natgillin/translations-raw huggingface dataset:
US EPA — United States Environmental Protection Agency.
US EPA – United States Environmental Protection Agency.
SSI — Swedish Standards Institute.
SSI –Swedish Standards Institute.
Sims I., Whitehouse P. and Lacey R. (1999) The OECD Lemna Growth Inhibition Test.
Sims I., Whitehouse P. i Lacey R. (1999.) The OECD Lemna Growth Inhibition Test.
Environmental Research Laboratory — Duluth, Minnesota 55804
Environmental Research Laboratory – Duluth, Minnesota 55804
Lockhart W.
Lockhart, W.
Hydrobiologia, 118/119, 353 — 359.
Hydrobiologia, 118/119, 353 – 359.
Christensen, E.R.,, Nyholm, N. (1984):
Christensen, E.R.,, Nyholm, N. (1984.):
Sources of Lemna species
Izvori vrsta Lemna
United States
Sjedinjene Američke Države Tel.:
Hillman, W.S.
Hillman, W.
(I. Sims, P. Whitehouse and R. Lacey. (1999) The OECD Lemna Growth Inhibition Test. Development and Ring-testing of draft OECD Test Guideline. R&D Technical Report EMA 003. WRc plc — Environment Agency.)
teoretski primjerena konačna koncentracija bikarbonata (kojom se izbjegava znatna prilagodba pH-a) iznosi 15 mg/l, a ne 300 mg/l (I.Sims, P.Whitehouse i R.Lacev (1999). The OECD Lemna Growth Inhibition Test. Development and Ring-testing of draft OECD Test Guideline. R&D Technical Report EMA 003. WRc plc – Environment Agency.)
Na;N
Na; N
190;84
190; 84
22 °C ± 10 °C;
22 °C ± 10 °C;
70 % ± 25 %;
70 % ± 25 %;
350 ± 50 μE/m2/s.
350 ± 50 μE/m2/s.
For example, if an EC50 value is required it would be desirable to test at rates that produce a 20 to 80 % effect.
Na primjer, ako se traži vrijednost EC50, poželjno je provesti ispitivanje s dozama primjene koje proizvode 20-postotni do 80-postotni učinak.
The recommended number of test concentrations/rates to achieve this is at least five in a geometric series plus untreated control, and spaced by a factor not exceeding three.
Da bi se to postiglo, preporučuje se najmanje pet ispitnih koncentracija / doza primjene u geometrijskom nizu, plus netretirana kontrola, s faktorom ne većim od tri.
Soil Quality -- Determination of the Effects of Pollutants on Soil Flora — Part 1:
Soil Quality – Determination of the Effects of Pollutants on Soil Flora – Part 1:
Soil Quality -- Determination of the Effects of Pollutants on Soil Flora — Part 2:
Soil Quality – Determination of the Effects of Pollutants on Soil Flora – Part 2:
Background — Non-target Plant Testing;
Background – Non-target Plant Testing;
McKelvey, R.A., Wright, J.P., Honegger, J.L. and Warren, L.W.
McKelvey, R. A., Wright, J. P., Honegger, J. L. i Warren, L. W.
Boutin, C. and Harper, J.L.
Boutin, C. i Harper, J. L. (1991.) A comparative study of the population dynamics of five species of Veronica in natural habitats.
Guidance Document, Current Approaches in the Statistical Analysis of Ecotoxicity Data:
A Guidance to Application.
