natgillin/translations-raw huggingface dataset:
Chapter C.19, Estimation of the adsorption coefficient (Koc ) on soil and on sewage sludge using high performance liquid chromatography (HPLC)
11–14
Chapter C.29, Ready biodegradability CO2 in sealed vessels
15–21
In Hutzinger, O. (editor), The Handbook of Environmental Chemistry, Vol.
V zvezi s prehransko izpostavljenostjo je bilo opravljeno predhodno delo, vendar se ta način izpostavljenosti ne uporablja pogosto.
2 Part J (Vol. editor: B. Beek):
fizikalno-kemijske lastnosti, informacije o stabilnosti in biološki razgradljivosti,
Influence of partition coefficient of lipophilic compounds on bioconcentration kinetics with fish.
metodo in pogostost priprave razredčin.
Res. 22, 701-707.
Informacije o preskusni kemikaliji vključujejo aktualne in nominalne koncentracije preskusne kemikalije ter v nekaterih primerih nematične kemikalije, kot je ustrezno.
Development of ecotoxicological test systems to assess contaminated sediments.
Priporoča se, da se pri statističnih analizah podatkov upoštevajo postopki, opisani v dokumentu Sedanji pristopi k statistični analizi podatkov o ekotoksičnosti:
A. Mudroch, J.M.
Kadar ni mogoče najti normalizacijske pretvorbe, se znaten učinek tretiranja določi na podlagi Mann-Whitney-Wilcoxonovega U-preskusa in Bonferroni-Holmove prilagoditve vrednostim p.
An upper limit is given by the necessity to achieve a complete separation phase after adjustments of the partitition equilibrium and before samples are taken out for analytical determinations.
Dunnettov preskus se uporablja neodvisno od katerega koli F-preskusa analize variance, Mann-Whitneyjev preskus pa se uporablja neodvisno od katerega koli Kruskall-Wallisovega preskusa.
If proper care is taken, the upper limit can be extended to higher values of Pow
Po 60. fazi se velikost in teža paglavcev zmanjšata zaradi resorpcije in zmanjšanja absolutne vsebnosti vode.
40).
Podatke o mokri teži in dolžini organizmov, ki so presegli 60. fazo po Nieuwkoopu in Faberju, je treba izključiti in se jih ne sme uporabiti pri analizah sredin ponovitev ali median ponovitev.
The same procedure should be followed with the reference chemical, to give flasks FR1-3
Za analizo teh parametrov, povezanih z rastjo, se lahko uporabita dva različna pristopa.
The recommended size is 0,1 litre to 1 litre.
OECD (2004).
The use of gas-tight silicone septa is recommended.
Report of the Validation of the Amphibian Metamorphosis Assay for the detection of thyroid active substances:
It is further recommended that the gas-tightness of caps, especially butyl rubber septa, be tested because several commercially available septa are not sufficiently gas-tight against methane and some septa do not stay tight when they are pierced with a needle under the conditions of the test.Gas tight coated septa are recommended and must be used for volatile chemicals (some commercial septa are relatively thin, less than 0,5 cm, and do not stay gas tight after piercing with syringe needle);Butyl rubber septa (about 1 cm) are recommended, if the test substances are not volatile (these normally stay gas tight after piercing.)Prior to the test it is recommended that the septa are carefully examined for their ability to stay gas tight after piercing.
Phase 1 – Optimisation of the Test Protocol.
The meter should be used and calibrated at regular intervals, according to the manufacturer's instructions.
OECD (2007).
If a pressure-meter of the prescribed quality is used e.g. capsulated with a steel membrane, no calibration is necessary in the laboratory.
Final Report of the Validation of the Amphibian Metamorphosis Assay:
If other measurement devices are used (without certified calibration by the manufacturer), conversion is recommended over the total range at regular intervals (Appendix 2).
ASTM (2002).
Aeration of water can be maintained through bubblers.
American Society for Testing and Materials, ASTM E729–96(2002), Filadelfija, PA.
It is recommended to set bubblers at levels that do not create undue stress on the tadpoles.
ASTM (2004).
