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Principle Principle of of Toxicity Toxicity Testing Testing Vladimír Kočí Vladimír Kočí Institute Institute of of Chemical Chemical Technology, Technology, Prague Prague Czech Czech Republic Republic 1 Bioassay Bioassay Experiments with organisms targetted to solve Experiments with organisms targetted to solve question how evaluated substance and/or sample question how evaluated substance and/or sample affect life in field condition. affect life in field condition. Both inhibitive and stimulative effect is Both inhibitive and stimulative effect is unaccetable. unaccetable. Intensity of effect is influenced by concentration Intensity of effect is influenced by concentration and/ot duration of exposition. and/ot duration of exposition. 2 Aim of Science on the Field of Aim of Science on the Field of Ecotoxicological Bioassays Ecotoxicological Bioassays The development of new standard methods. The development of new standard methods. Standard Standard – reproducible conditions, reproducible conditions, Comparison of effects of different substances Comparison of effects of different substances and/od different organisms and/od different organisms Reproducible between different laboratories Reproducible between different laboratories 3 Basic principles of bioassays Basic principles of bioassays Reproducibility Reproducibility Standard design Standard design Possibility of data extapolation on field conditions Possibility of data extapolation on field conditions Economy feasibility Economy feasibility Time feasibility Time feasibility 4

05 Principles Tox Testing Factors

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  • PrinciplePrinciple ofof Toxicity Toxicity TestingTesting

    Vladimr KoVladimr Ko

    Institute Institute ofof ChemicalChemical Technology, Technology, PraguePrague

    CzechCzech RepublicRepublic

    11

    BioassayBioassay Experiments with organisms targetted to solve Experiments with organisms targetted to solve question how evaluated substance and/or sample question how evaluated substance and/or sample affect life in field condition. affect life in field condition.

    Both inhibitive and stimulative effect is Both inhibitive and stimulative effect is unaccetable.unaccetable.

    Intensity of effect is influenced by concentration Intensity of effect is influenced by concentration and/ot duration of exposition.and/ot duration of exposition.

    22

    Aim of Science on the Field of Aim of Science on the Field of Ecotoxicological BioassaysEcotoxicological Bioassays

    The development of new standard methods.The development of new standard methods.

    Standard Standard reproducible conditions, reproducible conditions,

    Comparison of effects of different substances Comparison of effects of different substances and/od different organismsand/od different organisms

    Reproducible between different laboratoriesReproducible between different laboratories

    33

    Basic principles of bioassaysBasic principles of bioassays ReproducibilityReproducibility

    Standard designStandard design

    Possibility of data extapolation on field conditionsPossibility of data extapolation on field conditions

    Economy feasibilityEconomy feasibility

    Time feasibilityTime feasibility

    44

  • BiotestBiotest BioassayBioassay isis a a processprocess wherewhere isis a test systm a test systm ((tissuetissue,,organismorganism, , populationpopulation) ) exposedexposed underunderdefineddefined conditionsconditions to to differentdifferent knownknownconcentrationsconcentrations ofof testedtested compoundcompound oror sample.sample.

    EcotoxicologicalEcotoxicological bioassaysbioassays are such a are such a bioassaysbioassayswhatwhat forfor evaluationevaluation ofof observedobserved phenomenonphenomenon use use such a such a detectiondetection systemssystems ((tissuetissue, , organismorganism,) ,) whatwhat enableenable relevantrelevant interpretationinterpretation forforenvironmentalenvironmental conditionsconditions. .

    55

    Structuring of bioassaysStructuring of bioassaysDuration of expositionDuration of exposition

    AcuteAcute

    SemiSemi--acuteacute

    ChronicChronic

    66

    Structuring of bioassaysStructuring of bioassaysDesign, generationDesign, generation

    1st. generation 1st. generation -- classic (standard)classic (standard)

    2nd. generation 2nd. generation -- microbioassaysmicrobioassays

    3rd. generation 3rd. generation -- biosenzors, biomarkersbiosenzors, biomarkers

    77

    MicrobioassayMicrobioassay Economy ReasonsEconomy Reasons

    Saving ofSaving of

    TimeTime

    SpaceSpace

    WorkWork

    ChemicalsChemicals

    1. Batching

    2. Inoculation

    3. Exposition

    88

  • Structuring of bioassaysStructuring of bioassaysTrophic levelTrophic level

    ProducentProducent

    ConsumentConsument

    DestruentDestruent

    99

    Structuring of bioassaysStructuring of bioassaysTested matrixTested matrix

    WaterWater

    SoilSoil

    AirAir

    SedimentSediment

    WasteWaste

    Chemical compoundChemical compound

    1010

    Structuring of bioassaysStructuring of bioassaysSpectrum of organismsSpectrum of organisms

