natgillin/translations-raw huggingface dataset:
2,4-2,6 (14, 19)
17, 227–231.
0,85 -1,2 (14, 19)
Bull.
0,06-0,08 (4, 14)
Bodenkundliche Gesellschaft Schweiz 7, 26–33.
14-21
Priloga I k Direktivi Komisije 95/36/ES z dne 14. julija 1995 o spremembi Direktive Sveta 91/414/EGS o dajanju fitofarmacevtskih sredstev v promet, UL L 172, 22.7.1995, str. 8.
25-61 (14, 29)
Weber, J. B., in Peeper, T. F. (1977).
10-20 (6, 21)
In Research Methods in Weed Science, druga izdaja (B. Truelove, ur.).
10-20 (6, 10)
Weber, J. B., Swain, L. R., Strek, H. J., in Sartori, J. L. (1986).
14-18
Weed Sci., Champaign, IL, 190–200.
0,9-1,6
Oliveira idr.
0,5-0,7 (14, 19, 29)
7, 177–217.
0,52-0,6 (14, 30)
Hamaker, J. W. (1975).
5-8 (4, 14, 29)
Guth, J. A. (1985).
1,8-2,5 (14)
Schr.Reihe Verein WaBoLu, 68, 91–106.
2,1 -2,3 (14, 19)
Helling, C. S. (1971).
1,3-1,5 (4, 14, 19)
35, 743–748.
41 -56 (19, 29)
Evropski standard EN 335 – Del 1:
0,8 — 1,5 (14, 19)
Trajnost lesa in lesnih materialov – Definicije razredov uporabe – Del 1:
POST (4, 22 — 26)
American Society for Testing and Materials Standards, ASTM D 1193–77 Type II – 1983.
3(19)
je grafični prikaz bioakumulacijskih faktorjev v vseh obdobjih vzorčenja v odvisnosti od časa vzporeden s časovno osjo, (ii) se tri zaporedne analize BAF na vzorcih, odvzetih v razmiku najmanj dveh dni, druga od druge ne razlikujejo za več kot 20 % in (iii) ni statistično značilnih razlik med tremi obdobji vzorčenja (na podlagi statističnih primerjav, npr. analize variance in regresijske analize).
Academic Press, Toronto
Obdobje za uravnoteženje se uporablja za porazdelitev preskusne snovi med trdno fazo, porno vodo in vodo nad usedlino;
Boutin, C., Lee, H-B., Peart, T., Batchelor, P.S., & Maguire, R.J.
Vsak teden je treba izmeriti raztopljeni kisik, trdoto vode, temperaturo in pH.
Breeze, V., Thomas, G., & Butler, R. 1992.
Franke, C., Studinger, G., Berger, G., Böhling, S., Bruckmann, U., Cohors-Fresenborg, D., in Jöhncke, U. (1994).
Buhler, D.D.
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Clay, P.A.
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Fletcher, J.S., Johnson, F.L., & McFarlane, J.C. 1990.
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Kjaer, C. 1994.
An interpolation estimate for chronic toxicity:
Klingaman, T.E., King, C.A., & Oliver, L.R.
ZDA
Marrs, R.H., Williams, C.T., Frost, A.J., & Plant, R.A.
12,750 g.
Marrs, R.H., Frost, A.J., & Plant, R.A.
6,082 g.
Marrs, R.H., Frost, A.J., Plant, R.A., & Lunnis, P. 1993.
2,205 g.
(Herbiseed).
Take metode uporabljajo izmerjene podatke in naključno ponovno vzorčenje, ki se izbere z generatorjem naključnih števil, da se oceni empirična porazdelitev variance.
USEPA.
Chem.11, 1485–1494.
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celica in dodatki za merjenje koncentracije raztopljenega kisika, primerna kisikova elektroda, zaprta celica brez prostora nad fazno mejo plin-kapljevina, v kateri bo vzorec, in zapisovalnik (npr. št. 7, 8 in 9 na sliki 1 v Dodatku 2);
350 ± 50 ppm;
US EPA Report, št. EPA-600/3-77 108.
The vehicle is sprayed on or mixed with a small amount, for example 2,5 g, of fine quartz sand.
September 1977.
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).
Considerations in the assessment of toxicity using duckweeds.