At 20 °C under standard atmospheric pressure the ASV in freshwater equals 9,1 mg/l (60 % equals 5,46 mg/l)
Standard Guide for Conducting the Frog Embryo Teratogenesis Assay – Xenopus (FETAX).
Mercury (II) chloride (HgCl2) is a very toxic substance which should be handled with suitable precautions.
Chemosphere 39, str. 539–551.
Aqueous wastes containing this chemical should be disposed of appropriately;
Nieuwkoop, P. D., in Faber, J. (1994).
Digested sludge is a mixture of the settled phases of sewage and activated sludge, which have been incubated in an anaerobic digester at about 35 °C to reduce biomass and odour problems and to improve the dewater-ability of the sludge.
Dodd, M. H. I., in Dodd, J. M. (1976).
It consists of an association of anaerobic fermentative and methanogenic bacteria producing carbon dioxide and methane (11).
Physiology of Amphibia.
Proportion of n2
OECD (2006).
It is further recommended that the gas-tightness of caps, especially butyl rubber septa, be tested because several commercially available septa are not sufficiently gas-tight against methane and some septa do not stay tight when they are pierced with a needle under the conditions of the test.
Current Approaches in the Statistical Analysis of Ecotoxicity Data:
The device should be used and calibrated at regular intervals, according to the manufacturer's instructions.
TRET.
The accuracy of the calibration can be checked at the laboratory with a one-point measurement at 1 × 105 Pa against a pressure-meter with a mechanical display.
TRET.
If other measurement devices are used (without certified calibration by the manufacturer), calibration is recommended over the total range at regular intervals.
vsaka snov ali zmes, preskušena z uporabo te preskusne metode.
This should be re-evaluated if adsorptive and insoluble reference chemicals are included.
Uporabiti je treba ustrezne statistične metode v skladu z dokumentom OECD št. 54 o sedanjih pristopih k statistični analizi podatkov o ekotoksičnosti:
Column leaching studies with crop protection products may provide mobility information on a test chemical and its transformation products and may supplement batch sorption studies.
smernica za uporabo (9).
The amount to be applied to cylindrical soil columns can be calculated by the following formula:M μgA kgha109μgkgd2cm2π108cm2ha4where:M amount applied per column [μg]A rate of application [kg · ha– 1]d diameter of soil column [cm]π 3,14
Na splošno se škodljivi učinki preskusne kemikalije v primerjavi s kontrolo proučujejo s preskušanjem enostransko zastavljene hipoteze pri p ≤ 0,05.
§ The respective variables should preferably show values within the range given.
ISO (1999) Soil Quality – Effects of soil pollutants on Collembola (Folsomia candida):
If, however, difficulties in finding appropriate soil material occur, values below the indicated minimum are accepted.
Mednarodna organizacija za standardizacijo, Ženeva.
‡ Soils with less than 0,3 % organic carbon may disturb correlation between organic content and adsorption.
Burges, A., in Raw, F. (ur.) (1967).
Thus, it is recommended to use soils with a minimum organic carbon content of 0,3 %.
Soil Biology.
# Soils with very high carbon content (e.g. > 10 %) may not be acceptable legally e.g. for pesticide registration purposes.
London.
This simulates an extremely high rainfall.
Petersen, H., in Luxton, M. (1982).
The average yearly rainfall, for example, in Central Europe is of the order of 800-1000 mm.
A comparative analysis of soil fauna populations and their role in decomposition processes.
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
287–388.
Typical leachate volumes range from 230-260 ml corresponding to approx.
Petersen, H. (1994).
More than one major transformation product may be formed in soil which also may appear at different time points during a transformation study.
111– 118.
In such cases, it may be necessary to conduct leaching studies with aged residues of different age.
Hopkin, S. P. (1997).
The original proposal for this test method was based on an article by C.V. Eadsforth and P. Moser (1).
330 str.
total peak area %
Einfluss von Onychirurus fimatus Gisin (Collembola, Onychiuridae) und Folsomia fimetaria L.
area %i
(Collembola, Isotomidae) auf Pythium ultimum Trow. einen Erreger des Wurzelbrandes der Zuckerrübe.
