Volume 9, Manuscript ID es20260003,
p. 01-10, 2026
Doi: https://doi.org/10.32435/envsmoke-2026-0003
Environmental Smoke, e-ISSN: 2595-5527
“A leading multidisciplinary peer-reviewed
journal”
Full
Article:
MULTIPLE OBSERVATIONS OF
MORPHOLOGICAL ANOMALIES IN Macrobrachium amazonicum (HELLER, 1862) (DECAPODA:
PALAEMONIDAE) FROM AN AMAZONIAN URBANIZED AREA
Rafael Lima de Barros1 (https://orcid.org/0009-0000-9909-1771); Déborah Elena Galvão Martins1,2* (https://orcid.org/0000-0002-3829-4388); Girlene Fábia Segundo Viana3 (https://orcid.org/0000-0001-6127-3553); Israel Hidenburgo Aniceto Cintra1
(https://orcid.org/0000-0001-5822-454X); Flavio de Almeida Alves-Júnior1,2 (https://orcid.org/0000-0003-3002-6845)
1Laboratório de Crustáceos (LabCrus), Socio-Environmental and Water Resources
Institute (ISARH), Federal Rural University of Amazônia (UFRA), Avenida
Presidente Tancredo Neves, nº 2501, Terra Firme, CEP: 66077-830, Belém, Pará,
Brasil
2Núcleo de Ecologia Aquática
e Pesca da Amazônia (NEAP), Post-Graduate Programme in Aquatic
Ecology and Fisheries (PPGEAP), Federal University of Pará (UFPA), Avenida
Perimetral, 2651, Terra Firme, 66077-530 Belém, Pará, Brasil
3Bentos Laboratory (LABENTOS), Serra Talhada
Academic Unit (UAST), Federal Rural University of Pernambuco (UFRPE), Avenida
Gregório Ferraz Nogueira, s/n, 56909-535 Serra Talhada,
Pernambuco, Brasil
*Corresponding author: deborah.martins@ufra.edu.br
Submitted on: 27 Nov. 2025
Accepted on: 08 Jan. 2026
Published on: 06 Feb. 2026
License:
https://creativecommons.org/licenses/by/4.0/
Abstract
Herein, we describe multiple occurrences of
morphological abnormalities in Macrobrachium amazonicum
(Heller, 1862) collected in a hypertrophic urban river that flows through the
city of Belém, Pará State, Eastern Amazonia, Brazil. The samples were performed
between 2022 and 2025, using traditional local traps called “matapi” placed in shallow areas of the Guamá River
(01°27’54.2”S; 048°26’02.6”W).
After sampling, all individuals were transported to the
Laboratório de Crustáceos
(LabCrus/UFRA) where they were identified, sexed, measured, and only the
anomalous specimens were photographed. A total of 4,830 individuals of M.
amazonicum were collected, of which 54 (8 males and 46 females),
corresponding to 1.12% of the total, showed abnormalities. The deformities were
observed in the rostrum (68.5%) and in the telson (31.5%). The highest
incidence of abnormal females was observed in May and June 2022, with other
peaks in March and August 2023; while for males, the highest presence of
abnormalities was in August 2025. The Guamá River receives heavy inflows of
urban and industrial effluents, which may be one of the causes of the anomalies
observed in M. amazonicum. However, other conditions may be
associated with these anomalies, such as nutritional or genetic factors. This
study increases the knowledge on morphological abnormalities in shrimps,
especially in M. amazonicum, and highlights
the need for biological and environmental monitoring along the main urban river
(Guamá River) in the city of Belém, Pará.
Keywords: Rostral
anomalies. Telson abnormal. State of Pará. Prawn anomalies. Guamá River.
