natgillin/translations-raw huggingface dataset:
(Eds.) (1967) Soil Biology.
ASTM (2002) Standard Guide for Conducting Acute Toxicity Tests on Test Materials with Fishes, Macroinvertebrates, and Amphibians.
London.
American Society for Testing and Materials, ASTM E729-96(2002), Philadelpia, PA
Petersen H and Luxton M (1982) A comparative analysis of soil fauna populations and their role in decomposition processes.
ASTM (2004) Standard Guide for Conducting the Frog Embryo Teratogenesis Assay — Xenopus (FETAX).
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Kahl,M.D., Russom,C.L., DeFoe,D.L. & Hammermeister,D.E. (1999) Saturation units for use in aquatic bioassays.
Petersen, H.
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(1994) A review of collembolan ecology in ecosystem context.
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(1983) Einfluss von Onychirurus fimatus Gisin (Collembola, Onychiuridae) und Folsomia fimetaria L.
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(Collembola, Isotomidae) auf Pythium ultimum Trow. einen Erreger des Wurzelbrandes der Zuckerrübe.
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Scott-Fordsmand, J.
TRT#
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SVL (mm)
H.
SVL
(2005) Background report on prevalidation of an OECD springtail test guideline.
Any substance or mixture tested using this test method
Environmental Project Nr.
The pH should be measured at the beginning and the end of both the range-finding test and the definitive test.
986.
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.
Miljøstyrelsen pp.
Appropriate statistical methods should be used according to OECD Document 54 on the Current Approaches in the Statistical Analysis of Ecotoxicity Data:
Danish Ministry for the Environment.
a Guidance to Application (9).
Krogh, P.
In general, adverse effects of the test chemical compared to the control are investigated using one-tailed hypothesis testing at p ≤ 0,05.
H., 2009.
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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A graph of the fitted model used for calculation, its function equation and its parameters (See (9));
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(1980) Identification keys to Norwegian collembolans.
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Alternativně mohou být dospělí jedinci po nakladení vajíček na 2 nebo 3 dny ze synchronizovaných kultivačních schránek vyjmuti.
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
Extrakce začíná při 25 °C, přičemž teplota se každých 12 hodin automaticky zvyšuje o 5 °C, a trvá celkem 48 hodin.
OECD (2006), Current approaches in the statistical analysis of ecotoxicity data:
Extrakce se ukončí po 12 hodinách při teplotě 40 °C.
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Stejně jako u dafnií je dostačující provést 48hodinovou zkoušku akutní toxicity (podle (17).
Scott-Fordsmand JJ and Krogh PH (2005) Background report on prevalidation of an OECD springtail test guideline.
Dokud však není k dispozici platná metoda OECD pro zkoušky akutní toxicity, lze zvážit provedení zkoušky chronické toxicity podle kapitoly C.28 této přílohy.
Environmental Project Nr. 986.
Příkladem referenčních toxických látek úspěšně použitých v mezilaboratorních zkouškách a validačních studiích jsou: lindan, trifluralin, pentachlorfenol, chlorid kademnatý a chlorid draselný (1)(3)(6)(7)(18).
Miljøstyrelsen 61 pp.
VALIDITA ZKOUŠKY
Danish Ministry for the Environment.
střední hodnota poměru pohlaví plně vylíhlých, živých dospělců (vyjádřená podílem samiček/samečků) v kontrolní zkoušce v obou generacích by měla být nejméně 0,4, ale ne větší než 0,6,
Krogh, P.H., 2009.
v kontrolách první generace by počet šňůr vajíček v každé chovné kleci měl být nejméně 0,6 na jednu samičku nasazenou do chovné klece,
Krogh PH, Johansen K and Holmstrup M (1998) Automatic counting of collembolans for laboratory experiments.
podíl plodných šňůr vajíček v každé chovné kleci s kontrolou první generace by měl být nejméně 0,6,
7, 201-205
na konci období expozice obou generací se v každé nádobě změří pH a koncentrace rozpuštěného kyslíku.
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4–5 % (sušiny) rašeliny s pH co nejblíže 5,5 až 6,0;
Goto HE (1960) Simple techniques for the rearing of Collembola and a not on the use of a fungistatic substance in the cultures.
Koncentrace solubilizačního činidla v konečném zkušebním médiu by měla být minimální (tj. ≤ 0,1 ml/l) a měla by být u všech expozic stejná.
Entomologists' Monthly Magazine 96:138-140.
Použije-li se solubilizační činidlo, nemělo by mít významné účinky na přežití, což musí být prokázáno na kontrolní skupině vystavené rozpouštědlu ve srovnání s negativní kontrolní skupinou (vystavenou pouze vodě).
As an alternative, adult animals may be removed from the synchronisation culture boxes after producing eggs for 2 or 3 days.
Měla by však být vynaložena maximální snaha takové chemické látky nepoužívat.
After three days most of the eggs on the egg-paper will have hatched, and some juveniles may be found under the egg-paper.
Zásobní roztoky – obohacené sedimenty
To have evenly aged juveniles, the egg-paper with un-hatched eggs is removed from the Petri dish with forceps.
Faktor mezi koncentracemi nesmí být větší než 2 (výjimku lze učinit v případech, kdy má křivka závislosti odezvy na dávce malý sklon).
Extraction is started at 25 °C and the temperature is increased automatically every 12 h by 5 °C and has a total duration of 48 hours.
