natgillin/translations-raw huggingface dataset:
An objective of the egg and sac-fry test is to compare the non-zero concentrations with the control, i.e. to determine the LOEC.
Marjateradega ja rebukotiga vastsete uuringu eesmärk on võrrelda nullist erineva kontsentratsiooniga lahuseid kontrollkatsega, st kindlaks määrata LOEC.
Biometry, the Principles and Practice of Statistics in Biological Research, W.H.
Biometry, the Principles and Practice of Statistics in Biological Research, W.
(hrs)
(tundides)
Embryo
Embrüo
March, 1993.
March 1993.
at the time point ti
ajahetkel ti
g-1cm3 the adsorption test
g–1cm3 ruumala
Preferably, the same time intervals as in the adsorption kinetics experiment should be used; however, the total time may be extended as appropriate in order the system to reach desorption equilibrium.
Eelistatavalt tuleks kasutada samasid ajavahemikke, mida kasutati adsorptsioonikineetika katses; siiski võib kogu aeg vajaduse korral pikeneda, et süsteem jõuaks desorptsiooni tasakaaluoleku püstitamiseni.
In every experiment (one soil, one solution) one blank is run.
Iga katse (üks muld, üks lahus) korral tehakse üks pimekatse.
g-1)(cm3 substance in the soil phase and the mass concentration of the substance in the aqueous solution, under the test conditions, when adsorption equilibrium is reached.
g-1)(cm3 aine massikontsentratsiooni vaheline suhe katsetingimustes, kui adsorptsiooni tasakaaluolek on püstitunud.
g-1)(cm3 g);
g-1)(cm3 etega saadud väärtusi;
g-1)(cm3 stribution coefficient Kd to the content of organic carbon of the soil sample:
g-1)(cm3 jaotusteguri Kd mullaproovi orgaanilise süsiniku sisaldusega:
g-1)(cm3 s, the ratio between the content of the substance remaining in the soil phase and the mass concentration of the desorbed substance in the aqueous solution, when desorption equilibrium is reached:
g-1)(cm3 ine sisalduse ja vesilahuses desorbeerunud aine massikontsentratsiooni vaheline suhe, kui desorptsiooni tasakaaluolek on püstitunud:
Bailey G.W., J.L. White and Y.
Bailey G. W., J. L. White and Y.
2 Soils Selection of optimal soil/solution ratios
2 Soils
Determination of equilibrium time Check for adsorption on the vessel surface
Selection of optimal soil/solution ratios
Tier 1 Equilibrium plateau is achieved? Yes Adsorption kinetics
Check for adsorption on the vessel surface
Tier 2 If mass balance < 90%, test substance is unstable in the time scale of the test.
Check for the stability by means of parental mass balance
The test test can continue by analysing both phases (soil and aqueous solution).
Equilibrium plateau is achieved? Yes Yes No
Gerstl and Mingelgrin (1984) (66)
Gerstl ja Mingelgrin (1984) (66)
Vowles and Mantoura (1987) (67)
Vowles ja Mantoura (1987) (67)
g-1cm3 CaCl2 sol. to equilibrate the soil
g-1cm3 enevat parandust
O — Si
O - Si
The method can be used for mixtures which give unresolved elution bands.
Meetodit saab kasutada segude puhul, mille korral ei ole võimalik elueerimisribasid eristada.
In such a case, upper and lower limits of the log Koc values of the compounds of the test mixture should be stated.
Sellisel juhul tuleks märkida ära uuritavate ainete segu ühendite log Koc väärtuste ülemine ja alumine piir.
Triazoxide
Triasoksiid
UBA R & D Report No. 106 01 044 (1994).
UBA R&D Report No 106 01044 (1994)
However, it may be advisable to increase the number of sampling occasions during the first week (e.g. three sets of measurements) to ensure that the test concentrations are remaining stable.
Siiski võib olla soovitatav suurendada proovide võtmise arvu esimesel nädalal (nt kolm mõõtmist), et tagada uuritavate kontsentratsioonide püsivuse säilimine.
In these types of test, the flow-rate of diluent and test substance should be checked daily.
Seda tüüpi katsete puhul tuleks lahjendusvedeliku ja uuritava aine voolukiirust kontrollida iga päev.
Thermische Analyse, Begriffe
Thermisches Analyse, Begriffe
where tn, tn-1 are the times required for a given number N of revolutions.
kus tn ja tn-1 on N arvu pöörete tegemiseks kulunud ajavahemikud.
