natgillin/translations-raw huggingface dataset:
Maron, D., Katzenellenbogen, J. and Ames, B.N., (1981) Compatibility of Organic Solvents with the Salmonella/Microsome Test. Mutation Res., p. 88343-350.
Maron, D., Katzenellenbogen, J. and Arnes, B. N. (1981), Compatibility of Organic Solvents with the Salmonella/Microsome Test, Mutation Res., 88, s. 343–350.
Statistical Evaluation of Mutagenicity Test Data. Ed.
Statistical Evaluation of Mutagenicity Test Dala, ed.
A report from ICPEMC Task Group 9. Mutation Res., 257, p. 147-204.
A report from ICPEMC Task Group 9, Mutation Res., 25 7. s. 147–204.
Jr. and Yang, L.L., (1987) A Guide for the Performance of the Chinese Hamster Ovary Cell/Hypoxanthine-Guanine Phosphoribosyl Transferase Gene Mutation Assay. Mutation Res., 189, p. 135-141.
N., Hsie, A. W., Gupta, R. S., Loveday, K. S., O'Neill, J. P., Riddle, J. C, Stankowski, L. F. Jr. and Yang, L. L. (1987), A Guide for the Performance of the Chinese Hamster Ovary Cell/Hypoxanthine-Guanine Phosphoribosyl Transferase Gene Mutation Assay, Mutation Res., 189, s. 135–141.
Liber, H.L., Yandell, D.W and Little, J.B., (1989) A Comparison of Mutation Induction at the TK and HPRT Loci in Human Lymphoblastoid Cells: Quantitative Differences are Due to an Additional Class of Mutations at the Autosomal TK Locus. Mutation Res., 216, p. 9-17.
Liber, H. L, Yandell, D. W. and Little, J. B. (1989), A Comparison of Mutation Induction at the TK and HPRT Loci in Human Lymphoblastoid Cells: Quantitative Differences are Due to an Additional Class of Mutations at the Autosomal TK Locus, Mutation Res., 216, s. 9–17.
Jr., Tindall, K.R. and Hsie, A.W., (1986) Quantitative and Molecular Analyses of Ethyl Methanosulphonate -and ICR 191- Induced Molecular Analyses of Ethyl Methanosulphonate -and ICR 191-Induced Mutation in AS52 Cells. Mutation Res., 160, p. 133-147.
(1986), Quantitative and Molecular Analyses of Ethyl Methanosulphonate and ICR 191-Induced Molecular Analyses of Ethyl Methanosulphonate and 1CR 191 Induced Mutation in AS52 Cells, Mutation Res.. 160, s. 133–147.
Turner, N.T., Batson, A.G. and Clive, D., (1984) Procedures for the L5178Y/TK+/- — TK+/- Mouse Lymphoma Cell Mutagenicity Assay. In: Kilbey, B.J. et al (eds.)
Turner, N. T., Balton, A. G. and Clive, D. (1984), Procedure for the L51 78Y/TK+/- – TK+/- Mouse Lymphoma Cell Mutagenicity Assay, in: Kilbey, B.J. et all (eds.)
Arlett, C.F., Smith, D.M., Clarke, G.M., Green, M.H.L., Cole, J., McGregor, D.B. and Asquith, J.C., (1989) Mammalian Cell Gene Mutation Assays Based upon Colony Formation. In: Statistical Evaluation of Mutagenicity Test Data, Kirkland, D.J., Ed., Cambridge University Press, p. 66-101.
Arlett, C. F.. Smith, D. M., Clarke, G. M., Green, M. H. L., Cole, J., McGregor, D. B. and Asquith S. C. (1989), Mammalian Cell Gene Mutation Assays Based upon Colony Formation, in: Statistical Evaluationof Mutagenicity Test Data, Kirkland, D. J., ed., Cambirdge University Press, s. 66–101.
Abbondandolo, A., Bonatti, S., Corti, G., Fiorio, R., Loprieno, N. and Mazzaccaro, A., (1977) Induction of 6-Thioguanine-Resistant Mutants in V79 Chinese Hamster Cells by Mouse-Liver Microsome-Activated Dimethylnitrosamine. Mutation Res., 46, p. 365-373.
