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Article

Biochar Improves Root Growth of Sapium sebiferum (L.) Roxb. Container Seedlings

by
Hong Chen
,
Chen Chen
and
Fangyuan Yu
*
Collaborative Innovation Centre of Sustainable Forestry in Southern China, College of Forest Science, Nanjing Forestry University (NJFU), 159 Longpan Road, Nanjing 210037, China
*
Author to whom correspondence should be addressed.
Agronomy 2021, 11(6), 1242; https://doi.org/10.3390/agronomy11061242
Submission received: 31 May 2021 / Revised: 15 June 2021 / Accepted: 16 June 2021 / Published: 19 June 2021
(This article belongs to the Special Issue The Effects of Biochar on Organisms)
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Abstract

:
Background: The faulty development of the root system is a major threat that affects the survival rate of container seedlings of Sapium sebiferum in the transplanting and reforestation processes. The current study was conducted to determine the impact of biochar on the root growth and development of S. sebiferum container seedlings. Methods: Varied concentrations (1%, 3%, and 5%) of straw and bamboo biochar were applied in six groups, whereas the control group (CK) was only treated with matrix. Results: The treatment with 3% straw biochar (C2) proved to be the most effective soil conditioner for cultivating S. sebiferum seedlings. Moreover, C2 increased seedling height (58.92%); ground diameter (33.86%, biomass of the over-ground part (12.73 g), the underground part (7.48 g), and the fibrous part (0.076 g) compared to the CK (control). Conclusions: Biochar not only improved the root morphology by developing primary lateral roots, but it also accelerated the assimilation of N from the matrix to indirectly facilitate stem growth through enhancing NR activity. The change in root growth strategy contributed to the growth in S. sebiferum seedlings, thereby improving the survival rate during transplanting and reforestation.

1. Introduction

Sapium sebiferum (L.) Roxb. is commonly known as the Chinese tallow tree, belonging to the family Euphorbiaceae. It is a deciduous tree, native to semitropical regions of Southern and Central China. It was also introduced to Japan [1,2] (p. 93). S. sebiferum is an essentially economical tree due to the high oil content (up to 55%) in its seeds. It follows the algae and oil palm and is ranked the third highest biodiesel-producing crop in the world. It has been regarded as one of China’s four major woody oil plants (tallow, tea, tung oil, and walnuts) [3,4,5] (pp. 1–12). The waxy coating of its seeds can be the raw material for soap. Moreover, S. sebiferum is a colorful foliage tree species with high ornamental value. Thus, it can be planted in gardens and on roadsides. Furthermore, it has medical uses for preventing snail fever [6]. In general, S. sebiferum is a multi-functional plant. The mass planting of S. sebiferum is the result of its practical value. Hence, the container seedlings of this important species have become prevalent for transplanting and reforestation on a large scale. However, the survival rate of seedlings is negatively affected by insufficiently developed root systems [7]. To resolve this problem, our experiment aims to enhance its root growth with biochar based on previous studies finding that biochar can amend root growth [8,9].
Currently, there is a rising interest in a charcoal product termed biochar as a potential soil conditioner to improve soil quality and carbon sequestration to mitigate climate change [10,11]. Biochar is generated by the pyrolysis of biomass at temperatures between 300 and 1000 °C in oxygen-limited conditions [12,13], which is initially derived from chernozem in the Amazon River [14]. Biochar does not solely assist in retaining carbon, but also has impacts on soil physical property and soil biota. Independently, mixed biochar can reduce soil bulk density and improve whole soil porosity due to the porous structure of biochar [15]. The studies conducted by Burrell et al. [16] indicated that biochar can amend soil physical structures by improving soil aggregate stability and plant available water, especially in coarse-textured soil. In addition, biochar can act as a slow-release fertilizer, enhancing soil fertility of acidic soils in the long-term [16]. With respect to soil nitrogen, biochar can increase biological nitrogen fixation, accelerate organic nitrogen mineralization, and prevent NH3 loss from soils [17,18]. Biochar has direct impacts on the soil nitrogen cycle [19,20] through two mechanisms: improving the pH of soils and strengthening chemical signaling between the host and symbiont [17,21,22]. Moreover, previous studies concluded that biochar can affect soil microbial communities and enzymes activities [23,24,25].
Referring to previous studies, it was hypothesized that biochar can improve the root growth of S. sebiferum container seedlings by improving soil physical property, providing more nutrients, and activating microbes or enzymes [26]. Li et al. [27] reported that a 1.5% biochar addition can change root morphology and improve N absorption capacity of Phragmites australis. Compared to the study by Li et al. [27], we selected two types of biochar at three separate concentration levels. Our experiment not only aimed to prove the hypothesis above, but also to assess the superior type of biochar and proper concentration for enhancing root growth of S. sebiferum. In general, we explored the proper and scientific cultivation of S. sebiferum container seedlings, especially in its root system. Hence, the root system can become stronger and more resistant to stress, thereby improving the survival rate of transplanting and reforestation.

