Mode of Action : Target Organisms

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glyphosate use include soybeans, eld corn, pasture and hay. 2, 6 Some plants have been genetically engineered to be resistant to glyphosate. Glyphosatetolerant soybeans, corn, cotton, and canola are examples of such plants. 4, 9 This fact sheet does not address glyphosate-tolerant crops. Uses for individual products containing glyphosate vary widely. Always read and follow the label when applying pesticide products. Signal words for products containing glyphosate may range from Caution to Danger. The signal word re ects the combined toxicity of the active ingredient and other ingredients in the product.
See the pesticide label on the product and refer to the NPIC fact sheets on Signal Words and Inert or "Other" Ingredients.
To nd a list of products containing glyphosate which are registered in your state, visit the website http://npic.orst.edu/reg/state_agencies.html select your state then click on the link for "State Products."

Mode of Action: Target Organisms
In plants, glyphosate disrupts the shikimic acid pathway through inhibition of the enzyme 5enolpyruvylshikimate-3-phosphate (EPSP) synthase. The resulting de ciency in EPSP production leads to reductions in aromatic amino acids that are vital for protein synthesis and plant growth. 1, 4 Glyphosate is absorbed across the leaves and stems of plants and is translocated throughout the plant. 1, 3 It concentrates in the meristem tissue. 10 Plants exposed to glyphosate display stunted growth, loss of green coloration, leaf wrinkling or malformation, and tissue death. Death of the plant may take from 4 to 20 days to occur. 4, 10 The sodium salt of glyphosate can act as a plant growth regulator and accelerate ripening of speci c crops. 2

Non-target Organisms
The shikimic acid pathway is speci c to plants and some microorganisms. The absence of this pathway in mammals may explain the low toxicity of glyphosate to non-target organisms. 11,12 Studies indicate that the surfactant polyoxyethyleneamine or polyethoxylated tallow amine (both abbreviated POEA), used in some commercial glyphosate-based formulations, may be more toxic by the oral route to animals than glyphosate itself. 13, 14 The mechanism of toxicity of glyphosate in mammals is unknown, but it may cause uncoupling of oxidative phosphorylation. 15 However, this hypothesis has been disputed. 16 LD 50 /LC 50 : A common measure of acute toxicity is the lethal dose (LD 50 ) or lethal concentration (LC 50 ) that causes death (resulting from a single or limited exposure) in 50 percent of the treated animals. LD 50 is generally expressed as the dose in milligrams (mg) of chemical per kilogram (kg) of body weight. LC 50 is often expressed as mg of chemical per volume (e.g., liter (L)) of medium (i.e., air or water) the organism is exposed to. Chemicals are considered highly toxic when the LD 50 /LC 50 is small and practically non-toxic when the value is large. However, the LD 50 /LC 50 does not re ect any effects from long-term exposure (i.e., cancer, birth defects or reproductive toxicity) that may occur at levels below those that cause death.
The isopropylamine salt is of very low toxicity to rats, with an LD 50 greater than 5000 mg/kg. 1 The acute oral LD 50 for the ammonium salt is 4613 mg/kg in rats. 1 The acute oral LD 50 in three formulated products ranged from 3860 to greater than 5000 mg/kg in rats. 4

Dermal
Glyphosate is low in toxicity to rabbits when applied to the skin. The acute dermal LD 50 in rabbits is greater than 2 g/kg. 17 Glyphosate is low in toxicity for eye irritation and very low in toxicity for dermal irritation. In studies with glyphosate manufacturing use products, researchers observed mild eye irritation in rabbits that cleared in seven days. 18, 19 Glyphosate was not found to be a skin sensitizer. 6 The isopropylamine and ammonium salts are also low in toxicity via the dermal route. The LD 50 in rabbits was greater than 5000 mg/kg for both salts, and these salts are considered slight eye irritants but not skin irritants. 1 Of three formulated products tested, skin irritation varied from none to moderate, and eye irritation was rated as none, moderate, and severe. Dermal LD 50 values in rabbits exposed to these products were greater than 5000 mg/kg. 4 The formulated product Roundup®, containing 41% glyphosate, was applied to the skin of 204 male and female volunteers in a modi ed Draize test. No sensitization was observed. The researchers concluded that exposure would not lead to photoirritation or photosensitization. 20

Inhalation
Glyphosate is very low in toxicity to rats when inhaled. The acute inhalation LC 50 in rats is greater than 4.43 mg/L based on a 4-hour, nose-only inhalation study. 21 The 4-hour LC 50 for rats exposed to the isopropylamine form of glyphosate was greater than 1.3 mg/L air. 1 The LC 50 for rats exposed to the ammonium salt form of glyphosate was greater than 1.9 mg/L in a whole body exposure.

