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Identification of ABC Transporter Genes in Gonad Tissue of Two Mediterranean Sea Urchin Species: Black, Arbacia lixula L., and Rocky, Paracentrotus lividus L.

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Multixenobiotic resistance (MXR) represents an important cellular detoxification mechanism in aquatic organisms as it provides them robustness toward natural and man-made contaminants. Several ABC transporters have major roles in the MXR phenotype - P-gp/ABCB1, MRP1-3/ABCC1-3 and BCRP/ABCG2. In this study, we identified the presence of ABC transporters involved in the MXR mechanism of Arbacia lixula and Paracentrotus lividus. AlABCB1/P-gp, AlABCC3/MRP3, AlABCC9/SUR-like and AlABCG-like transcripts were identified in A. lixula; and PlABCC1/P-gp, PlABCC3/MRP3, PlABCC5/MRP5, and PlABCC9/SUR-like transcripts in P. lividus. For each of the new partial sequences, we performed detailed phylogenetic and identity analysis as a first step toward full characterization and understanding of the ecotoxicological role of these ABC transporters.
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1 23
Bulletin of Environmental
Contamination and Toxicology
ISSN 0007-4861
Volume 91
Number 4
Bull Environ Contam Toxicol (2013)
91:415-419
DOI 10.1007/s00128-013-1021-8
Identification of ABC Transporter Genes in
Gonad Tissue of Two Mediterranean Sea
Urchin Species: Black, Arbacia lixula L.,
and Rocky, Paracentrotus lividus L.
Ivana Bošnjak, Roko Zaja, Roberta
Sauerborn Klobučar, Lidija Šver, Jasna
Franekić & Tvrtko Smital
1 23
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Identification of ABC Transporter Genes in Gonad Tissue of Two
Mediterranean Sea Urchin Species: Black, Arbacia lixula L.,
and Rocky, Paracentrotus lividus L.
Ivana Bos
ˇnjak Roko Zaja Roberta Sauerborn Klob-
uc
ˇar Lidija S
ˇver Jasna Franekic
´
Tvrtko Smital
Received: 6 March 2013 / Accepted: 24 May 2013 / Published online: 7 June 2013
ÓSpringer Science+Business Media New York 2013
Abstract Multixenobiotic resistance (MXR) represents an
important cellular detoxification mechanism in aquatic
organisms as it provides them robustness toward natural
and man-made contaminants. Several ABC transporters
have major roles in the MXR phenotype P-gp/ABCB1,
MRP1–3/ABCC1–3 and BCRP/ABCG2. In this study, we
identified the presence of ABC transporters involved in
the MXR mechanism of Arbacia lixula and Paracentrotus
lividus.AlABCB1/P-gp, AlABCC3/MRP3, AlABCC9/
SUR-like and AlABCG-like transcripts were identified in
A. lixula; and PlABCC1/P-gp, PlABCC3/MRP3, PlABCC5/
MRP5, and PlABCC9/SUR-like transcripts in P. lividus. For
each of the new partial sequences, we performed detailed
phylogenetic and identity analysis as a first step toward full
characterization and understanding of the ecotoxicological
role of these ABC transporters.
Keywords ABC transporters MXR mechanism
Arbacia lixula Paracentrotus lividus
Organisms are constantly exposed to a vast variety of sub-
stances present in their surrounding aquatic environment,
including natural and anthropogenic contaminants. In order
to survive, aquatic organisms use a highly efficient cellular
protection system mediated by complementary activity of
the efflux transport proteins and detoxification enzymes
(Goldstone et al. 2006; Epel et al. 2008). Efflux transporters
are members of the large ATP binding cassette (ABC)
transporter superfamily and have the ability to actively efflux
various endogenous and exogenous substrates, including
xenobiotics, across cell membranes against their concen-
tration gradients (Szaka
´cs et al. 2008). Numerous studies
indicated that similar ABC transporters represent integral
parts of the cellular detoxification machinery for aquatic
organisms living in contaminated environments, mediating
the so-called multixenobiotic resistance (MXR) mechanism
(Kurelec 1992; Bard 2000). Key ABC efflux transport-
ers involved in the MXR mechanism are: P-glycoprotein
(MDR1/ABCB1/P-gp); multidrug resistance-associated pro-
teins 1–3 (MRP1–3/ABCC1–3); and the breast cancer resis-
tance protein (BCRP/ABCG2) (Szaka
´cs et al. 2008). The
MXR mechanism has also an important role in resistance
of very sensitive early stage embryos (Hamdoun and Epel
2007).
Sea urchins represent an ecologically relevant animal
group and a valuable model frequently used for assessing
toxicity of contaminants (Cesar et al. 2004; Bos
ˇnjak et al.
