natgillin/translations-raw huggingface dataset:
Total hardness and alkalinity should be measured in the controls and one vessel at the highest concentration at least once per week.
Partition Coefficient, Determination and Estimation, Pergamon Press, Elmsford (New York) och Oxford (1986).
OECD (2006a).
Chemical Reviews.
Report of the Initial Work Towards the Validation of the 21-Day Fish Screening Assay for the Detection of Endocrine active Substances (Phase 1A).
Riktlinjer för biologiska tester.
OECD Environmental Health and Safety Publications Series on Testing and Assessment No.60, ENV/JM/MONO(2006)27.
Albrecht-von-Haller-Institut
OECD (2006b).
Beredning av AAP-medium (enl.
Report of the Initial Work Towards the Validation of the 21-Day Fish Screening Assay for the Detection of Endocrine active Substances (Phase 1B).
EPA)
OECD (2007).
Andersen, J. S., Holst, H., Spliid, H., Andersen, H., Baun, A. och Nyholm, N. (1998).
Final report of the Validation of the 21-day Fish Screening Assay for the Detection of Endocrine Active Substances.
ISO 8192 Vattenundersökningar – Metod för bestämning av hämning av syreförbrukning hos mikroorganismer i aktivt slam (kol- och ammonium-oxidation), Internationella standardiseringsorganisationen.
Testing Negative Substances.
Återfinns i Annual Book of ASTM Standards, Vol.
OECD Environmental Health and Safety Publications Series on Testing and Assessment No.78, ENV/JM/MONO(2007)25.
11.05 Biological Effects and Environmental Fate;
Phase 3 report of the validation of the OECD Fish Screening Assay.
8.
Validation of the Fish Short-Term Reproduction Assay:
Bruce R. D. och Versteeg D. J. (1992) A statistical procedure for modelling continuous toxicity data.
US Environmental Protection Agency, Washington, DC.
SS 02 82 13, s.
Report of the Validation Peer Review for the 21-Day Fish Endocrine Screening Assay and Agreement of the Working Group of the National Coordinators of the Test Guidelines Programme on the Follow-up of this Report.
Lemna gibba:
Androgenic and estrogenic effects of the synthetic androgen 17alpha-methyltestosterone on sexual development and reproductive performance in the fathead minnow (Pimephales promelas) determined using the gonadal recrudescence assay.
ETH, Stiftung Rubel, Zürich, Schweiz.
Andersen L, Goto-Kazato R, Trant JM, Nash JP, Korsgaard B, Bjerregaard P (2006).
1,4 mg/l
Short-term exposure to low concentrations of the synthetic androgen methyltestosterone affects vitellogenin and steroid levels in adult male zebrafish (Danio rerio).
7,3 mg/l
Ankley GT, Kahl MD, Jensen KM, Hornung MW, Korte JJ, Makynen EA, Leino RL (2002).
Till exempel är det lämpligt att ha en till två plantor av majs, sojabönor, tomat, gurka eller sockerbetor per 15 cm behållare, tre plantor av raps eller ärtor per 15 cm behållare, och fem till tio plantor av lök, vete eller andra små frön per 15 cm behållare.
Panter GH, Hutchinson TH, Hurd KS, Sherren A, Stanley RD, Tyler CR (2004).
Canadian Wildlife Service (Headquarters), Environment Canada, Hull, Québec, Kanada.
70(1):11-21.
Non-Target Plant Testing and Evaluation, Centre for Toxicology, University of Guelph, Ontario, Kanada.
123(2):113-25.
EFTER (5, 22, 26)
Panter GH, Tyler CR, Maddix S, Campbell PM, Hutchinson TH, Länge R, Lye C, Sumpter JP, 1999.
EFTER (5, 22, 23)
Application of an ELISA to quantify vitellogenin concentrations in fathead minnows (Pimephales promelas) exposed to endocrine disrupting chemicals.
EFTER (4, 33)
Development and validation of a homologous zebrafish (Danio rerio Hamilton- Buchanan) vitellogenin enzyme-linked immunosorbent assay (ELISA) and its application for studies on estrogenic chemicals.
EFTER (5, 15, 22–26)
C 129 (3):
EFTER
217-232.
L > M (9)
Holbech H, Andersen L, Petersen GI, Korsgaard B, Pedersen KL, Bjerregaard P. (2001).
EFTER (10)
119-131
EFTER (13)
Rose J, Holbech H, Lindholst C, Noerum U, Povlsen A, Korsgaard B, Bjerregaard P. 2002.