Signs of Toxicity -Animals
Animals exposed to formulated glyphosate herbicides have displayed anorexia, lethargy, hypersalivation, vomiting, and diarrhea. Symptoms persisted for 2 to 24 hours following exposure. The surfactants in formulated products are thought to be responsible for the clinical signs. 22 Clinical signs typically appear within 30 minutes to 2 hours following ingestion. Animals may exhibit excitability and tachycardia at rst, followed by ataxia, depression, and bradycardia. Severe cases may progress to collapse and convulsions. 15 The Veterinary Poisons Information Service in London, England recorded 150 cases over an 8year period of dogs exposed to glyphosate primarily from eating grass recently treated with formulated products. Of these, roughly 40% of the dogs exhibited no clinical signs, 45% exhibited mild to moderate clinical signs, and roughly 15% were classi ed as serious. 15 The Centre National d'Informations Toxicologiques Veterinaires of France reported 31 certain cases of intoxication of domestic animals by glyposate-containing products in a 3-year period. Most exposures resulted from animals ingesting the product prior to application. Of these cases, 25 were dogs and 4 were cats. Vomiting occurred within 1-2 hours of ingestion in 61% of the cases. Hypersalivation occurred in 26% of cases, and mild diarrhea was reported in 16% of cases. Centre records did not report long-lasting effects or any fatalities. 23

Signs of Toxicity -Humans
In a review of 80 intentional ingestion cases, 79 of which were suicide attempts, researchers identi ed typical symptoms of erosion of the gastrointestinal tract, dysphagia or di culty swallowing, and gastrointestinal hemorrhage. Seven cases resulted in death. 24 Accidental ingestions are associated with mild gastrointestinal effects. 14 Eye and skin irritation have occasionally been reported from dermal exposure to glyphosate formulations. 13,14 However, adverse health effects are typically associated with exposure that occurs while mixing a concentrated product, not the use of dilute spray solutions. 13 Permanent ocular or dermal damage is very rare. 13,14, 25 Inhalation of spray mist may cause oral or nasal discomfort, as well as tingling and throat irritation. 14 npic.orst.edu/factsheets/archive/glyphotech.html 6/19

LOEL: Lowest Observed Effect Level
Always follow label instructions and take steps to minimize exposure. If any exposure occurs, be sure to follow the First Aid instructions on the product label carefully. For additional treatment advice, contact the Poison Control Center at 1-800-222-1222. If you wish to discuss an incident with the National Pesticide Information Center, please call 1-800-858-7378.

Chronic Toxicity: Animals
Researchers gave beagle dogs capsules containing 0, 20,100, or 500 mg/kg/day of glyphosate for one year. No effects were observed; the NOEL for systemic toxicity is greater than or equal to 500 mg/kg/day. 26 See the text box on NOAEL, NOEL, LOAEL, and LOEL.
Male rats were fed a diet containing glyphosate at 89, 362, or 940 mg/kg/day and females were similarly fed at concentrations of 113, 457, or 1183 mg/kg/day for 2 years. In the high-dose female group, researchers observed decreased body weight gain. In the highdose male group, researchers observed decreased urinary pH, increased evidence of cataracts and lens abnormalities, and increased liver weight. No effects were observed in the low-dose and mid-dose groups. The LOEL for systemic toxicity was 940 and 1183 mg/kg/day for males and females, respectively. The NOEL for systemic toxicity is 362 mg/kg/day for males and 457 mg/kg/day for females. 27 Laboratory rats were fed diets containing glyphosate at doses of 0, 100, 300, or 1000 mg/kg/day for two years. After 52 weeks, some rats in the two highest dose groups had enlarged salivary glands with cellular changes. The NOEL was determined to be 100 mg/kg/day. 28 Based on a battery of tests, glyphosate is not expected to have immunotoxicity or neurotoxicity. Laboratory mice were fed diets containing glyphosate for 28 days. The NOAEL for immunotoxicity was determined to be 1448 mg/kg/day. 29 The NOAEL for subchronic neurotoxicity in rats was determined to be 1546.5 and 1630.6 mg/kg/day for males and females, respectively. 30 The Acceptable Daily Intake (ADI) of a combination of glyphosate and certain metabolites (AMPA, N-acetyl glyphosate, and N-acetyl AMPA) for humans is 1.0 mg/kg. In 2011, the International Estimated Daily Intake (IEDI) of glyphosate and major metabolites was estimated to range from 0-2% of the ADI. 31, 32 The chronic reference dose for glyphosate is 1.75 mg/kg/day. 33 See the text box on Reference Dose (RfD).

