Next Article in Journal
Effects of Fertilization and Planting Modes on Soil Organic Carbon and Microbial Community Formation of Tree Seedlings
Next Article in Special Issue
Overexpression of Auxin/Indole-3-Acetic Acid Gene TrIAA27 Enhances Biomass, Drought, and Salt Tolerance in Arabidopsis thaliana
Previous Article in Journal
Sesame, an Underutilized Oil Seed Crop: Breeding Achievements and Future Challenges
Previous Article in Special Issue
Hydrogen Peroxide Is Involved in Methane-Alleviated Cadmium Toxicity in Alfalfa (Medicago sativa L.) Seedlings by Enhancing Cadmium Chelation onto Root Cell Walls
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Abiotic Stress Effect on Agastache mexicana subsp. mexicana Yield: Cultivated in Two Contrasting Environments with Organic Nutrition and Artificial Shading

by
Judith Morales-Barrera
1,
Juan Reséndiz-Muñoz
1,*,
Blas Cruz-Lagunas
2,
José Luis Fernández-Muñoz
3,*,
Flaviano Godínez-Jaimes
4,
Tania de Jesús Adame-Zambrano
5,
Mirna Vázquez-Villamar
3,
Teollincacihuatl Romero-Rosales
1,
María Teresa Zagaceta-Álvarez
6,
Karen Alicia Aguilar-Cruz
7,
Jorge Estrada-Martínez
8 and
Miguel Angel Gruintal-Santos
1,*
1
Unidad Tuxpan, Facultad de Ciencias Agropecuarias y Ambientales, Universidad Autónoma de Guerrero, km 2.5 Carretera Iguala-Tuxpan, Iguala de la Independencia 40101, Mexico
2
Facultad de Ciencias Agropecuarias y Ambientales, Universidad Autónoma de Guerrero, Periférico Poniente s/n, Iguala de la Independencia 40010, Mexico
3
Centro de Investigación en Ciencia Aplicada y Tecnología Avanzada Unidad Legaria, Instituto Politécnico Nacional, Ciudad de Mexico 11500, Mexico
4
Facultad de Matemáticas, Universidad Autónoma de Guerrero, Av. Lázaro Cárdenas s/n, Chilpancingo 39087, Mexico
5
Centro Regional de Educación Superior Campus Zona Norte, Universidad Autónoma de Guerrero, Carretera Taxco-Iguala km 42 s/n, Taxco el Viejo 40323, Mexico
6
Escuela Superior de Ingeniería Mecánica y Eléctrica Unidad Azcapotzalco, Instituto Politécnico Nacional, Av. Las Granjas 682, Col., Alcaldía Azcapotzalco 02550, Mexico
7
Escuela Superior de Ingeniería Mecánica y Eléctrica Unidad Zacatenco, Instituto Politécnico Nacional, Unidad Adolfo López Mateos Av. Luis Enrique Erro s/n, Zacatenco, Gustavo A. Madero 07738, Mexico
8
Centro de Investigación en Petroquímica Secundaria, Instituto Tecnológico de Ciudad Madero, Tecnológico Nacional de Mexico, Prol. Bahía de Aldhair y Av. de las Bahías, Parque de la Pequeña y Mediana Industria, Tecno, Altamira 89440, Mexico
*
Authors to whom correspondence should be addressed.
Plants 2024, 13(18), 2661; https://doi.org/10.3390/plants13182661
Submission received: 6 August 2024 / Revised: 11 September 2024 / Accepted: 17 September 2024 / Published: 23 September 2024
(This article belongs to the Special Issue Abiotic Stress Responses in Plants)

Abstract

:
Research on medicinal plants is essential for their conservation, propagation, resistance to environmental stress, and domestication. The use of organic nutrition has been demonstrated to improve soil fertility and plant quality. It is also important to study the effects of the Basic Cation Saturation Ratio (BCSR) approach, which is a topic where there is currently controversy and limited scientific information. Evaluating the growth and yields of Agastache mexicana subsp. mexicana (Amm) in different environments is crucial for developing effective propagation and domestication strategies. This includes examining warm and subhumid environments with rain in summer in comparison to mild environments with summer rain. Significant differences were observed in the effects of cold, waterlogging, and heat stresses on the plant’s biomass yield and the morphometric-quantitative modeling by means of isolines. The biomass yield was 56% higher in environment one compared to environment two, 19% higher in environment one with organic nutrition, and 48% higher in environment two with organic nutrition compared to using only BCSR nutrition. In the second harvesting cycle, the plants in environment one did not survive, while the plants in environment two managed to survive without needing additional nutrition. Statistical and mathematical analyses provided information about the population or sample. Additionally, further analysis using isolines as a new approach revealed new insights into understanding phenology and growth issues.

1. Introduction

The cultivation of medicinal and aromatic plants, such as “purple toronjil” or “Amm”, holds great promise for innovation in the pharmaceutical, food, and cosmetic industries. Thus, the importance of cultivation practices takes high relevance. To enhance the strength and viability of seeds, it is crucial to employ pre-germination treatments, including soaking them in water and subjecting them to biochemical processes such as GA3 or tetrazolium [1,2,3]. Additionally, it is essential to keep the soil well-humidified and improve its physical characteristics to ensure optimal vegetative development and thereby enhance the yield, especially considering that Amm is an undomesticated medicinal plant. Furthermore, the amount of soil organic matter is a key indicator of soil fertility and, therefore, organic farming systems prioritize the use of organic matter to maintain soil health and fertility, aiming to minimize the health risks associated with food production and ensure that the soil’s biological and chemical properties remain intact [4,5]. Crop yield refers to the weight of fresh and dry biomass and the weight and number of harvested seeds. It is influenced by genotype, agronomic management, and environmental conditions. The capability for yield varies among different plant types, depending on their ability to adapt to diverse conditions, including abiotic stresses. In such conditions, it is important to evaluate soil quality and its impact on crop yield by considering the following indicators: (a) the optimal balance of Na, P, Cu, minerals, and organic matter; (b) exploring and combining the relationships and functions among different biological, chemical, and physical parameters; and (c) the correlation among soil chemical composition, Cationic Exchange Capacity (CEC), and physical structure [4,6].
When aromatic plants are exposed to primary abiotic stresses such as low water availability and high salinity, extreme temperatures such as cold or heat stress (low and high temperatures, respectively), hypoxia/anoxia, and nutrient deficiency are the major causes of agricultural production losses. An incorrect combination of these factors and the amount of light, solar radiation, and relative humidity (RH) can affect plant growth and crop yield [7]. High temperatures can harm plants by denaturing proteins and deactivating chloroplast enzymes, increasing water loss through transpiration or evaporation. As a result, the time needed for photosynthesis to produce fruit or seed may be reduced. Also, “the cold stress below 20 °C has a harmful impact on plant growth, development limiting the productivity” and the quality of harvested plants. The affectations can be water intake, metabolic responses, membrane disintegration, and physiological phenomena related to growth and development, besides abnormal anaerobic respiration, leading to the synthesis of abnormal metabolites [8,9].
Without cationic exchange, plants would be unable to obtain sufficient quantities of the essential nutrients to grow, and the nutrients would be leached downward in the soil and lost. Soils with high CEC not only hold more nutrients, fertility and long-term productivity, but they are better able to buffer or avoid rapid changes in soil solution levels of nutrients by replacing them as the solution becomes depleted. The CEC of a particular soil is expressed in units of milliequivalents per 100 g (meq/100 g) of soil. The increase in CEC improved soil structural cohesion and water flow properties [10,11,12]. In a practical approach, the CEC is related to acidity indicators to control Al3+ ions saturation in soil. The more CEC (ions different from H+ and Al3+), the less acidity [13]. Soil balancing is a term that involves applying the Basic Cation Saturation Ratio (BCSR), which assumes that there is an ideal ratio of exchangeable bases, which are mainly cations such as Ca2+, Mg2+, and K+. Under these conditions, the assumptions may be reasonably reliable. If these parameters are absent, then a deficiency in one or more of these nutrients is presumed to exist [14,15]. Base saturation refers to the percent of exchangeable cations on the CEC (meq/100 g soil) and is calculated using the following formula:
B a s e   s a t u r a t i o n   % = t o t a l   b a s e s C E C 100
This method needs to take into account several parameters to optimize plant nutrient utilization and crop yield:
(a)
Percentage of cations;
(b)
Ratios of Ca/Mg, Ca/K, and Mg/K;
(c)
A relatively high CEC;
(d)
Naturally high soil pH (above 6).
Several studies propose different percentages of an ideal balance of the cations, but this issue can be solved like this: 65–85% of Ca2+, 6–20% of Mg2+, and 2–5% of K+. Additionally, the ideal Ca/Mg, Ca/K, and Mg/K ratios are 6.5/1, 13/1, and 2/1, respectively. The concept of an optimal BCSR is debatable because plant yield and the percentage of the CEC occupied by cations were not always highly correlated in experiments. It should be noted, however, that K, Mg, and Ca concentrations in plants, particularly vegetative parts, were always significantly correlated with BCSR values [14,15,16,17].
It has been suggested that incorporating the Balanced Cation Saturation Ratio (BCSR) approach into an overall soil management plan, which includes fertilization, cultural practices, and ensuring nutrient adequacy, is important. To enhance BCSR effectiveness, especially when the Cation Exchange Capacity (CEC) is low, it is essential to emphasize the significance of adding calcium (Ca) to the soil, improving its absorption, considering the entire trace mineral profile, and taking into account the interrelated biological and physical characteristics of the soil [16,18,19,20]. The use of Organic Nutrition (ON) or organic fertilization can greatly improve the physical, chemical, and biological conditions of the soil, such as water-holding capacity to support crop growth and development. A study was conducted on chamomile (Matricaria chamomilla L.) to determine the impact of chemical and organic fertilization (compost on soil + liquid compost or leachate). It was found that organic fertilization was more effective than chemical fertilization, as it increased the content of essential oils, the diameter of flower heads, and the dry weight [21]. When the ON content has humic and fulvic acids, consider the following: humic substances are absorbed through plant tissue, raising the amino acid content, nutrients, and vitamins. The indirect effect includes the improvement of the soil’s chemical, physical, and biological properties through water and nutrient retention, ventilation, permeability, greater CEC, root development; also, the direct effects include stimulates biomass accumulation, facilitates mineral nutrient absorption, and increases the resistance of plants to environmental stress [22,23,24,25,26,27].
In our efforts to efficiently propagate and domesticate Amm’s plants, we undertook: We conducted an experiment on germinating seeds to determine if they were dormant, in order to ensure their growth, studying the impact of abiotic stress in two contrasting environments and examined the interaction effect of the chemical BCSR approach-ON on biomass and fruit yield, considering both quality and quantity. Additionally, throughout the plant’s growth process, we utilized MATLAB software (v9.13, R2022a, The MathWorks Inc., USA) to create three-dimensional maps of the relationships between input and output factors. This approach represents an innovative method in horticulture and complements traditional statistical and mathematical analyses.

