Hormetic versus toxic effects of vegetable tannin in a multitest study

Tannin from mimosa trees (Acacia sp.) utilized in traditional leather tanning was tested for toxicity in sea urchin (Sphaerechinus granularis and Paracentrotus lividus) embryos and sperm, marine, and freshwater algae (Selenastrum capricornutum and Dunaliella tertiolecta), and Daphnia magna. Based on...

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Veröffentlicht in:Archives of environmental contamination and toxicology 2004-04, Vol.46 (3), p.336-344
Hauptverfasser: DE NICOLA, E, GALLO, M, PAGANO, G, IACCARINO, M, MERIC, S, ORAL, R, RUSSO, T, SORRENTINO, T, TÜNAY, O, VUTTARIELLO, E, WARNAU, M
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container_title Archives of environmental contamination and toxicology
container_volume 46
creator DE NICOLA, E
GALLO, M
PAGANO, G
IACCARINO, M
MERIC, S
ORAL, R
RUSSO, T
SORRENTINO, T
TÜNAY, O
VUTTARIELLO, E
WARNAU, M
description Tannin from mimosa trees (Acacia sp.) utilized in traditional leather tanning was tested for toxicity in sea urchin (Sphaerechinus granularis and Paracentrotus lividus) embryos and sperm, marine, and freshwater algae (Selenastrum capricornutum and Dunaliella tertiolecta), and Daphnia magna. Based on a two-step tanning procedure used in traditional tanneries, two mimosa tannin preparations, i.e., fresh tannin (FT) and used tannin (UT), were tested as suspensions. The early results in S. granularis embryos showed that UT exerted lower acute toxicity than FT, namely, 1 vs 100 mg/L, to obtain 100% mortality, respectively. Subsequent bioassays were conducted on fresh tannin water extracts (TWE) corresponding to nominal tannin concentrations ranging from 0.1 to 30 mg/L. Developmental toxicity, up to embryonic mortality was exerted by TWE at levels > 1 mg/L, S. granularis being more sensitive than P. lividus embryos/larvae. At the concentration of 0.1 mg/L, the frequencies of larval malformations were significantly lower than in controls. This positive stimulatory effect (currently termed as hormesis) was observed in extended numbers of culture replicates (up to 14) and was significant in the embryo cultures characterized by a relatively poor control quality (with < 70% viable larvae in controls), whereas this effect was not observed in good-quality cultures (with > or = 70% viable larvae in controls). Cytogenetic analysis of S. granularis embryos reared in FT or UT suspensions (1 mg/L to 1 g/L) showed mitotoxic effects (decrease in active mitoses per embryo) in FT-exposed, but not in UT-exposed embryos. Mitotic aberrations were significantly increased by 10 mg/L UT. Sperm fertilization success in both sea urchin species showed an increasing fertilization rate (FR) up to 0.3 mg/L TWE and a dose-related decrease in FR up to 30 mg/L. Again, the offspring of P. lividus sperm exposed to TWE (0.1 and 0.3 mg/L) showed a decrease in larval malformations compared to controls, whereas a dose-related increase in developmental defects was observed in the offspring of P. lividus sperm exposed to higher TWE levels (1 to 30 mg/L). Algal cell growth bioassays in two species (S. capricornutum and D. tertiolecta) also showed a maximum growth at TWE levels ranging from 0.3 to 3 mg/L and a subsequent decline up to 30 mg/L TWE. D. magna bioassays resulted in daphnid immobilization by TWE concentrations ranging from 100 to 300 mg/L. The results demonstrate that tannins utilized in tr
doi_str_mv 10.1007/s00244-003-2293-5
