SUPPLEMENTAL DATA The Supplemental data contains 9 Tables. 1 Table S1. Selected single species toxicity data set for tropical freshwater SSD analysis for Ametryn. Taxonomic group Algae Crustacea (Cladocera) Fish Amphibia Exposed temperature & chemical gradea 21°C, TG (97.8%) Exposure duration, endpoint & toxicity threshold (µg/L) 7 d Growth EC50: 0.9uM (204.6 ug/L)c (chronic) Reference [47] Chronic NOECb (µg/L) 40.9 Chlorella pyrenoidosa (algal cells) 25°C, TG (92%) 96 h Growth EC50: 0.3 µg/L (chronic) [48] 0.06 Scenedesmus obliquus (algal cells) 25°C, TG (92%) 96 h Growth EC50: 11.7 µg/L (chronic) [49] 2.34 Scenedesmus quadricauda (algal cells) 25°C, TG (92%) 96 h Growth EC50: 150 µg/L (chronic) [50] 30 Raphidocelis subcapitata (Pseudokirchneriella subcapitata) (algal cells) 25°C, TG,(92% ) 96 h Growth EC50: 11.6 µg/L (chronic) [51] 2.32 Daphnia magna (< 24 h) 21°C, TG ( ≥96%) 48 h immobilization EC50: 40,000 µg/L (acute) [52] 4,000 Lepomis macrochirus 24°C, TG (99%) 96 h mortalityLC50: 3,700 µg/L (acute) [53] 370 Bufo bufo ssp. japonicu 25°C, TG 24 h mortality LC50: 4,400( pH=7), 5,600(pH=8) Geomean:4,960 µg/L (acute) [53] 496 Species (age, size) Chlamydomonas moewusii (algal cells) a Technical grade (TG);Purity is indicated within brackets. Estimated chronic NOECs from reported LC50/EC50 data based on default acute to chronic ratio of 10 for acute LC50/EC50 and conversion factor of 5 for chronic EC50.cCalculated from molar mass of ametryn b 2 Table S2. Selected single species toxicity data set for tropical freshwater SSD analysis for Atrazine. Taxonomic group Green algae Species (age, size) Chlamydomonas reinhardtii (algal cells) Chlorella vulgaris (algal cells) Desmodesmus subspicatus Pseudokirchneriella subcapitata (algal cells) Pseudokirchneriella subcapitata (algal cells) Exposed temperature Exposure duration, endpoint & chemical gradea and toxicity threshold (µg/L) 25°C, TG 92.2% 96 h Growth EC50: 176 µg/L (chronic) [54] Chronic NOECb (µg/L) 35.2 Reference 25°C, TG 92.2% 96 h Growth EC50: 94 µg/L (chronic) [54] 18.8 23 ±2°C, TG 72 h Growth EC50: 41 µg/L (chronic) [55] 8.2 25°C, TG 96 h Growth NOEC: 75 µg/L (chronic) 72 h Growth EC50: 130 µg/L (chronic) 72 h Growth NOEC: 62 µg/L (chronic) [56] [57] 68.2* (experimental NOECs geomean) 24°C, AG Pediastrum sp. (algal cells) 20°C,TG 99.8% 7 d Growth EC50: 536.6 µg/L (chronic) [58] 107.3 Scenedesmus quadricauda (algal cells) 25°C, TG 92.2% 96 h Growth EC50: 169 µg/L (chronic) [54] 33.8 (lowest EC50 value 169 µg/L) Scenedesmus quadricauda (algal cells) 20°C, TG 99.8% 7 d Growth EC50: 171 µg/L (chronic) [58] 3 Table S2 (continued). Selected single species toxicity data set for tropical freshwater SSD analysis for Atrazine. Taxonomic group Species (age, size) Reference Chronic NOECb (µg/L) 96 h Growth EC50, 92 µg/L (acute) 96 h Growth EC50, 153 µg/L (acute) [54] [56] 5.89(estimated from EC50 geomean 119 µg/L & ACR 20.2) 25°C, TG 92.2% 14 d Growth EC50, 22 µg/L (chronic) [54] 4.4 Najas sp. (10 cm apical part) 25°C, TG 92.2% 14 d Growth EC50, 24 µg/L (chronic) [54] 4.8 Myriophyllum heterophyllum (10 cm apical part) 25°C, TG 92.2% 14 d Growth EC50, 132 µg/L (chronic) [54] 26.4 Macrophyte Lemna minor (Plant with 12 fronds) Lemna mino (Plant with 12 fronds) Ceratophyllum demersum, (10 cm apical part) Exposed temperature Exposure duration, endpoint & chemical gradea and toxicity threshold (µg/L) 25°C, TG 92.2% 25°C, TG 4 Table S2 (continued). Selected single species toxicity data set for tropical freshwater SSD analysis for Atrazine. Taxonomic group Species (age, size) Crustacea (Cladocera) Ceriodaphnia cf. dubia (<24 h neonates) Australian species Crustacea (Amphipod) Crustacea (Shrimp) Exposed Exposure duration, endpoint and temperature & toxicity threshold (µg/L) a chemical grade 25°C, TG 97% 7 d Reproduction NOEC 