Observed toxicity endpoints measured in prey species relevant to aquaculture food-web interactions.
| Predator (Aquaculture species) | Prey Species | Toxicity Type | Endpoint | Concentration in Prey (ppm) |
|---|---|---|---|---|
| Micropterus salmoides | Lepomis macrochirus | Chronic | NOEL | 18 |
| Micropterus salmoides | Oncorhynchus mykiss | Acute | LC50 | 2.596 |
| Micropterus salmoides | Oncorhynchus mykiss | Chronic | LOEL | 0.071 |
| Micropterus salmoides | Oncorhynchus mykiss | Chronic | NOEC | 0.033 |
| Micropterus salmoides | Pimephales promelas | Chronic | NOEC | 4.500e-4 |
| Micropterus salmoides | Pimephales promelas | Acute | LC50 | 0.329 |
| Micropterus salmoides | Pimephales promelas | Chronic | LOEL | 1 |
| Micropterus salmoides | Lepomis macrochirus | Acute | LC50 | 3.66 |
| Micropterus salmoides | Pimephales promelas | Chronic | NOEL | 0.1 |
| Oncorhynchus aguabonita | Oncorhynchus mykiss | Acute | LC50 | 2.596 |
| Micropterus salmoides | Oncorhynchus mykiss | Chronic | NOEL | 1.342 |
| Micropterus salmoides | Hyalella azteca | Acute | LC50 | 0.2 |
| Lithobates catesbeianus | Lithobates pipiens | Chronic | NOEC | 0.073 |
| Micropterus salmoides | Gambusia affinis | Chronic | NOEC | 0.077 |
| Micropterus salmoides | Daphnia pulex | Chronic | NOEC | 0.869 |
| Micropterus salmoides | Daphnia pulex | Acute | EC50 | 3.475 |
| Micropterus salmoides | Chironomus tentans | Chronic | NOEC | 1 |
| Micropterus salmoides | Chironomus tentans | Acute | LC50 | 0.4 |
| Micropterus salmoides | Chironomus tentans | Acute | EC50 | 0.28 |
| Micropterus salmoides | Chironomus riparius | Chronic | NOEC | 2.154 |
| Lepomis macrochirus | Hyalella azteca | Acute | LC50 | 0.2 |
| Lepomis macrochirus | Hyalella azteca | Acute | EC50 | 0.25 |
| Lepomis macrochirus | Daphnia pulex | Chronic | NOEC | 0.869 |
| Oncorhynchus aguabonita | Oncorhynchus mykiss | Chronic | LOEL | 0.071 |
| Lepomis macrochirus | Daphnia pulex | Acute | EC50 | 3.475 |
| Micropterus salmoides | Hyalella azteca | Acute | EC50 | 0.25 |
| Oncorhynchus aguabonita | Oncorhynchus mykiss | Chronic | NOEC | 0.033 |
| Salmo trutta | Chironomus riparius | Chronic | NOEC | 2.154 |
| Oncorhynchus mykiss | Oncorhynchus mykiss | Acute | LC50 | 2.596 |
| Ictalurus punctatus | Pimephales promelas | Chronic | NOEL | 0.1 |
| Salmo trutta | Oncorhynchus mykiss | Chronic | NOEL | 1.342 |
| Salmo trutta | Oncorhynchus mykiss | Chronic | NOEC | 0.033 |
| Salmo trutta | Oncorhynchus mykiss | Chronic | LOEL | 0.071 |
| Salmo trutta | Oncorhynchus mykiss | Acute | LC50 | 2.596 |
| Salmo trutta | Lepomis macrochirus | Chronic | NOEL | 18 |
| Salmo trutta | Lepomis macrochirus | Acute | LC50 | 3.66 |
| Salmo trutta | Chironomus tentans | Chronic | NOEC | 1 |
| Salmo trutta | Chironomus tentans | Acute | LC50 | 0.4 |
| Salmo trutta | Chironomus tentans | Acute | EC50 | 0.28 |
| Salmo salar | Oncorhynchus mykiss | Chronic | NOEL | 1.342 |
| Salmo salar | Oncorhynchus mykiss | Chronic | NOEC | 0.033 |
