natgillin/translations-raw huggingface dataset:
OECD (2007) Final Report of the Validation of the Amphibian Metamorphosis Assay:
OECD (2007.) Final Report of the Validation of the Amphibian Metamorphosis Assay:
Phase 2 — Multi-chemical Interlaboratory Study.
Phase 2 – Multi-chemical Interlaboratory Study.
American Society for Testing and Materials, ASTM E729-96(2002), Philadelpia, PA
American Society for Testing and Materials, ASTM E729-96(2002.), Philadelpia, PA
ASTM (2004) Standard Guide for Conducting the Frog Embryo Teratogenesis Assay — Xenopus (FETAX).
ASTM (2004.) Standard Guide for Conducting the Frog Embryo Teratogenesis Assay – Xenopus (FETAX).
Chemosphere 39, pp. 539-551
Chemosphere 39, str. 539. – 551.
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OECD (2007.) Guidance Document on Amphibian Thyroid Histology.
OECD (2006) Current Approaches in the Statistical Analysis of Ecotoxicity Data:
OECD (2006.) Current Approaches in the Statistical Analysis of Ecotoxicity Data:
ROW
REDAK
Any substance or mixture tested using this test method
Bilo koja tvar ili smjesa ispitivana primjenom ove ispitne metode.
Appropriate statistical methods should be used according to OECD Document 54 on the Current Approaches in the Statistical Analysis of Ecotoxicity Data:
Potrebno je upotrebljavati odgovarajuće statističke metode u skladu s OECD-ovom Smjernicom o sadašnjim pristupima statističke analize podataka o ekotoksičnosti:
a Guidance to Application (9).
Smjernice za primjenu (9).
In general, adverse effects of the test chemical compared to the control are investigated using one-tailed hypothesis testing at p ≤ 0,05.
Općenito, štetni učinci ispitivane kemikalije u usporedbi s kontrolom istražuju se primjenom jednosmjernog testiranja hipoteze na p ≤ 0,05.
the NOEC/LOEC values, LCx for mortality and ECx for reproduction (mostly LC50, LC10, EC50, and EC10) together with 95 % confidence intervals. A graph of the fitted model used for calculation, its function equation and its parameters (See (9));
vrijednosti NOEC-a/LOEC-a, LCx za smrtnost i ECx za reprodukciju (uglavnom LC50, LC10, EC50 i EC10) zajedno s 95 %-im intervalima pouzdanosti. grafikon prilagođenog modela koji se upotrebljava za izračun, njegova funkcionalna jednadžba i njegovi parametri (vidi (9));
International Organisation for Standardisation, Geneve
Međunarodna organizacija za normizaciju, Ženeva
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Petersen H (1994) A review of collembolan ecology in ecosystem context.
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Hopkin SP (1997).
Hopkin SP (1997.).
Oxford University Press.
Oxford University Press. str. 330.
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In New trends in soil Biology (Lebrun Ph, André HM, De Medts A, Grégoire-Wibo, Wauthy G (Eds), Proceedings of the VI. international colloquium on soil zoology, Louvain-la-neuve (Belgium), 30. kolovoza – 2. rujna 1982., I Dieu-Brichart, Ottignies-Louvain-la-Neuve, str. 261. – 268.
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OECD (2006.), Current approaches in the statistical analysis of ecotoxicity data:
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Environmental Project Nr. 986.
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Miljøstyrelsen 61 pp. Danish Ministry for the Environment.
Miljøstyrelsen str. 61. Danish Ministry for the Environment.
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Krogh PH, Johansen K and Holmstrup M (1998.) Automatic counting of collembolans for laboratory experiments.
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Fjellberg A (1980) Identification keys to Norwegian collembolans.
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Goto HE (1960) Simple techniques for the rearing of Collembola and a not on the use of a fungistatic substance in the cultures.
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Entomologists' Monthly Magazine 96:138-140.
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Extraction is started at 25 °C and the temperature is increased automatically every 12 h by 5 °C and has a total duration of 48 hours.