These time intervals tn and tn-1 succeed one another, and tn > t n-1.
Need ajavahemikud järgnevad üksteisele ja tn > tn-1.
10 = Fritted bubbler
Paagutatud mullitaja
Figure 6b
Joonis 6b
An example of system for the determination of vapour pressure by the gas saturation method, with a capillary placed after the saturation chamber
Näitlik küllastuskolonni järgi ühendatud kapillaartoruga süsteem aururõhu määramiseks gaasi küllastamise meetodi kohaselt
(interactious terms) where fi represents the different molecular fragment constants and ai the frequency of their occurrence in the molecule under investigation.
kus fi tähistab erinevaid rühmakonstante ja ai nende esinemissagedust uuritavas molekulis.
The total mass used to fill the tube to the 55 mm level is determined and two further increments, each tamped with 80 N force, are added.
Määratakse hülsi 55 mm tasemeni täitmiseks vajalik ainekogus ja lisatakse veel kaks lisakogust, mis kumbki 80 N jõuga tampimisel tihendatakse.
Material is then either added with tamping, or taken out, as required, to leave the tube filled to a level 15 mm from the top.
Seejärel ainet vastavalt vajadusele kas lisatakse ja tambitakse või eemaldatakse, nii et hülss täitub 15 mm kõrguseni ülaäärest.
A series of six tests are performed with a 360 N loading.
360 N koormusega tehakse kuuest katsest koosnev katseseeria.
If a positive event is obtained during these six tests, a further series of six tests must be performed with a 120 N loading.
Kui nende kuue katse käigus saadakse positiivne tulemus, tehakse 120 N koormusega veel üks kuuest katsest koosnev katseseeria.
In other apparatus, the sample is compared with the chosen reference substance using an established procedure (e.g. up-and-down technique, etc.).
Muudes seadmetes võrreldakse proovi tunnustatud meetodi (nt üles-alla tehnika jne) abil valitud võrdlusainega.
ignition temperature
süttimis- temperatuur
US CPSC
USA CPSC
Start
Algus
Elliot, B.M., Combes, R.D., Elcombe, C.R., Gatehouse, D.G., Gibson, G.G., Mackay, J.M. and Wolf, R.C., (1992). Report of UK Environmental Mutagen Society Working Party.
Elliot, B. M., Combes, R. D., Elcombe, C. R., Gatehouse, D. G., Gibson, G. G., Mackay, J. M. and Wolf, R. C. (1992), Report of UK Environmental Mutagen Society Working Party.
Adler, I.D., (1984) Cytogenetic Tests in Mammals. In: Mutagenicity Testing: a Practical Approach. S. Venitt and J.M. Parry (Eds).
Adler, I. D. (1984), Cytogenetic Tests in Mammals, in: Mutagenicity Testing: a Practical Approach, S. Venitt and J. M. Parry (eds), IRL Press, Oxford, Washington D. C, pp.
Richold, M., Chandley, A., Ashby, J., Gatehouse, D.G., Bootman, J. and Henderson, L., (1990) In Vivo Cytogenetic Assays. In: D.J. Kirkland (Ed.)
Richold, M., Chandley, A., Ashby, J., Gatehouse, D. G., Bootman, J. and Henderson, L. (1990), In vivo Cytogenetic Assays, in: D. J. Kirkland (ed.), Basic Mutagenicity Tests, UKEMS Recommended Procedures.
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) Statistical Analysis of In Vivo Cytogenetic Assays. In: D.J. Kirkland (Ed.)
Lovell, D. P., Anderson, D., Albanese, R., Amphlett, G. E., Clare, G., Ferguson R., Richold, M., Pap-worth, D. G. and Savage, J. R. K. (1989), Staticical Analysis of In Vivo Cytogenetic Assays, in: D. J. Kirkland (ed.), Statistical Evaluation of Mutagenicity Test Data.
Statistical Evaluation of Mutagenicity Test Data. UKEMS Sub-Committee on Guidelines for Mutagenicity Testing.
UKEMS Sub-Committee on Guidelines for Mutagenicity Testing.
Kier, L.D., Brusick D.J., Auletta, A.E., Von Halle, E.S., Brown, M.M., Simmon, V.F., Dunkel, V., McCann, J., Mortelmans, K., Prival, M., Rao, T.K. and Ray V., (1986) The Salmonella typhimurium/Mammalian Microsomal Assay: A Report of the U.S. Environmental Protection Agency Gene-Tox Program.
