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Published Instituto
Tecnológico Superior Corporativo Edwards Deming. Quito - Ecuador Frequency October - December Vol. 1, No. 31, 2026 Pp 17-43 http://centrosuragraria.com/index.php/revista Dates of receipt Received: July 11, 2026 Approved: September 11,
2026 Corresponding author Creative Commons License Creative Commons License,
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Cristiano De Angelis
Doctor en Gestion de Proyectos, Skema Business School, Lille, Francia,
generationoflove@gmx.com https://orcid.org/0000-0002-8025-7871
Key-words: biodynamic agriculture, cooperatives, emotion, false
economic miracle, rock dust.
Resumen: La
meteorización mejorada de rocas terrestres (ERW) es una tecnología prometedora
para la eliminación de dióxido de carbono que consiste en la aplicación de
rocas silicatadas trituradas, como el basalto, a los suelos agrícolas. Sin
embargo, los investigadores critican la falta de estudios, principalmente
físicos y biológicos de las rocas, para verificar si realmente benefician la
nutrición del suelo, ya que las ventajas de la reducción de la lixiviación y el
aumento de calcio, hierro (Fe), aluminio (Al) y magnesio (Mg) deben compararse
con los efectos negativos, como las pérdidas de CO₂ debidas a la mineralización
de la materia orgánica, la sodificación y la respiración del suelo. Algunos
autores afirman que las ventajas del polvo de roca son más pronunciadas en
países con climas tropicales, mientras que otros sostienen que no existen
ventajas significativas. En este contexto, este trabajo propone dos modelos: 1.
Un modelo de «Cultura-Conocimiento-Inteligencia» para comprender cómo la
cuestión cultural influye en los procesos de creación y aplicación del
conocimiento, y 2. Un modelo de agricultura biodinámica (fertilizantes caseros)
basado en cooperativas para mejorar las técnicas caseras en la agricultura
brasileña.
Palabras
clave: agricultura biodinámica,
cooperativas, emoción, falso milagro económico, polvo de roca.
Introduction
This study is a literature review
with an applied case study (Roraima, Brazil).
The literature review is heavily
based on rock dust, since biodynamic agriculture helps in the fight against
climate change.
Dupla et al. (2024) sustain that applying
ground silicate rock such as basalt on agricultural soils. On top of carbon
sequestration, Terrestrial enhanced rock weathering (ERW) has the potential to
raise the soil pH and release nutrients, thereby improving soil fertility.
According to Arma et al. ( 2024)
demonstrated an increase in total microminerals, fresh weight, total biomass,
better water retention, root development, mineralization, MUFA (monosaturated
fatty acid), protein content, and antioxidants in plant tissue produced using
RD-based media amendments.
According to Li and Dong (2013) the
nutritional content of Rock Dust - RD could be used as an amendment to improve
soil fertility, particularly in nutrient-poor soils. RD contains calcium and
trace elements such as iron (Fe), aluminum (Al), and magnesium (Mg) but lack a
substantial amount of nitrogen (N), phosphorus (P) and potassium (K).
In fact, according to these
researchers, most biological, physical, and chemical parameters remained
unaffected after 1 month and even 1 year of application, with significant
differences appearing primarily between fields rather than between rock powder treatments.
This multi-site field trial highlighted,
however, an increase in soil respiration and sodium concentration which,
despite being encouraging signs of short-term weathering kinetics, should be
further investigated before ERW can be deployed as both an efficient and safe
carbon dioxide removal technology (Dupla et al.,
2024).
It’s well known that rock dust
consists of pulverized rock particles and is gaining popularity as a
chemical-free soil amendment for improving soil health. Mined from geologic
rock deposits, rock dust can be used for carbon (CO2) capture, improving soil fertility,
modifying soil pH, as well as improving soil drainage and water holding
capacity (Arnott et al., 2019).
Bauwhede et al. (2024) suggest mixing lime
(e.g. 3–5 Mg/ha) with RD (e.g. 15–25 Mg/ha) as a potential solution to
sufficiently raise soil pH at an acceptable cost while still having sustainable
slow-release buffering by the rock dust.
Bauwhede et al. (2024b) found that the mixed
application of 3.1 Mg/ha basalt-diabase-lime rock powders and 1.6 Mg/ha of
bentonite did not sustainably alter the pH but did raise the topsoil base
saturation above 30 % in the top 10 cm of the mineral soil.