0,09-0,17 (4, 19)
0,09 – 0,17 (4, 19)
0-3 (2, 4, 14)
0 – 3 (2, 4, 14)
14-21 (100 %) (14)
14 – 21 (100 %) (14)
2,4-2,6 (14, 19)
2,4 – 2,6 (14, 19)
0,85 -1,2 (14, 19)
0,85 – 1,2 (14, 19)
0,06-0,08 (4, 14)
0,06 – 0,08 (4, 14)
14-21
14 – 21
25-61 (14, 29)
25 – 61 (14, 29)
10-20 (6, 21)
10 – 20 (6, 21)
10-20
10 – 20
10-20 (6, 10)
10 – 20 (6, 10)
23-28
23 – 28
14-18
14 – 18
0,9-1,6
0,9 – 1,6
7-37,5 (14, 30)
7 – 37,5 (14, 30)
0,45-2,28 (14, 29)
0,45 – 2,28 (14, 29)
0,5-0,7 (14, 19, 29)
0,5 – 0,7 (14, 19, 29)
0,52-0,6 (14, 30)
0,52 – 0,6 (14, 30)
10-20 (21)
10 – 20 (21)
10-20 (7, 21)
10 – 20 (7, 21)
4-5 (14, 30)
4 – 5 (14, 30)
14-28
14 – 28
1,53-2,2 (16, 19)
1,53 – 2,2 (16, 19)
0-10 (10, 19)
0 – 10 (10, 19)
5-8 (4, 14, 29)
5 – 8 (4, 14, 29)
0-2 (4, 29)
0 – 2 (4, 29)
1,8-2,5 (14)
1,8 – 2,5 (14)
3,6-7 (14, 29)
3,6 – 7 (14, 29)
2,1 -2,3 (14, 19)
2,1 – 2,3 (14, 19)
1,3-1,5 (4, 14, 19)
1,3 – 1,5 (4, 14, 19)
0,4-0,5 (4, 14, 19)
0,4 – 0,5 (4, 14, 19)
1,5-2 (14, 19, 29)
1,5 – 2 (14, 19, 29)
41 -56 (19, 29)
41 – 56 (19, 29)
0,8 — 1,5 (14, 19)
0,8 – 1,5 (14, 19)
7-9 (14, 19)
7 – 9 (14, 19)
POST (4, 22 — 26)
POST (4, 22 – 26)
0,5-0,6 (14, 19)
0,5 – 0,6 (14, 19)
3(19)
3 (19)
Pterophylla — Native Plants & Seeds
Pterophylla – Native Plants & Seeds
Boutin, C., Elmegaard, N., & Kjaer, C. 2004.
Boutin, C., Elmegaard, N. i Kjaer, C. 2004.
Breeze, V., Thomas, G., & Butler, R. 1992.
Breeze, V., Thomas, G. i Butler, R. 1992.
Brown, R.A., & Farmer, D. 1991.
Brown, R. A. i Farmer, D. 1991.
Fletcher, J.S., Johnson, F.L., & McFarlane, J.C. 1990.
Fletcher, J. S., Johnson, F. L. i McFarlane, J. C. 1990.
Fletcher, J.S., Pfleeger, T.G., Ratsch, H.C., & Hayes, R. 1996.
Fletcher, J. S., Pfleeger, T. G., Ratsch, H.C. i Hayes, R. 1996.
Seed Information Database (release 6.0, Oct 2004) Royal Botanic Gardens, Kew (www.rbgkew.org.uk/data/sid)
Seed Information Database (izdanje 6.0, listopad 2004.) Royal Botanic Gardens, Kew (www.rbgkew.org.uk/data/sid)
Grime, J.P., Mason, G., Curtis, A.V., Rodman, J., Band, S.R., Mowforth, M.A.G., Neal, A.M., & Shaw, S. 1981.
Grime, J. P., Mason, G., Curtis, A. V., Rodman, J., Band, S. R., Mowforth, M. A. G., Neal, A. M. i Shaw, S. 1981.
Grime, J.P., Hodgson, J.G., & Hunt, R. 1988.
Grime, J. P., Hodgson, J. G. i Hunt, R. 1988.
Marrs, R.H., Frost, A.J., Plant, R.A., & Lunnis, P. 1993.
Marrs, R. H., Frost, A. J., Plant, R. A. i Lunnis, P. 1993.
USEPA.
US EPA.
Webster, R.H.
Webster, R. H. 1979.
White, A. L. & Boutin, C. (National Wildlife Research Centre, Environment Canada).
White, A. L. i Boutin, C. (National Wildlife Research Centre, Environment Canada).
Zwerger, P. & Pestemer, W.
Zwerger, P. i Pestemer, W.
350 ± 50 ppm;
350 ± 50 ppm;
The vehicle is sprayed on or mixed with a small amount, for example 2,5 g, of fine quartz sand.
Nosač se poprska po maloj količini, npr. 2,5 g, finog kremenog pijeska ili se pomiješa s njom.
ISO (International Organization for Standardization) (1993).
ISO (International Organization for Standardization) (1993.) Soil Quality – Determination of dry matter and water content on a mass basis – Gravimetric method, No.
Didden, W.A.M.
Didden, W.
UWSF — Z. Umweltchem.
UWSF – Z. Umweltchem.
ISO (International Organization for Standardization) (1994).
ISO (International Organization for Standardization) (1994.) Soil Quality – Determination of pH, No.
Bell, A.W.
Bell, A. W.
Dunnett, C.W., (1955).
Dunnett, C. W.
