Research In Cellular and Natural Health

Cell damaging effects of glyphosate – Are we ready for Roundup?

M. Chatterjee., Ph.D.
V. Ivanov, M.D., Ph.D.
A. Niedzwiecki, Ph.D.
Dr. Rath Research Institute, CA, US

Dr. Aleksandra Niedzwiecki,
Dr. Rath Research Institute,
1260 Memorex Drive, Santa Clara, CA 95050, USA.
Email: author@jcmnh.org

Introduction

Glyphosate is the active ingredient of many widely used, broad-spectrum herbicides and is commonly applied as a broadleaf weedicide in commercial agriculture. Created by Monsanto in 1970 and marketed from 1974 as “Roundup”, glyphosate has been used extensively across the world ever since1. Although the USA remains its biggest consumer, the use of glyphosate has also increased in other countries. As such, from 1999 to 2010 glyphosate use in Germany increased by 100%, now being sprayed on nearly 40% of German farmland each year2. Due to such extensive use, the genetically modified crop plants called “Roundup Ready” were created, which are resistant to glyphosate. This further increases the use of this herbicide. The majority of soybean, cotton and corn crops grown in the USA today are of this Roundup Ready variety, which is heavily exposed to glyphosate3.

Glyphosate prevents plants from making aromatic amino acids and other organic compounds necessary for life. Since these processes do not occur in animals, glyphosate was considered relatively harmless for large scale use4. Epidemiological studies also found no causal link between glyphosate and cancer5. However, contradictory evidence began to appear soon after as more cases of long-term glyphosate exposure to humans became available. Glyphosate was implicated in Non-Hodgkin’s Lymphoma in cases of occupational exposure6. Experiments also showed that glyphosate and its co-formulations used in Roundup and other herbicides are harmful at doses below the toxic level7. Therefore, we conducted our own study to evaluate the effects of glyphosate at various doses on cell viability and find out if there are sources of possible protection from the harm caused by this widely used herbicide.

Materials and Methods

Roundup was used as Compare-N-Save Concentrate Grass and Weed Killer, 41-Percent Glyphosate, manufactured by Ragan & Massey.

Nutritional    supplements    tested    were    composed of vitamins, minerals and plant components and manufactured by different suppliers. Their overall composition is characterized in Table 1.

Other reagents as described in Methods.

Table 1: Characterization of tested nutritional supplements

Reagent preparation and Assays. All nutritional supplements were treated identically in accordance with the protocol recommended by the Unites States Pharmacopeia8. Three recommended daily doses of each supplement were powdered (tablets were crushed using ceramic pestle and mortar, capsules were cut open and powder poured out), placed into a glass container with 900 ml of 0.1N hydrochloric acid and incubated for 1 hour at 37°C in a shaking incubator set with rotation speed of 75 rpm.

Resulting solutions were filter-sterilized using 0.2 micrometer pore size filters, aliquoted and kept frozen at -20°C until analyses. Amounts of samples taken for analysis are expressed as number of millionth parts of recommended daily dose of the respective supplement.

Cell viability assay. The assay was performed using the CellTiter 96® AQueous One Solution Cell Proliferation Assay (MTS) supplied by Promega, Madison, WI, USA. This is a colorimetric assay for assessing cell metabolic activity. NAD(P)H-dependent cellular oxidoreductase enzymes in viable cells reduce the tetrazolium dye MTT 3-(4,5-dimethylthiazol-2-yl)-2,5-diphenyltetrazolium bromide) to formazan. The concentration of formazan produced is measured by optical density at 490 nm and it is directly proportional to the number of live cells in culture.

Protein Biomass Assay- Sulforhodamine B based. After appropriate treatments, dead cells were washed away. Cell proteins were fixed, and stained with Sulforhodamine B dye. The incorporated dye was then liberated from the cells by a Tris base solution and quantified by optical density at 565 nm. An increase or decrease in the number of cells (total biomass) defines the amount of dye incorporated by the living cells in the culture as the dead cells are washed away. The optical density therefore determines total protein biomass.

Treatment of Human Dermal Fibroblasts. Normal Human Dermal Fibroblasts (NHDF) were obtained from ATCC (American Type Culture Collection, Rockville, MD, USA) and maintained in Dulbecco’s  Modified Eagle’s Medium (DMEM) supplemented with 10% Fetal Bovine Serum (FBS), 100 U/ml penicillin and 100 U/ml streptomycin. In the experiments, the cells were grown to confluency in a 48 well plate.

NHDF’s Cells were treated with various supplements for 24 hours, all at 0.5 millionth part daily dose in DMEM supplemented with 5% FBS, except for the “No additions” and “No protection” controls which only received fresh media supplemented with 10% FBS.

After 24 hours, the media was aspirated away, and cells were exposed to various concentrations of glyphosate in a fresh solution containing respective supplements at 0.5 millionth part daily dose in DMEM supplemented with 5% FBS for 24 hours. The “No additions” wells were incubated with fresh DMEM supplemented with 5% FBS and the “No protection” wells were treated with various concentrations of glyphosate in media without supplements.