    Single SpeciesSingle Species

    Multi Species Multi Species -- wildlife populations / laboratory wildlife populations / laboratory mixturemixture

    1111

    Structuring of bioassaysStructuring of bioassaysType of sampleType of sample

    Pure compounds (hydrophobic, hydrophilic, Pure compounds (hydrophobic, hydrophilic, volatile)volatile)

    Mixture of compounds (known and/or unknown)Mixture of compounds (known and/or unknown)

    Environmental samples (usually unknown, Environmental samples (usually unknown, mixtures of different compounds with different mixtures of different compounds with different properties properties complicated interpretation)complicated interpretation)

    1212

  • Structuring of bioassaysStructuring of bioassaysPretreatmentPretreatment

    Defined very concentration of substancesDefined very concentration of substances

    Eluates, extracts of environmental samples Eluates, extracts of environmental samples liquid final sample, Whole Effluentliquid final sample, Whole Effluent

    Direct Tests, Solid Phase TestsDirect Tests, Solid Phase Tests

    Comparative tests of sorbtion matrix (for Comparative tests of sorbtion matrix (for example SPMD)example SPMD)

    1313

    Structuring of bioassaysStructuring of bioassaysComplexity of detection systemComplexity of detection system

    From the simplest to the more integralFrom the simplest to the more integral

    Enzymes, bioprobes, cell and tissue cultures in Enzymes, bioprobes, cell and tissue cultures in vitrovitro

    Whole living organismWhole living organism

    PopulationPopulation

    Micro/mezo kosmosMicro/mezo kosmos

    Field studyField study

    1414

    Structuring of bioassaysStructuring of bioassaysType of endpointType of endpoint

    Lethal effects (mortality)Lethal effects (mortality)

    sub lethal effects (immobilisation)sub lethal effects (immobilisation)

    Physiological activity (photosynthetic activity, Physiological activity (photosynthetic activity, enzymatic activity, biomass increase, resistance enzymatic activity, biomass increase, resistance to diseases, pests and/or parasitesto diseases, pests and/or parasites

    Reproductive activity, malformations, Reproductive activity, malformations, reproductive activityreproductive activity

    1515

    Special tests for Risc Special tests for Risc AssessmentAssessment

    AGP AGP

    Mutagenicity/genotoxicity (microbial, vascular Mutagenicity/genotoxicity (microbial, vascular plants, wildlife animals)plants, wildlife animals)

    Teratogenity (amphibianTeratogenity (amphibian-- Xenopus laevis)Xenopus laevis)

    EmbryotoxicityEmbryotoxicity

    Reproduction bioassaysReproduction bioassays

    Useful for clearly defined cases, where lethal Useful for clearly defined cases, where lethal effect as an endpoint is not appropriate for effect as an endpoint is not appropriate for interpretation.interpretation.

    1616

  • Battery of assaysBattery of assays The negative response in test with one specie The negative response in test with one specie does not means that substance is not toxic.does not means that substance is not toxic.

    Toxicity can be observed after longer exposition Toxicity can be observed after longer exposition and/or on different species.and/or on different species.

    Simple battery: algae, zooplancton, fish, Simple battery: algae, zooplancton, fish, bacteria.bacteria.

    1717

    Batery of bioassaysBatery of bioassays DifferentDifferent

    Trophic levelTrophic level

    SensitivitySensitivity

    Target effect/organTarget effect/organ

    Specific toxic effect (mutagenity, neurotoxicity, Specific toxic effect (mutagenity, neurotoxicity, etc)etc)

    1818

    Exposition testsExposition tests Exposed organism do not reproduce during time Exposed organism do not reproduce during time of assay.of assay.

    Quick.Quick.

    Influence on photosynthesis; synthesis of ATP, Influence on photosynthesis; synthesis of ATP, movement of organs.movement of organs.

    Mortality, immobilisationMortality, immobilisation

    1919

    Growth, reproductive testsGrowth, reproductive tests Better and more sensitive. Better and more sensitive.

    Reproductive process is the most sensitive Reproductive process is the most sensitive moment of living organism. moment of living organism.

    If no adverse effect will be observed during 3 If no adverse effect will be observed during 3 generations, there is very probable that testing generations, there is very probable that testing organism is not sensitive to tested concentration organism is not sensitive to tested concentration of toxicant.of toxicant.