In the mining and quarrying
industries, for example, Rock Dust is a mineral-rich by-product that can be
used to improve soil fertility, promote plant growth, raise the activity of
beneficial microflora, increase pest and disease resistance, as well as enhance
the quality of fruits and vegetables. Future research should focus on
optimizing these formulations for various crop types and conditions to maximize
their benefits, thereby supporting sustainable agriculture and addressing waste
management challenges in the mining sector (Khan et al. 2023).
However, Dekhordi
et al. (2024) explain that waste products generated through mining activities
can cause a significant loss of biodiversity, air quality, and water pollution
affecting humans, plants, and animals through soil degradation. Despite the
significant contributions to society, mining activities have become a severe
threat to biodiversity and food security
For instance, some mining activities adversely affect the ecosystem
functioning, including the loss of arable land, soil degradation, polluted air,
and reduced water quality, leading to declining agricultural productivity, food
insecurity, and economic growth (Dekhordi et al.,
2024), what is clear in the figure 1.
Fig. 1. Pollution generated by mining
activities and its consequences (Dehkordi et al.,
2024).
Some authors find no benefit in
using rock dust as a fertilizer.
For example, the results of Ramezanian et al. (2024) show that the tested rockdust had no positive or negative effect on plant growth
or nutrient composition. In addition, the microbial response to added
substrates, a sensitive measure of changes in soil environment, were unaltered
by the rockdust. As the rockdust
had no nutrient or toxic effect it can probably be considered as an inert
material which at least causes no harm but equally has no demonstrable
ecological or agricultural benefit.
The scientific evidence about its
effectiveness is however contradictory, which derives from inconsistent
weathering rates and the complex interactions of several factors. Rock dust led
to significant results when applied to highly weathered soils in tropical
environments, as well as in combination with organic materials and
microorganisms (Swoboda, 2016).
Application of rock fertilizers in
tropical environments has advantages.
Firstly, the dissolution rate of
rocks and minerals and the reaction between mineral surfaces and soil solution
is enhanced under high temperatures and moisture regimes.
Secondly, the potential of applying
ground rocks and minerals to soils is elevated as the soils are characterized
by low nutrient contents because of high amounts of weathering and leaching,
and thus highly receptive to addition of nutrients (Straaten, 2006).
In addition several farmers do not
consider rock dust as a Biodinamic Homemade
fertilizer. The difficulty of cooperatives engaging in the acquisition of
crushing machines depends on a closer relationship with agricultural entitles
to analyze both rocks and soils (compatibility examination) besides the union
among farmers for formation in this “novelty” and subsequent construction of
crushing machines in their own farms.
For this reason, the research
question is how culture relates to knowledge and intelligence in order to know
what type of culture we have to build for effective Bio-dynamic agriculture.
Therefore, this work brings two
research models that feed each other.
In addition to the
Culture-Knowledge-Intelligence (CKI) model, this article presents a Bio-dynamic
Agriculture model, a mature way of better using the resources available on the
farm itself. The study concluded that this model is useful for small farmers to
learn, through cooperatives, home-made farming practices, such as rock dust as
a new fertilizer mixed or not with cattle manure.
Given this brief summary of the main
topic and this proposal, the article is divided into the following chapters: 1.
A literature review on rock powder 2. Agricultural cooperatives in the context
of Biodynamic Agriculture 3. The Culture-Knowledge-Intelligence model 4. The
biodynamic agriculture model
A literature review on rock dust
According to Straaten (2006) natural
mineral and rock-based fertilizers can be subdivided into:
• Multi-Nutrient Silicate Rock
Fertilizers, e.g. fine grained volcanic rocks,
• Single-Nutrient Rock Fertilizers,
e.g. phosphate rock fertilizers,
• Rock Fertilizers from rock and
mineral ‘waste’
– unprocessed mine ‘waste’
– processed rock and coal waste’
(e.g. flyash).
• Translocated Rock Fertilizers:
– alluvial Rock Fertilizer (e.g.
nutrient rich river and reservoir sediments)
– airborne Rock Fertilizers (e.g.
nutrient rich ‘loess’ and volcanic ash)
• Specific Nutrient Rock Fertilizers
concomitantly applied with organic residues, or biolog-ically
modified e.g. by micro-organisms,
• Biofertilizers, organic forms of
nutrients extracted from rocks, e.g. organic matter, phyto-extracted
from phosphate rock.
