HEAVY METAL CONCENTRATIONS IN FISH FROM THE LOWER PORTION OF PARAIBA DO
SUL RIVER, RJ, BRAZIL.
Maria E. F. Totti (Laboratório de Estudo do Espaço Antrópico,
Universidade Esetadual do Norte Fluminense); Cristina Ma M. Souza
& Paulo Pedrosa (Laboratório de Ciências Ambientais, Universidade Estadual
do Norte Fluminense, CEP: 28015-620, RJ, Brazil, cristal@cbb.uenf.br).
Abstract
Fe, Mn, Cu, Cr, Zn, Cd and Hg were measured in edible parts of 4 non
carnivorous fish species (Prochilodus scrofa, Mugil platanus,
Tilapia rendalli, Geophagus brasiliensis) and 1 carnivorous specie (Hoplias
malabaricus), in lower portion of Paraiba do Sul river, RJ, Brazil. The
samples were obtained from local markets and or directly from local fishermen.
In general all metals showed lower concentrations values than that permissible
in Brazilian legislation. The exception were Cr for all samples (until 30 times
above) and Hg in Hoplias mallabaricus (1.1 times above). Cr values found
in this study suggest a point source
contamination in the area, probably a tanning, situated in neighborhood.
Mercury values found probably can be related with non point sources occurred in
the past such as the utilization of organomercurial fungicides and gold mining
activities.
Introduction
The role of heavy metals in aquatic organisms
has been drawn attention, since the events of mercury and cadmium poisoning
through seafood and fish in Japan. Only after this, has the accent been shifted
towards investigations dealing with the influences of heavy metals on the
metabolism of aquatic organisms and the ability of the latter to accumulate
both essential and non-essential metals (Förstner & Wittmann, 1984).
Elements like
copper, zinc, iron and cobalt have important biochemical functions in the
organism, participating as ligands in complex enzymatic compounds. Therefore,
their enrichment does not exceed the
level which allows the enzyme system to function without interference (Lowman
et al., 1971). This means that the concentrations of essential trace elements
are generally higher in the organism than in water. On the other side, if the
heavy metal concentration at the source of supply is too high, the homeostatic
mechanisms cease to function and the essential heavy metals act in either
acutely or chronically toxic manner (Phillips et al., 1982). Thus in the event
of a resulting extended bioaccumulation
of heavy metals the organism may be damaged (Balkas et al., 1982; Young et al.,
1981).
This work
investigate the heavy metal concentrations (Fe, Mn, Cr, Cd, Zn and Hg) in
edible parts of fish to evaluate the quality of this important protein source
to local population.
Methodology
The Paraiba do Sul river is the major
freshwater supply to the south-eastern Brazilian coast. It is a medium sized
river 1145 km long and also drains (55400 km2) an important
industrial park and the second largest sugar cane production area of the
country (Carvalho et al, 1999). Some works have been related heavy metals
contamination degrees in the area (Torres, 1992; Malm, 1986). Six surveys were
carried out in lower portion of the river, Campos dos Goytacazes city (210
45’23” S, 410 19’49” W), from April, 1997 to October, 1997. The 29
samples considered in this study are representatives of the 5 species (table 1)
caught and commercialized in the area.
Table 1: Fish species considered in this study.
|
Fish |
Food habits |
|
|
Scientific name |
Common name |
|
|
Prochilodus scrofa |
Xingó |
I |
|
Mugil platanus |
Tainha |
D, H |
|
Tilapia rendalli |
Tilapia |
O |
|
Geophagus brasiliensis |
Acará |
O |
|
Hoplias malabaricus |
Traíra |
C |
C= carnivorous ; D=
detritivorous ; I= iliofagous ; O= omnivorous
These samples were
obtained from local markets and or directly from local fishermen. Each fish was
weighted and its length measured at the laboratory. The edible parts were
separated and frozen until analysis. After lyophilized, the humidity weight was
calculated.
The digestion procedure utilized for total
metals determination was performed using 1g ± 0.001g of dried samples. After calcination at
450 0C during 24hours, the samples were placed in teflon bomb with
an acid mixture (HNO3/H2O2, 3:1) in a oven
(1100C) during 12h (Krause et al., 1995). For mercury, the samples were wet digested using a oxidant
mixture (H2SO4/HNO3, 1:1) and KMnO4
5% (Bastos et al., 1998). To certify the quality control, a reference fish
sample was analyzed (Standard reference material DORM 1- NIST), in the same way that a internal fresh fish sample
supplied by Biophysics Institute in Rio de Janeiro (Radioisotope Laboratory)
was performed. The results showed higher than 80% recovery for all metals with variation coefficients for
analytical replicates bellow than 10%. All metal determinations was performed
by ICP - AES (Varian Liberty Series II), using a VGA accessory for Hg.