2. Materials and Methods

2.1. Experiment Location and Soil Characteristics

The experimental research was conducted in two different environments located in the northern region of Guerrero, Mexico.
Environment 1 (E1) is situated in the experimental field of the Faculty of Agricultural and Environmental Sciences Unit “Tuxpan”, which is part of the municipality of Iguala de la Independencia in Guerrero, Mexico. Its geographical coordinates are 18°20′38.706″ N and −99°30′6.06″ O, and it stands at an altitude of 735 m above sea level (MASL). The climate is classified as warm and subhumid, with rain in summer (Awo) based on the Köppen classification. The average annual temperature is 26.4 °C, and the annual rainfall is approximately 1100 mm [28].
The soil is of the pelic vertisol type, in color dark brown, with a depth of more than 10 cm, a clay-loam texture and moderate drainage, with 0.536 to 1.47% organic matter, 30% or more clay, 24.16% sand and 41.28% silt, in all its horizons, the pH 7.6 to 8.2, 0.3% of N total, P = 15 ppm, and K = 2 cmol kg−1. The soil is not affected by soluble salts or exchangeable sodium [29,30].
Environment 2 (E2) is located at the agroecological ranch “El Romerito” in the southeast of the Taxco de Alarcón municipality in Guerrero, Mexico. Its geographical coordinates are 18°35′06.83″ N and −99°40′21.09″ O, and it stands at an altitude of 2334 MASL. The climate is classified as mild, with rain in summer (Cwb) based on the Köppen classification. The average annual temperature is 18.4 °C, and the annual rainfall is approximately 1252 mm [31].
The mountain range is characterized by folded turbidites with abundant fossils from the Late Cretaceous, where a block of foliated rocks consisting of volcanic, terrigenous, and limestone deposits outcrops. The soil type corresponds to a Luvisol, although in the municipality of Taxco, there are also soils classified as Lithosol, Chromic Cambisol, and Haplic Phaeozem [32].

2.2. Plant Material

For this research, Amm plants were obtained from botanical seeds from previous experimental research at Taxco Guerrero property of the Universidad Autónoma de Guerrero.
The procedure to obtain plants was as follows:
  • The seeds underwent chemical priming pre-treatment for germination (Citomax®), involving a solution with a dose of 1 mL per 1 L of distilled water, and were soaked for 24 h. The Supplementary Materials (see Table S1) provides further details regarding the hormonal components of the germination pre-treatment;
  • The seeds were placed inside a laboratory in sterilized box Petri dishes on a double layer of paper towel moistened with distilled water;
  • Seeds were subsequently watered on their surface by sprinkling until they were covered with a solution of GA3 at 200 ppm (or 200 mg) per liter of water for 4 days until their germination and transformation into seedlings;
  • Once the seedlings had cotyledons (four leaves), they were sown in a tray with 200 cavities in a substrate of Canadian peat and vermiculite mixed in a 3/2 ratio, respectively, until they transformed into plants. During this process, the maximum and minimum temperature and RH were recorded as 33.9 and 28.4 °C and 61.4 and 51.2%, respectively;
  • When the plants reached a height of 8 to 12 cm, they were immersed in a solution of water and rooting agent (at a proportion of 7 g/L) for 5 min. See Table S2 in the Supplementary Materials for further details about the chemical components of rooter treatment.
Note: Not all plants reached these dimensions; to avoid statistical biases, only those that achieved the aforementioned height were selected.
6.
They were then transplanted into 15 L polyethylene bags (40 × 40 cm). The substrate was a mixture in a ratio of 50/50 v/v of humus of leaves and mountain clay loam soil of Taxco de Alarcón municipality. The analysis in the Supplementary Materials (see Table S3) indicates that the soil is loamy;
7.
Soil analysis was performed. Refer to the Supplementary Materials for more information;
8.
The Supplementary Materials, Figure S7, includes pictures of the seeds, seedlings, and plants.

2.3. Experimental Design

2.3.1. Input Factors and Irrigation

(a)
The plants were placed with Artificial Shading (AS) as follows:
In E1, the plants were exposed to direct sunlight from the early hours until noon, when the light was photosynthetically active. The AS was produced because the plants were put under a “mango” tree branches were thinned to avoid direct sunlight during hours of the greatest radiation of the infrared spectrum of sunlight to avoid the plants’ death.
In E2, the AS was from the surrounding trees starting at 2 p.m. and from the clouds typical of the mild environment.
Note: Our group’s previous studies have demonstrated that AS has a beneficial effect on plant survival.
(b)
Four treatments were carried out, two in every environment; where: τ 1 = treatment one, τ 2 = treatment two, τ 3 = treatment three, τ 4 = treatment four, as follows:
τ 1 :   E 1 + AS + BCSR   soil   and   τ 2 :   E 1   +   ON   +   AS   +   BCSR   soil
τ 3 :   E 2 + AS + BCSR   soil   and   τ 4 :   E 2   +   ON   +   AS   +   BCSR   soil
(c)
The Temperature and RH were measured every hour during the crop time with a programmed datalogger instrument in E1 and E2. See the results in Figure 1;
(d)
ON = Organic Nutrition or nutrition organic solution. A volumetric solution based on humic and fulvic acids was applied (2 mL/L of water). Note: According to the results of the analysis of the ingredient used for ON (commercial trade Hortihumus®), it was considered as mature compost due to: (a) C/N (Carbon/Nitrogen ratio) exceeding 15, (b) the quantity of organic matter, (c) the liquid state, (d) high fulvic and humic acids (12%). See Table S6 in the Supplementary Materials;
(e)
I = Irrigation, see Table 1.
Table 1 shows the monthly irrigation profiles during the Crop season. To ensure the plants’ survival, the water quantity had to change over time to avoid the permanent wilting point caused by transpiration. In every environment, the quantity of water was different because temperature and RH were also different.

2.3.2. Output Factors Measure

It is worth noting that the following output factor measurements were performed on the main stem during the Crops time (168 days), 13 times each (all on the same day):
(a)
Plant height (HPl) from soil surface until the main stem’s apical meristem with a flexometer;
(b)
Leaf number (LN);
(c)
Internodes number (IN);
(d)
Branches number (BN);
(e)
The diameter of the stem (DT) was measured with a digital caliper (Vernier trademark SURTEK©, Minimum measuring range—Maximum measuring range = 1 mm–150 mm, Resolution = 0.01 mm) every 10 cm of length until the beginning of the inflorescence, based on the substrate surface. The measurements were made once only for every height in the vegetative development measurement throughout the time;
(f)
The Secondary Stem number (SSN) emerged from rhizomes
Also noted were:
(a)
Inflorescence length (IL) was measured with a Truper© FH-8M, Flexmeter Gripper from the first whorl of the inflorescence until the last one (cm);
(b)
Chlorophyll content (ChC) (Quantity of chlorophyll content in a leaf). The reading was taken with a chlorophyll meter (Model SPAD-502, Trademark Konica Minolta©, SPAD value: Relative chlorophyll content index; −9.9 to 199.9, difference in optical density at two wavelengths: 650 nm and 940 nm), which quantitatively evaluates the intensity of leaf green always at 01:00 PM, obtaining measurements in three strata of the plant: low, middle and high stratum, in the vegetative and reproductive stages of the plant. The Chlorophyll 1 and 2 content (ChC1, ChC2, respectively) refer to two different measurement dates during the Crops time. Both environments were measured in February (ChC1) and April (ChC2). The reported value in this research corresponds to the middle stratum;
(c)
Fresh Weight (WF) (biomass of all plants, including roots, before drying);
(d)
Dry weight (WD) (biomass of all plants, including roots, after the dry process) were weighed on a granite scale model BASE-5EP, Trademark Truper©, Capacity 5 kg, Minimum division 1 g/0.01 oz, Minimum weight 10 g/0.1 oz, measurement units Grams (g)/Ounces (oz).
Note: The dry process was performed at room temperature for seven days inside a laboratory, with temperatures 38.8 and 30.1 °C, and the RH was 37.3% and 30.8% maximum and minimum, respectively.

