natgillin/translations-raw huggingface dataset:
The temperature in the test vessels should be 24 ± 2 °C. The pH of the control medium should not increase by more than 1,5 units during the test.
94, ENV/JM/MONO(2008)21.
US EPA — United States Environmental Protection Agency.
Journal of Health Science 50: 301-308.
AFNOR — Association Française de Normalisation.
23(3): 774-81.
SSI — Swedish Standards Institute.
OECD (2000).
Water quality — Determination of growth inhibition (7-d) Lemna minor, duckweed.
Guidance Document on Aquatic Toxicity Testing of Difficult Substances and Mixtures.
Environment Canada.
Paris.
Sims I., Whitehouse P. and Lacey R. (1999) The OECD Lemna Growth Inhibition Test.
OECD environmental Health and Safety Publications Series on Testing and Assessment No. 54.
WRc plc — Environment Agency.
OECD (2012).
International Organisation for Standardisation.
OECD Conceptual Framework for Testing and Assessment of Endocrine Disrupters (revised).
Lockhart W.
Täiskasvanud kala ligikaudne märgkaal (g)
Huebert, D.B. and Shay J.M.
Tamhane-Dunnetti test
Bruce R.D. and Versteeg D.J.
dispersiooni stabiliseeriv teisendus?
OECD.
Tamhane'i-Dunnetti test
Brain P. and Cousens R. (1989).
0–4
Sources of Lemna species
5–7
Toronto, Ontario, Canada, M5S 3 B2
8–10
United States
11–14
SWEDEN
15–21
Germany
Söödaga manustamise teel saavutatud kokkupuute kohta on tehtud eeltöid, kuid sellist kokkupuuteviisi tavaliselt ei kasutata.
Hillman, W.S.
lahjenduste valmistamise meetod ja sagedus.
Landolt, E. (1986).
Uuritavat kemikaali käsitlev teave hõlmab selle tegelikke ja nimikontsentratsioone ning mõnel juhul, kui see on asjakohane, ka teavet süsteemis tekkivate ühendite kontsentratsioonide kohta.
Björndahl, G. (1982).
Andmete statistiline analüüs peaks eelistatavalt toimuma vastavalt korrale, mida on kirjeldatud dokumendis „Current Approaches in the Statistical Analysis of Ecotoxicity Data:
Wang, W.
Pärast 60. arengustaadiumi hakkab kulleste suurus ja mass vähenema kudede resorptsiooni ja absoluutse veesisalduse vähenemise tõttu.
Environmental Research, 52:7-22.
Märgkaalu ja ninamiku-päraku vahemaa mõõtmisi ei sobi seetõttu enam kasutada kasvukiiruste statistilises analüüsis.
The material is then shaken vigorously in clean water, followed by immersion in a 0,5 % (v/v) sodium hypochlorite solution for between 30 seconds and 5 minutes.
Selliste kasvuga seotud näitajate analüüsil võib kasutada kahte erinevat lähenemisviisi.
The plant material is then rinsed with sterile water and transferred, as a number of batches, into culture vessels containing fresh growth medium.
Phase 1 – Optimisation of the Test Protocol.
(mg/ߦl)
Phase 2 – Multi-chemical Interlaboratory Study.
The pH is adjusted to 6,5 ± 0,2 with either 0,1 or 1 mol HCl or NaOH, and the volume adjusted to one litre with deionised water.
ASTM (2004) Standard Guide for Conducting the Frog Embryo Teratogenesis Assay – Xenopus (FETAX).
AAP growth medium
RIDA
Stock solutions are prepared in sterile distilled or deionised water.
Ninamiku-pärakuava vahemaa (mm)
Under these conditions the stock solutions will have a shelf life of at least 6 - 8 weeks.
Ninamiku-pärakuava vahemaa
The 20 ml of each nutrient stock solution is added to approximately 850 ml deionised water to produce the growth medium.
iga aine või segu, mida uuritakse käesoleva katsemeetodi abil.
The pH is adjusted to 7,5 ± 0,1 with either 0,1 or 1 mol HCl or NaOH, and the volume adjusted to one litre with deionised water.