475 µg/L (chronic) Reference Chronic NOECb (µg/L) [59] 475* Daphnia carinata, (<24 h neonates) Australian species 25°C, TG 99% 48 h Immobilization EC50, 60,600 µg/L (acute) [60] 3503 (estimated with ACR 17.3) Pseudosida ramose (≤24 h neonates) tropical species Pseudosida ramose (≤24 h neonates) 25°C, TG 99% 48 h Survival LC50, 20,900 µg/L (acute) [61] 400* (Experimental NOEC) 25°C, TG 99% 21 d Reproduction NOEC, 400 µg/L (chronic) [61] Hyalella azteca (young) Hyalella azteca (young) 22-23°C, TG 98% 25°C, TG 98% 48 h Survival LC50 13,000 µg/L (acute) 96 h Survival LC50 1,500 µg/L (acute) [62] Paratya australiensis (1-1.5 cm length) Australian species 23°C, TG 97% 48 h Immobilization EC50, 9,800 µg/L and 9,900 µg/L for different water (acute ) [64] Insect [63] 87 (estimated with ACR 17.3 on 96 h LC50) 569 (estimated geomean 9850, & ACR 17.3) Chironomus tepperi 24 ± 1°C, TG 10 d survival LC50, [64] 3,330(estimated nd (2 instar larvae) 97% 16,600 µg/L & 16,700 µg/L from geomean Australian species for different water (chronic) 16,650) Table S2 (continued): Selected single species toxicity data set for tropical freshwater SSD analysis for Atrazine. 5 Taxonomic group Rotifer Species (age, size) Fish Cyprinus carpio (15. 5cm length) Tropical/subtropical Brachionus calyciflorus (< 4 h neonates) Danio rerio (larvae) Melanotenia fluviatilis (1.5-2 cm) Australian species Amphibians Rhinella arenarum (larvae) South American toad Rhinella arenarum (larvae) Exposed temperature Exposure duration, endpoint & chemical gradea and toxicity threshold (µg/L) 25 ± 1°C, TG 98.8% 24 h Survival LC50: 39,000µg/L (acute) 7 d Reproduction NOEC: 80 µg/L (chronic) Reference [65] Chronic NOECb (µg/L) 80* (observed) 23°C, TG 93.7% 96 h Survival LC50, 18,800 µg/L (acute) [66] 376 (estimated from ACR 49.9) 27±1°C, TG 98.4% 35 d Survival NOEC: 300 µg/L (chronic) [67] 300* (observed NOEC) 23°C, TG ≥97% 96 h Imbalance EC50, 10,400 and 8,200 µg/L for different test media (acute) [68] 185(estimated from geomean 9235 & ACR 49.9) 20±2°C, TG 98% 21 d Mortality LC50 2,320 µg/L; 21 d morality LC10=, 710 µg/L (chronic) 336 h development EC10, 2,500 µg/L (chronic) [69] 710* (observed chronic LC10) 20±2°C, TG 98% [70] 23°C, TG 98% 37 d mortality, growth, [71] 25* Xenopus laevis metamorphosis NOEC, 25 (observed (tadpoles) African µg/L (chronic) NOEC) clawed frog a Technical grade (TG) or analytical grade (AG);Purity is indicated within brackets. b Acute to chronic ratio (ACR) was used to convert Acute LC50/EC50 data (17.3 for crustacean, 49.9 for fish, 20.2 for other taxa) to chronic NOECs and conversion factor of 5 was used to convert chronic LC50/EC50 data to chronic NECs. Experimentally observed chronic NOECs/LC10 used for 7 species are indicated with asterisks. 6 Table S3. Selected single species toxicity data set for tropical freshwater SSD analysis for Simazine. Taxonomic group Green algae Species (age, size) Chlorella pyrenoidosa (algal cells) 25°C, TG (92%) 96 h Growth EC50 2,173.8 µg/L (chronic) [49] 434.8 Scenedesmus obliquus (algal cells) 20°C, TG (92%) 96 h Growth EC50 257 µg/L (chronic) [49] 51.4 24°C, AG 72 h Abundance EC50 297 µg/L (chronic) 72 h Abundance EC50 220 µg/L (chronic) [57] 51.1 25°C, TG 96 h Growth EC50 166 µg/L (acute) [56] 16.6 25°C. TG (99.6%) 7 d Growth NOEC 300 µg/L (chronic) [73] 300* (observed NOEC) 21°C, TG 24 h Survival LC50 5,600 µg/L (acute) [53] 560 Lemna minor (plant with 12 fronds) Typha latifolia perennial herb (individual plants) Crustacea [48] Chronic NOECb (µg/L) 16.4 Reference Chlorella vulgaris (algal cells) Pseudokirchneriella subcapitata (algal cells) Pseudokirchneriella subcapitata (algal cells) Macrophyte Exposed temperature Exposure duration, endpoint & chemical gradea and toxicity threshold (µg/L) 25°C, TG (92%) 96 h Growth EC50 82 µg/L (chronic) Palaemonetes kadiakensis (grass shrimp) 25°C, TG (99%) Fish [72] Pimephales promelas 25°C, TG 96 h Survival LC50 [53] 100 (22.2 cm length) 1,000 µg/L (acute) a Technical grade (TG); Purity is indicated within brackets when specified. Analytical grade (AG) b Estimated chronic NOECs from reported LC50/EC50 data based on default acute to chronic ratio of 10 for acute LC50/EC50; conversion factor of 5 for chronic EC50).Experimentally observed chronic NOEC used for 1 species is indicated with an asterisk. 