Holm, S., (1979):
Holm, S. (1979.):
Jonckheere, A. R. (1954);
Jonckheere, A. R. (1954.);
Terpstra, T. J. (1952);
Terpstra, T. J. (1952.);
Shirley, E. A. (1979);
Shirley, E. A. (1979.);
2nd edition.
izdanje.
Enchytraeus crypticus (Westheide & Graefe 1992):
Enchytraeus crypticus (Westheide i Graefe, 1992.):
Enchytraeus buchholzi (Vejdovsky 1879):
Enchytraeus buchholzi (Vejdovsky, 1879.):
Enchytraeus bulbosus (Nielsen & Christensen 1963):
Enchytraeus bulbosus (Nielsen i Christensen, 1963.):
Overview of the statistical assessment of data (NOEC determination) Dunnett's Test
Pregled statističke procjene podataka (određivanje NOEC-a)
Yes
Yes Da Da Da
Parametric Tests
Početak
log Kow;
log Kow,
(ISO (International Organization for Standardization) (1994). Soil Quality — Determination of pH, No. 10390. ISO, Geneve.
(ISO (International Organization for Standardization) (1994.) Soil Quality – Determination of pH, No. 10390. ISO, Ženeva.
Hund-Rinke, K, Römbke, J., Riepert, F. & Achazi R. (2000):
Hund-Rinke, K, Römbke, J., Riepert, F. i Achazi, R. (2000.):
ISO (International Organization for Standardization) (1992).
ISO (International Organization for Standardization) (1992.) Soil Quality – Determination of water retention characteristics – Laboratory methods, No.
Römbke, J. and Th.
Römbke, J. i Moser, Th.
Environ.
Sci.
Van Gestel, C.A.M., W.A. van Dis, E.M. van Breemen, P.M. Sparenburg (1988).
C. A. M. Van Gestel, W.
s.d.
s. d.
discussion of results, including any deviations from the procedures in this test method and discuss any deviations in the test results due to interferences and errors from what would be expected;
rasprava o rezultatima, uključujući sva odstupanja od postupaka navedenih u ovoj ispitnoj metodi, te rasprava o svim odstupanjima rezultata ispitivanja od očekivanih rezultata, a do kojih je došlo zbog interferencija i pogrešaka,
International Organisation for Standardisation (2003) ISO 13 641-1 Water Quality — Determination of inhibition of gas production of anaerobic bacteria — Part 1:
International Organisation for Standardisation (2003) ISO 13 641-1 Water Quality – Determination of inhibition of gas production of anaerobic bacteria – Part 1:
International Organisation for Standardisation (2003) ISO 13 641-2 Water Quality — Determination of inhibition of gas production of anaerobic bacteria — Part 2:
International Organisation for Standardisation (2003) ISO 13 641-2 Water Quality – Determination of inhibition of gas production of anaerobic bacteria – Part 2:
ISO (2000) Ring test of ISO 13 641-1 and ISO 13 641-2.
ISO (2000.) Ring test of ISO 13 641-1 and ISO 13 641-2.
HMSO (1986) Determination of the inhibitory effects of chemicals and waste waters on the anaerobic digestion of sewage sludge.
HMSO (1986.) Determination of the inhibitory effects of chemicals and waste waters on the anaerobic digestion of sewage sludge.
International Organization for Standardization (1995) ISO 10 634 Water Quality — Guidance for the preparation and treatment of poorly water-soluble organic compounds for the subsequent evaluation of their biodegradability in an aqueous medium.
Međunarodna organizacija za normizaciju (1995.) ISO 10 634 Water Quality – Guidance for the preparation and treatment of poorly water-soluble organic compounds for the subsequent evaluation of their biodegradability in an aqueous medium.
International Organization for Standardization (1997) ISO 11 923 Water Quality — Determination of suspended solids by filtration through glass-fibre filters.
Međunarodna organizacija za normizaciju (1997.) ISO 11 923 Water Quality – Determination of suspended solids by filtration through glass-fibre filters.
chemical identification data (common name, chemical name, structural formula, CAS number, etc.) including purity and analytical method for quantification of test chemical;
podaci za identifikaciju kemikalije (opći naziv, kemijski naziv, strukturna formula, CAS broj itd.), uključujući čistoću i analitičku metodu kvantifikacije ispitivane kemikalije;
source of the test chemical, identity and concentration of any solvent used.
izvor ispitivane kemikalije, identitet i koncentracija upotrijebljenog otapala,
Part I — IV.
Part I. – IV.
OECD (1992a).
OECD (1992.a).