2009). A fully sequenced genome of Strongylocentrotus
purpuratus is available, and characterization of chemical
defense genes and related activities were reported for this
species (Goldstone et al. 2006; Sea Urchin Genome
Electronic supplementary material The online version of this
article (doi:10.1007/s00128-013-1021-8) contains supplementary
material, which is available to authorized users.
I. Bos
ˇnjak (&)L. S
ˇver J. Franekic
´
Laboratory for Biology and Microbial Genetics, Department of
Biochemical Engineering, Faculty of Food Technology and
Biotechnology, University of Zagreb, Pierottijeva 6,
10000 Zagreb, Croatia
e-mail: ibosnjak@pbf.hr
R. Zaja T. Smital
Laboratory for Molecular Ecotoxicology, Division for Marine
and Environmental Research, Rud
¯er Bos
ˇkovic
´Institute,
Bijenic
ˇka cesta 54, 10000 Zagreb, Croatia
R. S. Klobuc
ˇar
Laboratory for Ichtyopathology - biological materials,
Division of Materials Chemistry, Rud
¯er Bos
ˇkovic
´Institute,
Bijenic
ˇka cesta 54, 10000 Zagreb, Croatia
123
Bull Environ Contam Toxicol (2013) 91:415–419
DOI 10.1007/s00128-013-1021-8
Author's personal copy
Sequencing Consortium 2006). Among defense genes, there
are 48 annotated ABC transporter, including orthologues,
involved in the MXR mechanism P-gp (ABCB1), MRP
(ABCC), BCRP-like (ABCG) efflux transporters, and also
the sulfonylurea receptor (ABCC9/SUR) from the ABCC
subfamily (Goldstone et al. 2006). In humans, SUR receptor
is responsible for mediating closure of the ATP-sensitive
potassium channel, and thereby stimulates insulin release in
the b-cell plasma membrane (Panten et al. 1996). But in S.
purpuratus genome, the SUR receptor is reported to be also
involved in the MXR mechanism (Goldstone et al. 2006).
The main goal of this study was the identification of various
ABC transporters in two Mediterranean sea urchin species:
black, Arbacia lixula and rocky, Paracentrotus lividus.
Targeted tissue for detection of ABC transporter mRNA
transcripts was gonad tissue for locating ABC transporter
proteins that are present in egg cells, which would contribute
to the MXR mechanism mediated protection of future
embryos. The main aim of the study was identification of all
possible ABC transporters involved in MXR activity.
Materials and Methods
Adult sea urchins A. lixula and P. lividus, were collected in
a coastal region (1–5 m depth) at two locations: Crikvenica
harbor (Crikvenica, Croatia, 45°1001100N14°4104400E)
located at the northern part and Marijan Peninsula (Split,
Croatia, 43°3001300N16°2403000E) located at the southern
part of the Adriatic coast. Both chosen sampling locations are
in areas of excellent sea water quality. Adult animals were
transported in tanks to laboratory where they were either
dissected immediately for collection of gonad tissue sam-
ples, or kept for 1–3 days in flow-through thanks (18 ±2°C)
until dissection. Only mature female gonad tissue samples
were collected. Samples were obtained in the spring (April)
when both species are at the peak of the reproduction cycle.
Primer pairs (Table 1) were designed based on the
highly conserved regions of Homo sapiens and S. purpu-
ratus Abcb1,Abcc1,Abcc3,Abcc5,Abcc9 and Abcg2 gene
sequences. All primers were obtained from Sigma to
Aldrich (St. Louis, MO, USA).
Total RNA was isolated from *30 mg of gonad tissue
pooled from 5 to 8 A. lixula and P. lividus females, respec-
tively. RNA was immediately placed into RNA later Sta-
bilization Reagent (Applied Biosystems, Foster City, CA,
USA) and kept at 4°C until RNA extraction was performed
with the RNeasy mini kit (Qiagen, Hilden, Germany)
according to the manufacturer’s instructions. cDNA was
synthesized from 4 lg of RNA using H Minus M-MulV
reverse transcriptase (Fermentas, Burlington, Canada).
ABC transporter orthologs were amplified in the PCR
reactions using either a Biometra thermal personal cycler
(Go
¨ttingen, Germany) or Mastercycler Personal (Hamburg,
Germany). PCR was performed for 35 cycles at 94°C (30 s),
55°C (30 s) and 72°C (2 min) or in a touchdown mode (from
60 to 45°C). Aliquots of each reaction were resolved by
electrophoresis on 1.2 % agarose gel in tris–acetate-EDTA
(TAE) buffer. The gels were stained with ethidium bromide,
and PCR products visualized under UV light. The expected
products were gel purified (MiniElute PCR Purification Kit
(Qiagen, Germany), cloned into the pGEM-T vector (Pro-
mega, Madison, WI, USA) and sequenced using an ABI
PRISM
Ò
3100-Avant Genetic Analyzer (Rud
¯er Bos
ˇkovic
´
Institute DNA Service, Zagreb, Croatia) using standard cycle
sequencing protocols.