1
Introduction
The Amazon river prawn Macrobrachium
amazonicum (Heller, 1862) is one of
the most representative species within the family Palaemonidae Rafinesque, 1815, which has a wide geographical
distribution in hydrographic basins and estuarine areas of South America,
especially associated with tropical and subtropical regions (HOLTHUIS, 1952; MAGALHÃES,
2000; RODRIGUES et al., 2025). In the Amazon region, M. amazonicum is characterized as a fishery
resource of great economic and social importance, where it is exploited both
for the subsistence of riverside communities and for local trade (MACIEL; VALENTI, 2009; ALCÂNTARA;
KATO, 2016; SILVA et al., 2017). Additionally,
this species may be assigned as an environmental biomonitor
(CARDENAS-CAMACHO; GONZÁLEZ-REINA; VELASCO-SANTAMARÍA, 2024); however, few
studies have been conducted in northern Brazil.
In this scenario, morphological
abnormalities may be seen as indicators of stress in the animal, since
structural deformities are often associated with chemical contamination and
ecological imbalances (MANTELATTO et al., 1999; LOPES et al.,
2008; MARQUES; AMÉRICO-PINHEIRO, 2020). Additionally, these changes may have multiple causes, including
genetic factors, failures in the molting process, parasitism, mechanical
injuries or environmental pressures such as pollution and reduced availability
of food resources (SCELZO, 1998; CAMPOS-CAMPOS; DUEÑAS-RAMÍREZ; GENES,
2015; SILVA; SHINOZAKI-MENDES, 2018).
Deformities in crustaceans are
frequently reported in marine shrimps, such as Glyphocrangon
aculeata (A. Milne-Edwards, 1881), Metapenaeus
affinis (H. Milne Edwards, 1837), Mierspenaeopsis hardwickii
(Miers, 1878), Penaeus (Litopenaeus) vannamei Boone, 1931, Penaeus (Farfantepenaeus)
duorarum Burkenroad,
1939 among other penaeid shrimps (SIVAGAM; RAO, 1968;
SAKAEW et al., 2008; RAIJKUMAR et al.,
2016; ALVES-JÚNIOR et al., 2018;
WAKIDA-KUSUNOKI et al., 2020). Recently,
some investigations have reported anomalies in freshwater shrimp, such as the
studies performed by Martins et al. (2022) and
Calandrini et al. (2025), which documented morphological changes in M.
amazonicum in the state of Pará (Northern Brazil), revealing deformities in
structures in the rostrum and telson.
The
Belém metropolitan area (Pará State) represents a region of intense anthropic
pressure, characterized by disorderly urban growth, the discharge of domestic
and industrial effluents, siltation, and changes in the water quality of rivers
and streams (SANTOS et al., 2014; LIMA; LIMA; KUBOTA, 2021).
These
factors, combined with continuous fishing (SILVA, FRÉDOU, ROSA-FILHO, 2007),
may contribute to the emergence of morphological changes in aquatic organisms,
especially due to environmental degradation.
Thus,
we describe the morphological anomalies observed in the Amazon
river prawn Macrobrachium amazonicum, collected from the Guamá
River, in Belém metropolitan area, Pará State.
2 Material
and Methods
The samples were collected in a floodplain area on the
banks of the Guamá River (01°27’54.2”S; 048°26’02.6”W), one
of the main rivers that flows through the city of Belém in the state of Pará (Figure
1).
Figure
1. Map of the study
area (Belém-PA), showing the sampling location of the Amazon river
prawn Macrobrachium amazonicum (Heller, 1862) on the banks of the Guamá
River.
The Guamá River basin occupies approximately 12,584 km2,
covering nineteen municipalities (ROCHA; LIMA, 2020).
In addition, it receives constant inputs of domestic
waste from Belém metropolitan area, as well as chemical elements from mining
activities, showing a high degree of eutrophication, characterized by waters
rich in suspended particles of silt and clay (PAIVA et al., 2006; SANTOS
et al., 2014; SANTOS et al., 2020; LIMA;
LIMA; KUBOTA, 2021).
