natgillin/translations-raw huggingface dataset:
Effects of waterborne exposure to 17β-estradiol on secondary sex characteristics and gonads of the fathead minnow (Pimephales promelas).
← Steklena kolona, napolnjena s preskusnimi tlemi (če se preskušajo fotolabilni produk-ti, je treba kolone oviti v aluminijasto folijo)
Aquat.
Evropski standard EN 84:1997:
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Evropski standard EN 113/A1:2004:
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Medaka
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25 ± 2 °C
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Age of test organisms
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Approximate wet weight of adult fish (g)
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21 d
Roghair, C. J., Buijze, A., Huys, M. P. A., Wolters-Balk, M. A. H., Yedema, E. S. E., in Hermens, J. L. M. (1996).
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predhodno oceno porazdelitvenega koeficienta, če je določena, ocenjene vrednosti in uporabljeno metodo, če je bila uporabljena računska metoda, pa tudi njen celotni opis, vključno z določitvijo zbirke podatkov in podrobnimi informacijami o izbiri fragmentov,
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ZDA
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% I y
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E-naslov:
Environ Toxicol Chem 22:1350-1360.
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100 mM EDTA
Diagram showing sexual difference in shape and size of the anal fin.
Ker v tem sklopu še ni preskusov za ocenjevanje anaerobne biološke razgradljivosti v anaerobnih gniliščih in je ta preskus namenjen zapolnitvi te vrzeli, morda ni uporaben za druge anoksične ekosisteme.
A, male; B, female.
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mh = 0,468 Δp × Vh
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Annual Book of ASTM Standards, zvezek 11.02.
209-218.
Annual Book of ASTM Standards, zvezek 11.01.
J.P., joint plate; A.S., axial space;
2 dni
B, Distal extremity of fin-ray.
8 dni
(Other methods can be used if they are performed on ice and the result is a homogenous mass).
22 dni
Important:
29 dni
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.
mg/m2/dan
(5) When a homogenous mass is achieved, 4 x the tissue weight of ice-cold homogenisation buffer is added.
Za sušenje črvov se ne priporoča uporaba absorpcijskega papirja, saj bi ta lahko povzročil stres pri črvih ali jih poškodoval.
Important note: New pistils are used for each fish.
Velika prednost L. variegatus pred drugimi vrstami vodnih maloščetincev je hitro razmnoževanje, zaradi katerega se biomasa v laboratorijsko gojenih populacijah hitro poveča (1) (6) (9) (10).
Dunnett test on nested ANOVA No
Metode gojenja
variance stabilising transform >=4 reps per conc
Druga izdaja.
Tamhane-Dunnett test
American Society for Testing and Materials, E 1391–94.
>=4 reps per conc <=3 reps per conc
Chemosphere 32, 1897–1905.
11-14
A test for differences between treatment means when several dose levels are compared with a zero dose control.
15-21
The comparison of several dose levels with a zero dose control.
Preliminary work has been conducted on dietary exposures; however, this route of exposure is not commonly used.
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These determinations are qualitative and should be considered akin to clinical signs of disease/stress and made in comparison to control animals.
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vzorci krvi se za določanje vitelogenina odvzamejo pri cebrici in črnoglavem pisancu, pri čemer se lahko pri cebricah namesto tega za določanje vitelogenina odvzame glava/rep (Dodatek 6), za analizo VTG pri medaki pa se odvzamejo jetra (Dodatek 6).
No. 92.
2,0 μM
Paris
0,25 μl
No. 23.
V erlenmajerice se odmerijo primerne prostornine preskusnih raztopin (primerna količina ne presega polovice prostornine erlenmajeric), nato pa se vse erlenmajerice ohlapno pokrijejo (npr. z aluminijasto folijo), tako da bo mogoča izmenjava plinov med bučko in okoliškim zrakom.
Paris
0,27 g
ASTM (2002) Standard Guide for Conducting Acute Toxicity Tests on Test Materials with Fishes, Macroinvertebrates, and Amphibians.
1,12 g
American Society for Testing and Materials, ASTM E729-96(2002), Philadelpia, PA
Železov (II) klorid tetrahidrat (FeCl2 · 4H2O)
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TRT#
Aquaculture 26, 155–160.
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Any substance or mixture tested using this test method
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The pH should be measured at the beginning and the end of both the range-finding test and the definitive test.
2196–2202.
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.
32, 1503–1508.
Appropriate statistical methods should be used according to OECD Document 54 on the Current Approaches in the Statistical Analysis of Ecotoxicity Data:
23, 588–595.
a Guidance to Application (9).