Obtained partial cDNA sequences were analyzed using
the National Center for Biotechnology Information (NCBI,
Bethesda, MD, USA) basic alignment search tool (tblastx
and protein blast). Multiple sequence alignments and
determinations of identity rates between amino acid
sequences of ABC transporters from different species were
performed using BioEdit software and Clustal X version
2.0 implemented in the MEGA 5 software, with default
parameters. MEGA 5 software was also used to perform
phylogenetic analysis (Neighbor-Joining (NJ) analysis).
Reliabilities of phylogenetic relationships were evaluated
using a non-parametric bootstrap analysis with 1,000 rep-
licates for NJ analysis. Bootstrap values exceeding 70 were
considered well supported.
Results and Discussion
Both A. lixula and P. lividus are frequently used as model
organisms in ecotoxicological studies (Cesar et al. 2004;
Table 1 Primer sequences used in PCR to detect the primary
ABCB1, ABCC1, ABCC3, ABCC5, ABCC9 and ABCG gene
sequences in the gonad tissue of A. lixula and P. lividus
ABC
subfamily
Primer
name (ID)
Primer sequence (50–30)
ABCB1 259 F: ATGCCATTGCCTTCTGGTATGG
260 R: CTGCTGCCGACCAGAGCCAG
ABCC1 263 F: CTCCGTTTCTGAGATCGGCT
264 R: AAGTCTCTTCAGCTGACGGGA
ABCC3 017-C3 F: GCACCATCAGAGCATATCAAT
018-C3 R: CGCTGACCAACACTGAGGTT
ABCC5 275 F: TTCTCWMRWGAYATKGATGAA
276 R: CCHACRATBCCDAYYTTCT
ABCC9 019-C9 F: ATGAGATTCTTTGACACCAC
020-C9 R: GAAGAGAGAAAGTGTAAGCGA
ABCG2 266 F: TTGAGTCCAGGCTCAGACCA
267 R: GTGCTATGATGGGCGAGATG
Fforward primer sequence, Rreverse primer sequence
416 Bull Environ Contam Toxicol (2013) 91:415–419
123
Author's personal copy
Arslan and Parlak 2007). Their rapid development and
transparent embryo and larval stages enable monitoring of
any morphological abnormalities and/or the developmental
arrest caused by exposure to toxic compounds. A low spec-
ificity for substrates, a typical feature of ABC efflux trans-
porters as key components of the MXR mechanism, certainly
represents an enormous advantage for aquatic organisms
(Epel et al. 2008). However, in highly complex mixtures of
pollutants, certain compounds may act as inhibitors of ABC
transporters and cause the chemosensitization and/or over-
saturation of ABC transporter efflux (Smital et al. 2004;Epel
et al. 2008). In an attempt to develop ecologically relevant
and technically feasible high throughput screening methods
for identification of potential environmental MXR inhibitors
(chemosensitizers), sea urchin embryos represent a promis-
ing model system. An embryotoxicity test utilizing the cell
cycle arrest as an end-point caused by the enhanced accu-
mulation of inorganic compounds (e.g. mercuric chloride,
tributyl tin) due to the inhibition of the ABCC/MRP-like
transport has already been established for both A. lixula and
P. lividus embryos (Bos
ˇnjak et al. 2011).
ABC transporters are present but not active in sea urchin
eggs, and their activation during fertilization is needed for
protection during embryonic development (Hamdoun et al.
2004; Shipp and Hamdoun 2012). Therefore, by sampling
only mature female gonad tissue, we focused on identifi-
cation of ABC transporters present in egg cells. Specific
pairs of primers (Table 1) generated fragments of desired
ABC transporter amplicons. Cloning, sequencing and
finally identification resulted with 8 partial ABC trans-
porter sequences. Respective translated amino acid
sequences of these partial PCR products showed a high
degree of identity with P-gp, MRP3, MRP5, SUR-like and
ABCG2/BCRP-like proteins, respectively, from various
other organisms, and this homology was confirmed with
NCBI Blast2 protein database query (data not shown). All
of the obtained sequence data were registered at the Gen-
Bank (Table 2).
Relationships of eight identified A. lixula and P. lividus
partial ABC transporter sequences with ABC transporter
orthologs from human, mouse, chicken, fish, frog, fruit fly,
mussel and purple sea urchin species are shown in the
presented phylogenetic trees (Fig. 1a–c). GenBank acces-
sion numbers of sequences of all compared orthologs are
shown in Table S1 I–III and all of the obtained identities
are shown in Fig. S1a–c. Identity of the PlABCB1
sequence is 77 % congruent with the egg permeability
glycoprotein from S. purpuratus (Fig. S1a) the main
protein from the ABCB subfamily involved in efflux of a
broad range of hydrophobic xenobiotics (Hamdoun et al.
