Meliponiculture in agroforestry systems in Belterra, Pará, Brazil
Meliponicultura em sistemas agroflorestais em Belterra, Pará
Meliponicultura en sistemas agroforestales en Belterra, Pará, Brasil
Ana
Paula da Silva Viana1, Daniela Pauletto2,
João Ricardo Vasconcellos Gama3, Adcléia
Pereira Pires4, Hierro Hassler
Freitas Azevedo5, Aline Pacheco6
1Engenheira
Florestal, Estagiária Voluntária no Instituto Chico Mendes de Conservação da
Biodiversidade, Santarém, Pará, anastm.paula@gmail.com; 2Mestre
em Ciências de Florestas Tropicas e Professora no Instituto de Biodiversidade e
Florestas, Universidade Federal do Oeste do Pará, Santarém, Pará, daniela.pauletto@ufopa.edu.br; 3Doutor
em Ciência Florestal e Professor no Instituto de Biodiversidade e Florestas,
Universidade Federal do Oeste do Pará, Santarém, Pará, jrvgama@gmail.com; 4
Mestranda
em Ciências Ambientais, Universidade Federal do Oeste do Pará, piresadcleia@gmail.com; 5Bacharel em produção animal, Instituto
de Biodiversidade e Florestas, Universidade Federal do Oeste do Pará, Santarém,
Pará, hierroazvdo@gmail.com, 6Doutora em Ciência
Animal e Professora no Instituto de Biodiversidade e Florestas, Universidade
Federal do Oeste do Pará, Santarém, Pará, alinepacheco@outlook.com
Recebido: 01/05/2020;
Aprovado: 23/11/2020; Publicado: 10/02/2021
Resumo: O objetivo do estudo
foi caracterizar a produção meliponícola em sistemas
agroflorestais e realizar um levantamento de espécies vegetais indicadas pela
visitação por abelhas sem ferrão no município de Belterra,
Pará. A pesquisa foi realizada a partir de um questionário aplicado a meliponicultores
com questões que abordaram aspectos socioeconômicos e da produção de abelhas
sem ferrão. Em relação ao pasto meliponícola foram
investigadas as espécies vegetais apontadas como visitadas pelas abelhas. Destaca-se que 15% dos criadores tem como
principal atividade econômica a meliponicultura e 54%
vivem com 1 ou 2 salários mínimos. O tempo na
atividade de meliponicultura apresenta amplitude de 2
a mais de 40 anos. Os entrevistados afirmaram se dedicarem à meliponicultura pela afinidade com a atividade e pela
consciência na importância das abelhas para o meio ambiente. Os
meliponicultores apontaram que os maiores entraves enfrentados estão
relacionados ao desmatamento e ao uso de agrotóxicos o que, segundo os mesmos, implica na redução na produção do mel, principal
produto comercializado. Observou-se que os sistemas agroflorestais (SAFs) onde estão inseridos os meliponários
apresentam, segundo os entrevistados, 38 espécies florestais distribuídas em 21
famílias botânicas. Predominaram as
espécies frutíferas, características de floresta primária e secundária, o que
poderá indicar potencial para introdução em quintais agroflorestais ou outros
sistemas consorciados minimizando os custos de implantação e manutenção de meliponários.
Palavras-chave: Quintais agroflorestais; Pasto meliponícola;
Agricultura urbana.
Abstract: In this study we characterized
the honey production in agroforestry systems and inventing the
species visited by stingless bees in the region of Belterra, Pará. We used a
questionnaire applied to honey producers with questions that addressed socioeconomic
conditions and the production of stingless bees, as well the plant species visited
by bees. Fifteen percent of bee breeders have meliponiculture
as their main economic activity and 54% live of 1 or 2 minimum wages. The time
in meliponiculture activity ranges from 2 to over 40
years. According to the interviewees, they dedicate themselves to meliponiculture due to their affinity with the activity and
their awareness of the environmental importance of the bees. The greatest
obstacles cited was the deforestation and the use of pesticides, which,
according to them, implies a reduction in the production of honey, the main
product sold. The agroforestry systems (SAFs) where the meliponaries
are inserted present, according to the interviewees, 38 forest species
distributed in 21 botanical families. Fruit species predominated,
characteristics of primary and secondary forest, indicating potential for
introduction into agroforestry yards or other intercropped systems, minimizing
the costs of implanting and maintaining meliponaries.
Key-words: Agroforestry yards, Meliponic
pasture; Urban agriculture.
Resumen: El
objetivo del estudio fue caracterizar la producción de miel en sistemas agroforestales y
realizar un relevamiento de
especies vegetales
indicadas por visitación de abejas
sin aguijón en el municipio
de Belterra, Pará. La investigación
se realizó a partir de un cuestionario aplicado a productores
de miel con preguntas que abordaban aspectos condiciones socioeconómicas y producción de abejas sin aguijón. En
cuanto al pasto melipónico,
se investigaron las especies vegetales identificadas
como visitadas por las abejas.
Es de destacar que el 15% de los
ganaderos tienen la meliponicultura como su principal
actividad económica y el
54% vive con 1 o 2 salarios
mínimos. El tiempo en la actividad meliponicultural
varía de 2 a más de 40 años.
Los entrevistados manifestaron que se dedican a la meliponicultura
por su afinidad con la actividad
y su conciencia de la importancia de las abejas para el medio ambiente. Los
meliponicultores señalaron que los
mayores obstáculos que enfrentan
están relacionados con la deforestación y el uso de pesticidas, lo que, según ellos, implica una reducción en la
producción de miel,
principal producto vendido. Se observó
que los sistemas agroforestales
(SAF) donde se insertan los
meliponarios presentan, según los entrevistados, 38 especies forestales distribuidas en 21 familias botánicas. Predominaron las especies frutales,
características de bosque primario y secundario, lo que puede indicar potencial de introducción
en patios agroforestales u otros sistemas
intercalados, minimizando los costos
de implantación y mantenimiento
de meliponarios.
