1
Revista de Biología Tropical, ISSN: 2215-2075, Vol. 73: e4ahgnf87, enero-diciembre 2025 (Publicado Jul. 28, 2025)
Population structure of freshwater prawn Macrobrachium amazonicum
(Crustacea, Palaemonidae) in two regions of the Amazon River, Brazil
Sting Silva-Duarte1*; https://orcid.org/0000-0001-6878-5762
Jô de Farias-Lima1,2; https://orcid.org/0000-0001-6910-7672
Sheyla Regina Marques-Couceiro1,3; https://orcid.org/0000-0001-8186-4203
1. Postgraduate Program in Tropical Biodiversity, Federal University of Amapá, Macapá, Amapá, Brazil (*Correspondence);
stingduarte@gmail.com
2. Embrapa Amapá, Rodovia Josmar Chaves Pinto, Km 5, n° 2.600, Caixa Postal 10, 68903-419 Macapá, AP, Brazil;
jo.lima@embrapa.br
3. Laboratory of Ecology and Taxonomy of Aquatic Invertebrates of Federal University of West of Pará; sheylacouceiro@
yahoo.com.br
Received 11-VI-2024. Corrected 30-V-2025. Accepted 24-VI-2025.
ABSTRACT
Introduction: Macrobrachium amazonicum is a species of shrimp native to South America, widely distributed
and exploited by artisanal fishermen in the North of Brazil.
Objective: This study aimed to analyze the population structure of M. amazonicum, with an emphasis on sex
ratio, frequency distribution of male and female size, also considering the rainy and dry period in the study areas.
Methods: For this, monthly collections were carried out from May 2017 to April 2018 with the help of “matapis
in two locations, Mazagão and Ilha das Marrecas.
Results: A total of 6 796 (4 163 females and 2 633 males) were captured, with a monthly average of 531.66 speci-
mens. The sex ratio in both areas was favorable to females with 1.32 : 1 (x² = 76.58, p < 0.001) in Mazagão and
2.34 : 1 (x² = 394.26, p < 0.001) in the Ilha das Marrecas. In both Mazagão and Ilha das Marrecas, abundance
was strongly related to precipitation.
Conclusions: The shrimps of Ilha das Marrecas were longer than those caught in Mazagão. Despite this fishing
pressure in Mazagão, the areas proved to be favorable for the growth of the species.
Keywords: morphometry; sex ratio; white water Amazon shrimp; estuary; river.
RESUMEN
Estructura poblacional del camarón de agua dulce Macrobrachium amazonicum
(Crustacea, Palaemonidae) en dos regiones del río Amazonas, Brasil
Introducción: Macrobrachium amazonicum es una especie de camarón nativa de América del Sur, ampliamente
distribuida y explotada por pescadores artesanales en el Norte de Brasil.
Objetivo: Este estudio tuvo como objetivo analizar la estructura poblacional de M. amazonicum, con énfasis
en la proporción de sexos, distribución de frecuencias de tallas de machos y hembras, considerando también el
período lluvioso y seco en las áreas de estudio.
Métodos: Para ello, se realizaron colectas mensuales de mayo de 2017 a abril de 2018 con la ayuda de «matapis»
en dos localidades, Mazagão e Ilha das Marrecas.
https://doi.org/10.15517/4ahgnf87
INVERTEBRATE BIOLOGY
2Revista de Biología Tropical, ISSN: 2215-2075 Vol. 73: e4ahgnf87, enero-diciembre 2025 (Publicado Jul. 28, 2025)
INTRODUCTION
The understanding of crustacean popu-
lation variability in different environments
provides information on the habits and charac-
teristics of the species life cycles and how these
are related to the environment, so permitting
an understanding of the ecological stability of
group members, including shrimp (infraorder
Caridea) (Bentes et al., 2016). Such information
provides the basic underpinning for manage-
ment of shrimp aquaculture. Information on
the size distribution of male and female speci-
mens, sex ratio, spatial distribution of indi-
viduals and population age structure can, for
example, be used to explain seasonal variations
in size, reproductive strategies and productive
potential (Silva et al., 2007; Silva et al., 2019).
In this context, population studies on Mac-
robrachium amazonicum (Heller, 1862) are
especially important, as the species is both
scientifically and commercially important in
north and Northeastern Brazil (Alcântara &
Kato, 2016; Costa et al., 2021; Lima et al., 2016;
Melo et al., 2022; Ramos et al., 2016). The spe-
cies is commercially exploited in the states of
Amazonas, Pará and Amapá by artisanal fishing
and indigenous populations (Bentes et al., 2016;
Lima et al., 2014). In general, M. amazonicum
populations are characterized by variations in
the population structure, and there may be dif-
ferences in the distribution of individuals in all
months of the year (Sampaio et al., 2007; Silva
et al., 2019). However, in the Amazon region
fishing pressures on the species may lead led to
unsustainable exploitation (Bentes et al., 2014;
Freire et al., 2012a; Lima et al., 2014; Lucena-
Frédou et al., 2010).
The knowledge of the proportions of the
sexes, sizes and growth stages is important for
effective management and to guarantee sus-
tainable use of M. amazonicum in the Amazon
region. Accordingly, the current study was per-
formed to examine the population structure of
M. amazonicum with emphasis on sex ratio and
size frequency distribution in the regions of the
Amazon river mouth and lower reaches.
MATERIAL AND METHODS
Study area and rainfall data: Samples of
M. amazonicum were collected monthly from
May 2017 to April 2010, on the Mazagão River
(00º15’39.9’’S & 051º20’ 42.3’W), located at the
mouth of the Amazon River, state of Amapá,
and in the Ilha das Marrecas complex on the
lower Amazon River (02º12’19.3’’S & 054º46’
17.9’W), state of Pará (Fig. 1). The shrimps
of the two study sites were pooled for analy-
sis because the areas studied shown relatively
different in their physiography. The Mazagão
River shows various drainage channels, with
varying sizes and depths and daily influence
of the tide, allowing the daily flooding and the
formation of a wide diversity of microhabitats.