2004). Identity of the AlABCB1 sequence is 41 % con-
gruent with the ABCB4 from S. purpuratus and 21 %–
27 % with ABCB1, ABCB4 and ABCB11 proteins from
various orthologs, respectively (Fig. S1a). The ABCB4
member is also similar to mammalian P-gp/ABCB1
member (Szaka
´cs et al. 2008). The phylogenetic tree shows
clustering of partial AlABCB-like and PlABCB1 with
respective ABCB1 and ABCB4 orthologs from S. purpu-
ratus and with ABCB1 orthologs from mussels (Fig. 1a).
The identified AlABCC3 sequence is 85 % identical with
partial PlABCC3 sequence, and 54 % congruent with the
ABCC3A protein from S. purpuratus (Fig. S1b). Identities
of PlABCC3 sequence are 57 % congruent with ABCC3A
protein from S. purpuratus. Overall, both of these
sequences were more identical with MRP proteins than
with SUR proteins from various orthologs (Fig. S1b). In
mammalian species, MRP3 is involved in the efflux of
organic and inorganic anions that are direct products of
phase I and II metabolism and present in the form of glu-
tathione, glucuronic or sulphate water soluble conjugates
(Cole and Deeley 2006). Therefore, this transporter most
likely has an important role in the MXR mechanism in sea
urchins.
Identities of the AlABCC9 sequence are 60 % congruent
with the partial PlABCC9 sequence and 32 % with the
ABCC9 protein from S. purpuratus. Identities of the
PlABCC9 sequence are 47 % congruent with the ABCC9
protein from S. purpuratus. Overall, both of these
sequences showed more identity with SUR proteins than
with MRP proteins from various orthologs (Fig. S1b). In S.
purpuratus, a high expression of ABCC9 mRNA was
determined during the first 58 h of development (Shipp and
Hamdoun 2012). It is more likely that this transporter acts
as a part of the MRP-like rather than SUR-like efflux
activity in sea urchins (Goldstone et al. 2006). The partial
PlABCC5 sequence was the shortest of all, and was 16 %
congruent with the ABCC5 protein from H. sapiens and
9 %–17 % with SUR and MRP proteins from various
orthologs (Fig. S1b). The phylogenetic tree shows clus-
tering of partial AlABCC3, PlABCC3 and PlABCC5
sequences within the MRP protein group, and partial
AlABCC9 and PlABCC9 sequences with the SUR protein
group (Fig. 1b). The last identified ABC transporter was an
ABCG/BCRP-like ortholog obtained from A. lixula gonad
tissue. Identities of the AlABCG-like sequence are 56 %
congruent with ABCG11 from S. purpuratus and 28 %–
34 % with other protein members of the ABCG subfamily
(Fig. S1c). The phylogenetic tree shows clustering of the
partial AlABCG-like protein with ABCG11 ortholog from
S. purpuratus (Fig. 1c). The identified ortholog has higher
similarity (56 %) with the ABCG11 from S. purpuratus
than with the ABCG2 (29 %) member.
Although the same primer pairs were used in PCR
reactions for detection of ABC transporters in both sea
urchin species, the ABCG-like partial sequence was
detected only in A. lixula, and the ABCC5-like partial
Bull Environ Contam Toxicol (2013) 91:415–419 417
123
Author's personal copy
Table 2 Summary of the obtained ABC transporter gene sequences from A. lixula and P. lividus
ABC
subfamily
Sea urchin
species
Gene Text abbreviation
code
Length of cloned fragment GenBank
accession no.
Nucleotide
(bp)
Amino acid
(a.a.)
ABCB A. lixula ABCB1/P-gp AlABCB1 528 176 HM134891
P. lividus ABCB1/P-gp PlABCB1 449 149 HM134889
ABCC A. lixula ABCC3/MRP3 AlABCC3 689 229 HM439620
A. lixula ABCC9/SUR-like AlABCC9 620 206 HM439621
P. lividus ABCC3/MRP3 PlABCC3 666 222 HM439622
P. lividus ABCC5/MRP5-like PlABCC5 508 169 HM134890
P. lividus ABCC9/SUR-like PlABCC9 703 234 HM439623
ABCG A. lixula ABCG-like AlABCG 749 249 HM134892
Fig. 1 Phylogenetic tree based on multiple alignments (Clustal X) of
different ABC transporter subtype sequences from various vertebrates
and invertebrates. aABCB, bABCC, cABCG. Tree was inferred by
the NJ method implemented in MEGA software. Bootstrap support
values for the NJ tree are shown at the nodes (out of 1,000 replicates).
