natgillin/translations-raw huggingface dataset:
Examples of bulk densities for disturbed soils are as follows:for a sand soil 1,66 g · ml– 1for a loam soil 1,17 g · ml– 1for a loamy sand soil 1,58 g · ml– 1for a silt soil 1,11 · g ml– 1
Preto sa navrhuje tento postup (24), (25):
Typical leachate volumes range from 230-260 ml corresponding to approx.
Zariadenie:
92-104 % of total artificial rain applied (251 ml) when using soil columns of 4 cm diameter and 30 cm length.
Tullgrenov lievik alebo porovnateľné metódy, ako napríklad McFadyenova (zahrievanie zhora, vzorka sa dáva nad lievik).
More than one major transformation product may be formed in soil which also may appear at different time points during a transformation study.
Režim zahrievania:
In such cases, it may be necessary to conduct leaching studies with aged residues of different age.
25 °C počas 12 hodín, 35 °C počas 12 hodín, 45 °C počas 24 hodín (spolu 48 hodín).
The original proposal for this test method was based on an article by C.V. Eadsforth and P. Moser (1).
Teplota by sa mala merať v substráte.
weighted averagelog Pow
Fixačná kvapalina:
area %
(MITOX), 23. január 2007
total peak area %
Z tohto dôvodu roztoč klepietkom prepichne kutikulu koristi a vstrekne do nej sekréty na trávenie.
area %i
Vzniknutú kašu potom môže roztoč vysať.
104-54-1 Cinnamyl alcohol
OECD (2006a).
C.V.
OECD (2006b).
Klein, W.
Owens JW (2007).
H. Ellgehausen, C. D'Hondt and R. Fuerer (1981).
OECD, 2008.
B. McDuffie (1981).
68(3):277 – 91.
OECD (2000).
76(3-4):343 – 52.
Guideline for Testing of Chemicals — Partition Coefficient (n-octanol/water):
Toxicological Sciences;67(1):121 – 30.
OSPAR (1995).
70(1):11 – 21.
M. Thatcher, M. Robinson, L. R. Henriquez and C. C. Karman.
123(2):113 – 25.
E. A. Vik, S. Bakke and K. Bansal.
217 – 232.
L.O.
119 – 131.
J.E.
531 – 539.
C. Hansch and A. J. Leo.
1699 – 1708.
C. Hansch, chairman;
Jpn J Environ Toxicol 4:87 – 98.
A tool for the quantitative prediction of bioactivity — Available from Pomona College Medical Chemistry Project, Pomona College, Claremont, California 91711
Journal of Health Science 50:301 – 308.
R. F. Rekker, H. M. de Kort.
1350 – 60.
interaction terms
Paríž.
C. Hansch and A.J.
69 – 92.
Leo, C. Hansch and D. Elkins.
Hutchinson TH, Ankley GT, Segner H, Tyler CR, 2006b.
Toshio Fujita, Junkichi Iwasa & Corwin Hansch (1964).
Environmental Health Perspectives;114 Suppl 1:106 – 14.
R.F.
47, 129 – 145.
R.A.
Toxicol.
ACS — Symposium Series 255, p.
Chem.
225, American Chemical Society, Washington, D.C.
27, 478 – 488.
Pseudokirchneriella subcapitata:
OECD (2012) OECD Conceptual Framework for Testing and Assessment of Endocrine Disrupters (revised).
(A zero algal concentration in one out of two or three replicate vessels may indicate the vessel was not inoculated correctly, or was improperly cleaned).
ENV/JM/MONO(2012)22.
Depending on the intended usage of data; the quality (precision) and amount of data as well as the availability of data analysis tools, it may be decided (and sometimes well justified) to stop the data analysis at this stage and simply read the key figures EC50 and EC10 (and/or EC20) from the eye fitted curve (see also section below on stimulatory effects).
26 ± 2°C
International Organisation for Standardisation (1993).
Vek testovacích organizmov
ISO 8692 Water quality — Algal growth inhibition test.
Približná mokrá hmotnosť dospelých rýb (g)
International Organisation for Standardisation (1998).
21 dní
Water quality — Guidelines for algal growth inhibition tests with poorly soluble materials, volatile compounds, metals and waster water.
Aquatic Toxicology, 81, 90 – 98.
ISO 5667-16 Water quality — Sampling — Part 16:
Environ Toxicol Chem 20:1276 – 1290.