ASTM International (2000).
ASTM International (2000.).
Phipps, G.L., Ankley, G.T., Benoit, D.A. and Mattson, V.R.
Phipps, G. L., Ankley, G. T., Benoit, D. A. i Mattson, V. R. (1993.) Use of the aquatic Oligochaete Lumbriculus variegatus for assessing the toxicity and bioaccumulation of sediment-associated contaminants.
U.S. EPA (2000).
US EPA (2000.).
Hill, I.R., Matthiessen, P., Heimbach, F. (eds), 1993, Guidance document on Sediment Toxicity Tests and Bioassays for freshwater and Marine Environments, From the SETAC-Europe Workshop On Sediment Toxicity Assessment, 8-10 November 1993, Renesse (NL).
Hill, I. R., Matthiessen, P., Heimbach, F. (ur.), 1993., Guidance document on Sediment Toxicity Tests and Bioassays for freshwater and Marine Environments, From the SETAC-Europe Workshop On Sediment Toxicity Assessment, 8. – 10. studenoga 1993., Renesse (NL).
Egeler, Ph., Meller, M., Schallnaß, H.J.
IZVOR:
Baily H.C., & Liu D.H.W.
Baily, H. C. i Liu, D. H. W.
Meyer J.S., Boese C.J.
Meyer, J. S., Boese, C. J. i Collyard, S. A. (2002.) Whole-body accumulation of copper predicts acute toxicity to an aquatic oligochaete (Lumbriculus variegatus) as pH and calcium are varied.
Schubauer-Berigan M.K., Dierkes J.R., Monson P.D.
Schubauer-Berigan, M. K., Dierkes, J. R., Monson, P. D. i Ankley, G. T. (1993.) pH-dependent toxicity of cadmium, copper, nickel, lead and zinc to Ceriodaphnia dubia, Pimephales promelas, Hyalella azteca and Lumbriculus variegatus.
Ingersoll, C.G., Ankley, G.T., Benoit D.A., Brunson, E.L., Burton, G.A., Dwyer, F.J., Hoke, R.A., Landrum, P. F., Norberg-King, T. J. and Winger, P.V.
Ingersoll, C.G., Ankley, G.T., Benoit D.A., Brunson, E.L., Burton, G.A., Dwyer, F.J., Hoke, R.A., Landrum, P. F., Norberg-King, T. J. i Winger, P.V.
Kukkonen, J. and Landrum, P.F.
Kukkonen, J. i Landrum, P. F. (1994.) Toxicokinetics and toxicity of sediment-associated Pyrene to Lumbriculus variegatus (Oligochaeta).
Ingersoll, C.G., Brunson, E.L., Wang N., Dwyer, F.J., Ankley, G.T., Mount D.R., Huckins J., Petty.
Ingersoll, C. G., Brunson, E. L., Wang N., Dwyer, F. J., Ankley, G. T., Mount D. R., Huckins J., Petty.
Rodriguez, P. & Reynoldson, T.B.
Rodriguez, P. i Reynoldson, T. B. (1999.) Laboratory methods and criteria for sediment bioassessment.
Liebig, M., Egeler, Ph. Oehlmann, J., & Knacker, Th.
Liebig, M., Egeler, Ph. Oehlmann, J. i Knacker, Th.
Bioaccumulation of 14C-17α-ethinylestradiol by the oligochaete Lumbriculus variegatus in artificial sediment.
Bioaccumulation of14C-17α-ethinylestradiol by the oligochaete Lumbriculus variegatus in artificial sediment.
Oetken, M., K.-U.
Oetken, M., Ludwichowski, K.-U.
OECD (1992c).
OECD (1992.c).
Egeler, Ph., Römbke, J., Meller, M., Knacker, Th., Franke, C., Studinger, G. & Nagel, R. (1997).
Egeler, Ph., Römbke, J., Meller, M., Knacker, Th., Franke, C., Studinger, G. & Nagel, R. (1997.).
Egeler, Ph., Römbke, J., Knacker, Th., Franke, C. & Studinger, G. (1999).
Egeler, Ph., Römbke, J., Knacker, Th., Franke, C. & Studinger, G. (1999.).
Environment Canada (1995).
Environment Canada (1995.).
Landrum, P.F.
Landrum, P. F. (1989.) Bioavailability and toxicokinetics of polycyclic aromatic hydrocarbons sorbed to sediments for the amphipod Pontoporeia hoyi.
Biometrics 28, 519 531.
Biometrics 28, 519 – 531.
OECD (1992).