After 24 hours all treatments were aspirated away, cells were washed 3 times with PBS and cell viability assay was performed or their pictures taken after staining with Hematoxylin and Eosin.

Treatment of Human Kidney Cells. Human Kidney Cells (HEK-293) were obtained from ATCC (American Type Culture Collection, Rockville, MD, USA) Catalog No. CRL-1573 and maintained in DMEM and supplemented with 10% FBS, 100 U/ml penicillin and 100 U/ml streptomycin. Cells were grown to 50% confluency in a 96 well plate.

Glyphosate mixed with each tested nutrient mixture was added to the cells in DMEM supplemented with 5% FBS and incubated for 24 hours. After 24 hours, treatments were removed and cells were incubated in fresh DMEM supplemented with 10% FBS for 48 hours for a recovery phase. After 48 hours of recovery period, protein biomass assay was performed as described.

The toxicity of a generic, easily available glyphosate concentrate solution was tested at a range of concentrations from 0.025 to 0.05% against human dermal fibroblasts (derived from the lower skin layers) and human kidney cells.

Figure 1 shows the effects of different concentrations of glyphosate on survival of the kidney cells evaluated by changes in the total protein mass of the cells in the culture. This test allows for estimating how many cells are left alive and can recover after their exposure to glyphosate. The results show that one day exposure to as low as 0.035% Glyphosate brings down cell biomass to a baseline level.

Figure 1: Changes in total protein biomass of human kidney cells exposed to different concentrations of Glyphosate

Figure 2 presents the effects of glyphosate applied individually and together with various nutritional supplements on the survival of kidney cells.  The results indicate that among six different commercially available nutritional supplements tested in the study (presented as different colored lines A-F), only one –Supplement A – shows some protective effect against glyphosate but at its lower than 0.035% concentrations. The Supplement “A” was formulated based on nutrient synergy principle.

Figure 2: Changes in total protein biomass of human kidney cells exposed to Glyphosate in the presence and absence of different multinutrient formulas (A through E) for 1 day

In addition, we analyzed the effect of glyphosate on viability of human dermal fibroblasts by applying MTT assay. The MTT reagent is metabolized in live cells into a purple colored Formazan compound whose intensity can be quantified by optical density. It provides an estimate of the number of cells left alive after treatment. The results show (Figure 3) that about 90% human dermal fibroblast cells are killed after exposure to 0.035% Glyphosate and 100% when exposed to its 0.04% concentrations.

Changes in morphology of normal human dermal fibroblasts after exposure to Glyphosate alone and together with select nutritional supplements are presented in Figure 4. The pictures show dramatic changes in cell appearance in the presence of 0.035% Glyphosate compared to control which confirms their severe damage. As an example, Supplement D, added to cells together with Glyphosate (0.035%), showed a lack of efficacy in protecting healthy cell morphology, however cells incubated in the presence of Supplement A show visible protection against Glyphosate- induced damage.

Figure 3: Changes in cell viability of normal human dermal fibroblasts after 1 day of exposure to Glyphosate (MTT assay)

Figure 4: Photos of normal human fibroblast cells (40x magnification) exposed to either Glyphosate alone or Glyphosate combined with nutritional supplement A and D, respectively for 1 day

Conclusion

Our study corroborates the findings of other researchers who have alerted that despite warnings to not become hysterical (9), the concerns of glyphosate must not be overlooked.

Our tests were conducted with human skin fibroblasts to mimic a direct exposure to this herbicide through skin contact and with kidney cells, since Round-up has been indicated with increased risk of kidney damage in workers exposed to it due to its strong metal chelating properties (10).

In selecting the glyphosate dose ranges for the study we considered the recommendations of the manufacturer and regulatory restrictions. As such, for field applications it is recommended that the 41% commercial solution is diluted to 0.57% for spot treatments and 0.8% to treat large areas. According to the EPA (Environmental Protection Agency) the livestock feed is allowed to have up to 400 PPM of glyphosate residues which is thousands of times higher than has been shown to cause harm in numerous studies. Our initial experiments (not shown) indicated that the cellular toxicity at these concentrations was so strong that there was no possibility left for the cells to recover if exposed to a potential protective agent. Therefore, we applied markedly diluted glyphosate solutions that allowed for testing cell recovery after their exposure to this toxic agent.

To account for the fact that we were adding this herbicide directly to cultured cells, we used only a day long exposure of glyphosate at nearly 20 times lower concentrations that are recommended for spraying but it still caused the death of both the cell types tested.

The results confirm extreme cellular toxicity of glyphosate and that specific micronutrients applied in proper combinations and dosages can provide some protective effects against this toxin. All commercially available multinutrient formulations tested in this study did not show any significant cell protection against glyphosate, except for Supplement A which showed positive effects in protecting cell morphology. This supplement contained plant extracts (green tea and quercetin) that are potent antioxidants and display pleiotropic metabolic effects in the cell. The study did not test the possible mechanisms of this protective effect.