Humans
Researchers collected urine samples over 8 months from workers at two forestry nurseries where glyphosate was used for weed control. No glyphosate was detected in any of the 355 urine samples. The researchers attributed the lack of detected glyphosate in worker urine samples to the poor absorption of glyphosate through the skin. 34 See the text box on Exposure.
npic.orst.edu/factsheets/archive/glyphotech.html 7/19 Exposure: Effects of glyphosate on human health and the environment depend on how much glyphosate is present and the length and frequency of exposure. Effects also depend on the health of a person and/or certain environmental factors.
Five forestry workers sprayed glyphosate for 6 hours a day over the course of a week. No statistically signi cant differences were found in medical examinations and laboratory testing performed on the workers following pesticide application. 35 Researchers collected urine samples from farm families in South Carolina and Minnesota as part of the Farm Family Exposure Study. On the day of application, 60% of farmers had a detectable level of glyphosate in their urine of at least 1 ppb. The geometric mean of glyphosate detected was 3 ppb, with a maximum value of 233 ppb. Mean urinary concentrations of glyphosate were higher in farmers who did not use rubber gloves during application. 36

Endocrine Disruption:
Rats and mice were fed a diet containing 0, 3125, 6250, 12,500, 25,000, or 50,000 ppm of 99% pure glyphosate for 13 weeks. The two highest dose groups of male rats had a signi cant reduction in sperm concentrations, although concentrations were still within the historical range for that rat strain. The highest dose group of female rats had a slightly longer estrus cycle than the control group. 37 Researchers reviewed the scienti c literature on glyphosate, its major metabolite AMPA, formulated Roundup® products manufactured by Monsanto, and the surfactant POEA. They found no evidence of endocrine effects in humans or other mammals. 13 Using results from the EPA's Endocrine Disruptor Screening Program (EDSP), glyphosate was not considered to be an endocrine disruptor based on a lack of potential interaction with the estrogen, androgen or thyroid pathways. 38 Carcinogenicity:

Animals
Researchers fed rats a diet containing glyphosate at 0, 89, 362, or 940 mg/kg/day (males) and 0, 113, 457, or 1183 mg/kg/day (females) for two years. The high dose in this study approaches or exceeds the limit dose recommended for carcinogenicity studies. Slight increases in pancreatic islet cell adenomas, hepatocellular adenomas, and thyroid C-cell adenomas were observed in some cases. None of these ndings were statistically signi cant. The incidence of tumors was within the range of historical controls (historical control data from seven years of laboratory research) for the evaluated tumor types in this study. The U.S. EPA concluded the tumors were not treatment-related. 27, 39 In a carcinogenicity study, mice were fed a diet containing glyphosate (0, 161/195, 835/968, 4945/6069 mg/kg/day for males and females, respectively) for 24 months. The moderate and high doses in this study exceed or approach the limit dose recommended for carcinogenicity studies. In the high-dose groups researchers observed decreased body weight gain in both male and female mice. In high-dose males, slightly increased incidence of renal tubular adenomas was noted. A later re-evaluation of tissues determined that renal tumors were not related to glyphosate exposure. An independent group of pathologists and biometricians also concluded that the occurrence of adenomas was not caused by glyphosate. Kidney tissue npic.orst.edu/factsheets/archive/glyphotech.html 8/19 examinations found chronic interstitial nephritis and tubular epithelial basophilia and hypertrophy in male rats. Overall, there was not an increase in tubular lesions observed in male mice. 39,40, 41 In a carcinogenicity study, technical grade glyphosate was given to male and female rats in their diet (0, 95, 316.9, and 1229.7 mg/kg/day). In female rats, a slight increase in mammary gland tumors was noted. Tumor incidence was not statistically signi cant in pairwise comparisons. 39 Gold sh (Carassius auratus) were exposed to 5, 10, or 15 ppm of the formulated product Roundup® containing the IPA salt of glyphosate and the surfactant POEA for 6 days. Researchers noted increased DNA and micronuclei damage in the peripheral erythrocytes. This may have resulted from decreased DNA repair. Genotoxicity test results are generally mixed, although formulated products appear to be more likely to cause effects than glyphosate alone. 42 Glyphosate has been the subject of numerous genotoxicity tests and the results are overwhelmingly negative. 31 Doses that showed positive results in vivo were too high to be considered relevant for human health risk assessment. 39