Tuleb kasutada vastavaid statistilisi meetodeid vastavalt OECD dokumendile 54 „Current Approaches in the Statistical Analysis of Ecotoxicity Data:
Growth medium intended for testing should be prepared 1-2 days before use to allow the pH to stabilise.
A Guidance to Application” (Ökotoksilisuse andmete statistilise analüüsi kaasaegsed meetodid.
(I. Sims, P. Whitehouse and R. Lacey.
Üldiselt otsitakse andmetest uuritava kemikaali negatiivset mõju võrreldes kontrollrühmaga, kasutades selleks ühepoolse hüpoteesi testimist p ≤ 0,05 juures.
(1999) The OECD Lemna Growth Inhibition Test.
ISO (1999) Soil Quality – Effects of soil pollutants on Collembola (Folsomia candida):
WRc plc — Environment Agency.)
Pärast 12 tundi temperatuuril 40 °C on väljavõtmine lõppenud.
(g/ߦl) [1]
täielikult arenenud ja elusate sääskede hulgas peaks sooline jaotumine (emas- ja isassääskede suhtarv) kontrollnõus olema vähemalt 0,4, kuid mitte üle 0,6;
(mg/ߦl) [1]
igas paljunduspuuris peaks 1. põlvkonna kontrollkatses olema vähemalt 0,6 munanööri iga sellesse puuri viidud emassääse kohta;
190;84
kokkupuuteaja lõpus tuleks mõlema põlvkonna puhul mõõta igas nõus pH ja lahustunud hapniku kontsentratsioon.
For crop protection products, the physical/chemical properties and use pattern of the test chemical, its maximum concentration or application rate, the number of applications per season and/or the persistence of the test chemical need to be considered.
Kui on tõendatud, et uuritav kemikaal ei adsorbeeru filtritele, võib sobida ka filtrimine.
The number and spacing of the concentrations or rates should be sufficient to generate a reliable dose-response relationship and regression equation and give an estimate of the ECx. or ERx.
J. Sanit.
A dose-response relationship is established in terms of a regression equation.
103–117.
Different models can be used:
Biometrics 28:
International Organisation of Standards.
Vogt, C., Belz, D., Galluba, S., Nowak, C., Oetken, M. and J. Oehlmann (2007), Effects of cadmium and tributyltin on development and reproduction of the non-biting midge Chironomus riparius (Diptera) – baseline experiments for future multi-generation studies, J. Environ.
Soil Quality -- Determination of the Effects of Pollutants on Soil Flora — Part 2:
Ülevaade asjakohastest liigispetsiifilistest katsetingimustest iga valideeritud liigi (jaapani riisikala, ogalik ja vöötdaanio) jaoks on esitatud 2. liites.
Background — Non-target Plant Testing;
asjakohased füüsikalis-keemilised omadused, kemikaali identifitseerimisandmed, sh andmed uuritava kemikaali puhtuse kohta ja kvantitatiivse sisalduse mõõtmiseks kasutatud analüütilise meetodi kohta.
AFNOR, X31-201.
30 % – 70 %
Boutin, C., Freemark, K.E. and Keddy, C.J.
(Võib kasutada ka muid meetodeid, kui homogeenimine toimub jää peal ja saadakse homogeenne mass.)
Forster, R., Heimbach, U., Kula, C., and Zwerger, P. (1997).
Oluline märkus:
Effects of Plant Protection Products on Non-Target Organisms — A contribution to the Discussion of Risk Assessment and Risk Mitigation for Terrestrial Non-Target Organisms (Flora and Fauna).
Neeldumine mõõdetakse lainepikkusel 450 nm (nt Molecular Devices Thermomax'i plaadilugejaga).
Soil Texture Classification (US and FAO systems):
lisada dest. vett 100 ml-ni
Beall, M.L., Jr. and Nash, R.G.
lahustunud orgaanilise süsiniku sisaldus;
Beetsman, G.D., Kenney, D.R. and Chesters, G. (1969).
selleks aereeritakse seda puhta suruõhuga umbes 20 minutit.
Boutin, C., and Rogers, C.A.
mg THT
Patterns of sensitivity of plant species to various herbicides — An analysis with two databases.
mg KHT
Boutin, C. and Harper, J.L.
Suure kloriidisisaldusega või suure mahuga proove võib selle meetodiga analüüsida siis, kui hoitakse ära kloriidi kogunemine oksüdatsiooninõusse.