Mayer, P., Cuhel, R. and Nyholm, N. (1997).
Environ Toxicol Chem 22:1350 – 1360.
Slovacey, R.E. and Hanna, P.J.
Environ Sci Technol 34:3003 – 3011.
919-925
J Fish Biol 59:515 – 523.
Simpson, S.L., Roland, M.G.E., Stauber, J.L. and Batley, G.E.
Aquat Toxicol 47:129 – 145.
Christensen, E.R., Nyholm, N. (1984).
Can J Zool 52:1031 – 1038.
Nyholm, N. Sørensen, P.S., Kusk, K.O. and Christensen, E.R.
209 – 218.
Bruce, R.D.,and Versteeg, D.J.
Stanovte, či je reakcia na dávku monotónna.
Dunnett, C.W.
Transformácia na stabilizáciu rozptylu?
1096-1121
Priemery repl. normálne rozdelené
Norberg-King T.J.
Uskutočnil sa predbežný výskum expozície v prípade aplikovania v potrave, ale tento spôsob expozície sa bežne nepoužíva.
Williams, D.A.
fyzikálno-chemické vlastnosti, údaje o stálosti a biodegradovateľnosti,
Draper, N.R. and Smith, H. (1981).
spôsob a frekvencia prípravy roztokov.
Brain, P. and Cousens, R. (1989).
Informácie o testovanej chemikálii zahŕňajú skutočné a nominálne koncentrácie testovanej chemikálie a v niektorých prípadoch podľa potreby nepôvodnej chemikálie.
American Type Culture Collection
Štatistické analýzy údajov by podľa možnosti mali vychádzať z postupov uvedených v dokumente Súčasné prístupy k štatistickej analýze údajov o ekotoxicite:
CCAP, Culture Collection of Algae and Protozoa
Ak nie je možné použiť žiadnu normalizačnú transformáciu, významný vplyv chemikálie sa stanoví pomocou Mann-Whitneyho-Wilcoxonovho U testu s použitím Bonferroniho-Holmovej úpravy hodnôt p.
Collection of Algal Cultures
Dunnettov test sa uplatňuje nezávisle od akéhokoľvek F-testu analýzy ANOVA a Mann-Whitneyho test sa uplatňuje nezávisle od celkového Kruskallovho-Wallisovho testu.
University of Göttingen
Po štádiu 60 sa pri žubrienkach prejaví zníženie veľkosti a hmotnosti v dôsledku resorpcie tkaniva a zníženia celkového obsahu vody.
Nikolausberger Weg 18
Merania mokrej hmotnosti a SVL preto nemožno primerane použiť na štatistické analýzy na zistenie rozdielov v rýchlostiach rastu.
GERMANY
Údaje o mokrej hmotnosti a dĺžke organizmov v štádiu > NF60 by sa preto mali cenzurovať a nemožno ich použiť na analýzy priemerov alebo mediánov pre replikáty.
UTEX Culture Collection of Algae
Na analýzu týchto parametrov rastu možno použiť dva rozdielne prístupy.
Section of Molecular, Cellular and Developmental Biology
OECD (2004) Report of the Validation of the Amphibian Metamorphosis Assay for the detection of thyroid active substances:
8-14 × 2-3
Phase 1 – Optimisation of the Test Protocol.
40-60 [1]
Phase 2 – Multi-chemical Interlaboratory Study.
60-80 [1]
OECD (2008) Report of the Validation Peer Review for the Amphibian Metamorphosis Assay and Agreement of the Working Group of the National Coordinators of the Test Guidelines Programme on the Follow-up of this Report.
40-50 [1]
ASTM (2002) Standard Guide for Conducting Acute Toxicity Tests on Test Materials with Fishes, Macroinvertebrates and Amphibians.
30-40 [1]
American Society for Testing and Materials aSTM E729-96(2002), Philadelpia, PA.
1,2-1,5
ASTM (2004) Standard Guide for Conducting the Frog Embryo Teratogenesis Assay – Xenopus (FETAX).
1,1-1,4
Chemosphere 39, s.
2,0-2,4
539 – 551.
92,760 mg.
OECD (2007) Guidance Document on Amphibian Thyroid Histology.
207,690 mg.
Dodd,M.H.I. a Dodd,J.M.
1,635 mg.