Abbondandolo, A., Bonatti, S., Corti, G., Fiorio, R., Loprieno, N. and Mazzaccaro, A. (1977), Induction of 6-Thioguanine-Resistant Mutants in V79 Chinese Hamster Cells by Mouse-Liver Microsome- Activated Dimethyllnitrosamine, Mutation Res., 46, s. 365–373.
Elliott, B.M., Combes, R.D., Elcombe, C.R., Gatehouse, D.G., Gibson, G.G., Mackay, J.M. and Wolf, R.C., (1992) Alternatives to Aroclor 1254-Induced S9 in In Vitro Genotoxicity Assays. Mutagenesis, 7, p. 175-177.
Elliott, E. M., Combes, R. D., Elcombe, C. R., Gatehouse, D. G., Gibson, G. G., Mackay, J. M. and Wolf, R. C. (1992), Alternatives to Aroclor 1254-Induced S9 in: In Vitro Genotoxicity Assays, Mutagenesis 7, s. 175–177.
Moore, M.M., Clive, D., Hozier, J.C., Howard, B.E., Batson, A.G., Turner, N.T. and Sawyer, J., (1985) Analysis of Trifluorothymidine-Resistant (TFTr) Mutants of L5178Y/TK+/- Mouse Lymphoma Cells. Mutation Res., 151, p. 161-174.
Moore, M. M., Clive, D. Hozier, J. C, Howard, B. E., Batson, A. G., Turner, N. T. and Sawyer, J. (1985), Analysis of Trifluoronthymidine, Resistant (TFT) Mutants of L5178Y/TK+/- – Mouse Lymphoma Cells, Mutation Res., 151, s. 161–174.
Moore, M.M. and Doerr, C.L., (1990) Comparison of Chromosome Aberration Frequency and Small-Colony TK-Deficient Mutant Frequency in L5178Y/TK+/- - 3.7.2C Mouse Lymphoma Cells. Mutagenesis, 5, p. 609-614.
Moore, M. M. and Doerr, C. L. (1990), Comparison of Chromosome Aberration Frequency and Small Colony TK-Deficient Mutant Frequency in L5178Y/TK+/- – 3.7.2C Mouse Lymphoma Cells, Mutagenesis, 5, s. 609–614.
Single administration of the test substance is the most widely used. Other treatment schedules may be used.
Normalt ges hela dosen på en gång men andra behandlingsscheman kan också användas.
Adler, I.D., (1984) Cytogenetic tests in Mammals. In: Mutagenicity Testing: a Practical Approach. Ed.
Adler, I. D., (1984), Cytogenetic tests in Mammals, in: Mutagenicity Testing: a Practical Approach, (ed.)
Venitt and J.M. Parry. IRL Press, Oxford, Washington DC, p. 275-306.
Venitt and J. M. Parry, 1RL Press, Oxford, Washington DC, s. 275–306.
Fielder, R.J., Allen, J.A., Boobis, A.R., Botham, P.A., Doe, J., Esdaile, D.J., Gatehouse, D.G., Hodson-Walker, G., Morton, D.B., Kirkland, D.J. and Richold, M., (1992) Report of British Toxicology Society/UK Environmental Mutagen Society Working group: Dose setting in In Vivo Mutagenicity Assays. Mutagenesis, 7, p. 313-319.
Fielder, R. J., Allen, J. A., Boobis, A. R., Botham, P. A., Doe, J., Esdaile, D. J., Gatehouse, D. G., Hodson- Walker, G.. Morton, D. B., Kirkland, D. J. and Richold, M. (1992), Report of British Toxicology Society/UK Environmental Mutagen Society Working Group: Dose setting in In Vivo Mutagenicity Assays, Mutagenesis, 7, s. 313–319.
The temperature in the experimental animal room should be 22 oC (± 3o) for rodents and 18 oC (± 3o) for rabbits.
Temperaturen i försöksdjurens rum bör vara 22 oC (± 3 oC) för gnagare och 18 oC (± 3 oC) för kaniner.