The vegetation is typical of the “várzea Ama-
zon, dense with large and wide bands of mac-
rophytes along the river margin.
In the Ilha das Marrecas, the vegetation is
similar to that observed in the Mazagão River,
with dense, large, and wide bands of macro-
phytes along the Amazon riverbed. However,
thus hydrodynamics is different. In Ilha das
Marrecas, not the daily influence of the tide
only annual variations in the river depth due to
the common floods in the winter period. These
Resultados: Se capturaron un total de 6 796 (4 163 hembras y 2 633 machos), con una media mensual de 531.66
ejemplares. La proporción de sexos en ambas áreas fue favorable a las hembras con 1.32 : 1 (x² = 76.58,
p < 0.001) en Mazagão y 2.34 : 1 (x² = 394.26, p < 0.001) en la Ilha das Marrecas. Tanto en Mazagão como en
Ilha das Marrecas, la abundancia estuvo fuertemente relacionada con la precipitación.
Conclusiones: Los camarones de Ilha das Marrecas eran más largos que los capturados en Mazagão. A pesar de
esta presión pesquera en Mazagão, las zonas resultaron favorables para el crecimiento de la especie.
Palabras clave: morfometría; proporción de sexos; camarón blanco del Amazonas; estuario; río.
3
Revista de Biología Tropical, ISSN: 2215-2075, Vol. 73: e4ahgnf87, enero-diciembre 2025 (Publicado Jul. 28, 2025)
natural floods cause cycles of erosion, trans-
portation and deposition of sediments, with
systematic annual morphological modification
of the riverbed (Farias & Carneiro, 2012).
Both areas have a humid Equatorial cli-
mate, with two seasonal periods marked by a
rainy period from December to June and a less
rainy (dry) period from July to November. To
assist the study with updated data on local sea-
sonality, monthly data on rainfall were obtained
from the website of the Instituto Nacional de
Meteorologia (INMET, 2021).
Shrimp collection: For the collection of
the shrimp 20 traps locally known as “matapis
were used. Traps were set and submerged over
Fig. 1. The location of Macrobrachium amazonicum captures areas in the mouth and lower Amazon between May 2017
and April 2018, and July 2021 to May. The black circle ( ) represents Mazagão, while the green triangle (p) represents
Marrecas Island.
4Revista de Biología Tropical, ISSN: 2215-2075 Vol. 73: e4ahgnf87, enero-diciembre 2025 (Publicado Jul. 28, 2025)
a single nocturnal tidal cycle (12 hours). All
captures occurred at daybreak. They were then
recovered one at a time and the contents were
removed, placed in plastic bags, labeled, stored
on crushed ice in a cooler, and transported to
the laboratory.
Shrimp Analysis: In the laboratory,
shrimps were identified, sexed and submitted
to biometrics. Taxonomic identification follow-
ing the taxonomic keys of Melo et al. (2003).
Sex was verified by the presence of masculine
appendix on the second pleopod. To biometrics
standard length (SL-linear distance from the
base of ocular orbit to the base of the telson)
and total wet mass (TM) of shrimps a digital
caliper (0.01 mm precision) and a digital scale
(0.01 g), were used to measure, respectively.
Individuals with measures below the small-
est identifiable male will be considered sexu-
ally undifferentiated, while shrimps with sizes
below the smallest female egg will be consid-
ered juveniles (Lima et al., 2014).
The monthly rainfall data of each region
was obtained at the data of base the INMET
(2021).
Data analysis: The statistical analysis of
the data was performed with the aid of the
BioEstat 5.0® software (Ayres et al., 2007). Nor-
mality and homoscedasticity of the variances
were tested with Shapiro-Wilk and Bartlett’s
tests, respectively.
The sex ration was determined per month
in each collection site using the chi-square
test (x², α = 0.05) according to Zar (1999).
The t-test was applied to verify differences sex
ration between collection sites. Kruskall-Wallis
test was applied to verify differences between
standard length of males and females during
the studied period. The t-test was applied to
verify differences regarding standard length
between sex and collection sites. All analysis
p-value equal or less than 0.05 were chosen
to indicate statistical significance. To verify if
there is a relationship between rainfall and the
abundance of prawn by area, one regression
analysis was performed (Zar, 1999).
RESULTS
A total of 6 796 shrimps were caught, of
which 4 132 (60.8 %) were in Mazagão and 2
664 (39.2 %) in Ilha das Marrecas. The total
number of shrimps caught in Mazagão was
higher than in Ilha das Marrecas (p < 0.05) in
most study months, except in June and April
2018 (Fig. 2). In general, the M. amazonicum
catch was higher during the period with less
rain (July to October), particularly for adult
shrimps (Fig. 2, Fig. 3).
Fig. 2. Abundance of M. amazonicum (Heller, 1862) collected between May 2017 and Apr 2018 in the mouth of Mazagão
River-AP and Ilha das Marrecas-PA; and their relationship with rainfall.
5
Revista de Biología Tropical, ISSN: 2215-2075, Vol. 73: e4ahgnf87, enero-diciembre 2025 (Publicado Jul. 28, 2025)
Chi-square test showed that the sex ratio
was significantly different from 1:1 in Ilha das
Marrecas (x² = 394.26, p < 0.001) and Mazagão
(x² = 76.58, p < 0.001), being 2.34 : 1 and
1.32 : 1 respectively. In Mazagão, M. amazo-
nicum showed significant differences in relation
to the expected sex ratio except in the months,
May, July, August and September of 2017 and
January of 2018. In contrast, in Ilha das Mar-
recas, sex ratio differences were observed in all
collection months (Table 1).