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PREDHODNO IN NAKNADNO (28, 31, 34)
355-361
PREDHODNO IN NAKNADNO
Holm, S., (1979):
PREDHODNO IN NAKNADNO (6, 10, 28, 31)
Jonckheere, A. R. (1954);
PREDHODNO IN NAKNADNO (28, 31)
Terpstra, T. J. (1952);
PREDHODNO IN NAKNADNO (18, 25, 31)
Shirley, E. A. (1979);
PREDHODNO IN NAKNADNO (3, 21, 28, 31)
Sokal, R.R. and F.J.
PREDHODNO (31)
2nd edition.
PREDHODNO IN NAKNADNO (6, 28)
Christensen, E.R., (1984).
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+44 1229581137
After shaking, the suspension is left to settle for at least 2 hours but not for longer than 24 hours.
Ecotoxicology, 12:271–285.
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).
Ecotoxicology, 13:349–369.
Enchytraeus crypticus (Westheide & Graefe 1992):
Environmental Pollution, 69:223–235.
Enchytraeus buchholzi (Vejdovsky 1879):
Uredila Esser, G., in Overdieck, D., str. 497–508.
Enchytraeus bulbosus (Nielsen & Christensen 1963):
Determination of effects on reproduction, št. 11268-2, ISO, Ženeva.
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;
John Wiley and Sons, Chichester, 73–94.
Posthuma, L., Baerselmann, R., Van Veen, R.P.M. and Dirven-Van Breemen, E.M.
Biometrics 20, 482–491.
Phillips, C.T., Checkai, R.T. and Kuperman, R.G.
25, 25–32.
At least four replicates per treatment?
Determination of effects on reproduction, št. 11268-2.
No success
ISO, Ženeva.
Yes
SETAC Press, 456 str.
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Finney, D. J. (1978).
Earlier work in the UK (6)(7) described a manometric method using undiluted digesting sludge, plus raw sewage sludge as the substrate, in 500 ml flasks; the apparatus was cumbersome and the stench of the raw sludge was offensive.
Miller, R. G., Jr.
micro syringes, for the gas-tight connection of the pressure transducer (see paragraph 12(c)) to the headspace in the bottles (see paragraph 12(b)); also for adding insoluble liquid test materials into the bottles;
Teil, G. Fischer, Jena, 523 str.
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;
241–249.
ISO (2000) Ring test of ISO 13 641-1 and ISO 13 641-2.
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HMSO (1986) Determination of the inhibitory effects of chemicals and waste waters on the anaerobic digestion of sewage sludge.
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Kawahara K, Yakabe Y, Chida T, and Kida K (1999).
Applied Soil Ecology 36, 130– 135.
International Organization for Standardization (1997) ISO 11 923 Water Quality — Determination of suspended solids by filtration through glass-fibre filters.
Nature 401, 581–583.
A.10 Paragraph 17.
Razvoj vrste Hypoaspis (Geolaelaps) aculeifer pri temperaturi 20 °C (odstranitev = samice, uporabljene za preskus).
Test substrate
Oregon State University Book Stores, Inc., 509 str.
Using a 500 μm mesh, most of the sediment particles will pass the sieve very quickly; however, sieving should be done quickly, in order to prevent the worms from crawling into or through the mesh.
Toxicological Sciences;
Using a 250 μm mesh will prevent the worms from crawling into or through the mesh; however, care should be taken that as little as possible of the sediment particles is retained on the mesh.
Ankley, G. T., Jensen, K. M., Makynen, E. A., Kahl, M. D., Korte, J. J., Homung, M. W., Henry, T. R., Denny, J. S., Leino, R. L., Wilson, V. S., Cardon, M. C., Hartig, P. C., Gray, L. E. (2003).
chemical identification data (common name, chemical name, structural formula, CAS number, etc.) including purity and analytical method for quantification of test chemical;
Smith, R. J. F. 1974.
source of the test chemical, identity and concentration of any solvent used.
Za namen tega preskusa je treba visoko preskusno koncentracijo določiti z mejo topnosti preskusne kemikalije, najvišjo tolerančno koncentracijo (MTC) za akutno strupene kemikalije ali 100 mg/l (kar koli je najnižje).
Part I — IV.
Saturation units for use in aquatic bioassays.
OECD (1992a).
Hutchinson, T. H., Shillabeer, N., Winter, M. J., Pickford, D. B. (2006).
Phipps, G.L., Ankley, G.T., Benoit, D.A. and Mattson, V.R.