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Based on a two-step tanning procedure used in traditional tanneries, two mimosa tannin preparations, i.e., fresh tannin (FT) and used tannin (UT), were tested as suspensions. The early results in S. granularis embryos showed that UT exerted lower acute toxicity than FT, namely, 1 vs 100 mg/L, to obtain 100% mortality, respectively. Subsequent bioassays were conducted on fresh tannin water extracts (TWE) corresponding to nominal tannin concentrations ranging from 0.1 to 30 mg/L. Developmental toxicity, up to embryonic mortality was exerted by TWE at levels &gt; 1 mg/L, S. granularis being more sensitive than P. lividus embryos/larvae. At the concentration of 0.1 mg/L, the frequencies of larval malformations were significantly lower than in controls. This positive stimulatory effect (currently termed as hormesis) was observed in extended numbers of culture replicates (up to 14) and was significant in the embryo cultures characterized by a relatively poor control quality (with &lt; 70% viable larvae in controls), whereas this effect was not observed in good-quality cultures (with &gt; or = 70% viable larvae in controls). Cytogenetic analysis of S. granularis embryos reared in FT or UT suspensions (1 mg/L to 1 g/L) showed mitotoxic effects (decrease in active mitoses per embryo) in FT-exposed, but not in UT-exposed embryos. Mitotic aberrations were significantly increased by 10 mg/L UT. Sperm fertilization success in both sea urchin species showed an increasing fertilization rate (FR) up to 0.3 mg/L TWE and a dose-related decrease in FR up to 30 mg/L. Again, the offspring of P. lividus sperm exposed to TWE (0.1 and 0.3 mg/L) showed a decrease in larval malformations compared to controls, whereas a dose-related increase in developmental defects was observed in the offspring of P. lividus sperm exposed to higher TWE levels (1 to 30 mg/L). Algal cell growth bioassays in two species (S. capricornutum and D. tertiolecta) also showed a maximum growth at TWE levels ranging from 0.3 to 3 mg/L and a subsequent decline up to 30 mg/L TWE. D. magna bioassays resulted in daphnid immobilization by TWE concentrations ranging from 100 to 300 mg/L. The results demonstrate that tannins utilized in traditional leather tanning industry may raise concern of environmental damage at relatively high concentrations, whereas low-level tannins may result in hormetic effects. The present study also points to the need for bioassay design that should rely on adequate criteria in control quality, allowing to detect both inhibitory and hormetic effects.</description><identifier>ISSN: 0090-4341</identifier><identifier>EISSN: 1432-0703</identifier><identifier>DOI: 10.1007/s00244-003-2293-5</identifier><identifier>PMID: 15195805</identifier><identifier>CODEN: AECTCV</identifier><language>eng</language><publisher>Heidelberg: Springer-Verlag</publisher><subject>Acacia ; Acacia - chemistry ; Acute toxicity ; Algae ; Animal, plant and microbial ecology ; Animals ; Applied ecology ; Bioassays ; Biological and medical sciences ; Biological Assay - methods ; Brackish ; Chlorophyta - genetics ; Chlorophyta - growth &amp; development ; Congenital Abnormalities - veterinary ; Daphnia - embryology ; Daphnia - genetics ; Daphnia - growth &amp; development ; Daphnia magna ; Dunaliella tertiolecta ; Echinoidea ; Ecotoxicology, biological effects of pollution ; Embryos ; Environmental degradation ; Fertilization - drug effects ; Freshwater ; Fundamental and applied biological sciences. Psychology ; General aspects ; Larva - growth &amp; development ; Larvae ; Marine ; Mimosa ; Mortality ; Offspring ; Paracentrotus lividu ; Paracentrotus lividus ; Quality Control ; Reproducibility of Results ; Sea Urchins - embryology ; Sea Urchins - genetics ; Sea Urchins - growth &amp; development ; Selenastrum capricornutum ; Sperm ; Sphaerechinus granularis ; Tanning industry ; Tannins ; Tannins - toxicity ; Toxicity</subject><ispartof>Archives of environmental contamination and toxicology, 2004-04, Vol.46 (3), p.336-344</ispartof><rights>2004 INIST-CNRS</rights><rights>Springer-Verlag 