    Nap.: Algal assay, daphnia reproductive assay, Nap.: Algal assay, daphnia reproductive assay, root prolongation testroot prolongation test

    2020

  • Standard toxicity Standard toxicity teststests Battery of bioassays:Battery of bioassays:

    algae, plants, zooplancton, fish, (bacterium)algae, plants, zooplancton, fish, (bacterium)

    2121

    Factors influencing results of Factors influencing results of bioassaysbioassays

    For reproducibility of results these main For reproducibility of results these main factors has to be standardized:factors has to be standardized:

    Time of expositionTemperatureLight period

    VolumeOxygen

    Composition of cultivation mediaAge of organism

    2222

    Limit Test negative

    Range finding Test

    Basic Test

    Data treatment

    Verify Test

    positive

    negativepositive, response 50%

    positive, response < 50%

    Sampling

    Pretreatment of sample(eluate, extract, pH, oxygen)

    2323

    SamplingSampling Way of sampling importantly influence results of Way of sampling importantly influence results of bioassaybioassay

    2424

  • PretreatmentPretreatment Pretreatment influence the chemical properties of Pretreatment influence the chemical properties of substances present in sample and thus their substances present in sample and thus their biological activity.biological activity.

    The manner of pretreatment can diverse activity The manner of pretreatment can diverse activity od different toxicants presented in sample.od different toxicants presented in sample.

    Treatment of pH, dewatering, filtration, aeration, Treatment of pH, dewatering, filtration, aeration, salinity treatmentsalinity treatment

    2525

    Pretreatment Pretreatment adjustment of adjustment of sample with a goalsample with a goal

    Distinguish toxicantsDistinguish toxicants

    Elimination of interferencesElimination of interferences

    2626

    TemperatureTemperature Sterilization Sterilization -- autoclave, environmental samplesautoclave, environmental samples

    Denaturation of proteins, pesticidesDenaturation of proteins, pesticides

    Decomposition of thermo labile compoundsDecomposition of thermo labile compounds

    Pointing out thermo stabile compoundsPointing out thermo stabile compounds

    Better do not carry outBetter do not carry out

    2727

    Osmotic pressureOsmotic pressure Low soluble sample Low soluble sample low osmotic pressurelow osmotic pressure

    Marine organisms Marine organisms need for higher osmotic need for higher osmotic pressurepressure

    Needed addition of cultivation saltsNeeded addition of cultivation salts

    The change of mineralization can change form The change of mineralization can change form and amount of solved substances.and amount of solved substances.

    2828

  • AerationAeration Oxygen for organismsOxygen for organisms

    Decrease of volatile substancesDecrease of volatile substances

    Changes in pHChanges in pH

    Stripping Stripping elimination of interference volatile elimination of interference volatile substancessubstances

    2929

    pH treatmentpH treatment Chemical form and thus toxic properties of Chemical form and thus toxic properties of substances can be modified. Metals, ammonium substances can be modified. Metals, ammonium ionion

    pH can be mentioned as a part of adverse effectspH can be mentioned as a part of adverse effects

    If the toxicity of sample is high, buffering ability If the toxicity of sample is high, buffering ability of media water solve pH problem. of media water solve pH problem.

    3030

    Pretreatment, liquid samplesPretreatment, liquid samples Aquatic organisms Aquatic organisms direct testingdirect testing

    Solubility in water is not grantedSolubility in water is not granted

    Some liquid substances form foam, emulsion Some liquid substances form foam, emulsion and/or jelly with water. and/or jelly with water.

    Oganic chemicals have to be examined for Oganic chemicals have to be examined for solubility in water.solubility in water.

    3131

    Pretreatment, solid samplesPretreatment, solid samples A) conversion into liquid form (leachate, extract) A) conversion into liquid form (leachate, extract) => aquatic organisms=> aquatic organisms

    Version Version -- solid phase test solid phase test -- suspensionsuspension

    B) terrestrial, contact bioassays (constant B) terrestrial, contact bioassays (constant moisture) => soil organismsmoisture) => soil organisms

    3232

  • Pretreatment of solid samples Pretreatment of solid samples for aquatic bioassaysfor aquatic bioassays

    Leachate Leachate useful for in water well soluble useful for in water well soluble substancessubstances

    Acid leachate Acid leachate for substances well soluble in for substances well soluble in lower pH lower pH metalsmetals

    Water saturated with CO2. Water saturated with CO2.