Belém has a humid equatorial climate, characterized by high
temperatures and high humidity throughout the year. The average annual
temperature is approximately 26.7 °C, accompanied by rainfall reaching around
3,000 mm per year, with a dry season from June to November and a rainy season
from December to May (SILVA-JUNIOR et al.,
2012; SANTOS et al., 2019).
The specimens of M. amazonicum were collected monthly between January 2022 and August 2025, using four traditional local
traps called “matapi”,
baited with babassu bran Attalea speciosa Martius,
1826.
After sampling, the individuals were transported to the Laboratório
de Crustáceos (LabCrus)
at the Universidade Federal Rural da
Amazônia (UFRA).
In the laboratory, the
shrimps were identified following Melo (2003), sexed and measured with analog
vernier calipers (0.05 mm) in total length (TL), carapace length (CL) and wet
weight (WW) (g).
The anomalous specimens were photographed using a
Nikon D5300 camera, and then they were stored
in 70% alcohol and deposited in the Carcinological Collection of the LabCrus-UFRA under voucher number 74.1.1 Z.
3 Results
and Discussion
We
collected 4,830 individuals of M. amazonicum, of which 54 (8 males and
46 females) showed morphological anomalies, corresponding to 1.12% of the total
samples. Among the abnormal specimens, the females were predominant, with the
sex ratio of 1M:5.75F. In natural Amazonian populations, several studies have indicated
that females are more abundant than males, reaching up to 85% of inland water
populations (ODINETZ-COLLART, 1887; GARCÍA-DÁVILA et al., 2000; MONTOYA,
2003; COSTA; MATOS; MACHADO, 2016); this observation may justify a higher
prevalence of anomalies in females of M. amazonicum in the Guamá River. The analysis of the
temporal distribution of the occurrences of morphological anomalies revealed
that the records were not continuous throughout the sampled years, showing the
highest incidence of abnormal females in August 2023; while the abnormal males
were more abundant in July 2024 and August 2025 (Figure
2).
Figure
2. Occurrence of morphological anomalies in Macrobrachium
amazonicum (Heller, 1862), collected between 2022 and 2025, in the Guamá River,
Belém metropolitan area, Pará.
Along the sampled months, a
low incidence of these anomalies in the Guamá River was observed (between one
and two individuals). Similar results were observed by Martins et al. (2022)
and Calandrini et al. (2025), which indicated that specific events of environmental
impact (sewage or chemical compounds) may be associated with a high prevalence
of anomalies in the population.
In studies developed by Fransozo
et al. (2012), the authors observed external anomalies in crabs Callinectes ornatus
(Ordway, 1863), Arenaeus cribrarius (Lamarck, 1818) and Leurocyclus tuberculosus (H. Milne Edwards & Lucas, 1843), from the state
of São Paulo, which indicated that
morphological anomalies may be associated with highly impacted environments.
Additionally, Silva and
Shinozaki-Mendes (2018) analyzed abnormalities
in Minuca rapax (Smith,
1870), with one male specimen showing bilateral hypertrophy.
Low incidences of these anomalies have been reported
in several studies (AGUIRRE; HENDRICKX, 2005;
GREGATI; NEGREIROS-FRANSOZO, 2009;
ALVES-JÚNIOR et al., 2018),
which suggested that these anomalies may be associated with specific factors
(e.g. nutritional, genetic changes or bacteriological/viral presence) and physicochemical
changes in water, affecting some individuals in the population.
Biometric analysis of anomalous specimens of M.
amazonicum revealed differences between the sexes
(Table 1). The females showed higher
mean values across all variables (TL: 63.6 mm, CL: 29.5 mm and WW: 2.32 g),
while the males showed lower mean values (TL:
52.8 mm, CL: 22.5 mm and WW: 15.2 g), all
variables including mean and standard deviation,
are placed in Table 1.
