg 100 g Fw−1), CW (76.4 mg 100 g Fw−1), COP (73.8 mg 100 g Fw−1), then B and NT that showed very low values (57.8 and 55.8 mg 100 g Fw−1, respectively). A similar trend was observed for CHL b (Figure 4c) and total CHL (Figure 4d). Indeed, the highest values of CHL b and total CHL were measured in CD2 (22.9 and 114.3 mg 100 g Fw−1, respectively), while the lowest values in B (14.0 and 71.0 mg 100 g Fw−1, respectively) that did not differed from NT (14.5 and 70.4 mg 100 g Fw−1, respectively). As observed for the leaf CA, CHL a, CHL b, and total CHL content, also the leaf SPAD values (Table 3), were significantly affected only by the organic amendment added to the soil (p ≤ 0.01). At the first leaf cut, plants treated with CW showed the highest chlorophyll content (SPAD reading), with SPADleaf equal to 40.9 and SPADplant to 31.8. At the second cut of Swiss chard leaves, SPADleaf and SPADplant, tend to be higher than the first cut, with more marked differences among the treatments, especially between plants treated with amendments from animal wastes (CW, CD1, and CD2) and plants treated with the other two amendments, i.e., compost from olive pomace (COP) and biochar (B), that did not differ from the non-treated control (NT).

4. Discussion

4.1. Influence of Organic Amendments on Plant Growth

According to the obtained results, Swiss chard growth was effectively enhanced by adding organic amendments to the soil, particularly the amendments deriving from animal wastes as cattle manure and cattle anaerobic digestate (CW, CD1, and CD2, respectively). Similar results were obtained by Doan et al. [43], who reported increased maize growth and yield after soil amendment with vermicompost and compost obtained from buffalo manure.
Swiss chard responded positively to CW, CD1, and CD2, likely due to a greater release of mineral nutrients, mostly of nitrogen, in the treated soil. Although the higher salinity of amendments from animal wastes (EC = 2.7, 4.3 and 2.0 dS m−1, respectively for CW, CD1, and CD2) than that of the receiving soil (EC = 0.4 dS m−1), a higher Swiss chard growth was still observed, due to the tolerance of this species to saline conditions [27].
Referring to results obtained from plants treated with olive pomace compost (COP), lower plant height, leaf area, and fresh weight values were observed. This effect was likely due to the higher C/N ratio of COP than the amendments deriving from animal wastes (C/N = 22, 12, 10, and 10 for COP, CW, CD1, and CD2, respectively). The higher C/N ratio likely resulted in a higher N immobilization in soil added with COP than CW, CD1, and CD2 that increased the competition for nitrogen in plants and soil microorganisms, determining a slower N release and a lower N availability for plant uptake. In this regard, Garcia-Ruiz et al. [44] reported the effects of N immobilization during the short-term (3–12 months) decomposition of an olive pomace compost, also evidenced by reduced nitrate lost from the soil. On the contrary, in the long term (15 years), the authors observed an increase of total N amount and N easily mineralized pool in the soil. Morra et al. [45] found that the higher the quantity of olive pomace compost applied to the soil, the slower the release of NO3−-N for crop needs.
The application of biochar did not show any positive effect on the productive response of Swiss chard plants. As reported in the literature, the effects of biochar addition to cultivated soil on crop growth are highly variable [46] and not always consistent [47], due to the different biochar feedstock types, pyrolysis conditions, biochar structure and composition [48,49,50,51], soil properties [52,53], and tested crop [54]. Gravel et al. [55] reported that the amendment of potting soil with biochar had no significant effect on shoot growth of sweet pepper, geranium, and basil; while increased coriander shoot weight and decreased the weight of lettuce plants. In a net-house experiment carried out to assess the impacts on plant growth of different biochar types in comparison with their biomass sources, Khan et al. [56] observed a better growth of the kalmi plant (Ipomea aquatica) under cow dung biomass treatment than cow dung biochar. Under the other treatments with two biochar types, respectively, from poultry manure and sludge, plant growth was lower than the non-treated control. Furthermore, the negative effects of biochar on horticultural crop growth were reported when biochar was made from poultry litter [57]. Shoot length and fresh/dry masses of red lettuce plants grown in a rice husk biochar substrate were decreased by 49% compared to the perlite substrate [58]. Decreased growth and nutrient uptake imbalance were observed in lettuce and corn plants after the application of freshly prepared biochar into the soil [59]. Atkinson et al. [60] observed that the usually high C/N ratios of biochar could lead to a higher N immobilization and eventually to N deficiencies in plants. In this regard, Clough and Condron [61] reported N immobilization in biochar amended soils; Novak et al. [62], in vitro experiments, reported a NO3−-N immobilization between 40% and 70% due to biochar application. Limiting N content by biochar application in soils due to the high C/N ratio, it might reduce crop productivity temporarily [63]. Biochar used in our experiment had a high C/N ratio (see Table 2), and our results could be likely due to a more limited supply of nitrogen for plant uptake. The negative impact of biochar on N availability for Swiss chard growth resulted even more critically, considering the short growth cycle of the plants and the biochar benefits that may be achieved over time in comparison with the composts.