In both study areas monthly distribution
of adult juveniles, males, and females showed
season variation (Fig. 3A, Fig. 3B). In Maza-
gão, numerical dominance of male and adult
female shrimps alternated in both seasons.
Adult male shrimps dominant in May, July,
August, September, and adult female shrimps
from December to April (rainy season). While
in Ilha das Marrecas, adult female shrimps were
not only more abundant than the adult males
in the rainy season (January to April), but also
across most of the period with little rain (July
to December).
Juvenile shrimps were found in all months
of the year, in both regions, with a recruitment
peak in June and July (Mazagão) and June, Sep-
tember, October and March (Marrecas), with
juveniles comprising between 35 % and 45 % of
the catch (Fig. 3A, Fig. 3B).
In Mazagão, male shrimps of the length
class 43.4 mm to 49.4 mm were commonest
while most female shrimps were between 49.4
mm and 55.4 mm. In Ilha das Marrecas, male
Fig. 3. Monthly absolute frequency distribution of juvenile, adult males and adult females of M. amazonicum (Heller, 1862)
collected between May 2017 and Apr 2018. A. in the mouth of Mazagão River-AP. B. in Ilha das Marrecas-PA.
6Revista de Biología Tropical, ISSN: 2215-2075 Vol. 73: e4ahgnf87, enero-diciembre 2025 (Publicado Jul. 28, 2025)
and female shrimps were most common in the
length classes 61.4 mm to 67.4 mm and 49.5
mm to 55.4 mm, respectively (Table 2). Analy-
sis of variance showed significant differences
in the standard lengths of males, females and
total shrimp lengths between the sites, but not
between collection months (Fig. 4).
Males captured in Ilha das Marrecas had
a higher mean length than those captured in
Mazagão in May and October 2017 and Feb-
ruary and April 2018 (Fig. 4A). Additionally,
females caught in Marrecas had longer mean
lengths than those caught in Mazagão between
June and September 2017 and March and April
Table 2
Frequency distribution of shrimps M. amazonicum in size classes (CP), collected between May 2017 and April 2018 in
Mazagão-AP and ilha das Marrecas.
Classe
(CP, mm)
Mazagão Ilha Marrecas
Adult
Males
Adult
Females
Juveniles
Males
Juveniles
Females
Adult
Males
Adult
Females
Juveniles
Males
Juveniles
Females
31.4-37.4 - - 70 123 - - 70 125
37.4-43.4 276 345 - - - 64 110
43.4-49.4 469 361 - - 25 165 - -
49.4-55.4 237 601 - - 107 638 - -
55.4-61.4 303 529 - - 125 499 - -
61.4-67.4 202 315 - - 206 235 - -
67.4-73.4 112 15 - - 50 59 - -
73.4-79.4 111 2 - - 51 56 - -
79.4-85.4 7 5 - - 15 18 - -
85.4-91.4 10 14 - - 12 11 - -
91.4-97.4 7 10 - - 10 6 - -
97.4-03.4 0 8 - - 5 2 - -
Total 1 734 2 205 70 123 606 1 689 134 235
Table 1
Chi-square values and sex ratio of M amazonicum sampled in Mazagão and Ilha das Marrecas between May 2017 and April
2018.
Months Mazagão Ilha das Marrecas Group Areas
Ratio Ratio Ratio
may/17 131 136 2.63 0.82:1 91 32 28.30 2.8:1* 216 184 2.6 1.17:1
jun/17 143 33 0.49 1.14:1* 350 115 118.76 3.04:1* 404 162 103.5 2.49:1*
jul/17 153 172 1.80 0.88:1 130 90 7.27 1.44:1* 413 342 6.7 1.20:1*
aug/17 220 221 0.08 0.97:1 172 108 14.63 1.59:1* 398 340 4.6 1.17:1*
sep/17 290 236 7.81 1.26:1* 354 184 53.72 1.92:1* 666 430 50.8 1.54:1*
oct/17 456 320 21.40 1.5:1* 152 50 51.50 3.04:1* 473 264 59.3 1.79:1*
nov/17 220 50 11.11 1.76:1* 90 38 21.31 2.36:1* 182 90 31.1 2.02:1*
dec/17 299 138 64.51 2.23:1* 79 19 36.73 4.15:1* 388 158 96.9 2.45:1*
jan/18 82 59 2.99 1.31:1 58 15 25.33 3.86:1* 150 85 18.0 1.76:1*
feb/18 186 112 17.52 1.60:1* 67 27 17.02 2.48:1* 265 150 31.9 1.76:1*
mar/18 176 101 17.28 1.63:1* 74 21 29.57 2.48:1* 260 135 39.6 1.92:1*
apr/18 147 51 0.45 087:1* 88 27 32.36 3.25:1* 138 84 13.1 1.64:1*
*Significant differences from the chi-square test, p < 0.05.
7
Revista de Biología Tropical, ISSN: 2215-2075, Vol. 73: e4ahgnf87, enero-diciembre 2025 (Publicado Jul. 28, 2025)
Fig. 4. Monthly variation of standard length between males, females and grouped sex of M. amazonicum collected in the
Mazagão River-AP and Ilha das Marrecas -PA, between May 2017 and Apr 2018. A. Males. B. Females and C. Grouped
sex. Different lower letters represent significant differences between the collection sites, while different upper-case letters
represent differences between the months.
8Revista de Biología Tropical, ISSN: 2215-2075 Vol. 73: e4ahgnf87, enero-diciembre 2025 (Publicado Jul. 28, 2025)
2018 (Fig. 4B). In the months of November and
December 2017 and January 2018 (Fig. 4C),
mean length for all shrimps captured in Maza-
gão exceeded those from Ilha das Marrecas.
