FOCUS Kinetics training workshop Chapter 7 Recommended Procedures to Derive Endpoints for Parent Compounds Ralph L. Warren, Ph.D. DuPont Crop Protection Delaware, USA 26-27 Jan 2005 Page 1 FOCUS Kinetics training workshop Presentation Objectives of this part of the training: • Description of the procedures to follow for a parent compound to derive endpoints for use as a) trigger values for additional work b) inputs for environmental exposure models (e.g. PECgw) • Assessment of kinetic model fits to the observed data using visual and statistical techniques. • Selection of the appropriate kinetic model and endpoints for the case of triggers and exposure modelling. 26-27 Jan 2005 Hands on exercise using Excel spreadsheet Page 2 FOCUS Kinetics training workshop Why the distinction between fitting for trigger endpoints versus exposure modelling endpoints? • Regulatory triggers are based on DT50 and DT90 values which are not constrained to any kinetic model form. The model that most appropriately describes the observed data should be used to generate the endpoint values. • Current regulatory environmental exposure models are based on SFO kinetics. Therefore, an endpoint (i.e. DT50) calculated using a non-SFO kinetic model will not appropriately represent the observed behavior when input into a SFO-based exposure model. A SFO endpoint, if appropriate, or a conservative estimate or a ‘work around’ must be used. 26-27 Jan 2005 Page 3 FOCUS Kinetics training workshop The same DT50 does not mean the same pattern of decline when calculated using different kinetic models 100 90 SFO FOMC DFOS DFOP M0 = 100% and DT50 = 5 days in each case 80 % remaining_ 70 60 50 40 30 20 10 0 0 5 10 15 20 25 30 35 time (days) 26-27 Jan 2005 Page 4 FOCUS Kinetics training workshop Regulatory triggers – examples Annex II to Directive 91/414/EEC • 7.1.1.2.2. Field dissipation studies are required when DT50lab > 60 days at 20C or 90 days at 10 C Annex III to Directive 91/414/EEC • 10.7.1 Testing for effects on soil micro-organisms required when DT90field > 100 days Draft Guidance Doc. Terrestrial Ecotoxicology (SANCO/10329/2002 rev. 2 final) • Sub-lethal earthworm tests required depending on number of applications and DT90field Guidance Doc. Aquatic Ecotoxicology (SANCO/3268/2001 rev. 4 final) • Chronic study on daphnids required when DT50 in water > 2 days 26-27 Jan 2005 Page 5 FOCUS Kinetics training workshop So what’s involved in the fitting procedure? Triggers for additional work modelling endpoints • Run SFO and FOMC as a first step • Run SFO as a first step • Check visual fit and calculate error percentage at which 2 test passed • If FOMC better than SFO, test other bi-phasic models • Check visual fit and calculate error percentage at which 2 test passed • If error % < 15% and visual fit acceptable, use SFO DT50 • If error % > 15% and visual fit not acceptable, run bi-phasic model • Use best model fit • If 10% of initial reached in study period then calculate DT50 as FOMC DT90/3.32 • If 10% of initial not reached in study period then use longer DT50 from slow phase of HS or DFOP Check optimized parameter uncertainty! 26-27 Jan 2005 Page 6 FOCUS Kinetics training workshop Chi-square (2) test statistic 2 C O 2 err 100 O 2 where C = calculated value O = observed value O = mean of observed (element of scale) err = measurement error (element of proportionality) If 2 > 2m, then the model is not appropriate at the chosen sig. level where m = degrees of freedom (No. of obs. used in the fitting – No. of optimized model parameters) = level of significance, typically 5% Remember to use average values where there are replicates! 26-27 Jan 2005 Page 7 FOCUS Kinetics training workshop Chi-square (2) test statistic • Since the measurement error is typically unknown (would require numerous replicate measurements) a common error model was proposed. The percent error value is scaled to the mean of the observed values. Therefore, the error term is constant through the measurement period. • The relative error is lower for early time points and increases for later time points, which is consistent with the recommendation for unweighted fitting. • The minimum error percentage at which the test is passed can be directly calculated. err 100 1 2 tabulated C O 2 O 2 2 where: C = calculated, O = observed, O = mean of observed, and 2tabulated = lookup value of 2 at the 0.05 significance level for the appropriate degrees of freedom (no. obs. values used in fitting – no. optimized parameters) 26-27 Jan 2005 Page 8 FOCUS Kinetics training workshop Chi-square (2) test statistic • The model with the lower 2 error percentage is defined as more appropriate. • Note that field data are inherently more variable than lab data. Therefore the error percentages at which 2 is passed will be larger. • Further note there is no inherent and definitive error value for any given test system. Choice of an acceptable value is pragmatic and should be considered in light of the visual assessment and parameter uncertainty. 