Ekstrakcija započinje na 25 °C i temperatura se automatski povećava svakih 12 sati za 5 °C te ima ukupno trajanje od 48 sati.
After 12 h at 40 °C the extraction is finished.
Nakon 12 sati na 40 °C ekstrakcija je završena.
The solubilising agent concentration in the final test medium should be minimal (i.e. ≤ 0,1 ml/l) and should be the same in all treatments.
Koncentracija otapajućeg sredstva u konačnom ispitnom mediju trebala bi biti minimalna (odnosno ≤ 0,1 ml/l) i trebala bi biti ista u svim grupama.
When a solubilising agent is used, it should have no significant effects on survival as revealed by a solvent control in comparison with a negative (water) control.
Kada se upotrebljava otapajuće sredstvo, ono ne smije imati nikakve znatne učinke na preživljavanje prema podacima kontrolne skupine s otapalom u usporedbi s podacima negativne kontrolne skupine s vodom.
However, every effort should be made to avoid the use of such materials.
Međutim, potrebno je uložiti sve napore da se izbjegne upotreba takvih tvari.
Stock solutions — Spiked sediment
Radne otopine – sediment obrađen spikingom
volume of overlying and pore water; weight of wet sediment with and without pore water for the test vessels and the crystallising dishes;
volumen vode iznad sedimenta i porne vode, masa mokrog sedimenta s i bez porne vode za ispitne posude i posude za kristalizaciju;
Entomologica Scandinavica, 30:
Entomologica Scandinavica, 30: 311.
SETAC (1993), Guidance Document on Sediment toxicity Tests and Bioassays for Freshwater and Marine Environments, From the WOSTA Workshop held in the Netherlands.
SETAC (1993.), Guidance Document on Sediment toxicity Tests and Bioassays for Freshwater and Marine Environments, From the WOSTA Workshop held in the Netherlands.
ASTM International (2009), E1706-05E01:
ASTM International (2009.), E1706-05E01:
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US-EPA/OPPTS 850.1735 (1996), Whole Sediment Acute Toxicity Invertebrates.
US-EPA/OPPTS 850.1735 (1996.), Whole Sediment Acute Toxicity Invertebrates.
US-EPA/OPPTS 850.1790 (1996), Chironomid Sediment toxicity Test.
US-EPA/OPPTS 850.1790 (1996.), Chironomid Sediment toxicity Test.
Kirby (1996), Recent intra- and inter-laboratory studies related to the development and standardisation of Environment Canada's biological test methods for measuring sediment toxicity using freshwater amphipods (Hyalella azteca) and midge larvae (Chironomus riparius), Technical Report, Environment Canada, National Water Research Institute, Burlington, Ontario, Canada.
Kirby (1996.), Recent intra- and inter-laboratory studies related to the development and standardisation of Environment Canada's biological test methods for measuring sediment toxicity using freshwater amphipods (Hyalella azteca) and midge larvae (Chironomus riparius), Technical Report, Environment Canada, National Water Research Institute, Burlington, Ontario, Canada.
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A glass tube (inner diameter ca. 5 mm) connected to a self-priming pump
A staklena cjevčica (unutarnji promjer otprilike 5 mm) spojena na samousisnu crpku
B cork of vulcanised rubber, perforated with glass tube (A).
B čep od vulkanizirane gume, probušen staklenom cjevčicom (A).
MOA
Način djelovanja
An overview of relevant test conditions specific for validated species: Japanese medaka, the three-spined stickleback and zebrafish is provided in Appendix 2.
Pregled relevantnih uvjeta ispitivanja specifičnih za validirane vrste, a to su medaka, koljuška i zebrica, prikazan je u Dodatku 2.
30-70 %
30 – 70 %
For the semi-static technique, two different renewal procedures may be followed.
Kod polustatičnog postupka mogu se primjenjivati dva različita postupka obnavljanja.
Either new test solutions are prepared in clean chambers and surviving eggs and larvae gently transferred into the new chambers, or the test organisms are retained in the test chambers whilst a proportion (at least two thirds) of the test water is changed daily.