Palavras claves:
Patios agroforestales; Pastos
melipónicos; Agricultura urbana.
INTRODUCTION
The western of Pará
has undergone changes in landscapes with the expansion of the agricultural
sector, mainly linked to the paving of the Cuiabá-Santarém
Federal Highway (BR - 163), one of the main frontiers for the expansion of agribusiness.
In the region, as well as in a considerable portion of the Amazonian territory,
there was a reduction or suppression of forests, generating the occurrence of
mosaics. The mosaics are based on a defined previous itinerary, followed by
forest exploitation with clear cutting, burning, and implantation of pastures
for breeding animals for slaughter, as well as the spread of mechanical crops
such as soybeans (LOUREIRO; PINTO, 2005; SILVA et
al., 2016).
In the area of Belterra, the production system
of high technological level provided the rapid growth of production based on
monoculture plantations such as rice, corn and
soybeans, which negatively affected the landscape of the region, and caused the
forest fragmentation (VENTURIERI et al., 2007). In 2010, 6.2% (27,274 ha of
planted area) of Belterra territory was occupied by crops, especially
monocultures, such as rice, soybeans and corn (DEEPAST, 2020).
The unrestrained
expansion is impacting family production systems and has been an obstacle for extractivists and small animal producers, such as bee, that
are susceptible to forest fragmentation and intensive use of pesticides (RAYOL;
MAIA, 2013). Among the species susceptible to these kind of
disturbances, the bees of the Meliponini tribe
can nest and forage in anthropized environments, however, they prefer
environments with greater plant diversity, availability and diversification of
food, being Meliponini tribe more diverse in these
environments (WINFREE et al., 2009). In these environments there is a
mutualistic relationship, through pollination (collection of nectar and pollen;
cross-fertilization) that benefits both bees and plants. Bees and vegetables
are intrinsically linked, that is, the loss of pollinating bee species, can
lead to the plant species extinction (SANTOS, 2010).
The availability of
nesting sites also contribute to maintaining the
diversity of bees in areas subjected to human pressure (SILVA et al., 2012). Therefore,
the knowledge of the species used as meliponic
pasture, plant species that provide nectar and pollen for the maintenance of
the colony and production of honey and other derivatives (SILVA; PAZ, 2012), is
essential for conservation actions and production of honey and other
by-products and services.
Characterizing meliponiculture exercised by breeders in the region of
Belterra and provide information is important to support the creation of
consortium systems that provide foraging, meliponiculture
and multiple use, providing resources for bees with low cost of implantation
for producers, also contributing with conservation strategies. Therefore, the
present study aimed to characterize honey production in agroforestry systems by
conducting a survey of plant species visited by stingless bees in the
municipality of Belterra, Pará.
MATERIAL AND METHODS
The study was carried
out in the area of Belterra, state of Pará, Brazil, in
13 agroforestry systems. The systems consisted of urban and peri-urban
perimeter, that is, the surroundings of the urban area with a predominance of
agricultural activities by the residents. We applied semi-structured questionnaires
to 13 meliponicultors, owners of the meliponiculture. Ten are located in
agroforestry yards, in the urban perimeter, and three in other agroforestry
systems located in areas of family farming production, at a distance of at
least 5 km from the residence, and adjacent to native forest areas.
As a criterion for
data collection, we identified and interviewed the producers that remain
exercising the activity of meliponiculture, by handling
and extracting the honey or other products and that worked in the central area
of the municipality or in the urban perimeter margins.
We adopted the snowball methodology (BAILEY, 1994),
sampling from January 2017 to January 2018. The questionnaire covered questions
about socio-economic profile of honey farmers, survey of honey pasture by the
indication of species visited by stingless bee species (SBS) and beekeeping
productivity data of SBS (years 2016 and 2017). The challenges and objectives
of creating SBS, the technical assistance received and training in the area of meliponiculture
were also investigated.
In the section on meliponic pasture, the interviewees pointed out, from
personal observations, the popular names of the plant species visited by the
SBS. The identification of these species was carried out with the support of
technicians from the Federal University of the West of Pará with para-botanical
knowledge and extensive experience in botanical identification. Subsequently, we
carried out a bibliographic survey of the scientific names of the species, as
well as their botanical families and use.
Meliponicultors had previously information
about the scientific names of SBS, which were identified by researchers from Embrapa. All interviews read a consent form for the
research and signed it. For data analysis, we used descriptive statistics for
the quantitative and qualitative interpretation of the results, and
identification of central tendency measures.
RESULTS AND DISCUSSION
Among the main
economic activities of SBS breeders in the municipality of Belterra - PA, are
agriculture (23%) and freelancers (23%) (Figure 1). For 15% of the meliponiculturists in Belterra, meliponiculture
is the main economic activity, also verified by Pinto (2012) in a study of the
profile of meliponiculturists in Belterra in 2010. Meliponiculture is a complementary activity in many regions
of Brazil, and agriculture is in most of the time, the main source of income
for honey farmers (MAGALHÃES; VENTURIERI, 2010).
Figure 1. Main sources of income of stingless bee producers in
the municipality of Belterra, Pará.