Animals dosed during the fertility study are allowed to litter normally and rear their progency to the stage of weaning without standardisation of litters. Where standardisation is done, the following procedure is suggested.
De djur som doseras i fertilitetsundersökningen bör ha möjlighet att föda normalt och att behålla sin avkomma tills den är avvand utan standardisering av kullar.
If data on spermatogenesis are available from a previous repeated dose study of sufficient duration, e.g. a 90-day study, males of the P generation need not be included in the evaluation.
Om data om spermatogenesen finns att tillgå från tidigare tillräckligt långa test med upprepad dos, t.ex. ett 90-dagars test, behöver P-generationens handjur inte inkluderas i utvärderingen.
It is recommended, however, that samples or digital recordings of sperm of the P generation are saved, to enable later evaluation.
Det rekommenderas dock att prover eller digitala registreringar av P-generationens sperma bevaras, så att senare utvärderingar vid behov kan göras.
Enumeration should be performed on the selected subset of males of all dose groups immediately after killing the animals unless video or digital recordings are made, or unless the specimens are freezed and analysed later.
Räkningen bör utföras omedelbart efter avlivningen för den valda undergruppen av handjur från alla dosgrupper. Undantag till detta är om man gör video- eller digitalregistreringar eller om proverna djupfryses och analyseras senare.
Test Guideline for a Developmental Neurotoxicity Study, OECD Guidelines for the Testing of Chemicals. In preparation.
”Test Guidline for a Developmental Neurotoxicitu Study, OECD Guidelines for the Testing of Chemicals” (under beredning).
Griffin, Weycombe, U.K., 1978.
Griffin, Weycombe, U. K., 1978.
Bioassay methods for acute toxicity.
II Bioassay methods for acute toxicity. Water Res.
Dilution water
Utspädningsvatten
Deionised or distilled water, free from inhibitory concentrations of toxic substances (e.g. Cu ++ ions) is used.
Avjoniserat eller destillerat vatten utan innehåll av toxiska substanser (t.ex. Cu++ joner) används.
It must contain no more than 10 % of the organic carbon content introduced by the test material.
Det får inte innehålla mer än 10 % av det organiska kol som tillförs med testämnet.
The high purity of the test water is necessary to eliminate high blank values.
Denna höga renhet är nödvändig för att undvika höga blindvärden.
PART II. DOC DIE-AWAY TEST (Method C.4-A)
DEL 2 DOC-ELIMINERING (DOC DIE-AWAY) (metod C.4-A)
PART VI. CLOSED BOTTLE TEST (Method C.4-E)
DEL 6 CLOSED BOTTLE-TEST (metod C.4-E)
PART VII. M.I.T.I. TEST (Method C.4-F)
DEL 7 MITI TEST (metod C.4-F)
A solution of 5,5-dichlorophenol can for example be prepared by dissolving 0,5 g 3,5-dichlorophenol in 10 ml of 1M NaOH, diluting to approximately 30 ml with distilled water, adding under stirring 0,5M H2SO4 to the point of incipient precipitation — approximately 8 ml of 0,5M H2SO4 will be required — and finally diluting the mixture to one litre with distilled water.
En lösning av 3,5-diklorfenollösning kan t.ex. framställas genom att lösa 0,5 g 3,5-diklorfenol i 10 ml 1 M NaOH vilket späds med destillerat vatten till ca 30 ml.
The pH should then be in the range 7 to 8.
Därefter tillsätts under omrörning 0,5 M H2SO4 upp till den punkt då utfällning börjar – det krävs ca 8 ml 0,5 M H2SO4 – och slutligen späds blandningen med destillerat vatten till 1 I. pH-värdet ska därefter vara omkring 7–8.
Final report to the Commission of the European Communities, p. 60. June 1990.
Final report to the Commission of the European Communities, 60 sidor, juni 1990.
Bluegill (8)
Solaborre (”Bluegill”) (8)
Gadus morhua
Gadus rnorhua
P ' % survival observed in the test concentration
P ' procentandel överlevande som observerats i testkoncentrationen,
C % survival in the control
C procentandelen överlevande i kontrollgruppen.