7 Table S4. Selected single species toxicity data set for tropical freshwater SSD analysis for Hexazinone. Taxonomic group Blue green algae Species (age, size) Green algae Pseudokirchneriella subcapitata (algal cells) Pseudokirchneriella subcapitata (algal cells) 24°C, TG (98%) 72 h Growth EC50, 56 µg/L (chronic) [74] 24±2°C, TG 96 h Abundance EC50 24.5 µg/L (chronic) [75] Macrophyte Lemna minor 25°C, TG (98%) 7 d Growth EC50 72 µg/L (chronic) [76] 14.4 Crustacea Daphnia magna (<24 h) 22°C, TG (98%) 48 h survival LC50 152,000 µg/L (acute) [77] 15,200 Fish Lepomis macrochirus 22°C, TG [53] Lepomis macrochirus 21±1°C, TG (98%) 96 h survival LC50 100,000 µg/L (acute) 24 h survival LC50 425,000 µg/L (acute) 10,000 (longer duration more sensitive) Pimephales promelas 21±1°C, TG (98%) Anabaena flos-aquae (algal cells) Exposed temperature Exposure duration, endpoint & chemical gradea and toxicity threshold (µg/L) 24 ±2°C, 72 h Growth EC50, TG (98%) 2,014 µg/L (chronic) Reference [74] [77] Chronic NOECb (µg/L) 402.8 7.4 (based on geomean 37 µg/L) 96 h survival LC50 [77] 27,400 274,000 µg/L (acute) a Technical grade (TG);Purity is indicated within brackets when specified. b Estimated chronic NOECs from reported LC50/EC50 data based on default acute to chronic ratio of 10 for acute LC50/EC50 and conversion factor of 5 for chronic EC50). 8 Table S5. Selected single species toxicity data set for tropical freshwater SSD analysis for Diuron. Taxonomic group Green algae Species (age, size) Chlamydomonas reinhardtii Desmodesmus subspicatus Scenedesmus obliquus Exposed temperature Exposure duration, endpoint & chemical gradea and toxicity threshold (µg/L) 25°C, TG 24 h growth EC50 0.17 µM (39.6 g/L) (acute) [78] Chronic NOECb (µg/L) 3.96 (estimated) Reference 23±2°C, TG. 72 h growth EC50 46.3 µg/L (chronic) [55] 9.26 (estimated) 21°C. TG 24 h growth EC50 10 µg/L (acute) 7 d Growth EC50 28.3 µg/L (chronic) [79] 1 (estimated) [80] 5.66 (estimated) 23°C, TG 96 h lethality LC50 8,800 µg/L (acute) [82] 880 (estimated) Macrophyte Lemna minor Duck weed Crustacea (Shrimp) Paratya australiensis Australian species Crustacea (Amphipod) Hyalella azteca (< 11 days) 22 -24°C, TG99.8% 10 d LC50 18,400 µg/L (acute) 10 d survival, growth NOEC 7,900 µg/L (acute) [81] 1,840 (estimated ) Crustacea (Cladoceran) Ceriodaphnia dubia Australian species (<24 h neonates) 25°C, concentration measured 48 h immobilization EC50, 1,700 µg/L and 1,000 µg/L in different waters (acute) [83] 20°C, TG 99.8% 7 d LC50 7,100 µg/L, 7 d reproduction, survival NOEC 4,000 µg/L (chronic) [81] 130.4 (estimated 1,304 µg/L EC50 geomean) 4,000*(observed) Daphnia pulex (5 days old) 24± 2°C, TG 9 Table S5 (continued). Selected single species toxicity data set for tropical freshwater SSD analysis for Diuron. Taxonomic group Insect (midge) Species (age, size) Fish Pimephales promelas (Juvenile, embryo-larvae) Chironomus tentans (1st instar larvae, 2 days old) Pimephales promelas (Juvenile, Eggs, embryolarvae-juvenile) Amphibian Rana catesbeiana Bull frog (tadpoles) Exposed temperature Exposure duration, endpoint & chemical gradea and toxicity threshold (µg/L) 24°C TG 99.8% 10 d lethality LC50 3,300 µg/L (chronic) 10 d growth NOEC 3,400 µg/L (chronic) 10 d survival NOEC 1,900 µg/L (chronic) 24 -25°C TG 99.8% 7 d lethality LC50 embryolarvae 