OECD (1992.) Guidelines for Testing of Chemicals No.
Development — Ecotoxicology
Development – Ecotoxicology
The reproductive output of the mites exposed to the test chemical is compared to that of the controls in order to determine the ECx (e.g. EC10, EC50) or the no observed effect concentration (NOEC) (see Appendix 1 for definitions), depending on the experimental design (see paragraph 29).
Reprodukcijska uspješnost grinja izloženih ispitivanoj kemikaliji uspoređuje se s onom u kontrolama kako bi se odredila vrijednost ECx (npr. EC10, EC50) ili najviša koncentracija bez vidljivog učinka (NOEC) (vidjeti dodatak 1. za definicije), ovisno o planu pokusa (vidjeti stavak 29.).
An overview of the test schedule is given in Appendix 8.
U Dodatku 8. naveden je pregled vremenskog rasporeda ispitivanja.
The vehicle is sprayed on or mixed with a small amount, for example 10 g, of fine quartz sand.
Nosač se poprska po maloj količini, npr. 10 g, finog kremenog pijeska ili se pomiješa s njom.
In specific cases (e.g. when ageing is considered to be a determining factor), the time between preparation of the final test substrate and the addition of the mites can be prolonged (for details of such ageing, see (18)).
U posebnim slučajevima (npr. kada se odležavanje smatra odlučujućim faktorom), vrijeme između pripreme konačnog ispitnog supstrata i dodavanja grinja može se produljiti (za detalje o takvom odležavanju vidi (18)).
However, in such cases a scientific justification must be provided.
Međutim, u tim se slučajevima mora navesti znanstveno obrazloženje.
Appropriate statistical methods should be used (according to OECD Document 54 on the Current Approaches in the Statistical Analysis of Ecotoxicity Data: A Guidance to Application).
Potrebno je primijeniti odgovarajuće statističke metode (u skladu s OECD-ovim Dokumentom 54. pod naslovom ‚Current Approaches in the Statistical Analysis of Ecotoxicity Data: A Guidance to Application’).
Multiple comparisons (e.g. Dunnett's t-test) or step-down trend tests (e.g. Williams' test in case of a monotonous dose-response relationship) can be used to calculate whether there are significant differences (p ≤ 0,05) between the controls and the various test item concentrations (selection of the recommended test according to OECD Document 54 on the Current Approaches in the Statistical Analysis of Ecotoxicity Data: a Guidance to Application).
Kako bi se izračunalo postoje li značajne razlike (p ≤ 0,05) između kontrola i različitih koncentracija ispitivane tvari, mogu se primijeniti testovi višestruke usporedbe (npr. Dunnettov t-test) ili testovi trenda postupnim snižavanjem (npr. Williamsov test u slučaju monotonog odnosa između doze i odgovora) (preporučeni se test bira u skladu s OECD-ovim Dokumentom 54. pod naslovom ‚Current Approaches in the Statistical Analysis of Ecotoxicity Data: a Guidance to Application’).
Casanueva, M.E.
Casanueva, M. E. (1993.) Phylogenetic studies of the free-living and arthropod associated Laelapidae (Acari: Mesostigmata).
JSS — Journal of Soils and Sediments 3, 73-77.
JSS – Journal of Soils and Sediments 3, 73 – 77.
Laboratory studies on the popualation development of Hypoaspis aculeifer (Acari: Parasitiformes).
Laboratory studies on the population development of Hypoaspis aculeifer (Acari: Parasitiformes).
Academia Prague & SPD Academic Publishing bv, The Hague, Vol. 2, 487-492
Academia Prague & SPD Academic Publishing bv, The Hague, Vol. 2, 487 – 492
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EPPO (2003.):
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OECD (2006c).
OECD (2006.c).
ENV/JM/MONO(2006)18
ENV/JM/MONO(2006.)18
Therefore the following procedure is proposed (24) (25):
Stoga se predlaže sljedeći postupak (24) (25):
Apparatus:
Oprema:
Tullgren funnel or comparable methods like e.g. McFadyen (heating from above, sample is put over a funnel)
Tullgrenov lijevak ili usporedive metode kao što je npr. McFadyenova metoda (grijanje odozgo, uzorak se postavlja na lijevak)
Heating regime:
Režim grijanja:
25 °C for 12 h, 35 °C for 12 h, 45 °C for 24 hours (in total 48 h).
25 °C tijekom 12 sati, 35 °C tijekom 12 sati, 45 °C tijekom 24 sata (ukupno 48 sati).