Kier, L. D., Brusick D. J., Auletta, A. E., Von Halle, E. S., Brown, M. M., Simmon, V. F., Dunkel, V., McCann, J., Mortelmans, K., Prival, M., Rao, T. K. and Ray V. (1986), The Salmonella typhimurium/Mammalian Microsomal Assay: A Report of the U. S. Environmental Protection Agency Gene-Tox Program, Mutation Res., 168, pp.
Matsushima, M., Sugimura, T., Nagao, M., Yahagi, T., Shirai, A. and Sawamura, M., (1980) Factors Modulating Mutagenicity Microbial Tests. In: Short-term Test Systems for Detecting Carcinogens. Ed.
Matsushima, M., Sugimura, T., Nagao, M., Yahagi, T., Shirai, A. and Sawamura, M. (1980), Factors Modulating Mutagenicity Microbial Tests, in: Short-term Test Systems for Detecting Carcinogens, ed.
Bridges (1984) The Fluctuation Test in Bacteria. In: Handbook of Mutagenicity Test Procedures. 2nd Edition. Ed.
(1984), The Fluctuation Test in Bacteria, in: Handbook of Mutagenicity Test Procedures, 2nd Edition, ed.
V. Results from the Testing of 311 Chemicals. Environ.
V. Results from the Testing of 311 Chemicals, Environ.
Simmon, V., Kauhanen, K. and Tardiff, R.G., (1977) Mutagenic Activity of Chemicals Identified in Drinking Water. In Progress in Genetic Toxicology, D. Scott, B. Bridges and F. Sobels (Eds.)
Simmon, V., Kauhanen, K. and Tardiff, R. G. (1977), Mutagenic Activity of Chemicals Identified in Drinking Water, in Progress in GeneticToxicology, D. Scott, B. Bridges and F., Sobels (eds.)
Matsushima, T., Sawamura, M., Hara, K. and Sugimura, T., (1976) A Safe Substitute for Polychlorinated Biphenyls as an Inducer or Metabolic Activation Systems. In: ‘In vitro metabolic Activation in Mutagenesis Testing’ Eds.
Matsushima, T., Sawamura, M., Hara, K. and Sugimura, T. (1976), A Safe Substitute for Polychlori-nated Biphenyls as an Inducer or Metabolic Activation Systems, in: In vitro Metabolic Activation in Mutagenesis Testing, eds.
Clive, D., McCuen, R., Spector, J.F.S., Piper, C. and Mavournin, K.H., (1983) Specific Gene Mutations in L5178Y Cells in Culture. A Report of the U.S. Environmental Protection Agency Gene-Tox Program.
Clive, D., McCuen, R., Spector, J. F. S., Piper, C. and Mavournin, K. H. (1983), Specific Gene Mutations in L5178Y Cells in Culture.
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, Batson, A. G. and Clive, D. (1984), Procedure for the L5178Y/TK+/„— TK+/" Mouse Lymphoma Cell Mutagenicity Assay, in: Kilbey, B. J. et al (eds.)
Applegate, M.L., Moore, M.M., Broder, C.B., Burrell, A. and Hozier, J.C., (1990) Molecular Dissection of Mutations at the Heterozygous Thymidine Kinase Locus in Mouse Lymphoma Cells. Proc.
Applegate, M. L., Moore, M. M., Broder, C. B., Burrell, A. and Hozier, J. C. (1990), Molecular Dissection of Mutations at the Heterozygous Thymidine Kinase Locus in Mouse Lymphoma Cells, Proc.
Route of administration Exposure may be oral, by injection or by exposure to gases or vapours.
Aineid võib loomadele manustada kas suukaudselt, süstevedelikuga või eksponeerides neid selle aine gaasidele või aurudele.
Adler, I.D., (1986) Clastogenic Potential in Mouse Spermatogonia of Chemical Mutagens Related to their Cell-Cycle Specifications. In: Genetic Toxicology of Environmental Chemicals, Part B: Genetic Effects and Applied Mutagenesis, Ramel, C., Lambert, B. and Magnusson, J. (Eds.)