2.3.3. Statistical Methodology

In order to determine which treatment yields the best performance based on the output factors, a completely randomized design (CRD) was used to analyze the data. This type of experiment is employed when the experimental units are homogeneous. The treatment comprises four levels, namely τ 1, τ 2, τ 3, τ 4. The design is balanced, with ten repetitions in each treatment, making it a CRD. The CRD can be expressed as an equation.
Y i j = μ + τ i + ε i j ;           ε i j ~ I I D N 0 , σ 2 ,   i = 1,2 , 3,4 ;           n 1 = n 2 = n 3 = n 4 = 10
where Y i j is the value of the response variable in treatment i and replication j; μ is the global mean of the response variable, τ i is the effect of treatment i , and the errors ε i j are supposed to be independent, have a normal distribution with zero mean and constant variance, σ 2 . The null hypothesis to test whether there was no effect in terms of treatment in the response variables or equivalently that the populational means of the response variables in the treatments are equal.
The statistical model assumes normal distribution and constant variance. These assumptions are checked with the Shapiro–Wilks and Bartlett’s tests [33] and car [34] library, respectively, at a significance level of alfa 0.05. However, not all response variables conform to a normal distribution as required by the statistical model. Furthermore, it is not always true that the variances of the response variables of the treatments are equal. If any of the above assumptions fail, then the response variable is transformed using the Box-Cox transformation.
y λ * = y λ 1 λ ,   λ 0 l n y ,   λ = 0
The Box-Cox transformation is implemented in the power Transform function of the car library [34] of the R statistical software version 4.0.3 [35]. When the null hypothesis was rejected, the best treatment was identified using Tukey’s test implemented in the agricolae Library [36].

2.3.4. Association Analysis of Input and Output Factors Using MATLAB Graphics

Isolines, also known as level curves or contour graphics, represent a function of multiple variables. This type of graphic demonstrates the three-dimensional relationship between two input factors, X and Y (predictors), plotted on the “x” and “y” axis, and the output factors on the “z” axis in various colors.
In this manuscript, the isolines by means of(R2022b) MATLAB’S (v9.13, R2022a, The MathWorks Inc., Natick, MA, USA) Figures in a 3D matrix-graphic arrangement with contour (X, Y, Z, n) are used to obtain the LN isolines as a function of temperature and RH factors where n = 20,000 (isolines analysis to create the image only in Figure 2, Figure 3, Figure 4, Figure 5, Figure 6, Figure 7, Figure 8 and Figure 9). Notice that the output factors of vegetative growth (HPl, IN, BN, DT, SSN) are input factors to know their relationship with LN. In Figure 2a–d, isolines are only straight because, for every RH, there is only one temperature.

2.3.5. Mathematical Principle Applied in the Plot by Means of MATLAB

We have a hypothetical multivariable function in mathematics f = f ( x 1 , x 2 , x 3 , x 4 , x 5 , x 6 , x 7 , x 8 , x 9 ) that would represent the entire history of the Amm plants crop representing the input and output variables where: x 1 environmental temperature (°C), x 2 relative humidity (%), x 3 is the crops time (days); x 4 , is the height of the plant (cm); x 5 is the number of branches (#); x 6 is the number of secondary stems (#); x 7 , is the number of internodes (#); x 8 , is the diameter of the stem (mm); x 9 is the number of leaves (#). Based on the above we can construct the following 3D figures: f 1 = f 1 ( x 1 , x 2 , x 9 ) see Figure 2; f 2 = f 2 ( x 1 , x 4 , x 9 ) ; see Figure 3; f 3 = f 3 ( x 2 , x 4 , x 9 ) see Figure 4; f 4 = f 4 ( x 3 , x 4 , x 9 ) see Figure 5; f 5 = f 5 ( x 5 , x 4 , x 9 ) see Figure 6; f 6 = f 6 ( x 6 , x 4 , x 9 ) see Figure 7; f 7 = f 7 ( x 7 , x 4 , x 9 ) see Figure 8; f 8 = f 8 ( x 8 , x 4 , x 9 ) see Figure 9, to know its behavior we change the x axis to x 1 , x 2 , x 3 , x 5 , x 6 , x 7 , x 8 , , We will set the y-axis with x 4 in all figures, and the z-axis with uppercase x 9 in all figures. Based on agronomic principles, the height and number of leaves are used as comparative references to analyze their behavior in relation to the plant’s physical parameters.

3. Results and Discussion

3.1. Statistical Results

Table 2 shows the values of Fresh Weight (g), Dry Weight (g), chlorophyll content (SPAD units), Height of plant (cm), number of leaves, number of nodes, branch number, diameter of stem (mm), and secondary stem number.
Table 3 contains the Box-Cox transformation equations for modeling statistical experimental output factors.
Table 4 shows the sample mean results being very similar in E1 ( τ 1 and τ 2 ) and very different in E2 ( τ 3 and τ 4 ). E1 outperformed E2 across all output factors in their values, except for Chlorophyll content and SSN.