4.2. Influence of Organic Amendments on Nitrogen, Nitrate and Pigment Leaf Content

Still considering the obtained results, total N leaf content was higher in Swiss chard plants growing on soil treated with amendments from animal wastes, particularly when the double dose (280 kg ha−1) was added, than the compost from olive pomace and biochar. Hernandez et al. [64], in a greenhouse experiment aimed at evaluating the effect on lettuce of compost and vermicompost from cattle manure with an estimated N contribution to the soil of 278 kg ha−1, observed a leaf N content of 1.4% and 1.6% dw in vermicompost and compost, respectively. The authors reported a lower nitrogen leaf content than our study if considering the double dose of amendment addition to the soil. Such differences will be likely due to the dynamic of nutrient release in the soil after incorporating organic fertilizers. The nutrient release and the consequent nutrient availability for plant uptake in the soil are not only related to the total amount of mineral elements contained in the amendment but largely depend on the amendment properties [65]. The stability of organic matter, maturity, and the physico-chemical characteristics are factors influencing the N availability in composts. The N dynamic in the soil after adding organic amendments can also be affected by environmental conditions (soil type and climate), which make difficult the comparison of different experiments [66,67,68]. Moreover, the nitrogen content of the Swiss chard is strongly affected by fertilization [1,6]. In our study, no mineral fertilization was applied, therefore, the increases in N content observed in plants growing in the amended soils relative to the non-treated control indicate a certain release of N from the organic amendments, net of possible N immobilization and volatile N losses. Although organic amendments were added to the soil in two doses in order to, respectively, provide 140 and 280 kg N ha−1, Swiss chard plants took up the amount of N that actually became available for plant growth. This may be the reason for the low nitrogen content observed in our study in comparison with the results found by other authors. For instance, Echer et al. [69] found a Swiss chard nitrogen content varying from 36 to 43 g kg−1 by increasing the mineral nitrogen fertilization dose from 0 to 160 kg ha−1.
Referring to our results about leaf NO3− content, it is worth to underline that, among leafy vegetables (i.e., rocket, spinach, lettuce, celery, and parsley), Swiss chard is known as one of the most prominent nitrate-accumulating species [6] (Santamaria, 2006). NO3− content of Swiss chard leaves evaluated in our experiment was in the range reported by EFSA [70] and an updated review by Colla et al. [71]. Moreover, it was well below the NO3− thresholds established by the European Commission regulations Nº 1881/2006 and 1258/2011 for fresh spinach (3500 mg kg−1 Fw); preserved, deep-frozen or frozen spinach (2000 mg kg−1 Fw); fresh lettuce (3000–5000 mg kg−1 Fw); Iceberg type lettuce (2000–2500 mg kg−1 Fw); salad and wild rocket. (6000–7000 mg kg−1 Fw).
Nitrate content in vegetables depends on the crop cultivation system adopted, as showed by Herencia et al. [72]. The authors reported a lower nitrate content in organic (from 546 to 1274 mg kg−1 Fw) than mineral fertilized (from 780 to 2113 mg kg−1 Fw) Swiss chard. Matallana González et al. [73] in samples of Swiss chard collected directly from an organic farm in Spain found values of nitrate content (2630.4 mg kg−1 Fw) near or higher than the ones purchased from organic food stores (2595 mg kg−1 Fw). Lower nitrate values (in the range of 546–1274 mg kg−1 Fw) were observed by Bosch Bosch et al. [74] in organic Swiss chard. Our results are very similar to those found by Raigon et al. [75] who reported for organically cultivated Swiss chard a nitrate content below 400 mg kg−1 Fw.
Despite the lower total N content, leaves of Swiss chard plants treated with compost from olive pomace (COP) showed a higher NO3− content than the other organic amendments, both applying the single and the double dose. This may have been due to the higher NO3−-N availability than NH4+-N from COP, likely occurred in the soil treated with such compost. This condition may have led to higher nitrate accumulation in the leaves of COP treated plants. Indeed, as previously reported by Barcelos et al. [76] and Conesa et al. [77], spinach (like Swiss chard, spinach is a very high accumulator vegetable of NO3−) accumulated more nitrate when grown with nutrient solutions containing high NO3−-N:NH4+-N ratio. In addition, the high NO3− content observed in plants treated with COP could also be related to lower nitrogen assimilation (conversion of mineral nitrogen in organic nitrogen) that likely occurred in the course of plant growth cycles. It is known that the nitrate assimilation pathway starts with nitrate uptake followed by nitrate reduction resulting in ammonium, which is fixed into the amino acids glutamine and glutamate in most plants [78]. The hypothesis that in COP treated plants, the nitrate uptake exceeded nitrate reduction could also be supported by their lower height, leaf area, and leaf fresh weight than the plants treated with the other organic amendments (Figure 2a,c,e, respectively). A critical examination of the factors that can affect nitrate accumulation in a wide range of horticultural crops is reported in Colla et al. [71].
The leaf chlorophyll readings performed in all the experimental treatments were within the range reported by other authors [76,77,79]. The higher leaf pigment content (carotenoids and chlorophyll) observed in plants treated with amendments from animal wastes (CW, CD1, and CD2) than compost from olive pomace (COP) and biochar (B) were likely due to an improved plant nutritional status. More specifically, this result may be due to the higher availability of nitrogen, which is known to be an integral part of chlorophyll molecules (in addition to amino acids, nucleic acids, phosphatides, alkaloids, enzymes, hormones, and vitamins) [80], which the Swiss chard plants experienced in the abovementioned treatments.

5. Conclusions

Under the adopted experimental conditions (pot cultivation and short crop growing cycle), Swiss chard responded positively to the application of organic amendments. Particularly when amendments from animal wastes (vermicompost from cattle manure and composts from cattle anaerobic digestate) were added to the soil, significant increases of plant growth parameters and pigment leaf contents were observed, indicating suitable soil growth conditions for ensuring plant yield and quality. Moreover, the higher nitrogen leaf content of Swiss chard growing in soil treated with amendments from animal wastes suggested the adequate fertilizing value of the tested products.
For all the considered organic amendments, the double dose (280 kg N ha−1) increased the growth parameters compared to the single dose (140 kg N ha−1) and the nitrate content of the leaves was always well below the threshold for NO3− concentration in other leafy vegetables (spinach, lettuce, and rocket), as established by the European Union to avoid harmful effects on human health of raw vegetable consumption. Unlike the amendments obtained from animal wastes, biochar from vine pruning did not lead to positive or negative effects on growth and pigment chlorophyll content of Swiss chard, with results equal to those detected on non-treated plants.
The conclusion to be drawn suggests that organic amendments applied to the soil can contribute to improving the quantitative and qualitative traits of Swiss chard. However, the different response of plants to biochar, vermicompost, and composts utilized in the experiment suggests that further experiments, as well as field-scale trials, are needed to better understand the effects of type and dose of amendment able to improve the production of fresh-cut vegetables characterized by short-growing cycle such as Swiss chard.

Author Contributions

Conceptualization, A.L. and A.R.R.; methodology, A.L. and A.R.R.; validation, A.L. and A.R.R.; formal analysis, A.L., A.R.R., and V.T.; investigation, A.L. and A.R.R.; resources, A.L. and A.R.R.; data curation, A.L. A.R.R., and V.T.; writing—original draft preparation, A.L.; writing—review and editing, A.L. and A.R.R.; visualization, A.L..; supervision, A.L. and A.R.R.; project administration, A.R.R.; funding acquisition, A.R.R. All authors have read and agreed to the published version of the manuscript.

