The role of organic matter in the acidification
of agricultural soils in Ecuadorian Amazonia
El papel de la materia orgánica en la acidificación de suelos
agrícolas de la amazonia ecuatoriana
Luis David Jiménez Jumbo
1
Jhandry Patricio Sarango Ordoñez
2
Joana Alexandra Moreno López
3
Luis Alejandro Fiallos Ulloa
4
Abstract: The research focuses on understanding how agricultural
practices and the decomposition of organic matter contribute to
changes in soil acidity, a phenomenon critical to soil health and
productivity in this area. The study uses scientific methods to analyze
soil samples, evaluating the composition of organic matter and its
relationship to soil acidity. The influence of organic matter on soil
acidity was evaluated, highlighting that Amazonian soils tend to be
more acidic and clay soils predominate. The study uses a coefficient
of determination of 0.662 to evaluate the relationship between organic
matter and soil acidity, indicating that approximately 66.2% of the
variability in soil acidity can be explained by organic matter. The
researchers conclude that the presence of organic matter plays a
significant role in soil acidification, especially in regions such as the
Amazon, where higher acidity is observed. They also highlight the
predominance of clay soils in these areas, which may influence
nutrient retention and the ability to neutralize soil acidity. These
findings underscore the importance of considering organic matter and
specific soil characteristics when developing agricultural
management and conservation strategies in regions with acid soils
such as the Amazon.
Keywords: hydrogen potential, organic carbon, organic matter, soil,
soil use potential, acidification
Resumen: La investigación se centra en comprender cómo las
prácticas agrícolas y la descomposición de la materia orgánica
contribuyen a cambios en la acidez del suelo, un fenómeno crítico
para la salud y productividad del suelo en esta área. El estudio utiliza
métodos científicos para analizar muestras de suelo, evaluando la
composición de la materia orgánica y su relación con la acidez del
suelo. Se evaluó la influencia de la materia orgánica en la acidez del
suelo, destacando que los suelos amazónicos tienden a ser más ácidos
y predominan los suelos arcillosos. El estudio utiliza un coeficiente
de determinación de 0.662 para evaluar la relación entre la materia
orgánica y la acidez del suelo, lo que indica que aproximadamente el
66.2% de la variabilidad en la acidez del suelo puede ser explicada
por la materia orgánica. Los investigadores concluyen que la
1
Biochemical Engineer, Universidad Estatal
Amazónica, ld.jimenezj@uea.edu.ec
https://orcid.org/0009-0000-0862-2048
2
Eng. Environmental Biotechnology,
Universidad Estatal Amazónica,
ja.morenol@uea.edu.ec
https://orcid.org/0009-0008-4427-670X
3
Biologist, Universidad Estatal Amazónica
Jp.sarangoo@uea.edu.ec
https://orcid.org/0009-0001-4305-6579
4
Master's Degree in Forestry, Universidad Estatal
Amazónica, la.fiallosu@uea.edu.ec
https://orcid.org/0009-0006-8477-9980
Published
Edwards Deming Higher Technological
Institute. Quito - Ecuador
Periodicity
January-March
Vol. 1, Num. 21, 2024
pp. 12-24
http://centrosuragraria.com/index.php/revista
Dates of receipt
Received: December 19, 2023
Approved: January 30, 2024
Correspondence author
ld.jimenezj@uea.edu.ec
Creative Commons License
Creative Commons License, Attribution-
NonCommercial-ShareAlike 4.0
International.https://creativecommons.org/lice
nses/by-nc-sa/4.0/deed.es
April - June vol. 1. Num. 21 - 2024
13
presencia de materia orgánica desempeña un papel significativo en la
acidificación de los suelos, especialmente en regiones como la
Amazonía, donde se observa una mayor acidez. Además, resaltan la
predominancia de suelos arcillosos en estas áreas, lo que puede influir
en la retención de nutrientes y en la capacidad de neutralizar la acidez
del suelo. Estos hallazgos subrayan la importancia de considerar la
materia orgánica y las características específicas del suelo al
desarrollar estrategias de manejo agrícola y conservación en regiones
con suelos ácidos como la Amazonía.