3.2. Environmental Inputs and Agronomic Results Analysis by Means of MATLAB Plots

Figure 1 contains the profile in both environments measured every one hour during the Crops time.
Figure 1. Shows the temperature and relative humidity profiles (maximum and minimum), for both environments: (a) Temperature in E1, (b) Temperature in E2, (c) RH in E1, (d) RH in E2.
Figure 1. Shows the temperature and relative humidity profiles (maximum and minimum), for both environments: (a) Temperature in E1, (b) Temperature in E2, (c) RH in E1, (d) RH in E2.
Plants 13 02661 g001
It is important to note that the RH is statistically or completely censored due to low night temperatures. As the temperature drops, the atmosphere becomes saturated with water due to dynamic equilibrium between soil and atmosphere. The difference between the maximum and minimum temperatures and RH is more significant in E2, indicating greater instability.
The ideal gas law PV = nRT can be used to model the environment before it reaches water saturation. However, in supersaturation, real gas equations are needed. Ions with the same charge, those with a smaller ionic radius, displace those with a greater cationic radius, such as Na+, displacing K+, Ca2+, and Mg2+.
These ions interact with water molecules from the environment and ON, and this interaction is useful in understanding the waterlogging stress on experimental results.
In Figure 2, Figure 3, Figure 4, Figure 5, Figure 6, Figure 7, Figure 8 and Figure 9 (sections a–d), the LN was selected as a reference for vegetative growth, because the leaves are responsible for converting nutrients into biomass through photosynthesis. Understanding the impact of temperature stress originates from the growth elements of the HPl-LN plant and its interaction with other output variables.
Figure 2 LN predictive values were calculated as means of RH and temperature interaction for each measured date throughout the experiment period.
The next analysis shows how agronomic analysis of vegetative growth can be performed using isolines:
When isoline lengths change color or direction, then initial and final values of Temperature and RH (and ΔX = ΔT = T 2 T 1 and ΔY = ΔRH = R H 2 R H 1 )
Where T 1 and T 2 , are the final and the beginning temperatures, also R H 2 and R H 1 are final and beginning relative humidities, which is reflected in the value of LN growth indicated by the color bar or “z” axis. This change is the rate or change ratio.
The length and slope values of each isoline in Figure 2a–d were calculated using the Euclidean distance formula:
d ( P 1 , P 2 ) = ( T 2 T 1 ) 2 + ( R H 2 R H 1 ) 2 ;   the   slope   is   m = R H 2 R H 1 ( T 2 T 1 )
The change ratio in color at each length d of every isoline is different by environment and ON effects. There are 11 and 12 straight intervals to analyze from right to left for treatments τ 1 - τ 2 (Table 5) and τ 3 - τ 4 (Table 6), respectively.
Table 5 and Table 6 show, for every isoline, the values d , m , and initial and final values L N i and L N f , respectively. ( L N f L N i ) ratio indicates how much the LN values have increased over time.
An isoline with a longer length and the same slope indicates that the relationship between RH and temperature is more stable over time. This means that fewer factors influence an abrupt change in the environment.
In E1, vegetative growth reaches its maximum more quickly, while in E2 it is slower. Several events can occur during vegetative development, such as a lack of nutrients, reaching the physiological age necessary to bear fruit, the growth of new secondary stems, thickening of the original stem, or an increase in height.
These events imply that vegetative development and crop yield continue. Moreover, analyzing the lengths and slopes can indicate the best moments for agronomic management (such as fertilization and pruning), which directly depend on the environment and the physiological phase of the plant.
A technological application for research can achieve higher crop yields under controlled conditions of temperature and humidity. Then, different zigzag profiles must be designed in relation to lengths and slopes of the isoline.
The following considerations have been made for each treatment in Figure 3 and beyond:
(a)
On the “y” axis, it is important to differentiate the difference between final and initial values as ΔY for each point on the “x” axis. Similarly, on the “x” axis, the ΔX should be considered as they represent the behavior of the population, the impact of nutrition, and the environment;
(b)
While analyzing ΔX and ΔY, it is important to pay attention to color change (LN values);
(c)
The length d of the slope m can be analyzed using the criteria and equations explained in Figure 2;
(d)
Pearson’s linear correlation coefficient has been calculated globally for the output factors of all treatments.
These criteria are proposed to analyze isolines, which are a key characteristic in the results.
Figure 2. Isolines of LN, obtained through relationship RH and Temperature; (a) τ 1 , (b) τ 2 , (c) τ 3 , (d) τ 4 .
Figure 2. Isolines of LN, obtained through relationship RH and Temperature; (a) τ 1 , (b) τ 2 , (c) τ 3 , (d) τ 4 .
Plants 13 02661 g002
A more specific analysis of the isolines can be carried out to determine the influence on the growth of HPl and LN; however, for each figure, only a few were performed to show its usefulness.
In Figure 3a–d ( τ 1 τ 4 ) the isolines show LN profiles by temperature effect. Comparing both environments E1 and E2, it is evident that HPl and LN are correlated with temperature. The isolines slope, ΔX and ΔY, are greater in E1 than in E2. Section 3.3 analyzes the temperature effect on abiotic stress and other factors in both environments.
Figure 3. Isolines for relationship among HPl, temperature and LN, (a) τ 1 , (b) τ 2 , (c) τ 3 , (d) τ 4 .
Figure 3. Isolines for relationship among HPl, temperature and LN, (a) τ 1 , (b) τ 2 , (c) τ 3 , (d) τ 4 .
Plants 13 02661 g003aPlants 13 02661 g003b
In Figure 4a–d ( τ 1 τ 4 ) the isolines show LN profiles by HPl and RH effect.
In Figure 4a,b, it is evident that as (RH) decreases, both the height of the plants (HPl) and the number of leaves (LN) increase. Specifically, when RH is at 44.8, the plant height increases from 130 to 175 cm (ΔHPl = 45 cm) at τ 1 , and from 130 to 190 cm (ΔHPl = 60 cm) at τ 2 . This variability suggests a strong impact of the treatment. Notably, the maximum HPl values do not align with the maximum LN values, potentially indicating the plant’s prioritization of fruit ripening by shedding more leaves. This phenomenon has been observed during drought stress, which will be elaborated on in Section 3.3.
In Figure 4c,d, as the RH increases, HPl and the LN increase. However, analyzing RH when it increases from 56.5 to 63.5% (ΔRH = 7%), the ΔHPl of τ 3 is lower than the ΔHPl of τ 4 . However, the maximum HPl value does not correspond to the maximum LN value due to the effect of cold stress, which will be explained in Section 3.3.
In summary, in the E1 environment, HPl and LN vegetative growth occurs as RH decreases from 60% to around 45%. Conversely, in E2, growth happens as RH increases from 50% to around 63%.
Figure 4. Isolines for relationship among HPl, RH, and LN: (a) τ 1 , (b) τ 2 , (c) τ 3 , (d) τ 4 .
Figure 4. Isolines for relationship among HPl, RH, and LN: (a) τ 1 , (b) τ 2 , (c) τ 3 , (d) τ 4 .
Plants 13 02661 g004
In Figure 5a–d ( τ 1 τ 4 ), the LN isolines represent an ascending sigmoidal profile effect in HPl, which is commonly reported in various publications from all disciplines [37,38]. However, these lines only provide a discrete representation of the population through specific curve fits and/or equations. This means that the sigmoidal profile cannot predict the entire population but only a part of it (See Figure S6 in Supplementary Materials).
Inside τ 1 τ 3 , the trend is that when HPl increases, LN also increases. The maximum HPl values decrease in the following order: τ 2 , τ 1 , τ 4 , τ 3 , indicating the effect of E1 above E2 and ON above control treatment. Additionally, the growth of HPl and LN in E2 remained without change for some time. The Pearson’s Linear Correlation Coefficient (PLCC) between HPl and LN is 0.75 (see Supplementary Materials), reflecting the behavior in τ 4 , where the maximum LN values correspond to minimum HPl values (reminder: not all population of plants have this behavior).
Figure 5. Isolines for relationship among HPl, Crops time, and LN: (a) τ 1 , (b) τ 2 , (c) τ 3 , (d) τ 4 .
Figure 5. Isolines for relationship among HPl, Crops time, and LN: (a) τ 1 , (b) τ 2 , (c) τ 3 , (d) τ 4 .
Plants 13 02661 g005
In Figure 6a–d ( τ 1 τ 4 ), when HPl and BN increase, LN also increases, although ΔBN can increase without needing to increase HPl. The value of BN increases in the following order: τ 4 , τ 1 , τ 3 , and τ 2 .
Analyzing PLCC values in the BN-HPl and BN-LN are 0.57 and 0.68, respectively. Therefore, it can be said that BN has a direct relationship with fresh and dry weight in general.
Note that ΔBN and ΔHPl (in the whole scale) are greater in E1 than E2.
Figure 6. Isolines for relationship among HPl, BN, and LN: (a) τ 1 , (b) τ 2 , (c) τ 3 , (d) τ 4 .
Figure 6. Isolines for relationship among HPl, BN, and LN: (a) τ 1 , (b) τ 2 , (c) τ 3 , (d) τ 4 .
Plants 13 02661 g006
In Figure 7a, the number of secondary stems increases very slowly when Hpl and LN values are maximum.
In Figure 7b, the maximum values of SSN have the minimum value of HPl and LN.
In Figure 7c,d, the growth of SSN is inversely proportional to Hpl.
The PLCC values for HPl-SSN and SSN-LN are −0.63 and −0.52, respectively, indicating that vegetative development and the emergence of secondary stems (and perhaps their development) occur alternately.
Figure 7. Isolines for relationship among HPl, SSN, and LN: (a) τ 1 , (b) τ 2 , (c) τ 3 , (d) τ 4 .
Figure 7. Isolines for relationship among HPl, SSN, and LN: (a) τ 1 , (b) τ 2 , (c) τ 3 , (d) τ 4 .
Plants 13 02661 g007aPlants 13 02661 g007b
Figure 8a–d depict a linear relationship where IN/LN = 1/2 with varying changes in ΔHpl. It is important to emphasize that, for each IN value, there is a corresponding ΔHpl, whose value reaches a maximum and then decreases, indicating the end of vegetative development and the start of inflorescence growth for some of the population; meanwhile, a smaller group is still in vegetative development. A possible cause is dormancy in plants.
The PLCC values between IN-LN and Hpl-IN are 1 and 0.75, respectively.
Figure 8. Isolines for relationship among HPl, IN, and LN: (a) τ 1 , (b) τ 2 , (c) τ 3 , (d) τ 4 .
Figure 8. Isolines for relationship among HPl, IN, and LN: (a) τ 1 , (b) τ 2 , (c) τ 3 , (d) τ 4 .
Plants 13 02661 g008
Figure 9a–d illustrate how plants change their diameter in a “mirror C” profile, increasing their Hpl to ending their growth with a similar diameter to their initial diameter (the more height, the final diameter moves away from the initial diameter), preparing for blooms and fruit production.
The PLCC values for Hpl-Ds and Ds-LN are 0.82 and 0.50, respectively. The plants experienced stress in both environments, and further investigation is needed to determine whether the thickening of the stem is caused by stress, as in the case of Pinus pinceana Gordon [39].
Remember that this plot represents the vegetative development measurement over time; the final diameter along HPl until harvest was not measured.
Figure 9. Isolines for relationship among HPl, DT, and LN: (a) τ 1 , (b) τ 2 , (c) τ 3 , (d) τ 4 .
Figure 9. Isolines for relationship among HPl, DT, and LN: (a) τ 1 , (b) τ 2 , (c) τ 3 , (d) τ 4 .
Plants 13 02661 g009