Pripremaju se nove ispitne otopine u čistim posudama te se preživjela jajašca i ličinke nježno prenose u nove posude ili se ispitni organizmi zadržavaju u ispitnim posudama dok se dio ispitne vode (najmanje dvije trećine) mijenja svakog dana.
Relevant physical-chemical properties; chemical identification data including purity and analytical method for quantification of the test chemical.
relevantna fizikalno-kemijska svojstva, podatke za identifikaciju kemikalije, uključujući podatke o čistoći i analitičkoj metodi za kvantifikaciju ispitivane kemikalije,
OECD (1992), Fish, Early Life Stage Toxicity Test, Test Guideline No. 210, Guidelines for the Testing of Chemicals, OECD, Paris.
OECD (1992.), Fish, Early Life Stage Toxicity Test, Test Guideline No. 210, Guidelines for the Testing of Chemicals, OECD, Pariz.
Tyler, C.R., R.van Aerle, T.H.
Tyler, C. R., R. van Aerle, T. H. Hutchinson, S. Maddix i H. Trip (1999.), ‚An in vivo testing system for endocrine disruptors in fish early life stages using induction of vitellogenin’, Environmental Toxicology and Chemistry 18, str. 337.
Brion, F., B.M. Nilsen, J.K. Eidem, A. Goksoyr, and J.M.
Brion, F., B. M. Nilsen, J. K. Eidem, A. Goksoyr i J. M. Porcher (2002.), ‚Development and validation of an enzyme-linked immunosorbent assay to measure vitellogenin in the zebrafish (Danio rerio)’, Environmental Toxicology and Chemistry 21, str. 1699.
Hahlbeck, E., I. Katsiadaki, I. Mayer, M. Adolfsson-Erici, J. James, and B.E.
Hahlbeck, E., I. Katsiadaki, I. Mayer, M. Adolfsson-Erici, J. James i B. E. Bengtsson (2004.), ‚The juvenile three-spined stickleback (Gasterosteus aculeatus L.) as a model organism for endocrine disruption – II – kidney hypertrophy, vitellogenin and spiggin induction’, Aquatic Toxicology 70, str. 311.
Jensen, K.M. and G.T.
Jensen, K. M., i G. T. Ankley (2006.), ‚Evaluation of a commercial kit for measuring vitellogenin in the fathead minnow (Pimephales promelas)’, Ecotoxicology and Environmental Safety 64, str. 101.
OECD (2010), Guidance Document on the Diagnosis of Endocrine-related Histopathology in Fish Gonads, Series on Testing and Assessment No. 123, ENV/JM/MONO(2010)14, OECD, Paris.
OECD (2010.), Guidance Document on the Diagnosis of Endocrine-related Histopathology in Fish Gonads, Series on Testing and Assessment No. 123, ENV/JM/MONO(2010)14, OECD, Pariz.
Kobayashi, T., M. Matsuda, H. Kajiura-Kobayashi, A. Suzuki, N. Saito, M. Nakamoto, N. Shibata, and Y.
Kobayashi, T., M. Matsuda, H. Kajiura-Kobayashi, A. Suzuki, N. Saito, M. Nakamoto, N. Shibata i Y.
Kidd, K.A., P.J. Blanchfield, K.H. Mills, V.P. Palace, R.E. Evans, J.M. Lazorchak, and R.W.
Kidd, K. A., P. J. Blanchfield, K. H. Mills, V. P. Palace, R. E. Evans, J. M. Lazorchak i R. W.
Palace,V.P., R.E. Evans, K.G. Wautier, K.H. Mills, P.J. Blanchfield, B.J. Park, C.L. Baron, and K.A.
Palace, V. P., R. E. Evans, K. G. Wautier, K. H. Mills, P. J. Blanchfield, B. J. Park, C. L. Baron i K. A. Kidd (2009.), ‚Interspecies differences in biochemical, histopathological, and population responses in four wild fish species exposed to ethynylestradiol added to a whole lake’, Canadian Journal of Fisheries and Aquatic Sciences 66, str. 1920.