Guidance Document, Current Approaches in the Statistical Analysis of Ecotoxicity Data:
ISO, Water quality – determination of total organic carbon.
Hatzios, K.K. and Penner, D. (1985).
mg lah. org.
Hamill, P.B., Marriage, P.B. and G. Friesen.
C/l
Frans, R.E. and Talbert, R.E.
abiootilise lagunemise %
Bruce, R.D. and Versteeg, D. J.(1992).
THTNH3
Solanum lycopersicon
mgglükoosi
0,09-0,17 (4, 19)
mgainet
14-21 (100 %) (14)
THTNO3
2,4-2,6 (14, 19)
uuritav ainemg
0,85 -1,2 (14, 19)
Kui uuritav aine lisati klaaskiudfiltri või orgaanilise lahusti kasutamisega, lisage tühikatsenõudesse filter või samasugune kogus lahustit, mis aurustati.
0,06-0,08 (4, 14)
Valmistage lisaks ette eraldi paralleelkatsed uuritava ainega pH väärtuse mõõtmiseks.
14-21
kus:
25-61 (14, 29)
12 süsiniku suhteline aatommass;
10-20 (6, 21)
kus:
10-20 (6, 10)
V gaasi ruumala (m3);
23-28
R universaalne gaasikonstant [8,314 J/(mol K)]
14-18
C net
0,9-1,6
S ib
7-37,5 (14, 30)
S eb
0,45-2,28 (14, 29)
C.9, Biodegradatsioon – Zahni-Wellensi test;
0,5-0,7 (14, 19, 29)
C.10, Reovee aeroobse töötlemise simulatsioonikatse:
0,52-0,6 (14, 30)
aktiivmuda, B:
1,53-2,2 (16, 19)
Δp (võrdlus)
5-8 (4, 14, 29)
9 (Environmental Behaviour of Agrochemicals – T.R. Roberts and P.C. Kearney, Eds.).
1,8-2,5 (14)
A review.
2,1 -2,3 (14, 19)
In Unser Boden – 70 Jahre Agrarforschung der BASF AG, 225-236.
41 -56 (19, 29)
European Standard, EN 335 – Part 1:
0,8 — 1,5 (14, 19)
Durability of wood and wood-based products – Definition of use classes – Part1:
POST (4, 22 — 26)
American Society for Testing and Materials Standards, ASTM D 1193-77 Type II – 1983.
Breeze, V., Thomas, G., & Butler, R. 1992.
Chemosphere 9: 683.
Buhler, D.D.
Hansch, C., esimees;
Clay, P.A.
McGraw-Hill, New York (1982).
Fletcher, J.S., Johnson, F.L., & McFarlane, J.C. 1990.
Sellist muudetud söödet tuleks üksikasjalikult kirjeldada ja selle kasutamist põhjendada (3, 4).
Flynn, S., Turner, R.M., and Dickie, J.B.
Bruce, R. D., ja Versteeg, D. J. (1992).
Kjaer, C. 1994.
Chem.
Klingaman, T.E., King, C.A., & Oliver, L.R.
11: 1485–1494.
Marrs, R.H., Williams, C.T., Frost, A.J., & Plant, R.A.
Toxic.
Marrs, R.H., Frost, A.J., & Plant, R.A.
Assess.
Marrs, R.H., Frost, A.J., Plant, R.A., & Lunnis, P. 1993.
1:
Marshall, E.J.P.
ErCx (tallusjate võsude arv), ErCx (tallusjate võsude üldpindala, kuivmass või märgmass), EyCx (tallusjate võsude arv) ja EyCx (tallusjate võsude üldpindala, kuivmass või märgmass).
McKelvey, R.A., Wright, J.P., & Honegger, J.L.
Statistilised meetodid
Morton, S.
ASTM International (2003).
USDA, NRCS.
Swedish Standards Institute (SIS) (1995).
USEPA.
Considerations in the assessment of toxicity using duckweeds.
Webster, R.H.
Environ.
Zwerger, P. & Pestemer, W.
Nyholm, N., Sørensen, P. S., Kusk, K. O., ja Christensen, E. R. (1992).
350 ± 50 ppm;
OECD (2006).