3.3. General Discussion

3.3.1. Germination and Comparison of Yields between Environments

Many medicinal plants have varying degrees of dormancy in their seeds, resulting in uneven germination and subsequent emergence [40]. Our research and other studies by our team have found that pre-treating Amm seeds for germination (which typically results in approximately 35% emergence in seedbeds) reveals the characteristic of dormancy in these seeds [41].
Germination began six days after sowing, and approximately 85% of the seeds had germinated after 16 days, demonstrating that the inorganic seed pre-treatment applying GA3 in germination and seedling vigor was successful.
According to our results in Azospirillum to ensure good vegetative development, the seed pre-treatment enhanced root growth and weight, which led to increased production of dry leaf, pod, and overall dry matter production in Cassia angustifolia [2,5].
In Table 7, the results show the output factors with the highest yields and productivity between environments, corresponding to E1 the favorable trends. Among the E1 treatments, the trend favors τ 2 . Regarding E2, the trend of higher yields and productivity favors τ 4 .
Regarding the previous results, it is relevant to explain that the value of IL/HPl and WD/WF ratios of the E1( τ 1 τ 2 ) indicates that the plants of both treatments have the same proportion between lengths and weights, being distinguished only by ON. In contrast, in E2, the output factors values and ratios between treatments are smaller, evidencing the effects of temperature, RH, cold stress and waterlogging.
According to research on the germination of ginger (Zingiber officinale) and turmeric (Curcuma longa L) rhizomes, the optimal temperatures for sprouting were 27.5 °C and 30.1 °C, respectively. Neither species sprouted at 14 °C, and it was found that the minimum temperature required for developing 5 cm shoots was slightly above 17 °C for both. Temperatures above 32 °C caused tissue damage and root loss [42]. Emergence of sugarcane stem pieces showed a linear increase with temperature at 30 °C, and no emergence was observed below 18 °C [43]. These temperature results are relevant to the conditions of E1 and E2 in the production of secondary stems and, in general, on the Amm’s vegetative development.
The results of the seed yield are presented in Table 8. Only in E1 were the secondary stems able to produce inflorescence with seed yield. In E2, only the plant with the τ 4 was able to produce seed yield; however, these plants also produced the heaviest seeds, which is why the number of seeds per 1 g is the lowest, as a quality indicator.
Environmental factors influence plant reproductive success. Plants can experience various types of stress, such as water stress, temperature, light, and nutrients, which can be caused by excess or lack of any of these factors. It is important to consider that seed yield occurred later in τ 3 , indicating that E2, along with the BCSR approach, is more suitable for survival and fruit production.

3.3.2. Impact of Heat Stress in E1

High-temperature stress can significantly impact cell division, which can restrict plant growth and cause oxidative damage. Even a short exposure to high temperatures during seed filling can lead to low quality and lower yields. High temperatures can be fatal for plants when combined with a limited water supply. The primary cause of water loss due to heat stress is increased transpiration during the day, which can damage critical physiological processes in crops. Heat stress can also reduce root growth, weight, and overall yield, reducing the plant’s access to water and nutrients [44].
In E1, the delay in plants’ flowering and the low is due to a lack of nutrients because of an increment in irrigation to prevent permanent wilting point by heat and drought stresses, reducing the time needed for photosynthesis, among others [8]. However, when the temperature increased, the plant grew, and few secondary stems were produced. At the beginning of the experiment, the temperatures were lower during the rainy season. However, the temperature increased at the start of the year, and RH progressively decreased.

3.3.3. Impact of Cold Stress in E2

In the E2 soil, abiotic stress was identified with plants’ waterlogging, hypoxia, and cold. This inhibits and/or reduces gas exchange, depriving roots of the oxygen they need for respiration. It also promotes nitrate reduction and affects metabolic conditions, reducing photosynthetic capacity and, thus, plant development yield. In τ 3 and τ 4 of E2, waterlogging stress is most likely caused by the clay soil conditions, the application of humic and fulvic acids, and the cationic exchange with the environment’s relative humidity, which will be discussed later.
Under cold stress conditions in E2, plants may begin natural torpor (dormancy) because fewer photosynthates are available for translocation to the reproductive areas. As a result, they stop growing, close their stomata, and reduce the availability of sugars in aerial growth meristems.
Photosynthates move towards the roots or crown, increasing short internode packing due to cold stress. When the soil temperature becomes favorable, rhizomes quickly reproduce and sprout from the surface as secondary stems. In the second phase of photosynthesis, known as the dark phase, plants are classified into three categories: C3, C4, and Crassulacean Acid Metabolism (CAM) plants. C3 plants can survive in very low light conditions but can only partially use solar energy. Maybe our research supports it so that Amm can adapt to high temperatures, intense solar radiation, and limited water supply like C4 plants [7].
The environment strongly influences the results in chlorophyll content in Table 2. Therefore, Amm plants are more easily adapted to E2 conditions and have more chlorophyll.
Based on their response to low temperatures, plants are categorized into three groups: (a) Chilling-sensitive plants are severely damaged at temperatures above 0 °C and below 15 °C, (b) Chilling-resistant plants sustain injury when ice formation begins in tissues, and (c) Frost-resistant plants can withstand exposure to very low temperatures [9]. Amm plants have shown the ability to survive in temperatures between 5 and 15 °C. Therefore, the Amm’s plants cannot be classified as chilling delicate plants but as chilling-sensitive plants.

3.3.4. Impact of BCSR Approach-ON in Yield and Soil Health

Amm is a perennial plant that generates new secondary stems from the soil surface after its fruit or seed matures. To observe the new vegetative cycle of these plants in two different environments, they were irrigated after harvested fresh matter and seed.
The plants in E1 died within three weeks, most likely due to temperature stress, which affected the roots and impacted not only the primary growth cycle but also the secondary growth cycle in woody plants like Amm [8].
In E2, new secondary stems were developed post-harvest. After 12 weeks, the following central tendency measures were recorded: for τ 3 , the average was 37.2; the mode was 46, the maximum was 57, and the minimum was 5; for τ 4 , the average was 65.3, the mode was 80, the maximum was 100, and the minimum was 20. All secondary stems of the plants developed inflorescence and produced seeds. These results reinforced the classification of Amm as a chilling-sensitive plant or C3 because cold stress did not affect its quality of life after harvest, in contrast to [8,9].
To explain the aforementioned and the results in Table 8, it is necessary to make use of healthy soil issues: this fact is achieved by means of elements and practices for soil regeneration, among them by adding organic matter. “A healthy soil can exhibit the following characteristics: It provides an adequate supply of nutrients to the aboveground biomass, ensuring that plants show no observable symptoms of nutrient deficiency. The soil also has sufficient aggregation of soil particles, allowing water to infiltrate the surface instead of running off. Additionally, it maintains soil organic matter levels relative to pre-row crop agriculture” [45].
The analysis indicates that the ON ingredient used in our experiments is a mature compost, as reflected by its C/N ratio exceeding 15, reflecting its significant humic and fulvic substance. This is an essential factor in determining the variations in the amount of Nitrogen (N) mineralized [5]. Therefore, it is an essential source of organic matter that maintains soil fertility and yield sustainability.
Researchers observed that BCSR also influences soil structure, particularly surface crusting, compaction, and hydraulic conductivity. The high exchangeable Ca2+ content (65%) of a “balanced soil” is beneficial in maintaining and improving soil structure and aggregate stability [18].
According to the soil’s values in our experiment, the base saturation percentages of the cations Ca2+, Mg2+, and K+ in the soil are 78.4%, 19.1%, and 2.01%, respectively. The ratios of Ca/K, Mg/K, (Ca+Mg)/K, and Ca/Mg are 30.9, 9.5, 48.4, and 4.1, respectively. The CEC value is 13.9, which is considered moderately low, and the pH = 6.76, which is considered an optimal value for crops. These ratios and values are consistent with the BCSR approach described in [14,16,45,46]. See Table S3 in the Supplementary Materials.
Then, improving the CEC by adding organic matter is necessary, considering the soil’s characteristics and the effects of fulvic and humic acids.
Loam soil is considered a combination of sand, silt, and clay with ranges of 23–52%, 28–50%, and 7–27%, respectively [47].
Clays and soil organic matter behave as negatively charged ions (anions), allowing them to retain or adsorb cations. This soil capacity enables it to retain the elements necessary to nourish plants [46].
The application of humic substances in soil has been shown to enhance fruit characteristics, diameter, weight, and the number of fruits per plant. Similarly, the use of fulvic acids has been found to increase plant height, leaf number, number of branches and leaves, dry weight, crop growth rate, as well as the number and weight of pods and seed yield, according to the findings of this research [48,49,50].
In sandy soils, including loam soils, humic acids bind to sand particles. This increases the CEC and the soil’s capacity to retain moisture and nutrients. As a result, the nutrients are kept in the soil along with water, which makes them accessible to plants. This, in turn, promotes increased plant growth and height [50].
In addition, the values of saturation point, field capacity, and permanent wilting point in the soil of our experiment are 99.8, 53.8, and 32%, respectively (see Table S3 in the Supplementary Materials). These values are very high and, combined with adequate amounts of humic and fulvic acids, ensure that nutrients remain available to the roots as needed, improving structure, fertility, and moisture retention [50].
The aforementioned applies to the textural class of loam soils, which retain too much moisture, become compacted in rainy areas, and must be drained. In E2, the pots were not drained, so waterlogging stress occurred [51].
The high CEC in soils enables better retention and utilization of various elements, including minerals and soil nitrogen. This helps to prevent the loss of these compounds through drainage from the root zone. However, in the case of E1, due to heat stress to maintain the field capacity or avoid the permanent wilting point, it was necessary to apply more water irrigation, but this was not enough to achieve better seed weight quality.
Finally, we have included more information about successful researchers on the BCSR approach. See Supplementary Materials.