Table 1. Total length (TL), carapace length (CL) and wet weight (WW) per sexes,
including minimum (Min.), maximum (Max.) mean, median and standard deviation
(Stand. Dev.) of anomalous specimens of Macrobrachium amazonicum
(Heller, 1862) collected in the Guamá River (Belém-PA) between 2022 and 2025.
|
Variables |
Sex |
Min. |
Max. |
Mean |
Median |
Stand. Dev. |
|
TL (mm) |
Males |
37.4 |
68.6 |
52.8 |
51.3 |
1.17 |
|
Females |
42.5 |
92.0 |
63.6 |
64.2 |
1.06 |
|
|
CL (mm) |
Males |
15.3 |
34.5 |
22.5 |
21.8 |
0.63 |
|
Females |
17.1 |
47.0 |
29.5 |
29.6 |
0.68 |
|
|
WW (g) |
Males |
0.45 |
3.8 |
1.52 |
1.43 |
1.05 |
|
Females |
0.61 |
4.99 |
2.32 |
2.15 |
1.00 |
The larger body size of females is consistent with
observations already reported for Palaemonidae, a pattern related to
reproductive biology, especially the need for greater body volume to
accommodate egg development and incubation (MULLER et al., 1996;
PASCHOAL; GUIMARÃES; COUTO, 2013).
However, other studies on M. amazonicum
reported opposite results, showing that males reach greater lengths, especially
in adults, with similar growth observed in both sexes only until they reach
sexual maturity (SILVA; SOUZA; CINTRA, 2002; FLEXA; SILVA; CINTRA, 2005; SILVA; FRÉDOU; ROSA FILHO, 2007; COSTA et al., 2016).
These sexual differences may reflect adaptive
strategies related to survival and reproductive success, since males and
females allocate energy differently between growth, reproduction, and
physiological maintenance. In addition, the type of environment, such as
freshwater (lotic or lentic) or estuarine areas, may influence the relative
growth of the species, which may indicate fluctuations in size due to the
natural environment or anthropogenic impacts in the region (ODINETZ-COLLART; 1988, 1991; ODINETZ-COLLART; MOREIRA,
1993; RODRIGUES et al., 2025).
We observed morphological anomalies in two body
regions: the rostrum and the telson. Most occurrences were identified
in the rostrum, accounting for 68.5% of all anomalies (Figure
3A-I), while the telson was anomalous in 31.5% of the specimens analyzed (Figure
4A-I). No specimens presented anomalies in both structures.
Figure
3.(A-I) - Records of rostral anomalies
in Amazon river prawn Macrobrachium amazonicum (Heller, 1862), collected in the Guamá River
(Belém-PA), between 2022 and
2025. Scale bar = 5 mm.
Figure
4.(A-I) - Records of telson anomalies in Amazon river prawn Macrobrachium
amazonicum (Heller, 1862), collected in the Guamá River (Belém-PA), between
2022 and 2025. Scale bar =
5 mm.
The occurrence of morphological deformities in
crustaceans is a relatively undocumented phenomenon in Amazonian freshwater
environments. For M. amazonicum, especially in Northern
Brazil, there are only two recent studies describing morphological
abnormalities (MARTINS et al., 2022; CALANDRINI et
al., 2025). Martins et al. (2022) provided the first description of
abnormalities from this species, indicating body changes in three specimens
from the low Tocantins River (Cametá, state of Pará).
Their specimens showed a short rostrum
with strong curvature and changes in rostral spines, in addition to the first
descriptions of the bifid telson for the species.
Recently, Calandrini et al.
(2025) reported 20 anomalous specimens (corresponding to 0.9% of the total
sampled), showing a large variation in the rostrum shape, from the Xingu River (also state of Pará), the
authors observed a reduction in rostrum length and a decrease in the number of
rostral teeth (covering 1-7 in superior margin and 1-5 in ventral margin).
Both
studies mentioned above emphasize that these deformities may be associated with
environmental impacts or genetic/nutritional alterations; however, further
studies are needed to understand their origin.