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OECD (2000), Guidance Document on Aquatic Toxicity Testing of Difficult Substances and Mixtures, Series on Testing and Assessment No. 23, OECD, Paris.
OECD (2000.), Guidance Document on Aquatic Toxicity Testing of Difficult Substances and Mixtures, Series on Testing and Assessment No. 23, OECD, Pariz.
OECD (2009), Fish Short Term Reproduction Assay, Test Guideline No. 229, Guidelines for the Testing of Chemicals, OECD, Paris.
OECD (2009.), Fish Short Term Reproduction Assay, Test Guideline No. 229, Guidelines for the Testing of Chemicals, OECD, Pariz.
OECD (2012), Fish Toxicity Testing Framework, Series on Testing and Assessment No. 171, OECD, Paris
OECD (2012.), Fish Toxicity Testing Framework, Series on Testing and Assessment No. 171, OECD, Pariz.
OECD (2011), Validation Report (Phase 1) for the Fish Sexual Development Test, Series on Testing and Assessment No 141, ENV/JM/MONO(2011)22, OECD, Paris.
OECD (2011.), Validation Report (Phase 1) for the Fish Sexual Development Test, Series on Testing and Assessment No 141, ENV/JM/MONO(2011)22, OECD, Pariz.
OECD (2011), Validation Report ( Phase 2) for the Fish Sexual Development Test, Series on Testing and Assessment No 142, ENV/JM/MONO(2011)23, OECD, Paris.
OECD (2011.), Validation Report (Phase 2) for the Fish Sexual Development Test, Series on Testing and Assessment No 142, ENV/JM/MONO(2011)23, OECD, Pariz.
OECD (2011), Peer Review Report of the validation of the Fish Sexual Development Test, Series on Testing and Assessment No 143, ENV/JM/MONO(2011)24, OECD, Paris.
OECD (2011.), Peer Review Report of the validation of the Fish Sexual Development Test, Series on Testing and Assessment No 143, ENV/JM/MONO(2011)24, OECD, Pariz.
30 %-70 %
30 % – 70 %
The absorbance is measured at 450 nm (e.g. on a Molecular Devices Thermomax plate reader).
Apsorbancija se mjeri na 450 nm (npr. na čitaču pločica Molecular Devices Thermomax).
Data are analysed on the associated software (e.g. Softmax).
Podaci se analiziraju povezanim softverom (npr. Softmaxom).
Denslow, N.D., Chow, M.C., Kroll, K.J., Green, L. (1999).
Denslow, N. D., Chow, M.C., Kroll, K. J., Green, L. (1999.).
ad 100 ml dest. H2O
dodaje se 100 ml destiliranog H2O
5 min 95 °C
pet minuta na 95 °C
DOC;
DOC,
An example of a theoretical degradation experiment illustrating a feasible way of estimating the values of tL (length of “lag phase”) and t50 (time interval, starting at tL), needed to reach 50 per cent removal, is given in the figure below. Dunnett's Test
Primjer pokusa teoretske razgradnje kojim se ilustrira izvediv način procjene vrijednosti tL (duljine ‚eksponencijalne faze razvoja’) i t50 (vremenskog intervala počevši od tL) potrebnog za postizanje 50 %-tnog uklanjanja prikazan je na slici u nastavku.
Saturate the test medium with air at the test temperature by aerating with clean compressed air for about 20 minutes.
Ispitni medij zasićuje se zrakom na ispitnoj temperaturi dozračivanjem čistim komprimiranim zrakom oko 20 minuta.
Determine the concentration of dissolved oxygen for control purposes.
Određuje se koncentracija otopljenog kisika u svrhu kontrole.
the blank BOD of the seawater; and
BPK morske vode u slijepim probama i
% biodegradation
% biorazgradnje
mgtested substance
mgispitivane tvari
mg ThOD
mg TPK
mg COD
mg KPK
de Kreuk J.F. and Hanstveit A.O. (1981). Determination of the biodegradability of the organic fraction of chemical wastes.
de Kreuk, J .F., i Hanstveit, A. O. (1981.) Determination of the biodegradability of the organic fraction of chemical wastes.