26-27 Jan 2005 Page 9 FOCUS Kinetics training workshop Visual Assessment • Subjective, yet powerful tool for assessing goodness of fit. • Keeps common sense in the assessment process. • Two recommended plots > Plot of fitted versus observed over time (typical plot) > Plot of residuals (Predicted – Observed) over time 100 90 80 15 70 10 5 50 residual % AR 60 40 30 0 0 20 40 60 80 100 120 140 -5 20 -10 10 -15 -20 0 0 20 40 60 80 100 120 t (days) t (days) 26-27 Jan 2005 Page 10 FOCUS Kinetics training workshop Parameter uncertainty • Confidence intervals or t-tests may be used. • The t-test is shown below, which assumes normally distributed parameters. t where âi = estimate of parameter i i = standard error of parameter i aˆi i • The probability (p-value) for the calculated t-value can be read from statistical tables or calculated with Excel TDIST(tcaclulated,df,1) • If p is < 0.05 then the parameter is considered significantly different than zero. If p is between 0.05 and 0.1 then weight of evidence should be considered. • The t-test is most applicable to degradation rates (k), not necessarily other parameters such as or for FOMC. 26-27 Jan 2005 Page 11 FOCUS Kinetics training workshop Parent only flow chart for deriving trigger endpoints Triggers flowchart Data entry M0 free, use all data, no weighting STEP 1: SFO appropriate? RUN SFO, FOMC (zoom to view) NO Modify fitting routine stepwise: 1. Exclude outliers 2. Constrain M0 3. Weighting SFO more appropriate than FOMC and gives acceptable fit? YES STOP RUN modified fitting SFO more appropriate than FOMC & fit acceptable? (modified fitting) YES STOP NO Deviation from SFO due to experimental artifact/decline in microbial activity? YES see text NO STEP 2: Identify best model other than SFO RUN DFOP (unmodified & modified fitting routine) Determine which of the models (FOMC, DFOP) is best STEP 3: Evaluate goodness of fit Case-by-case decision (see text) 26-27 Jan 2005 NO Does the best-fit model give an acceptable description of the data? YES STOP Page 12 FOCUS Kinetics training workshop modelling flowchart Parent only flow chart for deriving exposure modelling endpoints (zoom to view) Data entry M0 free, use all data, no weighting STEP 1: SFO appropriate? RUN SFO NO Modify fitting routine for SFO stepwise: 1. Exclude outliers 2. Constrain M0 3. Weighting SFO statistically and visually acceptable? YES Use SFO DT50 for fate modelling RUN modified SFO until best SFO fit achieved SFO statistically and visually acceptable? YES Use SFO DT50 (modified fitting routines) for fate modelling YES Aim: modelling metabolite fate linked to parent? NO STEP 2:Correction procedure NO Case-by-case decision (see text) Bi-phasic pattern? (assess experimental artefacts!) YES YES see text Aim: modelling fate of parent only? YES NO RUN HS or DFOP HS or DFOP statistically and visually acceptable? NO Case-by-case decision (see text) 26-27 Jan 2005 YES Use DT50 from slow phase of HS of DFOP model for fate modelling 10% initially measured concentration reached within experimental period? YES RUN FOMC FOMC statistically and visually acceptable? NO Case-by-case decision (see text) YES Back-calculate DT50 from DT90 for FOMC (DT50 = DT90 / 3.32) Page 13 FOCUS Kinetics training workshop Let’s look at an example for the triggers flowchart… % of applied radioactivity 0 0 3 3 7 7 14 14 30 30 45 45 62 62 90 90 120 120 93.1 99.7 72.9 83.8 60.3 60.3 41.7 37.4 23.3 26.0 20.9 17.1 18.8 18.8 17.9 18.5 16.7 15.9 26-27 Jan 2005 100 90 Laboratory degradation of a compound in aerobic soil 80 70 60 % AR Time (days) 50 40 30 20 10 0 0 20 40 60 80 100 120 t (days) Page 14 FOCUS Kinetics training workshop 100 100 90 90 SFO 80 80 70 2 70 error = 19% % AR DT50 = 18.1 d 50 DT90 = 60.2 d 40 2 error = 7% 60 60 % AR FOMC 50 DT50 = 10.6 d 40 DT90 = 160 d 30 30 20 20 10 10 0 0 0 20 40 60 80 100 0 120 20 40 60 10 10 5 5 0 20 40 60 80 100 120 140 residual residual 15 0 0 20 40 60 80 100 120 140 -5 -10 -15 -15 -20 -20 t (days) 120 0 -10 26-27 Jan 2005 100 t (days) t (days) 15 -5 80 t (days) Page 15 FOCUS Kinetics training workshop 100 100 FOMC 90 80 80 2 error = 7% 70 2 error = 1% 70 60 60 DT50 = 10.6 d 50 % AR % AR DFOP 90 DT90 = 160 d 40 DT50 = 10.0 d DT90 = 472 d 50 40 30 30 20 20 10 10 0 0 0 20 40 60 80 100 0 120 20 40 60 10 10 5 5 0 20 40 60 80 100 120 140 residual residual 15 0 0 20 40 60 80 100 120 140 -5 -10 -15 -15 -20 -20 t (days) 120 0 -10 26-27 Jan 2005 100 t (days) t (days) 15 -5 80 t (days) Page 16 FOCUS Kinetics training workshop Parameter uncertainty Model Parameter Optimized value Standard error Different than zero? (t-test) SFO M0 k 86.98 0.0382 5.399 0.0061 -Yes FOMC M0 98.20 0.7063 6.372 3.032 0.1038 1.976 ---- DFOP M0 g k1 k2 96.79 0.7914 0.09305 0.00149 1.768 0.0326 0.0085 0.00195 --Yes No (P=0.229) 26-27 Jan 2005 Page 17 FOCUS Kinetics training workshop Possible conclusions for this data set for the trigger flowchart • Use DFOP with associated endpoints > DT50 = 10.0 d, DT90 = 472 d > Relax t-test criteria for k2 based on visual fit and 2. > Check if other aerobic soil deg and fate studies support this DT90. • Use DFOP. Fix k2 to a conservative value (e.g. 1000 d) > 2 and visual fits equivalent to above. > DT50 = 10.1 d, DT90 = 922 d > Check if other aerobic soil deg and fate studies support this DT90. • For comparison with regulatory DT50 triggers, the result is the same. • For comparison with regulatory DT90 triggers, the result is the same. 26-27 Jan 2005 Page 18 FOCUS Kinetics training workshop Continuing with the same data, now let’s look at it using the modelling flowchart… 26-27 Jan 2005 Page 19 FOCUS Kinetics training workshop 100 100 90 SFO 90 80 80 70 70 2 error = 19% 60 2 error = 7% 60 DT50 = 18.1 d 50 % AR % AR FOMC DT90 = 60.2 d 40 50 DT50 = 10.6 d 40 DT90 = 160 d 30 30 20 20 10 10 0 0 0 20 40 60 80 100 120 0 20 40 60 15 10 10 5 5 0 0 20 40 60 80 -5 100 120 140 0 20 40 60 80 100 120 140 -5 -10 -15 -15 26-27 Jan 2005 120 0 -10 -20 100 t (days) 15 residual residual t (days) 80 -20 t (days) t (days) Page 20 FOCUS Kinetics training workshop • Assuming no artifacts, the data is clearly bi-phasic. FOMC fit to the data is superior based on visual assessments and 2 error. • If aim of modelling is to link parent with metabolites, then the guidance in Chapter 8 should be followed (covered tomorrow). • If the aim is to model parent fate only then check to see if 10% of the initially measured value was reached during the study period. > If yes, then use FOMC DT90/3.32 to derive a conservative estimate of SFO DT50 for modelling (i.e. 160 d/3.32 = 48.2 d). > If no, then use slower k from HS or slower k from DFOP to derive a conservative estimate of DT50 for modelling. 26-27 Jan 2005 Page 21 FOCUS Kinetics training workshop FOMC DT90/3.32 example (assume last point did reach 10%) 100 O SFO FOMC FOMC DT90/3.32 90 80 % AR 70 60 SFO DT50 = 18.1 d DT90 = 60.2 d FOMC DT50 = 10.6 d DT90 = 160 d FOMC DT90/3.32 = 48.2 d (SFO) 50 40 30 20 10 0 0 20 40 60 80 100 120 t (days) FOMC DT90/3.32 is a conservative option where parent only exposure modelling is desired (can’t link to metabolites!) 26-27 Jan 2005 Page 22 FOCUS Kinetics training workshop 100 100 HS 90 2 error = 3% 80 90 DFOP 80 2 error = 1% 70 70 DT50 fast phase = 10.7 d DT50 slow phase = 175 d 50 60 % AR % AR 60 50 40 40 30 30 20 20 10 10 0 0 0 20 40 60 80 100 120 0 20 40 60 t (days) 15 80 100 120 t (days) 15 10 10 5 5 0 0 20 40 60 80 -5 100 120 residual residual DT50 fast phase = 7.4 d DT50 slow phase = 466 d 0 140 0 -10 -10 -15 -15 -20 26-27 Jan 2005 20 40 60 80 100 120 140 -5 -20 t (days) t (days) Page 23 FOCUS Kinetics training workshop Parameter uncertainty Model Parameter Optimized value Standard error Different than zero? (t-test) HS M0 tb k1 k2 95.81 21.92 0.06448 0.00397 1.82 1.70 0.00375 0.00162 --Yes Yes DFOP M0 g k1 k2 96.79 0.7914 0.09305 0.00149 1.768 0.0326 0.0085 0.00195 --Yes No (P=0.229) 26-27 Jan 2005 Page 24 FOCUS Kinetics training workshop Possible conclusions for this data set for the modelling flowchart • Use longest phase of HS to derive conservative value of DT50 > 10% of initial not reached, so HS and DFOP were assessed. > Longest k from DFOP is not different than zero so it is unreliable. • Conduct higher-tier modelling using conservative value for DFOP slow phase DT50 (e.g. 1000 d). 26-27 Jan 2005 Page 25 FOCUS Kinetics training workshop Questions? 26-27 Jan 2005 Page 26 FOCUS Kinetics training workshop Now it’s your turn to work through the flowcharts using the observed and fitted data from this morning… 26-27 Jan 2005 Page 27