Funding

This research was carried out in the framework of the project “Smart Basilicata”, which was approved by the Italian Ministry of Education, University and Research (Notice MIUR n.84/2012, PON 2007–2013 of 2 March 2012) and was funded by the Cohesion Fund 2007–2013 of the Basilicata Regional Authority.

Acknowledgments

The authors are grateful to Susanna De Maria, Giuseppe Mercurio and Antonio Pisani for the technical assistance in the greenhouse experiment and the laboratory analyses.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Ivanović, L.; Milašević, I.; Topalović, A.; Ðurović, D.; Mugoša, B.; Knežević, M.; Vrvić, M. Nutritional and phytochemical content of Swiss chard from Montenegro, under different fertilization and irrigation treatments. Brit. Food J. 2019, 121, 411–425. [Google Scholar] [CrossRef]
  2. Miceli, A.; Miceli, C. Effect of nitrogen fertilization on the quality of Swiss chard at harvest and during storage as minimally processed produce. J. Food Qual. 2014, 37, 125–134. [Google Scholar] [CrossRef]
  3. Ninfali, P.; Angelino, D. Nutritional and functional potential of Beta vulgaris cicla and rubra. Fitoterapia 2013, 89, 188–199. [Google Scholar] [CrossRef] [PubMed]
  4. Pyo, Y.H.; Lee, T.C.; Logendra, L.; Rosen, R.T. Antioxidant activity and phenolic compounds of Swiss chard (Beta vulgaris subspecies cycla) extracts. Food Chem. 2004, 85, 19–26. [Google Scholar] [CrossRef]
  5. Santamaria, P.; Elia, A.; Serio, F.; Todaro, E. A survey of nitrate and oxalate content in fresh vegetables. J. Sci. Food Agric. 1999, 79, 1882–1888. [Google Scholar] [CrossRef]
  6. Santamaria, P. Nitrate in vegetables: Toxicity, content, intake and EC regulation. J. Sci. Food Agric. 2006, 86, 10–17. [Google Scholar] [CrossRef]
  7. Pokluda, R.; Kuben, J. Comparison of selected Swiss chard (Beta vulgaris ssp. cicla L.) varieties. Hort. Sci. 2002, 29, 114–118. [Google Scholar]
  8. Kolota, E.; Adamczewska-Sowińska, K.; Czerniak, K. Yield and nutritional value of Swiss Chard Grown for Summer and Autumn Harvest. J. Agric. Sci. 2010, 2, 120–124. [Google Scholar] [CrossRef] [Green Version]
  9. Libutti, A.; Monteleone, M. Soil vs. groundwater: The quality dilemma. Managing nitrogen leaching and salinity control under irrigated agriculture in Mediterranean conditions Agric. Water Manag. 2017, 186, 40–50. [Google Scholar]
  10. Dzida, K.; Pitura, K. The influence of varied nitrogen fertilization on yield and chemical composition of Swiss chard (Beta vulgaris L. var. cicla L.). Acta Sci. Pol.-Hortorum 2008, 7, 15–24. [Google Scholar]
  11. Engelbrecht, G.M.; Ceronio, G.M.; Motseki, P.C. Effect of nitrogen levels and sources on production of Swiss Chard (Beta vulgaris var. cicla). S. Afr. J. Plant Soil 2010, 27, 229–234. [Google Scholar] [CrossRef] [Green Version]
  12. Razgallah, N.; Chikh-Rouhou, H.; Boughattas, I.; M’hamdi, M. Nitrates contents in some vegetables in Tunisia. Arch. Agron. Soil Sci. 2016, 62, 473–483. [Google Scholar] [CrossRef]
  13. Martínez-Blanco, J.; Lazcano, C.; Christensen, T.H.; Muñoz, P.; Rieradevall, J.; Møller, J.; Antón, A.; Boldrin, A. Compost benefits for agriculture evaluated by life cycle assessment: A review. Agron. Sustain. Dev. 2013, 33, 721–732. [Google Scholar] [CrossRef] [Green Version]
  14. Nair, V.D.; Nair, P.K.R.; Dari, B.; Freitas, A.M.; Chatterjee, N.; Pinheiro, F.M. Biochar in the Agroecosystem-Climate-Change-Sustainability Nexus. Front. Plant Sci. 2017, 8, 1–9. [Google Scholar] [CrossRef]
  15. Demiraj, E.; Libutti, A.; Malltezi, J.; Rroço, E.; Brahushi, F.; Monteleone, M.; Sulçe, S. Effect of organic amendments on nitrate leaching mitigation in a sandy loam soil of Shkodra district, Albania. Ital. J. Agron. 2018, 13, 1136. [Google Scholar] [CrossRef] [Green Version]
  16. Libutti, A.; Mucci, M.; Francavilla, M.; Monteleone, M. Effect of biochar amendment on nitrate retention in a silty clay loam soil. Ital. J. Agron. 2016, 11, 273–276. [Google Scholar] [CrossRef] [Green Version]
  17. Gobbi, V.; Bonato, S.; Nicoletto, C.; Zanin, G. Spent mushroom substrate as organic fertilizer: Vegetable organic trials. Acta Hortic. 2016, 1146, 49–56. [Google Scholar] [CrossRef]
  18. Lehmann, J. Bio-energy in the black. Front. Ecol. Environ. 2007, 5, 381–387. [Google Scholar] [CrossRef] [Green Version]
  19. Zabaniotou, A.; Rovas, D.; Libutti, A.; Monteleone, M. Boosting circular economy and closing the loop in agriculture: Case study of a small-scale pyrolysis-biochar based system integrated in an olive farm in simbiosi with an olive mill. Environ. Dev. 2015, 14, 22–36. [Google Scholar] [CrossRef]
  20. Monlau, F.; Francavilla, M.; Sambusiti, C.; Antoniou, N.; Solhy, A.; Libutti, A.; Zabaniotou, A.; Barakat, A.; Monteleone, M. Toward a functional integration of anaerobic digestion and pyrolysis for a sustainable resource management. Comparison between solid-digestate and its derived pyrochar as soil amendment. Appl. Energy 2016, 169, 652–662. [Google Scholar] [CrossRef]
  21. Zabaniotou, A.; Rovas, D.; Delivand, M.K.; Francavilla, M.; Libutti, A.; Cammerino, A.R.B.; Monteleone, M. Conceptual vision of bioenergy sector development in Mediterranean regions based on decentralized thermochemical systems. Sustain. Energy Technol. Assess. 2017, 23, 33–47. [Google Scholar] [CrossRef]
  22. Libutti, A.; Cammerino, A.R.B.; Francavilla, M.; Massimo, M. Soil Amendment with Biochar Affects Water Drainage and Nutrient Losses by Leaching: Experimental Evidence under Field-Grown Conditions. Agronomy 2019, 9, 758. [Google Scholar] [CrossRef] [Green Version]
  23. Urra, J.; Alkorta, I.; Garbisu, C. Potential benefits and risks for soil health derived from the use of organic amendments in agriculture. Agronomy 2019, 9, 542. [Google Scholar] [CrossRef] [Green Version]
  24. Subedi, R.; Bertora, C.; Zavattaro, L.; Grignani, C. Crop response to soils amended with biochar: Expected benefits and unintended, risks. Ital. J. Agron 2017, 12, 161–173. [Google Scholar] [CrossRef] [Green Version]