Humans
The U.S. EPA classi ed glyphosate as "not likely to be carcinogenic to humans." Human carcinogenic potential was evaluated by reviewing available epidemiological, animal carcinogenicity, and genotoxicity data. research and effects seen at doses higher than the limit dose or the maximum tolerated dose (MTD). 51 Researchers reviewed the scienti c literature on glyphosate, its major metabolite AMPA, formulated Roundup® products manufactured by Monsanto, and the surfactant POEA. They found that Roundup® and its components did not cause mutations or tumor formation. The researchers concluded that glyphosate is not carcinogenic. 13 Researchers assessed the exposure-response relationship between use of products containing glyphosate and cancer in 57, 311 licensed pesticide applicators participating in the Agricultural Health Study. Exposure to glyphosate was not associated with overall cancer incidence or most cancer subtypes. In a small number of cases, there was a "suggested association" between glyphosate exposure and multiple myeloma incidence. 52 Additional reviews of AHS data and other epidemiological studies reveal no consistent association between glyphosate and solid tumors, leukemia, Hodgkin's Lymphoma, and multiple myeloma. Available data are insu cient to support conclusions regarding associations between glyphosate and Non-Hodgkin's Lymphoma. 39

Reproductive or Teratogenic Effects: Animals
In a developmental study, pregnant rabbits were given glyphosate by gavage (stomach tube) on gestation days 7-19 at doses of 0, 100, 175, 300 mg/kg/day. Rabbits in the middle and higher doses had diarrhea or few and/or no feces. Rabbits were the most sensitive animal species tested, with a developmental NOAEL of 300 mg/kg/day. Based on this rabbit study, the chronic dietary and incidental exposure NOAEL and LOAEL are 100 and 175 mg/kg/day, respectively. 30 Researchers dosed pregnant rats with glyphosate by gavage (stomach tube) on gestation days 6-19 at doses of 0, 300, 1000, or 3500 mg/kg/day. At the highest dose, they detected decreased body weight gains in both the dams and fetuses, increased maternal mortality, and an increased number of fetal skeletal abnormalities. The NOEL for maternal and developmental toxicity was 1000 mg/kg/day and the LOEL was 3500 mg/kg/day. 30, 53 In a developmental study, scientists exposed pregnant rabbits to glyphosate by gavage on gestation days 6-27 at doses of 0, 75, 175, or 350 mg/kg/day. They detected no developmental effects. At the highest dose tested, the animals exhibited diarrhea, nasal discharge, and increased mortality; too many animals died in this group to assess developmental effects at this dose. The NOEL for maternal effects was 175 mg/kg/day. 30, 54 After reviewing the toxicological database, EPA found no evidence of increased susceptibility of young rats and rabbits to in utero exposures of glyphosate. 30 Dietary concentrations of up to 10,000 ppm or 293 mg/kg/day of glyphosate given to rats over two generations had no effect on male or female sexuality and fertility. The NOAEL for parental and offspring toxicity is 3000 ppm, based upon a reduction of body weight at 10,000 ppm. 31 Questionnaires lled out by farm operators and eligible couples collected during the Ontario Farm Family Health Study suggested that there was an association between preconception exposure to pesticide products containing glyphosate and elevated risks of late spontaneous abortion. 56

Fate in the Body: Absorption
Animal studies have indicated that 30-36% of glyphosate is absorbed after ingestion. 11,13,57 Dermal absorption of glyphosate is poor. 6 An in vitro experiment with human skin resulted in a maximum of 2.2% of 2.6 μg/cm 2 glyphosate was absorbed across the skin. Absorption peaked 8 hours after administration. 58 Researchers applied glyphosate to abdominal skin of monkeys at doses of 5400 μg or 500 μg over 20 cm 2 of skin. Over a 7 day period, 73.5% and 77.1% of the applied dose remained on the skin. 58 Glyphosate is non-volatile. 6 Absorption from inhalation exposure is not expected to be signi cant. 14