EFTER (5, 22, 24–26)
Vitellogenin induction by 17β-estradiol and 17β-ethinylestradiol in male zebrafish (Danio rerio).
EFTER (5, 22, 25, 26)
Brion F, Nilsen BM, Eidem JK, Goksoyr A, Porcher JM, Development and validation of an enzyme-linked immunosorbent assay to measure vitellogenin in the zebrafish (Danio rerio).
R. Lower, W.
1699-1708.
Buhler, D. D. och Hoffman, M. L. (1999).
Yokota H, Morita H, Nakano N, Kang IJ, Tadokoro H, Oshima Y, Honjo T, Kobayashi K. 2001.
Anderson's guide to practical methods of propagating weeds and other plants.
Development of an ELISA for determination of the hepatic vitellogenin in Medaka (Oryzias latipes).
Clay, P. A. och Griffin, J. L. (2000).
Jpn J Environ Toxicol 4:87–98.
Cole, J. F. H. och Canning, L. (1993).
Tatarazako N, Koshio M, Hori H, Morita M and Iguchi T., 2004.
Gleason, H.A. och Cronquist, A. (1991).
Validation of an enzyme-linked immunosorbent assay method for vitellogenin in the Medaka.
Marrs, R. H. och Frost, A. J. (1997).
Journal of Health Science 50:301-308.
Marshall, E. J. P. och Bernie, J. E. (1985).
Ankley GT, Jensen KM, Makynen EA, Kahl MD, Korte JJ, Homung MW, Henry TR, Denny JS, Leino RL, Wilson VS, Cardon MC, Hartig PC, Gray LE (2003).
Pers. med.
22(6):
150 + 223.
1350-60.
46 s.
Seki M, Yokota H, Matsubara H, Maeda M, Tadokoro H, Kobayashi K (2004).
ISO (Internationella standardiseringsorganisationen) (1999).
Fish full life-cycle testing for androgen methyltestosterone on medaka (Oryzias latipes).
Bestämning av akut toxicitet med artificiell jord, nr 11268-1.
23(3):774-81.
ISO (Internationella standardiseringsorganisationen) (1999).
OECD (2000) Guidance Document on Aquatic Toxicity Testing of Difficult Substances and Mixtures.
Heiden, S., Erb, R., Dott, W. och Eisentraeger, A. (red.).
Paris
Probit Analysis (tredje upplagan), s.
Acute and chronic effects of carrier solvents in aquatic organisms:
Bestämning av akut toxicitet med artificiell jord, nr 11268-1.
Environmental Health Perspectives;114 Suppl 1:106-14.
Markundersökningar – Bestämning av den vattenhållande förmågan – Laboratoriemetoder, nr 11274.
Miles-Richardson, SR, Kramer VJ, Fitzgerald SD, Render JA, Yamini B, Barbee SJ, Giesy JP.
UBA-Texte 4/99, s.
Effects of waterborne exposure to 17β-estradiol on secondary sex characteristics and gonads of the fathead minnow (Pimephales promelas).
Hamilton, M. A., R. C. Russo och R. V. Thurston.
Aquat.
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47, 129-145.
A Distribution-free k-Sample Test Against Ordered Alternatives, Biometrika 41, 133–145.
Martinovic, D., L.S. Blake, E.J. Durhan, K.J. Greene, M.D. Kahl, K.M., Jensen, E.A. Makynen, D.L. Villeneuve and G.T. Ankley.
The comparison of treatment to control group means in toxicology studies, Applied Statistics 28, 144–151.
Toxicol.
Van Ewijk, P. H. och J. A. Hoekstra.
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Redaktörer:
27, 478-488.
Madsen, T., Rasmussen, H. B och Nilsson, L. (1996), Methods for screening anaerobic biodegradability and toxicity of organic chemicals.
OECD (2012) OECD Conceptual Framework for Testing and Assessment of Endocrine Disrupters (revised).
Byrån för Europeiska gemenskapernas officiella publikationer, Luxemburg.
ENV/JM/MONO(2012)22
Vol.
Medaka
11.05.
25 ± 2 °C
Redaktörer: M. Streloke och H.Köpp.
26 ± 2 °C
Meyer, J. S., Boese, C. J. och Collyard, S. A. (2002).
Age of test organisms
Ludwichowski och R. Nagel (2000).
Approximate wet weight of adult fish (g)
Leppänen, M. T. och Kukkonen, J. V. K. (1998).
21 d
Drewes, C. D. och Fourtner, C. R. (1990).