Bauwhede et al. (2024) aimed to: (1) compare
how rock dusts (RDs) dissolve depending on their mineralogy and surface area,
(2) examine RD dissolution in soils with different starting pH and buffer
capacities, and (3) evaluate tests that simulate weathering to predict how well
RDs improve soil pH. They tested five types of
commercially available RDs—including two basalts, phonolite, foidite, and trachy-andesite—on
four acidified forest soils with different textures and chemical properties.
The study underscores a key issue:
soil acidification is worsening worldwide, and while silicate RDs are seen as a
potential remedy, their effectiveness varies widely due to differences in
dissolution rates and acid neutralising capacity -
ANC. These properties are closely tied to the rock's mineral composition and
the soil's buffering capacity. Bauwhede et al. (2024)
emphasize the need for better evaluation methods to ensure the appropriate
selection and use of RDs in soil restoration efforts.
Duppa et al. (2024) observed that the
application of rock powder had a neutral to slightly positive influence on soil
biological fertility indicators. Among the measured parameters, only earthworm
abundance and soil respiration showed statistically significant changes, with
the abundance of earthworms increasing by an average of 71% in treated soils
after one month compared to controls. A general linear mixed model was used to
evaluate the influence of various factors on earthworm abundance, including
soil texture, soil organic carbon (SOC) content, pH, structural quality, bulk
density, and the presence of toxic trace elements. Notably, aside from the
effects of rock powder, elevated copper levels were the only factor with a
significant negative impact on earthworm populations.
Additionally, rock dusts can enhance
soil properties such as cation exchange capacity (Anda et al., 2015) and the
water retention capacity of sandy soils (Kahnt et al., 1986). However, their
effectiveness is inconsistent, and some contain potentially toxic elements at
harmful concentrations. Therefore, the agronomic outcomes of rock dust
applications, especially in tropical soils, are highly dependent on the
specific mineralogical and chemical composition of the rock, the deficiencies
of the soil, and the nutritional demands of target crops (van Straaten, 2017).
Swoboda, Döring, and Hamer (2022)
analyzed 48 crop trials and concluded that rock dusts, particularly those
derived from mafic and ultramafic rocks like basalt, nepheline, and
glauconite-bearing materials, show potential as alternative potassium sources and
multi-nutrient amendments in tropical soils. Basalt powders, in particular, are
notable for their richness in magnesium and iron silicates and their basic pH,
in addition to providing key nutrients such as phosphorus, potassium, calcium,
and various micronutrients.
Viana, Caetano, and Pontes (2021)
explored various techniques for improving soil fertility and found that
combining moderate amounts of basalt powder with higher doses of cattle manure
yielded the most effective results. Their findings suggest that the integration
of rock dust with organic fertilizers enhances nutrient availability and soil
health more efficiently than using rock dust alone.
Similarly, Da
Silva et al. (2017) emphasized
that the co-application of rock powders with organic materials that stimulate
biological activity can influence the mineral weathering process. However, they
also note a gap in knowledge regarding how such combinations affect the dissolution
of minerals, particularly in basalt rock powders.
During composting, the nitrogen
cycle is critical to compost quality, as noted by Hoang et al. (2022), who also
discuss strategies to mitigate nitrogen loss. While some studies provide
promising data, others lack rigorous scientific validation or real-world field
applications.
For example, Ramos et al. (2022)
report that combining organic fertilizers with rock powder can meet most macro-
and micronutrient requirements, and reduce application costs by more than 60%,
with long-lasting benefits for soil fertility. Conceição et al. (2022) observed
that corn and beans grown in basalt-enriched soils produced yields up to five
times higher than those in untreated soils.
Despite these benefits, it is widely
acknowledged that rock dust releases nutrients more slowly than chemical
fertilizers—a feature that, according to Theodoro and Leonardos (2006),
provides the advantage of prolonged nutrient availability in the soil. Bauwhede et al. (2024) support this view, stating that slow
nutrient release from rock dust reduces leaching, although its effectiveness
depends on rock mineralogy, soil pH, and testing methodologies.