4. Conclusions

According to our research, the use of BCSR soil + ON treatment resulted in higher crop yield compared to the BCSR soil treatment for Agastache Mexicana subsp. mexicana “Amm” grown in two different environments. Our analysis of the output factors showed that certain factors had an impact on yield, with higher values obtained in E1. The results of crop yield and seed quality were affected by cold, waterlogging, and heat stresses. We also evaluated the crop quality by measuring seed weight and found that the highest values were obtained in τ 4 (E2 and ON). The biomass yield between treatments with ON were τ 2 is 48% higher than τ 4 , and control τ 1 66% higher than τ 3 . Our research confirms the effectiveness of the BCSR approach for achieving higher crop yields, which has been reported by farmers and consultants.
In E1, the Amm plants can be cultivated to produce dry matter as a raw material source for infusions. Future research is necessary to measure terpenes, antioxidants, flavonoids, and others due to heat stress. Seeds can also be produced to improve resistance to extreme environments. Research about propagation by rhizomes, seed vigor and seed germination is necessary.
In regions where E2 is active, intensive organic cultivation is feasible due to the soil’s natural capacity to generate BCSR and maintain a well-balanced texture. Further research is needed to measure terpenes, antioxidants, flavonoids, and other compounds due to cold stress. Additionally, research on seed germination, seed vigor, and rhizome propagation is needed.
The selection, quantity, proportions, and composition of the ingredients in the experimental soil reflect the knowledge of people living in the mountains. It would be worthwhile to explore the social aspects of the environment as well.

Supplementary Materials

The following supporting information can be downloaded at: https://www.mdpi.com/article/10.3390/plants13182661/s1, Soil fertility analysis, physical and chemical properties, Cationic Ratios, Cation Exchange Capacity (CEC) and base saturation percentage of experimental soil, results of ON considered as mature compost, additional analysis to enable the best knowledge, output factors mean, multiple comparison of Tukey, Sample Variance Analysis, and Pictures. Ref. [52] was cited in the Supplementary Materials.

Author Contributions

Conceptualization by M.A.G.-S., J.R.-M., J.L.F.-M. and F.G.-J.; Methodology by B.C.-L., J.M.-B. and M.A.G.-S.; Software by J.L.F.-M., F.G.-J. and M.V.-V.; Validation of data by M.T.Z.-Á., K.A.A.-C., J.L.F.-M. and J.E.-M.; Formal Analysis by J.R.-M., J.L.F.-M., B.C.-L. and F.G.-J.; Investigation by M.A.G.-S., J.R.-M., J.M.-B. and T.R.-R.; Resources by, K.A.A.-C., B.C.-L., T.R.-R. and J.E.-M.; Data curation by F.G.-J., J.R.-M., M.T.Z.-Á., K.A.A.-C. and M.V.-V.; Writing by J.R.-M., F.G.-J., J.L.F.-M. and J.M.-B.; Writing—review and editing by T.d.J.A.-Z. and B.C.-L.; Visualization by T.d.J.A.-Z.; Supervision by M.A.G.-S., M.T.Z.-Á., J.R.-M. and K.A.A.-C.; Project Administration by M.A.G.-S., T.d.J.A.-Z., M.T.Z.-Á. and K.A.A.-C.; Funding Acquisition by T.d.J.A.-Z., J.E.-M. and M.A.G.-S. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Data Availability Statement

The data presented in this study are available on request from the corresponding author.

Acknowledgments

We thank CONAHCyT for supporting this manuscript via project 3981370. We are also grateful to the Instituto Politécnico Nacional, the Unidad CICATA Legaria, via project SIP-20240155, and the Universidad Autónoma de Guerrero, Facultad de Ciencias Agropecuarias y Ambientales for providing the space and vehicles. Julio Romero for the facilities in the experiment in Taxco.

Conflicts of Interest

The authors declare no conflicts of interest.