Doporučeným postupem izolace intersticiální (= kapilární) vody je odstřeďování např. při odstředivé síle 10000 g a při 4 °C po dobu 30 minut.
After 12 h at 40 °C the extraction is finished.
Pokud však filtry zkoušenou chemickou látku prokazatelně neadsorbují, je přijatelná i filtrace.
As with daphnids it would be sufficient to perform a 48-h acute test (following 17).
Procenta vylíhlých jedinců jsou kvantifikovatelné údaje a lze je analyzovat za použití postupně klesajícího Cochranova-Armitageova testu, pokud se předpokládá monotónní závislost dávka-odezva a údaje jsou s tímto očekáváním v souladu.
However, until a validated acute guideline is available a chronic test according to Chapter C.28 of this Annex may be considered.
objem vody nad sedimentem a kapilární vody a hmotnost vlhkého sedimentu s kapilární vodou a bez ní ve zkušebních nádobách a v krystalizačních miskách,
Examples of reference toxicants used successfully in ring-tests and validation studies are: lindane, trifluralin, pentachlorophenol, cadmium chloride and potassium chloride.
Shobanov, N.
(1) (3) (6) (7) (18).
A., Kiknadze, I.
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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;
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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;
(1999) Palearctic and Nearctic Chironomus (Camptochironomus) tentans Fabricius are different species (Diptera: Chironomidae).
the fraction of fertile egg ropes in each breeding cage of the controls of the 1st generation should be at least 0,6;
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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.
Fleming, R. et al.
4-5 % (dry weight) peat: as close to pH 5,5 to 6,0 as possible;
Sediment Toxicity Tests for Poorly Water-Soluble Substances, Final Report to the European Commission, Report No:
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.
SETAC (1993) Guidance Document on Sediment toxicity Tests and Bioassays for Freshwater and Marine Environments, From the WOSTA Workshop held in the Netherlands.
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.
ASTM International (2009) E1706-05E01:
However, every effort should be made to avoid the use of such materials.
Environment Canada (1997) Test for Growth and Survival in Sediment using Larvae of Freshwater Midges (Chironomus tentans or Chironomus riparius), Biological Test Method, Report SPE 1/RM/32, December 1997.
Stock solutions — Spiked sediment
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.
However, the 2nd generation has eight replicates again, which are initiated from the exposed populations in the breeding cages.
US-EPA/OPPTS 850.1735 (1996) Whole Sediment Acute Toxicity Invertebrates.
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).
US-EPA/OPPTS 850.1790 (1996) Chironomid Sediment toxicity Test.
Centrifugation at e.g. 10000 g at 4 °C for 30 min is the recommended procedure to isolate interstitial (= pore) water.
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However, if the test chemical is demonstrated not to adsorb to filters, filtration may also be acceptable.
Kirby (1996) Recent intra- and inter-laboratory studies related to the development and standardisation of Environment Canada's biological test methods for measuring sediment toxicity using freshwater amphipods (Hyalella azteca) and midge larvae (Chironomus riparius), Technical Report, Environment Canada, National Water Research Institute, Burlington, Ontario, Canada.
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;
K., Burton, G.
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If present, the egg masses should be carefully removed.
Christensen, E.
They should be transferred to a small dish containing a sample of the breeding water.
R.
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The peat is air dried and ground to a fine powder.
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Prováděcí nařízení Rady (EU) 2016/276
Council Implementing Regulation (EU) 2016/276
s ohledem na nařízení Rady (ES) č. 765/2006 ze dne 18. května 2006 o omezujících opatřeních vůči Bělorusku [1], a zejména na čl. 8a odst. 1 uvedeného nařízení,
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,
Dne 18. května 2006 přijala Rada nařízení (ES) č. 765/2006.
On 18 May 2006, the Council adopted Regulation (EC) No 765/2006.
Dne 25. února 2016 přijala Rada rozhodnutí (SZBP) 2016/280, kterým se mění rozhodnutí 2012/642/SZBP o omezujících opatřeních vůči Bělorusku [2], jímž se prodlužuje platnost omezujících opatření do dne 28. února 2017, mění příloha I a vypouští příloha II uvedeného rozhodnutí.
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.
Příloha I nařízení (ES) č. 765/2006 se nahrazuje zněním uvedeným v příloze tohoto nařízení.
Annex I to Regulation (EC) No 765/2006 is replaced by the text set out in the Annex to this Regulation.
L 134, 20.5.2006, s. 1.
Council Decision (CFSP) 2016/280 of 25 February 2016 amending Decision 2012/642/CFSP concerning restrictive measures against Belarus (see page 30 of this Official Journal).
Rozhodnutí Rady (SZBP) 2016/280 ze dne 25. února 2016, kterým se mění rozhodnutí 2012/642/SZBP o omezujících opatřeních vůči Bělorusku (viz strana 30 v tomto čísle Úředního věstníku).
ANNEX
„PŘÍLOHA I
Persons referred to in Article 2(1)
Osoby podle čl. 2 odst. 1
Names
Nařízení Rady (EU) 2016/277
Council Regulation (EU) 2016/277
kterým se mění nařízení (ES) č. 765/2006 o omezujících opatřeních vůči Bělorusku
amending Regulation (EC) No 765/2006 concerning restrictive measures in respect of Belarus
s ohledem na rozhodnutí Rady 2012/642/SZBP ze dne 15. října 2012 o omezujících opatřeních vůči Bělorusku [1],
Having regard to Council Decision 2012/642/CFSP of 15 October 2012 concerning restrictive measures against Belarus [1],