The vehicle is sprayed on or mixed with a small amount, for example 2,5 g, of fine quartz sand.
National Effluent Toxicity Assessment Center Technical Report 05–88.
Alternatively, a multiple U-test, e.g. the Bonferroni-U-test according to Holm (29), or when these data exhibit heteroscedasticity but are otherwise consistent with a underlying monotone dose-response, an other non-parametric test [e.g. Jonckheere-Terpstra (30) (31) or Shirley (32) (33)] can be applied and would generally be preferred to unequal-variance t-tests. (see also the scheme in Appendix 7).
Biometrics 20: 482–491.
Römbke, J. (1989).
USA Keskkonnakaitseamet (1996).
Entwicklung eines Reproduktionstests an Bodenorganismen — Enchytraeen.
XP T 90–337:
Römbke, J. and Moser, T. (1999).
+1 919 515 7572
Westheide, W. and Bethge-Beilfuss, D. (1991).
+46 8 674 7240 Faks:
ISO (International Organization for Standardization) (1993).
EDTA · 2H2O
Soil Quality — Effects of pollutants on earthworms (Eisenia fetida).
K2HPO4 · 3H2O
Römbke, J. (1995).
Environmental Assessment Technical Assistance Document 4.07, Seedling Growth, 14 lk, USA Toidu- ja Ravimiamet, Washington, DC.
Bodenorganismen — Prüfungskategorien der Forschung.
PÄRAST (2, 4)
UWSF — Z. Umweltchem.
5 (29)
Römbke, J. and Federschmidt, A. (1995).
ENNE ja PÄRAST (31)
Römbke, J., Riepert, F. & Achazi R. (2000):
ENNE ja PÄRAST (6)
Soil Quality — Determination of pH, No. 10390.
ENNE ja PÄRAST (28, 31, 34)
Nielsen, C.O. and Christensen, B. (1959).
ENNE ja PÄRAST (6, 10, 28, 31)
Bouguenec, V. and Giani, N. (1987).
ENNE ja PÄRAST (28, 31)
Korinkova, J. and Sigmund, J. (1968).
ENNE ja PÄRAST (18, 25, 31)
Finney, D.J.
ENNE (31)
Dunnett, C.W., (1955).
69: 223–235.
Dunnett, C.W., (1964) New tables for multiple comparisons with a control.
Toim.
Hoeven, N. van der, (1998).
Esser, G., ja Overdieck, D., lk 497–508.
355-361
John Wiley and Sons, Chichester, lk 73–94.
Holm, S., (1979):
Finney, D. J. (1971).
Jonckheere, A. R. (1954);
Biometrics 20:
Terpstra, T. J. (1952);
H. Freeman and Company, New York.
Shirley, E. A. (1979);
25: 25–32.
Sokal, R.R. and F.J.
Posthuma, L., Baerselmann, R., Van Veen, R. P. M., ja Dirven-Van Breemen, E. M. (1997).
2nd edition.
Bundesamt Land-Forstwirtsch., Berlin-Dahlem, 320, lk 50–82.
Christensen, E.R., (1984).
11268-2.
Van Ewijk, P.H. and J.A.
Rahvusvaheline Standardiorganisatsioon, Genf.
After shaking, the suspension is left to settle for at least 2 hours but not for longer than 24 hours.
SETAC Press, 456 lk.
The pH of the liquid phase is then measured using a pH-meter, that has been calibrated before each measurement using an appropriate series of buffer solutions (e.g. pH 4,0 and 7,0).
Pedobiologia 32: 367–371.
Enchytraeus crypticus (Westheide & Graefe 1992):
Evans, M. R., ja Painter, H. A. Brixham Environmental Laboratory, AstraZeneca UK Ltd., Brixham TQ5 8BA, Ühendkuningriik
Enchytraeus buchholzi (Vejdovsky 1879):
H3PO4 kasutamise korral tuleb kasutada eelkõige pH mõõtmiseks täiendavalt paari lisapudelit, kuhu ei lisata H3PO4.
Enchytraeus bulbosus (Nielsen & Christensen 1963):
VIIDE:
the duration of the reproduction test can (but need not) be shorter, i.e. four instead of six weeks; however, the duration of the Range-Finding Test should not be changed;
ASTM International 2004 Annual Book of Standards, Vol.