2. Materials and Methods

2.1. Experimental Materials

The container seedlings of S. sebiferum for the test were obtained from Shanghai Forest Vegetation Germplasm Resource Base (121°20′ E, 31°23′ N). In early April 2018, the seeds of S. sebiferum collected in Xinyi, Jiangsu, in mid-November 2017 were processed with 1% NaOH [28] and sowed in plug trays after cleaning. On 21 June 2018, the seedlings of appropriate 10 cm height were transplanted to a biochar matrix with different contents in a non-woven container.

2.2. Pot Experiment

Two types of biochar (straw and bamboo) were set up at three levels (1%, 3%, and 5%) for each type, including six treatment groups (C1, C2, C3, C4, C5, and C6). The control group (CK) contained the test substrate without biochar, while the experimental groups were mixed with various contents of biochar, which were the proportion of matrix mass (Table 1). Three replicates were evenly set for each treatment with 30 seedlings. Seedlings were cultivated in the same container and substrate.

2.3. Plant Samplings and Analysis

2.3.1. Seedling Height and Ground Diameter

Before harvest, 15 seedlings of S. sebiferum were randomly selected for each repetition to determine the seedling height and ground diameter with a tape measure (0.1 cm accuracy) and a Vernier caliper (0.01 mm accuracy), respectively. Furthermore, the height-diameter ratio was calculated.

2.3.2. Root System Indexes

Prior to the end of the trial, 5 S. sebiferum seedlings were randomly selected for each treatment and repetition (15 plants per treatment). After cleaning the root system with water, a transmission image was obtained under an EPSON scanner (Seiko Epson Corp., Gen, Japan), and the root image was analyzed with WinRHIZO PRO 2007 (Gen, Japan) [29]. Root system indexes include total root length, root surface area, root volume, average root diameter, and lateral root length, with a variety of diameters [30]. The number of primary lateral roots with a diameter greater than 1 mm (the roots on the main root were not included) was determined by direct observation.

2.3.3. Biomass

The 15 seedlings of S. sebiferum were divided into the aboveground part and underground parts (main lateral roots and fibrous roots) with root scanning. These seedlings were placed into an oven with envelopes. The oven temperature was initially at 105 °C for 30 min to kill them and was subsequently adjusted to 70 °C to dry them to a constant weight. Eventually, an electronic balance with an accuracy of 0.001 g was utilized to measure the dry weight of each part separately.

2.3.4. Non-Structure Carbohydrate

The 0.2 g of fresh root samplings was separately collected to determine soluble sugar content and starch content via colorimetric analysis [31].

2.3.5. Nitrate Reductase

Nitrate reductase (NR) is a key enzyme in plant nitrogen metabolism, which is correlated with plant absorption and the use of nitrogen fertilizer [32]. The experiment determined NR in vitro [33].

2.3.6. Nitrogen and Carbon Content

Samples for determination of nitrogen and carbon content were collected every 30 days. Samplings were taken a total of five times, starting at the beginning of the test in June 2018 and ending in late November.
Nitrogen and carbon content of stem and root samples were determined when dried via the method by Sorrenti et al. [34] and external heating of potassium dichromate methods (referring to GB7857-1987), respectively.

2.4. Statistical Analysis

Excel 2016 (Microsoft, Redmond, WA, USA) and Origin 2018 (OriginLab, Northampton, MA, USA) were adopted for processing data and figures. SPSS 23.0 (IBM, Armonk, NY, USA) was used for analysis of variance (ANOVA) and Duncan’s multiple range test. p values less than 0.05 were considered to indicate significance between groups.