Most meliponicultors (69%) are over 50 years old (Table 1),
which corroborates Pinto (2012) and Siqueira (2014) who also found that most meliponiculturists are over 50 years old. We also found
that the meliponicultors have been engaged in the
activity for more than 10 years (38%), 38% exercise the activity for less
than ten years, 8% are in the activity for over 20 years, and two of the
largest meliponicultors in numbers of colonies (15%),
have been carrying out the activity for more than 40 years. Meliponiculture
is a traditional activity in the study region, carried out a long time ago, by
the original peoples (RAYOL; MAIA, 2013), which may explain the execution of
the activity for more than 40 years by 15% of the interviewees.
Most of the meliponiculturists in Belterra have only elementary (15%)
or high school (46%) and 8% higher education. Regarding the monthly family
income, 54% receive from 1 to 2 minimum wages, those who receive more than 5
minimum wages (23%) are retired civil servants and traders (Table 1).
Table 1. Socioeconomic profile of stingless bee producers in Belterra, Pará. |
||
Variable |
Total respondents |
|
N. |
% |
|
Age range |
||
from 30 to 39 years |
2 |
15 |
from 40 to 49 years |
2 |
15 |
More
than 50 years |
9 |
69 |
Scholarship |
||
High
school |
6 |
46 |
Incomplete elementary school |
4 |
31 |
Complete
elementary school |
2 |
15 |
Higher education |
1 |
8 |
Family income |
||
Less than 1 wage |
1 |
8 |
1
to 2 wages |
7 |
54 |
2
to 3 wages |
1 |
8 |
3
to 5 wages |
1 |
8 |
More
than 5 wages |
3 |
23 |
Gender |
||
Male |
13 |
100% |
Meliponicultors generally inspect
the colonies once a week, but some said they were engaged in the activity
daily. Pereira et al. (2010) recommend the review of colonies at least every 30
days to check if they are moldy, with the presence of offspring and queen,
availability of food, presence of natural enemies and garbage that are
indicators of colony health.
Costa et al., (2012),
studying meliponiculture practiced in traditional
communities of Parintins/AM, observed that the
breeders who inspected the colonies at least once a week had stronger and more
vigorous colonies than those whose inspection was rare, which they were weak or
abandoned their nests.
The creation of SBS
generally occurs in line with other activities for 38.5% of the population,
such as poultry (80%) or other small animals (20%). Barth (2004) and Costa et
al., (2012) affirm that bees can collect material of fecal origin and,
therefore, the proximity of the meliponaries to the
breeding of small animals, such as poultry and pigs, is not recommended as contamination
of the produced honey.
In 69.2% of the
properties there is occurrence of native forest in the vicinity of the meliponary, within a radius of approximately 3 km, a
determining factor for honey production. According to Silva and Paz (2012),
each bee species has a different flight capacity (600 to 2,400 meters) varying
according to body size. Although there is native forest in the vicinity of the
studied meliponaries, the size of the vegetated areas
was not specified here.
According to the producers, 76.9% learned how
to manage bees without technical assistance, however, 54% of them participated
in courses on SBS creation offered at different events or they looked for
courses by themselves.
The majority of respondents (42%)
pointed out that they create SBS to obtain products for sale. However, 29%
stated that they exercise the activity only as hooby
and for 29% the creation of bees aims to obtain honey for their own
consumption. In addition, 46% of meliponicultors sell
honey, which is the main product sold. When asked about the sale of other
products, 43% stated that they sell “samburá”, “cerumen”
(29%) and “propolis” (28%).
Honey was the first
SBS product to be explored by man due to its nutritional and medicinal value,
which is why the product is still valued by many populations today
(CORTOPASSI-LAURINO et al., 2006; MELO et al, 2010). Gehrke
(2010) observed that those producers who practice meliponiculture
as a hobby are apt to be effective meliponicultors.
Regarding the
breeding stock, 82% of the breeders multiply their colonies to increase
production. Of these, 62% sell
the new colonies to other producers.
The price of honey is
different for species that have recognized medicinal value by the population.
In the case of the jataí species (Tetragonisca sp.), whose honey is
indicated for the treatment of cataracts, its value reaches R$ 200.00 kg-1. SBS honey has anti-inflammatory and healing
properties attributed to the habit of collecting resins with medicinal
properties. SBS honey also has a different characteristic from that of Apis melifera,
with no sucrose in its composition (SANTOS, 2010; LIMA and NOGUEIRA, 2017).
However, scientific studies with SBS are still very incipient when compared to
studies related to Apis melifera, as
well as the lack of development of appropriate technologies (SILVA and PAZ,
2012; SANTO et al., 2016).
The main problems
faced by SBS producers were deforestation, reported by 42% of respondents, and
the use of pesticides in the surrounding crops, for 34% of meliponicultors.
The impacts of deforestation were studied by Brown and Oliveira (2014) who
found in recent studies in the Amazon, a significant relationship between
deforestation and the reduction in the richness of stingless bee species,
revealing the important to discuss the advances of agribusiness in the region
and their impacts on economic activities traditionally performed by the peoples
of Belterra.
Freitas and Pinheiro
(2010) report that the attractiveness of flowering poisoned by pesticides is
the main reason for the death of pollinators (lethal effect). However, even low
doses, lower frequencies of use and even flowers affected by the pesticide
drift effect, that is, flowers close to the areas of application contaminated by
air, can cause side effects reducing the vigor of the colony. According to the
authors, in large areas of crops such as soybeans and corn, with a single
application of a large amount of pesticides, the
impact on bees may be more severe, because of the huge amount of poison
released into the environment in a short time.