104-54-1 Cinnamyl alcohol
V:
B. McDuffie (1981).
OECD series on testing and assessment Number 54, ENV/JM/MONO(2006)18, OECD Pariz.
OECD (2000).
Scott-Fordsmand, J. J., in Krogh, P. H. (2005).
Guideline for Testing of Chemicals — Partition Coefficient (n-octanol/water):
Background report on prevalidation of an OECD springtail test guideline.
E. A. Vik, S. Bakke and K. Bansal.
Krogh, P. H. (2009).
J.E.
Automatic counting of collembolans for laboratory experiments.
C. Hansch and A. J. Leo.
Fjellberg, A. (1980).
R. F. Rekker, H. M. de Kort.
Simple techniques for the rearing of Collembola and a not on the use of a fungistatic substance in the cultures.
Chim.
Entomologists' Monthly Magazine 96: 138– 140.
interaction terms
v vsaki kletki za razmnoževanje mora biti število nizov jajčec v kontrolah za prvo generacijo vsaj 0,6 na samico, dodano v kletko za razmnoževanje,
Pomona College, Medicinal Chemistry Project, Claremont, California 91711, USA, Log P Database and Med.
delež fertilnih nizov jajčec v posamezni kletki za razmnoževanje kontrol prve generacije mora biti vsaj 0,6,
C. Hansch and A.J.
na koncu obdobja izpostavljenosti je treba za obe generaciji v vsaki posodi izmeriti pH in koncentracijo raztopljenega kisika.
Leo, C. Hansch and D. Elkins.
Koncentracija sredstva za raztapljanje v končnem preskusnem mediju mora biti minimalna (tj. ≤ 0,1 ml/l) in enaka v vseh posodah s preskusno kemikalijo.
Toshio Fujita, Junkichi Iwasa & Corwin Hansch (1964).
Če se uporabi sredstvo za raztapljanje, to ne sme bistveno vplivati na preživetje, kar se kaže s kontrolo s topilom, ki se primerja z negativno kontrolo (z vodo).
R.F.
Vendar si je treba čim bolj prizadevati, da se taki materiali ne uporabijo.
R.A.
Založne raztopine – usedlina s primešano preskusno snovjo
ACS — Symposium Series 255, p.
Za izolacijo intersticijske (= porne) vode se priporoča 30-minutno centrifugiranje pri npr. 10000 g in 4 °C.
225, American Chemical Society, Washington, D.C.
Če pa se za preskusno kemikalijo izkaže, da se ne adsorbira na filtre, je sprejemljivo tudi filtriranje.
Pseudokirchneriella subcapitata:
Koeficienti preobrazbe so kvantni podatki in se lahko analizirajo s Cochran-Armitageovim preskusom, uporabljenim regresivno (step-down), kadar se pričakuje monotono razmerje med odmerek-učinek in so ti podatki v skladu s tem pričakovanjem.
(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).
Fleming, R., idr.
State reasons for rejection of a data point as an outlier clearly in the test report.
Sediment Toxicity Tests for Poorly Water-Soluble Substances, Final Report to the European Commission, Report No:
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).
SETAC (1993).
International Organisation for Standardisation (1993).
Guidance Document on Sediment toxicity Tests and Bioassays for Freshwater and Marine Environments, z delavnice WOSTA, ki je potekala na Nizozemskem.
ISO 8692 Water quality — Algal growth inhibition test.
ASTM International (2009).
International Organisation for Standardisation (1998).
E1706-05E01:
Water quality — Guidelines for algal growth inhibition tests with poorly soluble materials, volatile compounds, metals and waster water.
Environment Canada (1997).
ISO 5667-16 Water quality — Sampling — Part 16:
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.
Mayer, P., Cuhel, R. and Nyholm, N. (1997).
US-EPA (2000).
Slovacey, R.E. and Hanna, P.J.
Methods for Measuring the Toxicity and Bioaccumulation of Sediment-associated Contaminants with Freshwater Invertebrates, druga izdaja, EPA 600/R-99/064, marec 2000, sprememba prve izdaje iz junija 1994.
