This website was created for Biology 361: Genetically Modified Organisms at Davidson College.by Mike Chase and Monica Siegenthaler

The Possible Assuage of Parkinson’s Disease Risk, due to Pesticide Exposure, with Genetic Modification of Crops

Monica Siegenthaler

Bio 361, Davidson College

Attempts at controlling pests have been made for hundreds of years.  Farmers have, in the past, made use

of the natural processes of genetic selection to provide some resistant to weeds.  The chemical use of

toxins in preventing the proliferation of pests was first documented 200 years ago.  It was not until 1945

and 1946, however, that the first commercial selective broadleaf weed herbicides, 2.4-D and MCPA,

respectively, came onto the market.  Since then, the industry has experienced continual growth, having a

market value of $31 billion in 1998 (Cobb and Kirkwood, 2002).



Herbicides are the most widely used class of pesticides in the world accounting for 44% of all sales in

1988.   More than 90% of the total mass of pesticides applied each year in the U.S. is herbicides (Cobb and

Kirkwood, 2002).  It is estimated that without herbicide use, agricultural yield would drop by 30 to 50%

(Palmiera, 1999).  Even with the use of herbicides, weeds currently cause more than an estimated $40

billion in annual global agricultural losses (Cobb and Kirkwood, 2002).



Unfortunately, pesticides are known to cause detrimental effects on the environment and animal health. 

Pesticides can easily contaminate the soil, air, and water.  Detection of pesticide residues has even been

found in drinking water.  The US Geological Survey, for example, detected the herbicide atrazine in each

of 146 water samples collected at 8 locations throughout the Mississippi drainage basin.  Over 74% of the

samples also contained alachlor, metachlor, or cyanazine.  Atrazine concentration exceeded the EPA

maximum contaminant level for several weeks in rivers as large as the Missouri and Mississippi.  The

central US rivers supply drinking water to 18 million people and many herbicides are not removed from

drinking water by conventional filtration and treatment (Liebman et al, 1993). 



The presence of pesticides in the environment result in adverse health effects.  One debated effect is the

link between herbicides and cancer.  Some research shows significant results for a link, while others

discard the idea. Schreinemachers (2000), for example, demonstrated an increase in cancer mortality in

four northern wheat-producing states.  The study compared rare cancer cases in different counties that are

above and below the median of wheat acreage per county.  The findings verified increased mortality for

cancer of the nose and eye in men and women, brain and leukemia for boys and girls, and all cancers in

boys (Schreinemachers, 2000).  Another study, conducted in North Carolina, suggests that children

under14 have four times the normal risk of contracting cancer, namely soft tissue sarcoma, if their gardens

are treated with pesticides of herbicides (“Garden”, 1995).  Other studies linking herbicides to child

cancer include one in which agent orange causes a form of leukemia in Vietnam veteran’s children (“Agent

Orange Linked”, 2001).  Moreover, three Swedish case-control studies suggest that exposure to 2,4,5-T

and 2,4-D and similar compounds results in a six-fold increase in risk for soft tissue sarcoma.  Similar

survey conducted in New Zealand, however, found these associations weak (Coggon, 1987).



 Aside from cancer, pesticides have also been associated with the disruption of biological pathways, such

as the production of ATP.  For instance, three herbicides, paraquat, dinoseb, and 2,4-D, have been shown

to affect mitochondrial bioenergetics.  Each herbicide causes the effects by different mechanisms.  Their

effects lead to the disruption of cellular energetic and metabolism (Palmeira, 1999).  Interestingly, one

neurological disease in which neuronal mitochondria are unable to produce ATP has an unknown etiology,

but has recently been studied in the light of the industrial chemicals that have contaminated the

environment. 


Parkinson’s disease (PD) is characterized by tremor, rigidity, shuffling gait, decreased muscular activity

(hypokinesia), slowness of movement (bradykinesia), and difficulty initiating voluntary movement

(Veldman et al, 1998; King, 2002).  Such characteristics are a result of significant loss of substantia nigra

dopamine neurons.  For comparison, there is a 4.7-6.0% loss of nigral cell loss as one ages from their 5th

decade to their 9th decade of life, but such loss does not cause parkinsonian features (Veldman et al,

1998).  In order for the symptoms of Parkinson’s disease to appear, there must be an 80% loss of the nigral

dopamine neurons (King, 2002). 