Palabras clave: Potencial de hidrogeno, carbono orgánico, materia
orgánica, suelo, uso potencial, acidificación
Introduction
The Ecuadorian Amazon is home to an exceptional wealth of
biodiversity and plays a crucial role in global climate regulation.
However, the growth of agricultural activity in this region has raised
concerns about environmental impacts, particularly on soil health. Soil
acidification, a phenomenon that negatively affects the availability of
essential plant nutrients, has emerged as a significant challenge; this
decrease in soil pH alters the ability of nutrients to dissolve and be
available to plants, leading to nutritional deficiencies and negatively
affecting crop growth and yields (Queiroz et al., 2021)..
This study delves into the intricate relationship between organic matter
and the acidification of agricultural soils in the Ecuadorian Amazon.
Organic matter, consisting of decomposing plant and animal residues,
represents an essential component of soil structure and plays a
fundamental role in soil fertility. Organic matter, composed of
decomposing plant and animal residues, is fundamental to soil structure
and fertility; soil organic matter influences moisture retention,
improves soil structure and promotes beneficial biological activity. In
addition, it serves as a source of plant nutrients, harbors beneficial
microorganisms and helps regulate soil pH. Therefore, the presence and
maintenance of high levels of soil organic matter are crucial to mitigate
the negative effects of soil acidification and ensure the availability of
essential plant nutrients. However, processes involving organic matter
can also contribute to soil acidification, generating a delicate balance
that deserves detailed attention (Lal, 2015).
The objective of this study is to examine in depth the specific role of
organic matter in the process of soil acidification in Amazonian
agricultural contexts; specifically in the crop area of the Amazonian
Research and Production Experimental Center of the Amazon State
The role of organic matter in the acidification of agricultural soils in Ecuadorian Amazonia
14
University. Through detailed analyses of soil samples and evaluations
of local agricultural practices, we seek to provide a clearer
understanding of the mechanisms driving this phenomenon. These
insights are crucial to inform sustainable management strategies that
reconcile agricultural production with the long-term preservation of soil
health in this unique region.
Materials and methods
Specific tools and techniques were used to collect a representative soil
sample. A stainless steel shovel, airtight plastic bags, identification tags
and disposable gloves were used as key materials. Points within the
study area were randomly selected, ensuring an equal distribution. The
top layer of vegetation was removed at each point and excavated to a
predetermined depth using the shovel. To obtain a three-dimensional
representation of the soil, multiple samples were taken at each point,
which were combined and homogeneously mixed to form a composite
sample. Each sample was accurately labeled, stored in airtight bags, and
transported to the laboratory for subsequent analysis, ensuring
representative and consistent data collection ( (Bismarck et al., 2014)..
Samples were taken within the Experimental Center for Amazonian
Research and Production (CEIPA); where agricultural practices are
implemented with different crops in order to implement a teaching
system to students of the Amazon State University.
Determination of pH
For the determination of pH in a soil sample, the following materials
and method were implemented according to the FAO proposal. A
calibrated glass electrode, buffer solutions of known pH (pH 4.01, 7.00
and 10.01), magnetic stirrer and soil samples were used. Initially, the
glass electrode was calibrated using the prepared buffer solutions.
Subsequently, a soil suspension was prepared by mixing a measured
amount of soil with distilled water. The glass electrode was immersed
in the suspension to record the pH of the sample. This procedure was
repeated with several samples to obtain representative and accurate
results in the evaluation of the soil pH. (Food and Agriculture
Organization of the United Nations, 2020).
April - June vol. 1. Num. 21 - 2024
15
Determination of organic matter
In the analysis of organic matter in a soil sample, tools and procedures
were used according to the validation of the calcination method. The
materials included a muffle furnace, porcelain capsules, a spatula and
soil samples. In the method, a known amount of soil was weighed into
dry capsules and the initial weight was recorded. Subsequently, the
capsules with the soil were placed in the muffle furnace and heated to a
constant temperature for a given time. After cooling in a desiccator,
they were weighed again to calculate the weight loss as an indicator of
the organic matter present in the soil. This procedure was replicated on
several samples to obtain a representative assessment (Aguilar and
Yuleysi, 2019)..