919-925
US-EPA/OPPTS 850.1735 (1996).
Simpson, S.L., Roland, M.G.E., Stauber, J.L. and Batley, G.E.
Whole Sediment Acute Toxicity Invertebrates.
Christensen, E.R., Nyholm, N. (1984).
US-EPA/OPPTS 850.1790 (1996).
Nyholm, N. Sørensen, P.S., Kusk, K.O. and Christensen, E.R.
Chironomid Sediment toxicity Test.
Bruce, R.D.,and Versteeg, D.J.
Milani, D., Day, K. E., McLeay, D. J., in Kirby, R. S. (1996).
Dunnett, C.W.
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, Kanada.
1096-1121
2662–2674.
Norberg-King T.J.
Taenzler, V., Bruns, E., Dorgerloh, M., Pfeifle, V., in Weltje, L. (2007).
Williams, D.A.
Chironomids:
Draper, N.R. and Smith, H. (1981).
221–230.
Brain, P. and Cousens, R. (1989).
Intra-specific variations of the susceptibility of insecticides in Chironomus yoshimatsui, Jp.
American Type Culture Collection
J. Sanit.
CCAP, Culture Collection of Algae and Protozoa
345–350.
Collection of Algal Cultures
Kawai, K. (1986).
University of Göttingen
Fundamental studies on chironomid allergy, I. Culture methods of some Japanese chironomids (Chironomidae, Diptera), Jp.
Nikolausberger Weg 18
47–57.
GERMANY
OECD (2000).
Section of Molecular, Cellular and Developmental Biology
23, ENV/JM/MONO(2000)6, OECD, Pariz.
7-15 × 3-12
The chironomid acute toxicity test:
40-50 [1]
353–361.
30-40 [1]
1163– 1175.
1,2-1,5
Naylor, C., in Rodrigues, C. (1995), Development of a test method for Chironomus riparius using a formulated sediment, Chemosphere, 31:
79,880 mg.
510–531.
0,714 mg.
94– 102.
0,006 mg.
Christensen, E. R. (1984), Dose-response functions in aquatic toxicity testing and the Weibull model, Water Res., 18:
Normalising by the mean control response gives some principle problems and gives rise to a rather complicated variance structure.
Dose-response modelling of continuous endpoints.
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).
1165– 1176.
The pH should be adjusted to 7,5 ± 0,5, if necessary;
Vogt, C., Belz, D., Galluba, S., Nowak, C., Oetken, M. in Oehlmann, J. (2007).
Finally, adsorptive substances should be also weighed directly into the test vessels; and the vessels should be silanised in order to minimise losses through adsorption.
Effects of cadmium and tributyltin on development and reproduction of the non-biting midge Chironomus riparius (Diptera) – baseline experiments for future multi-generation studies, J. Environ.
is the rate of oxygen uptake due to nitrification (mg/lh);
OECD (2010).
Brown, D., Hitz, H.R. and Schäfer, L. (1981).
Elendt, B. P., in W.-R.
Painter, H. A. (1986).
A steklena cev (notranji premer približno 5 mm), priključena na samosesalno črpalko;
Fiebig S. and Noack, U. (2004).
Pregled zadevnih preskusnih pogojev, specifičnih za validirane vrste, tj. japonsko medako, zeta in cebrico, je naveden v Dodatku 2.
The use of copper(II)sulphate pentahydrate as reference substance in the activated sludge respiration inhibition test — acc. to the OECD guideline 209.
30–70 %
ISO (1995).
Za polstatično tehniko se lahko uporabita dva različna postopka obnove;
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.
bodisi se pripravijo nove preskusne raztopine v čistih posodah ter se preživele ikre in ličinke nežno prenesejo v nove posode bodisi preskusni organizmi ostanejo v preskusnih komorah, medtem ko se vsak dan zamenja del (vsaj dve tretjini) preskusne vode.
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.
zadevne fizikalno-kemijske lastnosti, identifikacijski podatki kemikalije vključno s čistostjo in analitsko metodo za kvantifikacijo preskusne kemikalije.