OECD (2006) Current Approaches in the Statistical Analysis of Ecotoxicity Data:
79,880 mg.
RIADOK
0,714 mg.
akákoľvek látka alebo zmes, ktorá sa testuje pomocou tejto testovacej metódy.
3,630 mg.
Mali by sa použiť vhodné štatistické metódy podľa dokumentu OECD 54 o súčasných prístupoch k štatistickej analýze údajov o ekotoxicite:
150,000 mg.
Vo všeobecnosti sa nepriaznivé účinky testovanej chemikálie v porovnaní s kontrolnou skupinou analyzujú pomocou jednostranného testu hypotézy s p ≤ 0,05.
[Disodium (Ethylenedinitrilo) tetraacetate].
hodnoty NOEC/LOEC, LCx pre úmrtnosť a ECx pre rozmnožovanie (väčšinou LC50, LC10, EC50 a EC10) s 95 % intervalmi spoľahlivosti, graf vhodného modelu použitého na výpočet, rovnica jeho funkcie a jeho parametre [pozri (9)],
Dividing the responses by the mean control response for obtaining the percentage of inhibition, one introduces an additional error caused by the error on the control mean.
ISO (1999) Soil Quality – Effects of soil pollutants on Collembola (Folsomia candida):
Test mixtures (FT as in Table 1) containing water, synthetic sewage feed and the test chemical should be prepared to obtain different nominal concentrations of the test chemical (See Table 1 for example of volumes of constituents).
Medzinárodná organizácia pre normalizáciu, Ženeva.
The pH should be adjusted to 7,5 ± 0,5, if necessary;
Burges A a Raw F (Eds) (1967) Soil Biology.
is the rate of oxygen uptake due to nitrification (mg/lh);
Petersen H a Luxton M (1982) A comparative analysis of soil fauna populations and their role in decomposition processes.
If a statistical analysis is intended to determine the NOEC, per-vessel statistics (individual vessels are considered as replicates) are necessary.
287 – 388.
Appropriate statistical methods should be used according to the OECD Document on Current Approaches in the Statistical Analysis of Ecotoxicity Data:
Petersen H (1994) A review of collembolan ecology in ecosystem context.
and, if possible, 95 per cent confidence limits, possibly EC20, EC80; possibly NOEC and the used statistical methods, if the EC50 cannot be determined;
111 – 118.
Brown, D., Hitz, H.R. and Schäfer, L. (1981).
Hopkin SP (1997).
King, E. F. and Painter H. A. (1986).
330 s.
OECD (1984), Activated sludge, Respiration inhibition test, Test Guideline No. 209, Guidelines for the testing of chemicals, OECD, Paris.
(ISBN 0-19-854084-1).
ISO (2007).
Ulber B (1983) Einfluss von Onychirurus fimatus Gisin (Collembola, Onychiuridae) und Folsomia fimetaria L.
Bealing, D. J. (2003).
(Collembola, Isotomidae) auf Pythium ultimum Trow. einen Erreger des Wurzelbrandes der Zuckerrübe.
Painter, H A, Jones K (1963).
V 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, s.
Robra, B. (1976).
OECD (2006), Current approaches in the statistical analysis of ecotoxicity data:
Fiebig S. and Noack, U. (2004).
OECD series on testing and assessment Number 54, ENV/JM/MONO(2006)18, OECD Paríž
The use of copper(II)sulphate pentahydrate as reference substance in the activated sludge respiration inhibition test — acc. to the OECD guideline 209.
Scott-Fordsmand JJ a Krogh PH (2005) Background report on prevalidation of an OECD springtail test guideline.
ISO (1995).
Miljøstyrelsen 61 s.
ISO 10634 Water Quality — Guidance for the preparation and treatment of poorly water-soluble organic compounds for the subsequent evaluation of their biodegradability in aqueous medium, International Organization for Standardization.
Danish Ministry for the Environment.
The temperature in the test vessels should be 24 ± 2 °C. The pH of the control medium should not increase by more than 1,5 units during the test.
Krogh, P.H., 2009.
EyCx (frond number); and EyCx (total frond area, dry weight, or fresh weight).
Krogh PH, Johansen K and Holmstrup M (1998) Automatic counting of collembolans for laboratory experiments.
ASTM International.
7, 201 – 205
US EPA — United States Environmental Protection Agency.