DISCUSSION
Macrobrachium amazonicum was more
abundant in Mazagão than in Ilha das Marre-
cas, except in the months of June 2017 and April
2018. In general, the coastal areas of the Ama-
zon show a greater abundance of this species
compared to more continental sites (Lima et
al., 2014; Meireles et al., 2013). This difference
in abundance may be linked to the amount of
suspended organic matter and nutrients avail-
able. This is a consequence of differences in
the intensity of tidal activity and bioturbation,
which favor the development of a remarkable
productivity of micro invertebrates, algae and
fine particulate organic matter in more coastal
areas. Another aspect is the proximity of estua-
rine areas to the oceanic itself. Macrobrachium
amazonicum is an eurihaline species, tolerating
a wide range of salinity, but with larva which
develop best in waters with a particular salinity
concentration, as shown by a number of labora-
tory studies (Araujo & Valenti, 2010; Perroca et
al., 2022; Soeiro et al., 2016; Sterzelecki et al.,
2021). Despite tolerating a wide concentration
of salinity as adults, there are changes in the
larval stages of this species, which include mor-
phological changes in the gills and expression
of the sodium and potassium ATPase pump
(Na+, K+ ATPase-NKA), which reduce larval
survival at low salinities (Boudour-Boucheker
et al., 2013). Thus, M. amazonicum populations
in estuarine areas have better conditions to
complete their larval development than popula-
tions from more continental sites.
Differences in abundance between sea-
sonal periods is a particular trend of each spe-
cies in the genus Macrobrachium: M. brasiliense
(Heller, 1862) (Mantelatto & Barbosa, 2005),
M. macrobrachion (Herklots, 1851) and M.
vollenhovenii (Herklots, 1857) (Lawal-Are &
Owolabi, 2012) all display greater rainy sea-
son abundance, unlike M. iheringi (Ortmann,
1897), M. ohione (Smith, 1874) (Truesdale &
Mermilliod, 1979), M. tenellum (Smith, 1871)
(Román-Contreras, 1979), M. olfersi (Wieg-
mann, 1836) (Mossolin & Bueno, 2003) and M.
amazonicum, which are clearly more abundant
during the less rainy season.
Data for the current study followed this
pattern, so that in both Mazagão and Ilha
das Marrecas, abundance was strongly related
to precipitation, with highest catches during
the less rainy season (July to October). These
results corroborate data from other parts of the
Amazon which show reproductive peaks of M.
amazonicum coinciding with the rainy season
period (Lima et al., 2014; Melo et al., 2022), and
the recruitment period coinciding with the dry
season (Bentes et al., 2016; Costa et al., 2016;
Costa et al., 2021).
In the current study, a predominance of
females was observed at both study sites. This
bias seems to be common in the genus Macro-
brachium (dos Santos-Antunes & Oshiro, 2004;
Fransozo et al., 2004; Meireles et al., 2013; Melo
et al., 2022). It has been reported for estuarine
and coastal populations of M. amazonicum in
the Amazon region (Freire et al., 2012b; Lima et
al., 2014; Montoya, 2003; Sampaio et al., 2007;
Silva et al., 2007). However, an excess of males
(Mantel & Dundgeon, 2005) and equal male :
female ratios (Mattos & Oshiro, 2009) have also
been observed for the genus.
Although a predominance of females was
common, the monthly mean sex ratio values in
favor of females was higher in Marrecas than in
Mazagão, while in some months no significant
differences were observed. In crustaceans devi-
ations in the sex ratio may be a consequence
of many factors, including between-sex differ-
ences in size, mortality, and hatching rates. But
factors such as development rates, dispersion,
reproduction, differential migration, environ-
mental conditions, geographic characteristics
and anthropogenic interference may also be
influential (Botelho et al., 2001; Lima et al.,
2014; Perroca et al., 2022; Sterzelecki et al.,
2021). As the environmental characteristics and
availability of nutritional resources are similar
between the two study areas, it is likely that the
9
Revista de Biología Tropical, ISSN: 2215-2075, Vol. 73: e4ahgnf87, enero-diciembre 2025 (Publicado Jul. 28, 2025)
greater abundance of females in Marrecas is
related to the reproductive strategy adopted by
M. amazonicum populations in each region. In
Marrecas, there is a clear reduction in the avail-
ability of salinity and there is little tidal influ-
ence, thus an increase the number of females
there means that a larger number of larvae
are available to close their cycle and increase
the availability of juveniles for dispersion, so
maintaining the population (Bentes et al., 2016;
Silva et al., 2019).
The unplanned, unmanaged and intensive
exploitation of these shrimps is another fac-
tor that may be related to sex ratio changes,
as observed in populations of M. amazonicum
from the island of Combú in Pará State, Brazil
(Lucena-Frédou et al., 2010; Silva et al., 2002).
However, in Ilha das Marrecas, where fishing
pressure is currently very low compared to
Mazagão, the sex-ratio distortion cannot be
attributed to this fact. Instead, it is likely to
be associated with the fact that the M. ama-
zonicum population on the lower Rio Tocan-
tins (State of Pará), became isolated after the
construction of a dam. This appears to have
strongly affected the shrimps, resulting in a
reduction in the average size of the captured
specimens and a doubling of sex ratio in favor
of females (Odinetz-Collart, 1991).
For the biometric variables, young and
adult shrimp caught in Ilha das Marrecas had a
greater standard length than the those caught in
Mazagão, except in November and December
2017 and January 2018 (Fig. 4C). As climatic,
environmental and nutritional conditions are
similar between Ilha de Marrecas and Mazagão,
this difference is most likely explained by fish-
ing pressure, which is substantially higher in
the region of the mouth at the Amazon River
where Mazagão occurs than in the lower river
Amazonas, where the Ilha das Marrecas lies.