  25. Paredes, C.; Cegarra, J.; Bernal, M.P.; Roig, A. Influence of olive mill wastewater in composting and impact of the compost on a Swiss chard crop and soil properties. Environ. Int. 2005, 31, 305–312. [Google Scholar] [CrossRef]
  26. Abbey, L.; Young, C.; Teitel-Payne, R.; Howe, K. Evaluation of proportions of vermicompost and coir in a medium for container-grown Swiss chard. Int. J. Veg. Sci. 2012, 18, 109–120. [Google Scholar] [CrossRef]
  27. Smith, D.C.; Beharee, V.; Hughes, J.C. The effects of compost produced by a simple composting procedure on the yields of Swiss chard (Beta vulgaris L. var. flavescens) and common bean (Phaseolus vulgaris L. var. nanus). Sci. Hortic. 2001, 91, 393–406. [Google Scholar]
  28. Trupiano, D.; Cocozza, C.; Baronti, S.; Amendola, C.; Vaccari, P.F.; Lustrato, G.; Di Lonardo, S.; Fantasma, F.; Tognetti, R.; Scippa, G.S. The Effects of Biochar and Its Combination with Compost on Lettuce (Lactuca sativa L.) Growth, Soil Properties, and Soil Microbial Activity and Abundance. Int. J. Agron. 2017, 2017, 3158207. [Google Scholar] [CrossRef] [Green Version]
  29. Liu, B.; Cai, Z.; Zhang, Y.; Liu, G.; Luo, X.; Zheng, H. Comparison of efficacies of peanut shell biochar and biochar-based compost on two leafy vegetable productivity in an infertile land. Chemosphere 2019, 224, 151–161. [Google Scholar] [CrossRef]
  30. Carter, S.; Shackley, S.; Sohi, S.; Suy, T.B.; Haefele, S. The Impact of Biochar Application on Soil Properties and Plant Growth of Pot Grown Lettuce (Lactuca sativa) and Cabbage (Brassica chinensis). Agronomy 2013, 3, 404–418. [Google Scholar] [CrossRef] [Green Version]
  31. Olsen, S.R.; Cole, C.V.; Watanabe, F.S.; Dean, L.A. Estimation of Available Phosphorus in Soil by Extraction with Sodium Bicarbonate; USDA Circular 939; USDA: Washington, DC, USA, 1954; pp. 1–19.
  32. Walkley, A.; Black, I.A. An examination of the Degtjareff method fordetermining soil organic matter and a proposed modification of the chromicacid titration method. Soil Sci. 1934, 37, 29–38. [Google Scholar] [CrossRef]
  33. Bremner, J.M. Nitrogen-total. In Methods of Soil Analysis Part 3—Chemical Methods; SSSA Book Ser. No. 5; Sparks, D.L., Page, A.L., Johnston, C.T., Summ, M.E., Eds.; SSSA: Madison, WI, USA, 1996; pp. 1058–1121. [Google Scholar]
  34. Keeney, D.R.; Nelson, D.W. Nitrogen Inorganic Forms. In Methods of Soil Analysis Part 2, 2nd ed.; Page, A.L., Miller, R.H., Keeney, D.R., Eds.; American Society of Agronomy and Soil Science Society of America Publisher: Madison, WI, USA, 1982; pp. 643–698. [Google Scholar]
  35. Chan, K.Y.; Xu, K. Biochar: Nutrient properties and their enhancement. In Biochar for Environmental Management. Science and Technology; Lehmann, J., Joseph, S., Eds.; Earthscan: London, UK, 2009; pp. 67–84. [Google Scholar]
  36. EBC. European Biochar Certificate Guidelines for a Sustainable Production of Biochar; European Biochar Certificate (EBC): Arbaz, Switzerland, 2012. [Google Scholar]
  37. IBI. International Bichar Inititative, Standardized Product Definition and Product Testing Guidelines for Biochar that is Used in Soil; IBI-STD-2.0; IBI: Toronto, ON, Canada, 2014. [Google Scholar]
  38. Cheng, C.H.; Lehmann, J.; Engelhard, M.H. Natural oxidation of black carbon in soils: Changes in molecular form and surface charge along a climosequence. Geochim. Cosmochim. Acta 2008, 72, 1598–1610. [Google Scholar] [CrossRef]
  39. Schimmelpfennig, S.; Glaser, B. One step forward toward characterization: Some important material properties to distinguish biochars. J. Environ. Qual. 2012, 41, 1001–1013. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  40. Cataldo, D.A.; Maroon, M.; Schrader, L.E.; Youngs, V.L. Rapid Colorimetric Determination of Nitrate in Plant-Tissue by Nitration of Salicylic-Acid. Commun. Soil Sci. Plan Anal. 1975, 6, 71–80. [Google Scholar] [CrossRef]
  41. Porra, R.J.; Thompson, W.A.; Kriedemann, P.E. Determination of accurate extinction coefficients and simultaneous equations for assaying chlorophylls a and b extracted with four different solvents: Verification of the concentration of chlorophyll standards by atomic absorption spectrometry. Biochim. Biophys. Acta 1989, 975, 384–394. [Google Scholar] [CrossRef]
  42. Wellburn, A.R. The spectral determination of chlorophylls a and b, as well as total carotenoids, using various solvents with spectrophotometers of different resolution. J. Plant Physiol. 1994, 144, 307–313. [Google Scholar] [CrossRef]
  43. Doan, T.T.; des Tureaux, T.H.; Rumperl, C.; Janeau, J.; Jouquet, P. Impact of compost, vermicompost and biochar on soil fertility, maize yield and soil erosion in Northern Vietnam: A three year mesocosm experiment. Sci. Total Environ. 2015, 514, 147–154. [Google Scholar] [CrossRef]
  44. Garcia-Ruiz, R.; Ochoa, V.; Gómez-Muñoz, B.; Alvarez de la Puente, J.M. Does the composted olive mill pomace increase the sustainable N use of olive oil cropping? In Proceedings of the 16th Nitrogen Workshop on Connecting Different Scales of Nitrogen Use in Agriculture, Torino, Italy, 28 June–1 July 2009. [Google Scholar]
  45. Morra, L.; Pizzolongo, G.; Baiano, S.; Pentangelo, A. Comparison of olive pomace and biowaste composts in vegetable cropping systems. Ital. J. Agron. 2013, 8, 206–216. [Google Scholar] [CrossRef]
  46. Paz-Ferreiro, J.; Fu, S.; Méndez, A.; Gascó, G. Interactive effects of biochar and the earthworm Pontoscolex corethrurus on plant productivity and soil enzyme activities. J. Soil. Sediments 2014, 14, 483–494. [Google Scholar] [CrossRef]
  47. Jones, L.; Rousk, J.; Edwards-Jones, G.; DeLuca, T.H.; Murphy, D.V. Biochar-mediated changes in soil quality and plant growth in a three year field trial. Soil Biol. Biochem. 2012, 45, 113–124. [Google Scholar] [CrossRef]