Cyprinus carpio
Cyprinus
Russell M.H., (1995), ‘Recommended approaches to assess pesticide mobility in soil’ in Environmental Behavior of Agrochemicals (ed. T.R.
Russell M. H. (1995), ”Recommended approaches to assess pesticide mobility in soil” in Environmental Behavior of Agrochemicals (ed.
Guth J.A., Burkhard N., and D.O. Eberle, (1976) ‘Experimental models for studying the persistence of pesticides in soils’.
Guth J. A., Burkhard N. and D. O. Eberle (1976), ”Experimental models for studying the persistence of pesticides in soils”.
These particles, with a size less than 0,2 μm, can have an important impact on the whole adsorption mechanism of a substance in a soil suspension.
Dessa partiklar är mindre än 0,2 μm och kan ha viktig inverkan på hela adsorptionsmekanismen för ett ämne i en jordsuspension.
When centrifugation is performed as described above, colloids remain in the aqueous phase and are subjected to analysis together with the aqueous phase.
När centrifugeringen utförs på ovan beskrivet sätt blir kolloiderna kvar i vattenfasen och analyseras då tillsammans med den.
Ebulliometer 1.1. Melting temperature devices with liquid bath
Ebulliometer
ΔH v
A H v
ΔH vb
Δ H vh
Dibenzyl
Dibensyl
Shock test apparatus
Slagpåverkanapparatur
toothed rack
kuggstång
Fig. 4b Fall-hammer, lower part
Fig. 4b Fallhammare, lägre del
However, if further confirmation of the classification is required, an optional supplementary procedure may be conducted, as follows.
Om det ändå behövs ytterligare bekräftelse av klassificeringen kan ett valfritt tilläggsförfarande genomföras.
Animal welfare override If this dose level caused death in the sighting study, then no futher animals will be tested. Go directely to outcome
Djurens välbefinnande styr : Om denna dosnivå orsakar dödsfall i det inledande testet skall inga fler djur testas Gå direkt till utfall
Measurements should be made weekly of the animals' weight. It is also recommended that food consumption is measured weekly.
Djurens ska vägas varje vecka och vidare rekommenderas att foderförbrukningen mäts per vecka.
Genotoxic Effects of Airborne Agents.
Genotoxic Effects oj Airborne Agents.
MMS.
Mutation Res.
With organic compounds that are water insoluble not more than a 2 % solution v/v of organic solvents such as ethanol, acetone or dimethylsulphoxide (DMSO) should be used. The final concentration of the vehicle should not significantly affect cell viability and growth characteristics.
Om organiska kemiska förbindelser som inte går att lösa i vatten används, bör organiska lösningsmedel som etanol, aceton eller dimetylsulfoxid (DMSO) användas i koncentrationer på upp till 2 % v/v.
Male Chinese hamsters and mice are commonly used.
Handjur av kinesiska hamstrar och möss används i stor utsträckning.
However, males of other appropriate mammalian species may be used.
Det är även möjligt att använda hanar från andra lämpliga däggdjursarter.
PIF=IC50
PIF=EC50
Part 1: Static method.
Del 1: Static method.
50 g/l
50 g/l.
Standard Methods for the Examination of Water and Wastewater, 12th ed, Am.
Standard Methods for the Examination of Water and Wastewater, 12th ed., Am.
Chemosphere, 1987, vol. 16, 833.
Chemosphere, 1987, Vol. 16, s. 833.
Chemosphere, 1984, vol. 13, 169.
Chemosphere, 1984, Vol. 13, s. 169.
Chemosphere, 1987, vol. 16, 2259.
Chemosphere, 1987, Vol. 16, s. 2259.
40 g/l
40 g/l.
Water Quality Institute, Denmark.
Biokoncentration i fisk: Jämförelse av biokoncentrationsfaktorer från OECD:s och ASTM:s provningsmetoder, partikelformigt organiskt materials påverkan på kemikaliers biotillänglighet), Water Quality Institute, Danmark.
July 1994.
Tekniskt underlag för kvalitetsinitiativet för vattnet i Stora sjöarna, för fastställande av bioackumulationsfaktorer), juli 1994.