Simple techniques for rearing Collembola, Symphyla and other small soil inhabiting arthropods.
U.S. EPA (2000).
V:
BBA (1995).
Suedel, B. C., in Rodgers, J. H. (1994).
ASTM International (2004).
The comparison of several dose levels with a zero dose control.
Egeler, Ph., Meller, M., Schallnaß, H.J.
Jungmann, D., Bandow, C., Gildemeister, T., Nagel, R., Preuss, T. G., Ratte, H. T., Shinn, C., Weltje, L., in Maes, H. M. (2009).
In co-operation with R. Nagel and B. Karaoglan.
Rao, J. N. K., in Scott, A. J. (1992).
Environment Canada (2003).
Bruce, R. D., in Versteeg, D. J. (1992).
Nikkilä A., Halme A., Kukkonen J.V.K.
Benoit, D. A., Sibley, P. K., Juenemann, J. L., in Ankley, G. T. (1997).
Schubauer-Berigan M.K., Dierkes J.R., Monson P.D.
Uporabljeni postopek (npr. pretočni semi-statični/obnavljajoči; načrt preskusa, vključno s preskusnimi koncentracijami, metodo priprave založnih raztopin (v prilogi), pogostostjo obnavljanja (navesti je treba sredstvo za raztapljanje in njegovo koncentracijo, če se uporabi),
Ingersoll, C.G., Ankley, G.T., Benoit D.A., Brunson, E.L., Burton, G.A., Dwyer, F.J., Hoke, R.A., Landrum, P. F., Norberg-King, T. J. and Winger, P.V.
Direktiva 2010/63/EU Evropskega parlamenta in Sveta z dne 22. septembra 2010 o varstvu živali, ki se uporabljajo za znanstvene namene.
Leppänen, M.T.
30,75 μl
Brunson, E.L., Canfield, T.J., Ingersoll, C.J.
Nyholm, N., in Kristensen, P. (1987).
Rodriguez, P. & Reynoldson, T.B.
Osnutek mednarodnega standarda ISO/DIS 8245, 16. januar, 1986.
Bioaccumulation of 14C-17α-ethinylestradiol by the oligochaete Lumbriculus variegatus in artificial sediment.
(Objavljeno tudi kot ECETOC Technical Report No.
Oetken, M., K.-U.
Shelton D. R., in Tiedje, J. M. (1984).
Brinkhurst, R.O.
Za nadzor obnovljivosti postopka polnjenja se določi skupna teža tal v kolonah [25], teže ponovitvenih kolon morajo biti podobne.
Environment Canada (1995).
odstranitev ponovitev za vzorčenje, nadzor dovajanja zraka, obnašanja črvov in kakovosti vode (glej odstavek 56), odvzem vzorcev vode, usedline in črvov za določitev koncentracije preskusne snovi
Brooke, L.T., Ankley, G.T., Call, D.J.
Suspenzija se vsaj dva dni kondicionira z rahlim mešanjem pri 20 ± 2 °C, da se stabilizira pH in vzpostavi stabilna mikrobna komponenta. pH se znova izmeri in po potrebi s CaCO3 uravna na 6,0 ± 0,5.
OECD 2006.
ASTM International 2004 Annual Book of Standards.
Liebig M., Meller M. & Egeler P. (2004).
Urad za publikacije Evropskih skupnosti, Luksemburg.
Sedimenttoxizitätstests mit aquatischen Oligochaeten — Einfluss verschiedener Futterquellen im künstlichen Sediment auf Reproduktion und Biomasse von Lumbriculus variegatus.
Egeler, Ph., Meller, M., Schallnaß, H. J., in Gilberg, D. (2006).
New tables for multiple comparisons with a control.
Effects of tributyltin within a Thalassia seagrass ecosystem.
Biometrics 28, 519 531.
Leppänen, M. T., in Kukkonen, J. V. K. (1998).
Dissolve 11,76 g CaCl2·2H2O in deionised water; make up to 1 l with deionised water
Factors affecting feeding rate, reproduction and growth of an oligochaete Lumbriculus variegatus (Müller).
Dissolve 4,93 g MgSO4·7H2O in deionised water; make up to 1 l with deionised water
Relationship between reproduction, sediment type and feeding activity of Lumbriculus variegatus (Müller):
Dissolve 2,59 g NaHCO3 in deionised water; make up to 1 l with deionised water
Evaluation of selected lipid methods for normalising pollutant bioaccumulation.