  48. Rajkovich, S.; Enders, A.; Hanley, K.; Hyland, C.; Zimmermann, A.R.; Lehmann, J. Corn growth and nitrogen nutrition after additions of biochars with varying properties to a temperate soil. Biol. Fertil. Soils 2012, 48, 271–284. [Google Scholar] [CrossRef]
  49. Chatterjee, S.; Santos, F.; Abiven, S.; Itin, B.; Stark, R.E.; Jeffrey, A.B. Elucidating the chemical structure of pyrogenic organic matter by combining magnetic resonance, mid-infrared spectroscopy and mass spectrometry. Org. Geochem. 2012, 51, 35–44. [Google Scholar] [CrossRef]
  50. Windeatt, J.H.; Ross, A.; Williams, P.T.; Forster, P.; Nahil, M.A.; Singh, S. Characteristics of biochars from crop residues: Potential for carbon sequestration and soil amendment. J. Environ. Manag. 2014, 146, 189–197. [Google Scholar] [CrossRef] [PubMed]
  51. Meschewski, E.; Holm, N.; Sharma, B.K.; Spokas, K.; Minalt, N.; Kelly, J.J. Pyrolysis biochar has negligible effects on soil greenhouse gas production, microbial communities, plant germination, and initial seedling growth. Chemosphere 2019, 228, 565–576. [Google Scholar] [CrossRef] [PubMed]
  52. Spokas, K.A.; Cantrell, K.B.; Novak, J.M.; Archer, D.W.; Ippolito, J.A.; Collins, H.P.; Boateng, A.A.; Lima, I.M.; Lamb, M.C.; McAloon, A.J.; et al. Biochar: A synthesis of its agronomic impact beyond carbon sequestration. J. Environ. Qual. 2012, 41, 973–989. [Google Scholar] [CrossRef] [PubMed]
  53. Ding, Y.; Liu, Y.; Liu, S.; Li, Z.; Tan, X.; Huang, X.; Zeng, G.; Zhou, L.; Zheng, B. Biochar to improve soil fertility. A review. Agron. Sustain. Dev. 2016, 36, 36. [Google Scholar] [CrossRef] [Green Version]
  54. Olszyk, D.; Johnson, M.; Shiroyama, T.; Novak, J.; Cantrell, K.; Watts, D. Effects of Biochar Feedstock and Pyrolysis Temperature on Growth of Corn, Soybean, Lettuce and Carrot; Society for Environmental Toxicology and Chemistry, US Environmental Protection Agency: Vancouver, BC, Canada, 2014. [Google Scholar]
  55. Gravel, V.; Dorais, M.; Menard, C. Organic potted plants amended with biochar: Its effect on growth and Pythium colonization. Can. J. Plant Sci. 2013, 93, 12171227. [Google Scholar] [CrossRef]
  56. Khan, T.F.; Salma, M.U.; Hossain, S.A. Impacts of Different Sources of Biochar on Plant Growth Characteristics. Am. J. Plant Sci. 2018, 9, 1922–1934. [Google Scholar] [CrossRef] [Green Version]
  57. Revell, K.T.; Maguire, R.O.; Agblevor, F.A. Influence of poultry litter biochar on soil properties and plant growth. Soil Sci. 2012, 177, 402–408. [Google Scholar] [CrossRef]
  58. Awadi, Y.M.; Lee, S.S.; Ahmed, M.B.M.; Vu, N.T.; Farooq, M.; Seop, K.I.; Kim, H.S.; Vithanage, M.; Usman, A.R.A.; Al-Wabel, M.; et al. Biochar, a potential hydroponic growth substrate, enhances the nutritional status and growth of leafy vegetables. J. Clean. Prod. 2017, 156, 181–188. [Google Scholar] [CrossRef]
  59. McClellan, T.; Deenik, J.; Uehara, G.; Antal, M. Effects of Flashed Carbonized Macadamia Nutshell Charcoal on Plant Growth and Soil Chemical Properties. In Proceedings of the ASA-CSSA-SSA International Annual Meetings, New Orleans, LA, USA, 6 November 2007; p. 194. [Google Scholar]
  60. Atkinson, C.J.; Fitzgerald, J.D.; Hipps, N.A. Potential mechanisms for achieving agriculture benefits from biochar application to temperate soils: A review. Plant Soil 2010, 337, 11–18. [Google Scholar] [CrossRef]
  61. Clough, T.J.; Condron, L.M. Biochar and the nitrogen cycle: Introduction. J. Environ. Qual. 2010, 39, 1218–1223. [Google Scholar] [CrossRef] [PubMed]
  62. Novak, J.M.; Busscher, W.J.; Watts, D.W.; Laird, D.A.; Ahmedna, M.A.; Niandou, M.A.S. Short-term CO2mineralization after additions of biochar and switchgrass to aTypic Kandiudult. Geoderma 2010, 154, 281–288. [Google Scholar] [CrossRef]
  63. Lehmann, J.; Pereira, J.; Steiner, C.; Nehls, T.; Zechs, W.; Glaser, B. Nutrient availability and Leaching in the Archaeological Anthrosols and Ferrosol of the Central Amazon Basin: Fertilizer, Manure and Charcoal Amendments. Plant Soil 2003, 249, 343–357. [Google Scholar] [CrossRef]
  64. Hernández, A.; Castillo, H.; Ojeda, D.; Arras, A.; López, J.; Sánchez, E. Effect of vermicompost and compost on lettuce production. Chil. J. Agric. Res. 2010, 70, 583–589. [Google Scholar] [CrossRef] [Green Version]
  65. Helgason, B.; Larney, F.L.; Janzen, H.H.; Olson, B.M. Nitrogen dynamics in soil amended with composted cattle manure. Can. J. Soil Sci. 2007, 87, 43–50. [Google Scholar]
  66. Wolkowski, R. Nitrogen management considerations for landspreading municipal solid waste compost. J. Environ. Qual. 2003, 32, 1844–1850. [Google Scholar] [CrossRef]
  67. Hartl, W.; Erhart, E. Crop nitrogen recovery and soil nitrogen dynamics in a 10- year field experiment with biowaste compost. J. Plant Nutr. Soil Sci. 2005, 168, 781–788. [Google Scholar] [CrossRef]
  68. Gutser, R.; Ebertseder, T.; Weber, A.; Schraml, M.; Schmidhalter, U. Short-term and residual availability of nitrogen after long-term application of organic amendments on arable land. J. Plant Nutr. Soil Sci. 2005, 168, 439–446. [Google Scholar] [CrossRef]
  69. Echer, M.M.; Zoz, T.; Rossol, C.D.; Steiner, F.; Castagnara, D.D.; Lana, M.C. Plant density and nitrogen fertilization in Swiss chard. Hortic. Bras. 2012, 30, 703–707. [Google Scholar] [CrossRef]
  70. EFSA. Opinion of the scientific panel on contaminants in the food chain on a request from the European commission to perform a scientific risk assessment on nitrate in vegetables. EFSA J. 2008, 6, 689. [Google Scholar] [CrossRef]
  71. Colla, G.; Kim, H.J.; Kyriacou, M.C.; Rouphael, Y. Nitrate in fruits and vegetables. Sci. Hortic. 2018, 237, 221–238. [Google Scholar] [CrossRef]
  72. Herencia, J.F.; Ruiz-Porras, J.C.; Melero, S.; Garcia-Galavis, P.A.; Morillo, E.; Maqueda, C. comparison between organic and mineral fertilization for soil fertility levels, crop macronutrient concentration and yield. Agron. J. 2007, 99, 973–983. [Google Scholar] [CrossRef]