Gasterosteus aculeatus
Gasteroteus aculeatus
Partitioning of organic compounds in octanol-water systems.
(1982), Partitioning of organic compounds in octanol-water systems.Environ.
Oryzias latipes
Oryzias latipes Japanese
V T
V r
Cohen S.Z., Creeger S.M., Carsel R.F., and Enfield C.G. (1984), ‘Potential pesticide contamination of groundwater from agricultural uses’, in Treatment and Disposal of Pesticide Wastes, p. 297-325, ACS Symp.
Cohen S. Z., Creeger S. M., Carsel R. F. and Enfield C. G. (1984), ”Potential pesticide contamination of groundwater from agricultural uses”, in Treatment and Disposal of Pesticide Wastes, s. 297–325, ACS Symp.
Kördel, J. Müller (1994). Bestimmung des Adsorptionskoeffizienten organischer Chemikalien mit der HPLC.
Kördel, J. Müller (1994), Bestimmung des Adsorplionskoeffizienten organischer Chemikalien mit der HPLC, UBA R & D Report No.
Standard method for assessing the thermal stability of chemicals by methods of differential thermal analysis
Standard method for assessine the thermal stability of chemicals by methods or differential thermal analysis
ΔZ b
Δ Z b
sample under test, approximately 10 mm3
testprov, cirka 10 mm3
Fig. 5b Starting position of peg on sample
Fig. 5b Startposition for pinne på prov
An Evaluation of the Proposed OECD Testing Strategy for Skin Corrosion.
Curren, L.K. Earl, J. Esdaile, M. Liebsch (1998), ”An Evaluation of the Proposed OECD Testing Strategy for Skin Corrosion”, ATLA.
Concurrent measures of cytotoxicity for all treated and negative control cultures in the main aberration experiments should also be recorded. Individual culture data should be provided.
Olika typer av strukturella kromosomavvikelser bör listas med antal och frekvenser för experimentella kulturer samt kontrollkulturer.
The animals are identified uniquely. The animals are acclimated to the laboratory conditions for at least five days.
Burar bör arrangeras på ett sådant sätt att möjliga effekter beroende på placeringen av burarna blir så små som möjligt.
Report Part III.
III.
In: D.J. Kirkland (Ed.)
In: D. J. Kirkland (ed.)
Acad. Sci.
Acad.Sci.
Cd(t)
medel Cd(t)
BOD Biochemical oxygen demand (g) is the amount of oxygen consumed by micro-organisms when metabolising a test compound; also expressed as g oxygen uptake per g test compound.
BOD Biokemisk syreförbrukning (g) definieras som den mängd syre som mikroorganismer förbrukar vid metabolism av testämnet.
(See method C.5).
Resultatet uttrycks också som gram upptaget syre per gram testat ämne (se metod C.5).
COD Chemical oxygen demand (g) is the amount of oxygen consumed during oxidation of a test compound with hot, acidic dichromate; it provides a measure of the amount of oxidisable matter present; also expressed as 9 oxygen consumed per g test compound.
COD Kemisk syreförbrukning (g) definieras som den mängd syre som förbrukas vid oxidering av testämnet med varm dikromat i sur vätska.
DOC [1]mg/l
DOC [1](mg/l)
s DR
SDr
Toxicol. and Chem.
Toxicol. and Chem. (ung.
SCOPE, 1985, John Wiley & Sons Ltd. N.Y.
(1985), Accumulation in aquatic organisms. In: Appraisal of tests to predict the environmental behaviour of chemicals (ung. Ackumulering i vattenorganismer. In: Bedömning av provningar för att förutsäga kemikaliers beteende i miljön). Författad av Sheehman P., Korte F., Klein W. och Bourdeau P.H., del 4.4 sid 243–255. SCOPE, John Wiley & Sons Ltd. N.Y.
ρ s
p s
From Fig.1a the influence of the soil density appears obvious; for example, for a classical centrifugation of 3000 rpm the centrifugation time is approximately 240 min for 1,2 g cm3 soil density, while it is only 50 min for 2,0 g cm3.