As observed previously, high fishing pressure
can alter M. amazonicum population structure
and dynamics, especially the size and sexual
proportion (Lucena-Frédou et al., 2010; Melo
et al., 2022; Silva et al., 2002). Comparing our
results with other studies, it appears that the
average size of the shrimp caught in Mazagão
is similar to that reported in studies at other
estuarine sites in the Amazon region (Bentes
et al., 2011; Costa et al., 2021; Silva et al., 2002;
Silva et al., 2007), while size of shrimp caught in
Ilha das Marrecas were similar in that of those
caught in more coastal areas (Borges, 2003) and
in reservoir areas such as Rômulo Campos in
Bahia State, Brazil (Costa et al., 2016).
For recruitment it was apparent that young
shrimps constantly entered the population
every month. However, there were months
when these individuals were more abundant
(June and July in Mazagão; June, September,
October and March in Ilha das Marrecas). The
presence of juvenile shrimps throughout the
year in both study areas suggests that M. ama-
zonicum has continuous recruitment. A contin-
uous pattern of recruitment was also observed
in estuarine and continental populations in Ilha
de Combu in Pará state (Lucena-Frédou et al.,
2010), in Guajará Bay, Pará (Bentes et al., 2011),
in the reservoir of the Miranda hydroelectric
power-plant, Rio Araguari in Minas Gerais
state (Silva, 2014). The continuous recruitment
of juveniles at the two study sites likely reflects
the reproductive strategy of M. amazonicum
adopted in each region. In both areas, a pre-
dominance of females was observed, with con-
tinuous reproduction, reflecting the constant
recruitment of youngsters (Rocha et al., 2023;
Ventura et al., 2019).
In the Amazon region, shrimps are mainly
exploited with traps popularly known as mata-
pís (Costa et al., 2016). Such traps are usu-
ally produced with jupati palm (Raphia vinifer)
splint, with have very small gaps between the
splints (three millimeters on average) that allow
the capture of shrimp in the immature stages or
early in maturation (Lima, 2014). This fact was
shown in Mazagão and in Ilha de Marrecas,
where shrimps below the size at first matura-
tion were captured in all months of the study.
Evidence of similar current fishing impacts on
the M. amazonicum population was reported
from the ilha de Combú, Pará state (Silva et al.,
2007), and at the mouth of the Amazon River in
the state of Amapá (Lima, 2014). At both sites
matapi fishing is affecting local M. amazonicum
10 Revista de Biología Tropical, ISSN: 2215-2075 Vol. 73: e4ahgnf87, enero-diciembre 2025 (Publicado Jul. 28, 2025)
populations (Lucena-Frédou et al., 2010), and
negatively implicating the natural stocks of the
species in the region.
Based on our results of juvenile-stage cap-
ture and data presented by Camargo et al.
(2009), it is highly likely that the splint-sepa-
ration distance of 2.0 mm to 5.0 mm currently
used by artisanal fishermen in the Amazon
region is not appropriate. For M. amazonicum
the length at first maturation (between 45.0
mm and 60.0 mm) reported by Guest (1979),
Moraes-Riodades and Valenti (2002), Sampaio
et al. (2007), Lima et al. (2014) and Bentes et al.
(2014) is lower than those found in Mazagão
and Ilha das Marrecas, indicating that shrimp
fishing in these areas has not yet reached the
level of exploitation reported at other sites.
Given the results of the current study, it is
recommended that the minimum spacing of
1 cm between the matapís splints be adjusted
downwards, a proposal already made for M.
amazonicum by both Camargo et al. (2009)
and Lima (2014). In an attempt to reduce fish-
ing pressure, studies such as Camargo et al.
(2009) and Lima (2014) have suggested changes
in traps and capture strategies. In addition
to changing in the distance between matapí
splints, these authors suggest that the local
and state authorities, who police the environ-
ment, implement and monitor an active fishery
management policy for the species. This should
include setting the size between 60 and 70
mm (first maturation) as the lower catch size
limit for the species in the estuary region. For
Mazagão and Ilha das Marrecas, we can see that
such catch limits would also be appropriate.
Such a measure would result in a considerable
increase in the number of breeding specimens
and, consequently, an increase in the size of
shrimp caught later, generating more income
for fishermen and merchants, as well as greater
satisfaction for consumers, who will be able
to purchase larger products, which are more
attractive to consumers.
M. amazonicum showed variations in the
pattern of population structure in Mazagão
and in the Ilha das Marrecas. In Mazagão a
greater abundance of specimens was observed.
In relation to females, in Mazagão and in the
Ilha das Marrecas, they were significantly larger
and heavier than males, denoting differentiated
metabolism, probably due to reproduction, in
addition, a predominance of females and varia-
tion between the average length was observed
indicating that the populations of Mazagão and
Ilha das Marrecas are distinct. In both areas
M. amazonicum showed a reproductive peak
closely related to the rainy season, however,
the species reproduction occurs continuously
throughout the year.
Ethical statement: The authors declare
that they all agree with this publication and
made significant contributions; that there is no
conflict of interest of any kind; and that we fol-
lowed all pertinent ethical and legal procedures
and requirements. All financial sources are fully
and clearly stated in the acknowledgments sec-
tion. A signed document has been filed in the
journal archives.
ACKNOWLEDGMENTS
To the Coordenação de Aperfeiçoamento
de Pessoal de Nível Superior (CAPES) for
the Master’s scholarship granted to the first
author. To the Conselho Nacional de Desen-
volvimento Científico e Tecnológico (CNPq)
for the financial support according to process
no. 407698/2013-2, process no. 444367/2014-4,
process no. 405234/2024-4 and Fapeap (Call
003/2022-# 193). To the Empresa Brasileira de
Pesquisa Agropecuária for structural and logis-
tical support for data analysis. To the Ministério
do Meio Ambiente - MMA and Instituto Chico
Mendes de Conservação da Biodiversidade -
ICMBio for Permanent license for collection of
zoological material n° 24578-2.