3. Results

3.1. Seedling Height, Ground Diameter, and Height–Diameter Ratio

The discrepancies in seedling height, ground diameter, and the height–diameter ratio between treatment groups and CK were significant (p < 0.05), indicating that biochar had a positive impact on the seedling morphological indicators of S. sebiferum above. Compared to other treatments, C2 significantly enhanced growth of both seedling height and ground diameter. This result illustrated that S. sebiferum treated with 3% straw biochar performed the best in terms of seedling growth. Moreover, the height–diameter ratios of all treatments were elevated compared to CK, on account of biochar having a stronger promotion effect on seedling height growth compared to ground diameter growth (Table 2).

3.2. Biomass

Table 3 displays the biomass of the aboveground part, the underground part, and fibrous roots treated with two biochar types at three content levels. Obvious differences occurred between treatment groups and CK (p < 0.05). The C2 treatments were affected more positively on the aboveground biomass and underground biomass, showing that treatments containing 3% straw biochar produced the strongest acceleration of growth of the aboveground and underground biomass. Despite biochar facilitating both the biomass of aboveground and underground parts, the facilitation of the former was superior to that of the latter. Thereby, the root–stem ratios of all treatment groups were inferior to the control group. Nonetheless, slight discrepancies in the root–stem ratio appeared among all treatments.

3.3. Root System

The root morphological indexes of S. sebiferum container seedlings under a variety of biochar treatments, as displayed in Table 4, include primary lateral root number, total root length, root surface area, and root volume. The results indicated that all biochar contents in the trial can promote these root morphological indicators, and that significant discrepancies between treatments and CK occurred (p < 0.05). The results presented that straw charcoal better-facilitated the generation of fibrous roots than bamboo charcoal, especially for 3% straw charcoal due to the increase in porosity of the matrix in retaining moisture [34]. In addition, the matrix mixing 5% straw biochar with 3% straw biochar contributed to the largest root volume.

3.4. The Concentration of Non-Structure Carbohydrate and Nitrate Reductase Activity

The concentration of non-structure carbohydrate and nitrate reductase activity in the roots of S. sebiferum container seedlings treated with biochar are shown in Table 5. The discrepancies of soluble sugar and starch concentration among the treatments and control were significant (p < 0.05). The results indicated that biochar can significantly reduce the content of soluble sugar and starch in the root system. The pattern of response of plants for soluble sugar concentration was CK > C1, C5, C4, C3, C6 > C2, while the starch concentration followed the order CK > C1, C6, C5, C3, C2 > C4. Compared to the other concentrations, 3% straw biochar proved to be the non-structure carbohydrate most consumed by seedlings in producing energy for photosynthesis, ultimately enhancing plant growth and development.
It is evident from Table 5 that the NR activity of the roots of S. sebiferum increased with the age of the plant and further increased with the application of straw charcoal. Maximum NR activity was noted in the plants treated with 3% (C2) straw charcoal. The pattern of response of plants with straw charcoal was C2 > C3, C5, CK, C6 > C1, C4. Moreover, C2 had a striking discrepancy with other treatments (p < 0.05). Out of the two charcoals used, the response toward straw charcoal was more pronounced compared to bamboo charcoal.

3.5. Nitrogen Concentration, Carbon Concentration, and N/C Ratio in Roots

The nitrogen concentration in the roots of S. sebiferum container seedlings treated with various biochars in different periods (from July to November) is indicated in Figure 1. In general, biochar significantly increased N concentration in the early stage (July), and the matrix mixed with straw charcoal led to more N accumulation than bamboo charcoal. It was reported earlier that loose and porous straw charcoal increased the interstices of the matrix, benefiting the maintenance of moisture and the growth in the root system [35]. Subsequently, N concentration decreased rapidly in August, followed by the gentle uptrend or downtrend in the latter stages. Nevertheless, N concentration in CK kept the gentle uptrend without reduction. The peak value of N in CK did not exceed the N concentration of treatments in July due to the slow growth of CK, which did not reach the declining stage.
The entire carbon concentration of all treatments was retained at a similar level. In November, the carbon concentration of C3 and C4 had noticeable discrepancies compared to other experimental groups and CK. No significant difference occurred in the first four months (Figure 2), illustrating that biochar had slight impacts on the carbon concentration in the roots of S. sebiferum. The trends in the carbon–nitrogen ratio in roots agree with the trends in the N concentration in roots (Figure 3).