OECD (1992).
Habilitationsschrift, Johannes Gutenberg-Universität Mainz, Nemčija.
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;
Dietary zinc reduces uptake but not metallothionein binding and elimination of cadmium in the springtail Orchesella cincta.
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)).
A. Mudroch, J. M. Azcue, in P. Mudroch (ur.):
Preparation
Toxicity and toxicokinetics for benthic organisms;
Development — Ecotoxicology
pKa = 5,3
Finland
Environmental Modelling & Software Vol.
Via Mornera 25
13, str. 529–537.
I-20047 Brugherio MI
E., Meurs,G.
MDD:
On determination of hold-up time in reversed-phase liquid chromatography.
The reproductive output of the mites exposed to the test chemical is compared to that of the controls in order to determine the ECx (e.g. EC10, EC50) or the no observed effect concentration (NOEC) (see Appendix 1 for definitions), depending on the experimental design (see paragraph 29).
F., in Rosenblatt, D. H. (ur.).
An overview of the test schedule is given in Appendix 8.
Partition Coefficient, Determination and Estimation, Pergamon Press, Elmsford (New York) in Oxford (1986).
The vehicle is sprayed on or mixed with a small amount, for example 10 g, of fine quartz sand.
Navodilo za biološke preskuse vzorcev.
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)).
Slovacey, R. E., in Hanna, P. J. (1997).
Appropriate statistical methods should be used (according to OECD Document 54 on the Current Approaches in the Statistical Analysis of Ecotoxicity Data: A Guidance to Application).
150,000 mg.
Tenorio, J. M. (1982).
< 1 mg/l,
Bakker, F.M., Feije, R., Grove, A. J., Hoogendorn, G., Jacobs, G., Loose, E.D. and van Stratum, P. (2003).
ISO 8192 Kakovost vode – Preskus inhibicije porabe kisika z aktivnim blatom za oksidacijo ogljika in amonija.
JSS — Journal of Soils and Sediments 3, 73-77.
Mednarodna organizacija za standardizacijo.
Ruf, A. (1991).
Mednarodna organizacija za standardizacijo.
Laboratory studies on the popualation development of Hypoaspis aculeifer (Acari: Parasitiformes).
μ i – j
2, 487-492
15 str. (v švedščini).
Ruf, A. (1995).
Toxicol., 10:1959–1969.
Ruf, A. (1996).
Limnol., 19:2102–2111.
Krogh, P.H. and Axelsen, J.A.
ETH, Stiftung Rubel, Zürich, Švica.
Schlosser, H.-J. and Riepert, F. (1992).
0,012 mg/l
Heckmann, L.-H., Maraldo, K. and Krogh, P. H. (2005).
Metoda merjenja zaviranja rasti korenin.
Fairbrother, A., Glazebrock, P.W., Van Straalen, N.M. and Tarazona, J.V.
Canadian Wildlife Service (Headquarters), Environment Canada, Hull, Québec, Kanada.
Schlosser, H.J., und Riepert, F. 1992.
Non-Target Plant Testing and Evaluation, Centre for Toxicology, University of Guelph, Ontario, Kanada.
Heckmann, L.-H., Ruf, A., Nienstedt, K. M. and Krogh, P. H. 2007.
Elmegaard, N., in Kjær, C. (2004).
Southwood, T.R.E.
NAKNADNO (5)
Ruf, A. (1989).
NAKNADNO (5, 22, 26)
Ruf, A. (1993).
NAKNADNO (5, 22, 23)
Ignatowicz, S. (1974).
NAKNADNO (4, 33)
Kevan, D.K.
NAKNADNO (5, 22)
OECD (2006c).
NAKNADNO (5, 15, 22–26)
ENV/JM/MONO(2006)18
NAKNADNO
A maximum oviposition rate is reached between 10 and 40 days (after becoming adults) and amounts to 2,2 eggs female– 1 day– 1.
S > T (9)
Developmental time from egg to adult female is approximately 20 days at 20 °C.
NAKNADNO (10)
More than one culture should be maintained and held beforehand.
NAKNADNO (2)
Rearing of Typrophagus putrescentiae:
NAKNADNO (13)
The food mites are placed on top of this powder.
NAKNADNO (5, 22, 25, 26)
Afterwards, they are carefully mixed with the powder (which has to be replaced twice a week) using a spatula.