Adler, I. D., (1986), Clastogenic Potential in Mouse Spermatogonia of Chemical Mutagens Related to their Cell-Cycle Specifications, in: Genetic Toxicology of Environmental Chemicals, Part B: Genetic Effects and Applied Mutagenesis, Ramel, C, Lambert, B. and Magnusson, J. (eds) Liss, New York, pp.
Richold, M., Ashby, J., Chandley, A., Gatehouse, D.G. and Henderson, L., (1990) In Vivo Cytogenetic Assays, In: D.J. Kirkland (Ed.)
Richold, M., Ashby, J., Chandley, A., Gatehouse, D. G. and Henderson, L. (1990), In Vivo Cytogenetic Assays, in: D. J. Kirkland (ed.), Basic Mutagenicity Tests, UKEMS Recommended Procedures.
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) Statistical Analysis of In Vivo Cytogenetic Assays In: D.J. Kirkland (Ed.) Statistical Evaluation of Mutagenicity Test Data.
Lovell, D. P., Anderson, D., Albanese, R., Amphlett, G. E., Clarc, G., Ferguson, R., Richold, M., Pap-worth, D. G. and Savage J. R. K. (1989), Statistical Analysis of In Vivo Cytogenetic Assays, in: D. J. Kirkland (ed.), Statistical Evaluation of Mutagenicity Test Data.
At least three dose levels are required with a controle or a vehicle control if a vehicle is used. The exposure period should be at least six hours per day.
Kasutada tuleb vähemalt kolme erinevat annust saavat rühma ja ühte kontrollrühma või vehiikli kontrollrühma, kui kasutatakse vehiiklit.
The temperature in the experimental animal room should be 22 oC (± 3o) for rodents and 18 oC (± 3o) for rabbits.
Loomade katseruumi temperatuur peaks närilistel olema 22 oC (± 3o) ja küülikutel 18 oC (± 3o).
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.
Kui spermatogeneesi käsitlevad andmed on olemas varasemast, korduvaid annuseid kasutavast uurimusest, mille kestus on piisav, nt 90päevane uurimus, ei ole vaja lisada hindamisse P-põlvkonna isasloomi.
It is recommended, however, that samples or digital recordings of sperm of the P generation are saved, to enable later evaluation.
On siiski soovitav, et P-põlvkonna spermaproove või digitaalseid salvestusi säilitatakse hilisema hindamise tarbeks.
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.
Arvutamised tuleks teha kõikide valitud isasloomade osarühmade kõikides annuserühmades pärast loomade surmamist, välja arvatud juhul, kui tehakse video- või digitaalsalvestusi või kui proovid külmutatakse ja analüüsitakse hiljem.
This area is practicable with rats of 200-250 g bodyweight.
Selline ala on saavutatav 200–250 g kaaluvatel rottidel.
After preparation, the animals are returned to metabolism cages.
Pärast loomade ettevalmistamist pannakse nad tagasi metabolismi uurimise puuridesse.
Testing Method B.45.
Testing Method B.45.
Three types of procedure can be used: Static test:
Kasutada võib kolme tüüpi katseskeemi.
CaCl2, 2H2O
, 2H2O
MgSO4, 7H2O
, 7H2O
SeO3
Na2SeO3
MITI
MITI katse
Dilution water
Lahjendusvesi
Deionised or distilled water, free from inhibitory concentrations of toxic substances (e.g. Cu ++ ions) is used.
Kasutatakse deioniseeritud või destilleeritud vett, mis ei sisalda inhibeerivates kontsentratsioonides mürgiseid aineid (nt Cu++ ioone).
It must contain no more than 10 % of the organic carbon content introduced by the test material.
Orgaanilise süsiniku sisaldus ei tohi olla suurem kui 10 % testainest tulenevast orgaanilise süsiniku sisaldusest.
The high purity of the test water is necessary to eliminate high blank values.
Vee kõrge puhtusaste aitab välistada kõrgete tulemuste saamise nullproovidega.
PART II. DOC DIE-AWAY TEST (Method C.4-A)
II OSA DOC KÕRVALDAMISE KATSE (meetod C.4-A)
The degree of biodegradation is calculated by expressing the concentration of DOC removed (corrected for that in the blank inoculum control) as a percentage of the concentration initially present.
Arvutatakse biolagundumise määr, väljendades kõrvaldatud DOC kontsentratsiooni (mida on parandatud inokulaadiga nullproovi vastava väärtuse võrra) protsendina algkontsentratsioonist.