Posthuma, L., Baerselmann, R., Van Veen, R.P.M. and Dirven-Van Breemen, E.M.
Biotechnology;
Phillips, C.T., Checkai, R.T. and Kuperman, R.G.
Pesticides.
Transform data Yes Yes Yes
Phipps, G. L., Ankley, G. T., Benoit, D. A., ja Mattson, V. R. (1993).
Yes No
Toim.
At least four replicates per treatment?
Streloke, M., ja Köpp, H. Berliin, 1995.
No success
Egeler, Ph., Meller, M., Schallnaß, H. J., ja Gilberg, D. (2005).
log Kow;
West, C. W., Mattson, V. R., Leonard, E. N., Phipps, G. L., ja Ankley, G. T. (1993).
Since a single summary statistic cannot be prescribed for the test, this test method makes provision for the determination of the NOEC and the ECx.
Comparison of the relative sensitivity of three benthic invertebrates to copper-contaminated sediments from the Keweenaw Waterway.
Jaenicke, J. (1982).
Kukkonen, J., ja Landrum, P. F. (1994).
Oien, N. and J. Stenerson (1984).
Brunson, E. L., Canfield, T. J., Ingersoll, C. J., ja Kemble, N. E. (1998).
Kula, C. (1996).
20: 2000–2007.
Development of a test method on sublethal effects of pesticides on the earthworm species Eisenia fetida/Eisenia andrei — comparison of two ringtests.
FKZ 360 12 001, märts 2000.
SETAC (1998).
Brinkhurst, R. O. (1971).
(ISO (International Organization for Standardization) (1994).
Finney, D. J. (1978).
Soil Quality — Determination of pH, No. 10390.
parandus:
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;
väljaanne.)
Appl.
Park, C.L.
Battersby NS and Wilson V (1988).
ELT L 276, 20.10.2010, lk 33.
International Organization for Standardization (1997) ISO 11 923 Water Quality — Determination of suspended solids by filtration through glass-fibre filters.
Laboratory methods and criteria for sediment bioassessment.
A.10 Paragraph 17.
A guide for the identification of British aquatic oligochaeta.
Test substrate
Software 13: 529–537.
U.S. EPA (2000).
11.05 Biological Effects and Environmental Fate; Biotechnology;
Environment Canada (1997).
Environment Canada (1999).
BBA (1995).
Swedish Standards Institute (SIS) (1995).
Riedhammer C. & B. Schwarz-Schulz (2001).
15 lk (rootsi keeles).
In co-operation with R. Nagel and B. Karaoglan.
Umweltbundesamt (UBA)
Environment Canada (2003).
ETH, Stiftung Rubel, Zürich, Šveits.
Nikkilä A., Halme A., Kukkonen J.V.K.
3,3 mg/l
Environment Canada (1995).
8240 Ulmerton Road, Largo, FL 33771–3948, USA,
Landrum, P.F.
9006 Mercer Pike, Meadville, PA 16335, USA,
Mount, D.R., Dawson, T.D.
Blackburn, L. G., ja Boutin, C. (2003).
OECD 2006.
Buhler, D. D., ja Hoffman, M. L. (1999).
Sedimenttoxizitätstests mit aquatischen Oligochaeten — Einfluss verschiedener Futterquellen im künstlichen Sediment auf Reproduktion und Biomasse von Lumbriculus variegatus.
Clay, P. A., ja Griffin, J. L. (2000).
New tables for multiple comparisons with a control.
Cole, J. F. H., ja Canning, L. (1993).
Biometrics 28, 519 531.
Gleason, H. A., ja Cronquist, A. (1991).
Dissolve 11,76 g CaCl2·2H2O in deionised water; make up to 1 l with deionised water
Marrs, R. H., ja Frost, A. J. (1997).
Dissolve 4,93 g MgSO4·7H2O in deionised water; make up to 1 l with deionised water
Marshall, E. J. P., ja Bernie, J. E. (1985).
Dissolve 2,59 g NaHCO3 in deionised water; make up to 1 l with deionised water
Isiklik suhtlus.
e.g. Urtica powder (Folia urticae), leaves of Urtica dioica (stinging nettle), finely ground (particle size ≤ 0,5 mm); in accordance with pharmacy standards, for human consumption;
Heiden, S., Erb, R., Dott, W., ja Eisentraeger, A. (toim.).