Grecco et al. (2016) further
highlight that the low processing cost and demand for alternative fertilizers
encourage the use of ground rocks in agriculture. Nonetheless, they caution
that the variability in weathering reactions across rock types makes it
difficult to predict nutrient release rates, and that more research is needed
in this field.
Dos Santos et al. (2016) explain
that the nutrient release from rock dust occurs at a significantly slower rate
compared to chemical fertilizers. While this gradual release can offer
long-term benefits for soil fertility, it also presents challenges, such as
requiring higher application rates and longer periods before noticeable
agronomic responses are observed.
Lopes-Assad et al. (2006) reported
that the fungus Aspergillus niger effectively
solubilizes phosphate rocks by producing organic acids. Their study noted pH
fluctuations during treatment: in acidic conditions, solubilization of
potassium increased, whereas in treatments involving alkaline ultramafic rocks,
a reduction in acidity was associated with a decrease in potassium release.
To address soil acidity effectively,
liming with calcium and/or magnesium carbonates—such as calcite and dolomite—is
considered the most efficient method. According to Goulding (2016), these
minerals react with hydrogen ions in the soil solution and with aluminum
compounds, thereby reducing aluminum toxicity and improving soil pH.
The suitability of rock dust as a
fertilizer also varies depending on the crop type. For instance, crops like
lettuce, which demand high concentrations of soluble nutrients over a short
growth period, are unlikely to benefit from basalt application. Hanish et al.
(2024) found that applying up to 100 grams of basalt powder per pot failed to
improve lettuce yields, which remained nearly four times lower than those
produced with conventional fertilizers. This result reinforces that basalt
powder, due to its low nutrient concentration and slow release, is inadequate
for short-cycle, high-demand crops.
Guimarães et al. (2020) observed
that banana orchards fertilized exclusively with mineral fertilizers yielded
more fruit than those treated with organic-mineral blends. However, the latter
resulted in reduced soil acidification and greater availability of phosphorus
and potassium. The study also noted that excessive potassium levels could lead
to nutrient imbalances, negatively affecting plant productivity. Therefore,
further research is necessary to develop optimized fertilization strategies for
bananas that promote yield while maintaining soil health.
Finally, as emphasized by Viana,
Caetano, and Pontes (2021), while rock dust holds considerable promise in
Brazilian agriculture, particularly when combined with organic amendments like
animal manure, its effectiveness is still under-researched. Caution should be
exercised to avoid overestimating its benefits without sufficient empirical
support.
Organicospro (2018) notes that limestone, a
widely recognized ground rock, is composed primarily of calcium carbonate (in
the form of calcite) or calcium magnesium carbonate (dolomite). In contrast,
basalt powder is rich in silicate minerals, providing silicon—a vital nutrient
for plant health and productivity. These contrasting compositions illustrate
the distinct benefits each material offers. Basalt powder, in particular, plays
a valuable role in restoring degraded or nutrient-depleted soils, enhancing
microbial activity, and increasing overall agricultural output. Among the
reported advantages of biomineralization using basalt are:
– Restoration of nutrient-deficient soils
– Progressive reduction of soil acidity
– Improvement in soil aeration and structure
– Lower dependence on chemical fertilizers
– Enhanced seed germination
– Better root and shoot development
– Strengthened plant stems and bark
– Formation of a protective leaf film against pests and environmental stress
– Improved post-harvest durability
– Increased nutrient density in crops
Batista (2016) investigated the
effects of basalt powder applied in varying amounts, with and without
limestone. Treatments with added limestone showed higher potassium content and
elevated pH levels compared to those without. However, overall pH correction
was less effective than in treatments using limestone alone.
Hammerschmitt et al. (2021) emphasized that soil
re-acidification is a gradual process, and that superficial reapplication of
limestone is generally adequate for correction. Their study showed that both
surface application and incorporation of limestone produced similar soil
chemical conditions. Soybean responded positively, though modestly, to
reapplication (252 kg ha⁻¹ year⁻¹ average yield increase), whereas corn
exhibited minimal response.