REFERENCES
Alcântara, G. L. C., & Kato, H. C. de A. (2016). Good
handling practices of fresh shrimp sold in street fairs
of Belém, PA, Brazil. Journal of Bioenergy and Food
Science, 3(3), 139–148. http://dx.doi.org/10.18067/
jbfs.v3i3.98
11
Revista de Biología Tropical, ISSN: 2215-2075, Vol. 73: e4ahgnf87, enero-diciembre 2025 (Publicado Jul. 28, 2025)
Araujo, M. C., & Valenti, W. C. (2010). Efeito de baixas sali-
nidades sobre larvas de Macrobrachium amazonicum
(Crustacea, Palaemonidae) submetidas à inaniçao.
Magistra, 22(1), 191–197.
Ayres, M., Ayres Jr., M., Ayres, D. L., & Santos, A. de A. S.
(2007) BioEstat- aplicações estatísticas nas áreas das
ciências bio-médicas (5th ed.). Embrapa Amazônia
Oriental (CPATU).
Bentes, B., Martinelli-Lemos, J. M., Paes, E. T., Fernandes,
S. C. P., Paula, J. D., & Isaac, V. (2014). Experimental
study on the efficiency of different types of traps
and baits for harvesting Macrobrachium amazonicum
(Heller, 1862). Acta Scientiarum. Biological Sciences,
36(4), 383–391. https://doi.org/10.4025/actascibiolsci.
v36i4.22852
Bentes, B., Martinelli, J. M., Souza, L. S., Cavalcante, D. V.,
Almeida, M. C., & Isaac, V. J. (2011). Spatial distri-
bution of the Amazon River prawn Macrobrachium
amazonicum (Heller 1862) (Decapoda, Caridea,
Palaemonidae) in two perennial creeks of an estuary
on the northern coast of Brazil (Guajará Bay, Belém,
Pará). Brazilian Journal of Biology, 71(4), 925–935.
http://dx.doi.org/10.1590/S1519-69842011000500013
Bentes, B., Silva, J. C. S., Martinelli-Lemos, J. M., &
Isaac-Nahum, V. J. (2016). Abundance and mor-
phometric relationships of Amazon shrimp -Macro-
brachium amazonicum (Heller, 1862) (Decapoda,
Palaemonidae)- in an Amazon estuary-North coast
of Brazil. Biota Amazônia, 6(4), 1–9. http://dx.doi.
org/10.18561/2179-5746/biotaamazonia.v6n4p1-9
Borges, M. S. (2003). Distribuição, abundância e biologia
reprodutiva de Macrobrachium amazonicum (Heller,
1862) and Macrobrachium jelskii (Miers, 1877) (Crus-
tacea, Decapoda) [Unpublished Licenciate thesis].
Universidade Federal da Bahia, Salvador, Brazil.
Botelho, E. R. O., Santos, M. C. F., & Souza, J. R. B. (2001).
Aspectos populacionais do guaiamum, Cardisoma
guanhumi Latreille 1825, do estuário do rio Una
(Pernambuco–Brasil). Boletim tecnico-cientifico do
CEPENE, 9(1), 123–146.
Boudour-Boucheker, N., Boulo, V., Lorin-Nebel, C., Elgue-
ro, C., Grousset, E., Anger, K., Charmantier-Daures,
M., & Charmantier, G. (2013). Adaptation to fresh-
water in the palaemonid shrimp Macrobrachium
amazonicum: comparative ontogeny of osmoregula-
tory organs. Cell and Tissue Research, 353(1), 87–98.
https://doi.org/10.1007/s00441-013-1622-x
Camargo, M., Leão, J., Oliveira, A., Márcio, A., Silva, E.,
Acácio, F., Silva, G., Sampaio, L., Viana, M., Antunes,
T., & Silva, W. (2009). Matapi pet: uma nova proposta
para a exploração sustentável do camarão amazônico
Macrobrachium amazonicum (Heller, 1862). UAKA-
RI, 5(1), 91–96.
Costa, D. A. S., Martins, J. C., Silva, K. C. A., Klautau, A.
G. C. M., & Cintra, I. H. A. (2016). Seletividade do
matapi nas capturas de Macrobrachium amazonicum
no baixo Rio Tocantins, Amazon, Brasil. Boletim
do Instituto de Pesca, 42(2), 403–417. https://doi.
org/10.20950/1678-2305.2016v42n2p403
Costa, D. P., Castilho, C. L., Santos, U. R. A., Gemaque, T.
C., Damasceno, L. F., Lima, J. F., & Filho, K. C. M.
(2021). Effect of dietary carotenoids on reproducers
of Amazon River prawn Macrobrachium amazoni-
cum. Part 1: metabolism, morphometric / zootechni-
cal indexes, body composition and gametes. Journal
of Agricultural Studies, 9(2), 32–56. http://dx.doi.
org/10.5296/jas.v9i2.18156
dos Santos-Antunes, L., & Oshiro, L. M. Y. (2004). Aspectos
reprodutivos do camarão de água doce Macrobrachium
potiuna (Müller) (Crustacea, Decapoda, Palaemoni-
dae) na Serra do Piloto, Mangaratiba, Rio de Janeiro,
Brasil. Revista Brasileira de Zoologia, 21(2), 261–266.
https://doi.org/10.1590/S0101-81752004000200015
Farias, E. M. B., & Carneiro, D. S. (2012). Alterações geo-
morfológicas no rio Amazonas Santarém/PA. Revista
Geonorte, 2(4), 72–79.
Fransozo, A., Rodrigues, F. D., Freire, F. A. M., & Costa,
R. C. (2004). Reproductive biology of the freshwa-
ter prawn Macrobrachium iheringi (Ortmann, 1897)
(Decapoda: Caridea: Palaemonidae) in the Botucatu
region, São Paulo, Brazil. Nauplius, 12(2), 119–126.