The cause of such substantial loss is unknown.  Research has shown, however, that relatives of PD

patients are two to five times more likely to have PD than the relatives of controls, suggesting the role of

inheritance.  Some research has found that certain genes, such as the dopamine receptor gene D2, may be

genetic determinants of PD.  There are, however, certain environmental trends, that undermine a solely

genetic cause in the manifestation of PD (Veldman et al, 1998).



 
Parkinson’s disease tends to be more prevalent in industrialized countries than in underdeveloped

countries.  The frequency of PD, for example, in China (57 per 100,000) is less than in the US (347 per

100,000).  Further, there is a difference between the occurrences of PD in genetically homogenous

populations living in different locations.  Parkinson’s disease, for instance, is much lower in Nigeria that it

is among the Afro- American population in the US.  The prevalence of PD among Afro-Americans in the

US, in fact, is about the same as that for white people in the US.  The incidence of PD in Japanese or

people of Okinawan ancestry living in the US is similar as well to that of the white people in the US, but is

much higher than the incidence among Asians living in an Asian country (Veldman et al, 1998).

Another trend, as described in by Rajput in 1984 is the relation between PD and rural living, which in this

case is an industrialized for of rural living.  Rural living, for example in industrialized countries makes use

of many industrial products, such as tractors and pesticides, whereas rural living in underdeveloped

countries makes use of oxen and tilling instead.  Rajput’s initial findings that rural living significantly

increases the risk of PD has since been supported by several studies (Tanner et al, 1987; Rajput et al,

1987; Ho et al, 1989; Tanner et al, 1990; Won et al, 1991; Stern et al, 1991; Vieregge et al, 1992;

Butterfield et al, 1993; Svenson et al, 1993; De Michele et al, 1996; Liou et al, 1997).  Although there are

studies that did not find this relationship, they are few in comparison to those that do support rural living

as a risk factor of PD (Veldman et al, 1998). 

The relation between farming and PD may be explained by studies, such as that of Semchuck et al (1992),

in which occupational herbicide use was a significant predictor of PD risk.  This association was made by

interviewing 130 Calgary residents with neurologist confirmed PD and 260 randomly selected age- and

sex-matched community controls (Semchuck et al, 1992).  A similar sort of study, conducted in Detroit,

suggests that PD is linked with occupational exposure to pesticides (Gorell et al, 1998).

MPTP (1-methyl-4-phenyl-1,2,3,6-tetrahydropyridine) is a toxic molecule belonging to the bipyridyl chemical group (Veldman et al, 1998; IPCS Inchem, 2002).  Research has shown that MPTP is converted to MPP+, a highly neurotoxic metabolite, in the brain by monoamine oxidase (MAO).   It has been suggested that MPP+ causes the selective neuronal degeneration by binding to neuromelanin, a pigment molecule of the substantia nigra.  Once bound to the pigment, MPP+ is accidentally taken up by mitochondria, where it inhibits complex I, resulting in mitochondrial respiratory chain dysfunction.  The production of energy is ultimately diminished, leading to calcium release and cell death (Kopin et al, 1987; Velderman et al, 1998; King, 2002).  The resulting cell death often gives rise to parkinsonism, which is a term used to describe “any of a group of nervous disorders similar to Parkinson's disease, marked by muscular rigidity, tremor, and impaired motor control and often having a specific cause, such as the use of certain drugs or frequent exposure to toxic chemicals” (Dictionary.com, 2002).   Therefore, victims of parkinsonism experience the same symptoms as Parkinson’s patients.

 It is believed that pesticides that are structurally similar to MPP+, such as paraquat, may cause the same degenerative effects.  In one study, Liou et al (1997) discovered that Taiwanese farmers using paraquat in conjunction with other pesticides had a 4.74 fold increased risk for PD, whereas the farmers that used pesticides other than paraquat had a 2.17 fold increased risk (Liou et al, 1997). 