2004</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c387t-343d16c5abd2ef5f922d48d3d0edecaea8fba3818f81f88b69c540565cae642e3</citedby></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,776,780,27903,27904</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&amp;idt=15783673$$DView record in Pascal Francis$$Hfree_for_read</backlink><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/15195805$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>DE NICOLA, E</creatorcontrib><creatorcontrib>GALLO, M</creatorcontrib><creatorcontrib>PAGANO, G</creatorcontrib><creatorcontrib>IACCARINO, M</creatorcontrib><creatorcontrib>MERIC, S</creatorcontrib><creatorcontrib>ORAL, R</creatorcontrib><creatorcontrib>RUSSO, T</creatorcontrib><creatorcontrib>SORRENTINO, T</creatorcontrib><creatorcontrib>TÜNAY, O</creatorcontrib><creatorcontrib>VUTTARIELLO, E</creatorcontrib><creatorcontrib>WARNAU, M</creatorcontrib><title>Hormetic versus toxic effects of vegetable tannin in a multitest study</title><title>Archives of environmental contamination and toxicology</title><addtitle>Arch Environ Contam Toxicol</addtitle><description>Tannin from mimosa trees (Acacia sp.) utilized in traditional leather tanning was tested for toxicity in sea urchin (Sphaerechinus granularis and Paracentrotus lividus) embryos and sperm, marine, and freshwater algae (Selenastrum capricornutum and Dunaliella tertiolecta), and Daphnia magna. Based on a two-step tanning procedure used in traditional tanneries, two mimosa tannin preparations, i.e., fresh tannin (FT) and used tannin (UT), were tested as suspensions. The early results in S. granularis embryos showed that UT exerted lower acute toxicity than FT, namely, 1 vs 100 mg/L, to obtain 100% mortality, respectively. Subsequent bioassays were conducted on fresh tannin water extracts (TWE) corresponding to nominal tannin concentrations ranging from 0.1 to 30 mg/L. Developmental toxicity, up to embryonic mortality was exerted by TWE at levels &gt; 1 mg/L, S. granularis being more sensitive than P. lividus embryos/larvae. At the concentration of 0.1 mg/L, the frequencies of larval malformations were significantly lower than in controls. This positive stimulatory effect (currently termed as hormesis) was observed in extended numbers of culture replicates (up to 14) and was significant in the embryo cultures characterized by a relatively poor control quality (with &lt; 70% viable larvae in controls), whereas this effect was not observed in good-quality cultures (with &gt; or = 70% viable larvae in controls). Cytogenetic analysis of S. granularis embryos reared in FT or UT suspensions (1 mg/L to 1 g/L) showed mitotoxic effects (decrease in active mitoses per embryo) in FT-exposed, but not in UT-exposed embryos. Mitotic aberrations were significantly increased by 10 mg/L UT. Sperm fertilization success in both sea urchin species showed an increasing fertilization rate (FR) up to 0.3 mg/L TWE and a dose-related decrease in FR up to 30 mg/L. Again, the offspring of P. lividus sperm exposed to TWE (0.1 and 0.3 mg/L) showed a decrease in larval malformations compared to controls, whereas a dose-related increase in developmental defects was observed in the offspring of P. lividus sperm exposed to higher TWE levels (1 to 30 mg/L). Algal cell growth bioassays in two species (S. capricornutum and D. tertiolecta) also showed a maximum growth at TWE levels ranging from 0.3 to 3 mg/L and a subsequent decline up to 30 mg/L TWE. D. magna bioassays resulted in daphnid immobilization by TWE concentrations ranging from 100 to 300 mg/L. The results demonstrate that tannins utilized in traditional leather tanning industry may raise concern of environmental damage at relatively high concentrations, whereas low-level tannins may result in hormetic effects. The present study also points to the need for bioassay design that should rely on adequate criteria in control quality, allowing to detect both inhibitory and hormetic effects.