Thorpe KL, Benstead R, Hutchinson TH, Tyler CR, 2007.
Martinez-Madrid, M., Rodriguez, P., Perez-Iglesias, J. I. och Navarro, E. (1999).
An optimised experimental test procedure for measuring chemical effects on reproduction in the fathead minnow, Pimephales promelas.
Mount, D. R., Dawson, T. D. och Burkhard, L. P. (1999).
2001.
Om mortaliteten under sju dagar är högre än 10 % av populationen ska hela partiet förkastas.
Aspects of basic reproductive biology and endocrinology in the fathead minnow (Pimephales promelas).
Om mortaliteten under sju dagar är lägre än 5 % av populationen ska partiet godtas.
Comp Biochem Physiol C 128:127-141.
Sumpter och Jobling (1995).
Diagram showing sexual difference in shape and size of the anal fin.
Hutchinson, T. H., Shillabeer, N., Winter, M.J. och Pickford, D. B. (2006a).
A, male; B, female.
Thorpe, K. L, Benstead, R., Hutchinson, T.H och Tyler C. R. (2007).
Oka, T. B., 1931.
Jensen, K. M., Korte, J. J., Kahl, M. D., Pasha, M. S. och Ankley, G. T. (2001).
Sci., Tokyo Univ., IV, 2:
Typiska uppgifter inbegriper omgivande temperatur, testtemperatur, fotoperiod, status för de viktiga komponenterna i exponeringssystemet (t.ex. pumpar, räknare för cykler, tryck), flödeshastigheter, vattennivåer, byten av flaskor med stamlösning och utfodringsuppgifter.
209-218.
Allmänna parametrar för vattenkvaliteten inbegriper pH-värde, halt av löst syre, konduktivitet, total jodhalt, alkalinitet, hårdhet,
B, Distal extremity of fin-ray.
2 ml 5M NaCl
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.
Träskydd – Accelererad åldring av träskyddsbehandlat virke före biologisk provning – Laboratoriemetod.
Dunnett test on nested ANOVA No
Träskydd – Bestämning av den relativa förebyggande skyddseffekten hos ett träskyddsmedel i markkontakt – Fältprovning
variance stabilising transform >=4 reps per conc
Markwell, R. D., Connell, D. W. och Gabric, A. J. (1989).
Tamhane-Dunnett test
Gabric, A. J., Connell, D. W. och Bell, P. R. F. (1990).
>=4 reps per conc <=3 reps per conc
Hawker, D. W. och Connell, D. W.
Nested ANOVA not normal No
Aston, R. J. och Milner, A. G. P. (1981).
variance stabilising transformation
Marchese, M. R. och Brinkhurst, R. O. (1996).
11-14
Chapman, P. M., Farrell, M. A. och Brinkhurst, R. O. (1982b).
15-21
Roghair, C. J., Buijze, A., Huys, M. P. A., Wolters-Balk, M. A. H., Yedema, E. S. E. och Hermens, J. L. M. (1996).
Preliminary work has been conducted on dietary exposures; however, this route of exposure is not commonly used.
Aston, R. J. (1984).
physical-chemical properties; information on stability and biodegradability;
Version 1.0, 3 augusti.
Test chemical information includes actual and nominal concentrations of the test chemical, and in some cases, non-parent chemical, as appropriate.
Organisationen för ekonomiskt samarbete och utveckling (OECD), Paris.
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.
Under alla omständigheter ska prover tas från testkärlen efter 3 timmar, och vid behov efter ytterligare 30 minuter, för mätning av syreupptagningshastigheten i syreelektrodcellen.
After stage 60, tadpoles show a reduction in size and weight due to tissue resorption and reduction of absolute water content.
%I y
OECD (2004) Report of the Validation of the Amphibian Metamorphosis Assay for the detection of thyroid active substances:
t.ex. nässelpulver (Folia urticae) från blad av Urtica ciodica (brännässla), finmalet (partikelstorlek ≤ 0,5 mm), av apotekskvalitet för livsmedelsbruk, som tillsats till torrt sediment
OECD (2007) Final Report of the Validation of the Amphibian Metamorphosis Assay:
Kvalster/Parasitiformes/Gamasida
ASTM (2002) Standard Guide for Conducting Acute Toxicity Tests on Test Materials with Fishes, Macroinvertebrates, and Amphibians.
Nr 76.
American Society for Testing and Materials, ASTM E729-96(2002), Philadelpia, PA
Nr 92.