Meliponiculturists
interviewed also cited as challenges the influence of seasonality in production
(8%), since flower production is also conditioned by seasonal conditions, and
the lack of technical training, pointed out by 4% of producers. All interviewed
breeders claim not to receive continuous and permanent technical assistance
from government agencies or private institutions, do not market their products
with labels and do not have organic certification.
The
incipient legislation was reported by 8% of the interviewees as another
bottleneck for the consolidation of the activity, while the low availability of
places with meliponic pasture that offer security for
the installation of colonies was cited 4% of the meliponicultors.
The frequent thefts of colonies reported by the interviewees makes impossible
to install the meliponaries in remote areas. The
CONAMA resolution No. 346, of June 6, 2004, provides guidelines for the
implementation of the activity, although it is necessary laws that regulate the
activity at the state level considering regional characteristics.
Barth (2004) pointed
out the advance of deforestation, use of pesticides, vandalism in rational
creations as challenges to be overcome by meliponiculture.
The author also cited as a limiting factor the lack of standardization in
production, linked to the limitation in specific legislation for the sector.
These obstacles generate discrepancies in the form of collection and packaging
of SBS products leading to greater or lesser care, contamination
or alteration of the quality of the product and, consequently, loss of
credibility in the market.
Agroforestry yards
are suitable spaces for the creation of ASF for the safety of the colonies and
the possibility of developing the activity together with the family. These
spaces form true refuges for pollinators, mainly bees, and the creation of
these in agroforestry yards provides important sources of foraging,
contributing to the preservation of these species (FERNANDES et al., 2009;
IMPERATRIZ-FONSECA et al., 2012).
The producers
revealed that despite the difficulties encountered in the creation, they are
very fond of the activity and do not intend to abandon it. Another determining
factor for maintaining the activity for so long is the ecological awareness
that the interviewees have, since they all cited the importance of bees for the
maintenance of the forest and of the man himself. This conservationist attitude
of the breeders was also observed by another study (MEIRELES et al., 2018).
Most producers are
owners of the site (84.6%) and 15.4% maintain the beekeeping in partnership
with other meliponicultors because they do not have
enough pasture on their properties or do not have enough time to inspect the
SBS colonies.
We found eight species
of stingless bees present in the meliponaries, the
most frequent being Jataí, occurring in 10 yards and
totaling 49 colonies (Table 2). However, the largest population found was Scaptotrigrona sp.
with 814 colonies in 8 yards. Species of this genus generally have a good honey
production and are easy to handle due to their low defensive behavior (COSTA et
al., 2012).
Table 2. Species, occurrence and number
and percentage of colonies counted of stingless bee breeding in the urban
area of Belterra, Pará. |
||||
Popular
name |
Cientific
name |
Occurence* |
Nº
Colonies |
%
Colonies |
“Jataí” |
Tetragonisca
angustula |
10 |
49 |
5,0 |
“Canudo” |
Scaptotrigona
aff. xanthotricha |
8 |
814 |
83,4 |
“Jandaíra” |
Melipona
interrupta |
6 |
18 |
1,8 |
“Cacho de uva” |
Frieseomelitta
longipes |
6 |
36 |
3,7 |
“Jataí mirim” or “mosquito” |
Plebeia mínima |
5 |
27 |
2,8 |
“Uruçu amarela” |
Melipona
flavolineata |
4 |
10 |
1,0 |
“Uruçu cinzenta” |
Melipona
sp |
2 |
2 |
0,2 |
“Uruçu boca de renda” |
Melipona
semingra |
2 |
20 |
2,0 |
*Number of yards in which they
occur |
The products produced
from the species of the genus Melipona are widely used by populations, both in
food and medicinal use and when well
managed, they can have their production optimized for about 1L of
honey/colony/year (COSTA et al., 2012).
The species Melipona seminingra
is considered endemic to the Belterra region, according to the survey carried
out with the producers. It is a subspecies, which in Belterra has an orange
thorax and the first abdominal segment is lighter than the subspecies M. seminigra perningra occurring in the eastern portion of the
Amazon (VETURIERI, 2009).
The species Frieseomelitta longipes,
according to local producers, has great potential due to the different flavor
of honey, although its colony production is inferior to the “canudo” species, considered as the most productive of the
listed species. However, based on the reports from the producers, the “caho de uva” species is
identified as the largest producer of propolis. F. longipes was identified by Cordeiro
and Menezes, (2014) as a good producer of pure resine
propolis.
Species of the genus Scaptotrigona (Canudo), found in
the Belterra region, are largely bred by small farmers in various regions of
the country, who even have meliponaries with more
than 200 boxes and with a record of productivity above 8 liters/box/ year
(LOPES et al., 2005). In the present study, the largest population of “canudo” found corresponded to 300 colonies distributed over
an area of 6,250 m2.
The type of modular box was the most frequent among producers (42%),
followed by the “Porronca” model, with 32% of the
options (Figure 2). There are places where there is more than one box model on
the property, therefore, the quantity presented is related to the number of
yards that have such models and not to the number of boxes installed in
Belterra.
Figure 2. Percentage of option
by type of stingless bee box found in the areas of honey producers in Belterra,
Pará.
As for the structure
of the boxes, the modular one has a nest, over-nest
and beehive (Figure 3A and 3B), which presents advantages in the time of the
multiplication of the swarms as ease of removal of the brood discs, and
separate compartment with the necessary supply for temporary feeding of the new
colony. In addition, this type of box is indicated to improve the development
of the swarm, increase the production of honey and
provide welfare to the bees (LIMA; NOGUEIRA, 2017).