Results And Discussion
Table 2 presents
the average total concentration of heavy metals and its respective
concentration ranges in all samples analyzed in this study. The ranges for all
elements are: Fe= 0.2 – 18 mg.g -1 wet wt; Mn= 0.24 – 0.80mg.g -1 wet wt; Cd= <DL – 0.23mg.g -1 wet wt; Zn= 2.4 – 5.8mg.g -1 wet wt; Cr= 0.2 – 2.8mg.g -1 wet wt.
In general all metals showed lower
concentrations values than that permissible in Brazilian legislation. The
exception were Cr for all samples (until 30 times above) and Hg in Hoplias
mallabaricus (1.1 times above).
Table 2: Heavy metals in muscle tissues of fresh fish (mg.g -1 wet wt). Average, and
concentration ranges.
|
Fish species |
Metals (mg.g -1 w wt) |
|||||
|
|
Fe |
Mn |
Cr |
Cd |
Zn |
Hg |
|
|
---- |
---- |
0.1* |
1.0* |
50* |
0.5* |
|
Prochilodus scrofa n = 6 |
8.1 5.1-10.5 |
0.53 0.30-0.70 |
0.31 0.15-0.52 |
<DL |
3.5 3.2-4.1 |
0.09 0.05-0.14 |
|
Mugil platanus n = 5 |
18.4 8.9-38.3 |
0.80 0.27-1.6 |
0.23 0.17-0.30 |
<DL |
4.1 3.8-4.8 |
0.11 0.05-0.16 |
|
Tilapia rendalli n = 6 |
15.2 1.5-48.5 |
0.34 0.08-0.62 |
2.8 0.23-10.4 |
<DL |
3.7 3.2-3.9 |
0.09 0.06-0.15 |
|
Geophagus brasiliensis n = 6 |
0.2 0.12-0.25 |
0.39 0.11-0.78 |
0.20 0.12-0.25 |
<DL-0.01 |
2.4 4.1-5.2 |
0.27 0.25-0.29 |
|
Hoplias malabaricus n = 6 |
0.27 0.25-0.29 |
0.24 0.16-0.34 |
0.27 0.25-0.29 |
<DL-0.23 |
5.8 4.2-6.7 |
0.53 0.49-0.57 |
w wt = wet weight <DL=
lower than detection limit *safety
limit for human consumption in Brazilian legislation (Ministério da Saúde,
1975).
Chromium concentrations (0.12 - 10.4 mg.g -1 wet wt) in all analyzed
samples were higher than that established for the Brazilian legislation. In
comparison with other works these results are upper than that found by Fernandes et al. (1994) (0.08 mg.g -1 wet wt) realized in a tropical lake without contamination,
considering similar species like Geophagus
sp and Tilapia sp. On the other hand, study realized in an area with a knowledge chromium
contamination, Jordão et al. (1997)
found high concentrations (0.2 - 1.6 mg.g -1 wet wt) in different fish
species and sediments (about 80mg.g -1 ). Similar results in
suspended particulate matter (81± 42 mg.g -1 ) were found by Carvalho et
al. (1999) in lower portion of Paraiba do Sul river, suggesting chromium
remobilization processes from sediment to water. The probably source in the
area is a tanning, situated in neighborhood.
Mercury concentration ranges showed higher
values for carnivorous (0.49 - 0.57 mg.g -1 wet wt) than the other fish
species (0.05 - 0.29 mg.g -1 wet wt). This behavior is
commonly described in the literature, since this heavy metal typically
undergoes biomagnification through food chains, presenting the highest
concentrations in high trophic level fish (Huckabee et al., 1979, Lacerda &
Salomons, 1998). Besides, non point sources occurred in the past such as
utilization of organomercurial fungicides (Câmara, 1986) and gold mining activities
(Souza, 1994), probably were responsible to metal cycling inside the system.
The concentrations of Fe, Mn, Cd, Zn, and Cr
compared with Azcue (1987) in a work developed in medium portion of Paraiba do
Sul River (Fe= 8 – 77mg.g -1 ; Mn= 1.6 – 5.4mg.g -1 ; Cd= <DL – 0.11mg.g -1 ; Zn= 11 – 21mg.g -1; Cr= <DL – 0.84 mg.g -1) showed values lower than that, exceptions for Cd (almost 10 times
above) and Cr (5 times above).
In conclusion, the Cr values found in this
study suggest a point source
contamination in the area, since another research in medium portion described by Azcue did not show
that. Since these species are considered largely caught and consumed by the
local population, it should be take with care, since the hexavalent chromium
may induce carcinogenic effects. The high mercury value is restricted to
carnivorous specie (Hoplias malabaricus) suggesting organification
processes occurring in the area.
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