If elevated ammonia concentrations are expected, e.g. if the test chemical is known to inhibit nitrification, it may be useful to replace 50 % of the nitrogen-rich urtica powder by cellulose (e.g., α-Cellulose powder, chemically pure, particle size ≤ 0,5 mm; (1) (2)).
Probit Analysis (3. väljaanne), lk 19–76.
Preparation
Kaks kontrollrühma on sarnased?
Finland
Biol.
Via Mornera 25
Aruanne EUR 8714 EN, Euroopa Ühenduste Komisjon.
I-20047 Brugherio MI
Greig-Smith, P. W., Becker, H., Edwards, P. J., ja Heimbach, F. (toim.) (1992).
MDD:
Biology and Ecology of Earthworms, 3. väljaanne.
An overview of the test schedule is given in Appendix 8.
UBA-Texte 4/99, 150 + 223 lk.
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)).
parandus: Environ.
JSS — Journal of Soils and Sediments 3, 73-77.
Sokal, R. R., ja Rohlf, F. J. (1981).
Schlosser, H.-J. and Riepert, F. (1992).
Euroopa Ühenduste Ametlike Väljaannete Talitus, Luksemburg.
Petersen, H. (1978).
Aruanne SPE 1/RM/32.
EPPO (2003):
Detsember 1997.
Fairbrother, A., Glazebrock, P.W., Van Straalen, N.M. and Tarazona, J.V.
Guidance Document on Statistical Methods for Environmental Toxicity Tests, viies kavand, märts 2003;
Schlosser, H.J., und Riepert, F. 1992.
Leppänen, M. T., ja Kukkonen, J. V. K. (1998c).
Heckmann, L.-H., Ruf, A., Nienstedt, K. M. and Krogh, P. H. 2007.
Drewes, C. D., ja Fourtner, C. R. (1990).
Southwood, T.R.E.
Martinez-Madrid, M., Rodriguez, P., Perez-Iglesias, J. I., ja Navarro, E. (1999).
Ruf, A. (1993).
Cambridge Univ.
Synchronisation of culture:
54, ENV/JM/MONO(2006)18.
The mites of stored food and houses.
USA Keskkonnakaitseameti sööde AAP, vastab ka USA Materjalide Katsetamise Ühingu standardile.
Ministry of Agriculture, Fisheries and Food, Technical Bulletin 9:
Peale selle kaasneb pindaktiivse aine lahuse aereerimisega aine kontsentreerumine vahukihti ning vahu kadu katsesüsteemist põhjustab kokkupuutekontsentratsiooni vähenemist.
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.
Faks:
The food mash can then be sucked by the mite.
E-post:
During the test, dissolved oxygen, temperature, and pH should be measured in all test vessels at least once per week.
12307 Berliin
Total hardness and alkalinity should be measured in the controls and one vessel at the highest concentration at least once per week.
mg/l
Report of the Initial Work Towards the Validation of the 21-Day Fish Screening Assay for the Detection of Endocrine active Substances (Phase 1A).
Allpool kirjeldatud meetod mulla pH määramiseks põhineb kirjeldusel, mis on esitatud standardis ISO/DIS 10390 „Soil Quality – Determination of pH” (1).
OECD Environmental Health and Safety Publications Series on Testing and Assessment No.60, ENV/JM/MONO(2006)27.
OECD, Pariis.
OECD (2006b).
Vitellogeniin on peaaegu tuvastamatu isaskalade ja ebaküpsete emaskalade vereplasmas, kuna sellistel kaladel ei ole vereringes piisavalt östrogeeni, kuid nende maks on võimeline vitellogeniini sünteesima ja verre eritama vastuseks stimuleerimisele eksogeense östrogeeniga.
Report of the Initial Work Towards the Validation of the 21-Day Fish Screening Assay for the Detection of Endocrine active Substances (Phase 1B).
Nagu eespool märgitud, ei tarvitse vitellogeniini sisalduse vähenemine olla tingitud üksnes endokriinsest mehhanismist, kuid positiivset tulemust tuleks üldiselt tõlgendada tõendina endokriinse mõju kohta in vivo ja seda tuleks selguse saamiseks tavaliselt täiendavalt uurida.