NAKNADNO (5, 22, 24, 26)
Synchronisation of culture:
New Farm, Mire Lane, West End, Twyford RG10 0NJ VELIKA BRITANIJA + 44 1189349464
Specimens that are used in the test should be of similar age (ca.
8240 Ulmerton Road, Largo, FL 33771-3948 ZDA
7 days after reaching the adult stage).
9006 Mercer Pike, Meadville, PA 16335 ZDA
Therefore the following procedure is proposed (24) (25):
Bortree Stile, Ulverston, Cumbria LA12 7PB VELIKA BRITANIJA
Tullgren funnel or comparable methods like e.g. McFadyen (heating from above, sample is put over a funnel)
R. Lower, W.
Heating regime:
Wang, in M. A. Lewis, ur.
25 °C for 12 h, 35 °C for 12 h, 45 °C for 24 hours (in total 48 h).
American Society for Testing & Materials, Philadelphia.
The temperature should be measured in the substrate.
Buhler, D. D., in Hoffman, M. L. (1999).
Fixation liquid:
Anderson's guide to practical methods of propagating weeds and other plants.
Remove lid and wrap a piece of mesh or fabric around the opening.
Cole, J. F. H., in Canning, L. (1993).
(MITOX), 23 January 2007
Gleason, H. A., in Cronquist, A. (1991).
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.
Determination of acute toxicity using Artificial Soil substrate, št. 11268-1.
The food mash can then be sucked by the mite.
Heiden S., Erb R., Dott W. in Eisentraeger A. (ur.).
During the test, dissolved oxygen, temperature, and pH should be measured in all test vessels at least once per week.
Probit Analysis (3. izdaja), str. 19–76.
Total hardness and alkalinity should be measured in the controls and one vessel at the highest concentration at least once per week.
Obe kontroli je mogoče združiti.
Report of the Initial Work Towards the Validation of the 21-Day Fish Screening Assay for the Detection of Endocrine active Substances (Phase 1A).
Greig-Smith, P. W., Becker, H., Edwards, P. J., in Heimbach, F. (ur.) (1992).
OECD Environmental Health and Safety Publications Series on Testing and Assessment No.60, ENV/JM/MONO(2006)27.
Biology and ecology of Earthworms, 3. izdaja.
OECD (2006b).
Kakovost tal – Določevanje karakteristik zadrževanja vode – Laboratorijske metode, št. 11274.
Report of the Initial Work Towards the Validation of the 21-Day Fish Screening Assay for the Detection of Endocrine active Substances (Phase 1B).
UBA-Texte 4/99, 150 + 223 str.
OECD (2007).
A Distribution-free k-Sample Test Against Ordered Alternatives, Biometrika 41, 133– 145.
Final report of the Validation of the 21-day Fish Screening Assay for the Detection of Endocrine Active Substances.
The comparison of treatment to control group means in toxicology studies, Applied Statistics 28, 144– 151.
Phase 2:
A Note on Shirley's Nonparametric Test for Comparing Several Dose Levels with a Zero-Dose Control, Biometrics 42, 183– 186.
Phase 3 report of the validation of the OECD Fish Screening Assay.
Splošen preskus.
US EPA 2007.
Preskus z nizkimi koncentracijami biomase.
Validation of the Fish Short-Term Reproduction Assay:
Madsen, T., Rasmussen, H. B., in Nilsson, L. (1996), Methods for screening anaerobic biodegradability and toxicity of organic chemicals.
US Environmental Protection Agency, Washington, DC.
Projekt št. 336, Inštitut za kakovost vode, Danska agencija za varstvo okolja, Köbenhavn.
OECD, 2008.
Tehnični usmeritveni dokument v podporo Direktivi Komisije 93/67/EGS o ocenjevanju tveganj v zvezi z novimi prijavljenimi snovmi, Uredbi Komisije (ES) št. 1488/94 o ocenjevanju tveganja, ki ga predstavljajo obstoječe snovi, in Direktivi 98/8/ES Evropskega parlamenta in Sveta o dajanju biocidnih pripravkov v promet;
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.
Urad za publikacije Evropske unije (Evropska komisija), Luksemburg.
OECD Environmental Health and Safety Publications Series on Testing and Assessment No.94, ENV/JM/MONO(2008)21.
Organizacija za gospodarsko sodelovanje in razvoj (OECD), Pariz.
Sumpter and Jobling (1995).
Zvezek 11.05.
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