11,700 g/L (chronic) 7 d lethality embryo-larvae NOEC 4,200 µg/L (chronic) 24 -26°C TG 98.6% 192 h lethality LC50 juvenile 7,700 µg/L (acute) 64 day survival, growth NOEC, 33.4 µg/L (chronic) 24°C, TG 99.8% Reference [81] Chronic NOECb (µg/L) 1,900*(observe d) [81] [84] 33.4* ( 64 d observed data sensitive) 21 d lethality LC50 [85] 7,600* 12,700 µg/L (chronic) (observed) 21 day lethality NOEC 7,600 µg/L (chronic) a Technical grade (TG);Purity is indicated within brackets when specified. b Estimated chronic NOECs from reported LC50/EC50 data based on default acute to chronic ratio of 10 for acute LC50/EC50; conversion factor of 5 for chronic EC50). Experimentally observed NOECs are indicated in asterisk. 10 Table S6. Selected single species toxicity data set for tropical freshwater SSD analysis for Tebuthiuron. Taxonomic Species (age, size) Exposed temperature Exposure duration, endpoint Reference group & chemical gradea and toxicity threshold (µg/L) Green algae Chlorella sp. 27°C, TG 72 h Growth IC50 [86] Australian tropical species 281 µg/L (chronic) 72 h Growth NOEC 101 µg/L (chronic) Chronic NOECb (µg/L) 101* (observed) Pseudokirchneriella subcapitata 25°C, TG 14 d Growth EC50, 307 µg/L (chronic) 14 d Growth NOEC 33 µg/L (chronic) [87] 33* (observed) Macrophyte Lemna aequinoctialis Australian tropical species 30°C, TG 96 h Growth IC50 181 µg/L (acute) [86] 18.1 Coelenterate Hydra viridissima Australian tropical species TG 96 h Growth LC50 150000 µg/L (acute) [87] 15,000 Crustacea (Cladoceran) Moinodaphnia macleayi Australian tropical species TG 3 brood reproduction EC50 134,000 µg/L 3 brood reproduction NOEC 20,000 µg/L (chronic) [87] 20,000* (observed) Daphnia magna 22°C, TG 21 d reproduction NOEC 21,800 µg/L (chronic) [88] 21,800 Mogurnda mogurnda Australian tropical species 22°C, TG 96 h survival LC50 214,000 µg/L (acute) [87] 21,400 22-24°C, TG 33 d Growth NOEC 9,300 µg/L (chronic) [88] 9,300* (observed) Fish Pimephales promelas 11 a Technical grade (TG) bEstimated chronic NOECs from reported LC50/EC50data based on Assessment Factors(10 for acute LC50/EC50; 5 for chronic EC50) and experimentally observed NOECs used for 3 species indicated with an asterisk. 12 Table S7. Selected single species toxicity data set for tropical freshwater SSD analysis for Metolachlor. Taxonomic group Green algae Species (age, size) Chronic NOECb µg/L) 228 Exposed temperature & chemical gradea 25°C, TG (95%) Exposure duration, endpoint and toxicity threshold (µg/L) 96 h Growth EC50 1,138 µg/L (chronic) Reference 25°C, TG (96% rac, 96% S) 96 h Growth EC50 -rac 152 µg/L (chronic) 96 h Growth EC50 -S 68 µg/L (chronic) [89] 20 (based on geo mean EC50s 102µg/L) 25°C, TG (95%) 96 h Growth EC50 203 µg/L (chronic) [54] 41 Scenedesmus vacuolatus 28°C, TG (98.4% S) [90] Scenedesmus vacuolatus 25°C, TG(98.4%S) 24 h Reproduction EC50-S, 341 µg/L (acute) 48 h Growth EC50-S 2,300 and 3,000 µg/L (chronic) 34 (reproduction estimate more sensitive) 96 h Growth EC50, 55.5 µg/L (chronic) 96 h Growth EC50, 84 µg/L (chronic) 96 h Growth EC50, 77 µg/L (chronic) 96 h Growth NOEC, 38 µg/L (chronic) [75] 38* (experimental) 96 h Growth EC50-S, 130 µg/L (chronic) 96 h Growth EC50-rac, 256 µg/L (chronic) [91] Chlamydomonas reinhardtii Chlorella pyrenoidosa Chlorella vulgaris Pseudokirchneriella subcapitata 24±2°C, TG Pseudokirchneriella subcapitata 25°C, TG (95%) Pseudokirchneriella subcapitata 25°C, TG Scenedesmus obliquus 25°C, TG (rac-96%, S-96%) 13 [54] [54] [56] 36 (estimated from geomean EC50 182 µg/L) Table S7 (continued). Selected single species toxicity data set for tropical freshwater SSD analysis for Metolachlor. Taxonomic Species (age, size) group Macrophytes Lemna minor (12 fronds) Lemna minor (12 fronds) Exposed temperature & chemical gradea 25°C,TG 25°C, TG (95%) Exposure duration, endpoint