Aluminosilicate minerals found in
rock dusts (RDs) include orthosilicates (e.g., olivine), inosilicates (e.g.,
pyroxenes like diopside, and amphiboles like hornblende), tectosilicates (e.g.,
orthoclase, plagioclase, nepheline, and leucite), and phyllosilicates (e.g.,
biotite and muscovite micas) (Calabrese et al., 2022; Swoboda et al., 2022; van
Straaten, 2006). While RDs can serve as an alternative to liming, they
typically exhibit lower acid neutralizing capacity (ANC) and a slower release
of alkalinity. Nonetheless, they provide essential nutrients such as calcium
(Ca), magnesium (Mg), potassium (K), phosphorus (P), and sulfur (S) (de Vries
et al., 2021; Ramos et al., 2022; Swoboda et al., 2022).
Supporting this, Swoboda, Döring,
and Hamera (2020) observed that specific modifications to silicate rock powders
(SRPs) can significantly improve their agronomic efficiency. Furthermore,
enhanced weathering of SRPs may contribute to atmospheric CO₂ sequestration,
while the silicon supplied through these amendments can bolster plant
resilience to both biotic and abiotic stressors.
More research is needed to
understand the use of silicate rock powders (SRPs) associated with limestone,
or with a chemical fertilizer or with animal manure, and in particular the
importance of the type of rock related to the type of soil and crop, in addition
to the quantity, as is very clear in figure 1 below.
Figure 1- Factors influencing the use of
silicate rock powders - SRPs (Swoboda Döringb & Hamera, 2022)
Bergmann and Holland (2014)
emphasize that when evaluating a rock for use as a soil remineralizer, it is
essential to analyze it using petrography—a technique that identifies minerals
and assesses their texture, crystallization sequence, grain size, and degree of
alteration. Additionally, any material applied to the soil must meet strict
criteria, particularly regarding the presence of harmful or potentially harmful
substances. These include toxic heavy metals, compounds that may lead to soil
salinization, or inert minerals—such as sodium and quartz—that could negatively
affect soil structure.
2. Best practices and lessons
learned from bio-dynamic agriculture
An effective alternative to
conventional industrial agriculture—which is increasingly criticized for its
over-reliance on mechanization, synthetic chemicals, herbicides, and its
disregard for ecological sustainability—is biodynamic agriculture. This approach
builds upon organic principles and extends them through a holistic, ecological,
and ethical framework that encompasses farming, gardening, nutrition, and
broader human-nature relationships. It promotes a lifestyle rooted in a deep
awareness of the landscape, personal development, and community engagement.
Biodynamic practices, as described
by Paull (2011), emphasize striving for energy and input self-sufficiency (in
fertilizers, seeds, and livestock), working in harmony with natural rhythms,
cultivating biodiversity, and approaching farm work with diligence, precision,
and mindful observation. Timeliness and attention to seasonal cycles are
central to the system.
Soil fertility management is
foundational in biodynamic farming. According to Campbell and Watson (2012) and
Raupp (2001), improvements are achieved through effective humus management,
including the use of well-fermented composts and manures, diverse crop
rotations, protection against erosion (e.g., windbreaks), cover crops, green
manures, and polycultures to promote interspecies support.
Boicean and Dent (2020) emphasize the
importance of alternating soil-depleting crops like corn, potatoes, and
cruciferous vegetables with soil-enriching legumes such as beans, peas, and
clover. Crop rotations should also alternate deep- and shallow-rooted species
and those requiring external nutrients with those that grow with minimal
inputs.
In alignment with these principles,
the FAO (2021) reported that sustainable agricultural practices, including
those within the biodynamic paradigm, can mitigate environmental degradation,
increase resilience to climate stressors, and progressively enhance soil and
land quality.
Potential for Rock Dust Use in
Roraima
An insightful study by Bergmann and
Holland (2014), as part of Brazil’s "Geodiversity of the State of
Roraima" program, assessed the potential for soil remineralization using
rock dust in the region. Their work delineated six geographic zones based on
soil diversity, topography, climate, and land use limitations.
The most promising zone for rock
dust application comprises areas dominated by mafic and ultramafic rocks
(diabase, basalt, and gabbro), where soils like red argisols,
red oxisols, vertisols, chernosols,
and nitisols prevail.
In Roraima, most soils are naturally
acidic and low in fertility, posing substantial barriers to conventional
agriculture. Although more fertile eutrophic soils exist, they are less
geographically widespread and often used with limited technological input,
relying heavily on empirical practices in rural and settler communities.