Aquatic Oligochaeta Biology, 175–184.
In general, adverse effects of the test chemical compared to the control are investigated using one-tailed hypothesis testing at p ≤ 0,05.
18, 1244–1249.
the NOEC/LOEC values, LCx for mortality and ECx for reproduction (mostly LC50, LC10, EC50, and EC10) together with 95 % confidence intervals.
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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;
Applied Regression Analysis, druga izdaja.
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;
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at the end of the exposure period for both generations, pH and the dissolved oxygen concentration should be measured in each vessel.
Water Research, 30, 1625–1632.
4-5 % (dry weight) peat: as close to pH 5,5 to 6,0 as possible;
Journal of Agricultural, Biological and Environmental Statistics, 3, 405–420.
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.
245–261.
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.
27–39.
However, every effort should be made to avoid the use of such materials.
471–483.
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).
1556–1557.
However, if the test chemical is demonstrated not to adsorb to filters, filtration may also be acceptable.
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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.
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If not, a Fisher's exact or Mantel-Haentzal test with Bonferroni-Holm adjusted p-values can be used.
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volume of overlying and pore water; weight of wet sediment with and without pore water for the test vessels and the crystallising dishes;
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20 ± 2 °C
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5 min 95 °C
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Linaceae (lanovke)
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.
Polygonaceae (dresnovke)
Determination of volatile organic carbon can subsequently be performed, if relevant, for the sample type in question.
Solanaceae (razhudnikovke)
ISO, Water quality — determination of total organic carbon.
MONOCOTYLEDONAE (ENOKALIČNICE)
American Public Health Association, Standard Methods for the Estimation of Water and Wastewater.
Liliaceae (Amarylladaceae) (lilijevke (narcisovke))
Schreurs W.
Poaceae (Gramineae) (trave)
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APIACEAE (KOBULNICE)
mg DOC/l
ASTERACEAE (NEBINOVKE)
% abiotic degradation
BRASSICACEAE (KRIŽNICE)
ThODNH3
CARYOPHYLLACEAE (KLINČNICE)
ThODNO2
CYPERACEAE (OSTRIČEVKE)
ThODNO3
FABACEAE (METULJNICE)
test substancemg
PAPAVERACEAE (MAKOVKE)
12 relative atomic mass of carbon; n
Limnology and Oceanography, 30, 1099–1105.
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Fazo absorpcije je treba izvajati največ 28 dni (1) (6) (11), razen če se lahko dokaže, da je bilo ravnovesje doseženo že prej.
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145 μg/l
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riba se vnese v raztopino za evtanazijo, riba se iz raztopine odstrani, ko neha dihati in se ne odziva na zunanje dražljaje;
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Chapter C.7, degradation — abiotic degradation: hydrolysis as a function of pH
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Council Implementing Regulation (EU) 2016/276
Izvedbena uredba Sveta (EU) 2016/276
implementing Article 8a(1) of Regulation (EC) No 765/2006 concerning restrictive measures in respect of Belarus
o izvajanju člena 8a(1) Uredbe (ES) št. 765/2006 o omejevalnih ukrepih v zvezi z Belorusijo
Having regard to Council Regulation (EC) No 765/2006 of 18 May 2006 concerning restrictive measures in respect of Belarus [1], and in particular Article 8a(1) thereof,
ob upoštevanju Uredbe Sveta (ES) št. 765/2006 z dne 18. maja 2006 o omejevalnih ukrepih v zvezi z Belorusijo [1] ter zlasti člena 8a(1) Uredbe,
On 25 February 2016, the Council adopted Decision (CFSP) 2016/280 amending Decision 2012/642/CFSP concerning restrictive measures against Belarus [2], extending the application of the restrictive measures until 28 February 2017 and amending Annex I and deleting Annex II to that Decision.
Svet je 25. februarja 2016 sprejel Sklep (SZVP) 2016/280 o spremembi Sklepa 2012/642/SZVP o omejevalnih ukrepih proti Belorusiji [2], na podlagi katerega so bili omejevalni ukrepi za Belorusijo podaljšani do 28. februarja 2017, Priloga I k navedenemu sklepu spremenjena, Priloga II k navedenemu sklepu pa črtana.
Annex I to Regulation (EC) No 765/2006 is replaced by the text set out in the Annex to this Regulation.
Priloga I k Uredbi (ES) št. 765/2006 se nadomesti z besedilom iz Priloge k tej uredbi.