Syngenta currently sells paraquat in over one hundred countries.  This non-selective, broad-leaf herbicide

is extensively used on plantations of bananas, cocoa, coffee, cotton, palm oil, pineapple, rubber and sugar

cane (“Time”, 2002; “Paraquat”, 1996).  Paraquat is often applied to destroy weeds in preparing the land

for planting, and to desiccate and defoliate crops in preparation for field burning.  The use of paraquat is

currently restricted in the US so that it can be purchased and used only by certified applicators.  Some

countries, however, such as the UK, do not have any regulatory measures against the use of paraquat

(“Paraquat”, 1996).



Due to the strictly regulated use of paraquat, the high prevalence of PD in the US then cannot be explained

solely by the use of paraquat.  Associations between PD and pesticides in general, however, have been

suggested in several studies (Veldman et al, 1998).  Nelson reported at the 2000 American Academy of

Neurology annual meeting that exposure to home pesticides is linked to increase risk of PD.  Exposure to

herbicides, for example, increased the risk for PD by 30% with a low-level of exposure (less than 30

days total) and 70% with a high-level of exposure (average of 160 days total).  Garden insecticides

increased the risk of PD, and in-home use of insecticides, with an average exposure of 77days, increased

showed a 70% increased risk.  The specific kinds of pesticides used are unknown, however, because

studies relating PD to pesticide exposure often consist of interviews in which the participants are asked

about their past exposure to pesticides in general, rather than exposure to specific pesticides.  Parkinson’s

disease expert William Koller, MD, PhD explains, “the whole concept is tantalizing, but there’s never

been a single agent or even a class of agents that have been identified as a risk factor.”  Nelson and her

colleges, however, hope to re-interview the participants of the original study to determine any trends in the

brands or type of pesticides used (Stevenson, 2000).

If exposure to pesticides really is a risk factor for PD, biotechnology may hold a key to reducing the use of

pesticides, and in turn reducing the overall incidence of PD.  The discovery, isolation, and manipulation of

genes have flourished over the past few decades, leading up to the advent of herbicide-tolerant crops

(Marshall, 1998).  The most common of these transgenic crops are Bt crops and Roundup-ready

crops. Roundup-ready crops contain a transgene, derived from a petunia, that produces large quantities of

the phenylalanine-producing enzyme, EPSP synthase (Kleiner, 1998).  Glyphosate, also known as

Roundup, is a broad-spectrum herbicide that Monsanto introduced in 1974 (Mendelson, 1998).  It works

by inhibiting the production of EPSP synthase, which results in the absence of the amino acid

phenylalanine, leading to plant death (Kliener, 1998; Wade, 1999).  The idea behind the Roundup-ready

crops is that the inserted gene produces an amount of EPSP synthase that is overwhelming for glysophate.

In the past, farmers used caution when spraying Roundup, so as not to spray too much and cause damage to

the crop in addition to the targeted species.  Roundup-ready crops, however, allow the farmer to spray

without worries of killing the crop.  Currently, Roundup-ready soybeans, canola, cotton, and corn exist,

covering over 33 million acres worldwide.  Monsanto plans to add sugar beets, wheat, and potatoes to the

Roundup-ready line (Kliener, 1998).


Bt crops, another line of transgenic plants, contain a gene gun-inserted gene that produces the Bacillus

thuringiensis
(Bt) toxin (Levidow, 1999).  Bt has been used as an insecticide in the US since 1958.  The

toxin is used on fruits, vegetables, and other cash crops including corn, potatoes, and cotton for the

effective control of beetle larvae, moth and butterfly caterpillars, mosquito and blackfly larvae, mites,

flatworms, and nematodes (Swadener, 1994).

The toxin works by being activated within the insect’s digestive system.  The delta- endotoxin, which is

the toxic constituent of the bacterium, binds to specific receptors on the intestinal lining of the insect.  The

binding causes a conformational change in the intestinal membrane, resulting in the formation of pores. 

The pores cause the intrinsic balance of ions to be disrupted, and leads to the cessation of feeding and the

eventual death by starvation (Levidow, 1999).

Thus, the insertion of the Bt gene in plants results in the constituent release of Bt. Therefore, the farmer

does not need to spray in order to control for such pests.  These crops, such as Bt cotton, BT corn, and Bt

potatoes are widely grown in countries such as the United States, Spain, Canada, Argentina, South Africa,

and France (Levidow, 1999).

