24 research outputs found
Can the integration of multiple biomarkers and sediment geochemistry aid solving the complexity of sediment risk assessment?: a case study with a benthic fish
Surveying toxicity of complex geochemical media as aquatic sediments often yields results that are either
difficult to interpret or even contradictory to acknowledged theory. Multi-level biomarkers were
investigated in a benthic fish exposed to estuarine sediments through laboratory and in situ bioassays, to
evaluate their employment either in ecological risk assessment or in more mechanistic approaches to
assess sediment-bound toxicity. Biomarkers reflecting lesions (such as genotoxicity or histopathology),
regardless of their low or absent specificity to contaminants, are efficient in segregating exposure to
contaminated from uncontaminated sediments even when classical biomarkers like CYP1A and metallothionein induction are inconclusive. Conversely, proteomics and gene transcription analyses provided
information on the mechanics of toxicity and aided explaining response variation as a function of
metabolic imbalance and impairment of defences against insult. In situ bioassays, although less expedite
and more affected by confounding factors, produced data better correlated to overall sediment
contamination.info:eu-repo/semantics/publishedVersio
Estuarine ecological risk based on hepatic histopathological indices from laboratory and in situ tested fish
Juvenile Senegalese soles were exposed through 28-day laboratory and field (in situ) bioassays to sediments
from three sites of the Sado estuary (W Portugal): a reference and two contaminated by metallic
and organic contaminants. Fish were surveyed for ten hepatic histopathological alterations divided by
four distinct reaction patterns and integrated through the estimation of individual histopathological condition
indices. Fish exposed to contaminated sediments sustained more damage, with especial respect to
regressive changes like necrosis. However, differences were observed between laboratory- and fieldexposed
animals, with the latest, for instance, exhibiting more pronounced fatty degeneration and hepatocellular
eosinophilic alteration. Also, some lesions in fish exposed to the reference sediment indicate
that in both assays unaccounted variables produced experimental background noise, such as hyaline
degeneration in laboratory-exposed fish. Still, the field assays yielded results that were found to better
reflect the overall levels of contaminants and physico-chemical characteristics of the tested sediments.info:eu-repo/semantics/publishedVersio
Ecological risk assessment of sediment management areas : application to Sado Estuary, Portugal
The purpose of this work was to integrate different
methodologies to assess the potential ecological risk
of estuarine sedimentary management areas, using the Sado
Estuary in Portugal as case study. To evaluate the environmental
risk of sediment contamination, an integrative
and innovative approach was used involving assessment of
sediment chemistry, sediment toxicity, benthic community
structure, human driving forces and pressures and management
areas organic load levels. The basis for decisionmaking
for overall assessment was a statistical multivariate
analysis appended into a score matrix tables, using a best
expert judgment. The integrated approach allowed to
identify from the 19 management areas analyzed, three
with no risk but other three with high risk to cause adverse
effects in the biota, related with the contaminants analyzed.
The methodologies used showed to be effective as a support
for decision making leading to future estuarine management
recommendations.peerreviewe
Biochemical endpoints on juvenile Solea senegalensis exposed
Juvenile Solea senegalensis were exposed to
fresh sediments from three stations of the Sado estuary
(Portugal) in 28-day laboratory assays. Sediments revealed
distinct levels of total organic matter, fine fraction, redox
potential, trace elements (arsenic, cadmium, chromium,
copper, nickel, lead and zinc) and organic contaminants
(polycyclic aromatic hydrocarbons, polychlorinated
biphenyls and a pesticide: dichloro diphenyl trichloroethane).