ASTM (2004) Standard Guide for Conducting the Frog Embryo Teratogenesis Assay — Xenopus (FETAX).
Nr 23.
Kahl,M.D., Russom,C.L., DeFoe,D.L. & Hammermeister,D.E. (1999) Saturation units for use in aquatic bioassays.
Nr 82.
Chemosphere 39, pp. 539-551
Aquatic Toxicology, 76, s. 69–92.
Nieuwkoop,P.D. & Faber,J.
Nr 11267.
Normal Table of Xenopus laevis.
M. Streloke och H. Köpp.
Garland Publishing, New York
American Water Works Association & Water Pollution Control Federation, 16:e upplagan, 1985.
OECD (2007) Guidance Document on Amphibian Thyroid Histology.
mh = 0,468Δp × Vh
Dodd,M.H.I. & Dodd,J.M.
2 d.
Physiology of Amphibia.
4 d.
Lofts,B.
8 d.
OECD (2006) Current Approaches in the Statistical Analysis of Ecotoxicity Data:
15 d.
Environmental Health and Safety Publications.
22 d.
Series on Testing and Assessment, No. 54.
29 d.
Paris
OECD Monographs nr 60.
Acute and chronic effects of carrier solvents in aquatic organisms:
Chemosphere 32, 1897–1905.
ROW
(För mätinstrument som kalibrerats i lux motsvarar den rekommenderade ljusintensiteten 60–120 μE · m– 2 · s– 1 för kallt vitt ljus ungefär 4440–8880 lux.)
TRT#
Ljusintensiteten över inkuberingsytan ska ligga inom ± 15 % från genomsnittsvärdet.
SVL (mm)
Proposed Guidelines for Registration of Chemical Pesticides:
SVL
OECD Environmental Health and Safety Publications, Series on Testing and Assessment No.
Any substance or mixture tested using this test method
23.
The pH should be measured at the beginning and the end of both the range-finding test and the definitive test.
A statistical procedure for modelling continuous toxicity data.
Measurements should be made in one extra control sample and one extra sample of the treated (all concentrations) soil samples prepared and maintained in the same way as the test cultures, but without addition of the collembolans.
A Multiple Comparisons Procedure for Comparing Several Treatments with a Control.
Appropriate statistical methods should be used according to OECD Document 54 on the Current Approaches in the Statistical Analysis of Ecotoxicity Data:
A test for differences between treatment means when several dose levels are compared with a zero dose control.
a Guidance to Application (9).
The comparison of several dose levels with a zero dose control.
In general, adverse effects of the test chemical compared to the control are investigated using one-tailed hypothesis testing at p ≤ 0,05.
Raleigh, NC 27695–8002
the NOEC/LOEC values, LCx for mortality and ECx for reproduction (mostly LC50, LC10, EC50, and EC10) together with 95 % confidence intervals.
Weed Science, 33, Suppl.
ISO (1999) Soil Quality — Effects of soil pollutants on Collembola (Folsomia candida):
Polygonum persicaria
International Organisation for Standardisation, Geneve
Pest Management Science, 58, 1161–1174.
Burges A and Raw F (Eds) (1967) Soil Biology.
Markundersökningar – Föroreningars effekt på daggmaskar (Eisenia fetida).
London
Carolinea 57, 93–100.
Petersen H (1994) A review of collembolan ecology in ecosystem context.
Replikatmedelvärden ej normalfördelade
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 August-2 September 1982, I Dieu-Brichart, Ottignies-Louvain-la-Neuve, pp. 261-268
Estuaries 13, 301–310.
Environmental Project Nr. 986.
J. 43, 165–172.
Miljøstyrelsen 61 pp.
235–276.
Krogh, P.H., 2009.
35, 191–201.
7, 201-205
Aquaculture 26, 155–160.
Goto HE (1960) Simple techniques for the rearing of Collembola and a not on the use of a fungistatic substance in the cultures.
32, 1503–1508.
the mean sex ratio of fully emerged and alive adults (as female or male fraction) in the control treatment of both generations should be at least 0,4, but not exceed 0,6;
Aquaculture 29, 137–145.
for each breeding cage the number of egg ropes in the controls of the 1st generation should be at least 0,6 per female added to the breeding cage;
Aquaculture 40, 89–94.
at the end of the exposure period for both generations, pH and the dissolved oxygen concentration should be measured in each vessel.
17, 361.
4-5 % (dry weight) peat: as close to pH 5,5 to 6,0 as possible;
C. V. Eadsforth.
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.