References

  1. Martínez, M.A.; Montechiarini, N.H.; Gosparini, C.O.; Arango, M.R.; Gallo CD, V.; Craviotto, R.M. Viabilidad, vigor y germinación de semillas verdes de soja. Para Mejor. Prod. 2019, 58, 15–22. [Google Scholar]
  2. Tiwari, P.; Kumar, R. Effects of pre-sowing seed treatments on germination and seedling growth performance of Ocimum basilicum L. J. Pharmacogn. Phytochem. 2020, 9, 1401–1405. [Google Scholar]
  3. Mwase, W.F.; Mvula, T. Effect of seed size and pre-treatment methods of Bauhinia thonningii Schum. on germination and seedling growth. Afr. J. Biotechnol. 2011, 10, 5143–5148. [Google Scholar]
  4. Raei, Y.; Alami-Milani, M. Organic cultivation of medicinal plants: A review. J. Biodivers. Environ. Sci. 2014, 4, 6–18. [Google Scholar]
  5. Carrubba, A. Sustainable fertilization in medicinal and aromatic plants. In Medicinal and Aromatic Plants of the World: Scientific, Production, Commercial and Utilization Aspects; Springer: Dordrecht, The Netherlands, 2015; pp. 187–203. [Google Scholar]
  6. Karlen, D.L.; Mausbach, M.J.; Doran, J.W.; Cline, R.G.; Harris, R.F.; Schuman, G.E. Soil quality: A concept, definition, and framework for evaluation (a guest editorial). Soil Sci. Soc. Am. J. 1997, 61, 4–10. [Google Scholar] [CrossRef]
  7. Ferrante, A.; Mariani, L. Agronomic management for enhancing plant tolerance to abiotic stresses: High and low values of temperature, light intensity, and relative humidity. Horticulturae 2018, 4, 21. [Google Scholar] [CrossRef]
  8. Husen, A.; Iqbal, M. (Eds.) Medicinal Plants: Their Response to Abiotic Stress; Springer Nature: Singapore, 2023. [Google Scholar]
  9. Yadav, S.; Modi, P.; Dave, A.; Vijapura, A.; Patel, D.; Patel, M. Effect of abiotic stress on crops. Sustain. Crop Prod. 2020, 3, 5–16. [Google Scholar]
  10. Radulov, I.; Berbecea, A.; Sala, F.; Crista, F.; Lato, A. Mineral fertilization influence on soil pH, cationic exchange capacity and nutrient content. Res. J. Agric. Sci. 2011, 43, 160–165. [Google Scholar]
  11. Hodges, S.C. Soil Fertility Basics; Soil Science Extension North Carolina State University; North Carolina State University: Raleigh, NC, USA, 2010. [Google Scholar]
  12. Pernes-Debuyser, A.; Tessier, D. Soil physical properties affected by long-term fertilization. Eur. J. Soil Sci. 2004, 55, 505–512. [Google Scholar] [CrossRef]
  13. Cruz-Macías, W.O.; Rodríguez-Larramendi, L.A.; Salas-Marina M, Á.; Hernández-García, V.; Campos-Saldaña, R.A.; Chávez-Hernández, M.H.; Gordillo-Curiel, A. Efecto de la materia orgánica y la capacidad de intercambio catiónico en la acidez de suelos cultivados con maíz en dos regiones de Chiapas, México. Terra Latinoam. 2020, 38, 475–480. [Google Scholar] [CrossRef]
  14. Saha, N.; Mandal, B. Soil testing protocols for organic farming—Concept and approach. Commun. Soil Sci. Plant Anal. 2011, 42, 1422–1433. [Google Scholar] [CrossRef]
  15. Linder, K.J. The Effect of Soil Cation Balancing on Soil Properties and Weed Communities in an Organic Rotation. Master’s Thesis, The Ohio State University, Columbus, OH, USA, 2015. [Google Scholar]
  16. Kopittke, P.M.; Menzies, N.W. A review of the use of the basic cation saturation ratio and the “ideal” soil. Soil Sci. Soc. Am. J. 2007, 71, 259–265. [Google Scholar] [CrossRef]
  17. Chaganti, V.N.; Culman, S.W.; Herms, C.; Sprunger, C.D.; Brock, C.; Leiva Soto, A.; Doohan, D. Base cation saturation ratios, soil health, and yield in organic field crops. Agron. J. 2021, 113, 4190–4200. [Google Scholar] [CrossRef]
  18. Zalewska, M.; Nogalska, A.; Wierzbowska, J. Effect of basic cation saturation ratios in soil on yield of annual ryegrass (Lolium multiflorum L.). J. Elem. 2018, 23, 95–105. [Google Scholar] [CrossRef]
  19. Brock, C.; Jackson-Smith, D.; Culman, S.; Doohan, D.; Herms, C. Soil balancing within organic farming: Negotiating meanings and boundaries in an alternative agricultural community of practice. Agric. Hum. Values 2021, 38, 449–465. [Google Scholar] [CrossRef]
  20. Badalingappanavar, R.; Hanumanthappa, M.; Veeranna, H.K.; Kolakar, S.; Khidrapure, G. Organic fertilizer management in cultivation of medicinal and aromatic crops: A review. J. Pharmacogn. Phytochem. 2018, 7, 126–129. [Google Scholar]
  21. Hendawy, S.F.; Khalid, K.A. Effect of chemical and organic fertilizers on yield and essential oil of chamomile flower heads. Med. Aromat. Plant Sci. Biotechnol. 2011, 5, 43–48. [Google Scholar]
  22. Tan, K.H. Humic Matter in Soil and the Environment: Principles and Controversies; CRC Press: Boca Raton, FL, USA, 2003. [Google Scholar]
  23. Melo López, L. Análisis y caracterización de ácidos fúlvicos y su interacción con algunos metales pesados. 2006.
  24. Cooper, L.; Abi-Ghanem, R. El Valor de las Sustancias Húmicas en el Ciclo de Vida del Carbón de los Cultivos: Ácidos Húmicos, ácidos Fúlvicos; Huma Gro: Gilbert, AZ, USA, 2017; pp. 1–8. [Google Scholar]
  25. Veobides-Amador, H.; Guridi-Izquierdo, F.; Vázquez-Padrón, V. Las sustancias húmicas como bioestimulantes de plantas bajo condiciones de estrés ambiental. Cultiv. Trop. 2018, 39, 102–109. [Google Scholar]
  26. Haghighi, M.; Kafi, M.; Colmillo, P. Actividad fotosintética y metabolismo de N de la lechuga afectados por el ácido húmico. Rev. Int. Cienc. Veg. 2012, 18, 182–189. [Google Scholar]
  27. Canellas, L.P.; Olivares, F.L.; Aguiar, N.O.; Jones, D.L.; Nebbioso, A.; Mazzei, P.; Piccolo, A. Humic and fulvic acids as biostimulants in horticulture. Sci. Hortic. 2015, 196, 15–27. [Google Scholar] [CrossRef]
  28. García, E. Modificaciones al Sistema de Clasificación Climática de Köppen; Universidad Nacional Autónoma de México: Mexico City, Mexico, 2005. [Google Scholar]
  29. Alcántara Jiménez, J.Á.; Hernandez Castro, E.; Ayvar Serna, S.; Nava, A.D.; Brito Guadarrama, T. Phenotypic and agronomic characteristics of six genotypes of papaya (Carica papaya L.) from Tuxpan, Guerrero, Mexico. Rev. Venez. Cienc. Tecnol. Aliment. 2010, 1, 35–46. [Google Scholar]
  30. Damián-Nava, A.; González-Hernández, V.A.; Sánchez-García, P.; Peña-Valdivia, C.B.; Livera-Munoz, M.; Brito-Guadarrama, T. Crecimiento y fenología del guayabo (Psidium guajava L.) cv.“Media China” en Iguala, Guerrero. Rev. Fitotec. Mex. 2004, 27, 349. [Google Scholar] [CrossRef]
  31. García, E. Modificaciones al Sistema de Clasificación Climática de Köppen; Universidad Nacional Autónoma de México: Mexico City, Mexico, 2004. [Google Scholar]
  32. Chávez-Hernández, C.G.; Barrera Aguilar, C.C.; Téllez Espinosa, G.J.; Chimal-Sánchez, E.; García-Sánchez, R. Colonización micorrízica y comunidades de hongos micorrizógenos arbusculares en plantas medicinales del bosque templado “Agua Escondida”, Taxco, Guerrero, México. Sci. Fungorum 2021, 51, e1325. [Google Scholar] [CrossRef]
  33. Gross, J.; Ligges, U. Nortest: Tests for Normality. R Package Version 1.0-4. 2015. Available online: https://cran.r-project.org/web/packages/nortest/ (accessed on 20 September 2023).
  34. Fox, J.; Weisberg, S. An R Companion to Applied Regression, 3rd ed.; Sage: Thousand Oaks, CA, USA, 2019; Available online: https://cran.r-project.org/web/packages/car/index.html (accessed on 20 September 2023).
  35. R Core Team. R: A Language and Environment for Statistical Computing; R Foundation for Statistical Computing: Vienna, Austria, 2020; Available online: https://www.R-project.org/ (accessed on 20 September 2023).
  36. Felipe de Mendiburu. Agricolae: Statistical Procedures for Agricultural Research. R Package Version 1.3-5. 2021. Available online: https://cran.r-project.org/web/packages/agricolae/index.html (accessed on 20 September 2023).
  37. Longhi, D.A.; Dalcanton, F.; Aragão, G.M.F.D.; Carciofi, B.A.M.; Laurindo, J.B. Microbial growth models: A general mathematical approach to obtain μ max and λ parameters from sigmoidal empirical primary models. Braz. J. Chem. Eng. 2017, 34, 369–375. [Google Scholar] [CrossRef]
  38. Yuan, R.; Yang, B.; Liu, Y.; Huang, L. Modified Gompertz sigmoidal model removing fine-ending of grain-size distribution. Open Geosci. 2019, 11, 29–36. [Google Scholar] [CrossRef]
  39. Martiñón-Martínez, R.J.; Vargas-Hernández, J.; López-Upton, J.; Gómez-Guerrero, A.; Vaquera-Huerta, H. Respuesta de Pinus pinceana Gordon a estrés por sequía y altas temperaturas. Rev. Fitotec. Mex. 2010, 33, 239–248. [Google Scholar] [CrossRef]
  40. Saeedeh, R.; Mehrnaz, H.; Mansour, G. Silicon-nanoparticle mediated changes in seed germination and vigor index of marigold (Calendula officinalis L.) compared to silicate under PEG-induced drought stress. Gesunde Pflanz. 2021, 73, 575–589. [Google Scholar]
  41. Reséndiz-Muñoz, J.; Cruz-Lagunas, B.; Fernández-Muñoz, J.L.; de Jesús Adame-Zambrano, T.; Delgado-Núñez, E.J.; Zagaceta-Álvarez, M.T.; Aguilar-Cruz, K.A.; Urbieta-Parrazales, R.; Miranda-Viramontes, I.; Morales-Barrera, J.; et al. Influence of artificial shading and SiO2 on Agastache mexicana subsp. mexicana Ability to survive under water stress. Horticulturae 2023, 9, 995. [Google Scholar] [CrossRef]
  42. Retana-Cordero, M.; Fisher, P.R.; Gómez, C. Modeling the effect of temperature on ginger and turmeric rhizome sprouting. Agronomy 2021, 11, 1931. [Google Scholar] [CrossRef]
  43. Smit, M.A. Characterising the factors that affect germination and emergence in sugarcane. Int. Sugar J. 2011, 113, 65. [Google Scholar]
  44. Passioura, J.B. Roots and drought resistance. In Developments in Agricultural and Managed Forest Ecology; Elsevier: Amsterdam, The Netherlands, 1983; Volume 12, pp. 265–280. [Google Scholar]
  45. Dougherty, B. Regenerative Agriculture: The Path to Healing Agroecosystems and Feeding the World in the 21st Century; A Report for Nuffield International Farming Scholars, Nuffield International Project; Nuffield International: Moama, NSW, Australia, 2019; Volume 45. [Google Scholar]
  46. Garrido Valero, M. Interpretación de Análisis de Suelos. 1994. Available online: https://www.mapa.gob.es/ministerio/pags/biblioteca/hojas/hd_1993_05.pdf (accessed on 20 September 2023).
  47. FAO. Organización de las Naciones Unidas Para la Alimentación y Agricultura. Textura del Suelo. 2019. Available online: https://www.fao.org/fishery/docs/CDrom/FAO_Training/FAO_Training/General/x6706s/x6706s06.htm (accessed on 20 September 2023).
  48. Yildirim, E. Foliar and soil fertilization of humic acid affect productivity and quality of tomato. Acta Agric. Scand. Sect. B-Soil Plant Sci. 2007, 57, 182–186. [Google Scholar] [CrossRef]
  49. Abdel-Baky, Y.R.; Abouziena, H.F.; Amin, A.A.; Rashad El-Sh, M.; Abd El-Sttar, A.M. Improve quality and productivity of some faba bean cultivars with foliar application of fulvic acid. Bull. Natl. Res. Cent. 2019, 43, 2. [Google Scholar] [CrossRef]
  50. Varas Abad, P.L. Evaluación de Dosis de Ácido Húmico Granulado de Leonardita y Ácidos Húmicos y Fúlvicos con Macro y Micro Nutrientes en el Cultivo de Cebollita China (Var. Roja chiclayana), Bajo Condiciones Agroecológicas en la Provincia de Lamas; Universidad Nacional de San Martín: Buenos Aires, Argentina, 2012. [Google Scholar]
  51. Available online: https://agrawdata.com/blog/suelos-francos/ (accessed on 20 September 2023).
  52. Blevins, R.L.; Frye, W.W. Conservation tillage: An ecological approach to soil management. Adv. Agron. 1993, 51, 33–78. [Google Scholar]
Table 1. Irrigation doses during experimental time.
Table 1. Irrigation doses during experimental time.
StageTotal Irrigation per Week
τ 1 τ 2 τ 3 τ 4
13 L water2 L water + ON2 L water1 L water + ON
25.5 L water4.5 L water + ON2 L water1 L water + ON
37 L water6 L water + ON3 L water2 L water + ON
47 L water6 L water + ON3.5 L water2.5 L water + ON
Note 1: For the treatments with ON, one liter of water is prepared as explained in materials and methods. Stage 1: covers the months of August and September, for all treatments the total liters of water are 3 L. Irrigation is applied only on Saturday. Stage 2: covers the months of October, November and December, weekly irrigations were distributed between Wednesday and Saturday in the case of E1 and only on Saturday in the case of E2. Stage 3 and 4 cover the months of January and February, weekly irrigations were distributed between Tuesday, Thursday and Saturday. Note 2: After harvest, the plants in E2 were maintained with only 2.5 L of water per week in the period between the months of May and August.
Table 2. Normality and variances homogeneity assumptions results, Box-Cox transformation, and ANOVA results.
Table 2. Normality and variances homogeneity assumptions results, Box-Cox transformation, and ANOVA results.
ConceptOutput Factors p-Value
WFWDChC1ChC2HPlLNINBNDTSSN
ANOVA
Assumptions
N0.050.080.250.840.480.300.300.910.790.14
H0.210.170.670.950.900.190.190.390.270.57
Box-Cox
Parameter
λ 00.50−2.407.600------−0.300.39
R-squared%75%83%65%5%89%65%66%29%50%71%
Treatment
ANOVA
SSTr9.55293.961.08 × 10−81.26 × 1027.612692673.0414.882.57172.26
TMS3.1897.993.60 × 10−94.19 × 10−22.54897.3224.3138.290.8657.42
F c ( 3 ,   36 ) 36.7457.5521.80.6196.0522.922.94.8412.1229.5
P4.7 × 10−118.2 × 10−143.1 × 10−80.61<2.2 × 10−161.8 × 10−81.8 × 10−86.2 × 10−31.2 × 10−58.3 × 10−10
Residuals
ANOVA
RSS3.1261.305.93 × 10−92.50 × 10−40.951410.4352.61028.92.5570.07
RMS0.091.701.65 × 10−106.83 × 10−20.02639.189.828.580.071.95
N = Normality (Shapiro–Wilk) H = Homogeneity of variances (Bartlett), TSS Treatment sum of squares, TMS Treatment mean squared, RSS = Residuals sum of squares, RMS Residuals mean squared, A.V. (Analysis of variance), λ = Box-Cox parameter, R-squared = Determination coefficient.
Table 3. Box-Cox transformations of the output factors.
Table 3. Box-Cox transformations of the output factors.
TBox-Cox Transformation
WFWDHPlChc1ChC2DSSSN
Ec = l n W F = W D 0.5 1 0.5 = l n H P l = C h c 1 2.397 1 2.397 = C h c 2 7.599 1 7.599 = D T 0.3011 1 0.3011 = S S N 0.3863 1 0.3863
Table 4. Sample means of the response variables of interest and their Tukey grouping.
Table 4. Sample means of the response variables of interest and their Tukey grouping.
τ i Sample Mean
WFWDChC1ChC2HPlLNINBNDTSSN
O67.0520.6341.745.7118.143.821.925.82.06.2
τ 1 83.1 a28.5 a37.3 b44.6 b157.6 a53.2 a26.6 a27.3 ab2.4 a1.0 c
τ 2 103.0 a34.9 a35.7 b46.4 b170.3 a50.6 a25.3 a30.4 a2.8 a2.0 c
τ 3 28.2 c6.3 c44.8 a46.1 a59.8c34.4 b17.2 b22.6 b1.3 b7.1 b
τ 4 53.9 b12.8 b49.1 a45.9 a84.6b37.0 b18.5 b23.0 b1.5 b14.8 a
τ i = Treatment i , O = Overall sample mean. Same letter means no statistically significant difference among the means.
Table 5. Values of d , m , of L N f / L N i in E1.
Table 5. Values of d , m , of L N f / L N i in E1.
#Isoline/Concept1234567891011
d 0.213.71.651.773.231.4570.622.451.183.23
m 0.33.180.141.643.510.522.170.117.368.361.68
τ 1   ( L N f L N i ) 11.62.63.23.83.94.84.84.84.84.8
τ 2   ( L N f L N i ) 1.62.02.233.23.43.44.24.44.44.4
Table 6. Values of d , m , of L N f / L N i in E2.
Table 6. Values of d , m , of L N f / L N i in E2.
#Isoline/Concept123456789101112
d 4.854.622.672.834.444.742.602.102.034.110.462.95
m 12.077.161.122.274.622.853.640.1315.6124.170.642.71
τ 3   ( L N f L N i ) 1.01.61.21.62.23.03.23.64.04.64.64.6
τ 4   ( L N f L N i ) 1.31.11.31.42.22.72.83.03333
Table 7. Results of output factors, the relationships between treatments, environments, Organic Nutrition, and control treatments.
Table 7. Results of output factors, the relationships between treatments, environments, Organic Nutrition, and control treatments.
Yield and Productivity
EnvironmentTrHpl
(cm)
LN
(#)
WF
(g)
WD
(g)
Bloom
(%)
IL
(cm)
IL/HplWD/WF
E1 τ 1 157.653.283.128.59024.50.1550.343
τ 2 170.350.6103.034.9100260.1530.339
E2 τ 3 59.834.428.26.32010.0170.223
τ 4 84.6237.053.912.810011.30.1340.237
E1 τ 1 + τ 2 319.46103.8186.163.49550.50.3080.681
E2 τ 3 + τ 4 144.3971.482.119.16012.30.1500.460
E2/E1 ( τ 3 + τ 4 ) ( τ 1 + τ 2 ) 0.440.690.440.30630.240.490.68
Ratios between Treatments
Concept/OutputRatioHpl
(cm)
LN
(#)
WF
(g)
WD
(g)
Bloom
(%)
IL
(cm)
IL/HplWD/WF
E1 τ 1 τ 2 0.931.050.810.820.900.941.011.01
E2 τ 3 τ 4 0.710.930.520.490.200.090.130.94
ON τ 4 τ 2 0.500.730.520.371.000.430.880.70
BCSR τ 3 τ 1 0.380.650.340.220.220.040.110.65
IL = Inflorescence Length, ON = Organic Nutrition, Tr = treatment. Mathematical ratios are a comparison of the amount of one output contained in another output to understand the impact of environments and treatments. Productivity encompasses the following in outputs: number, lengths, chlorophyll content and percentages.
Table 8. Seed characteristics results for τ 1 , τ 2 , τ 3 , τ 4 .
Table 8. Seed characteristics results for τ 1 , τ 2 , τ 3 , τ 4 .
Concept/
Treatment
MSS
(#)
SSS
(#)
TS
(#)
WMS
(mg)
WSS
(mg)
TW
(mg)
MSSW
(mg)
SSSW
(mg)
AWpS
(mg)
Sp1gr
(#)
τ 1 942042985.239.044.20.0550.1910.1485621
τ 2 6862669413.9149.7163.60.2040.2390.2364242
τ 3 0000000000
τ 4 5505513.9013.90.25300.2533957
MSS = Main Stem Seeds, SSS = Secondary Stem Seeds, TS = Total Seeds, WMS = Weight Main Stem, WSS = Weight Secondary Stems, TW = Total Weight, MSSW = Main Stem Seeds Weight, SSSW = Secondary Stem Seeds Weight, AWpS = Average Weight per Seed, Sp1gr = Seeds per 1 g.
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Morales-Barrera, J.; Reséndiz-Muñoz, J.; Cruz-Lagunas, B.; Fernández-Muñoz, J.L.; Godínez-Jaimes, F.; de Jesús Adame-Zambrano, T.; Vázquez-Villamar, M.; Romero-Rosales, T.; Zagaceta-Álvarez, M.T.; Aguilar-Cruz, K.A.; et al. Abiotic Stress Effect on Agastache mexicana subsp. mexicana Yield: Cultivated in Two Contrasting Environments with Organic Nutrition and Artificial Shading. Plants 2024, 13, 2661. https://doi.org/10.3390/plants13182661

