Volume 8, Manuscript ID
es20250001, p. 01-07, 2025
Doi: https://doi.org/10.32435/envsmoke-2025-0001
Environmental
Smoke, e-ISSN: 2595-5527
“A leading multidisciplinary
peer-reviewed journal”
Full
Article:
RECORDS OF ROSTRAL
ANOMALIES IN Macrobrachium amazonicum (HELLER, 1862) (DECAPODA: PALAEMONIDAE) COLLECTED
ALONG THE GREAT AMAZON RIVER BASIN
Gabriel San Machado
Calandrini1* (https://orcid.org/0000-0001-6321-2228); Yuri Antonio da Silva
Rocha2 (https://orcid.org/0009-0004-3055-5653); Paulo José Cabral de Miranda Lima3 (https://orcid.org/0009-0003-6434-4275); Fabiola Seabra Machado3
(https://orcid.org/0000-0003-3292-6441); Danielly Torres Hashiguti de Freitas1 (https://orcid.org/0000-0001-9443-6646); Flavio de Almeida Alves-Júnior1 (https://orcid.org/0000-0003-3002-6845)
1Universidade Federal
do Pará, Núcleo de Ecologia Aquática e Pesca (NEAP), Programa de Pós-Graduação
em Ecologia Aquática e Pesca (PPGEAP), Rua Augusto Corrêa, S/N Guamá, CEP:
66075-110, Belém, Pará, Brasil
2Universidade Federal
do Pará (UFPA), Instituto de Geociências (IG), Rua Augusto Corrêa, S/N Guamá,
CEP: 66075-110, Belém, Pará, Brasil
3Universidade Federal
do Pará (UFPA), Grupo de Ecologia Aquática (GEA), Rua Augusto Corrêa, S/N
Guamá, CEP: 66075-110, Belém, Pará, Brasil
*Corresponding author: gabriel_alandrini@hotmail.com
Submitted on: 26 Feb. 2025
Accepted on: 16 Mar. 2025
Published on: 22 Mar. 2025
License:
https://creativecommons.org/licenses/by/4.0/
Abstract
Morphological
anomalies in decapod crustaceans are frequently reported in studies around the
world, some of which are due to anthropogenic actions through environmental
impacts. These deformities can affect different structures (e.g., carapace,
scaphocerite, rostrum, chelipeds, abdomen and telson) and interfere with
development, feeding, resource competition, and reproductive behavior of
crustaceans. The palaemonid shrimps occur in various ecosystems, covering
marine and freshwater areas; however, few studies report morphological
anomalies in freshwater shrimps in Brazil. Therefore, this study aimed to
report and catalog the morphological anomalies in the rostral forms of the
shrimp Macrobrachium amazonicum (Heller, 1862), collected from the Great
Amazon River Basin, Pará, Brazil. The specimens were captured during
collections carried out along the Xingu River watershed, near the
municipalities of Altamira and Vitória do Xingu, using bamboo traps, known as “matapis,” baited with babassu. After the samples, the
specimens were sorted out, and transported to the laboratory for subsequent
biometric measurements, weighing, taxonomic identification, and registration of
the abnormalities. A total of 2.199 specimens of the M. amazonicum were
collected, being identified twenty shrimps with anomalies in the rostral
region, corresponding to 0.9% of the total number of shrimps analyzed. Herein,
the anomalies observed consisted of a reduction in the size of the rostrum,
with varying shapes, and a decrease in the number of rostral teeth compared to
the expected for the species. Further studies are needed to identify the
potential causes of the anomalies in shrimps from the Amazon region.
Keywords: Amazon River
shrimp. Morphological anomalies. Eastern Amazon. State of Pará.
1
Introduction
Morphological anomalies in decapod crustaceans have been
recorded since the nineteenth century (AGUIRRE; HENDRICKX, 2005) and are
frequently reported in studies worldwide, involving shrimps, crayfish,
lobsters, and crabs (MARIAPPAN; BALASUNDARAM; SCHMITZ, 2000; FOLLESA et al.,
2008; ARAÚJO; CALADO, 2012). These anomalies can affect various body
structures, including the carapace, scaphocerite, rostrum, chelipeds, uropods
and telson, potentially interfering with species development, feeding, and
ecological interactions, such as competition for resources or reproductive
behaviour (ARAÚJO; CALADO, 2012; LEVESQUE et al., 2018).