L. O. Renberg, S. G. Sundström och K. Sundh-Nygård.
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.
J. E. Haky och A. M. Young.
However, every effort should be made to avoid the use of such materials.
Log P and Parameter Database:
The factor between concentrations should not be greater than two (an exception could be made in cases when the dose response curve has a shallow slope).
Rosenblatt (red.).
However, if the test chemical is demonstrated not to adsorb to filters, filtration may also be acceptable.
R. F. Rekker.
Emergence ratios are quantal data, and can be analysed by the Cochran-Armitage test applied in a step-down manner where a monotonic dose-response is expected and these data are consistent with this expectation.
R. A. Scherrer.
If not, a Fisher's exact or Mantel-Haentzal test with Bonferroni-Holm adjusted p-values can be used.
Detta kan göras grafiskt eller med ett etablerat test (17), t.ex.
volume of overlying and pore water; weight of wet sediment with and without pore water for the test vessels and the crystallising dishes;
Levenes eller Bartletts test.
Entomologica Scandinavica, 30:
2073–2079.
, Sediment Toxicity Tests for Poorly Water-Soluble Substances, Final Report to the European Commission, Report No:
Nyholm, N., Sørensen, P. S., Kusk, K. O. och Christensen, E. R. (1992).
ASTM International (2009), E1706-05E01:
Norberg-King, T. J. (1988).
US-EPA (2000), Methods for Measuring the Toxicity and Bioaccumulation of Sediment-associated Contaminants with Freshwater Invertebrates, Second edition, EPA 600/R-99/064, March 2000, Revision to the first edition dated June 1994.
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US-EPA/OPPTS 850.1735 (1996), Whole Sediment Acute Toxicity Invertebrates.
519–531.
Milani, D., Day, K.E., McLeay, D.J. and R.S.
Weed Research 29, 93–96.
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Chem., 25:
Water Research, 30, 1625–1632.
suitable test organisms for risk assessment investigations on the potential endocrine-disrupting properties of pesticides, Ecotoxicology, 16:
245–261.
221-230.
27–39.
Kawai, K. (1986), Fundamental studies on chironomid allergy, I. Culture methods of some Japanese chironomids (Chironomidae, Diptera), Jp.
Levenes eller Bartletts test.
Zool., 37:
Pesticides, ASTM, West Conshohocken, PA, USA.
47-57.
L., Billeck, B. N. och Baron, C. L. (1989).
OECD (2000), Guidance Document on Aquatic Toxicity Testing of Difficult Substances and Mixtures, Environment, Health and Safety Publications, Series on Testing and Assessment No. 23, ENV/JM/MONO(2000)6, OECD, Paris.
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Weltje, L., Rufli, H., Heimbach, F., Wheeler, J., Vervliet-Scheebaum, M. and M. Hamer (2010), The chironomid acute toxicity test:
Environmental Toxicology and Chemistry, 11, 1485–1494.
Environment Canada.
Assoc., 50, 1096–1121.
Toxicol., 49:
Saf., 5, 87–96.
353-361.
Toxicol. and Chem., 12, 481–483.
Suedel, B.C. and J.H. Rodgers (1994), Development of formulated reference sediments for freshwater and estuarine sediment testing, Environ.
Institutionen för tillämpad miljövetenskap (ITM), Stockholms universitet
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Environmental Pollution, Ser B, 11, 1–14.
1163-1175.
Applied Soil Ecology, 7, 189–193.
Naylor, C. and C. Rodrigues (1995), Development of a test method for Chironomus riparius using a formulated sediment, Chemosphere, 31:
FIFRA, 40CFR, Del 158.540.
Assoc., 50:
Beall, M. L., Jr. och Nash, R. G. (1969).
1096-1121.
61, 571–575.
, New tables for multiple comparisons with a control, Biometrics, 20:
61, 247–250.
482-491.
Boutin, C., Elmegaard, N. och Kjær, C. (2004).
Biometrics, 27:
Boutin, C. och Harper, J. L. (1991).
J Soils Sediments, 9:
Environmental Toxicology and Chemistry 11, 1485–1492.
Rao, J.N.K. and A.J. Scott (1992), A simple method for the analysis of clustered binary data.
L = M (11)
Biometrics, 48:
L > M (6)
577-585.
L > M
1165-1176.
Track-sprayer and glasshouse techniques for terrestrial plant bioassays with pesticides.
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.
Plants for toxicity assessment, vol.
Health Part A, 42:
2.