The fact that glyphosate is used widely and is available cheaply must prompt the scientific community, the general public and regulatory authorities to take proper steps in protecting public and animal health against this extremely toxic agent.

Acknowledgments

The authors appreciate the assistance of Dr. Svetlana Ivanova in preparing supplement solutions tested in the study and valuable discussions.

References

  1. http://worldwide.espacenet.com/publicationDe-tails/originalDocument?CC=US&NR=3799758A&KC=A&FT=D&ND=1&date=19740326&DB=&locale=en_EP
  2. Steinmann HH, Dickeduisberg M, Theuvsen L. Uses and benefits of glyphosate in German arable farming, Crop Protection. 2012; 42: 164-169
  3. http://www.isaaa.org/resources/publications/briefs/43/executivesummary/
  4. Mink PJ, Mandel JS, Lundin JI, Sceurman BK. Epi- demiologic studies of glyphosate and non-cancer health outcomes: A review. Regul Toxicol Pharma- col. 2011; 61(2): 172-184.
  5. Mink PJ, Mandel JK, Sceurman BK, Lundin JI. Epidemiologic studies of glyphosate and cancer: A review. Regul Toxicol Pharmacol. 2012; 63(3): 440-452.
  6. Schinasi L, Leon ME. Non-Hodgkin lymphoma and occupational exposure to agricultural pesticide chemical groups and active ingredients: a syste- matic review and meta-analysis. Int J Environ Res Public Health. 2014;11(4): 4449-527.
  7. Defarge N, Takács E, Lozano VL, et al. Co-Formulants in Glyphosate-Based Herbicides Disrupt Aromatase Activity in Human Cells Below Toxic Levels. Int J Environ Res Public Health. 2016; 13(3).
  8. Disintegration and Dissolution of Dietary Supple- ments . The United States Pharmacopeial Convention. 2010 March 1
  9. Faria MA. Glyphosate, neurological diseases – and the scientific method. Surg Neurol Int. 2015; 6: 132.
  10. Jayasumana C, Gunatilake S, Senanayake P. Gly- phosate, Hard Water and Nephrotoxic Metals: Are They the Culprits Behind the Epidemic of Chronic Kidney Disease of Unknown Etiology in Sri Lanka? Int J Environ Res Public Health. 2014; 11(2): 2125-2147.

Table 1: Characterization of tested nutritional supplements

Figure 1: Changes in total protein biomass of human kidney cells exposed to different concentrations of Glyphosate

Figure 2: Changes in total protein biomass of human kidney cells exposed to Glyphosate in the presence and absence of different multinutrient formulas (A through E) for 1 day

Figure 3: Changes in cell viability of normal human dermal fibroblasts after 1 day of exposure to Glyphosate (MTT assay)

Figure 4: Photos of normal human fibroblast cells (40x magnification) exposed to either Glyphosate alone or Glyphosate combined with nutritional supplement A and D, respectively for 1 day

  1. http://worldwide.espacenet.com/publicationDe-tails/originalDocument?CC=US&NR=3799758A&KC=A&FT=D&ND=1&date=19740326&DB=&locale=en_EP
  2. Steinmann HH, Dickeduisberg M, Theuvsen L. Uses and benefits of glyphosate in German arable farming, Crop Protection. 2012; 42: 164-169
  3. http://www.isaaa.org/resources/publications/briefs/43/executivesummary/
  4. Mink PJ, Mandel JS, Lundin JI, Sceurman BK. Epi- demiologic studies of glyphosate and non-cancer health outcomes: A review. Regul Toxicol Pharma- col. 2011; 61(2): 172-184.
  5. Mink PJ, Mandel JK, Sceurman BK, Lundin JI. Epidemiologic studies of glyphosate and cancer: A review. Regul Toxicol Pharmacol. 2012; 63(3): 440-452.
  6. Schinasi L, Leon ME. Non-Hodgkin lymphoma and occupational exposure to agricultural pesticide chemical groups and active ingredients: a syste- matic review and meta-analysis. Int J Environ Res Public Health. 2014;11(4): 4449-527.
  7. Defarge N, Takács E, Lozano VL, et al. Co-Formulants in Glyphosate-Based Herbicides Disrupt Aromatase Activity in Human Cells Below Toxic Levels. Int J Environ Res Public Health. 2016; 13(3).
  8. Disintegration and Dissolution of Dietary Supple- ments . The United States Pharmacopeial Convention. 2010 March 1
  9. Faria MA. Glyphosate, neurological diseases – and the scientific method. Surg Neurol Int. 2015; 6: 132.
  10. Jayasumana C, Gunatilake S, Senanayake P. Gly- phosate, Hard Water and Nephrotoxic Metals: Are They the Culprits Behind the Epidemic of Chronic Kidney Disease of Unknown Etiology in Sri Lanka? Int J Environ Res Public Health. 2014; 11(2): 2125-2147.