  73. Matallana- Gonzales, M.C.; Martinez-Tomè, M.J.; Isasa, M.E.T. Nitrate and nitrite content in organically cultivated vegetables. Food Addit. Contam. Part B 2010, 3, 19–29. [Google Scholar] [CrossRef]
  74. Bosch, M.N.; Alvarez, J.M.; Rodriguez, M.L.P. Influencia del tipo de abono sobre la acumulacion de nitrato en vegetales. Ann. Bromatol. 1991, 2, 215–220. [Google Scholar]
  75. Raigon, M.D.; Gento, A.D.; Sierra, J.M.C.; Vidal, E. Comparacion de parametros de calida en hortalizas de hoja ancha bajo sistemas de produccion ecologica y convencional. Agric. Vergel 2002, 241, 26–32. [Google Scholar]
  76. Barcelos, C.; Machado, R.M.A.; Alves-Pereira, I.; Ferreira, R.; Bryla, D.R. Effects of substrate type on plant growth and nitrogen and nitrate concentration in spinach. Int. J. Plant. Biol. 2016, 7, 6325. [Google Scholar] [CrossRef] [Green Version]
  77. Conesa, E.; Niñirola, D.; Vicente, M.J.; Ochoa, J.; Bañón, S.; Fernández, J.A. The influence of nitrate/ammonium ratio on yield quality and nitrate, oxalate and vitamin C content of baby leaf spinach and bladder campion plants grown in a floating system. Acta Hortic. 2008, 843, 269–273. [Google Scholar] [CrossRef]
  78. Tischner, R. Nitrate uptake and reduction in higher and lower plants. Plant Cell Environ. 2000, 23, 1005–1024. [Google Scholar] [CrossRef]
  79. Liu, Y.J.; Tong, Y.P.; Zhu, Y.G.; Ding, H.; Smith, E.A. Leaf chlorophyll readings as an indicator for spinach yield and nutritional quality with different nitrogen fertilizer applications. J. Plant Nutr. 2006, 29, 1207–1217. [Google Scholar] [CrossRef]
  80. Castellanos, J.Z.; Uvalle-Bueno, J.X.; Aguilar-Santelises, Y.A. Manual de Interpretación de Análisis de Suelos, Aguas Agrícolas, Plantas ECP, 2nd ed.; INIFAP: Chapingo, Mexico, 2000. [Google Scholar]
Agronomy 10 00346 g001 550
Figure 1. Number of leaves produced during 60 days after transplanting by Swiss chard plants treated with different organic amendments (B, biochar; COP, compost from olive pomace; CW, vermicompost from cattle manure; CD1, compost from 90% cattle anaerobic digestate with 10% wheat straw addition; CD2, compost from 79% cattle anaerobic digestate with 11% crop residues and 10% wheat straw addition), each added to provide 140 and 280 of kg N ha−1 (black and white symbols, respectively), plus a non-treated soil or control (NT). The arrows indicate the first and second leaf cut (at 34 and 60 DAT, respectively). Values are means (n = 4) ± standard errors.
Figure 1. Number of leaves produced during 60 days after transplanting by Swiss chard plants treated with different organic amendments (B, biochar; COP, compost from olive pomace; CW, vermicompost from cattle manure; CD1, compost from 90% cattle anaerobic digestate with 10% wheat straw addition; CD2, compost from 79% cattle anaerobic digestate with 11% crop residues and 10% wheat straw addition), each added to provide 140 and 280 of kg N ha−1 (black and white symbols, respectively), plus a non-treated soil or control (NT). The arrows indicate the first and second leaf cut (at 34 and 60 DAT, respectively). Values are means (n = 4) ± standard errors.
Agronomy 10 00346 g001
Agronomy 10 00346 g002 550
Figure 2. Plant height (a,b), leaf area (c,d) and leaf fresh weight (e,f) of Swiss chard treated with different organic amendments (B, biochar; COP, compost from olive pomace; CW, vermicompost from cattle manure; CD1, compost from 90% cattle anaerobic digestate with 10% wheat straw addition; CD2, compost from 79% cattle anaerobic digestate with 11% crop residues and 10% wheat straw addition), each added to provide 140 and 280 of kg N ha−1 (grey and black bars, respectively), plus a non-treated soil or control (NT, white bar). The graphs on the left refer to the first cut of the leaves (a,c,e) while on the right to the second cut (b,d,f). Values are means (n = 4) ± standard errors. Data presented in each graph were analyzed by two-way ANOVA followed by the Duncan test at p ≤ 0.05. A, amendment; D, dose; *, p ≤ 0.05; **, p ≤ 0.01; ***, p ≤ 0.001; n.s., not significant.
Figure 2. Plant height (a,b), leaf area (c,d) and leaf fresh weight (e,f) of Swiss chard treated with different organic amendments (B, biochar; COP, compost from olive pomace; CW, vermicompost from cattle manure; CD1, compost from 90% cattle anaerobic digestate with 10% wheat straw addition; CD2, compost from 79% cattle anaerobic digestate with 11% crop residues and 10% wheat straw addition), each added to provide 140 and 280 of kg N ha−1 (grey and black bars, respectively), plus a non-treated soil or control (NT, white bar). The graphs on the left refer to the first cut of the leaves (a,c,e) while on the right to the second cut (b,d,f). Values are means (n = 4) ± standard errors. Data presented in each graph were analyzed by two-way ANOVA followed by the Duncan test at p ≤ 0.05. A, amendment; D, dose; *, p ≤ 0.05; **, p ≤ 0.01; ***, p ≤ 0.001; n.s., not significant.
Agronomy 10 00346 g002
Agronomy 10 00346 g003 550
Figure 3. Total nitrogen (a,b) and nitrate content (c,d) of Swiss chard treated with different organic amendments (B, biochar; COP, compost from olive pomace; CW, vermicompost from cattle manure; CD1, compost from 90% cattle anaerobic digestate with 10% wheat straw addition; CD2, compost from 79% cattle anaerobic digestate with 11% crop residues and 10% wheat straw addition), each added to provide 140 and 280 of kg N/ha, (grey and black bars, respectively), plus a non-treated soil or control (NT, white bar). The graphs on the left refer to the first leaf cut (a,c) while on the right to the second cut (b,d). Values are means (n = 4) ± standard errors. Data in each graph were analyzed by two-way ANOVA followed by Duncan test at p ≤ 0.05. A, amendment; D, dose; **, p ≤ 0.01; ***, p ≤ 0.001.