US EPA — United States Environmental Protection Agency.
Jobling, S., Sheahan, D., Osborne, J. A., Matthiessen, P., in Sumpter, J. P. (1996).
AFNOR — Association Française de Normalisation.
Tyler, C. R., van Aerle, R., Hutchinson, T. H., Maddix, S. in Trip, H. (1999).
SSI — Swedish Standards Institute.
Holbech, H., Andersen, L., Petersen, G. I., Korsgaard, B., Pedersen, K. L. in Bjerregaard, P. (2001a).
Water quality — Determination of growth inhibition (7-d) Lemna minor, duckweed.
Orn, S., Holbech, H., Madsen, T. H., Norrgren, L., in Petersen, G. I. (2003).
Environment Canada.
Panter, G. H., Hutchinson, T. H., Lange, R., Lye, C. M., Sumpter, J. P., Zerulla, M., in Tyler, C. R. (2002).
Sims I., Whitehouse P. and Lacey R. (1999) The OECD Lemna Growth Inhibition Test.
Sun, L. W., Zha, J. M., Spear, P. A., in Wang, Z. J. (2007).
WRc plc — Environment Agency.
Parks, L. G., Cheek, A. O., Denslow, N. D., Heppell, S. A., McLachlan, J. A., LeBlanc, G. A., in Sullivan, C. V. (1999).
International Organisation for Standardisation.
Brion, F., Nilsen, B. M., Eidem, J. K., Goksoyr, A., in Porcher, J. M. (2002).
Lockhart W.
Nilsen, B. M., Berg, K., Eidem, J. K., Kristiansen, S. I., Brion, F., Porcher, J. M. in Goksoyr, A. (2004).
Huebert, D.B. and Shay J.M.
123, ENV/JM/MONO(2010)14, OECD, Pariz.
Bruce R.D. and Versteeg D.J.
Palace,V.
OECD.
Panter, G. H., Hutchinson, T. H., Hurd, K. S., Bamforth, J., Stanley, R. D., Duffell, S., Hargreaves, A., Gimeno, S., in Tyler, C. R. (2006).
Brain P. and Cousens R. (1989).
Holbech, H., Kinnberg, K., Petersen, G. I., Jackson, P., Hylland, K., Norrgren, L., in Bjerregaard, P. (2006).
Sources of Lemna species
Panter, G. H., Hutchinson, T. H., Hurd, K. S., Sherren, A., Stanley, R. D., in Tyler, C. R. (2004).
Toronto, Ontario, Canada, M5S 3 B2
Kinnberg, K., Holbech, H., Petersen, G. I., in Bjerregaard, P. (2007).
United States
OECD (2000).
SWEDEN
Guidance Document on Aquatic Toxicity Testing of Difficult Substances and Mixtures, Series on Testing and Assessment No.
Germany
23, OECD, Pariz.
Hillman, W.S.
OECD (2009).
Landolt, E. (1986).
Fish Short Term Reproduction Assay, Test Guideline No.
Björndahl, G. (1982).
229, Guidelines for the Testing of Chemicals, OECD, Pariz.
Wang, W.
OECD (2012).
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.
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, Pariz.
The plant material is then rinsed with sterile water and transferred, as a number of batches, into culture vessels containing fresh growth medium.
OECD (2011), Validation Report (Phase 2) for the Fish Sexual Development Test, Series on Testing and Assessment No 142, ENV/JM/MONO(2011)23, OECD, Pariz.
(mg/ߦl)
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, Pariz.
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.
27 ± 2 °C
AAP growth medium
20 ± 2 °C
Stock solutions are prepared in sterile distilled or deionised water.
30 %–70 %
Under these conditions the stock solutions will have a shelf life of at least 6 - 8 weeks.
(Druge metode se lahko uporabijo, če se izvajajo na ledu in zagotovijo homogeno maso.)
The 20 ml of each nutrient stock solution is added to approximately 850 ml deionised water to produce the growth medium.
Opozorilo:
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.
Absorpcija se meri pri 450 nm (npr. na čitalniku plošč Molecular Devices Thermomax).