Additional constraints to
agricultural productivity include poor infrastructure, an underdeveloped road
network, lack of skilled labor, insufficient public investment, and a
burdensome tax regime. Despite these challenges, the region benefits from an
equatorial climate highly conducive to agriculture—often outperforming other
regions in Brazil.
Promoting sustainable agricultural
practices such as soil remineralization through rock dust represents a
strategic opportunity to enhance productivity, foster environmental
stewardship, support indigenous livelihoods, and drive inclusive economic
development.
Biodynamic agriculture offers a
compelling alternative to industrial farming, which is increasingly
unsustainable due to its overuse of machinery, chemicals, herbicides, and
neglect of environmental impacts. Going beyond organic farming, biodynamic
agriculture takes a holistic and ethical approach to food production. It
emphasizes the interconnectedness between people, land, and nature, focusing on
ecological balance, personal awareness, and community involvement.
As outlined by Paull (2011), common
biodynamic practices include achieving self-sufficiency in energy, fertilizers,
and livestock; aligning work with natural rhythms; using diverse plant and
animal systems; and maintaining precision, observation, and timeliness in
farming tasks.
According to Campbell and Watson
(2012) and Raupp (2001), healthy soil in biodynamic systems is maintained
through composted organic materials, crop rotation, soil protection (e.g.,
windbreaks), and the use of mixed cropping instead of monocultures. Boicean and Dent (2020) also recommend alternating
nutrient-depleting crops (e.g., corn, potatoes, cabbage) with enriching ones
(e.g., legumes) and balancing shallow- and deep-rooted crops to sustain soil
fertility.
The FAO (2021) confirms that
sustainable farming practices like biodynamics can protect ecosystems, improve
food resilience in the face of climate change, and improve soil health over
time.
In Roraima, the potential for
applying rock dust as a soil amendment was analyzed in a key study by Bergmann
and Holland (2014), under the broader “Geodiversity of the State of Roraima”
initiative. The study identified six distinct land zones, with the most
suitable for rock dust use being areas with basic rocks like basalt, gabbro,
and diabase. These regions feature red oxisols, argisols,
and other weathered tropical soils.
Roraima’s soils are mostly acidic
and nutrient-poor, limiting agricultural productivity. Eutrophic soils with
better fertility exist but are less widespread and often managed with low-tech
methods in isolated rural zones. Compounding this are challenges like poor
infrastructure, limited labor skills, and lack of government investment.
Nonetheless, Roraima’s favorable
equatorial climate gives it a competitive edge for crop performance compared to
other parts of Brazil. Applying sustainable methods such as remineralization
with rock dust could address many challenges—boosting yields, improving soil
health, supporting indigenous agriculture, and promoting regional
sustainability.
In Roraima, agriculture is mostly
practiced in the La Sabana region. According to Júnior and Schaefer
(2010), the dominant soils here include several types of canosols
(yellow, red-yellow, and red), argisols (red
and yellow-red), and neosols (hydromorphic,
organic, fluvic, and litholic). These soils typically
have low fertility, with high acidity, low base saturation, and weak nutrient
retention. Exchangeable phosphorus is especially low, so regular pH correction
is needed for successful farming.
The most fertile agricultural soils
in the state are found in areas with basic rock formations:
· The Pedra Preta sill in the Uiramutã region,
·
Apoteri volcanic rocks near Serra de Nova Olinda,
and
· The Taiano
area, known for its fertile basalt-derived soils.
· Top sites include:
· Vila do Taiano
(northwest Roraima),
·
Serra de Nova Olinda (central
Roraima), and
· Near Flechal,
an indigenous village in Uiramutã.
In these areas, soils formed from
weathered basalt and other basic rocks—such as oxisols, chernosols,
and organic soils—are rich in nutrients. In the Pedra Preta sill, rocks like
diabase, diorite, and gabbro contribute to fertile soils such as nitisols,
found in hilly forested areas.
A diabase rock sample from the Taiano region (Alto Alegre municipality), shown in Figure 1,
gave a strong positive reaction in the phosphomolybdate test, confirming its
potential as a phosphorus-rich soil amendment.
In addition to the municipality of
Alto Alegre, in the municipality of Iracema, the presence of rare earth
minerals, niobio, barium and phosphate are cited.