and toxicity threshold (µg/L) 96 h Growth EC50, 343 µg/L (acute) 96 h Growth EC50, 360 µg/L (acute) Reference [56] Chronic NOECb (µg/L) 35(estimated from geomean) [54] Ceratophyllum demersum (10 cm apical portions) 25°C, TG (95%) 14 d Growth EC50, 70 µg/L (chronic) [54] 14 Elodea canadensis (10 cm apical portions) 25°C, TG (95%) 14 d Growth EC50, 2,355 µg/L (chronic) [54] 471 Najas sp (Water Nymph) (10 cm apical portions) 25°C, TG (95%) 14 d Growth EC50, 242 µg/L (chronic) [54] 48 Ceriodaphnia dubia (Australian species) (<24h neonates) 25°C (EC50 based on measured levels, source not reported) 48 h Immobilization EC50, 2,000 µg/L and 1,100 µg/L in different waters (acute) [83] 148(estimated from geomean) Daphnia magna (<24 h neonates) 20°C, TG (95.3 rac, 96% S) 21 reproduction NOEC rac-1 µg/L, s-100 µg/L (chronic) [92] 10* (experimental geomean) Crustacea (Amphipod) Hyalella azteca 22°C, TG (97.2%) 96 h Lethality LC50, 6,000 µg/L (acute) [93] 600 Insect Chironomus plumosus 22°C, TG 95.4% 48 h Immobilization EC50 3,800 µg/L (acute) Crustacea (Cladocera) 14 [53] 380 Table S7 (continued). Selected single species toxicity data set for tropical freshwater SSD analysis for Metolachlor. Taxonomic group Fish Species (age, size) Amphibian Xenopus laevis (Larvae) Pimephales promelas Exposed temperature & chemical gradea 22°C, TG 95.4% Exposure duration, endpoint and toxicity threshold (µg/L) 96 h Lethality LC50, 8,000 µg/L (acute) 24°C, TG 98% Reference [53] Chronic NOECb (µg/L) 800 96 h Development EC50 [53] 1,383 13,830 µg/L (acute)abnormal larvae a b Technical grade (TG) Estimated chronic NOECs from reported LC50/EC50 data based on default acute to chronic ratio of 10 for acute LC50/EC50; conversion factor of 5 for chronic EC50) and experimentally observed NOECs used for 3 species indicated with an asterisk.. Racemic Metolachlor (rac, R and S) and/or S-,Metolachlor are the two types of enantiomers tested. 15 Table S8. Selected single species toxicity data set for tropical freshwater SSD analysis for Imidacloprid. Exposed temperature & chemical gradea 21°C, TG Exposure duration, endpoint and toxicity threshold (µg/L) 72 h growth EC50: 389 µg/L( chronic ) Reference [94] Chronic NOECb (µg/L) 77.8 Daphnia magna, (24 h neonates) 22° C, TG (>99.5%) 48 h immobility EC50, 6029 µg/L (acute) [95] 602.9 Chydorus sphaericus 22° C, TG (>99.5%) 48 h immobility EC50, 2209 µg/L (acute) [95] 220.9 Cypretta seuratti 22° C, TG (>99.5%) 48 h immobility EC50, 16 µg/L (acute) [95] 1.6 Cypridopsis vidua 22° C, TG (>99.5%) 48 h immobility EC50, 3 µg/L (acute) [95] 0.3 Ilyocypris dentifera 22° C, TG (>99.5%) 48 h immobility EC50, 3 µg/L (acute) [95] 0.3 Crustacea (Amphipod) Hyalella Azteca 23±1° C, TG (99.2%) 96 h lethality LC50: 65.43 µg/L (acute) [96] 6.54 Insects Chironomus tentans (midge) 23±1° C, TG (99.2%) 96 h lethality LC50: 5.75 µg/L (acute) [96] 0.58 Aedes albopictus strains of mosquito (larvae, 4th instar) 25° C, TG (97.7%) 24 h lethality LC50,500, 600, 300, 600, 800 µg/L (acute) [97] 53.3(based on geo mean 533 µg/L) Taxonomic group Green algae Species (age, size) Crustacea (Cladocera) Crustacea (Ostracod) Desmodesmus subspictatus (cells) 16 Table S8 (continued). Selected single species toxicity data set for tropical freshwater SSD analysis for Imidacloprid. Taxonomic group Fish Species (age, size) Amphibian Rana nigronaculata Hallowell tadpoles (0.5 months old) Danio rerio Exposed temperature & chemical gradea 21° C, TG 20° C, TG (95%) Exposure duration, endpoint and toxicity threshold (µg/L) 96 h lethality LC50 241,000 µg/L (acute) 96 h lethality LC50 129,000 µg/L (acute) [94] Chronic NOECb (µg/L) 24,100 [98] 12,900 Reference Rana limnocharis 20° C, TG (95%) 96 h lethality LC50 [98] 8,200 (tadpoles, 1 months old) 82,000 µg/L (acute) a Technical grade (TG) bEstimated chronic NOECs from reported LC50/EC50 data based on Assessment Factors(10 for acute LC50/EC50; 5 for chronic EC50) 17 Table S9. Additional References for the toxicity data presented in the supplemental tables S1S8 47. Cain JR, Cain RK. 1983. The effects of selected herbicides on zygospore germination and growth of Chlamydomonas moewusii (chlorophyceae, volvocales). Journal of Phycology 19(3): 301-305. 