ThODmg O2
ThODO2
% COD =BODmg O2
% COD =BODO2
PART VI. CLOSED BOTTLE TEST (Method C.4-E)
VI OSA KINNISE PUDELI KATSE (meetod C.4-E)
PART VII. M.I.T.I. TEST (Method C.4-F)
VII OSA MITI KATSE (meetod C.4-F)
ThOD mg O2
ThOD O2
0,05 M borax +0,1 N HCl
0,05 M booraks + 0,1 N HCl
Test organisms should be adult Eisenia foetida (see note in Appendix) (at least two months old with clitellum) wet weight 300 to 600 mg. (For breeding method see Appendix.)
Katseorganismideks peavad olema täiskasvanud Eisenia foetida eksemplarid (vt märkust liites) (vähemalt kahe kuu vanused, klitellumiga) kaaluga 300 kuni 600 mg (kasvatamise meetodeid vt liitest).
Bouche. M. B., 1972, Lombriciens de France, Ecologie et Systematique, Institut National de la Recherche Agronomique, p. 671.
Bouche, M. B., 1972, Lombriciens de France, Ecologie et Systematique, Institut National de la Recherche Agronomique, 671 pp.
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.
5,5-dikloorfenooli lahuse saab näiteks valmistada 0,5 g 3,5-dikloorfenool lahustamisel 10 ml 1 M NaOH lahuses, saadud lahus lahjendatakse ligikaudu 30 ml destilleeritud veega, lisades samaaegsel segamisel 0,5 M H2SO4 kuni sademe tekke alguseni – vajalik võib olla ligikaudu 8 ml 0,5 M H2SO4 lahuse lisamine – ja lõpuks lahjendatakse segu destilleeritud veega kuni ühe liitrini.
The pH should then be in the range 7 to 8.
Saadud lahuse pH peaks olema vahemikus 7 kuni 8.
Alternative models for describing the bioconcentration of organics in fish.
Alternative models for describing the bioconcentration of organics in fish.
< 20 mg/l
< 20 mg/l
< 2 mg/l
< 2 mg/1
< 1 μg/l
< 1μg/l
P ' % survival observed in the test concentration
P ' uuritava kontsentratsiooni korral täheldatud ellujäämise protsent
C % survival in the control
C ellujäämine kontrollkatses
silt loam
ladestunud saviliiv
loam
saviliiv
loamy sand
saviliivane liiv
clay loam/clay
gleistunud saviliiv/savi
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.
Roberts and P.C. Kearney).
Roberts and P. C. Kearney).
Briggs G.G. (1969) ‘Molecular structure of herbicides and their sorption by soils’.
Briggs G. G. (1969), „Molecular structure of herbicides and their sorption by soils”.
Grover R., and Hance R.J. (1970) ‘Effect of ratio of soil to water on adsorption of linuron and atrazine’.
Grover R., and Hance R. J. (1970), „Effect of ratio of soil to water on adsorption of linuron and atrazine”.
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.
Nendel osakestel, mille suurus on alla 0,2 μm, võib olla tähtis mõju kogu aine adsorptsioonimehhanismile mulla suspensioonis.
When centrifugation is performed as described above, colloids remain in the aqueous phase and are subjected to analysis together with the aqueous phase.
Kui tsentrifuugitakse eespool kirjeldatud viisil, jäävad kolloidid vesifaasi ja neid analüüsitakse koos vesifaasiga.
Chiou, P.E. Porter, D.W.
C T. Chiou, P. E. Porter, D.W.
Standard recommended practices for testing polymeric powder coatings
76 Standard recommended practices for testing polymeric powder coatings
Dibenzyl
Dibensüül
Shock test apparatus
Löögikatse seade
toothed rack
hammaslatt
Fig. 4b Fall-hammer, lower part
Joonis 4b. Langev vasar, alumine osa
However, if further confirmation of the classification is required, an optional supplementary procedure may be conducted, as follows.
Kui on siiski nõutav klassifitseerimise täiendav kinnitamine, võib teha järgmise valikulise lisaprotseduuri.
Krahn, D.F., Barsky, F.C. and McCooey, K.T., (1982) CHO/HGPRT Mutation Assay: Evaluation of Gases and Volatile Liquids. In: Tice, R.R., Costa, D.L., Schaich, K.M. (eds).