    Extract Extract organic, hydrophobic compounds organic, hydrophobic compounds (solvents: methanol, aceton, DMSO).(solvents: methanol, aceton, DMSO).

    3333

    Leachate of solid samplesLeachate of solid samplesChoice of Choice of leachateleachate pH influence pH influence which substances (or chemical which substances (or chemical form) will be form) will be eluatedeluated and thus and thus resulting toxicityresulting toxicity

    Systems of Systems of leachateleachate buffers, buffers, offering possibility of continuous offering possibility of continuous changing of pH from pH 2 to pH 12changing of pH from pH 2 to pH 12

    HO

    H

    3434

    Pretreatment of sample, Pretreatment of sample, leachateleachate

    After homogenization of sample dry content is After homogenization of sample dry content is determined, 105determined, 105C. C.

    24 hours of shaking in tilt24 hours of shaking in tilt--over shakerover shaker

    Filtration, porosity 5 Filtration, porosity 5 m.m. SShelf lifehelf life up to 1 month, 4up to 1 month, 4CC

    3535

    Extraction of solid samplesExtraction of solid samples Extract = organic solvent Extract = organic solvent

    (water = leachate)(water = leachate)

    Extract Extract hydrophobic contaminationhydrophobic contamination

    DMSO, methanol, ethanol, aceton, octanol, DMSO, methanol, ethanol, aceton, octanol, hexanol, isopropanolhexanol, isopropanol

    3636

  • Dewatering of solid samplesDewatering of solid samples Toxicological data are referred to weight of soil.Toxicological data are referred to weight of soil.

    It is necessary to keep exact moisture of sample.It is necessary to keep exact moisture of sample.

    Dewatering is usually carried out in air stream at Dewatering is usually carried out in air stream at room temperature. room temperature. Until constant weight.Until constant weight.

    3737

    Pretreatment of solid samples Pretreatment of solid samples for terrestrial assaysfor terrestrial assays

    HomogenisationHomogenisation

    AgitationAgitation

    Grinding, crushing down to recommended Grinding, crushing down to recommended gradinggrading

    3838

    Pretreatment Pretreatment -- summarysummary Pretreatment imortantly influence final data of Pretreatment imortantly influence final data of bioassays. bioassays.

    The manner of pretreatment has to been chosen The manner of pretreatment has to been chosen regarding to:regarding to:

    Final interpretation of dataFinal interpretation of data

    Objective of study (what we want to know)Objective of study (what we want to know)

    Detailed specification of pretreatment should be a Detailed specification of pretreatment should be a part of final report of bioassaypart of final report of bioassay

    3939

    Standard toxicantStandard toxicant

    Standard ZnSO4 . 7H2O K2Cr2O7 p-nitrofenol

    Average value EC50, mg.l-1

    9,6 0,67 12,9

    Range EC50, mg.l-1 1-25 0,62,1 5-20

    Example for Daphnia magna, 48 Hours

    4040

  • MediaMedia Composition of media (water, soil) has strong Composition of media (water, soil) has strong impact on results.impact on results.

    Standardization is needed.Standardization is needed.

    4141

    Composition of water mediaComposition of water media Fish, daphnidsFish, daphnids

    CaCl2 . 2H2OCaCl2 . 2H2O

    MgSO4.7H2OMgSO4.7H2O

    NaHCO3NaHCO3

    KClKCl

    AlgaeAlgae

    NaNO3NaNO3

    Ca(NO3)2 . 4H2OCa(NO3)2 . 4H2O

    K2HPO4K2HPO4

    MgSO4 . 7H2OMgSO4 . 7H2O

    Na2CO3Na2CO3

    FeFe--EDTAEDTA

    Gaffron solutionGaffron solution

    4242

    Limit testLimit test To recognize if the samle is toxic or not.To recognize if the samle is toxic or not.

    4343

    Limit testLimit test Unknown sample is overviewed if it is or is not Unknown sample is overviewed if it is or is not toxic.toxic.

    Two parallels with two controls are usually Two parallels with two controls are usually carrying out.carrying out.

    If no response is observed, the test is interpreted If no response is observed, the test is interpreted as negative. Verify test follows. as negative. Verify test follows.

    If response is observed then RangeIf response is observed then Range--finding test finding test follows.follows.

    4444

  • Vertification testVertification test

    To verify negative result from previous limit test.To verify negative result from previous limit test.