OECD (2007).
A Guidance to Application” (Ökotoksilisuse andmete statistilise analüüsi kaasaegsed meetodid.
Final report of the Validation of the 21-day Fish Screening Assay for the Detection of Endocrine Active Substances.
Rakendamisjuhend) (11).
Panter GH, Hutchinson TH, Hurd KS, Sherren A, Stanley RD, Tyler CR (2004).
Bacteriol.
Vitellogenin induction by 17β-estradiol and 17β-ethinylestradiol in male zebrafish (Danio rerio).
ISO 11269-2:
1699-1708.
1 (1985) ja Soil Sci.
Development of an ELISA for determination of the hepatic vitellogenin in Medaka (Oryzias latipes).
Polygonum persicaria
Jpn J Environ Toxicol 4:87–98.
58: 1161–1174.
Validation of an enzyme-linked immunosorbent assay method for vitellogenin in the Medaka.
Carolinea 57: 93–100.
Acute and chronic effects of carrier solvents in aquatic organisms:
Dimetüülsulfoksiidi (DMSO)
Aquat.
Hydrobiologia 11: 181–184.
26 ± 2 °C
Assessment of Reverse Phase Chromatographic Methods for Determining Partition Coefficients.
Age of test organisms
Chemosphere 12: 1459.
Approximate wet weight of adult fish (g)
Kördel, W., Weiss, M., ja Poremski, H. J. (1988).
21 d
Updating of the OECD Test Guideline 107 Partition Coefficient n-Octanol-Water, OECD Laboratory Intercomparison Test on the HPLC Method.
Thorpe KL, Benstead R, Hutchinson TH, Tyler CR, 2007.
Chemosphere 17: 361.
An optimised experimental test procedure for measuring chemical effects on reproduction in the fathead minnow, Pimephales promelas.
Eadsforth, C. V. (1986).
Oka, T. B., 1931.
Chromat.
On the processes on the fin rays of the male of Oryzias latipes and other sex characters of this fish.
πX = log Pow (PhX) – log Pow (PhH),
Sci., Tokyo Univ., IV, 2:
J., Reehl, W.
209-218.
F., ja Rosenblatt, D. H. (toim.).
(Other methods can be used if they are performed on ice and the result is a homogenous mass).
Chem.
The tubes should be numbered properly so that the head and tail from the fish can be related to their respective body-section used for gonad histology.
Rekker, R. F. The Hydrophobic Fragmental Constant.
Dunnett test on nested ANOVA No
ISO/DIS 14442:
variance stabilising transform >=4 reps per conc
A simple in vitro fluorescence method for biomass measurements in algal growth inhibition tests.
Tamhane-Dunnett test
Water Res.
Nested ANOVA not normal No
2073–2079.
variance stabilising transformation
Environ.
Variances unequal
713–718.
Dunn or Mann-Whitney test Nested ANOVA normal
Nyholm, N., Sørensen, P. S., Kusk, K. O., ja Christensen, E. R. (1992).
11-14
Norberg-King, T. J. (1988).
15-21
USA Keskkonnakaitseamet, Duluth, MN.
Preliminary work has been conducted on dietary exposures; however, this route of exposure is not commonly used.
Williams, D. A. (1971).
method and frequency of preparation of dilutions.
An equation to describe dose-responses where there is stimulation of growth at low doses.
Test chemical information includes actual and nominal concentrations of the test chemical, and in some cases, non-parent chemical, as appropriate.
Weed Res.
Statistical analyses of the data should preferably follow procedures described in the document Current Approaches in the Statistical Analysis of Ecotoxicity Data:
29: 93–96.
Where no normalising transformation can be found, a significant treatment effect is determined from the Mann-Whitney-Wilcoxon U test using a Bonferroni-Holm adjustment to the p-values.
Manassas, Virginia 20110–2209
The Dunnett test is applied independently of any ANOVA F-test and the Mann-Whitney test is applied independently of any overall Kruskall-Wallis test.
University of Texas at Austin
After stage 60, tadpoles show a reduction in size and weight due to tissue resorption and reduction of absolute water content.
SiO3 · 9H2O