With
approximately 1.200 described species occupying diverse environments and
ecosystems worldwide (FROLOVÁ; HORKÁ; ĎURIŠ, 2022), shrimps of the family Palaemonidae Rafinesque, 1815 are abundant organisms in
marine and freshwater areas, with significant economic and ecological
importance (GARCÍA-GUERRERO et al., 2013) serving as excellent bioindicators of
environmental quality (WEBB, 2011). However, environments impacted by the
release of organic or chemical pollutants, along with factors such as climate
change, can severely affect the development of shrimp and other decapods,
leading to various issues, including morphological anomalies (BÉGUER et al.,
2010; ARAÚJO; CALADO, 2012; FEUILLASSIER et al., 2012; LEVESQUE et al., 2018).
Some
genera of palaemonid shrimps, such as Macrobrachium Spence Bate, 1868
and Palaemon Weber, 1795, have already been documented with structural
deformities (DE GRAVE, 1999; DE GRAVE; MENTLAK, 2008; MARTINS et al., 2022). Up
to date, countless anthropogenic impacts have affected the morphology of the
shrimps, for instance, Feuillassier et al. (2012)
reported anomalies in the cephalothorax and rostrum of Palaemon longirostris
Milne Edwards, 1837, and Palaemon macrodactylus
Rathbun, 1902, and Levesque et al. (2018) observing abnormalities in the Palaemon
longirostris, which both authors indicated environmental impacts as
possible causes of these anomalies.
The
Amazon River shrimp Macrobrachium amazonicum Heller, 1862, is a taxon widely distributed across Brazil and abundant in the
Amazon Basin, with high ecological and social importance (BÉGUER et al., 2010;
BENTES et al., 2011). Additionally,
Martins et al. (2022) observed body abnormalities in the M. amazonicum.
For
shrimps of the genus Macrobrachium, certain anomalies can potentially
hinder taxonomic identification, as features like the number of rostral spines
or telson shape are critical for species-rank classification (MELO, 2003).
Although
these anomalies have been recorded in the literature, studies focusing on
morphological anomalies in Macrobrachium shrimps remain scarce,
particularly concerning shrimp from Amazonian rivers. Therefore, this study
aims to characterize the morphological anomalies observed in the shrimp M.
amazonicum collected from the Great Amazon River Basin (Xingu River), Pará,
Brazil.
2 Material
and Methods
Study
Area
The samples were carried out in
the Xingu River (see Supplementary Table 1) (Fig. 1), which is a major
clearwater tributary of the Amazon River (Schmid et al., 2024).
Figure 1. Map of the
monitoring points (MP) for shrimp in the hydrographic region of the Xingu River
(Pará, Brazil).
The monitoring points (MP)
correspond to hydrographic locations of the Xingu River, covering the
municipalities of Altamira, Anapu, Brasil Novo, Senador José
Porfírio, and Vitória do Xingu (Fig. 1). According to the climatic zoning
conducted by Alvares et al. (2013) based on Köppen’s
criteria (1936), the region has a tropical climate of the Am type (Tropical
monsoon zone).
Field
and laboratory procedure
Sampling
was conducted along the banks of the Xingu River using artisanal traps (“matapis”), which consist of tubes made of splints with
openings at both ends through which the crustaceans can enter but have
difficulty exiting.
The
traps were baited with hydrated babassu flour (Attalea spp.), a species
of palm tree common in the Amazon region (see BENTES et al., 2011). Four traps
(“matapis”) were placed at each collection point, set
at night and retrieved in the morning. Sampling occurred quarterly between
January and October 2024.
After
collection, the samples were frozen and transported in thermal boxes to the
laboratory for identification, following the taxonomic key of Melo (2003).
Subsequently,
the organisms were measured using a calliper (0.01 mm) to determine the Total
Length (TL) and Carapace Length (CL); weighed using a precision scale (0.001 g)
to obtain the Wet Weight (WW); and finally, photographed for the preparation of
identification plates, through the camera Nikon D5300 and the Photoshop
software®.
Once
the procedures were completed, the organisms were registered in the Carcinological Collection of the Carcinology Laboratory (Labcrus) at the Federal Rural University of the Amazon
(UFRA).
3 Results
A total of 2.199 specimens of Macrobrachium
amazonicum were collected along the
Xingu River, of which 20 individuals exhibited morphological anomalies in the
rostrum shape only two stations (MP4: 3°22'14.94" S; 52°1'48.71" W [7
exemplars] and MP7: 3°34'0.37" S; 51°55'53.29" W [13 exemplars]),
accounting for 0.9% of the total shrimp collected along the total sampled area;
with the range sizes and weights (TL: 4.58-8.12 cm; CL: 1.75-2.25 cm; WW:
1.8-3.2 g). The plate of shrimp images below was made based on the specimens
with the best morphological preservation among those collected (Fig. 2).
According to Melo (2003), the species M.
amazonicum has a long rostrum with
approximately nine to twelve teeth on the upper part and eight to ten teeth on
the lower part. However, most of the anomalous shrimp had shorter, more
irregular rostrums with fewer teeth, ranging from 1 to 7 on the upper side and
1 to 5 on the lower side, with most structures being smaller than the
scaphocerite.