Organisms were surveyed for contaminant bioaccumulation
and induction of two hepatic biochemical
biomarkers: metallothionein (MT) and cytochrome P450
(CYP1A), as potential indicators of exposure to metallic
and organic contaminants, respectively. Using an integrative
approach it was established that, although bioaccumulation
is in general accordance with sediment
contamination, lethality and biomarker responses are not
linearly dependent of the cumulative concentrations of
sediment contaminants but rather of their bioavailability
and synergistic effects in organisms. It is concluded that
metals and organic contaminants modulate both MT and
CYP1A induction and it is suggested that reactive oxygen
species may be the link between responses and effects of
toxicity.peerreviewe
Genotoxic damage in Solea senegalensis exposed to sediments from the Sado Estuary (Portugal): effects of metallic and organic contaminants
Juvenile Solea senegalensis (Senegalese sole) were exposed to freshly collected sediments from three sites
of the Sado Estuary (West-Portuguese coast) in 28-day laboratory assays in order to assess the ecological
risk from sediment contaminants, by measuring two genotoxicity biomarkers in peripheral blood: the
percentage of Erythrocyte Nuclear Abnormalities (ENA) by use of an adaptation of the micronucleus test,
and the percentage of DNA strand-breakage (DNA-SB) with the Comet assay. Sediments were surveyed for
metallic (Cr, Ni, Cu, Zn, As, Cd and Pb) and organic (PAHs (polycyclic aromatic hydrocarbons), PCBs (polychlorinated biphenyls) and DDTs (dichloro-diphenyl-trichloroethane)) contaminants. Sediments from site
A (farthest from hotspots of contamination) were found to be the least contaminated and weaker inducers
of genotoxic damage, whereas sediments from sites B (urban influence) and C (affected by industrial effluents and agricultural runoffs) were responsible for a very significant increase in both ENA and DNA-SB,
site B being most contaminated with metals and site C mainly with organic pollutants, especially PAHs
and PCBs . Analysis of genotoxic effects showed a strong correlation between the concentrations of PAHs
and PCBs and both biomarkers at sampling times T14 and T28, while the amounts of Cu, As, Cd and Pb
were less strongly correlated, and at T28 only, with ENA and DNA-SB. These results show that organic
contaminants in sediment are stronger and faster acting genotoxic stressors. The results also suggest that
metals may have an inhibitory effect on genotoxicity when interacting with organic contaminants, at least
during early exposure. ENA and DNA-SB do not show a linear relationship, but a strong correlation exists
between the overall increase in genotoxicity caused by exposure to sediment, confirming that they are
different, and possibly non-linked effects that respond similarly to exposure. Although the Comet assay
showed enhanced sensitivity, the two analyses are complementary and suitable for the biomonitoring of
sediment contaminants in a benthic species like S. senegalensis.info:eu-repo/semantics/publishedVersio
Assessment of the genotoxic potential of contaminated estuarine sediments in fish peripheral blood: laboratory versus in situ studies
Juvenile Senegalese soles (Solea senegalensis) were exposed to estuarine sediments through 28-day
laboratory and in situ (field) bioassays. The sediments, collected from three distinct sites (a reference
plus two contaminated) of the Sado Estuary (W Portugal) were characterized for total organic matter,
redox potential, fine fraction and for the levels of metals, polycyclic aromatic hydrocarbons (PAHs) and
organochlorines, namely polychlorinated biphenyls (PCBs) and dichloro diphenyl tricholoethane plus
its main metabolites (DDTs). Genotoxicity was determined in whole peripheral blood by the single-cell
gel electrophoresis (SCGE or ‘‘comet’’) assay and by scoring erythrocytic nuclear abnormalities (ENA).