</description><subject>Acacia</subject><subject>Acacia - chemistry</subject><subject>Acute toxicity</subject><subject>Algae</subject><subject>Animal, plant and microbial ecology</subject><subject>Animals</subject><subject>Applied ecology</subject><subject>Bioassays</subject><subject>Biological and medical sciences</subject><subject>Biological Assay - methods</subject><subject>Brackish</subject><subject>Chlorophyta - genetics</subject><subject>Chlorophyta - growth &amp; development</subject><subject>Congenital Abnormalities - veterinary</subject><subject>Daphnia - embryology</subject><subject>Daphnia - genetics</subject><subject>Daphnia - growth &amp; development</subject><subject>Daphnia magna</subject><subject>Dunaliella tertiolecta</subject><subject>Echinoidea</subject><subject>Ecotoxicology, biological effects of pollution</subject><subject>Embryos</subject><subject>Environmental degradation</subject><subject>Fertilization - drug effects</subject><subject>Freshwater</subject><subject>Fundamental and applied biological sciences. Psychology</subject><subject>General aspects</subject><subject>Larva - growth &amp; development</subject><subject>Larvae</subject><subject>Marine</subject><subject>Mimosa</subject><subject>Mortality</subject><subject>Offspring</subject><subject>Paracentrotus lividu</subject><subject>Paracentrotus lividus</subject><subject>Quality Control</subject><subject>Reproducibility of Results</subject><subject>Sea Urchins - embryology</subject><subject>Sea Urchins - genetics</subject><subject>Sea Urchins - growth &amp; development</subject><subject>Selenastrum capricornutum</subject><subject>Sperm</subject><subject>Sphaerechinus granularis</subject><subject>Tanning industry</subject><subject>Tannins</subject><subject>Tannins - toxicity</subject><subject>Toxicity</subject><issn>0090-4341</issn><issn>1432-0703</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2004</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><sourceid>BENPR</sourceid><recordid>eNpdkE1LxDAQhoMouq7-AC9SBL1VJ19tepTFVWHBi55Dmk6kSz80ScX992bZBUUIhEyeeWd4CLmgcEsByrsAwITIAXjOWMVzeUBmVHCWQwn8kMwAKsgFF_SEnIawBqBMKXFMTqiklVQgZ2T5NPoeY2uzL_RhClkcv9MDnUMbQza6VH_HaOoOs2iGoR2ydEzWT11sI4aYhTg1mzNy5EwX8Hx_z8nb8uF18ZSvXh6fF_er3HJVxpwL3tDCSlM3DJ10FWONUA1vABu0Bo1yteGKKqeoU6ouKisFyEKmv0Iw5HNys8v98OPnlMbrvg0Wu84MOE5BM6BVJUqewKt_4Hqc_JB20yWnSlZUbiG6g6wfQ_Do9Idve-M3moLeGtY7wzoZ1lvDWqaey33wVPfY_HbslSbgeg-YYE3nvBlsG_5wpeJF2vAHSpCDbQ</recordid><startdate>20040401</startdate><enddate>20040401</enddate><creator>DE NICOLA, E</creator><creator>GALLO, M</creator><creator>PAGANO, G</creator><creator>IACCARINO, M</creator><creator>MERIC, S</creator><creator>ORAL, R</creator><creator>RUSSO, T</creator><creator>SORRENTINO, T</creator><creator>TÜNAY, O</creator><creator>VUTTARIELLO, E</creator><creator>WARNAU, M</creator><general>Springer-Verlag</general><general>Springer Nature B.V</general><scope>IQODW</scope><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>3V.</scope><scope>7T7</scope><scope>7TV</scope><scope>7U7</scope><scope>7WY</scope><scope>7WZ</scope><scope>7X7</scope><scope>7XB</scope><scope>87Z</scope><scope>88E</scope><scope>88I</scope><scope>8C1</scope><scope>8FD</scope><scope>8FI</scope><scope>8FJ</scope><scope>8FK</scope><scope>8FL</scope><scope>ABUWG</scope><scope>AEUYN</scope><scope>AFKRA</scope><scope>ATCPS</scope><scope>AZQEC</scope><scope>BENPR</scope><scope>BEZIV</scope><scope>BHPHI</scope><scope>C1K</scope><scope>CCPQU</scope><scope>DWQXO</scope><scope>FR3</scope><scope>FRNLG</scope><scope>FYUFA</scope><scope>F~G</scope><scope>GHDGH</scope><scope>GNUQQ</scope><scope>HCIFZ</scope><scope>K60</scope><scope>K6~</scope><scope>K9.