Fjellberg A (1980) Identification keys to Norwegian collembolans.
AFNOR — Association Française de Normalisation.
Goto HE (1960) Simple techniques for the rearing of Collembola and a not on the use of a fungistatic substance in the cultures.
SSI — Swedish Standards Institute.
Entomologists' Monthly Magazine 96: 138 – 140.
Environment Canada.
Po 12 hodinách pri 40 °C sa extrakcia končí.
Sims I., Whitehouse P. and Lacey R. (1999) The OECD Lemna Growth Inhibition Test.
priemerný pomer pohlaví úplne vykuklených a živých dospelých jedincov (ako podiel samčekov alebo samičiek) v kontrolnej skupine v obidvoch generáciách by mal byť aspoň 0,4, ale nie vyšší ako 0,6,
WRc plc — Environment Agency.
v každej chovnej klietke by počet šnúr vajíčok v kontrolných skupinách 1. generácie mal byť aspoň 0,6 na samičku pridanú do chovnej klietky,
International Organisation for Standardisation.
podiel fertilných šnúr vajíčok v každej chovnej klietke s kontrolnou skupinou 1. generácie by mal byť aspoň 0,6,
Water Quality — Determination of the Toxic Effect of Water Constituents and Waste Water to Duckweed (Lemna minor) — Duckweed Growth Inhibition Test.
na konci obdobia expozície pre obidve generácie je potrebné odmerať v každej nádobe pH a koncentráciu rozpusteného kyslíka.
Walbridge C. T. (1977).
Koncentrácia solubilizačného prostriedku v konečnom testovacom médiu by mala byť minimálna (t. j. ≤ 0,1 ml/l) a mala by byť pre všetky testované koncentrácie chemikálie rovnaká.
Environmental Research Laboratory — Duluth, Minnesota 55804
Ak sa použije solubilizačný prostriedok, nesmie mať žiadne významné účinky na prežívanie na základe porovnania kontrolnej skupiny s rozpúšťadlom s negatívnou (vodnou) kontrolnou skupinou.
Lockhart W.
Je však potrebné vynaložiť maximálne úsilie, aby sa predišlo použitiu takýchto materiálov.
Hydrobiologia, 118/119, 353 — 359.
Zásobné roztoky – obohatené sedimenty
Huebert, D.B. and Shay J.M.
Na izolovanie intersticiálnej (= pórovej) vody je odporúčaným postupom centrifugácia napr. pri 10000 g a 4 °C počas 30 minút.
Christensen, E.R.,, Nyholm, N. (1984):
Ak sa však preukáže, že testovaná chemikália sa na filtroch neadsorbuje, môže byť prijateľná aj filtrácia.
Bruce R.D. and Versteeg D.J.
Pomery vykuklenia sú kvantové údaje a môžu sa analyzovať pomocou Cochranovho-Armitageho testu aplikovaného zostupne v prípadoch, keď sa očakáva monotónny priebeh krivky závislosti dávka-odpoveď a tieto údaje zodpovedajú tomuto očakávaniu.
OECD.
objem nadložnej vody a vody nachádzajúcej sa v póroch sedimentu, hmotnosť mokrého sedimentu s vodou nachádzajúcou sa v póroch sedimentu a bez nej pre testovacie nádoby a kryštalizačné misky,
Brain P. and Cousens R. (1989).
SETAC (1993), Guidance Document on Sediment toxicity Tests and Bioassays for Freshwater and Marine Environments, From the WOSTA Workshop held in the Netherlands.
Sources of Lemna species
ASTM International (2009), E1706-05E01:
Toronto, Ontario, Canada, M5S 3 B2
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.
United States
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.
SWEDEN
US-EPA/OPPTS 850.1735 (1996), Whole Sediment Acute Toxicity Invertebrates.
Germany
US-EPA/OPPTS 850.1790 (1996), Chironomid Sediment toxicity Test.
Hillman, W.S.
Milani, D., Day, K.E., McLeay, D.J. a R.S.
Landolt, E. (1986).
2662 – 2674.
Björndahl, G. (1982).
Taenzler, V., Bruns, E., Dorgerloh, M., Pfeifle, V. a L. Weltje (2007), Chironomids:
Wang, W.
221 – 230.
Environmental Research, 52:7-22.
Sugaya, Y.