In Brazilian family farming, farmers
often combine rock powders with organic waste, like animal manure and green
fertilizers, to improve soil health. These inputs are usually made on the farm
through composting, using microorganisms to help release nutrients. Nitrogen is
typically supplied by planting green manure species, especially Tithonia diversifolia (Mexican sunflower), which can add up to
4.3% potassium through its leaves and stems (Palm et al., 1997 apud van
Straaten, 2007). To get the best results, it’s important to understand that
rock powder interacts with the entire soil system, including soil microbes and
the specific ways that plant roots absorb nutrients (Mundstock, 2013).
Studies show that rock dust can be
used on most crops and applied in grain sizes between 0.105 mm and 4.0
mm—similar to how lime is applied—either by hand or with machinery. Recommended
doses range from 0.5 to 8 tons per hectare depending on the soil and crop. In
Brazil, basalts and diabases from the Serra Geral
region are promising for use in agriculture. These rocks are rich in calcium,
magnesium, and iron and are often already available in powder form from
quarrying. Because their minerals break down more easily, they can release
nutrients relatively quickly when ground to the right size.
Alkaline volcanic rocks, which have
high potassium content and fine crystal structures, are also excellent for soil
remineralization. So far, only one rock—phonolite from Poços
de Caldas—has been officially approved in Brazil as a local replacement for
imported potassium chloride (KCl) fertilizer (Cortes et al., 2009). Still, it’s
essential to test these rocks for micronutrient levels and any potentially
harmful elements (Bergmann & Holland, 2014).
Brazil’s Dependence on Imported
Fertilizers
Rock powders provide a wider variety
of nutrients than most chemical fertilizers. In addition to the main nutrients
(P, K, Ca, S, Mg), they can supply important micronutrients like Zn, Cu, Fe,
Mn, Mo, B, Co, and Ni—depending on the rock type. On the other hand, standard
fertilizers usually offer just N, P, and K, and only some newer products
include Ca, Mg, or micronutrients like B and Zn. However, these highly soluble
fertilizers often lose nutrients quickly in Brazil’s hot, rainy climate.
de
Figure 4 - Production andmand
graph of fertilizers in Brazil. Adapted from Martins (2013). Source: ANDA
(2011). Mbagro Project.
Goulart et al. (2023) report that
the Novos Campos region in Roraima contains magmatogenic phosphate deposits linked to the
anorthosite-manager-chanockite-shanite
(AMCG) rock association. There are also magmatic-hydrothermal phosphate
minerals and rare earth elements tied to alkaline volcanic complexes. The gabroanorthosite units of the AMCG Mucajaí
group have the highest phosphate potential in the area.
Brazil’s heavy reliance on imported
fertilizers makes it vulnerable to international market changes like currency
fluctuations, trade policies, and shipping delays. These factors can disrupt
the steady supply of fertilizers essential for farming, which risks
agricultural production and food security. Fertilizer imports require
long-distance transport and solid infrastructure for storage and distribution,
which drives up costs and ultimately increases prices for farmers. Taxes on
fertilizer imports, such as ICMS, add to these costs and lead to higher food
prices for consumers.
To address this, the Brazilian
government launched the National Fertilizer Plan (PNF) in November 2022. This
plan aims to reduce dependence on fertilizer imports and guide the fertilizer
sector through 2050. Despite this, many farmers remain hesitant to adopt
biodynamic or homemade fertilization methods. Small farmers often lack
education on these practices, while medium and large farms continue relying on
imported chemical fertilizers.
There is also a gap in laws and
government support for easier farmer access to alternative fertilizers, like
rock dust, and for developing infrastructure such as rock crushers. More
support is needed for soil studies and sharing scientific research from agencies
like Embrapa and the Geological Service of Brazil.
Brazil’s Law No. 12,890 (2013)
regulates the production and marketing of fertilizers, soil amendments,
inoculants, biofertilizers, and remineralizers. Regulatory Instruction No. 39
(2018) sets detailed rules for mineral fertilizer registration, labeling, and
advertising.
Recently, the Ministry of
Agriculture (MAPA) standardized rules for producing and selling remineralizers
(rock dust), which improve soil quality differently from regular fertilizers
mainly due to lower solubility. With these new rules, farmers can now verify
product quality through official registration. The regulations published in
June 2023 (Instructions 5 and 6) require manufacturers to meet strict
standards, ensuring consistent and safe products.
