TABLE 4:
Summary of the 250 species and metal combination entries in the compilation of metal bioavailability toxicity model studies in Supplemental Data, Table S1
| Category | Typea | Percent (number)b |
|---|---|---|
| Type of model | BLMc | 66.0 (165) |
| WHAM-FTOXd | 11.6 (29) | |
| MRM | 14.8 (37) | |
| Mixed | 9.2 (23) | |
| FIAM | 4.4 (11) | |
| Hardness | 1.6 (4) | |
| GLMM + WHAM | 0.4 (1) | |
| MixTox | 0.4 (1) | |
| TKTD | 0.4 (1) | |
| TOX | 0.4 (1) | |
| WHAM regression | 0.4 (1) | |
| Type of validation | Autovalidation | 49.6 (124) |
| Independent validation | 25.6 (64) | |
| Autovalidation and independent validation | 16.8 (42) | |
| Cross-species extrapolation | 8.0 (20) | |
| Method used to present results | Predicted versus observed (1:1) plot | 80.4 (201) |
| Other graphical method | 17.6 (44) | |
| Table | 5.2 (13) | |
| Narrative | 0.4 (1) |
Types of models: BLM = biotic ligand model-type model (e.g., Di Toro et al. 2001); FIAM = free-ion activity model; GLMM = generalized linear mixed model; Hardness = based on hardness regression; Mixed = mixture of model types; MixTox = MixTox model of Jonker et al. (2005); MRM = multiple regression–type model; TKTD = toxicokinetic/toxicodynamic model; TOX = Tox function–type model (e.g., Balistrieri et al. 2015); WHAM = WHAM-FTOX-type model (e.g., Tipping and Lofts 2013); WHAM = Windermere humic aqueous model (e.g., Tipping 1994); WHAM regression = regression based on WHAM speciation.
For types of models and for methods used to present results, the sum of the types exceeds 100% because for some entries more than one type of model was validated or more than one type of method was used to present the validation results.
In addition, 1 metal speciation-validation analysis was conducted for a BLM.
In addition, 4 metal speciation-validation analyses were conducted for a WHAM.