Organic Carbon Determination
It is possible to estimate soil organic carbon content using the organic
matter content as a reference. Soil organic matter consists mainly of
carbon, but also includes other elements such as hydrogen, oxygen,
nitrogen and small amounts of sulfur and other elements. Although not
all components of organic matter are pure carbon, it is common to use
an empirical ratio to estimate organic carbon content from organic
matter content. The most commonly used ratio is the Van Bemmelen
ratio, which states that approximately 58% of the organic matter content
in soil is organic carbon. However, this ratio can vary depending on
several factors, such as soil type, soil use history, surrounding
vegetation, and soil management practices.
Despite these variations, estimating organic carbon content from
organic matter content is a common and useful practice in soil quality
management and monitoring, especially when specific organic carbon
data are not available (Martinez et al., 2017).
Determination of texture
To determine soil texture by bulk density, soil samples are taken from
different depths using a cylinder of known volume or a suitable
sampling tool. These samples are dried in the laboratory until a dry
weight constant is obtained. The bulk density is then calculated by
dividing the mass of dry soil by the total volume of the sample.
The relationship between bulk density and soil texture is established
through soil theory, where different soil textures, such as clay, silt and
The role of organic matter in the acidification of agricultural soils in Ecuadorian Amazonia
16
sand, have different bulk densities due to their physical and structural
properties. For example, clay soils tend to have a higher bulk density
due to compaction caused by small particles and high water holding
capacity, while sandy soils tend to have a lower bulk density due to their
looser structure and the presence of large particles.
Although the determination of soil texture through bulk density
provides an indirect and less accurate estimate than other methods of
textural analysis, it can be useful in situations where other resources or
more advanced techniques are not available. (Ibañez, 2007).
Table 1. Texture of soils with respect to their bulk density.
Texture
Bulk density (mg/m )
3
Sandy
1,55 - 1,80
Franco
1,35 - 1,50
Clay loam
1,30 - 1,40
Clayey
1,20 - 1,30
Source: (Ibañez, 2007)
Relationship between pH and organic matter
GeoGebra, with its interactive and visual capabilities, presents itself as
a highly effective tool in soil laboratories. It facilitates soil texture
analysis by allowing the visualization and evaluation of the relationship
between different particle sizes through scatter plots and curve fitting.
It is also useful for exploring correlations between various soil
parameters, such as the relationship between organic matter content and
water holding capacity, taking advantage of dynamic plots to identify
trends. GeoGebra is also used to visually model soil permeability and
analyze drainage capacity using infiltration rate plots. In spatial
variation studies, the tool creates interactive maps that visualize and
analyze the distribution of soil properties. In addition, GeoGebra acts
as a valuable educational tool, allowing students to interact with models
and graphs to improve their understanding of soil phenomena and
processes. In addition, it enables the simulation of soil laboratory
experiments, providing the opportunity to perform virtual practice
before conducting real experiments, which not only streamlines data
analysis, but also provides a more intuitive and visual understanding of
April - June vol. 1. Num. 21 - 2024
17
key concepts, thus facilitating informed decision-making in soil
management and study.
3. Result
Table 2. Results of CEIPA agricultural soil parameters
Soil
PH
Organic
Carbon (%)
Texture
Coffee
6,01
17,3884
Clayey
Pastures
5,52
15,0684
Clayey
Medicinal
Plants PB
6,89
24,2846
Clayey
Cocoa
6,18
10,962
Clay loam
Bio
Fertilizers
6,54
11,6
Franco
Citrus
5,59
0,2204
Clayey
Forestry
program
(balsa and
guadua)
5,98
18,6296
Clayey
Forestry
program
6,5
13,8562
Clayey
Banana
orchard
5,86
16,762
Clay loam
Banana
study
6,89
22,562
Clayey
The role of organic matter in the acidification of agricultural soils in Ecuadorian Amazonia
18
Old Coffee
5,86
8,236
Franco
Grass study
5,48
7,4762
Clayey
Medicinal
plants PA
6,795
23,950
Clayey
Coffee
research
6,190
8,700
Franco
Sajinos
5,871
16,026
Clay loam
Pastures 2
5,441
14,852
Clayey
Source: Author
Illustration 1. pH vs. organic matter in CEIPA's agricultural soils.