The accession numbers retrieved in this study for ABCB and ABCC
transporters are listed in Table S1 I–III
418 Bull Environ Contam Toxicol (2013) 91:415–419
123
Author's personal copy
sequence was detected only in P. lividus. Some ABC efflux
transporters could be identified only in one species, pos-
sibly because of some differences in expression of ABC
transporters in otherwise closely related sea urchin species.
The ABCC1 sequence was not detected in gonad tissue of
either sea urchin species which could also indicate that this
transporter is not expressed. Further research is needed in
order to clarify these results.
The presented identification of ABCB1, ABCC3, ABCC9
and ABCG-like partial sequences in A. lixula and ABCB1,
ABCC3, ABCC5 and ABCC9 partial sequences in P. lividus
represents the first and necessary step in characterization of
ABC transporters in these two urchin species. There is no
doubt, however, that a full understanding of the role and
ecological relevance of ABC efflux transporters in these
species can be obtained only by identification and sub-
sequent in-depth molecular characterization of individual
proteins. Therefore, we are directing our research efforts
toward completion of the characterization of all proteins
potentially involved in the MXR defense in Mediterranean
sea urchins.
Acknowledgments This work has been supported by the Ministry
of Science, Education and Sports of the Republic of Croatia, Project
Nos. 058-0582261-2246 and 098-0982934-2745.
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... Among mechanisms involved in cellular uptake and disposition of exogenous compounds, including environmental pollutants, the MXR phenotype has been well documented in marine species (Kurelec 1992) and therefore considered as the first line of cell defense against natural and anthropogenic stressors (Hamdoun, Griffin, and Cherr 2002;Smital et al. 2004;Goldstone et al. 2006;Epel et al. 2008;Anselmo et al. 2012;Bo snjak et al. 2013;Huang et al. 2015;Wu et al. 2015). The activity of ATP-binding cassette (ABC) transporters has been described in sea urchins' gametes, embryos, larvae, and immune system cells Silva-Neta et al. 2012;Torrezan, Figueiredo, and Marques-Santos 2012;Marques-Santos et al. 2017) and several works have reported the effect of marine contaminants on their expression and activity (Luckenbach, Corsi, and Epel 2004;Smital et al. 2004;Della Torre et al. 2012). ...
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... Five genes involved in detoxification processes were targeted by both HEPEs. The gene MDR1 belongs to ATP-binding cassette transporters, which are activated by sub-lethal doses of specific contaminants (such as oxybenzone, mercuric chloride and tributyltin) during embryonic development (from the zygote to the blastula stage) of sea urchins (Bošnjak et al., 2013). Moreover, sea urchin embryos utilize this gene in cell signaling and lysosomal and mainly mitochondrial homeostasis (Shipp and Hamdoun, 2012). ...
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Oxylipins (including polyunsaturated aldehydes PUAs, hydoxyacids and epoxyalcohols) are the end-products of a lipoxygenase/hydroperoxide lyase metabolic pathway in diatoms. To date very little information is available on oxylipins other than PUAs, even though they represent the most common oxylipins produced by diatoms. Here, we report, for the first time, on the effects of two hydroxyacids, 5-and 15-HEPE, which have never been tested before, using the sea urchin Paracentrotus lividus as a model organism. We show that HEPEs do induce developmental malformations but at concentrations higher when compared to PUAs. Interestingly, HEPEs also induced a marked developmental delay in sea urchin embryos, which has not hitherto been reported for PUAs. Recovery experiments revealed that embryos do not recover following treatment with HEPEs. Finally, we report the expression levels of 35 genes (involved in stress, development, differentiation, skeletogenesis and detoxification processes) to identify the molecular targets affected by HEPEs. We show that the two HEPEs have very few common molecular targets, specifically affecting different classes of genes and at different times of development. In particular, 15-HEPE switched on fewer genes than 5-HEPE, up-regulating mainly stress-related genes at a later pluteus stage of development. 5-HEPE was stronger than 15-HEPE, targeting twenty-four genes, mainly at the earliest stages of embryo development (at the blastula and swimming blastula stages). These findings highlight the differences between HEPEs and PUAs and also have important ecological implications because many diatom species do not produce PUAs but rather these other chemicals derived from the oxidation of fatty acids.
... The transporters involved in biological defense mechanism include P-glycoprotein (Pgp, multidrug resistance protein) belonging to the ABCB subfamily, multidrug resistance associated proteins 1-5 (Mrp1-5) from the ABCC subfamily and breast cancer resistance protein (Bcrp) from the ABCG family. High expressions and activities of these transporters have been reported in the larval and adult stages of many aquatic organisms, such as rainbow trout (Kennedy et al., 2014), blue mussels (Rioult et al., 2014) and Mediterranean sea urchin (Bosnjak et al., 2013). ABC transporters could be induced by a wide variety of exogenous agents such as heavy metals and polycyclic aromatic hydrocarbons (PAHs), pumping them out of the cell in an energydependent process (Costa et al., 2013;Navarro et al., 2012). ...