48. Ma J, Liang W, Xu L,Wang S, Wei Y, Lu J. 2001. Acute toxicity of 33 herbicides to the green alga Chlorella pyrenoidosa. Bulletin of Environmental Contamination and Toxicology 66: 536-541. 49. Ma J. 2002. Differential sensitivity to 30 herbicides among populations of two green algae, Scenedesmus obliquus and Chlorella pyrenoidosa Bulletin of Environmental Contamination and Toxicology 68: 275-281 50. Ma J, Lin F, Wang S, Xu L. 2003. Toxicity of 21 herbicides to the green alga Scenedesmus quadricauda. Bulletin of Environmental Contamination and Toxicology 71: 594-601. 51. Ma J. Wang S, Wang P, Ma L, Chen X, Xu R. 2006. Toxicity assessment of 40 herbicides to the green alga Raphidocelis subcapitata. Ecotoxicology and Environmental Safety 63: 456462. 52. Marchini S, Passerini L, Cesareo D, Tosato ML. 1988. Herbicidal triazines - acute toxicity on daphnia, fish, and plants and analysis of its relationships with structural factors. Ecotoxicology and Environmental Safety 16: 148-157. 18 53. USEPA/ECOTOX 2013. United States Environmental Protection Agency, ECOTOX Database. Available from http://cfpub.epa.gov/ecotox (Last access on 11th December 2013). 54. Fairchild JF, Ruessler DS, Carlson AR. 1998. Comparative sensitivity of five species of macrophytes and six species of algae to atrazine, metribuzin, alachlor, and metolachlor. Environmental Toxicology and Chemistry 17(9): 1830-1834. 55. Masojídek, J, Souček P, Máchová J, Frolík J, Klem K Malý J. 2011. Detection of photosynthetic herbicides: Algal growth inhibition test vs. electrochemical photosystem II biosensor. Ecotoxicology and Environmental Safety 74(1): 117-122. 56. Fairchild JF, Ruessler DS, Haverland PS, Carlson AR. 1997. Comparative sensitivity of Selenastrum capricornutum and Lemna minor to sixteen herbicides. Archives of Environmental Contamination and Toxicology 32(4): 353-357. 57. Sbrilli G, Bimbi B, Cioni F, Pagliai L, Luchi F, Lanciotti E. 2005. Surface and ground waters characterization in Tuscany (Italy) by using algal bioassay and pesticide determinations: comparative evaluation of the results and hazard assessment of the pesticides impact on primary productivity. Chemosphere 58(5): 571-578. 58. Tang JX, Hoagland KD, Siegfried BD. (1997). Differential toxicity of atrazine to selected freshwater algae. Bulletin of Environmental Contamination and Toxicology 59(4): 631-637. 59. Phyu YL, Palmer GC, Warne MStJ, Dowse R, Mueller S, Chapman J, Hose GC, Lim RP. 2013. Assessing the Chronic Toxicity of Atrazine, Permethrin, and Chlorothalonil to the Cladoceran Ceriodaphnia cf. dubia in Laboratory and Natural River Water. Archives of Environmental Contamination and Toxicology 64(3): 419-426. 19 60. He H, Yu J, Chen G, Li W, He J, Li H. 2012. Acute toxicity of butachlor and atrazine to freshwater green alga Scenedesmus obliquus and cladoceran Daphnia carinata. Ecotoxicology and Environmental Safety 80: 91-96. 61. Freitas EC, Rocha O. 2012. Acute and chronic effects of atrazine and sodium dodecyl sulfate on the tropical freshwater cladoceran Pseudosida ramosa. Ecotoxicology 21(5): 1347-1357. 62. Wan MT, Buday C, Schroeder G, Kuo J, Pasternak J. 2006. Toxicity to Daphnia magna, Hyalella azteca, Oncorhynchus kisutch, Oncorhynchus mykiss, Oncorhynchus tshawytscha, and Rana catesbeiana of Atrazine, Metolachlor, Simazine, and Their Formulated Products. Bulletin of Environmental Contamination and Toxicology. 