Distribution
Rats dosed orally with 10 mg/kg glyphosate attained peak concentrations in their tissues 6 hours following dosing. The gastrointestinal tract contents accounted for 50% of the dose, with the tissue of the small intestine accounting for an additional 18%. Approximately 5% of the dose was found in bone and 6% in the carcass, with 1% or less of the dose distributed to abdominal fat, blood, colon, kidney, liver, and stomach. 57 Researchers gave rats a single oral dose of 10 mg/kg or 1000 mg/kg of glyphosate. Seven days after administration, the absorbed dose had distributed throughout the body, although it was primarily concentrated in the bone. 59 Researchers fed hens and goats glyphosate and found glyphosate and its major metabolite AMPA in eggs, milk, and the animals' body tissues. 13,60,61

Metabolism
Glyphosate undergoes little metabolism and is excreted mostly unchanged in the feces and secondarily in the urine. 3,13,62 Samples taken from goats and hens fed glyphosate contained the parent compound and AMPA, but there was no evidence of other glyphosate metabolites in body tissues, eggs, or milk. 6 High ratios of glyphosate to AMPA were detected in a human patient's blood serum 8 hrs (22.6 μg/mL glyphosate to 0.18 μg/mL AMPA) and 16 hrs (4.4 μg/mL glyphosate to 0.03 μg/mL AMPA) post-ingestion, as well as in the patient's total amount of urine. This indicates that glyphosate metabolism was minimal. 63 Excretion npic.orst.edu/factsheets/archive/glyphotech.html 11/19 The "half-life" is the time required for half of the compound to break down in the environment. Animal studies indicate that glyphosate is primarily excreted through the urine and feces. 3,13,62 A rat given a single oral dose of glyphosate eliminated 0.27% of the administered dose as carbon dioxide, and excreted 97.5% as glyphosate in urine and feces. Researchers detected AMPA in urine (0.2-0.3% of administered dose) and feces (0.2-0.4% of administered dose). 64, 65 Glyphosate is cleared from the body of rats 168 hours after administration. 11 Two human patients who were poisoned with glyphosate had peak plasma glyphosate concentrations within 4 hours of ingestion. After 12 hours, glyphosate was almost undetectable. 66

Medical Tests and Monitoring:
Glyphosate exposure can be monitored through measurement of glyphosate and AMPA concentrations in blood or urine. Glyphosate is relatively stable to chemical and photo decomposition. 6 The primary pathway of glyphosate degradation is soil microbial action, which yields AMPA and glyoxylic acid. Both products are further degraded to carbon dioxide. 3 Glyphosate adsorbs tightly to soil. Glyphosate and its residues are expected to be immobile in soil. 6

Water
The median half-life of glyphosate in water varies from a few days to 91 days. 1 Glyphosate did not undergo hydrolysis in buffered solution with a pH of 3, 6, or 9 at 35 °C. Photodegradation of glyphosate in water was insigni cant under natural light in a pH 5, 7, and 9 buffered solution. 72, 73 Glyphosate in the form of the product Roundup® was applied to aquatic plants in fresh and brackish water. Glyphosate  of glyphosate to bottom sediments depended heavily on the metals in the sediments. If chelating cations are present, the sediment half-life of glyphosate may be greatly increased. 74 Glyphosate has a low potential to contaminate groundwater due to its strong adsorptive properties. However, there is potential for surface water contamination from aquatic uses of glyphosate and soil erosion. 6 Volatilization of glyphosate is not expected to be signi cant due to its low vapor pressure. 6

Air
Glyphosate and all its salts are very low in volatility with vapor pressures ranging from 1.84 x 10 -7 mmHg to 6.75 x 10 -8 mmHg at 25 °C. 1,4, 8 Glyphosate is stable in air. 1

Plants
Glyphosate is absorbed by plant foliage and transported throughout the plant through the phloem. 3 Glyphosate absorption across the cuticle is moderate, and transport across the cell membrane is slower than for most herbicides. 4 Because glyphosate binds to the soil, plant uptake of glyphosate from soil is negligible. 3 Glyphosate accumulates in meristems, immature leaves, and underground tissues. Studies with technical grade glyphosate found an 8-day dietary LC 50 greater than 4000 ppm for mallard ducks and bobwhite quail, indicating slight toxicity. 78, 79 Glyphosate is not expected to cause reproductive impairment in birds at dietary levels of up to 1000 ppm. 6 An ecological risk assessment concluded that the greatest risk posed by glyphosate and its formulated products to birds and other wildlife results from alteration of habitat. 7