Producers usually
test new models of boxes according to the technical and empirical knowledge
acquired over the years of creation. Among the new models, the round box stands
out (Figure 3C), which is similar to the natural
nesting of bees established in the trunk of trees and is in the experimental
stage of use.
The "porronca" or "cabocla"
(Figure 3D) has a more simplified structure, without compartments, has as the
main advantage the possibility of expanding the nest due to the availability of
space. However, the producers reported that this model presents difficulty at
the time of nest multiplication, since the absence of compartments in the box
structure limits the partial removal of the daughter colony without causing
damage to the remaining colony.
Figure 3. Modular box (A and B) and round box (C) and “Porronca”
(D) models used in Belterra, Pará.
Source: Personal archive,
2017.
The average honey
production per colony/year was 3.0 to 3.1 L ± 0.5. According to Maia-Silva et
al. (2016) the size of the foraging area directly influences the amount of food
sources, on the other hand, botanical varieties are important, as the SBS will
be able to choose according to preference.
The honey collection is carried out in the least rainy period of the
year, just after the end of the blooms. This product is first removed in
containers, then filled in the packaging, usually glass or plastic bottles, and
stored in the refrigerator or at room temperature.
Analyzing the honey
production in 2016, 34% of the producers extracted 60 to 90 L, and 11% of them
extracted 1,000 L in the same period, which may suggest that productivity is
related not only to the number of colonies, but also with the availability of meliponic pasture. However, in 2017, the majority (67%) of
producers were unable to commercialize honey because the colonies did not
produce enough for the harvest and only 17% managed to obtain more than 50 L of
production (Figure 4), and of these 23% reported who lost colonies due to the
death of bees or abandonment of the colony.
Figure 4. Production of honey from stingless bees by meliponary
per year, in the municipality of Belterra, Pará.
Two producers who
owned more than one hundred colonies reported that they were giving up the
activity with a commercial bias and that they would continue with few boxes due
to their affinity with the creation and conservation of these. The reason for
the withdrawal reflects the difficulties faced, as the increase in the
production of these has come up against the lack of meliponic
pasture, since the forest areas in the region are becoming fragmented and the
producers report the death of many swarms.
The analysis of the
dynamics in the landscape in Belterra over 13 years, through analysis of
satellite images by the Normalized Difference Vegetation Index (NDVI),
concluded that there were significant changes in vegetation, mainly due to the
increase in anthropized areas, which implies in loss of habitat and resources
for various components of fauna, including bees (CORRÊA et al., 2011).
The use of pesticides
in the vicinity of the meliponaries has been cited by
producers as a preponderant to swarm deaths, becoming yet another obstacle in
production, especially in peri-urban areas. In their studies Venturieri (2009) warned that in the medium term, the
exploitation of trees with diameters over 50 cm would affect the density of
stingless bees, causing low reproduction of tree species intrinsically
dependent on these pollinators.
The plant species in
the meliponaries and surroundings, identified by the
producers as meliponic pasture, were 39 forest species
typical of both primary and secondary forest (Table 3). These species belong to
21 different families, some of which are spontaneous
and others have been introduced into the system to enrich the vegetation.
The average of plant
species present in the meliponarios was approximately
12 species ± 8, with a maximum of 24 species, found in a yard of one hectare,
while the lowest riches were found in 3 yards with a size of 2 ha and 0.5 ha.
Table 3. List of species, botanical families and visitation by stingless bee
species, according producers in Belterra, Pará. |
|||||
Popular name |
Cientific name |
Botanical Family |
Use |
Visitation by species of SBS** |
Flowering period |
“Tatapiririca” |
Tatapirira guianensis
Aubl. |
Anacardiaceae |
Wood Reforestation |
All |
Jun
to Sep |
“Cajarana” |
Cambrela canjerana |
Anacardiaceae |
Food |
Jataí |
No information |
“Taperebá” |
Spondias mombin
L. |
Anacardiaceae |
Food |
Trigona Jataí |
Aug
to Nov |
Mango |
Mangifera indica L. |
Anacardiaceae |
Food |
Canudo Jataí |
No information |
“Sucuuba” |
Himatanthus sucuuba (Spruce ex Mull. Arg.)
Woodson |
Apocynaeae |
Wood |
N.I |
Apr
to Jul |
“Marupá” |
Simarouba sp
Aubl. |
Araliaceae |
Wood |
N.I |
No information |
“Açaí” |
Eutherpe oleraceae
Mart. |
Arecaceae |
Food |
Jataí Canudo |
Feb
to May |
“Bacaba” |
Oenecarpus bacaba Mart. |
Arecaceae |
Food |
N.I |
Jun
to Oct |
“Pupunha” |
Bactris
gasipaes (Kunt) |
Arecaceae |
Food |
N.I |
No information |
“Urucum’ |
Bixa
orellana L. |
Bixaceae |
Food |
N.I |
No information |
“Piquiá” |
Caryocar brasiliensis (Aubl.) Pers. |
Caryocaraceae |
Wood Food |
N.I |
Aug
to Oct |
“Pau ferro” |
Libidibia férrea (Mart.