76:52–58 63. Ralston-Hooper K, Hardy J, Hahn L, Ochoa-Acuňa H, Lee LS, Mollenhauer R, Sepūlveda MS. 2009. Acute and chronic toxicity of atrazine and its metabolites deethylatrazine and deisopropylatrazine on aquatic organisms. Ecotoxicology 18(7): 899-905. 64. Phyu YL, Warne MStJ, Lim RP. 2005. Toxicity and bioavailability of atrazine and molinate to the freshwater shrimp (Paratya australiensis) under laboratory and simulated field conditions. Ecotoxicology and Environmental Safety 60: 113–122. 65. Lu Z, Zhaoa B, Yanga J, Snell TW. 2012. Effects of atrazine and carbaryl on growth and reproduction of the rotifer Brachionus calyciflorus Pallas. Journal of Freshwater Ecology 27(4): 527-537. 66. Neṥković, NK, Elezović I, Karan V, Poleksić V, Budimir M. (1993). Acute and subacute toxicity of atrazine to carp (Cyprinus carpio). Ecotoxicology and Environmental Safety 25(2): 173-182. 20 67. Gorge G, Nagel R. 1990. Toxicity of lindane, atrazine and deltamethrin to early life stages of zebra fish (Brachydanio rerio) . Ecotoxicology and Environmental Safety 20:246-255. 68. Phyu YL, Warne MStJ, Lima RP. 2006. Toxicity and bioavailability of atrazine and molinate to the freshwater fish (Melanotenia fluviatilis) under laboratory and simulated field conditions. Science of the Total Environment 356(1-3): 86-99. 69. Brodeur JC, Svartz G, Perez-Coll CS, Marino DJG, Herkovits J. 2009. Comparative susceptibility to atrazine of three developmental stages of Rhinella arenarum and influence on metamorphosis: Non-monotonous acceleration of the time to climax and delayed tail resorption. Aquatic Toxicology 91: 161–170 70. Svartz GV, Herkovits J, Pĕrez-Coll CS. 2012. Sublethal effects of atrazine on embryo-larval development of Rhinella arenarum (Anura: Bufonidae). Ecotoxicology 21(4): 1251-1259. 71. Zaya RM, Amini, Z, Whitaker AS, Kohler SL, Ide CF. 2011. Atrazine exposure affects growth, body condition and liver health in Xenopus laevis tadpoles. Aquatic Toxicology 104(3-4): 243-253. 72. Okamura H, Aoyama I, Liu D, Maguire RJ, Pacepavicius GJ, Lau YL. 2000. Fate and ecotoxicity of the new antifouling compound Irgarol 1051 in the aquatic environment. Water Research 34(14): 3523-3530. 73. Wilson PC, Whitwell T, Klaine SJ. 2000. Metalaxyl and simazine toxicity to and uptake by Typha latifolia. Archives of Environmental Contamination and Toxicology 39(3): 282-288. 74. Abou-Waly H,Abou-Setta MM, Nigg HN, Mallory LL. 1991. Growth-response of freshwater algae, Anabaena flos aquae and Selenastrum capricornutum to atrazine and 21 hexazinone herbicides. Bulletin of Environmental Contamination and Toxicology 46(2): 223229. 75. St-Laurent D, Blaise C, Macquarrie P, Scroggins R, Trottier B. 1992. Comparativeassessment of herbicide phytotoxicity to Selenastrum capricornutum using microplate and flask bioassay procedures. Environmental Toxicology and Water Quality 7(1): 35-48. 76. Peterson HG, Boutin C, Freemark KE, Martin PA. 1997. Toxicity of hexazinone and diquat to green algae, diatoms, cyanobacteria and duckweed. Aquatic Toxicology 39(2): 111-134. 77. Kennedy GL. (1984). "Acute and environmental toxicity studies with hexazinone." Fundamental and Applied Toxicology 4(4): 603-611. 78. Nestler, H, Groh KJ, Schönenberger R, Behra R, Schirmer K, Eggen RIL, Suter MJF. 2012. Multiple-endpoint assay provides a detailed mechanistic view of responses to herbicide exposure in Chlamydomonas reinhardtii. Aquatic Toxicology 110: 214-224. 79. Geoffroy L, Teisseire H, Couderchet M, Vernet G. 2002. Effect of oxyfluorfen and diuron alone and in mixture on antioxidative enzymes of Scenedesmus obliquus. Pesticide Biochemistry and Physiology. 