Figure
2. (A-H) Rostral morphological anomalies observed in
specimens of Macrobrachium amazonicum (Heller, 1862) collected in the
Xingu River, Pará State, Brazil.
Studies on morphological anomalies are rare; however, specific records
in M. amazonicum have been observed
on the rostrum and telson structures by Martins et al. (2022) for the state of
Pará, Tocantins River, Great Amazon River Basin, representing in this study the
first record of M. amazonicum morphological
anomalies reported in Brazilian freshwater environments.
Other shrimp species have also been recorded with different types of
morphological anomalies, such as those in the abdomen, as reported for Penaeus indicus Milne Edwards, 1837, by
Furthermore, De Grave; Mentlak (2008) and Feuillassier et al. (2012) documented anomalies in the
rostrums of shrimp species Palaemon
longirostris and Palaemon macrodactylus in the Gironde estuary in southwestern France.
The invasive shrimp species commonly known as the giant Malaysian prawn,
Macrobrachium rosenbergii De Man, 1879, has
also been recorded with morphological anomalies, as observed by Stalin et al.
(2013), who reported deformities in the abdominal somites,
telson, and other structures. This species was also documented by Pillai et al.
(2005) with anomalies caused by pathogens, affecting the rostrum and other
structures. Additionally, it is speculated that changes in physicochemical
factors of water, such as dissolved oxygen levels - particularly in cases of
eutrophication, or due to increases in temperature and pH - may affect shrimp
malformations (RAJKUMAR et al., 2016). Exposure to extreme environments and
physical damage caused by competition may also contribute to structural
malformations (PANDOURSKI; EVTIMOVA, 2009; BÉGUER et al., 2010; FEUILLASSIER et
al., 2012; MARTINS et al., 2022).
Aguirre and Hendrickx (2005) suggest that the observed malformations in
the shrimp analyzed may result from the regeneration
of these structures, triggered by various factors, including potential injuries
caused by trawling. On the other hand, some studies performed by Rajkumar et
al. (2016) and Ayub and Ahmed (1996) observed that environmental pollution,
pesticide contamination, and other chemical compounds can contribute to the
emergence of morphological anomalies in marine shrimps. Supporting this perspective,
Levesque et al. (2018) identified high concentrations of herbicide compounds in
areas where Palaemon longirostris
shrimp exhibited multiple morphological anomalies.
Levesque et al. (2018) and Martins et al. (2022) associated these anomalies with environmental changes that might
induce malformations in crustacean structures, potentially arising from the
larval stage, or in adults by the presence of contaminants in water and
sediments. In addition, Alves-Júnior et al. (2018) proposed that anomalies
could also originate from natural processes such as ecdysis, associated with
nutritional or congenital malformation. Finally, changes/anomalies in the
defensive structures of crustaceans can impair competition for resources and
compromise feeding, reproduction, and migration, potentially leading to higher
mortality rates among individuals (BÉGUER et al., 2010; FEUILLASSIER et al.,
2012).
4 Conclusions
Morphological anomalies can impact several aspects of the biology and
behaviour of decapod shrimp, such as changes in the rostrum, which can
primarily affect their defence strategies, making them more vulnerable to
predation and thus influencing the population dynamics. Although morphological
anomalies can affect shrimp, only 0.9% of the shrimp analyzed
in this study exhibited any abnormalities.
Therefore, more depth studies are needed to investigate the potential
causes of morphological anomalies in shrimp from the Xingu River region, and
other Amazon rivers. The causes of this phenomenon should also be studied in
further research to possibly enable prevention of the potential
environmental/anthropogenic impacts.
CREDIT AUTHORSHIP CONTRIBUTION STATEMENT
Conceptualization: F.A.A.J and
G.S.M.C.; Research, development and writing: G.S.M.C.; Sample Analysis:
G.S.M.C. and P.J.C.M.L; Map development: Y.A.S.R.; Review: F.S.M.; Review and
correction: F.A.A.J., D.T.H.F. Translation to English: G.S.M.C.
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
This study
was funded by Norte Energia S.A. (P&D-02-2020) and
the Fundação de Amparo e Desenvolvimento da Pesquisa
(FADESP) (PR-C-006/2020). The
funders had no role in the design, execution, or analyses of this study.
ACKNOWLEDGEMENTS
We thank the Federal University
of Pará (UFPA), the Center for Amazon Aquatic Ecology
and Fisheries (NEAP) and the Aquatic Ecology Group (GEA) for making this
research possible. The authors would, especially, like to thank the Editor Dr.
Dimitri Araújo Costa for his support and the anonymous reviewers for their
precious comments on this paper.
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