Ex Tul.) |
Fabaceae |
Wood |
Jataí |
No information |
“Cumaru” |
Dipteryx odorata
(Aubl.) Wild. |
Fabaceae |
Wood Seeds Oil |
N.I |
Feb
to Mar |
“Tachi preto” |
Tachigalia paniculata
Aubl. |
Fabaceae |
Buildings |
N.I |
Dec
a Feb |
“Tachi branco” |
Tachigalia
paraenses (Huber) Barneby |
Fabaceae |
Energy RDA* |
N.I |
Jun
to Sep |
“Ingazeiro” |
Inga sp |
Fabaceae |
Food |
N.I |
No information |
“Uchi” |
Endopleura
uchi (Huber) Cuatrec. |
Humiriaceae |
Wood Food |
N.I |
Jul to Nov |
“Louro” |
Laurus nobillis
L. |
Lauraceae |
No information |
N.I |
No information |
Avocado tree |
Persea americana |
Lauraceae |
Food |
Frisiomelita |
No information |
“Castanha do Pará” |
Bertholethia excelsa
Bonpl. |
Lecythidaceae |
Food |
Solitárias |
Sep
to Dec |
“Fava de espinho” |
Não
identificado |
Lecythidaceae |
RDA |
N.I |
No information |
“Muruci da mata” |
Não
identificado |
Malpighiaceae |
RDA |
N.I |
No information |
“Murucizeiro” |
Byrsonima
crassifólia ((L.) Rich.) |
Malpighiaceae |
Food |
N.I |
No information |
“Cupuaçu” |
Theobroma grandiflorum (Willd. ex
Spreng.) Schum. |
Malvaceae |
Food |
Plebeia |
No information |
“Canela de velho” |
Miconia albicans
(Sw.) Triana |
Melastomataceae |
RDA Medicinal |
N.I |
No information |
“Andiroba” |
Carapa guianensis
Aubl. |
Meliaceae |
Oil,
seeds |
N.I |
Aug
to Sep |
“Jaqueira” |
Artocarpus
heterophyllus Lam. |
Moraceae |
Food |
N.I |
No information |
Banana tree |
Musa
spp L. |
Musaceae |
Food |
N.I |
No information |
“Murta” |
Myrtus spp
L. |
Myrtaceae |
Medicinal |
N.I |
No information |
“Jambo” |
Syzygium
jambos (L.) Auston |
Myrtaceae |
Food |
N.I |
No information |
“Araçá” |
Psidium
cattleianum Sabine |
Myrtaceae |
Food |
N.I |
No information |
“Princesa da Amazônia” |
Não
identificado |
Não identificado |
No information |
All |
No information |
“Pau fumaça” |
Não
identificado |
Não identificado |
RDA |
All |
No information |
“Preciosa” |
Não
identificado |
Não identificado |
Food |
All |
No information |
“Limão caiano” |
Averrhoa
bilimbi L. |
Oxalidaceae |
Food |
Jataí |
No information |
“Limoeiro” |
Citrus limon
(L.) Burm. |
Rutaceae |
Food |
Jataí |
No information |
“Rambutã” |
Nephelium
lappaceum L. |
Sapindaceae |
Food |
N.I |
No information |
Non-identified |
Não
identificado |
Melastomataceae |
RDA |
N.I |
No information |
* Recovery
of Degraded Areas ** N.I – Non-Identified - there was no information about
the stingless bee species |
Table 3 shows the number of species with potential for multiple uses,
which can reduce the costs of implementing the systems for producers, since the
diversification of products with the potential to be commercialized can allow a
faster financial return. Eighteen fruit species with food use are visited by SBS
in Belterra which may indicate great potential for introduction in agroforestry
yards or other intercropped systems minimizing the costs of implementation and
maintenance. This diversity of species was also observed in the region by other
authors (SILVA; RAYOL, 2016). The number of plant species visited by SBS in the
Amazon region is high due to the coevolution of plant species with SBS, since
native bees are better adapted to the pollination of native plant species.
Barth (2004) found
that in the North Region, specifically in the State of Pará, the most commonly visited genera, species and families were Artocarpus, Bellucia, Carica, Cassia, Cocos, Leucaena, Maximiliana, Miconia, Myrtaceae, Stachytarpheta and Triplaris, Protium, besides Caesalpiniaceae, Mimosa pudica and Tapirira guianensis. Protium,
Borreria, Cassia, Cecropia, Eugenia, Miconia, Mimosa scabrella,
Tapirira
and Vismia
prevail in the city of Manaus.
Species such as “tatapiririca” and “cajueiro”,
representatives of the genera Anacardium and Tatapira,
were indicated by the producers as one of the favorites by bees, with a great
abundance of individuals in these species being observed during the flowering
period. According to Fernandes et al. (2012), the great abundance and diversity
of floral visitors in the “Tatapiririca” flowers,
occur due to the high bee potential of this species, which offers pollen and
nectar in volume and concentration of solutes attracting small insects.
The Jataí bee species,
with the highest occurrence in the studied backyards, was defined by Cortopassi-Laurino (1982) as an eclectic species in floral
visitation, while Knoll (1990) reports that the species has a
preference for the Euphorbiaceae family.
Families such as Anacardiaceae,
Caesalpiniaceae, Oxalydaceae, Rutaceae
and Sapotaceae, may have their species visited to
collect nectar and pollen (CARVALHO et al., 1995). In the interviews, the
following representatives of these families were identified, respectively: “tatapiririca”, “cajarana”, “taperebá” and mango; no representative of the
Caesalpiniaceae and Sapotaceae families and “limão caiano” were mentioned.
Maués et al. (1996) highlight that, for species such as “cupuaçu”
and “cacao”, there is a very high flowering concerning
to the number of fruits, called “Insect gratification syndrome”, an example of
mutualism and coevolution, given that, there is greater pollination intensity
of the plant and greater availability of resources for the insect, benefiting
both.