4. Discussion

The experiment aimed at testing the impacts of two biochar types on the morphological and physiological indicators of the root system of S. sebiferum container seedlings. The results indicated that biochar can improve seedling height, ground diameter, biomass, primary lateral roots, total root length, root surface area, and root volume of the model plant. These findings are consistent with a meta-analysis of the biochar effects on root traits [9,36,37]. Among the different treatments of biochar, C2 (3%) proved to be the best for the development of seedlings.
Biochar can improve the physical characteristics of the soil matrix, including porosity and aeration. In general, the porosity of biochar can decrease the total bulk density of soil, thereby enlarging the growing habitat for the underground parts of seedlings. Compared to bamboo charcoal, straw charcoal is a finer biochar in nature [38], offering more space for the development of the primary lateral roots (Table 4). In addition, biochar contains a larger proportion of aromatic C, especially for fused aromatic C structures [14]. According to the above characteristics, biochar has excellent water absorption and permeability properties, owing to its low bulk density and large surface area [39]. Straw biochar can preserve more water and nutrients over bamboo biochar [40]. Thus, the roots are inclined to horizontally obtain nutrients and moisture in shallow soils via adding lateral roots [41].
Biochar application increases the availability of nutrients with potassium, phosphorus, and zinc [42]. The leaning alkalinity of biochar can adjust the soil pH to a particularly ameliorate acidic soil [25]. Furthermore, H+ and Al3+ are present in soils and react with the cations (Ca2+, Mg2+, and K+, etc.) in biochar, reducing the soil base saturation. Chen et al. [43] reported that biochar can promote direct interspecies electron transfer (DIET). The application of biochar can increase total soil charge and cation exchange capacity (CEC) via its rich functional groups, thereby enhancing soil fertility [44,45]. As a mechanism of nutrient delivery to plants, biochar enhances soil fertility and soil quality by increasing the retention of soil moisture and nutrients, improving soil pH slightly, and stimulating the microbial activities of useful fungi [46,47]. Thus, biochar addition can accelerate the biomass accumulation and growth of seedling height and ground diameter (Table 2 and Table 3).
More importantly, plant growth and NR activity are positively related [48]. Biochar accelerates the assimilation of N from the matrix to indirectly facilitate stem growth through enhancing NR activity. According to Table 5, 3% straw biochar can markedly increase the NR activity of roots, thereby stimulating root system growth (Table 4 and Table 5). Regarding the N content in roots, biochar amends soils with a slower release of nitrate to generate agronomic advantages [49]. It also enhances the mineralization of organic N, the capability of which strengthens by adding more biochar [50,51]. Nielsen et al. [52] discovered that biochar application increased the soil pH by 0.2–0.3 units, which accelerates the nitrification reduction reaction and reduces the NO3− concentration in soils. Therefore, biochar provides more inorganic N for roots. Contrary to this, Laird et al. [51] reported that biochar enhances N leaching from the soil to restrict N assimilation of plants. Nevertheless, our experiment was implemented with container seedlings without the N leaching issue. Whereas biochar has fewer effects on carbon absorption by plants (Figure 2), several reports claim that biochar contributes to a larger carbon accumulation in soils [11]. Combined with the finding that biochar can promote root system growth and N absorption, the nutrients were absorbed into the stems during seedling growth, especially in the aboveground parts. An important finding in the present study is that the application of biochar enhanced seedling growth along with seedling height, ground diameter, and aboveground and underground biomass.
Additionally, both straw biochar and bamboo biochar can reduce soil contamination of heavy metals [38], benefiting the healthy development of plants. Compared to bamboo, straw biochar is finer, which can remove more soil contamination [38]. It may therefore be concluded from the above discussion and from the reports of Harel et al. [53] that a 3% concentration of straw biochar relieves plants from external stress and is most beneficial to the cultivation of S. sebiferum container seedlings.

5. Conclusions

This study revealed that biochar is beneficial to the root growth of S. sebiferum seedlings and that C2 (3% straw biochar) is the most suitable soil conditioner for cultivating S. sebiferum seedlings. Biochar not only improved the root morphology by developing primary lateral roots, but also accelerated the assimilation of N from the matrix to indirectly facilitate stem growth by enhancing NR activity. The change in root growth strategy contributed to the growth in S. sebiferum seedlings, thereby improving the survival rate during transplanting and reforestation. Moreover, it was reported that biochar application increases soil pH due to the diffusion of minerals (K, Ca, and Mg) from the biochar surface to soil. In addition, biochar has a rapid localized impact on soil pH with the distance from biochar [54,55]. Thus, the impact of biochar on plants is related to the original soil condition and the adaptability of plants to soil pH. Combined with the growth habitat of certain plants, the methods of biochar application (e.g., location, concentration, etc.) should be studied in the future. Furthermore, different contents of biochar mixed with other fertilizers to form a composite matrix will be studied to explore its influence on the growth quality and survival rate of plants. Eventually, the optimal ratio of biochar and other fertilizers will be obtained to apply to production, providing impetus for the better promotion and application of biochar.