A sample of the contaminated plant material is taken and the roots cut off.
J. Sanit.
The material is then shaken vigorously in clean water, followed by immersion in a 0,5 % (v/v) sodium hypochlorite solution for between 30 seconds and 5 minutes.
345 – 350.
The plant material is then rinsed with sterile water and transferred, as a number of batches, into culture vessels containing fresh growth medium.
Kawai, K. (1986), Fundamental studies on chironomid allergy, I. Culture methods of some Japanese chironomids (Chironomidae, Diptera), Jp.
(mg/ߦl)
47 – 57.
The pH is adjusted to 6,5 ± 0,2 with either 0,1 or 1 mol HCl or NaOH, and the volume adjusted to one litre with deionised water.
OECD (2000), Guidance Document on Aquatic Toxicity Testing of Difficult Substances and Mixtures, Environment, Health and Safety Publications, Series on Testing and Assessment No.
AAP growth medium
23, ENV/JM/MONO(2000)6, OECD, Paríž.
Under these conditions the stock solutions will have a shelf life of at least 6 - 8 weeks.
Oetken, M, Nentwig, G., Löffler, D, Ternes, T. a J. Oehlmann (2005), Effects of pharmaceuticals on aquatic invertebrates, Part I, The antiepileptic drug carbamazepine arch.
The 20 ml of each nutrient stock solution is added to approximately 850 ml deionised water to produce the growth medium.
353 – 361.
The pH is adjusted to 7,5 ± 0,1 with either 0,1 or 1 mol HCl or NaOH, and the volume adjusted to one litre with deionised water.
1163 – 1175.
Growth medium intended for testing should be prepared 1-2 days before use to allow the pH to stabilise.
Naylor, C. a C. Rodrigues (1995), Development of a test method for Chironomus riparius using a formulated sediment, Chemosphere, 31:
The pH of the growth medium should be checked prior to use and readjusted if necessary by the addition of 0,1 or 1 mol NaOH or HCl as described above.
3291 – 3303.
(I. Sims, P. Whitehouse and R. Lacey.
a multiple comparisons procedure for comparing several treatments with a control.
(1999) The OECD Lemna Growth Inhibition Test.
1096 – 1121.
Development and Ring-testing of draft OECD Test Guideline.
482 – 491.
WRc plc — Environment Agency.)
510 – 531.
(mg/ߦl) [1]
577 – 585.
Na;N
213 – 221.
The pH should be to 5,5 +/– 0,2 (adjust by addition of a minimised volume of NaOH solution or HCl).
Slob, W.
Adjust with water to 1000 ml.
298 – 312.
350 ± 50 μE/m2/s.
OECD (2010), Validation report of the Chironomid full life-cycle toxicity test, Forthcoming publication in the Series on Testing and Assessment, OECD, Paríž.
For crop protection products, the physical/chemical properties and use pattern of the test chemical, its maximum concentration or application rate, the number of applications per season and/or the persistence of the test chemical need to be considered.
Elendt, B.P. a W.-R.
The number and spacing of the concentrations or rates should be sufficient to generate a reliable dose-response relationship and regression equation and give an estimate of the ECx. or ERx.
1157 – 1167.
The selected concentrations/rates should encompass the ECx or ERx values that are to be determined.
Meller, M., Egeler, P., Roembke, J., Schallnass, H., Nagel, R. a B. Streit (1998), Short-term toxicity of lindane, hexachlorobenzene and copper sulfate on tubificid sludgeworms (Oligochaeta) in artificial media, Ecotox.
The recommended number of test concentrations/rates to achieve this is at least five in a geometric series plus untreated control, and spaced by a factor not exceeding three.
B zátka z vulkanizovaného kaučuku perforovaná sklenenou trubičkou (A).
A dose-response relationship is established in terms of a regression equation.
Prehľad príslušných podmienok testu špecifických pre validované druhy medaka japonská, pichľavka sivá a dánio pruhované je uvedený v dodatku 2.
Different models can be used:
30 – 70 %
Schrader G., Metge K., and Bahadir M. (1998).
V prípade semistatickej metódy možno použiť dva rôzne postupy obnovy.
International Organisation of Standards.
Buď sa nové testovacie roztoky pripravia v čistých komorách a prežívajúce vajíčka a larvy sa opatrne prenesú do nových komôr alebo sa testovacie organizmy nechajú v skúšobných komorách a časť (aspoň dve tretiny) testovacej vody sa mení každý deň.