 

Although there is much debate concerning the adverse effects of such genetically altered crops on the

environment, Monsanto advertises these crops with the claim that they will significantly reduce the volume

of pesticides used, which is an obvious favorable effect on the environment.  GMO opposition has

expressed their thoughts on the pesticide use issue and argues that Roundup-ready crops and Bt crops will

increase the use of pesticides since farmers will not worry about the detrimental effects on the crops. 

Published data, however, shows that pesticide use on Bt cotton in Australia has decreased by 50%, and

insecticides used on Bt corn in the US has decreased by 30% (Levidow, 1999).  In addition, the volume of

herbicides used by US farmers has decreased by 50% since the introduction of Roundup-ready crops

(Barton and Dracup, 2000).

The associations found between exposure to pesticides and increased risk of PD suggests that a decrease

in the use of pesticides, due to the advent and use of Bt crops and Roundup-ready crops, may lessen the

occurrence of PD.  Even if such correlations do not exist, biotechnology can be applied for medicinal

purposes.  Pargyline, a MAO-blocking drug prevents MPTP-induced parkinsonism and inhibits cell death

in substantia nigra (King, 2002).  Insertion of the pargyline gene in plants, such as tobacco, can produce a

medicinal product for the cautionary prevention of Parkinson’s deleterious effects. Smoking the medicinal

tobacco, moreover, would provide further measures in the prevention of the disease.  The risk of PD has

been shown to have an inverse relation with smoking.  A proposed explanation of this association asserts

that cigarette smoke contains MAO inhibitors, and actually reduces the amount of MAO in the brain by

40%.  Furthermore, nicotine has been shown to stimulate the release of dopamine, which is the deficient

chemical in PD patients (Veldman, 1998).

Therefore, genetic modification of plants, whether directed to the improvement of health or not, may

greatly reduce current health risks, such as that of PD.  Although opposition object to the current trends of

genetic modification in biotechnology, the delineated benefits certainly outweigh the postulated minute

adverse effects that genetic modification may have on the environment.

 

Works Cited

----.  (2001).  Agent Orange linked to leukemia, contamination.  Jul 2001.  The Nation’s Health 31(6): 5.

Barton, JE, Dracup, M.  (2000).  Genetically modified crops and the environment.  Agronomy Journal, 92(4): 797-803.

Butterfield, PG, Valanis, BG, Spencer, PS, Lindeman, CA, Nutt, JG.  (1993).  Environmental antecedents of young-onset Parkinson’s disease.  Neurology, 43: 1150-1158.

Cobb, A.H., Kirkwood, R.C.  (2000).  Challenges for herbicide development.  Pages 1-24 in Cobb, A.H., Kirkwood, R.C., editors.  Herbicides and their mechanisms of action.  CRC, Boca Raton, Florida, USA.

Coggon, D.  (1987).  Are pesticides carcinogenic?  21 March 1987.  British Medical Journal 294:725.

De Michele, G, Filla, A, Volpe, G, et al.  (1996).  Environmental and genetic risk factors in Parkinson’s disease:a case-control study in southern Italy.  Movement Disorders, 11: 17-23.

Dicationary.com.  (2002).  Query: parkinsonism.  Accessed 8 Dec 2002.  <http://www. dictionary.com>.

----.  (1995).  Garden pesticides linked to cancer in children.  BioCycle 36(4): 6.

Gorell, JM, Johnson, CC, Rybicki, BA, Peterson, EL, Richardson, RJ.  (1998)  The risk of Parkinson’s disease with exposure to pesticides, farming, well water, and rural living.  Neurology, 50(5): 1346-1350.

Ho, SC, Woo, J, Lee, CM.  (1989).  Epidemiologic study of Parkinson’s disease in Hong Kong.  Neurology, 39: 1314-1318.

IPCS Inchem.  (2002).  Paraquat.  Accessed 2 Dec 2002.  <http://www.inchem.org/ documents/pds/pds/pest4_e.htm>.

King, WB.  (2002).  The case of the frozen addict.  Department of Psychology, Coastal Carolina University.  Accessed 2 Dec 2002.  <http://ww2.coastal.edu/kingw/

psyc415/frozenaddict.html>.

Kleiner, K. (1998). Let us spray. New Scientist 158 (2128): 16.