Krahn, D. F., Barsky, F. C. and McCooey, K. T. (1982), CHO/HGPRT Mutation Assay: Evaluation of Gases and Volatile Liquids, in: Ticc, R. R., Costa, D. L., Schaich, K. M. (eds), Genotoxic Effects of Airborne Agents, New York, Plenum, pp.
Male Chinese hamsters and mice are commonly used.
Enamasti kasutatakse isaseid hiina hamstreid ja hiiri.
However, males of other appropriate mammalian species may be used.
Võib kasutada ka muude sobivate imetajate liikide isaseid loomi.
Eugenol
eugenool
National Institute of Environmental Health Sciences, Research Triangle Park, NC, USA. http://iccvam.niehs.nih.gov/docs/guidelines/validate.pdf.
National Institute of Environmental Health Sciences, Research Triangle Park, NC, USA. http://iccvam.niehs.nih.gov/docs/guidelines/validate.pdf
ethanol
etanool
Norfloxacin
norfloksatsiin
When possible, numerical results should be evaluated by an appropriate and generally acceptable statistical method. The statistical methods should be selected during the design of the study.
Võimaluse korral tuleks hinnata numbrilisi tulemuse sobiva ja üldiselt heakskiidetud statistilise meetodi abil Statistilised meetodid tuleks valida uuringu väljatöötamise ajal.
ACUTE IMMOBILISATION TEST
LIIKUMISVÕIME AKUUTSE PÄRSSIMISE KATSE
Test (mg)
Katselahus (mg)
2 NH4Cl + 4 O2 = 2 HNO3 + 2 HCl + 2 H2O
2 HN4Cl + 4 O2 = 2 HNO3 + 2 HCl + 2 H2O
K2HPO4:
K2HPO4
Accumulation in Aquatic organisms.
Accumulation in Aquatic organisms.
Symbol
Tähis
Eberle, (1976) ‘Experimental models for studying the persistence of pesticides in soils’. Proc.
Proc. BCPC Symposium: Persistence of Insecticides and Herbicides, pp.
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, pp.297-325, ACS Symp.
Standard method for assessing the thermal stability of chemicals by methods of differential thermal analysis
Standard method for asseying the thermal stability of chemicals by methods of differential thermal analysis
133 Pa 1 mm Hg = 1 Torr
133 Pa 1mm Hg=1 Torr
Buffering is recommended. Care must be taken to avoid salt precipitation and column deterioration which occur with some organic phase/buffer mixtures.
Hoolikalt tuleks vältida soolade sadestumist ja kolonni omaduste halvenemist, mida tuleb ette mõningate orgaanilise faasi/puhverlahuse segude puhul.
sample under test, approximately 10 mm3
uuritav proov, ligikaudu 10 mm3
Fig. 5b Starting position of peg on sample
Joonis 5b Pulga algpositsioon proovil
Matsushima, T., Sawamura, M., Hara, K. and Sugimura, T., (1976) A Safe Substitute for Polychlorinated Biphenyls as an Inducer of Metabolic Activation Systems. In: de Serres, F.J., Fouts, J.R., Bend, J.R. and Philpot, R.M.
Matsushima, T., Sawamura, M., Hara, K. and Sugimura, T. (1976), A. Safe Substitute for Polychlori-nated Biphenyls as an Inducer of Metabolic Activation Systems, in: de Serres, F. J. Fouts, J. R. Bend, J. R. and Philpot, R. M. (eds), In Vitro Metabolic Activation in Mutagenesis Testing, Elsevier, North-Holland, pp.
MacGregor, J.T., Heddle, J.A. Hite, M., Margolin, G.H., Ramel, C., Salamone, M.F., Tice, R.R., and Wild, D., (1987) Guidelines for the Conduct of Micronucleus Assays in Mammalian Bone Marrow Erytrocytes.
MacGregor, J. T., Heddle, J. A. Hite, M., Margolin, G. H., Ramel, C, Salamone, M. F., Tice, R. R., and Wild, D. (1987), Guidelines for the Conduct of Micronucleus Assays in Mammalian Bone Marrow Erythrocytes, Mutation Res., 189, pp.
Mahon, G.A.T., Green, M.H.L., Middleton, B., Mitchell, I., Robinson, W.D. and Tweats, D.J., (1989) Analysis of Data from Microbial Colony Assays. In: UKEMS Sub-Committee on Guidelines for Mutagenicity Testing.
Mahon, G. A. T., Green, M. H. L., Middleton, B., Mitchel, I., Robinson, W.