Soil Quality -- Determination of the Effects of Pollutants on Soil Flora — Part 1:
fyzikálno-chemické vlastnosti, chemické identifikačné údaje vrátane čistoty a analytickej metódy kvantifikácie testovanej chemikálie.
Soil Quality -- Determination of the Effects of Pollutants on Soil Flora — Part 2:
OECD (1992), Fish, Early Life Stage Toxicity Test, Test Guideline No.
American Standard for Testing Material (ASTM).
210, Guidelines for the Testing of Chemicals, OECD, Paríž.
U.S.
Jobling, S., D. Sheahan, J.A.
US EPA.
Tyler, C.R., R.van Aerle, T.H.
Background — Non-target Plant Testing;
Nishi, K., M. Chikae, Y.
AFNOR, X31-201.
Hahlbeck, E., I. Katsiadaki, I. Mayer, M. Adolfsson-Erici, J. James a B.E.
Boutin, C., Freemark, K.E. and Keddy, C.J.
Jensen, K.M. a G.T.
Forster, R., Heimbach, U., Kula, C., and Zwerger, P. (1997).
OECD (2010), Guidance Document on the Diagnosis of Endocrine-related Histopathology in Fish Gonads, Series on Testing and Assessment No.
Effects of Plant Protection Products on Non-Target Organisms — A contribution to the Discussion of Risk Assessment and Risk Mitigation for Terrestrial Non-Target Organisms (Flora and Fauna).
123, ENV/JM/MONO(2010)14, OECD, Paríž.
Hale, B., Hall, J.C., Solomon, K., and Stephenson, G. (1994).
Kobayashi, T., M. Matsuda, H. Kajiura-Kobayashi a.
Dieldrin uptake by corn as affected by soil properties, J. Agro.
23, OECD, Paríž.
Boutin, C.;
229, Guidelines for the Testing of Chemicals, OECD, Paríž.
Boutin, C. and Harper, J.L.
OECD (2011), Validation Report (Phase 1) for the Fish Sexual Development Test, Series on Testing and Assessment No 141, ENV/JM/MONO(2011)22, OECD, Paríž.
Guidance Document, Current Approaches in the Statistical Analysis of Ecotoxicity Data:
OECD (2011), Peer Review Report of the validation of the Fish Sexual Development Test, Series on Testing and Assessment No 143, ENV/JM/MONO(2011)24, OECD, Paríž.
Hatzios, K.K. and Penner, D. (1985).
30 – 70 %
Hamill, P.B., Marriage, P.B. and G. Friesen.
Absorbancia sa meria pri 450 nm (napr. na zariadení na čítanie platní Thermomax od spoločnosti Molecular Devices).
Frans, R.E. and Talbert, R.E.
Údaje sa analyzujú na pripojenom softvéri (napr. Softmax).
Bruce, R.D. and Versteeg, D. J.(1992).
385 – 398.
Solanum lycopersicon
5′ GGG ACG AGC AAG ATT TAT TGG 3′
0,09-0,17 (4, 19)
DOC,
2,4-2,6 (14, 19)
hodnotu BSK morskej vody v slepej vzorke a
0,85 -1,2 (14, 19)
% biodegradácie
14-21
Vzorky s vysokou koncentráciou chloridu a/alebo väčším objemom možno touto metódou analyzovať za predpokladu, že sa zabráni hromadeniu chloridu v oxidačnej nádobe.
25-61 (14, 29)
Následne sa podľa možnosti môže pre daný druh vzorky vykonať stanovenie prchavého organického uhlíka.
10-20 (6, 21)
ISO, Water quality – determination of total organic carbon.
10-20 (6, 10)
Schreurs W.
7-37,5 (14, 30)
mglátky
0,45-2,28 (14, 29)
testovaná látkamg
0,5-0,7 (14, 19, 29)
C.9, biodegradácia – Zahn-Wellensov test;
0,52-0,6 (14, 30)
C.10, simulačný test – aeróbne čistenie odpadových vôd:
10-20 (21)
Jednotky s technológiou aktivovaného kalu, B:
10-20 (7, 21)
Biofilmy
4-5 (14, 30)
C.11, biodegradácia – respiračno-inhibičný test aktivovaného kalu
14-28
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