Author Contributions

Conceptualization, F.Y. and H.C.; methodology, F.Y. and H.C.; software, C.C. and H.C.; validation, F.Y.; investigation, C.C.; resources, F.Y.; writing—original draft preparation, H.C.; writing—review and editing, F.Y.; project administration, F.Y.; funding acquisition, F.Y. All authors have read and agreed to the published version of the manuscript.

Funding

The research was funded by National Natural Science Foundation of China, grant number 3197140894.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Not applicable.

Acknowledgments

The work was sponsored by National Natural Science Foundation of China (3197140894), Joint Research Project based on Cooperative Program for Bachelor of Science in Forestry by Nanjing Forestry University and University of British Columbia, and A Project Funded by the Priority Academic Program Development of Jiangsu Higher Education Institutions (PAPD).

Conflicts of Interest

The authors declare no conflict of interest.

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Agronomy 11 01242 g001 550
Figure 1. The nitrogen concentration in the roots of S. sebiferum container seedlings with different biochar treatments. Lowercase letters represent significance at 0.05 level and the same letter indicates no significant difference in full text.
Figure 1. The nitrogen concentration in the roots of S. sebiferum container seedlings with different biochar treatments. Lowercase letters represent significance at 0.05 level and the same letter indicates no significant difference in full text.
Agronomy 11 01242 g001
Agronomy 11 01242 g002 550
Figure 2. The carbon concentration in the roots of S. sebiferum container seedlings with different biochar treatments. Lowercase letters represent significance at 0.05 level and the same letter indicates no significant difference in full text.
Figure 2. The carbon concentration in the roots of S. sebiferum container seedlings with different biochar treatments. Lowercase letters represent significance at 0.05 level and the same letter indicates no significant difference in full text.
Agronomy 11 01242 g002
Agronomy 11 01242 g003 550
Figure 3. The carbon-nitrogen ratio in the roots of S. sebiferum container seedlings with different biochar treatments. Lowercase letters represent significance at 0.05 level and the same letter indicates no significant difference in full text.
Figure 3. The carbon-nitrogen ratio in the roots of S. sebiferum container seedlings with different biochar treatments. Lowercase letters represent significance at 0.05 level and the same letter indicates no significant difference in full text.
Agronomy 11 01242 g003
Table
Table 1. The design of biochar treatments.
Table 1. The design of biochar treatments.
TreatmentsStraw Biochar ContentBamboo Biochar Content
CK00
C11%0
C23%0
C35%0
C401%
C503%
C605%
Table
Table 2. The seedling height, ground diameter, and height–diameter ratio of S. sebiferum container seedlings in different biochar treatments.
Table 2. The seedling height, ground diameter, and height–diameter ratio of S. sebiferum container seedlings in different biochar treatments.
TreatmentSeedling Height (cm)Ground Diameter (mm)Height-Diameter Ratio
CK63.60 ± 4.68 c7.56 ± 0.39 c83.1 ± 3.20 c
C1100.67 ± 3.76 a9.99 ± 0. 37 ab101.7 ± 3.83 ab
C2101.07 ± 3.92 a10.12 ± 0.34 a100.2 ± 3.13 b
C389.47 ± 2.71 b8.97 ± 0.26 b100.1 ± 2.39 b
C4101.27 ± 1.85 a9.22 ± 0.23 bc110.5 ± 2.73 a
C591.40 ± 2.11 ab8.75 ± 0.26 b105.2 ± 2.86 ab
C696.13 ± 2.28 ab8.84 ± 0.24 b109.2 ± 2.18 ab