This regulation opens up new options
for farmers, especially organic growers who avoid mineral fertilizers but
accept rock dust. It addresses a long-standing demand and is recognized in the
Official Gazette as a valuable alternative for soil fertility restoration.
3. The Culture – Knowledge-
Intelligence model
According
to Kroeber (1949), humans differ from animals primarily because of culture.
Culture allows humans to surpass their biological limits by accumulating
experiences over time, creating a shared legacy.
Culture, more than genetics, guides
behavior and influences human actions.
Humans develop and age according to
cultural norms, as many instincts have weakened through long evolutionary
changes.
Culture is a cumulative process
formed by the historical experiences of past generations, which can either
limit or encourage an individual’s creativity.
Based on these ideas, the
Culture-Knowledge-Intelligence (CCI) model was created (see Figure 3). Its main
points include:
(i)
Culture consists of a society’s beliefs, values, assumptions, and traditions
(Schein, 2010).
(ii) For education to be effective, curricula should be restructured around
four learning pillars: knowing, doing, living together, and being (Smith,
2018).
(iii) Intelligence depends on three pillars: prediction, strategy, and action
(Rothberg & Erickson, 2004).
Figure 5. THE CULTURE-KNOWLEDGE-INTELLIGENCE
MODEL (adapted from Choo, 1998)
The CCI model is based on three
hypotheses (Table I):
Table I. Assumptions of the CCI model
|
Hypotheses |
Sources |
Results |
|
Cultural has a positive impact
on Knowledge |
Leidner et al. (2006), Deal and Kennedy (1982) and Tweed and Lehman ( 2002) suggest that the way in which individuals
perceive, organize and process information and the way in which they
communicate with others and the way in which understand, organize and
generate knowledge and solve problems, is related to culture. |
SUPPORTED |
|
Cultural has a positive impact on intelligence |
Culture, more than genetics, determines behavior and determines its
actions (KROEBER, 1949). Umuteme et
al.(2023) posit that factors such as values, norms, beliefs and practices
embedded in organizational culture significantly shape the overall project
environment and affect team dynamics. |
SUPPORTED |
|
Knowledge has a positive impact on intelligence |
Rothberg and Erickson (2004) maintain that knowledge is static and,
ultimately, only has value if people use it (intelligence) |
SUPPORTED |
4. Bio-dynamic AGRICULTURE MODEL
Thanks to their ability to create
and share collective knowledge, cooperatives have made significant
contributions to local and national development. Silva et al. (2006) found that
60 agricultural cooperatives increased their profits by 130%.
Cooperatives exist in many sectors,
such as agriculture, health, credit, transport, and education. Of these,
agriculture is the most developed and widely recognized sector both nationally
and internationally.
Rural cooperatives play a key role
in building social capital by uniting cooperative members and the surrounding
community in common efforts.
Figure 4 presents the Bio-dynamic
family farming model.
Figure 4: Bio-dynamic family farming model. Fuente: Author, 2024
The Bio-dynamic agriculture model
shows that agricultural cooperatives are central to this farming system. For
farmers to unite and solve their problems, there must be a culture that
welcomes training, especially on fertilizers, as discussed earlier. Training
focused on rock dust application is a key foundation for developing and
sustaining Bio-dynamic agriculture.
Additionally, this model
demonstrates that cultural changes among small family farmers positively affect
knowledge management within cooperatives and help develop and implement the
Farmers' Technical and Financial Assistance Plan, representing the intelligence
component.
Conclusions
Bio-dynamic agriculture depends on a
mature culture that encourages farmers to create farm-based solutions using
natural resources. This article reviewed literature on rock dust and biological
nitrogen fixation and proposed two connected models: the Culture-Knowledge-Intelligence
model and the Bio-dynamic Agriculture model based on cooperative knowledge
sharing.
The study found that more research
is needed to address challenges related to dissolving silicate rock powders in
crops, including the material’s quality and quantity, and the possibility of
mixing it with limestone, manure, or chemical fertilizers.
This work happens in a cooperative,
collaborative setting between farmers and researchers, highlighting how
important it is to understand culture’s role in managing knowledge and
intelligence to build a strong culture that applies useful knowledge.
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