To prepare the combined stock solution (II): mix the following amounts (ml) of stock solutions (I) and make up to 1 litre of deionised water
Flynn, S., Turner, R. M., och Dickie, J. B. (2004).
A glass tube (inner diameter ca.
Weed Science, 40, 227–232.
B cork of vulcanised rubber, perforated with glass tube (A).
Environmental Pollution, 59, 71–86.
MOA
Environmental Pollution, 73, 25–42.
Tyler, C.R., R.van Aerle, T.H.
Løkke, H. och C. A. M. Van Gestel, Handbook of soil invertebrate toxicity tests.
27 ± 2 °C
Chemosphere, 39 (12), 2007–2018.
20 ± 2 °C
EPA 600/R-99/064, amerikanska miljöskyddsmyndigheten (EPA), Duluth, MN, mars 2000.
385-398.
12(7):1261–1266.
5 min 95 °C
292–302.
Saturate the test medium with air at the test temperature by aerating with clean compressed air for about 20 minutes.
Morphallaxis in an aquatic oligochaete, Lumbriculus variegatus:
Determination of the biodegradability of the organic fraction of chemical wastes.
2–14
Screening Test Methods for Assessment of Biodegradability of Chemical Substances in Seawater.
57, 21–46.
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.
Pacific Insects 24, 259–274.
Determination of volatile organic carbon can subsequently be performed, if relevant, for the sample type in question.
Dahl, F. (red.):
ISO, Water quality — determination of total organic carbon.
Symp.
American Public Health Association, Standard Methods for the Estimation of Water and Wastewater.
1994, Columbus, Ohio, s.
Schreurs W.
621–628.
Hydrobiological Bulletin 12, 137-142.
Krogh, P. H. och Axelsen, J. A. (1998).
% abiotic degradation
Løkke, H., Janssen, C. R., Lanno, R. P., Römbke J., Rundgren, S. och Van Straalen, N. M. (2002).
ThODNH3
Fairbrother, A., Glazebrook, P. W., van Straalen, N. M. och Tarazona, J. V. (red.).
ThODNO2
Die Vermehrungsrate von Hypoaspis aculeifer Canestrini (Acarina, Laelapidae) bei Ernährung mit Onychiurus fimatus Gisin (Collenbola).
ThODNO3
Mitt.
test substancemg
Ges. allg. angew.
12 relative atomic mass of carbon; n
SIS – Svenska standardiseringsinstitutet.
where: p
Technical Guidance Document in support of Commission Directive 93/67/EEC on Risk Assessment for new notified substances, Commission Regulation (EC) No 1488/94 on Risk Assessment for existing substances and Directive 98/8/EC of the European Parliament and of the Council concerning the placing of biocidal products on the market, del I–IV.
pressure of the gas (Pascals); V
Workshop on ’Bioaccumulation: Sediment test using benthic oligochaetes’, 26–27 april 1999, Hochheim/Main, Tyskland.
C.9, Biodegradation — Zahn-Wellens Test;
Lysrör bör användas för att ge en fotoperiod på 12 timmar ljus/12 timmar mörker vid en intensitet som varierar från 600–2000 lux (lumen/m2) vid vattenytan.
Owen, W.F., Stuckey, DC., Healy J.B., Jr, Young L.Y. and McCarty, P.L.
I annat fall anges LateStage = ’nej’.
Healy, J.B.Jr. and Young, L.Y.
Därefter kan en tvåfaktors ANOVA för koncentrationen och LateStage och deras interaktion utföras, med Rep(Conc) som slumpmässig faktor och Tadpole(Rep) en ytterligare slumpmässig effekt.
Proposed standard practice for the determination of the anaerobic biodegradation of organic chemicals.
Utöver de vanliga ANOVA F-testerna för effekterna av Conc, LateStage, och deras interaktioner kan F-testet för interaktion ’delas upp’ i ytterligare två ANOVA F-tester, ett för de genomsnittliga responserna över alla koncentrationer för LateStage = ’Nej’ och ett annat för de genomsnittliga responserna över alla koncentrationer för LateStage = ’ja’.
Battersby, N.S. and Wilson, V. (1988) Evaluation of a serum bottle technique for assessing the anaerobic biodegradability of organic chemicals under methanogenic conditions.
Ytterligare jämförelser av testkärlens medelvärden mot kontrollen görs inom varje nivå av LateStage.
E1192-92.
En Bonferroni-Holm-justering av p-värdena görs endast om motsvarande F-skärning inte är signifikant.
Test temperature:
561–573.