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On April 3, 2025 at 9:16:35 AM UTC,
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Added resource raths_thi_SIB.xlsx to Data for: Elimination resistant: Characterizing multi-compartment toxicokinetics of the neonicotinoid thiacloprid in the amphipod Gammarus pulex using bioconcentration and receptor binding assays
f | 1 | { | f | 1 | { |
2 | "author": [ | 2 | "author": [ | ||
3 | "Raths, Johannes", | 3 | "Raths, Johannes", | ||
4 | "Schinz, Linda", | 4 | "Schinz, Linda", | ||
5 | "Mangold-D\u00f6ring, Annika", | 5 | "Mangold-D\u00f6ring, Annika", | ||
6 | "Hollender, Juliane" | 6 | "Hollender, Juliane" | ||
7 | ], | 7 | ], | ||
8 | "author_email": null, | 8 | "author_email": null, | ||
9 | "citation_publication": "Raths, J., Schinz, L., Mangold-D\u00f6ring, | 9 | "citation_publication": "Raths, J., Schinz, L., Mangold-D\u00f6ring, | ||
10 | A., & Hollender, J. (2023). Elimination Resistance: Characterizing | 10 | A., & Hollender, J. (2023). Elimination Resistance: Characterizing | ||
11 | Multi-compartment Toxicokinetics of the Neonicotinoid Thiacloprid in | 11 | Multi-compartment Toxicokinetics of the Neonicotinoid Thiacloprid in | ||
12 | the Amphipod Gammarus pulex Using Bioconcentration and | 12 | the Amphipod Gammarus pulex Using Bioconcentration and | ||
13 | Receptor-Binding Assays. Environmental Science & Technology, | 13 | Receptor-Binding Assays. Environmental Science & Technology, | ||
14 | 57(24), 8890\u20138901. https://doi.org/10.1021/acs.est.3c01891\n", | 14 | 57(24), 8890\u20138901. https://doi.org/10.1021/acs.est.3c01891\n", | ||
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16 | "doi": "10.25678/000841", | 16 | "doi": "10.25678/000841", | ||
17 | "geographic_name": [ | 17 | "geographic_name": [ | ||
18 | "Bubikon", | 18 | "Bubikon", | ||
19 | "D\u00fcbendorf", | 19 | "D\u00fcbendorf", | ||
20 | "Switzerland" | 20 | "Switzerland" | ||
21 | ], | 21 | ], | ||
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28 | "license_id": null, | 28 | "license_id": null, | ||
29 | "license_title": null, | 29 | "license_title": null, | ||
30 | "maintainer": "Raths, Johannes", | 30 | "maintainer": "Raths, Johannes", | ||
31 | "maintainer_email": "Raths, Johannes <johannes.raths@eawag.ch>", | 31 | "maintainer_email": "Raths, Johannes <johannes.raths@eawag.ch>", | ||
32 | "metadata_created": "2025-04-03T09:16:34.781753", | 32 | "metadata_created": "2025-04-03T09:16:34.781753", | ||
n | 33 | "metadata_modified": "2025-04-03T09:16:35.340212", | n | 33 | "metadata_modified": "2025-04-03T09:16:35.830438", |
34 | "name": | 34 | "name": | ||
35 | limination-resistant-characterizing-multi-compartment-toxicokinetics", | 35 | limination-resistant-characterizing-multi-compartment-toxicokinetics", | ||
36 | "notes": "Delayed toxicity is a phenomenon observed for aquatic | 36 | "notes": "Delayed toxicity is a phenomenon observed for aquatic | ||
37 | invertebrates exposed to nicotinic acetylcholine receptor (nAChR) | 37 | invertebrates exposed to nicotinic acetylcholine receptor (nAChR) | ||
38 | agonists such as neonicotinoids. Furthermore, recent studies observed | 38 | agonists such as neonicotinoids. Furthermore, recent studies observed | ||
39 | an incomplete elimination of neonicotinoids from exposed amphipods. | 39 | an incomplete elimination of neonicotinoids from exposed amphipods. | ||
40 | However, a mechanistic link between receptor binding and toxicokinetic | 40 | However, a mechanistic link between receptor binding and toxicokinetic | ||
41 | modeling has not been demonstrated yet.\r\nThe elimination of the | 41 | modeling has not been demonstrated yet.\r\nThe elimination of the | ||
42 | neonicotinoid thiacloprid in the freshwater amphipod Gammarus pulex | 42 | neonicotinoid thiacloprid in the freshwater amphipod Gammarus pulex | ||
43 | was studied in several toxicokinetic exposure experiments, | 43 | was studied in several toxicokinetic exposure experiments, | ||
44 | complemented with in vitro and in vivo receptor binding assays. Based | 44 | complemented with in vitro and in vivo receptor binding assays. Based | ||
45 | on the results, a two-compartment model was developed to predict | 45 | on the results, a two-compartment model was developed to predict | ||
46 | uptake and elimination kinetics of thiacloprid in G. pulex.\r\nAn | 46 | uptake and elimination kinetics of thiacloprid in G. pulex.\r\nAn | ||
47 | incomplete elimination of thiacloprid independent of elimination phase | 47 | incomplete elimination of thiacloprid independent of elimination phase | ||
48 | duration, exposure concentrations and pulses was observed. | 48 | duration, exposure concentrations and pulses was observed. | ||
49 | Additionally, the receptor binding assays indicated irreversible | 49 | Additionally, the receptor binding assays indicated irreversible | ||
50 | binding of thiacloprid to the nAChRs. Accordingly, a | 50 | binding of thiacloprid to the nAChRs. Accordingly, a | ||
51 | toxicokinetic-receptor model consisting of a structure and a membrane | 51 | toxicokinetic-receptor model consisting of a structure and a membrane | ||
52 | protein (i.e., nAChR) compartment was developed. The model | 52 | protein (i.e., nAChR) compartment was developed. The model | ||
53 | successfully predicted internal thiacloprid concentrations across | 53 | successfully predicted internal thiacloprid concentrations across | ||
54 | various experiments. \r\nOur results help understanding the delayed | 54 | various experiments. \r\nOur results help understanding the delayed | ||
55 | toxic and receptor-mediated effects towards arthropods caused by | 55 | toxic and receptor-mediated effects towards arthropods caused by | ||
56 | neonicotinoids. Furthermore, the results suggest that more awareness | 56 | neonicotinoids. Furthermore, the results suggest that more awareness | ||
57 | towards long-term toxic effects of irreversible receptor binding is | 57 | towards long-term toxic effects of irreversible receptor binding is | ||
58 | needed in a regulatory context. The developed model supports future | 58 | needed in a regulatory context. The developed model supports future | ||
59 | toxicokinetic assessment of receptor binding contaminants. \r\n", | 59 | toxicokinetic assessment of receptor binding contaminants. \r\n", | ||
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64 | "approval_status": "approved", | 64 | "approval_status": "approved", | ||
65 | "created": "2019-09-18T14:11:45.483866", | 65 | "created": "2019-09-18T14:11:45.483866", | ||
66 | "description": "We study the presence, fate and behaviour of | 66 | "description": "We study the presence, fate and behaviour of | ||
67 | organic contaminants in natural and treated waters with currently two | 67 | organic contaminants in natural and treated waters with currently two | ||
68 | main focuses. First, we improve and apply target and non-target | 68 | main focuses. First, we improve and apply target and non-target | ||
69 | analysis using high resolution mass spectrometry to obtain a more | 69 | analysis using high resolution mass spectrometry to obtain a more | ||
70 | comprehensive picture of contamination in aquatic environments and to | 70 | comprehensive picture of contamination in aquatic environments and to | ||
71 | characterize natural and technical elimination processes. Secondly, we | 71 | characterize natural and technical elimination processes. Secondly, we | ||
72 | study uptake and biological transformation of contaminants in aquatic | 72 | study uptake and biological transformation of contaminants in aquatic | ||
73 | organisms to better understand the effects on the organisms.", | 73 | organisms to better understand the effects on the organisms.", | ||
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124 | "status": "incomplete", | 153 | "status": "incomplete", | ||
125 | "substances": [ | 154 | "substances": [ | ||
126 | "Thiacloprid | 155 | "Thiacloprid | ||
127 | H9ClN4S/c11-9-2-1-8(5-13-9)6-15-3-4-16-10(15)14-7-12/h1-2,5H,3-4,6H2)" | 156 | H9ClN4S/c11-9-2-1-8(5-13-9)6-15-3-4-16-10(15)14-7-12/h1-2,5H,3-4,6H2)" | ||
128 | ], | 157 | ], | ||
129 | "substances_generic": [ | 158 | "substances_generic": [ | ||
130 | "insecticide", | 159 | "insecticide", | ||
131 | "neonicotinoid" | 160 | "neonicotinoid" | ||
132 | ], | 161 | ], | ||
133 | "systems": [ | 162 | "systems": [ | ||
134 | "lab", | 163 | "lab", | ||
135 | "water", | 164 | "water", | ||
136 | "gammarid tissue" | 165 | "gammarid tissue" | ||
137 | ], | 166 | ], | ||
138 | "tags": [ | 167 | "tags": [ | ||
139 | { | 168 | { | ||
140 | "display_name": "Organic contaminants", | 169 | "display_name": "Organic contaminants", | ||
141 | "id": "9db2001d-fe70-4bf0-bbe0-0db07bac3122", | 170 | "id": "9db2001d-fe70-4bf0-bbe0-0db07bac3122", | ||
142 | "name": "Organic contaminants", | 171 | "name": "Organic contaminants", | ||
143 | "state": "active", | 172 | "state": "active", | ||
144 | "vocabulary_id": null | 173 | "vocabulary_id": null | ||
145 | }, | 174 | }, | ||
146 | { | 175 | { | ||
147 | "display_name": "bioaccumulation", | 176 | "display_name": "bioaccumulation", | ||
148 | "id": "258b08dc-5c66-41a6-ab11-15969737d31f", | 177 | "id": "258b08dc-5c66-41a6-ab11-15969737d31f", | ||
149 | "name": "bioaccumulation", | 178 | "name": "bioaccumulation", | ||
150 | "state": "active", | 179 | "state": "active", | ||
151 | "vocabulary_id": null | 180 | "vocabulary_id": null | ||
152 | }, | 181 | }, | ||
153 | { | 182 | { | ||
154 | "display_name": "insecticides", | 183 | "display_name": "insecticides", | ||
155 | "id": "8d228132-eb95-4dd7-84ff-52980a48de3f", | 184 | "id": "8d228132-eb95-4dd7-84ff-52980a48de3f", | ||
156 | "name": "insecticides", | 185 | "name": "insecticides", | ||
157 | "state": "active", | 186 | "state": "active", | ||
158 | "vocabulary_id": null | 187 | "vocabulary_id": null | ||
159 | }, | 188 | }, | ||
160 | { | 189 | { | ||
161 | "display_name": "invertebrates", | 190 | "display_name": "invertebrates", | ||
162 | "id": "075b09f0-ad7d-4463-91be-4fe86abd446e", | 191 | "id": "075b09f0-ad7d-4463-91be-4fe86abd446e", | ||
163 | "name": "invertebrates", | 192 | "name": "invertebrates", | ||
164 | "state": "active", | 193 | "state": "active", | ||
165 | "vocabulary_id": null | 194 | "vocabulary_id": null | ||
166 | }, | 195 | }, | ||
167 | { | 196 | { | ||
168 | "display_name": "micropollutants", | 197 | "display_name": "micropollutants", | ||
169 | "id": "4d6921db-c058-412e-b9e4-1c7c3155e3da", | 198 | "id": "4d6921db-c058-412e-b9e4-1c7c3155e3da", | ||
170 | "name": "micropollutants", | 199 | "name": "micropollutants", | ||
171 | "state": "active", | 200 | "state": "active", | ||
172 | "vocabulary_id": null | 201 | "vocabulary_id": null | ||
173 | } | 202 | } | ||
174 | ], | 203 | ], | ||
175 | "tags_string": | 204 | "tags_string": | ||
176 | "bioaccumulation,invertebrates,micropollutants,Organic | 205 | "bioaccumulation,invertebrates,micropollutants,Organic | ||
177 | contaminants,insecticides", | 206 | contaminants,insecticides", | ||
178 | "taxa": [ | 207 | "taxa": [ | ||
179 | "Gammarus pulex" | 208 | "Gammarus pulex" | ||
180 | ], | 209 | ], | ||
181 | "taxa_generic": [ | 210 | "taxa_generic": [ | ||
182 | "invertebrates", | 211 | "invertebrates", | ||
183 | "crustaceans", | 212 | "crustaceans", | ||
184 | "amphipods", | 213 | "amphipods", | ||
185 | "gammarids" | 214 | "gammarids" | ||
186 | ], | 215 | ], | ||
187 | "timerange": [ | 216 | "timerange": [ | ||
188 | "2021-10 TO 2022-10" | 217 | "2021-10 TO 2022-10" | ||
189 | ], | 218 | ], | ||
190 | "title": "Data for: Elimination resistant: Characterizing | 219 | "title": "Data for: Elimination resistant: Characterizing | ||
191 | multi-compartment toxicokinetics of the neonicotinoid thiacloprid in | 220 | multi-compartment toxicokinetics of the neonicotinoid thiacloprid in | ||
192 | the amphipod Gammarus pulex using bioconcentration and receptor | 221 | the amphipod Gammarus pulex using bioconcentration and receptor | ||
193 | binding assays", | 222 | binding assays", | ||
194 | "type": "dataset", | 223 | "type": "dataset", | ||
195 | "url": "https://doi.org/10.25678/000841/", | 224 | "url": "https://doi.org/10.25678/000841/", | ||
196 | "variables": [ | 225 | "variables": [ | ||
197 | "concentration" | 226 | "concentration" | ||
198 | ], | 227 | ], | ||
199 | "version": null | 228 | "version": null | ||
200 | } | 229 | } |