Source: Author
April - June vol. 1. Num. 21 - 2024
19
The results reflect a clear inverse relationship between pH and organic
matter in agricultural soils that is mainly due to the buffering capacity
of organic matter. Organic matter, composed mainly of decomposing
plant and animal residues, contains organic acids that can neutralize the
bases in the soil, thus lowering its pH. When there is a greater amount
of organic matter present in the soil, microbial activity that decomposes
these residues increases, releasing organic acids and other compounds
that acidify the soil.
On the other hand, organic matter can also help improve soil structure
and nutrient holding capacity, which in turn can influence pH.
However, as organic matter decomposes and nutrients are absorbed by
plants, pH tends to decrease due to the release of organic acids (Toledo,
2016).
Table 3. Regression data between pH and organic matter.
Regression model
Power
Formula
y = a * x
b
Parameters
a = 5296,844
b = -2,978
Coefficient of determination
R
2
= 0.662
Source: Author
The power regression model is used when the relationship between
variables is not linear, but follows an exponential trend. The behavior
of this model is such that when X increases, Y also increases, but not in
a constant manner. It is important to keep in mind that this type of model
can be sensitive to outliers, as small changes in x can result in large
changes in y due to the exponential nature of the relationship (Frias et
al., 2010).
In a potential model, an inverse relationship, as shown in Figure 1,
implies that as an independent variable increases, the dependent
variable decreases exponentially. That is, as X increases, Y decreases.
A coefficient of determination of 0.662 can be considered acceptable in
many contexts of statistical analysis. This value indicates that
approximately 66.2% of the variability in the dependent variable can be
explained by the regression model used. Although there is no single
criterion for determining the acceptability of a DC, in general, a value
The role of organic matter in the acidification of agricultural soils in Ecuadorian Amazonia
20
of 0.662 suggests a moderately strong relationship between the
variables. However, the evaluation of the acceptability of the coefficient
of determination should also consider other factors, such as the purpose
of the study, the expectations of the investigator, and the nature of the
data. In some cases, a CD of 0.662 may be sufficient to support
meaningful and useful conclusions, while, in other cases, a higher level
of model fit may be required. Ultimately, the decision on the
acceptability of a coefficient of determination should be based on a
comprehensive assessment of the context and the usefulness of the
model for the specific purposes of the research (Novales, 2010).
Table 4. Inverse relationship of pH and organic matter in clay soils.
Source: Author
0 5 10 15 20 25 30 35 40 45
Café
Pastos
Plantas Medicinales PB
Citricos
Programa forestal (balsa y guadua)
Programa forestal
Platano estudio
Estudio de pasto
Plantas medicinales PA
Pastos 2
Organic Matter (%) PH
April - June vol. 1. Num. 21 - 2024
21
Table 5. Inverse relationship between pH and organic matter in loam
soils.
Table 6. Inverse relationship between pH and organic matter in sandy
loam soils.
Source: Author
The great part of soils according to their topography turned out to be
clayey; according to Astorga (2018): in Ecuadorian Amazonian soils, a
0 5 10 15 20 25
Bio Abonos
Café Viejo
Investigacion café
Organic Matter (%) PH
0 5 10 15 20 25 30 35
Cacao
Huerta de platanos
Sajinos
Organic Matter (%) PH
The role of organic matter in the acidification of agricultural soils in Ecuadorian Amazonia
22
clay texture predominates. This texture is characterized by having a
high proportion of clay particles compared to sand and silt particles.
Clay is a mineral fraction of the soil with extremely small particles and
a high water and nutrient retention capacity. In Amazonian soils, the
presence of clay contributes to the high fertility of the soil and its ability
to retain moisture, which is fundamental to the diversity and lush
vegetation of the region (Astorga et al., 2018)..
Naturally, organic matter (OM) is integrated into the soil through the
decomposition of organic plant residues, concentrating predominantly
in the surface layers and decreasing in depth. Scientific literature
indicates that the presence of high levels of OM is associated with a
more acidic soil pH, although this behavior may vary depending on the
original soil material. MO and pH are crucial indicators of soil fertility
and health, underscoring the importance of ensuring that these attributes
are at adequate levels and at the optimum depth to support plant growth.