Anomalies are commonly reported in
estuarine and marine (including
deep-sea) caridean shrimps; these observations usually include a shortened rostrum
with strong curvature, absence or reduction in the number of spines, and
a bifid telson or one that is strongly curved to the side (SIVAGAM; RAO, 1968;
SAKAEW et al., 2008; ALVES-JÚNIOR et al.,
2018).
According
to Melo (2003), the Amazon river prawn M.
amazonicum has a long and slender rostrum, surpassing the scaphocerite,
with the middle portion curved upward; containing 9 to 13 dorsal spines and 8
to 10 in ventral margin.
In
our specimens, all anomalous shrimps presented a shortened rostrum, with
reduced number of spines (ranging from 1-7 dorsal spines and 1-5 ventral
spines), or without spines in some specimens (see Fig. 3A and C). These
morphological changes may compromise their survival in the natural environment,
as the animals have reduced or absent defenses against predators (BENETTI;
NEGREIROS-FRANSOZO, 2003; GREGATI; NEGREIROS-FRANSOZO, 2009; PINHEIRO; TOLEDO,
2009; WAKIDA-KUSUNOKI et al., 2020). Normal specimens of M. amazonicum
have a conical telson, with the posterior margin ending in an acute median
point, surrounded by four spines (two long and two reduced) and two pairs of
dorsal spines (MELO, 2003).
Nonetheless, most of our individuals
showed a bifid telson, with some specimens presenting curved forms or absence
of telson tip (see Fig. 4). These
modifications reduce the protective function against predators and also compromise swimming mobility (AYUB; AHMED, 2004; ALVES-JÚNIOR et al., 2018; MARTINS et al.,
2022).
4
Conclusions
In
conclusion, our results reveal a continual yet reduced presence of
morphological abnormalities in M. amazonicum collected from the Guamá
River (54 individuals, 1.12% of the total sampled), showing a high range of
rostrum and telson shape forms. Despite the environmental degradation observed
in the Guamá River, these morphological anomalies may also be related to
nutritional or genetic factors, as well as to the presence of microorganisms
(fungi, bacteria, and viruses) that could have a negative effect on the shrimp
morphology. In this scenario, we expanded knowledge about anomalies in shrimp
in northern Brazil, highlighting the need for further studies to identify the
causes of the morphological anomalies reported for Amazon river
prawn M. amazonicum, and how anthropogenic actions are impacting aquatic
populations along the urbanized areas of the Guamá River.
CREDIT AUTHORSHIP CONTRIBUTION STATEMENT
Conceptualization:
R.L.B., D.E.G.M., G.F.S.V., I.H.A.C. and F.A.A.J. Research, development and
writing: R.L.B., D.E.G.M., I.H.A.C. and F.A.A.J. Sample Analysis: R.L.B.,
D.E.G.M. and F.A.A.J. Map and images development: R.L.B. and D.E.G.M. Review:
D.E.G.M., G.F.S.V., and F.A.A.J. Review and correction: D.E.G.M. and F.A.A.J.
Translation to English: D.E.G.M and F.A.A.J.
DECLARATION OF INTEREST
The authors disclose that
they have no known competing financial interests or personal relationships that
could have appeared to influence the study reported in this manuscript.
FUNDING SOURCE
The author Israel Cintra
has the productivity grant award, reference number: 304401/2025-0 by the Conselho Nacional de Desenvolvimento
Científico e Tecnológico – CNPq
(Brasil).
ACKNOWLEDGEMENTS
The
authors would like to thank the Centro
Nacional de Pesquisa e Conservação da Biodiversidade Marinha do Norte, Instituto Chico Mendes
de Conservação da Biodiversidade
(CEPNOR/ICMBIO) for the support in the laboratory. Additionally, we would like
to thank the anonymous reviewers for all comments throughout the manuscript.
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