</scope><scope>L.-</scope><scope>M0C</scope><scope>M0S</scope><scope>M1P</scope><scope>M2P</scope><scope>P64</scope><scope>PATMY</scope><scope>PQBIZ</scope><scope>PQBZA</scope><scope>PQEST</scope><scope>PQQKQ</scope><scope>PQUKI</scope><scope>PYCSY</scope><scope>Q9U</scope><scope>7QH</scope><scope>7SN</scope><scope>7TN</scope><scope>7UA</scope><scope>F1W</scope><scope>H97</scope><scope>L.G</scope></search><sort><creationdate>20040401</creationdate><title>Hormetic versus toxic effects of vegetable tannin in a multitest study</title><author>DE NICOLA, E ; GALLO, M ; PAGANO, G ; IACCARINO, M ; MERIC, S ; ORAL, R ; RUSSO, T ; SORRENTINO, T ; TÜNAY, O ; VUTTARIELLO, E ; WARNAU, M</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c387t-343d16c5abd2ef5f922d48d3d0edecaea8fba3818f81f88b69c540565cae642e3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2004</creationdate><topic>Acacia</topic><topic>Acacia - chemistry</topic><topic>Acute toxicity</topic><topic>Algae</topic><topic>Animal, plant and microbial ecology</topic><topic>Animals</topic><topic>Applied ecology</topic><topic>Bioassays</topic><topic>Biological and medical sciences</topic><topic>Biological Assay - methods</topic><topic>Brackish</topic><topic>Chlorophyta - genetics</topic><topic>Chlorophyta - growth &amp; development</topic><topic>Congenital Abnormalities - veterinary</topic><topic>Daphnia - embryology</topic><topic>Daphnia - genetics</topic><topic>Daphnia - growth &amp; development</topic><topic>Daphnia magna</topic><topic>Dunaliella tertiolecta</topic><topic>Echinoidea</topic><topic>Ecotoxicology, biological effects of pollution</topic><topic>Embryos</topic><topic>Environmental degradation</topic><topic>Fertilization - drug effects</topic><topic>Freshwater</topic><topic>Fundamental and applied biological sciences. Psychology</topic><topic>General aspects</topic><topic>Larva - growth &amp; development</topic><topic>Larvae</topic><topic>Marine</topic><topic>Mimosa</topic><topic>Mortality</topic><topic>Offspring</topic><topic>Paracentrotus lividu</topic><topic>Paracentrotus lividus</topic><topic>Quality Control</topic><topic>Reproducibility of Results</topic><topic>Sea Urchins - embryology</topic><topic>Sea Urchins - genetics</topic><topic>Sea Urchins - growth &amp; development</topic><topic>Selenastrum capricornutum</topic><topic>Sperm</topic><topic>Sphaerechinus granularis</topic><topic>Tanning industry</topic><topic>Tannins</topic><topic>Tannins - toxicity</topic><topic>Toxicity</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>DE NICOLA, E</creatorcontrib><creatorcontrib>GALLO, M</creatorcontrib><creatorcontrib>PAGANO, G</creatorcontrib><creatorcontrib>IACCARINO, M</creatorcontrib><creatorcontrib>MERIC, S</creatorcontrib><creatorcontrib>ORAL, R</creatorcontrib><creatorcontrib>RUSSO, T</creatorcontrib><creatorcontrib>SORRENTINO, T</creatorcontrib><creatorcontrib>TÜNAY, O</creatorcontrib><creatorcontrib>VUTTARIELLO, E</creatorcontrib><creatorcontrib>WARNAU, M</creatorcontrib><collection>Pascal-Francis</collection><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>ProQuest Central (Corporate)</collection><collection>Industrial and Applied Microbiology Abstracts (Microbiology A)</collection><collection>Pollution Abstracts</collection><collection>Toxicology Abstracts</collection><collection>ABI/INFORM Collection</collection><collection>ABI/INFORM Global (PDF only)</collection><collection>Health &amp; 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Based on a two-step tanning procedure used in traditional tanneries, two mimosa tannin preparations, i.e., fresh tannin (FT) and used tannin (UT), were tested as suspensions. The early results in S. granularis embryos showed that UT exerted lower acute toxicity than FT, namely, 1 vs 100 mg/L, to obtain 