Fish and Aquatic Life
Technical grade glyphosate ranges from slightly toxic to practically non-toxic to freshwater sh, with a 48-hour LC 50 of greater than 24 mg/L to 140 mg/L. 6 Formulated glyphosate products range from moderately toxic to practically non-toxic to freshwater sh, with 96-hour LC 50 values ranging from 1.3 mg/L to greater than 1000 mg/L. 6 The preparation of the surfactant POEA known as MON 0818 is used in some glyphosate formulations. 7 POEA is moderately toxic to very highly toxic to freshwater sh. The 96-hour LC 50 values ranged from 0.65 mg/L to 13 mg/L. Products containing MON 0818 state on the label "This pesticide is toxic to sh". 6 The LC 50 of glyphosate for rainbow trout (Onchorynchus mykiss) was 140 mg/L, for fathead minnows (Pimephales promelas) was 97 mg/L, for channel cat sh (Icalurus punctatus) was 130 mg/L and for bluegill sun sh (Lepomis macrochirus) was 150 mg/L. When they were exposed to Roundup®, the LC 50 s for these same sh were 8.3, 2.4, 13.0, and 6.4 mg/L, respectively. 80 Technical grade glyphosate is slightly toxic to practically non-toxic to freshwater invertebrates, with a 48-hour LC 50 ranging from 55 ppm to 780 ppm. 6 The 48-hour LC 50 for Daphnids was 3.0 mg/L and the LC 50 for midge larvae was 16 mg/L when exposed to the formulated product Roundup®. 80 Researchers calculated LC 50 values for four species of amphibians (the northern leopard frog (Rana pipiens), the wood frog (R. sylvatica), the green frog (R. clamitans), and the American toad (Bufo americanus)) exposed to the original Roundup® formulation of glyphosate. The 24hour LC 50 values for the different species ranged from 6.6 to 18.1 mg/L. 81 Green frogs (R. clamitans) were exposed to technical glyphosate in the form of the isopropylamine salt, the surfactant POEA, and six formulated products containing glyphosate. The surfactant was most toxic to R. clamitans with a 24 and 96-hour LC 50 of 1.1 mg/L (95% CI 1.1-1.2) and 1.1 mg/L (95% CI 1.0-1.1), respectively. Technical glyphosate was least toxic, with 24 and 96-hour LC 50 of >38.9 g/L. The toxicity of the formulated products fell between these values. 81 A chronic toxicity study with technical grade glyphosate reported reduced reproductive capacity in Daphnia magna with a maximum acceptable toxicant concentration of 50 to 96 ppm. 82 Technical grade glyphosate is practically non-toxic to slightly toxic to estuarine and marine organisms. The 96-hour LC 50 is 281 ppm for grass shrimp (Palaemonetas vulgaris) and 934 ppm for ddler crab (Uca pagilator). 83 The 48 https://www.epa.gov/ground-water-and-drinkingwater/national-primary-drinking-water-regulations#one Studies indicate that both technical and formulated glyphosate are practically non-toxic to honeybees, with acute oral and acute contact LD 50 values greater than 100 μg/bee. 85 An ecological risk assessment of Roundup® concluded that the greatest risks to arthropods were from altered habitat structure and food availability. 7 The earthworm LC 50 in soil is greater than 5000 ppm for Monsanto's formulated product Roundup®. 4 Regulatory Guidelines: The U.S. EPA classi ed glyphosate as "not likely to be carcinogenic to humans." 30, 39 The reference dose (RfD) for glyphosate is 1.75 mg/kg/day. 33 See the text box on Reference Dose (RfD). The Acceptable Daily Intake (ADI) of a combination of glyphosate and certain metabolites (AMPA, N-acetyl glyphosate, and N-acetyl AMPA) for humans is 1.0 mg/kg. 31, 32 The U.S. EPA has set a One-Day Health Advisory of 20 mg/L. 86 The U.S. EPA has set a Ten-day Health Advisory of 20 mg/L. 86 The maximum contaminant level (MCL) is 0.7 mg/L. 86 See the text box on Maximum Contaminant Level (MCL).