Article
Adenosine triphosphate-binding cassette (ABC) transporters, including ABCB, ABCC and ABCG families represent general biological defenses against environmental toxicants in varieties of marine and freshwater organisms, but their physiological functions at differential developmental stages of zebrafish embryos remain undefined. In this work, functional expressions of typical ABC transporters including P-glycoprotein (Pgp), multiresistance associated protein 1 (Mrp1) and Mrp2 were studied in zebrafish embryos at 4, 24, 48 and 72 h post-fertilization (hpf). As a result, both the gene expressions and activities of Pgp and Mrps increased with the development of embryos. Correspondingly, 4-72 hpf embryos exhibited an increased tolerance to the toxicity caused by cadmium chloride (CdCl2 ) and β-naphthoflavone (BNF) with time. Such a correlation was assumed caused by the involvement of ABC transporters in the detoxification of chemicals. In addition, the assumption was supported by the fact that model efflux inhibitors of Pgp and Mrps such as reversine 205 and MK571 significantly inhibited the efflux of toxicants and increased the toxicity of Cd and BNF in zebrafish embryos. Moreover, exposure to CdCl2 and BNF induced the gene expressions of Pgp and Mrp1 in 72 hpf embryos. Thus, functional expressions of Pgp and Mrps increased with the development of zebrafish embryos, which could cause an increasing tolerance of zebrafish embryos to CdCl2 and BNF. Copyright © 2015 John Wiley & Sons, Ltd.
... Alongside P-gp, multidrug resistance-associated proteins (MRP/ABCC; members of ABCC subfamily) and the breast cancer resistance protein (BCRP, ABCG2) are toxicologically important MXR transporters involved in efflux of metabolites in the form of glutathione, glucuronic, or sulfate conjugates (Haimeur et al. 2004;Leslie et al. 2005). The presence of P-gp, MRPs, and BCRP proteins or their high efflux activity have been reported in tissues of many aquatic species including sponges, sea urchins, mussels, and fish (Bošnjak et al. 2013;Della Torre et al. 2014;Hamdoun et al. 2004;Mueller et al. 1996;Stevenson et al. 2006;Žaja et al. 2007, 2008. ...
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Abstract Mussel (Mytilus galloprovincialis (Lamarck, 1819)) is directly exposed to sea water contamination that elicits significant physiological and cellular response, although its extent mounted in aquaculturereared in comparison to wild bivalve populations is scarcely known. Therefore, we have compared contamination biomarkers in mussels from reared (Marina farm) and wild, anthropogenically affected site (Vranjic Bay). While predictably, the levels of metals (Cu, Cd, Pb, Zn, Fe, and Hg) in whole bivalve tissues determined by atomic absorption spectrophotometry resulted in significantly higher concentrations in wild mussels, accompanied by elevated number of apoptotic cells in gills, the activity of multixenobiotic resistance defense mechanism (MXR), measured as the accumulation rate of model substrate rhodamine B (RB) gave contrasting results. The functional RB assay evidenced a lower MXR efflux activity in the gill tissue of wild mussels, indicating two possible scenarios that will need further focus: (1) persisting sea water pollution increased cell damage of bivalve gill cells and consequently led to leakage of the RB into cytoplasm and dysfunctional MXR efflux in wild mussels; or/and (2) a mixture of different toxic compounds present in Vranjic Bay sea water induced oversaturation of MXR efflux, inducing elevated accumulation of the dye. Consequently, it seems that an efficient physiological functioning of MXR in wild mussels is strongly hampered by existence of an unknown quantity of sea water pollutants that may endanger intrinsic organismal defense system and lead toward the enhancement of toxicity.
... Abcb1, belonging to ABC transport proteins and encoding for P-glycoprotein (P-gp) efflux pump, is highly expressed throughout sea urchin embryo development 65 and recognized as one of the most toxicologically relevant efflux pumps in sea urchin species, including P. lividus. 78,79 As a first line of defense toward toxins and environmental pollutants, P-gp has been demonstrated to have a protective role during sea urchin embryo development. 80,81 Several NPs-based approaches have been recently proposed to reverse/overcome efflux-mediated resistance played by P-gp in human cell lines to increase cytotoxic drugs accumulation in tumor cells. ...