Av figur 1 a framgår inverkan av jordens densitet tydligt – vid klassisk centrifugering med 3000 rpm är centrifugeringstiden cirka 240 minuter när jordens densitet är 1,2 g cm3, men bara 50 minuter när densiteten är 2,0 g cm3.
Similarly, from Fig 1b, for a classical centrifugation of 3000 rpm the centrifugation time is approximately 50 min for a length of the mixture of 10 cm and only seven min for a length of 1 cm.
Likaså visar figur 1 b att centrifugeringstiden vid klassisk centrifugering med 3000 rpm är cirka 50 minuter om blandningens höjd är 10 cm men bara 7 minuter om höjden är 1 cm.
var.
varierande
100 kPa 1 bar = 0,1 MPa
100 kPa bar = 0,1 MPa
The power supply is connected to the external terminals of the firing plug and 10 A applied.
Kraftförsörjningen ansluts till tändstiftets yttre anslutningar och 10 A läggs på.
The time between the start of mixing and switching on the power should not exceed 10 minutes.
Tiden mellan det att blandningen påbörjas och inkopplingen av strömmen får inte överstiga 10 minuter.
Lovell, D.P., Anderson, D., Albanese, R., Amphlett, G.E., Clare, G., Ferguson, R., Richold, M., Papworth, D.G. and Savage, J.R.K. (1989).
Lovell, D. P., Anderson, D., Albanese, R., Amphlett, G. E., Clare, G., Ferguson, R., Richold, M., Papworth, D. G. och Savage, J. R. K. (1989), Statistical Analysis of In Vivo Cytogenetic Assays.
Wilson and F.C. Fraser (eds.), Plenum Press, New York.
Wilson och F.C Fraser (red.), Plenum Press, New York.
magnesium sulphate (154 mM) epidermis of skin disc
magnesiumsulfat (154 mM)
The ECVAM international validation study on in vitro tests for skin corrosivity.
(1998), The ECVAM international validation study on in vitro tests for skin corrosivity.
KCl
K Cl
PART III. MODIFIED OECD SCREENING TEST (Method C.4-B)
DEL 3 MODIFIERAT OECD-SCREENINGTEST (metod C.4-B)
PART IV. CO2 EVOLUTION TEST (Method C.4-C)
DEL 4 CO2-UTVECKLING (metod C.4-C)
Hoar and D.J. Randall Eds., Fish Physiology, vol. XIA, Academic press, p. 1-58.
Hoar and D. J. Randall eds., Fish Physiology, Vol. XIA, Academic press, s. 1–58.
Aquatic Toxicology and Hazard Assessment: Fifth Conference, ASTM STP 766, J.G. Pearson, R.B.
Aquatic Toxicology and Hazard Assessment: Fifth Conference, ASTM STP 766, J. G. Pearson, R. B, Foster and W.
Hodson, N.A. Williams, (1988) The estimation of the adsorption coefficient (Koc) for soils by HPLC.
Hodson, N. A. Williams (1988), The estimation of the adsorption coefficient (Koc) for soils by HPLC.
DIN 12790, ISO 387
DIN 12790, ISO 3S7
Ambrose, D.; Lawrenson, I.J.; Sprake, C.H.S. J. Chem.
Ambrose, D.; Lawrenson, I. J.; Sprake, C. H. S, J. Chem.
Comsa, J.K. Fremerey and B. Lindenau.
Comsa, J. K. Fremerey och B. Lindenau, J. Vac.
Vac. Sci.
Sci.
Reehl, D.H. Rosenblatt.
Reehl, D, H. Rosenblatt.
The support material for the column elution method should be inert. Possible materials which can be employed are glass beads and sand.
Till kolonnelueringsmetoden ska ett inert bärarmaterial användas, t.ex. glaspärlor och sand.
Hansch and A.J. Leo, Substituent Constants for Correlation Analysis in Chemistry and Biology, John Wiley, New York, 1979.
Hansch och A. j. Leo, Substituent Constants for Correlation Analysis in Chemistry and Biology, John Wiley, New York, 1979.