Lowercase letters represent significance at the 0.05 level and the same letter indicates no significant difference in full text.
Table
Table 3. The biomass of various parts of S. sebiferum container seedlings in different biochar treatments.
Table 3. The biomass of various parts of S. sebiferum container seedlings in different biochar treatments.
TreatmentOver-Ground Part (g)Underground Part (g)Fibrous Roots (g)Root-Stem Ratio
CK3.77 ± 0.78 d3.59 ± 0.65 c0.036 ± 0.009 c1.05 ± 0.09 a
C115.08 ± 1.83 ab9.88 ± 1.16 a0.189 ± 0.032 ab0.66 ± 0.03 b
C216.50 ± 2.94 a11.07 ± 1.69 a0.112 ± 0.022 b0.70 ± 0.05 b
C39.29 ± 0.80 c6.22 ± 0.74 bc0.182 ± 0.040 ab0.66 ± 0.04 b
C410.67 ± 0.97 bc6.46 ± 0.77 bc0.193 ± 0.063 ab0.60 ± 0.05 b
C59.35 ± 0.75 c6.37 ± 0.51 bc0.122 ± 0.103 a0.70 ± 0.06 b
C611.19 ± 1.31 bc8.20 ± 0.77 ab0.131 ± 0.015 b0.76 ± 0.07 b
Lowercase letters represent significance at 0.05 level and the same letter indicates no significant difference in full text.
Table
Table 4. The root morphological indexes of S. sebiferum container seedlings in different biochar treatments.
Table 4. The root morphological indexes of S. sebiferum container seedlings in different biochar treatments.
TreatmentPrimary Lateral Root NumberTotal Root Length (cm)Root Surface Area (cm2)Root Volume (cm3)
CK2.00 ± 0.41 c145.7 ± 20.10 d122.3 ± 23.07 b2.33 ± 0.95 b
C15.33 ± 0.55 a365.3 ± 33.55 bc194.2 ± 12.20 b7.84 ± 0.53 c
C25.56 ± 0.78 a463.6 ± 40.63 ab227.8 ± 15.94 ab11.39 ± 1.01 bc
C35.22 ± 0.68 a455.5 ± 21.74 ab241.1 ± 16.12 ab11.55 ± 1.24 abc
C43.00 ± 0.33 bc345.1 ± 40.54 c284.7 ± 26.06 a10.43 ± 2.57 a
C54.33 ± 0.94 ab391.9 ± 24.83 bc243.3 ± 14.30 ab10.14 ± 2.03 abc
C64.67 ± 0.58 ab420.9 ± 50.66 a239.0 ± 16.26 ab10.77 ± 6.16 ab
Lowercase letters represent significance at 0.05 level and the same letter indicates no significant difference in full text.
Table
Table 5. The concentration of non-structure carbohydrate and nitrate reductase activity in the roots of S. sebiferum container seedlings with different biochar treatments.
Table 5. The concentration of non-structure carbohydrate and nitrate reductase activity in the roots of S. sebiferum container seedlings with different biochar treatments.
TreatmentSoluble Sugar
(mg/g FW)		Starch
(mg/g FW)		NR Activity (µg·g−1·h−1)
CK31.06 ± 1.39 a92.10 ± 12.27 a9.37 ± 0.68 b
C126.26 ± 3.47 ab67.22 ± 25.45 ab4.25 ± 0.65 c
C221.15 ± 1.67 b52.32 ± 7.61 ab32.50 ± 1.12 a
C323.56 ± 0.96 ab56.83 ± 6.59 ab11.61 ± 2.24 b
C423.68 ± 5.22 ab41.80 ± 8.72 b3.77 ± 0.15 c
C524.41 ± 1.67 ab59.82 ± 5.54 ab9.92 ± 1.86 b
C622.61 ± 1.68 ab63.50 ± 7.43 ab9.12 ± 0.54 b
Lowercase letters represent significance at 0.05 level and the same letter indicates no significant difference in full text.
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Chen, H.; Chen, C.; Yu, F. Biochar Improves Root Growth of Sapium sebiferum (L.) Roxb. Container Seedlings. Agronomy 2021, 11, 1242. https://doi.org/10.3390/agronomy11061242

AMA Style

Chen H, Chen C, Yu F. Biochar Improves Root Growth of Sapium sebiferum (L.) Roxb. Container Seedlings. Agronomy. 2021; 11(6):1242. https://doi.org/10.3390/agronomy11061242

Chicago/Turabian Style

Chen, Hong, Chen Chen, and Fangyuan Yu. 2021. "Biochar Improves Root Growth of Sapium sebiferum (L.) Roxb. Container Seedlings" Agronomy 11, no. 6: 1242. https://doi.org/10.3390/agronomy11061242

APA Style

Chen, H., Chen, C., & Yu, F. (2021). Biochar Improves Root Growth of Sapium sebiferum (L.) Roxb. Container Seedlings. Agronomy, 11(6), 1242. https://doi.org/10.3390/agronomy11061242

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