Article
Nanoplastic debris, resulted from run-off and weathering breakdown of macro and microplastics, represent an emerging concern for marine ecosystems. The aim of the present study was to investigate disposition and toxicity of polystyrene nanoparticles (PS NPs) in early development of sea urchin embryos Paracentrotus lividus. NPs with two different surface charges where chosen, carboxylated (PS-COOH) and amine (PS-NH2) polystyrene, the latter being a less common variant, known to induce cell death in several in vitro cell systems. NPs stability in natural seawater (NSW) was measured while disposition and embryotoxicity were monitored within 48 h post-fertilization (hpf). Modulation of genes involved in cellular stress response (cas8, 14-3-3ε, p-38 MAPK, Abcb1, Abcc5) was investigated. PS-COOH form micro-aggregates (PDI > 0.4) in NSW, while PS-NH2 result better dispersed (89 nm ± 2 nm) initially, though they also aggregated partially with time. Their respectively anionic and cationic nature was confirmed by zeta potential measurements. No embryotoxicity was observed for PS-COOH up to 50 µg mL-1 while PS-NH2 caused severe developmental defects (EC50 3.85 µg mL-1 -24 hpf and EC50 2.61 µg mL-1 -48 hpf). PS-COOH accumulated inside embryo's digestive trait while PS-NH2 were more dispersed. Abcb1 gene resulted up-regulated at 48 hpf by PS-COOH while PS-NH2 induced cas8 gene at 24 hpf, suggesting an apoptotic pathway. In line with the results obtained with the same PS NPs in several human cell lines, also in sea urchin embryos, differences in surface charges and aggregation in sea water strongly affect their embryotoxicity.
... The induction of other metallothioneins may require exposure to higher concentrations of PUAs or may depend on the nature of the stress agent, considering that metallothioneins seem to respond very specifically to heavy metal exposure. The gene, MDR1, belongs to ATP-binding cassette transporters, which are activated by sub-lethal doses of specific contaminants (such as oxybenzone, mercuric chloride and tributyltin) during embryonic development (from the zygote to the blastula stage) of sea urchins [20]. Moreover, sea urchin embryos utilize it in cell signalling and lysosomal and mainly mitochondrial homeostasis [48]. ...
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Diatoms are dominant photosynthetic organisms in the world's oceans and represent a major food source for zooplankton and benthic filter-feeders. However, their beneficial role in sustaining marine food webs has been challenged after the discovery that they produce secondary metabolites, such as polyunsaturated aldehydes (PUAs), which negatively affect the reproductive success of many invertebrates. Here, we report the effects of two common diatom PUAs, heptadienal and octadienal, which have never been tested before at the molecular level, using the sea urchin, Paracentrotus lividus, as a model organism. We show that both PUAs are able to induce teratogenesis (i.e., malformations), as already reported for decadienal, the better-studied PUA of this group. Moreover, post-recovery experiments show that embryos can recover after treatment with all three PUAs, indicating that negative effects depend both on PUA concentrations and the exposure time of the embryos to these metabolites. We also identify the time range during which PUAs exert the greatest effect on sea urchin embryogenesis. Finally, we report the expression levels of thirty one genes (having a key role in a broad range of functional responses, such as stress, development, differentiation, skeletogenesis and detoxification processes) in order to identify the common targets affected by PUAs and their correlation with morphological abnormalities. This study opens new perspectives for understanding how marine organisms afford protection from environmental toxicants through an integrated network of genes.
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The detoxification of toxic substances is of general relevance in all biological systems. The plethora of exogenous xenobiotic compounds and endogenous toxic metabolic products explains the evolutionary pressure of all organisms to develop molecular mechanisms to detoxify and excrete harmful substances from the body. P-glycoprotein and other members of the ATP-binding cassette (ABC) transporter family extrude innumerous chemical compounds out of cells. Their specific expression in diverse biological contexts cause different phenotypes: (1) multidrug resistance (MDR) and thus failure of cancer chemotherapy, (2) avoidance of accumulation of carcinogens and prevention of carcinogenesis in healthy tissues, (3) absorption, distribution, metabolization and excretion (ADME) of pharmacological drugs in human patients, (4) protection from environmental toxins in aquatic organisms (multi-xenobiotic resistance, MXR). Hence ABC-transporters may have opposing effects for organismic health reaching from harmful in MDR of tumors to beneficial for maintenance of health in MXR. While their inhibition by specific inhibitors may improve treatment success in oncology and avoid carcinogenesis, blocking of ABC-transporter-driven efflux by environmental pollutants leads to ecotoxicological consequences in marine biotopes. Poisoned seafood may enter the food-chain and cause intoxications in human beings. As exemplified with ABC-transporters, joining forces in interdisciplinary research may, therefore, be a wise strategy to fight problems in human medicine and environmental sciences.
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The sediment formed by the tailings of an abandoned mine, which discharged into Portmán Bay, Murcia, SE-Spain, was tested to establish a possible gradient of heavy metals. The results were compared with tolerance limits of what was calculated from control sites. Whole sediment toxicity tests were performed on two amphipod species, Gammarus aequicauda and Microdeutopus gryllotalpa, while sediment-water interface and porewater toxicity tests were performed on three sea urchins species, Arbacia lixula, Paracentrotus lividus and Sphaerechinus granularis. The sensitivity of these marine organisms was evaluated by exposure tests using the reference substances: ammonium chloride (NH4Cl), cadmium chloride (CdCl2), potassium dichromate (K2Cr2O7), sodium dodecyl sulfate (C12H25NaO4S) and zinc sulfate (ZnSO4). The concentration of heavy metals decreased along the pollution gradient. Amphipod 10 day acute toxicity tests clearly demonstrated the gradient of toxicity. The sediment-water interface tests conducted with sea urchins also pointed to a pollution gradient and were more sensitive than the tests involving amphipods.