Kopin, IJ.  (1987).  MPTP: an industrial chemical and contaminant of illicit narcotics stimulates a new era in research on Parkinson’s disease.  Environmental Health Perspective, 75: 45-51.

Levidow, L.  (1999).  Regulating Bt maize in the United States and Europe.  Environment, 41(10): 10-26.

Liebman, M., Dyck, E.  (1993).  Weed management:  a need to develop ecological approaches.  Feb 1993.  Ecological Applications (3)1: 39-41.

Liou, HH, Tsai, MC, Chen, CJ, Jeng, JS, Chang, YC, Chen, SY, Chen, RC.  (1997).  Environmental risk factors and Parkinson’s disease: a case-control study in Taiwan.  Neurology, 48: 1583-1588.

Marshall, G.  (1998).  Herbicide-tolerant crops- real farmer opportunity or potential environmental problem?  Pesticide Science, 52: 394-402.

Mendelson, J. (1998). Roundup: the world’s biggest-selling herbicide. The Ecologist 28(5): 270-275.

Palmiera, CM.  (1999).  Herbicide-induced mitochondria and cellular liver toxicity: a review of paraquat, dinoseb, and 2,4-D effects.  Toxic Substance Mechanisms, 18: 187-204.

---.  (1996).  Paraquat.  Pesticides News, (32): 20-21.

Rajput, AH, Uitti, RJ, Stern, W, et al.  (1987).  Geography, drinking water chemistry, pesticides and herbicides and the etiology of Parkinson’s disease.  Canadian Journal of Neurological Science, 14: 414-418.

Schreinemachers, D.M.  (2000).  Cancer mortality in four northern wheat-producing states.  Sept 2000.  Environmental Health Perspectives 108(9): 837-881.

Semchuck, KM, Love, EJ, Lee, RG.  (1992).  Parkinson’s disease and exposure to agricultural work and pesticide chemicals.  Neurology, 42(7): 1328-1335.

Stephenson, J.  (2000).  Exposure to home pesticides linked to Parkinson’s disease.  JAMA, 283(23): 3055-3056.

Stern, M, Dulaney, E, Gruber, SB, et al.  (1991).  The epidemiology of Parkinson’s disease.  A case-control study of young-onset and old-onset patients.  Archives of Neurology, 48: 903-907.

Svenson, LW, Platt, GH, Woodhead, SE.  ( 1993).Geographic variations in the prevalence rates of Parkinson’s disease in Alberta.  Canadian Journal of Neurological Science, 20: 307-311.

Swadener, C.  (1994).  Bacillus thuringiensis Insecticide Fact Sheet.   Accessed 2 Dec 2002.  <http://www.mindfully.org/GE/Bacillus-thuringiensis-Bt.htm>.

Tanner, CM, Chen, B, Wang, WZ, et al.  (1987).  Environmental factors in the etiology of Parkinson’s disease.  Canadian Journal of Neurological Science, 14: 419-423.

Tanner, CM, Langston, JW.  (1990).  Do environmental toxins cause Parkinson’s disease?  A critical review.  Neurology, 40:17-30.

---.  (2002).  Time to phase out paraquat- Syngenta’s controversial pesticide.  PAN UK.  Accessed 2 Dec 2002.  <http://www.pan-uk.org/press/paraquat.htm>.

Vieregge, P, von Maravic, C, Friedrich, HJ.  (1992).  Life-style and dietary factors early and late in Parkinson’s disease.  Canadian Journal of Neurological Science, 19: 170-173.

Vledman, BAJ, Wijn, A, Knoers, N, Praastra, P, Horstink, MWIM.  (1998).  Genetic and environmental risk factors in Parkinson’s disease.  Clinical Neurology and Neurosurgery, 100: 15-26.

Wade, L.G. (1999). Organic Chemistry, 4th edition.

Wong, GF, Gray, CS, Hassanaein, RE, Koller, WC.  (1993).  Environmental risk factors in siblings with Parkinson’s disease.  Archives of Neurology, 48:287-289.

 

 

 

 

© Copyright 2002 Department of Biology, Davidson College, Davidson, NC 28035
Send comments, questions, and suggestions to: michase@davidson.edu or mosiegenthaler@davidson.edu