Freire, J. L., Marques, C. B., & Bentes-da Silva, B. (2012a).
Crescimento e avaliação do estoque de Macrobra-
chium amazonicum em um estuário do Nordeste
do Pará, Brasil. Boletim do Instituto de Pesca, 38,
215–229.
Freire, J. L., Marques, C. B., & Bentes-da Silva, B. (2012b)
Estrutura populacional e biologia reprodutiva do
camarão-da-Amazônia Macrobrachium amazonicum
(Heller,1862) (Decapoda: Palaemonidae) em um
estuário da região nordeste do Pará, Brasil. Brazilian
Journal of Aquatic Science and Technology, 16(2),
65–76. http://dx.doi.org/10.14210/bjast.v16n2.p65-76
Guest, W. C. (1979). Laboratory life history of the palae-
monid shrimpMacrobrachium amazonicum (Heller)
(Decapoda, Palaemonidae). Crustaceana, 37(2),
141–152.
Instituto Nacional de Meteorologia (August 10, 2021).
Informativos [Database]. https://portal.inmet.gov.br/
informativos
Lawal-Are, A. O. & Owolabi, A. T. (2012). Comparative
biology of the prawns Macrobrachium macrobrachion
(Herklots) and Macrobrachium vollenhovenii (Herk-
lots) from two interconnecting fresh/brackish water
lagoons in South-West Nigeria. Journal of Marine Sci-
ence Research & Development, 2(2), 108. http://dx.doi.
org/10.4172/2155-9910.1000108
Lima, J. de F. (2014). Viabilidade de matapis adaptados com
diferentes espaçamentos entre talas sobre a captura do
12 Revista de Biología Tropical, ISSN: 2215-2075 Vol. 73: e4ahgnf87, enero-diciembre 2025 (Publicado Jul. 28, 2025)
camarão da Amazônia (Macrobrachium amazonicum
Heller, 1862) no estuário do Rio Amazonas [Techni-
cal Report]. Embrapa Amapá, Comunicado técnico
95. http://www.infoteca.cnptia.embrapa.br/infoteca/
handle/doc/984373
Lima, J. de F., Cintra, I. H. A., Bastos, A. M., Damas-
ceno, L. F., Montagner, D., & Varela, E. S. (2016).
Caracterização do sistema pesqueiro de produção do
camarão-da-Amazônia no Estuário Amazônico (1st
ed.). Embrapa Amapá Documentos. http://www.info-
teca.cnptia.embrapa.br/infoteca/handle/doc/1064543
Lima, J. de F., Silva, L. M. A., Silva, T. C., Garcia, J. da S.,
Pereira, I. da S., & Amaral, K. D. S. (2014). Reproduc-
tive aspects of Macrobrachium amazonicum (Decap-
oda: Palaemonidae) in the state of Amapá, Amazon
River mouth. Acta Amazonica, 44(2), 245–254. http://
dx.doi.org/10.1590/S0044-59672014000200010
Lucena-Frédou, F., Rosa-Filho, J. S., Silva, M. C. N., &
Azevedo, E. F. (2010). Population dynamics the river
prawns Macrobrachium amazonicum (Heller, 1862)
(Decapoda, Palaemonidae) on Combú island (Ama-
zon estuary). Crustaceana, 83(3), 277–290. http://
dx.doi.org/10.1163/001121609X12596543952298
Mantel, S. K., & Dudgeon, D. (2005). Reproduction and
sexual dimorphism of the palaemonid shrimp Macro-
brachium hainanense in Hong Kong streams. Journal
of Crustacean Biology, 25(3), 450–459.
Mantelatto, F. L. M., & Barbosa, L. R. (2005). Population
structure and relative growth of freshwater prawn
Macrobrachium brasiliense (Decapoda, Palaemoni-
dae) from São Paulo State, Brazil. Acta Limnologica
Brasiliensia, 17(3), 245–255.
Mattos, L. A., & Oshiro, L. M. Y. (2009). Estrutura popula-
cional de Macrobrachium potiuna (Crustacea, Palae-
monidae) no Rio do Moinho, Mangaratiba, Rio de
Janeiro, Brasil. Biota Neotropica, 9(1), 81–86. https://
doi.org/10.1590/S1676-06032009000100010
Meireles, A. L., Valenti, W. C., & Mantelatto, F. L. (2013).
Reproductive variability of the Amazon River
prawn, Macrobrachium amazonicum (CARIDEA,
PALAEMONIDAE): influence of life cycle on egg
production. Latin American Journal of Aquatic
Research, 41(4), 718–731. https://doi.org/10.3856/
vol41-issue4-fulltext-8
Melo, G. A. S. de, Magalhães, C., Bond-Buckup, G., & Buc-
kup, L. (2003). Manual de identificação dos crustacea
decapoda de água doce do Brasil (1st ed.). Museu de
Zoologia USP.
Melo, O. de A., da Silva, L. M. A., Lima, J. de F., Silva, S. L. F.,
Sousa, P. H. C., Duarte, S. S., & Cintra, I. H. A. (2022).
Estrutura populacional do camarão-da-Amazônia
Macrobrachium amazonicum (Heller 1862) na foz
do Rio Amazonas. Brazilian Journal of Animal and
Environmental Research, 5(1), 490–511. https://doi.
org/10.34188/bjaerv5n1-038
Montoya, J. V. (2003). Freshwater shrimps of the genus
Macrobrachium associated with roots of Eichhornia
crassipes (Water Hyacinth) in the Orinoco Delta (Ven-
ezuela). Caribbean Journal of Science, 39(1), 155–159.