When performing melissopalinological
analyzes on species of the genus Melipona and Trigona, in forest
fragments in Manaus, Oliveira et al. (2009) found that the families most
visited by bees were: Caesalpiniaceae, Fabaceae, Mimosaceae, Myrtaceae, and the family with the highest frequency of
visits was Melastomastaceae. Likewise, in Belterra,
the interviewees also mentioned that the above mentioned
botanical families are visited by bees of the genera Melipona and Trigona.
Five species of the Fabaceae family were cited by
honey farmers as visited by the SBS, empirically characterizing the group with
the highest frequency of species. This fact was also cited by Oliveira et al.
(2009) for visitation by bees in Manaus, Amazonas.
CONCLUSIONS
Meliponiculture in the municipality
of Belterra is an activity adopted by affinity and environmental commitment of
the beekeepers, predominantly as an income supplement, exercised for a long
time, by experienced people and with honey as their main commercialized product.
The maintenance of meliponaries implies constant dedication carried out in
line with other work activities, without having continuous technical assistance
and having as main threat the deforestation and the application of pesticides,
implying the indication of agroforestry yards as the best option for the
development of the activity.
Fruit-bearing plant
species were indicated as predominant by honey farmers, characteristics of
primary and secondary forest, indicating the potential for introduction into
agroforestry yards or other intercropped systems, minimizing the costs of
implanting and maintaining meliponaries.
ACKNOWLEDGEMENTS
To the beekeepers of Belterra for allowing us to access their
properties and for the kindness to share their experience, knowledge
and difficulties regarding the breeding of stingless bees. To the Federal
University of Western Pará and the Institute of Biodiversity and Forests for
logistical support for data sampling.
REFERENCES
BAILEY, K. Methods of social reserch. 4, ed. New York: The Free Press, 1994.
BARTH,
O. M. Melissopalynology in Brazil: a review of pollen
analysis of honeys, propolis and pollen loads of bees. Science Agricultural,
v.61, n.3, p.342-350, 2004.
BRASIL. RESOLUÇÃO CONAMA nº 346, de 16 de agosto de 2004.
Publicada no DOU nº 158, de 17 de agosto de 2004, Seção 1, página 70.
Disciplina a utilização das abelhas silvestres nativas, bem como a implantação
de meliponários.
BROWN, J. C.; OLIVEIRA, M. L. The
impact of agricultural colonization and deforestation on stingless bee (Apidae:
Meliponini) composition and richness in Rondônia,
Brazil. Apidologie, v.45, p.172-188, 2014. 10.1007/s13592-013-0236-3.
CARVALHO, C.A.L. de; MARQUES, O.M.;
SAMPAIO, H.S. de V. Abelhas (Hymenoptera, Apoidea) em Cruz das Almas-Bahia: espécies coletadas em
fruteiras. Insecta, v.4,
n.1, p.11-17, 1995.
CORDEIRO,
H. K. C.; MENEZES, C. Análise
da capacidade produtiva de própolis em diferentes espécies de abelhas sem
ferrão. XXIV CONGRESSO
BRASILEIRO DE ZOOTECNIA, 2014.
CORTOPASSI-LAURINO, M. Divisão de
recursos tróficos entre abelhas sociais, principalmente em Apis
mellifera Linn. e Trigona (Trigona) spinipes Fabricius(Apidae, Hymenoptera). 1982. 180f.
Tese (Doutorado) Instituto de
Biociências, Universidade de São Paulo, São Paulo, 1982.
CORTOPASSI-LAURINO, M;
IMPERATRIZ-FONSECA, V. L.; ROUBIK, D W.; DOLIN, A.; HEARD, T.; AGUILAR, I.;
VENTURIERI, V. C.; EARDLEY, C.; NOGUEIRA-NETO, P. Global meliponiculture:
challenges and opportunities. Apidologie, 37, p.
275-292, 2006.
COSTA, T. V.; FARIAS, C. A.
G.; BRANDÃO, S. C. Meliponicultura em comunidades tradicionais do Amazonas. Revista Brasileira de Agroecologia, v.7,
n.3, p.106-115, 2012.
DEEPAST.
Agricultura: Veja produção agrícola e área plantada por cidade do Brasil -
BELTERRA, PA. Disponível em: <http://www.deepask.com/goes?page=belterra/PA-Agricultura:-Confira-a-producao-agricola-e-a-area-plantada-no-seu-municipio>.
Acesso em 17 de agosto de 2020.
FARIA,
L, M. S. Aspectos gerais da Agroecologia no Brasil. Revista Agroambiental, v.6, n.2, p.101-111, 2014. http://dx.doi.org/10.18406/2316-1817v6n22014556
FERNANDES, M. M.; VENTURIERI, G. C.; JARDIM, M. A. G.
Biologia, visitantes florais e potencial melífero de Tapirira
guianensis (Anacardiaceae)
na Amazônia Oriental. Revista de Ciências Agrárias, v.55, n.3, p.167-175, 2012.
GEHRKE, R. Meliponicultura:
O estudo de caso dos criadores de abelha nativa sem ferrão do Vale do Rio
Rolante (RS) - Porto Alegre. 2010. 215f. Dissertação (Mestrado em
Desenvolvimento Rural) Universidade Federal do Rio Grande do Sul, Porto Alegre,
2010.
KERR, W. E.; CARVALHO, G. A.; NASCIMENTO, V. A. Abelha uruçu: biologia, manejo e conservação.
Fundação Acangau. Coleção Manejo da vida silvestre,
2. Belo Horizonte: 1996. 143p.
KNOLL, F. do R. N. Abundância relativa, sazonalizada e preferências florais de Apidae
(Hymenoptera) em uma área urbana (23º 33’S; 46º
43’W). 1990. 127f. Tese (Doutorado) Instituto de Biociências, Universidade de
São Paulo, São Paulo, 1990.