Chemosphere, 10 (6);
Chemosphere, 10 (6), 561.
Nyholm N. and Kristensen P. (1987). Screening Test Methods for Assessment of Biodegradability of Chemical Substances in Seawater.
Nyholm, N., i Kristensen, P. (1987.) Screening Test Methods for Assessment of Biodegradability of Chemical Substances in Seawater.
Samples of high chloride concentrations and/or larger sample volumes can be analysed according to this method provided that build-up of chloride in the oxidation vessel is prevented.
Uzorci s visokim koncentracijama klorida i/ili veliki volumeni uzoraka mogu se analizirati u skladu s navedenom metodom pod uvjetom da se spriječi stvaranje klorida u oksidacijskoj posudi.
Determination of volatile organic carbon can subsequently be performed, if relevant, for the sample type in question.
Nakon toga po potrebi se može odrediti hlapljivi organski ugljik za predmetnu vrstu uzorka može.
ISO, Water quality — determination of total organic carbon.
ISO, Kvaliteta vode – utvrđivanje ukupnog organskog ugljika.
Schreurs W.
Schreurs, W.
Hydrobiological Bulletin 12, 137-142.
Hydrobiological Bulletin 12, 137. – 142.
% abiotic degradation
% abiotička razgradnja
ThODNH3
TPKNH3
ThOD
TPK
mgglucose
mgglukoze
mgsubstance
mgtvari
ThODNO2
TPKNO2
ThODNO3
TPKNO3
test substancemg
ispitivana tvarmg
0,10 g
0,10 g
If the test substance was administered using glass fibre filters or organic solvents, add to the blanks a filter or an equivalent volume solvent that has been evaporated.
Ako je ispitivana tvar bila dodana s pomoću filtara od staklenih vlakana ili organskih otapala, slijepim probama dodajte filtar ili istovjetnu količinu otapala koje je isparilo.
Prepare an extra replicate with test substance for the measurement of the pH value.
Pripremite dodatno ponovljeno višestruko određivanje s ispitivanom tvari za mjerenje pH-vrijednosti.
Seb
Sib
C.9, Biodegradation — Zahn-Wellens Test;
C.9. Biorazgradnja – Zahn-Wellensov test;
C.10, Simulation Test — Aerobic Sewage Treatment:
C.10. Biorazgradnja – Simulacijski testovi s aktivnim muljem:
Activated Sludge Units, B:
Jedinice s aktivnim muljem, B:
Biofilms
Biofilmovi;
C.11, Biodegradation — Activated sludge respiration inhibition
C.11. Aktivni mulj, test inhibicije disanja (oksidacija ugljika i amonijaka).
OECD (2009) Inherent Biodegradability:
OECD (2009.) Inherent Biodegradability:
Screening of chemicals for anaerobic biodegradation.
Screening of chemicals for anaerobic biodegradation.
Chemosphere 19, 1527-1550.
Chemosphere 19, 1527. – 1550.
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Mircobiology, 47, 850. – 857.
38, 84-89.
38, 84. – 89.
Proposed standard practice for the determination of the anaerobic biodegradation of organic chemicals.
Proposed standard practice for the determination of the anaerobic biodegradation of organic chemicals.
Battersby, N.S. and Wilson, V. (1988) Evaluation of a serum bottle technique for assessing the anaerobic biodegradability of organic chemicals under methanogenic conditions.
Battersby, N.S. and Wilson, V. (1988.) Evaluation of a serum bottle technique for assessing the anaerobic biodegradability of organic chemicals under methanogenic conditions.
Chemosphere, 17, 2441-2460.
Chemosphere, 17, 2441. – 2460.
US-EPA (1998) Fate, Transport and Transformation Test Guidelines OPPTS 835.3400 Anaerobic Biodegradability of Organic Chemicals.
US-EPA (1998.) Fate, Transport and Transformation Test Guidelines OPPTS 835.3400 Anaerobic Biodegradability of Organic Chemicals.