72:178-185 80. Gatidou G, Stasinakis AS, Iatran E. 2014. Joint toxicity of 3 phenyl urea herbicides using Lemna minor and Vibrio fisheri bioassays. Chemosphere. Available at http://dx.doi.org/10.1016/j.chemosphere.2014.04.030 81. Nebeker AV, Schuytema GS. 1998. Chronic effects of the herbicide diuron on freshwater cladocerans, amphipods, midges, minnows, worms, and snails. Archives of Environmental Contamination and Toxicology 35(3): 441-446. 22 82. Kumar A, Correll R, Grocke S, Bajet C. 2010. Toxicity of selected pesticides to freshwater shrimp, Paratya australiensis (Decapoda: Atyidae): Use of time series acute toxicity data to predict chronic lethality. Ecotoxicology and Environmental Safety 73(3): 360-369. 83. Foster, S, Thomas M, Korth W. 1998. Laboratory-derived acute toxicity of selected pesticides to Ceriodaphnia dubia. Australasian Journal of Ecotoxicology. 4:53-59. 84. Call DJ, Brooke LT, Kent RJ, Knuth ML, Poirier SH, Huot JM, Lima AR. 1987. Bromacil and diuron herbicides - toxicity, uptake, and elimination in fresh-water fish. Archives of Environmental Contamination and Toxicology 16(5): 607-613. 85. Schuytema GS, Nebeker AV. 1998. Comparative toxicity of diuron on survival and growth of Pacific treefrog, bullfrog, red-legged frog, and African clawed frog embryos and tadpoles. Archives of Environmental Contamination and Toxicology 34(4): 370-376. 86. van Dam RA, Camilleri C, Turley C, Binet MT, Stauber JL. 2004a Chronic toxicity of the herbicide tebuthiuron to the tropical green alga. Chlorella sp and the duckweed Lemna aequinoctialis Australasian Journal of Ecotoxicology 10:97-104. 87. van Dam RA, Camilleri C, Markich SJ, Bayliss P. 2004b. Ecological risk assessment of tebuthiuron following application on tropical Australian wetlands. Human and Ecological Risk Assessment 10(6): 1069-1097. 88. Meyerhoff RD, Grothe DW, Sauter S, Dorulla GK. 1985. Chronic toxicity of tebuthiuron to an alga (Selenastrum capricornutum), a cladoceran (daphnia-magna), and the fathead minnow (Pimephales promelas). Environmental Toxicology and Chemistry 4(5): 695-701. 89. Liu H, Xiong M. 2009. Comparative toxicity of racemic metolachlor and S-metolachlor 23 to Chlorella pyrenoidosa. Aquatic Toxicology 93:100–106 90. Vallotton N, Moser D, Eggen RIL, Junghans M, Chèvre N. 2008. S-metolachlor pulse exposure on the alga Scenedesmus vacuolatus: Effects during exposure and the subsequent recovery. Chemosphere 73(3): 395-400. 91. Liu, HJ, Cai WD, Huang RN, Xia HL, Wen YZ. 2012. Enantioselective toxicity of metolachlor to Scenedesmus obliquus in the presence of cyclodextrins. Chirality 24(2): 181187. 92. Liu HJ, Ye W, Zhana X, Liuet W. 2006. A comparative study of rac- and S-metolachlor toxicity to Daphnia magna. Ecotoxicology and Environmental Safety 63(3): 451-455. 93. Wan MT, Buday C, Schroeder G, Kuo J, Pasternak J. 2006. Toxicity to Daphnia magna, Hyalella azteca, Oncorhynchus kisutch, Oncorhynchus mykiss, Oncorhynchus tshawytscha, and Rana catesbeiana of Atrazine, Metolachlor, Simazine, and Their Formulated ProductsBull. Environ. Contam. Toxicol. 76:52–58 94. Tišler T, Jemec A, Mozetič B, Trebše P. 2009. Hazard identification of imidacloprid to aquatic environment. Chemosphere 76(7): 907-914 95. Sanchez-Bayo F, Goka K. 2006. Influence of light in acute toxicity bioassays of imidacloprid and zinc pyrithione to zooplankton crustaceans. Aquatic Toxicology 78(3): 262-271. 96. Stoughton SJ, Liber K, Culp J, Cessna A. 2008. Acute and chronic toxicity of imidacloprid to the aquatic invertebrates Chironomus tentans and Hyalella azteca under constant- and pulseexposure conditions. Archives of Environmental Contamination and Toxicology 54(4): 662673. 24 97. Liu, H., et al. 2004. Insecticide resistance in Alabama and Florida mosquito strains of Aedes albopictus. Journal of Medical Entomology 41(5): 946-952. 98. Feng S, Kong Z, Wang X, Zhao L, Peng P. 2004. Acute toxicity and genotoxicity of two novel pesticides on amphibian, Rana N-Hallowell." Chemosphere 56(5): 457-463. 25