Figure 3. Total nitrogen (a,b) and nitrate content (c,d) of Swiss chard treated with different organic amendments (B, biochar; COP, compost from olive pomace; CW, vermicompost from cattle manure; CD1, compost from 90% cattle anaerobic digestate with 10% wheat straw addition; CD2, compost from 79% cattle anaerobic digestate with 11% crop residues and 10% wheat straw addition), each added to provide 140 and 280 of kg N/ha, (grey and black bars, respectively), plus a non-treated soil or control (NT, white bar). The graphs on the left refer to the first leaf cut (a,c) while on the right to the second cut (b,d). Values are means (n = 4) ± standard errors. Data in each graph were analyzed by two-way ANOVA followed by Duncan test at p ≤ 0.05. A, amendment; D, dose; **, p ≤ 0.01; ***, p ≤ 0.001.
Agronomy 10 00346 g003
Agronomy 10 00346 g004 550
Figure 4. Carotenoids (a), chlorophyll a (b), chlorophyll b (c), and total chlorophyll (d) contents in Swiss chard treated with different organic amendments (B, biochar; COP, compost from olive pomace; CW, vermicompost from cattle manure; CD1, compost from 90% cattle anaerobic digestate with 10% wheat straw addition; CD2, compost from 79% cattle anaerobic digestate with 11% crop residues and 10% wheat straw addition), each added to provide 140 and 280 of kg N/ha, (grey and black bars, respectively), plus a non-treated soil or control (NT, white bar). Values are means (n = 4) ± standard errors. Data in each graph were analyzed by two-way ANOVA followed by a Duncan test at p ≤ 0.05. A, amendment; D, dose; *, p ≤ 0.05; n.s., not significant.
Figure 4. Carotenoids (a), chlorophyll a (b), chlorophyll b (c), and total chlorophyll (d) contents in Swiss chard treated with different organic amendments (B, biochar; COP, compost from olive pomace; CW, vermicompost from cattle manure; CD1, compost from 90% cattle anaerobic digestate with 10% wheat straw addition; CD2, compost from 79% cattle anaerobic digestate with 11% crop residues and 10% wheat straw addition), each added to provide 140 and 280 of kg N/ha, (grey and black bars, respectively), plus a non-treated soil or control (NT, white bar). Values are means (n = 4) ± standard errors. Data in each graph were analyzed by two-way ANOVA followed by a Duncan test at p ≤ 0.05. A, amendment; D, dose; *, p ≤ 0.05; n.s., not significant.
Agronomy 10 00346 g004
Table
Table 1. Main physico-chemical properties of the soil utilized in the experiment.
Table 1. Main physico-chemical properties of the soil utilized in the experiment.
PropertyValue
Clay (%)22.40 ± 0.72
Silt (%)11.50 ± 0.81
Sand (%)66.10 ± 0.81
pH (-)7.50 ± 0.08
EC (dS m−1)0.42 ± 0.12
Olsen P2O5 (mg kg−1)28.00 ± 0.61
Organic carbon (g kg−1)7.90 ± 0.74
Organic matter (%)1.40 ± 0.74
C/N (-)7.20 ± 0.82
Total nitrogen (‰)1.10 ± 0.53
NO3− (mg kg−1)48.00 ± 0.32
Na+ (mg kg−1)25.00 ± 0.38
Ca2+ (mg kg−1)3289.00 ± 0.89
Mg2+ (mg kg−1)215.00 ± 0.91
K+ (mg kg−1)368.00 ± 0.78
Values are means (n = 3) ± standard errors.
Table
Table 2. Main chemical properties of biochar, vermicompost, and composts applied to the soil.
Table 2. Main chemical properties of biochar, vermicompost, and composts applied to the soil.
PropertyBCOPCWCD1CD2
pH11.26 ± 0.077.92 ± 0.037.64 ± 0.076.89 ± 0.028.74 ± 0.04
EC (dS m−1)3.63 ± 0.152.35 ± 0.052.65 ± 0.034.33 ± 0.051.95 ± 0.01
Fixed carbon (%)69.77 ± 0.043.93 ± 0.100.53 ± 0.042.35 ± 0.022.37 ± 0.04
Volatile solids (%)16.95 ± 0.0353.87 ± 0.0332.34 ± 0.0944.61 ± 0.1469.77 ± 0.01
Ash (%)13.28 ± 0.0342.20 ± 0.1167.13 ± 0.0953.04 ± 0.1027.85 ± 0.12
Moisture (%)5.22 ± 0.0428.75 ± 0.1035.45 ± 0.0854.55 ± 0.4033.96 ± 0.10
C (%)67.70 ± 0.3060.90 ± 1.2325.20 ± 0.1024.50 ± 0.6334.50 ± 0.34
H (%)2.36 ± 0.064.55 ± 0.221.36 ± 0.172.17 ± 0.204.44 ± 0.06
N (%)1.48 ± 0.022.61 ± 0.111.62 ± 0.012.27 ± 0.122.59 ± 0.02
Corg (%)66.74 ± 0.0456.30 ± 0.1420.05 ± 0.1823.33 ± 0.5826.56 ± 0.63
C/N45.10 ± 0.7621.57 ± 0.8412.38 ± 0.0810.31 ± 0.5610.25 ± 0.29
H/Corg ratio 0.42 ± 0.01----
B, biochar; COP, compost from olive pomace; CW, vermicompost from cattle manure; CD1, compost from 90% cattle anaerobic digestate with 10% wheat straw addition; CD2, compost from 79% cattle anaerobic digestate with 11% crop residues and 10% wheat straw addition. Values are means (n = 3) ± standard errors.
Table
Table 3. SPAD meter values relatively to the youngest fully expanded leaf (SPADleaf) and the whole plant (SPADplant), at the first and second cut of Swiss chard leaves grown on soil mixed with different organic amendments, each added in two doses to, respectively, provide 140 and 280 kg N ha−1.
Table 3. SPAD meter values relatively to the youngest fully expanded leaf (SPADleaf) and the whole plant (SPADplant), at the first and second cut of Swiss chard leaves grown on soil mixed with different organic amendments, each added in two doses to, respectively, provide 140 and 280 kg N ha−1.
AmendmentDose (Kg N ha−1)First Leaf CutSecond Leaf Cut
SPADleafSPADplantSPAD leafSPAD plant
NT-32.8 ± 2.925.9 ± 2.636.1 ± 1.932.8 ± 2.0
average32.8 B25.9 B36.0 C32.8 C
B14035.3 ± 1.927.1 ± 0.836.7 ± 1.834.1 ± 1.4
28032.9 ± 2.426.6 ± 1.535.3 ± 1.132.1 ± 0.9
average34.1 AB26.8 AB36.0 C33.0 C
COP14039.7 ± 2.328.7 ± 2.135.0 ± 0.831.5 ± 0.7
18040.0 ± 2.729.4 ± 2.139.3 ± 1.635.6 ± 1.0
average39.8 AB29.0 AB37.1 BC33.5 BC
CW14042.4 ± 1.632.9 ± 2.042.0 ± 1.136.1 ± 1.4
28039.4 ± 2.730.6 ± 0.839.8 ± 0.935.9 ± 1.1
average40.9 A31.8 A40.9 AB36.0 AB
CD114036.9 ± 0.730.7 ± 1.141.0 ± 1.236.8 ± 0.8
28041.2 ± 4.330.6 ± 1.743.0 ± 1.239.5 ± 1.2
average39.1 AB30.6 AB42.0 A38.2 A
CD214036.7 ± 0.726.6 ± 0.639.9 ± 1.635.4 ± 0.8
28042.3 ± 2.729.5 ± 2.539.6 ± 1.936.1 ± 0.6
average39.5 AB28.0 AB39.8 AB35.8 AB
NT, non-treated soil or control; B, biochar; COP, compost from olive pomace; CW, vermicompost from cattle manure; CD1, compost from 90% cattle anaerobic digestate with 10% wheat straw addition; CD2, compost from 79% cattle anaerobic digestate with 11% crop residues and 10% wheat straw addition. Values are means (n = 4) ± standard errors. In each column, the average values of the two amendment doses followed by the same letters are not significantly different at p ≤ 0.05, according to the Duncan test.