Growth medium intended for testing should be prepared 1-2 days before use to allow the pH to stabilise.
Podatki se analizirajo s povezano programsko opremo (npr. Softmax).
(I. Sims, P. Whitehouse and R. Lacey.
385–398.
(1999) The OECD Lemna Growth Inhibition Test.
k 100 ml destilirane H2O
WRc plc — Environment Agency.)
5′ GGG ACG AGC AAG ATT TAT TGG 3′;
(g/ߦl) [1]
5′ TAT AGT TAG CCA GGA GAT GG 3′.
(mg/ߦl) [1]
raztopljeni organski ogljik,
Na;N
Preskusni medij se nasiči z zrakom pri preskusni temperaturi, tako da se 20 minut prezračuje s čistim stisnjenim zrakom.
190;84
Za namene kontrole se določi koncentracija raztopljenega kisika.
350 ± 50 μE/m2/s.
Schreurs, W.
For general chemicals, these include the physical/chemical properties of the chemical.
Hydrobiological Bulletin 12, 137–142.
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.
68,7 ± 30,7
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.
72,2 ± 18,8
The selected concentrations/rates should encompass the ECx or ERx values that are to be determined.
79,8 ± 28,0
A dose-response relationship is established in terms of a regression equation.
Kalcijev klorid dihidrat (CaCl2 · 2H2O)
Different models can be used:
0,10 g
International Organisation of Standards.
Za merjene vrednosti pH se pripravi dodatna ponovitev s preskusno snovjo.
Background — Non-target Plant Testing;
Birch, R. R., Biver, C., Campagna, R., Gledhill, W. E., Pagga, U., Steber, J., Reust, H., in Bontinck, W.
AFNOR, X31-201.
J. (1989).
Boutin, C., Freemark, K.E. and Keddy, C.J.
Screening of chemicals for anaerobic biodegradation.
Forster, R., Heimbach, U., Kula, C., and Zwerger, P. (1997).
Chemosphere 19, 1527– 1550.
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).
Mircobiology, 47, 850–857.
Hale, B., Hall, J.C., Solomon, K., and Stephenson, G. (1994).
Owen, W. F., Stuckey, DC., Healy J. B., Jr, Young L. Y., in McCarty, P. L. (1979).
Soil Texture Classification (US and FAO systems):
Healy, J. B. Jr., in Young, L. Y.
Beall, M.L., Jr. and Nash, R.G.
Gledhill, W.
Beetsman, G.D., Kenney, D.R. and Chesters, G. (1969).
E. (1979).
Boutin, C., and Rogers, C.A.
Chemosphere, 17, 2441–2460.
Patterns of sensitivity of plant species to various herbicides — An analysis with two databases.
Mednarodna organizacija za standardizacijo (1995) ISO 11 734 Kakovost vode – Vrednotenje ‚končne‘ anaerobne biorazgradljivosti organskih spojin v presnovljenem blatu – Metoda z merjenjem nastalega bioplina.
Boutin, C. and Harper, J.L.
Mednarodna organizacija za standardizacijo (2003) ISO 13 641-1 Kakovost vode – Določevanje zaviranja nastanka plina, ki ga proizvedejo anaerobne bakterije – 1. del: Splošen preskus.
Guidance Document, Current Approaches in the Statistical Analysis of Ecotoxicity Data:
Anaerobic biodegradation test for organic compounds.
Hatzios, K.K. and Penner, D. (1985).
Chemosphere, 27, 1499– 1509.
Hamill, P.B., Marriage, P.B. and G. Friesen.
Preskusna temperatura:
Frans, R.E. and Talbert, R.E.
(milibari)
Bruce, R.D. and Versteeg, D. J.(1992).
mv [7] …(mg):
Solanum lycopersicon
In progress in Pesticide Biochemistry and Toxicology, Vol.
0,09-0,17 (4, 19)
9 (Environmental Behaviour of Agrochemicals – T. R. Roberts in P. C. Kearney, ur.).
14-21 (100 %) (14)
Chiou, C. T., Porter, P. E., in Schmedding, D. W.