    More parallels more organismsMore parallels more organisms

    4545

    Range finding testRange finding test To find interval, where EC50 can be expectedTo find interval, where EC50 can be expected

    Wide range of concentrationsWide range of concentrations

    Small number of organismsSmall number of organisms

    4646

    Basic testBasic test Exact determination of EC50Exact determination of EC50

    Usually at least 7 concentrations, based on range Usually at least 7 concentrations, based on range finding test.finding test.

    2 2 -- 3 paralels3 paralels

    Accompanying parameters should be recorded at Accompanying parameters should be recorded at the beggining and on the end of exposition the beggining and on the end of exposition (pH,O2, temperature)(pH,O2, temperature)

    4747

    EndpointEndpoint DeathDeath

    Inhibition of growthInhibition of growth

    ImmobilisationImmobilisation

    Inhibition of physiological function Inhibition of physiological function (bioluminiscence)(bioluminiscence)

    Etolgical observationEtolgical observation

    4848

  • Ecotoxicological parametersEcotoxicological parameters Magnitudes focused on kvantitative description Magnitudes focused on kvantitative description of substance effect on organism.of substance effect on organism.

    Function: estimate of risk, evaluation of Function: estimate of risk, evaluation of environmental acceptability of substances, environmental acceptability of substances, comparation of toxic effect of different samplescomparation of toxic effect of different samples

    Output of toxicity testing (TIE).Output of toxicity testing (TIE).

    4949

    Calculated parametersCalculated parameters EC 50 : Effective concentration of tested toxicant EC 50 : Effective concentration of tested toxicant causing 50% response of testing population. causing 50% response of testing population.

    EEffective ffective CConcentrationoncentration, mg/L, ml/L, mg/L, ml/L

    Lethal Concentration, LC50Lethal Concentration, LC50

    Inhibition Concentration, IC50Inhibition Concentration, IC50

    EC05, EC20, EC90, EC05, EC20, EC90,

    5050

    Determined parametersDetermined parameters NOEC: No Observed Effect Concentration. The NOEC: No Observed Effect Concentration. The highest tested concentration of toxicant what do highest tested concentration of toxicant what do not cause statistically significant effect in not cause statistically significant effect in comparing to control.comparing to control.

    LOEC: The immediate higher concentration than LOEC: The immediate higher concentration than NOEC.NOEC.

    NOEL: No Observed Effect Level.NOEL: No Observed Effect Level.

    NOAEL: No Observed Adverse Effect Level. The effect NOAEL: No Observed Adverse Effect Level. The effect is observed, but do not considered as dangerous.is observed, but do not considered as dangerous.

    5151

    Design of toxicity testDesign of toxicity testControl 6 mg/L 12 mg/L 25 mg/L 50 mg/L 100 mg/L

    Exposed 20 pcsExposed 20 pcs

    Response after 24 hours, pcsResponse after 24 hours, pcs

    00 00 11 66 1313 1717

    Response after 96 hours, pcsResponse after 96 hours, pcs

    00 00 44 99 1515 2020

    5252

  • Recording of testRecording of test

    ConcentrationConcentration ControlControl 6 mg/L6 mg/L12 12

    mg/Lmg/L25 25

    mg/Lmg/L50 50

    mg/Lmg/L100 100 mg/Lmg/L

    EffectEffect

    24 hour24 hour 0%0% 0%0% 5%5%3030%%

    6565%%

    85%85%

    EffectEffect

    96 hour96 hour 0%0% 0%0%2020%%

    3535%%

    7575%%

    100100%%

    5353

    Dvka-Odpov

    0 25 50 75 1000

    25

    50

    75

    100 24 hod.96 hod.

    Koncentrace

    M

    o

    r

    t

    a

    l

    i

    t

    a

    Dose - response

    24 hrs96 hrs

    M

    o

    r

    t

    a

    l

    i

    t

    y

    Concentration

    5454

    Ideal dose Ideal dose response curveresponse curve

    0

    20

    40

    60

    80

    100

    0 500 1000Concentration

    e

    f

    f

    e

    c

    t

    ,

    %

    Linear scale is often blind

    5555

    Ideal dose Ideal dose response curveresponse curve

    0102030405060708090

    100

    0,1 1 10 100 1000 10000

    Logaritmic scale

    Estimate of EC50

    Lethal effects

    LC

    Non toxic

    NOECLOEC

    5656

  • Presentation of resultsPresentation of results EC50 + confidence intervals,95%EC50 + confidence intervals,95%

    NOEC, EC05NOEC, EC05

    LOEC, EC20LOEC, EC20

    LC, EC95LC, EC95

    5757