| Oncorhynchus aguabonita | Oncorhynchus mykiss | Chronic | NOEL | 1.342 |
| Salmo salar | Oncorhynchus mykiss | Chronic | LOEL | 0.071 |
| Oreochromis niloticus | Gambusia affinis | Chronic | NOEC | 0.077 |
| Oncorhynchus tshawytscha | Oncorhynchus mykiss | Chronic | NOEL | 1.342 |
| Oncorhynchus tshawytscha | Oncorhynchus mykiss | Chronic | NOEC | 0.033 |
| Oncorhynchus tshawytscha | Oncorhynchus mykiss | Chronic | LOEL | 0.071 |
| Oncorhynchus tshawytscha | Oncorhynchus mykiss | Acute | LC50 | 2.596 |
| Oncorhynchus mykiss | Pimephales promelas | Chronic | NOEL | 0.1 |
| Oncorhynchus mykiss | Pimephales promelas | Chronic | NOEC | 4.500e-4 |
| Oncorhynchus mykiss | Pimephales promelas | Chronic | LOEL | 1 |
| Oncorhynchus mykiss | Pimephales promelas | Acute | LC50 | 0.329 |
| Oncorhynchus mykiss | Oncorhynchus mykiss | Chronic | NOEL | 1.342 |
| Oncorhynchus mykiss | Oncorhynchus mykiss | Chronic | NOEC | 0.033 |
| Oncorhynchus mykiss | Oncorhynchus mykiss | Chronic | LOEL | 0.071 |
| Salmo salar | Oncorhynchus mykiss | Acute | LC50 | 2.596 |
| Ictalurus punctatus | Pimephales promelas | Chronic | NOEC | 4.500e-4 |
| Cyprinus carpio | Chironomus tentans | Acute | EC50 | 0.28 |
| Ictalurus punctatus | Pimephales promelas | Acute | LC50 | 0.329 |
| Ctenopharyngodon idella | Chironomus tentans | Chronic | NOEC | 1 |
| Ctenopharyngodon idella | Chironomus tentans | Acute | LC50 | 0.4 |
| Ctenopharyngodon idella | Chironomus tentans | Acute | EC50 | 0.28 |
| Carassius carassius | Daphnia magna | Chronic | NOEL | 0.081 |
| Ictalurus punctatus | Pimephales promelas | Chronic | LOEL | 1 |
| Carassius carassius | Daphnia magna | Chronic | LOEL | 0.01 |
| Carassius carassius | Daphnia magna | Acute | LC50 | 0.242 |
| Carassius carassius | Daphnia magna | Acute | EC50 | 0.481 |
| Carassius carassius | Chironomus tentans | Chronic | NOEC | 1 |
| Carassius carassius | Chironomus tentans | Acute | LC50 | 0.4 |
| Carassius carassius | Chironomus tentans | Acute | EC50 | 0.28 |
| Carassius carassius | Chironomus riparius | Chronic | NOEC | 2.154 |
| Carassius auratus | Chironomus tentans | Chronic | NOEC | 1 |
| Carassius auratus | Chironomus tentans | Acute | LC50 | 0.4 |
| Carassius auratus | Chironomus tentans | Acute | EC50 | 0.28 |
| Carassius auratus | Chironomus riparius | Chronic | NOEC | 2.154 |
| Anguilla anguilla | Oncorhynchus mykiss | Chronic | NOEL | 1.342 |
| Anguilla anguilla | Oncorhynchus mykiss | Chronic | NOEC | 0.033 |
| Anguilla anguilla | Oncorhynchus mykiss | Chronic | LOEL | 0.071 |
| Anguilla anguilla | Oncorhynchus mykiss | Acute | LC50 | 2.596 |
| Anguilla anguilla | Dreissena polymorpha | Chronic | NOEC | 4.101e-4 |
| Anguilla anguilla | Chironomus tentans | Chronic | NOEC | 1 |
| Anguilla anguilla | Chironomus tentans | Acute | LC50 | 0.4 |
| Anguilla anguilla | Chironomus tentans | Acute | EC50 | 0.28 |
| Anguilla anguilla | Chironomus riparius | Chronic | NOEC | 2.154 |
| Ctenopharyngodon idella | Lemna minor | Acute | EC50 | 1.369 |
| Cyprinus carpio | Chironomus riparius | Chronic | NOEC | 2.154 |
| Carassius carassius | Daphnia magna | Chronic | NOEC | 0.091 |
| Cyprinus carpio | Chironomus tentans | Acute | LC50 | 0.4 |
| Ictalurus punctatus | Oncorhynchus mykiss | Chronic | NOEL | 1.342 |
| Ictalurus punctatus | Oncorhynchus mykiss | Chronic | NOEC | 0.033 |
| Ictalurus punctatus | Oncorhynchus mykiss | Chronic | LOEL | 0.071 |
| Ictalurus punctatus | Oncorhynchus mykiss | Acute | LC50 | 2.596 |
| Ictalurus punctatus | Lepomis macrochirus | Chronic | NOEL | 18 |
| Ictalurus punctatus | Hyalella azteca | Acute | LC50 | 0.2 |
| Ictalurus punctatus | Hyalella azteca | Acute | EC50 | 0.25 |
| Gadus morhua | Solea solea | Chronic | NOEC | 28.955 |
| Gadus morhua | Psammechinus miliaris | Chronic | NOEC | 0.072 |
| Gadus morhua | Psammechinus miliaris | Acute | EC50 | 0.091 |
| Gadus morhua | Daphnia pulex | Chronic | NOEC | 0.869 |
| Gadus morhua | Daphnia pulex | Acute | EC50 | 3.475 |
| Ictalurus punctatus | Lepomis macrochirus | Acute | LC50 | 3.66 |
| Daphnia magna | Raphidocelis subcapitata | Chronic | NOEL | 0.003 |
| Dicentrarchus labrax | Dicentrarchus labrax | Chronic | NOEC | 28.955 |
| Cyprinus carpio | Chironomus tentans | Chronic | NOEC | 1 |
| Cyprinus carpio | Dreissena polymorpha | Chronic | NOEC | 4.101e-4 |
| Danio rerio | Algae | Acute | EC50 | 0.364 |
| Danio rerio | Daphnia magna | Acute | EC50 | 0.481 |
| Danio rerio | Algae | Chronic | NOEC | 0.209 |
| Danio rerio | Daphnia magna | Chronic | LOEL | 0.01 |
| Danio rerio | Daphnia magna | Chronic | NOEC | 0.091 |
| Danio rerio | Daphnia magna | Chronic | NOEL | 0.081 |
| Daphnia magna | Raphidocelis subcapitata | Acute | EC50 | 0.023 |
| Daphnia magna | Raphidocelis subcapitata | Chronic | NOEC | 2.000e-4 |
| Danio rerio | Daphnia magna | Acute | LC50 | 0.242 |
Observed bioconcentration factors (BCF) measured in prey species relevant for aquaculture food-web interactions.
Select an aquaculture-relevant species to explore trophic interactions associated with this chemical. The network contains two types of edges: (i) edges connecting the chemical to prey species, which are annotated with toxicity endpoints or bioconcentration factor (BCF) values depending on the selected filter, and (ii) trophic edges connecting prey to predator species, where the predator represents the aquaculture species. When neither toxicity nor BCF is selected, only the food-web (prey–predator) network is displayed. Hover over nodes and edges to view additional details.
ReCAnt is a database of chemicals used in aquaculture and their ecotoxic effects, compiled from published literature. The authors are not liable for any inaccuracies or omissions of any chemicals in this resource. Importantly, our sole goal to build this resource on chemicals used in aquaculture is to enable future basic research on this topic, and it does not necessarily reflect the views or objectives of our employers or funders.