LIMA, L. N. NOGUEIRA, E. de. S. Produção e uso dos
recursos melíferos por meliponicultores da região de Cícero Dantas, BA. Gaia Scientia, v.11, n.3, p.73-82, 2017. 10.22478/ufpb.1981-1268.2017v11n3.29111
LOPES, M; FERREIRA; SANTOS, J. B. G.
dos. Abelhas sem-ferrão: a biodiversidade invisível. Agriculturas, v.2, n.4, p.7-9, 2005.
MAGALHÃES, T. L de; VENTURIERI, G. C. Aspectos
econômicos da criação de abelhas indígenas sem ferrão (Apidae:
Meliponini) no Nordeste paraense. Embrapa Amazônia Oriental-Documentos
(INFOTECA-E), 2010.
MAIA-SILVA, C. et al. Stingless bees (Melipona subnitida) adjust brood production rather than foraging
activity in response to changes in pollen stores. Journal of Comparative Physiology A, v. 202, p. 723-732, 2016.
MAUÉS, M. M.; VENTURIERI, G. C.; DE SOUZA, L. A.;
NAKAMURA, J. Identificação e técnicas
de criação de polinizadores de espécies vegetais de importância econômica no
estado do Pará. EMBRAPA. Centro de Pesquisa Agroflorestal da Amazônia
Oriental (Belém,PA). Geração
de tecnologia agroindustrial para o desenvolvido do trópico úmido. Belém:
EMBRAPA - CPATU / JICA. p.305, 1996.
MEIRELES, A. M.; TAVARES, F.
B.; LOPES, E. L. N.; CORDEIRO, Y. E. M. Aspectos econômicos, sociais e
ambientais inerentes a atividade de meliponicultura
no baixo Tocantins, estado do Pará”, Revista Observatorio
de la Economía Latinoamericana, 2018.
MELLO, F. P.; SOUZA, B, A;
LOPES, M. T. R. Instalação e manejo de meliponário -
Teresina: Embrapa Meio-Norte, p. 26, 2010.
OLIVEIRA,
F. P. M.; ABSY, M. L.; MIRANDA, I. S. Recurso polínico coletado por abelhas sem ferrão (Apidae,
Meliponinae) em um fragmento de floresta na região de
Manaus – Amazonas. Acta Amazonica. v.39, n.3,
p.505–518, 2009.
PEREIRA, F. M. Instalação e manejo de meliponários. Embrapa Meio-Norte, 2010.
PINHEIRO, J.N.; FREITAS, B.M.
Efeitos letais dos pesticidas agrícolas sobre polinizadores. Oecologia Australis.
v. 14, n.1, p, 266-281, 2010.
PINTO, G. S. Diagnóstico da meliponicultura em Belterra, PA e
caracterização física, química e microbiológica de méis de Scaptotrigona sp. (canudo-amarela). Belem,
Tese, 100 p. 2012.
RAYOL, Breno Pinto; MAIA, Raimundo
Tarcísio Feitosa. Potencial da inserção de abelhas em sistemas agroflorestais
no oeste do estado do Pará, Brasil. Revista Brasileira de Agroecologia, v.8, n.3, p.101-108, 2013.
SANTOS, A. B. Abelhas nativas: polinizadores em
declínio. Natureza on line v.8, n.3, p.103- 106, 2010.
SILVA, F. L. da;
OLIVEIRA, F. de A.; AMIN, M. M.; BELTRÃO, N. E. S.; ANDRADE, V. M. S. Dimensões do uso e cobertura de terra nas
mesorregiões do estado do Pará. Espacios, v.37, n.05,
p.5, 2016.
SILVA, J. C. N.; RAYOL, B. P.
Diversidade de árvores nos quintais urbanos do município de Belterra,
Oeste do Pará. Cadernos de
Agroecologia, v. 10, n. 3, 2016.
SILVA, M. D.; MONTEIRO, D.; SILVA, M.; OLIVEIRA, R. B.;
QUEIROZ, M. V. M; SANTOS, J. F. Padrão de distribuição espacial de ninhos de Meliponini (Hymenoptera: Apidae) em função da disponibilidade de recursos para
nidificação em um fragmento de Mata Atlântica em Salvador, Bahia, Brasil.
Magistra, Cruz das Almas-BA, v.24, p.91-98, 2012.
SILVA, W. P.; PAZ, J. R. L. Abelhas sem
ferrão: muito mais do que uma importância econômica. Natureza on line, v.10, n.3, p.146-152, 2012.
SIQUEIRA, A. L. Estudo da ação
antibacteriana do extrato hidroalcoólico de própolis
vermelha sobre Enterococcus faecalis. Revista de Odontologia da UNESP, v.43,
n.6, p.359-366, 2014.
VENTURIERI,
A; COELHO, A. de S.; THALES, M. C.; BACELAR, M. D. R. Análise da expansão da
agricultura de grãos na região de Santarém e Belterra,
Oeste do estado do Pará. Anais XIII Simpósio Brasileiro de Sensoriamento
Remoto, Florianópolis, Brasil, INPE, p. 7003-7010, 2007.
VENTURIERI, G. C., The impacto
f forest exploitation on Amazonian stinglees bees
(Apidae, Meliponini). Genetics and Molecular Research v8: p.684-689,
2009.
WINFREE, R.; AGUILAR, R.;
VAZQUEZ, D. P.; LEBUHN G.; AIZEN, M. A. A meta-analysis of bees' responses to
anthropogenic disturbance. Ecology, v.90, n.8, p.2068-2076, 2009.