This study focused on determining the MO content and pH in a specific
agricultural soil. The results revealed a high concentration of OM
throughout the soil and a neutral pH, which is beneficial for a wide
variety of crops. An inverse relationship was observed between these
properties, where higher levels of OM were associated with lower pH,
especially in Amazonian soils, due to the anion richness of the original
soil material (Mora et al., 2016).
4. Conclusions
This study has provided significant evidence of the influence of organic
matter on the pH of Amazonian soils. With a coefficient of
determination of 0.662, we have shown that approximately 66.2% of
the variability in soil pH can be explained by organic matter.
Furthermore, we have found that the relationship between these
parameters is inversely proportional, suggesting that as organic matter
increases, soil pH tends to decrease, following a potential regression.
This relationship is especially relevant in the context of Amazonian
soils, where a clay texture predominates. The presence of clay in these
soils not only influences water and nutrient retention, but can also
modulate the influence of organic matter on pH. These findings
underscore the importance of considering the interaction between
organic matter, soil pH and soil texture in the management and
conservation of Amazonian soils, highlighting the need for
management strategies that promote an adequate balance of these
April - June vol. 1. Num. 21 - 2024
23
factors to maintain ecosystem health and agricultural productivity in the
region.
References
Aguilar, S., & Yuleysi, S. (2019). Validation of the calcination
method in the determination of soil organic matter content.
Universidad Nacional Agraria La Molina, Lima.
https://repositorio.lamolina.edu.pe/bitstream/handle/20.500.12
996/4154/aguilar-silva-sumiry-
yuleysi.pdf?sequence=1&isAllowed=y.
https://repositorio.lamolina.edu.pe/bitstream/handle/20.500.12
996/4154/aguilar-silva-sumiry-
yuleysi.pdf?sequence=1&isAllowed=y
Bismarck, R., Corrales, M., & Espinoza, A. (2014). Guía Muestreo de
Suelos. Water and Soil for Agriculture, 1, 19-33.
https://doi.org/efaidnbmnnnibpcajpcglclefindmkaj/https://repo
sitorio.una.edu.ni/3613/1/P33M539.pdf.
Food and Agriculture Organization of the United Nations (2020). Soil
testing methods. Rome: FAO.
efaidnbmnnnibpcajpcglclefindmkaj/https://www.fao.org/3/ca2
796en/CA2796EN.pdf
Frias, M., Fernandez, J., & Sordo, C. (2010). Estadistica. University
of Cantabria:
https://ocw.unican.es/pluginfile.php/2010/course/section/1746/
tema_02.pdf
Ibañez, J. (2007). How much does a square meter of arable soil layer
weigh: What is Apparent Density (by Régulo León Arteta). An
invisible universe under our feet.
https://doi.org/https://www.madrimasd.org/blogs/universo/200
7/05/16/65688
Lal, R. (2015). Restoring Soil Quality to Mitigate Soil Degradation.
Sustainability, 7(5), 5875-5895.
https://doi.org/https://doi.org/10.3390/su7055875
Martínez, J., Duval, M., López, F., Iglesias, J., & Galantini, J. (2017).
Adjustments in organic carbon estimation by the Calcination
method in molisols of southwestern Buenos Aires. Asociacion
The role of organic matter in the acidification of agricultural soils in Ecuadorian Amazonia
24
Argentina de las Ciencias del Soil.
https://doi.org/https://www.suelos.org.ar/publicaciones/v35n1-
html/vol35-n1-html/v35n1a16.htm.
Novales, A. (2010). Regression Analysis. Department of Quantitative
Economics. Universidad Complutense:
https://www.ucm.es/data/cont/docs/518-2013-11-13-
Analisis%20de%20Regresion.pdf
Queiroz , A., Wada , M., Perillo, F., Pelissari, C., & Trierveiler, M.
(2021). Effects of serum-free culture media on human apical
papilla cells properties. Archives of oral biology,(104962),
121. https://doi.org/10.1016/j.archoralbio.2020.104962.
Toledo, M. (2016). Manejo de suelos ácidos de las zonas altas de
honduras conceptos y métodos (Vol. 1). Honduras: Dirección
de Ciencia y Tecnología Agropecuaria (DICTA).
https://doi.org/https://repositorio.iica.int/bitstream/11324/3108
/1/BVE17069071e.pdf