AMA Style

Morales-Barrera J, Reséndiz-Muñoz J, Cruz-Lagunas B, Fernández-Muñoz JL, Godínez-Jaimes F, de Jesús Adame-Zambrano T, Vázquez-Villamar M, Romero-Rosales T, Zagaceta-Álvarez MT, Aguilar-Cruz KA, et al. Abiotic Stress Effect on Agastache mexicana subsp. mexicana Yield: Cultivated in Two Contrasting Environments with Organic Nutrition and Artificial Shading. Plants. 2024; 13(18):2661. https://doi.org/10.3390/plants13182661

Chicago/Turabian Style

Morales-Barrera, Judith, Juan Reséndiz-Muñoz, Blas Cruz-Lagunas, José Luis Fernández-Muñoz, Flaviano Godínez-Jaimes, Tania de Jesús Adame-Zambrano, Mirna Vázquez-Villamar, Teollincacihuatl Romero-Rosales, María Teresa Zagaceta-Álvarez, Karen Alicia Aguilar-Cruz, and et al. 2024. "Abiotic Stress Effect on Agastache mexicana subsp. mexicana Yield: Cultivated in Two Contrasting Environments with Organic Nutrition and Artificial Shading" Plants 13, no. 18: 2661. https://doi.org/10.3390/plants13182661

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