Analysis was complemented with the determination of lipid peroxidation in blood plasma by the
thiobarbituric acid reactive substances (TBARS) protocol and cell type sorting. The results showed that
exposure to contaminated sediments induced DNA fragmentation and clastogenesis. Still, laboratory
exposure to the most contaminated sediment revealed a possible antagonistic effect between metallic
and organic contaminants that might have been enhanced by increased bioavailability. The laboratory
assay caused a more pronounced increase in ENA whereas a very significant increase in DNA
fragmentation was observed in field-tested fish exposed to the reference sediment, which is likely
linked to increased lipid peroxidation that probably occurred due to impaired access to food. Influence
of natural pathogens was ruled out by unaltered leukocyte counts. The statistical integration of data
correlated lipid peroxidation with biological variables such as fish length and weight, whereas the
genotoxicity biomarkers were more correlated to sediment contamination. It was demonstrated that
laboratory and field bioassays for the risk assessment of sediment contamination may yield different
genotoxicity profiles although both provided results that are in overall accordance with sediment
contamination levels. While field assays may provide more ecologically relevant data, the multiple
environmental variables may produce sufficient background noise to mask the true effects of
contamination.info:eu-repo/semantics/publishedVersio
Histological biomarkers in liver and gills of juvenile Solea senegalensis exposed
Young juvenile Solea senegalensis were exposed to three sediments with distinct contamination profiles
collected from a Portuguese estuary subjected to anthropogenic sources of contamination (the Sado estuary,
western Portugal). Sedimentswere surveyed formetals (cadmium, chromium, copper, nickel, lead and
zinc), ametalloid (arsenic) and organic contaminants (polycyclic aromatic hydrocarbons, polychlorinated
biphenyls and a pesticide, dichloro-diphenyl-trichloroethane plus itsmetabolites), aswell as total organic
matter, redox potential and particle fine fraction. The fish were exposed to freshly collected sediments
in a 28-day laboratorial assay and collected for histological analyses at days 0 (T0), 14 (T14) and 28 (T28).
Individual weighted histopathological indices were obtained, based on presence/absence data of eight
and nine liver and gill pathologies, respectively, and on their biological significance. Although livers sustained
more severe lesions, the sediments essentially contaminated by organic substances caused more
damage to both organs than the sediments contaminated by both metallic and organic contaminants,
suggesting a possible synergistic effect. Correlation analyses showed that some alterations are linked,
forming distinctive histopathological patterns that are in accordance with the severity of lesions and
sediment characteristics. The presence of large eosinophilic bodies in liver and degeneration of mucous
cells in gills (a first-time described alteration)were some of the most noticeable alterations observed and
were related to sediment organic contaminants. Body size has been found to be negatively correlated
with histopathological damage in livers following longer term exposures. It is concluded that histopathological
indices provide reliable and discriminatory data even when biomonitoring as complex media as
natural sediments. It is also concluded that the effects of contamination may result not only from toxicant
concentrations but also from their interactions, relative potency and sediment characteristics that
ultimately determine bioavailability.peerreviewe
A description of chloride cell and kidney tubule alterations in the flatfish Solea senegalensis exposed to moderately contaminated sediments from the Sado estuary (Portugal)
The effects of sediment-bound contaminants on kidney and gill chloride cells were surveyed in juvenile Solea
senegalensis exposed to fresh sediments collected from three distinct sites of the Sado Estuary (Portugal) in a
28-day laboratorial assay. Sediments were analyzed for metallic contaminants, polycyclic aromatic
hydrocarbons and organochlorines as well as for total organic matter, redox potential and fine fraction.
The potential for causing adverse biological effects of each surveyed sediment was assessed by comparison of
contaminant levels to available guidelines for coastal sediments, namely the Threshold Effects Level (TEL)
and the Probable Effects Level (PEL). The Sediment Quality Guideline Quotient indices (SQGQ) were
calculated to compare the overall contamination levels of the three stations. A qualitative approach was
employed to analyze the histo/cytopathological traits in gill chloride cells and body kidney of fish exposed to
each tested sediment for 0, 14 and 28 days. The results showed that sediment contamination can be
considered low to moderate and that the least contaminated sediment (from a reference site, with the lowest
SQGQ) caused lesser changes in the surveyed organs. However, the most contaminated sediment (by both
metallic and organic xenobiotics, with highest SQGQ) was neither responsible for the highest mortality nor
for the most pronounced lesions. Exposure to the sediment presenting an intermediate SQGQ, essentially
contaminated by organic compounds, caused the highest mortality (48%) and the most severe damage to
kidneys, up to full renal necrosis. Chloride cell alterations were similar in fish exposed to the two most
contaminated sediments and consisted of a pronounced cellular hypertrophy, likely involving fluid retention
and loss of mitochondria. It can be concluded that sediment contamination considered to be low or moderate
may be responsible for severe injury to cells and parenchyma involved in the maintenance of osmotic
balance, contributing for the high mortality levels observed. The results suggest that sediment-bound
organic contaminants such as PAHs (polycyclic aromatic hydrocarbons) and PCBs (polychlorinated
biphenyls) may be very toxic to the analyzed organs, especially the kidney, even when present in lowrisk concentrations.info:eu-repo/semantics/publishedVersio
Hepatic proteome changes in solea senegalensis exposed to contaminated estuarine sediments: a laboratory and in situ survey
Assessing toxicity of contaminated estuarine
sediments poses a challenge to ecotoxicologists due to the
complex geochemical nature of sediments and to the
combination of multiple classes of toxicants. Juvenile
Senegalese soles were exposed for 14 days in the laboratory and in situ (field) to sediments from three sites (a
reference plus two contaminated) of a Portuguese estuary.