Moraes-Riodades, P., & Valenti, W. C. (2002). Cresci-
mento relativo do camarão canela Macrobrachium
amazonicum (Heller) (Crustacea, Decapoda, Palae-
monidae) em viveiros. Revista Brasileira de Zoo-
logia, 19(4), 1169–1176. https://doi.org/10.1590/
S0101-81752002000400023
Mossolin, E. C., & Bueno, S. L. S. (2003). Relative growth
of the second pereiopod in Macrobrachium olfersi
(Wiegmann 1836) Decapoda, Palaemonidae). Crusta-
ceana, 76(3), 363–376.
Odinetz-Collart, O. (1991). Stratégie de reproduction de
Macrobrachium amazonicum en Amazinie Centrale.
Crustaceana, 61(3), 253–270.
Perroca, J. F., Nogueira, C. S., Carvalho-Batista, A., & Costa,
R. C. (2022) Population dynamics of a hololimnetic
population of the freshwater prawn Macrobrachium
amazonicum (Heller, 1862) (Decapoda, Palaemoni-
dae) in southeastern Brazil. Aquatic Ecology, 56(1),
21–34. https://doi.org/10.1007/s10452-021-09889-8
Ramos, A. S., Pereira, L. de J. G., Cintra, I. H. A., & Bentes,
B. (2016). Etnoconhecimento de pescadores artesa-
nais de Macrobrachium rosenbergii em campos alaga-
dos de uma região Amazônica-Brasil. Acta of Fisheries
and Aquatic Resources, 4(1), 93–105.
Rocha, G. L., Costa, T. V. da., Machado, N. de J. B., Gual-
berto, T. L., & Muniz-Júnior, J. C. B. (2023). Effect
of two diets on the fecundity of ablated and nona-
blated females of Macrobrachium amazonicum. Acta
Scientiarum. Animal Sciences, 45, 59–78. https://doi.
org/10.4025/actascianimsci.v45i1.59780
Román-Contreras, R. (1979). Contribución al conocimien-
to de la biología y ecología de Macrobrachium tene-
llum (Smith) (Crustacea, Decapoda, Palaemonidae).
Anales del Centro de Ciencias del Mar y Limnología,
2, 137–160.
Sampaio, C. M. S., Silva, R. R., Santos, J. A., & Sales, S. P.
(2007). Reproductive cycle of Macrobrachium ama-
zonicum females (Crustacean, Palaemonidae). Brazil-
ian Journal of Biology, 67(3), 551–559. https://doi.
org/10.1590/S1519-69842007000300022
Silva, K. C. de A., Souza, R. A. L., & Cintra, I. H. A. (2002).
Camarão-cascudo Macrobrachium amazonicum
(Heller, 1862) (Crustacea, Decapoda, Palaemonidae)
no município de Vigia, Pará, Brasil. Boletim Técnico-
Científico do CEPNOR, 2(1), 41–73.
Silva, M. C. N, Frédou, F. L., & Filho, J. S. R. (2007). Estudo
do crescimento do camarão Macrobrachium amazoni-
cum (Heller, 1862) da Ilha de Combú, Belém, Estado
do Pará. Amazônia: Ciência e Desenvolvimento, 2(4),
85–104.
13
Revista de Biología Tropical, ISSN: 2215-2075, Vol. 73: e4ahgnf87, enero-diciembre 2025 (Publicado Jul. 28, 2025)
Silva, R. C. (2014). Ecologia populacional e reprodutiva de
Macrobrachium amazonicum (Heller, 1862) (Deca-
poda: Palaemonidae) no reservatorio da usina hidre-
létrica de Miranda, rio Araguari, MG [Unpublished
Licenciate thesis]. Universidade Federal de Uberlân-
dia, Minas Gerais, Brazil.
Silva, R. C., Cunha, M. C., Mossolin, E. C., & Jacobucci,
G. B. (2019). Population structure of Macrobrachium
amazonicum (Heller, 1862) (Decapoda: Palaemo-
nidae) in Miranda Hydroelectric Plant Reservoir,
Araguari river, Minas Gerais, Brazil. Acta Limno-
logica Brasiliensia, 31, e14. https://doi.org/10.1590/
S2179-975X4318
Soeiro, R. K. S., Rocha, C. P., Maciel, M., Abrunhosa, F.
A., & Maciel, C. R. (2016). Relação entre a origem
costeira de Macrobrachium amazonicum e o nível de
salinidade na larvicultura. Boletim do Instituito de
Pesca, 42(3), 691–703.
Sterzelecki, F. C., Santos, G. R., de Gusmão, M. T. A., de
Carvalho, T. C. C., dos Reis, A. R., Guimarães, R.,
Santos, M. de L. S., de Melo, N. F. A. C., Luz, R. K., &
Palheta, G. D. A. (2021). Effects of hydroponic supple-
mentation on Amazon river prawn (Macrobrachium
amazonicum Heller, 1862) and lettuce seedling (Lac-
tuca sativa L.) development in aquaponics system.
Aquaculture, 543, 736916. https://doi.org/10.1016/j.
aquaculture.2021.736916
Truesdale, F. M., & Mermilliod, W. J. (1979). The river
shrimp Macrobrachium ohione (Smith) (Decapoda,
Palaemonidae): Its abundance, reproduction, and
growth in the Atchafalaya River basin of Louisiana,
U.S.A. Crustaceana, 36(1), 61–73. https://ui.adsabs.
harvard.edu/link_gateway/1979Crust..36...61T/
doi:10.1163/156854079X00212
Ventura, E., Winick-Silva, A., & Shinozaki-Mendes, R.
A. (2019). Ovarian development and spawning of
Macrobrachium amazonicum (Crustacea, Decapoda).
Iheringia. Série Zoologia, 109, e2019026. https://doi.
org/10.1590/1678-4766e2019026
Zar, J. H. (1999). Biostatistical Analysis (4th ed.).
Prentice-Hall.