Share and Cite

MDPI and ACS Style

Libutti, A.; Trotta, V.; Rivelli, A.R. Biochar, Vermicompost, and Compost as Soil Organic Amendments: Influence on Growth Parameters, Nitrate and Chlorophyll Content of Swiss Chard (Beta vulgaris L. var. cycla). Agronomy 2020, 10, 346. https://doi.org/10.3390/agronomy10030346

AMA Style

Libutti A, Trotta V, Rivelli AR. Biochar, Vermicompost, and Compost as Soil Organic Amendments: Influence on Growth Parameters, Nitrate and Chlorophyll Content of Swiss Chard (Beta vulgaris L. var. cycla). Agronomy. 2020; 10(3):346. https://doi.org/10.3390/agronomy10030346

Chicago/Turabian Style

Libutti, Angela, Vincenzo Trotta, and Anna Rita Rivelli. 2020. "Biochar, Vermicompost, and Compost as Soil Organic Amendments: Influence on Growth Parameters, Nitrate and Chlorophyll Content of Swiss Chard (Beta vulgaris L. var. cycla)" Agronomy 10, no. 3: 346. https://doi.org/10.3390/agronomy10030346

APA Style

Libutti, A., Trotta, V., & Rivelli, A. R. (2020). Biochar, Vermicompost, and Compost as Soil Organic Amendments: Influence on Growth Parameters, Nitrate and Chlorophyll Content of Swiss Chard (Beta vulgaris L. var. cycla). Agronomy, 10(3), 346. https://doi.org/10.3390/agronomy10030346

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop