From: Aquatic ecotoxicity of glyphosate, its formulations, and co-formulants: evidence from 2010 to 2023
Test organism | Type of tested compound | Tested concentrations | Duration | Tested endpoints | Observed effects | References |
---|---|---|---|---|---|---|
P. lineatus | Roundup | 10 mg l−1 | 6–96 ha | Antioxidant analysis, AChEb | Reduced SODc and glutathione peroxidase activity, increased glutathione levels and GSTd activity, inhibited AChE in brain (96 h) and in muscle (24–96 h) | [214] |
R. quelen | Roundup | 0.45 and 0.95 mg l−1 | 8 de | Oxidative stress parameters (e.g., antioxidant enzymes, GST activity) | Increased thiobarbituric acid reactive species and protein carbonyl levels (≥ 0.45 mg l−1), decreased GST activity (≥ 0.45 mg l−1), no effects on SOD and ascorbic acid | [215] |
D. rerio | Roundup Flex | 1, 5 and 10 mg AIf l−1 | 4 h 30 min | Biochemical parameters (e.g., ROSg, SOD, lipid peroxidation, apoptosis) | Increased ROS and cell death (10 mg AI l−1), no effects on SOD, GSH and lipid peroxidation | [216] |
S. trutta | GLYh, roundup | 0.01–10 mg a.e.i GLY l−1 | 14 d | Transcripts encoding components of the antioxidant system, stress-response proteins and pro-apoptotic signaling molecules | Upregulation of the antioxidant system, significant changes in the expression of transcripts encoding components of the antioxidant system, stress-response proteins, pro-apoptotic signaling molecules | [84] |
C. auratus | GLY | 2.5–5 mg l−1 | 120 h | Hematological and biochemical parameters | Decreased SOD, glutathione peroxidase (5 mg l−1), and catalase (≥ 2.5 mg l−1), increased malondialdehyde concentration, slightly decreased number of erythrocytes, hemoglobin and hematocrit levels | [217] |
Annual killifish (Cynopoecilus sp.) | Roundup original | 65–260 µg AI l−1 | 7 d | Oxidative stress parameters (e.g., SOD, GST, lipid peroxidation) | Age-dependent effects on the activity of SOD, catalase and the level of thiobarbituric acid reactive species, no effects on catalase activity | [218] |
P. reticulata | Roundup transorb | 0.91–3.66 mg l−1 | 24 h | Micronucleus, nuclear abnormalities | Concentration-dependent frequency of nuclear abnormalities, increased number of damaged cells | [219] |
P. mesopotamicus | Roundup full II | 2.75–13.25 mg l−1 | 96 h | Acute toxicity, micronucleus, nuclear abnormalities | LC50j = 8.92 mg l−1, higher frequency of micronucleus and nuclear abnormalities (2.75 mg l−1) | [220] |
A. anguilla | GLY, Roundup Ultra, POEAk | GLY: 17.9–35.7 µg l−1, GBHl: 58–116 µg l−1, POEA: 9.3–18.6 µg l−1 | 1–3 d | Genetic damage | Genotoxic potential of GLY, GBH and POEA | [221] |
L. rohita | Roundup | acute test: 6–14 mg l−1, chronic test: 0.63–2.06 mg l−1 | Acute test: 96 h, chronic test: 28 d | Haematological and biochemical parameters | 96-h LC50 = 10.16 mg l−1, reduced level of red blood cells, hemoglobin, and hematocrit value, increased level of white blood cells, altered biochemical and stress parameters (e.g., decreased activity of blood glucose, total protein, and alkaline phosphatase | [222] |
D. rerio | GLY | 0–1000 µg l−1 | 96 h | Mortality, heart rate, hatching rate | No mortality, lower heart rates (100 and 1000 µg l−1 at 48 h), altered transcriptome profiles (1000 µg l−1 after 96 h) | [223] |
D. rerio | GLY | 30–120 mg l−1 | 72 h | Survival and hatching rate, body lengths, embryo morphology, apoptosis, cardiovascular toxicity | Reduced survival, cardiac malformations apoptosis in the cardiac and vascular regions (≥ 60 mg l−1), decreased hatching rate and body length (≥ 90 mg l−1), altered caspase activity and ATPm level | [224] |
D. rerio | GLY, roundup original DI | 250–1000 µg l−1 | 96 h | Rate of survival and hatching, heart rate, malformations, behavior, biochemical biomarkers (e.g., GST and catalase, lipid peroxidation) | Decreased survival (500 µg l−1 GBH), no behavioral effects, increased hatching (GBH at 48 hpfn), higher rate of malformations (GBH), reduced heart rate, decreased activity of GST and AChE, no effects on other biochemical parameters | [225] |
C. macropomum | Roundup | 10 and 15 mg AI l−1 | 96 h | Blood analysis, enzyme activities | Affected hematological parameters and biotransformation processes, ROS production, increased DNA damage, inhibited AChE activity | [226] |
C. punctatus | Roundup | 3.25–6.51 mg AI l−1 | 35 d | DNA damage, lipid peroxidation, antioxidant enzymes activities | Concentration-dependent and tissue-specific DNA damage, increased lipid peroxidation, suppressed antioxidant enzymes | [227] |
D. rerio | GLY | 700 µg l−1 | 28 d | Hepatic metabolism | Sex-specific effects on hepatic metabolism, increased stress responses | [228] |
D. rerio | GLY | 0.7–35 mg l−1 | 1–1.5 h | Body length, heart rate, hormone levels, oxidative stress, inflammation reactions, apoptosis | Malformations, reduced heart rate and body length (≥ 7 mg l−1), decreased T3/T4 ratio (35 mg l−1), oxidative stress (≥ 7 mg l−1), induced inflammatory response and apoptosis | [229] |
D. rerio | GLY, AMPA, GBHs (Dominator Extra 680 SL, Fozat 480, Roundup Mega, Total | 0.35–2.8 mg a.e. l−1 | 120 hpf | Development, in vivo estrogenicity | Acute toxicity: AMPA > GLY > GBHs, sublethal abnormalities (0.35–2.8 mg l−1 GBHs), in vivo estrogenicity | [230] |
C. carpio, in vitro: cell fish line | GLY | In vivo: 0.5 and 15 mg l−1; in vitro: 0.65 and 3.25 mg l−1 | in vivo: 30 d; in vitro: 48 h | In vivo: histopathological analysis, biochemical analysis, swimming behavior; in vitro: cell proliferation, intracellular ROS, mitochondrial membrane potential, DNA damage | In vivo: oxidative DNA damage, liver inflammation, altered physical intestinal barrier (5–15 mg l−1), inhibited AChE (15 mg l−1), altered swimming behavior; in vitro: ROS production, mitochondrial dysfunction, reduced cell viability | [231] |
D. rerio | GLY | 1, 65, and 5000 µg l−1 | 72 h | Nuclear abnormalities and micronuclei | Increased frequency of nuclear morphological abnormalities and micronuclei formation | [232] |
D. rerio, C. carpio | GLY | 0.005–50 mg l−1 | 120 h | Mortality, hatching rate, developmental disorders | Highest cumulative mortality at 50 mg l−1, reduced hatching rate in C. carpio (especially at 50 mg l−1), hatching stimulation in D. rerio (96 hpf), concentration-dependent malformations | [81] |
D. rerio | GLY | 65 μg l−1 | 15 d | Morphological ultrastructural, biochemical parameters | No observable changes in general morphology, but altered ultrastructure of ovaries, increased oocyte diameter, higher expression of SF-1 | [233] |
D. rerio | GLY, AMPA | 1–700 ng ml l−1 | 72 h | Morphological changes, apoptotic cells, ATPase activity | Reduced survival, hatching and deformity rate (≥ 10 ng ml l−1), disturbed cardiac development and apoptosis, inhibited Na + /K + -ATPase and Ca2 + -ATPase activity (≥ 1 ng ml l−1) | [234] |
D. rerio | GLY, Roundup | GLY: 10 mg l−1, GBH: 0.01–10 mg a.e. GLY l−1 | 21 d | Mortality, reproductive parameters (e.g., hatching) | Decreased egg production, but no effects on fertilization rate (10 mg l−1 GLY), increased mortality and premature hatching (10 mg l−1 GLY/GBH) | [235] |
J. multidentata | Roundup Max | Acute test: 5–100 mg l−1, chronic test: 0.5 mg l−1 | Acute test: 96 h, chronic test: 28 d | LC50, male sexual activity, histological analysis, gill morphometric | LC50 = 19.02 mg l−1, concentration-dependent histological changes in the gills and liver (≥ 0.5 mg l−1), reduced number of copulations and mating success in males | [236] |
D. rerio | GLY | 5 or 10 mg l−1 | 24 or 96 h | Sperm quality (e.g., concentration and motility) | No effects on sperm concentration, reduced motility, mitochondrial function, sperm membrane and DNA integrity (≥ 5 mg l−1) | [237] |
D. rerio | GBH | 1–100 mg AI l−1 | 24–96 h | Mortality, morphological abnormalities, carbonic anhydrase activity, ROS, apoptosis | Decreased survival (≥ 1 mg l−1) and hatching rate (100 mg l−1), malformations and decreased carbonic anhydrase activity (≥ 1 mg l−1) ROS production, increased apoptosis | [238] |
H. transpacificus | Roundup | 0.064–640 mg AI l−1 | 6 h | Hepatic 17β-estradiol, AChE, total glutathione | No effects on AChE, altered 17β-estradiol in males (≥ 0.078 mg l−1), reduced glutathione concentration in males (0.7 mg l−1) | [239] |
C. gariepinus | Forceup | 0.02–1 mg l−1 | 24 h–8 d | Haematological and biochemical parameters, exploratory behavior, growth performance | Decreased body weight, (≥ 0.02 mg l−1), growth (≥ 0.05 mg l−1) and survival (1 mg l−1), altered behavioral parameters (≥ 0.02 mg l−1), increased malondialdehyde (≥ 0.05 mg l−1), decreased reduced glutathione and SOD activity (≥ 0.1 mg l−1), hematological effects | [240] |
O. mykiss | GLY, GBHs (roundup innovert and Viaglif Jardin) | 1 μg l−1 | 10 months | Survival of the eggs, hematologic, immunologic, metabolic parameters, oxidative stress | No effects on average body weight, relative fecundity, fertility, and enzyme activities, decreased level of macrophages and phagocytic activity (GBHs, two months before spawning). Lower level of tumor necrosis factor-α (1 month after spawning) | [241] |
C. decemmaculatus | Roundup Max | 0.2–2 mg l−1 | 42 d | Somatic indexes (condition factor, hepato-somatic index), locomotor activity, enzymatic activities (e.g., AChE, catalase, GST) | No effects on locomotor activity, somatic indexes, AChE and catalase activity Higher GST activity in liver, reduced aspartate aminotransferase, alanine aminotransferase activity | [242] |
C. decemmaculatus | GLY | 1–35 mg l−1 | 96 h | AChE activity | Inhibited AChE activity (≥ 1 mg l−1) | [243] |
C. carpio | Roundup | 0.5–10.0 mg l−1 | 96 h | AChE activity, oxidative stress | Inhibited AChE activity (increased level after the recovery period), increased levels of thiobarbituric acid reactive species in the brain | [244] |
R. quelen | GBHs (Orium, Roundup Original and Biocarb) | 2.5 and 5.0 mg AI l−1 | 96 h | Oxidative stress indicators (e.g., TBARSo, antioxidant enzymes), transaminases | Increased TBARS and reduced catalase activity (≥ 2.5 mg l−1), significant effects on SOD and GST, moderate to severe histopathological alterations, reduced levels of transaminases (Biocarb: 2.5 mg AI l−1) | [245] |
P. reticulata | GLY, AMPAp | GLY: 50–73.2 mg l−1, AMPA: 86.8–180 mg l−1 | 96 h | LC50, histopathological and histomorphometric analyses | LC50GLY = 68.78–70.87 mg l−1, LC50AMPA = 164.3–180 mg l−1, sex- and tissue-specific histopathological responses in the gills and liver (GLY: 35 mg l−1, AMPA: 82 mg l−1) | [246] |
Surubim (crossbred between two Neotropical catfish species) | Roundup original | 2.25–15 mg l−1 | 96 h | Metabolic and behavioral parameters | Concentration-dependent and tissue-specific effects on metabolic parameters (e.g., glucose, lactate levels), decreased plasma cholesterol (2.25–15 mg l−1), concentration-dependent behavioral effects | [247] |
D. rerio | GLY, roundup | 0.01–0.5 mg AI l−1 | 96 h | Survival, morphological defects, behavioral parameters (e.g., exploratory and aggressive behavior, aversive memory) | No effects on survival, reduced body length (GBH: 0.01–0.5 mg AI l−1) and altered behavior (≥ 0.01 mg AI l−1) in larvae, in adults: altered exploratory (≥ 0.065 mg l−1) and aggressive (≥ 0.01 mg AI l−1) behavior, impaired memory | [248] |
C. carpio | Aria | 20.5–61.5 g l−1 | 96 h | LC50, histopathological and behavioral parameters | LC50 = 28.2 g l−1, hyperplasia, hypertrophy, and hyperemia of the gills, significant differences in the swimming behavior | [249] |
Crossbred red tilapia (Oreochromis niloticus × Oreochromis mossambicus) | GLY | 25–150 mg l−1 | 7 weeks | Growth, somatic indexes | Concentration-dependent growth inhibition, alteration of HSIq and GSIr, decreased body weight and length (≥ 25 mg l−1) | [250] |
P. reticulata | Roundup transorb | 0.34–5.2 mg GLY l−1 | 2–96 h | LC50, proteomic response, histopathological effects | LC50 = 3.4 mg l−1, time-dependent histopathological effects in the gills (1.82 mg AI l−1), regressive, vascular and progressive disorders were indicated by histopathological indexes, 14 proteins (e.g., involved in metabolism and stress response) were affected | [251] |
C. carpio | GLY | 5 and 15 mg l−1 | 60 d | Growth, AChE activity, behavior parameters, microbiome | Reduced weight growth (15 mg l−1), affected blood–brain barrier permeability (≥ 5 mg l−1), decreased AChE activity, reduced swimming speed (5 mg l−1), altered microbiome | [252] |
O. niloticus | GLY | 2 mg l−1 | 60 d | Biochemical parameters, transcriptome and proteome analysis | No effects on GPTs and GOTt activities, increased SOD activity and MDAu content, reduced GSHv and T-AOCw levels, 94 up-regulated and 131 down-regulated genes (e.g., involved in ion transport, lipid metabolism) | [253] |
Novel 3D S. salar co-culture model (primary hepatocytes and kidney epithelial cells) | GLY | 0.8–84.5 mg l−1 | 48 h | Cell viability, metabolomic profiling | Higher cell viability in 3D cultivated hepatocytes, affected lipid metabolism, increased cholesterol level and down-regulation of clusterin (84.5 mg l−1) | [254] |
D. rerio | GLY, AMPA | 0.02–1.69 mg l−1 (combination 1:1) | 7 d | Survival, hatching, ROS, behavioral parameters | No effects on mortality, hatch success, development, and ROS production, concentration-dependent and substance-specific effects on enzymes (e.g., SOD), hyperactivity (GLY), lack of anxiety-like behaviors | [255] |
O. niloticus | Roundup | 0.6 mg AI l−1 | 2–4 weeks | Oxidative stress, immunosuppression, liver and kidney dysfunction | Reduced body weight, no effects on growth, liver and kidney dysfunction, reduced level of tested proteins, oxidative stress response, antioxidant activity, lipid peroxidation, immunosuppression | [256] |
D. rerio | GLY | Larvae: 0.2456 µg l−1 larvae/day (dietary) Adults: 1, 5, and 10 mg l−1 | 96 h | Larvae: survival, adults: bioconcentration factors in the gills, liver, and muscle | Increased mortality, affected energy metabolism and feeding behavior of larvae, altered dynamics between zooplankton and fish larvae, bioaccumulation in zooplankton | [257] |
P. lineatus | POEA | 0.15–1.5 mg l−1 | 24 h | DNA damages, biochemical and physiological parameters | Increased plasma lactate levels and decreased hepatic catalase activity, red blood cell counts and hemoglobin content, DNA damage, lipid peroxidation and hemolysis, no effects on hematocrit levels | [258] |
A. anguilla | GLY, Roundup Ultra, POEA | GLY: 17.9 and 35.7 μg l−1, GBH: 58 and 116 μg l−1, POEA: 9.3 and 18.6 μg l−1 | 1–3 d | DNA damage, GDI | Higher levels of DNA damage (GBH: 116 μg l−1, GLY: 17.6 μg l−1, POEA: 9.3–18.6 μg l−1, synergistic interaction between POEA and GLY in promoting non-specific DNA damage | [221] |
D. rerio | GLY, Atanor 48, AMPA, POEA | GLY, GBH, AMPA: 1.7–100 mg l−1, POEA: 0.4–16 mg l−1 | 96 h | Acute toxicity, genetic damage index | No acute toxic effects of GLY and AMPA, LC50GBH = 76.50 mg l−1, LC50POEA = 5.49 mg l−1, genotoxic potential, direct genotoxic properties of POEA | [259] |