Sediment characterization confirmed the combination of
metals, polycyclic aromatic hydrocarbons and organochlorines in the two contaminated sediments. Changes in liver
cytosolic protein regulation patterns were determined by a
combination of two-dimensional electrophoresis with de
novo sequencing by tandem mass spectrometry. From the
forty-one cytosolic proteins found to be deregulated, nineteen were able to be identified, taking part in multiple
cellular processes such as anti-oxidative defence, energy
production, proteolysis and contaminant catabolism (especially oxidoreductase enzymes). Besides a clear distinction
between animals exposed to the reference and contaminated sediments, differences were also observed between
laboratory- and in situ-tested fish. Soles exposed in the
laboratory to the contaminated sediments failed to induce,
or even markedly down-regulated, many proteins, with the
exception of a peroxiredoxin (an anti-oxidant enzyme) and
a few others, when compared to reference fish. In situ
exposure to the contaminated sediments revealed significant up-regulation of basal metabolism-related enzymes,
comparatively to the reference condition. Down-regulation
of basal metabolism enzymes, related to energy production
and gene transcription, in fish exposed in the laboratory to
the contaminated sediments, may be linked to sedimentbound contaminants and likely compromised the organisms’ ability to deploy adequate responses against insult.info:eu-repo/semantics/publishedVersio
Metal Pollution and Mining in the Iberian Pyrite Belt: New Remediation Technologies to Improve the Ecosystem Services of the River Basins
The highly metal-contaminated Odiel-Tinto River basin, located in the Iberian Pyrite Belt (IPB), has been the focus of many environmental studies as a natural lab for biodiversity and environmentally catastrophic scenarios and as a reference site for mining places with similar conditions. This study demonstrates the feasibility and effectiveness of two different technologies to recover ecosystems affected by acid mine drainage (AMD) in the area of IPB. The current study compiles results of two newest technologies for AMD remediation: passive remediation (dispersed alkaline substrate—DAS) and a new disruptive technology (Adiabatic Sonic Evaporation and Crystallization—ASE&C) that purifies the contaminated water, obtaining two by-products (high-quality water and metal conglomerates) that improve the general quality of the ecosystem including biodiversity by eliminating more than 90% of the contaminants from AMD and mining waters. The removal of contaminants, enhancement of AMD treatment efficiency, and offset operating costs were compared and analyzed for the different uses of the decontaminated effluents, including an old tailing pond failure, the Aznalcóllar mining spill. The efficiency of the removal of elements from the contaminated water is significant using both technologies, although the passive DAS does not still reach the international benchmark for some compounds (such as Fe, sulfates, and Mn); whereas ASE&C obtains distilled water fulfilling all the international benchmarks with conductivity values lower than 120 µS cm−1 or metal concentrations lower than µg/L. Both technologies are eco-friendly and cost-effective as a result of the generation of valuable by-products such as fresh water and metal conglomerates as potentially commercial products while remediating aquatic ecosystems impacted by mining activities