100% mortality, respectively. Subsequent bioassays were conducted on fresh tannin water extracts (TWE) corresponding to nominal tannin concentrations ranging from 0.1 to 30 mg/L. Developmental toxicity, up to embryonic mortality was exerted by TWE at levels &gt; 1 mg/L, S. granularis being more sensitive than P. lividus embryos/larvae. At the concentration of 0.1 mg/L, the frequencies of larval malformations were significantly lower than in controls. This positive stimulatory effect (currently termed as hormesis) was observed in extended numbers of culture replicates (up to 14) and was significant in the embryo cultures characterized by a relatively poor control quality (with &lt; 70% viable larvae in controls), whereas this effect was not observed in good-quality cultures (with &gt; or = 70% viable larvae in controls). Cytogenetic analysis of S. granularis embryos reared in FT or UT suspensions (1 mg/L to 1 g/L) showed mitotoxic effects (decrease in active mitoses per embryo) in FT-exposed, but not in UT-exposed embryos. Mitotic aberrations were significantly increased by 10 mg/L UT. Sperm fertilization success in both sea urchin species showed an increasing fertilization rate (FR) up to 0.3 mg/L TWE and a dose-related decrease in FR up to 30 mg/L. Again, the offspring of P. lividus sperm exposed to TWE (0.1 and 0.3 mg/L) showed a decrease in larval malformations compared to controls, whereas a dose-related increase in developmental defects was observed in the offspring of P. lividus sperm exposed to higher TWE levels (1 to 30 mg/L). Algal cell growth bioassays in two species (S. capricornutum and D. tertiolecta) also showed a maximum growth at TWE levels ranging from 0.3 to 3 mg/L and a subsequent decline up to 30 mg/L TWE. D. magna bioassays resulted in daphnid immobilization by TWE concentrations ranging from 100 to 300 mg/L. The results demonstrate that tannins utilized in traditional leather tanning industry may raise concern of environmental damage at relatively high concentrations, whereas low-level tannins may result in hormetic effects. The present study also points to the need for bioassay design that should rely on adequate criteria in control quality, allowing to detect both inhibitory and hormetic effects.</abstract><cop>Heidelberg</cop><cop>Berlin</cop><cop>New York, NY</cop><pub>Springer-Verlag</pub><pmid>15195805</pmid><doi>10.1007/s00244-003-2293-5</doi><tpages>9</tpages></addata></record>
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identifier ISSN: 0090-4341
ispartof Archives of environmental contamination and toxicology, 2004-04, Vol.46 (3), p.336-344
issn 0090-4341
1432-0703
language eng
recordid cdi_proquest_miscellaneous_20199473
source MEDLINE; SpringerLink Journals - AutoHoldings
subjects Acacia
Acacia - chemistry
Acute toxicity
Algae
Animal, plant and microbial ecology
Animals
Applied ecology
Bioassays
Biological and medical sciences
Biological Assay - methods
Brackish
Chlorophyta - genetics
Chlorophyta - growth & development
Congenital Abnormalities - veterinary
Daphnia - embryology
Daphnia - genetics
Daphnia - growth & development
Daphnia magna
Dunaliella tertiolecta
Echinoidea
Ecotoxicology, biological effects of pollution
Embryos
Environmental degradation
Fertilization - drug effects
Freshwater
Fundamental and applied biological sciences. Psychology
General aspects
Larva - growth & development
Larvae
Marine
Mimosa
Mortality
Offspring
Paracentrotus lividu
Paracentrotus lividus
Quality Control
Reproducibility of Results
Sea Urchins - embryology
Sea Urchins - genetics
Sea Urchins - growth & development
Selenastrum capricornutum
Sperm
Sphaerechinus granularis
Tanning industry
Tannins
Tannins - toxicity
Toxicity
title Hormetic versus toxic effects of vegetable tannin in a multitest study
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