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The sediment formed by the tailings of an abandoned mine, which discharged into Portman Bay, Murcia, SE-Spain, was tested to establish a possible gradient of heavy metals. The results were compared with tolerance limits of what was calculated from control sites. Whole sediment toxicity tests were performed on two amphipod species, Gammarus aequicauda and Microdeutopus gryllotalpa , while sediment-water interface and porewater toxicity tests were performed on three sea urchins species, Arbacia lixula, Paracentrotus lividus and Sphaerechinus granularis . The sensitivity of these marine organisms was evaluated by exposure tests using the reference substances: ammonium chloride (NH 4 Cl), cadmium chloride (CdCl 2 ), potassium dichromate (K 2 Cr 2 O 7 ), sodium dodecyl sulfate (C1 2 H 25 NaO 4 S) and zinc sulfate (ZnSO 4 ). The concentration of heavy metals decreased along the pollution gradient. Amphipod 10 day acute toxicity tests clearly demonstrated the gradient of toxicity. The sediment-water interface tests conducted with sea urchins also pointed to a pollution gradient and were more sensitive than the tests involving amphipods.
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The main goals of this study were (1) to standardize a simple and reliable embryotoxicity test for environmental contaminants and (2) to evaluate the presence and possible protective role of the multidrug resistance-associated (MRP) protein-mediated multixenobiotic defense in two Mediterranean sea urchin species, Paracentrotus lividus and Arbacia lixula. Toxic end-point used was the success of the first cell division in sea urchin embryos. Embryotoxicities of three environmentally relevant contaminants: mercuric chloride (HgCl2, 0.05–6μM), trybutiltin (TBT, 2.5–500nM), and oxybenzone (OXI, 0.1–100μM); as well as seawater samples collected from the polluted and unpolluted locations, were determined and compared. A. lixula embryos were more sensitive to all three toxic compounds, and both P. lividus and A. lixula embryos were highly sensitive to TBT at nanomolar concentrations (EC50 49 ± 5 and 36.8 ± 3nM, respectively). Inhibition of MRP protein by specific inhibitor MK571 caused significant increase in embryotoxic potency of HgCl2 (EC50 0.697 ± 0.03 and 0.245 ± 0.04μM, respectively), TBT (EC50 24 ± 3 and 7.4 ± 1nM, respectively) and polluted seawater sample, but not of OXI or unpolluted, natural seawater. Therefore, our results demonstrated for the first time the protective relevance of MRP proteins in early development of these two Mediterranean sea urchin species. Finally, the embryotoxicity protocol described in this study represents a simple and rapid bioassay for determination of environmentally relevant seawater contamination. KeywordsSea urchin embryotoxicity test–MRP activity inhibition
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The environmental presence of chemosensitizers or inhibitors of the multixenobiotic resistance (MXR) defense system in aquatic organisms could cause increase in intracellular accumulation and toxic effects of other xenobiotics normally effluxed by MXR transport proteins (P-glycoprotein (P-gps), MRPs). MXR inhibition with concomitant detrimental effects has been shown in several studies with aquatic organisms exposed to both model MXR inhibitors and environmental pollutants. The presence of MXR inhibitors has been demonstrated in environmental samples from polluted locations at concentrations that could abolish P-gp transport activity. However, it is not clear whether the inhibition observed after exposure to environmental samples is a result of saturation of MXR transport proteins by numerous substrates present in polluted waters or results from the presence of powerful MXR inhibitors. And are potent environmental MXR inhibitors natural or man-made chemicals? As a consequence of these uncertainties, no official action has been taken to monitor and control the release and presence of MXR inhibitors into aquatic environments. In this paper we present our new results addressing these critical questions. Ecotoxicological significance of MXR inhibition was supported in in vivo studies that demonstrated an increase in the production of mutagenic metabolites by mussels and an increase in the number of sea urchin embryos with apoptotic cells after exposure to model MXR inhibitors. We also demonstrated that MXR inhibitors are present among both conventional and emerging man-made pollutants: some pesticides and synthetic musk fragrances show extremely high MXR inhibitory potential at environmentally relevant concentrations. In addition, we emphasized the biological transformation of crude oil hydrocarbons into MXR inhibitors by oil-degrading bacteria, and the risk potentially caused by powerful natural MXR inhibitors produced by invasive species.