Log P and Parameter Database, A tool for the quantitative prediction of bioactivity (C. Hansch, chairman, A.J. Leo, dir.)
Log P and Parameter Database, A took for the quantitative prediction of bioactivity (C. Hasch, chairman, A. J. Leo, dir.)
Haky and A.M. Young, J. Liq.
Haky och A. M. Youg, J. Liq.
Hansch, A. Leo, S.H. Unger, K.H. Kim, D. Nikaitani and E.J. Lien, J. Med.
Hansch, A. Leo, S. H. Unger, K. H. Dim, D. Nikaitani och E. J. Lien, J. Med.
Seydel and K.J. Schaper, Chemische Struktur und biologische Aktivität von Wirkstoffen, Verlag Chemie, Weinheim, New York, 1979.
Seydel och K. J. Schaper, Chemische Struktur und biologische Aktivität von Wirkstoffen, Verlag Chemiw, Weinheim, New York, 1979.
Hansch, A.J. Leo, Substituent Constants for Correlation Analysis in Chemistry and Biology, John Wiley, New York, 1979.
Hansch och A. J. Leo, Substituent Constants for Correlation Analysis in Chemistry and Biology, John Wiley, New York, 1979.
3, 1999, page 342.
3, 1999, sid. 342.
In: Tice, R.R., Costa, D.L., Schaich, K.M. (eds).
In: Tice, R. R., Costa, D. L., Schaich, K. M. (eds).
Mutation Res. 119, p. 403-413.
Mutation Res., 119, s. 403–413.
Mutation Res., 123, p. 61-118.
Mutation Res. 123. s. 61–118.
In: Basic Mutagenicity Tests: UKEMS Part 1 Revised. Ed.
P., Callender, R. D. and Foster, R. (1980), Bacterial Mutation Assays, in: Basic Mutagenicily Tests: UKEMS Part I Revised. ed.
Matsushima, T., Sawamura, M., Hara, K. and Sugimura, T., (1976) A Safe Substitute for Polychlorinated Biphenyls as an Inducer of Metabolic Activation Systems. In: In vitro Metabolic Activation in Mutagenesis Testing, de Serres, F.J., Fouts, J.R., Bend, J.R. and Philpot, R.M. (eds), Elsevier, North-Holland, p. 85-88.
Matsushima, T., Sawamura, M., Hara, K. and Sugimura, T. (1976), A Safe Substitute for Polycholrinated Biphenyls as an Inducer of Metabolic Activation Systems, in:In Vitro Metabolic Activation in MutagenesisTesting, de Serres, F. J., Fouts, J. R., Bend, J. R. and Philpot, R. M. (eds), Elsevier, North-Holland, s. 85–88.
Evans, E.P., Breckon, G. and Ford, C.E., (1964) An Air-Drying Method for Meiotic Preparations from Mammalian Testes. Cytogenetics and Cell Genetics, 3, p. 289-294.
Evans, E. P., Breckon, G. and Ford, C. E. (1964), An Air-drying Method for Meiotic Preparations from Mammalian Testes, Cytogenetics and Cell Genetics, 3, s. 289–294.
However, in the case of dusts and aerosols, this level of control may not be achievable and a wider range would then be acceptable. During the total duration of the study, the day-to-day concentrations should be held as constant as practicable.
En sådan kontrollnivå kan emellertid var omöjlig att uppnå vid test med stoft och vissa aerosoler, och i sådana fall kan större avvikelser accepteras.
Interlaboratory Comparison of Motor Activity Experiments: Implication for Neurotoxicological Assessments.
Tilson och R.C.
10% hydrolysis of a test substance at 50°C corresponds to a half-life of approx. 30 days which corresponds to a value of approx. 1 year at 20°C. No
10 % hydrolys av en testsubstans vid 50 °C motsvarar en halveringstid på ungefär 30 dagar, vilket motsvarar ungefär ett år vid 25 °C.
Litchfield, J. T. andWilcoxon, F., A simplified method of evaluation dose effect experiments. I. Pharm.
Litchfield, J. T. och Wilcoxon J.(1949), A simplified method of evaluating dose-effect experi ments, J. Pharm.