The temperature should be measured in the substrate.
Temperaturu je potrebno mjeriti u supstratu.
Fixation liquid:
Tekućina za fiksiranje:
(MITOX), 23 January 2007
F. Faraji, (MITOX), 23. siječnja 2007.
Tierwelt Deutschlands 59, 2nd revised edition:
Tierwelt Deutschlands 59, 2. revidirano izdanje:
For that reason the cuticula of the prey is pierced with the chelicers and a secretion for the extra intestinal digestion is emitted into the prey.
U tu svrhu kliještima probijaju kutikulu plijena i u plijen ispuštaju izlučevinu koja omogućuje izvanželučanu probavu.
The food mash can then be sucked by the mite.
Grinja potom može usisati takvu kašastu hranu.
OECD (2006a).
OECD (2006.a).
OECD Environmental Health and Safety Publications Series on Testing and Assessment No.60, ENV/JM/MONO(2006)27.
OECD Environmental Health and Safety Publications Series on Testing and Assessment No.60, ENV/JM/MONO(2006.)27.
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OECD (2006.b).
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Report of the Initial Work Towards the Validation of the 21-Day Fish Screening Assay for the Detection of Endocrine active Substances (Phase 1 B).
OECD Environmental Health and Safety Publications Series on Testing and Assessment No.61, ENV/JM/MONO(2006)29.
OECD Environmental Health and Safety Publications Series on Testing and Assessment No.61, ENV/JM/MONO(2006.)29.
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1699 – 1708.
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OECD (2000.) Guidance Document on Aquatic Toxicity Testing of Difficult Substances and Mixtures.
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OECD environmental Health and Safety Publications Series on Testing and Assessment No. 54.
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OECD (2012.) OECD Conceptual Framework for Testing and Assessment of Endocrine Disrupters (revised).
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25 ± 2 °C
25 ± 2 °C
26 ± 2 °C
26 ± 2 °C
21 d
21 dan
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Can J Zool 52:1031-1038.
Can J Zool 52: 1031.–1038.
Dunnett test on nested ANOVA No
Pretvorba radistabilizacije varijanci?
Yes Dunn or Mann-Whitney test on rep means
Dunn ili Mann-Whitneyjev test na s rednjoj vrijednosti ponavljanja
Tamhane-Dunnett test
Varijance nejednake
variance stabilising transformation
<=3 ponav. po konc. Dunnov test Da Ne
Variances unequal
Tamhane-Dunnettov test
method and frequency of preparation of dilutions.
način i učestalost priprema razrjeđivanja.
Test chemical information includes actual and nominal concentrations of the test chemical, and in some cases, non-parent chemical, as appropriate.
Informacije o ispitivanoj kemikaliji uključuju stvarne i nazivne koncentracije ispitivane kemikalije, a u nekim slučajevima nepolaznu kemikaliju ako je to prikladno.
Statistical analyses of the data should preferably follow procedures described in the document Current Approaches in the Statistical Analysis of Ecotoxicity Data:
Statističke analize podataka trebale bi po mogućnosti poštovati postupke opisane u dokumentu Sadašnji pristupi u statističkoj analizi podataka o ekotoksičnosti:
After stage 60, tadpoles show a reduction in size and weight due to tissue resorption and reduction of absolute water content.
Nakon 60. stadija punoglavci pokazuju smanjenje veličine i težine zbog resorpcije tkiva te smanjenje apsolutnog sadržaja vode.
Thus, measurements of wet weight and SVL cannot appropriately be used in statistical analyses for differences in growth rates.
Dakle, mjerenja mokre mase i SVL-a ne mogu se primjereno upotrebljavati u statističkim analizama razlika u brzinama rasta.
Therefore, wet weight and length data from organisms > NF60 should be censored and cannot be used in analyses of replicate means or replicate medians.
Stoga, podatke o mokroj masi i duljini organizama > NF60 potrebno je kritički osuditi i te ih nije moguće upotrebljavati u analizama ponavljanja prosjeka ili ponavljanja srednje vrijednosti.
Two different approaches could be used to analyse these growth-related parameters.
Mogu se upotrebljavati dva različita pristupa za analizu tih parametara povezanih s rastom.
OECD (2004) Report of the Validation of the Amphibian Metamorphosis Assay for the detection of thyroid active substances:
OECD (2004.) Report of the Validation of the Amphibian Metamorphosis Assay for the detection of thyroid active substances:
Phase 1 — Optimisation of the Test Protocol.
Phase 1 – Optimisation of the Test Protocol.