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Trichloroethylene: An Invisible Cause of Parkinson’s Disease?

68 minutes


The etiologies of Parkinson’s disease (PD) remain unclear. Some, such as certain genetic mutations and head trauma, are widely known or easily identified. However, these causes or risk factors do not account for the majority of cases. Other, less visible factors must be at play. Among these is a widely used industrial solvent and common environmental contaminant little recognized for its likely role in PD: trichloroethylene (TCE). TCE is a simple, six-atom molecule that can decaffeinate coffee, degrease metal parts, and dry clean clothes. The colorless chemical was first linked to parkinsonism in 1969. Since then, four case studies involving eight individuals have linked occupational exposure to TCE to PD. In addition, a small epidemiological study found that occupational or hobby exposure to the solvent was associated with a 500% increased risk of developing PD. In multiple animal studies, the chemical reproduces the pathological features of PD.

Exposure is not confined to those who work with the chemical. TCE pollutes outdoor air, taints groundwater, and contaminates indoor air. The molecule, like radon, evaporates from underlying soil and groundwater and enters homes, workplaces, or schools, often undetected. Despite widespread contamination and increasing industrial, commercial, and military use, clinical investigations of TCE and PD have been limited. Here, through a literature review and seven illustrative cases, we postulate that this ubiquitous chemical is contributing to the global rise of PD and that TCE is one of its invisible and highly preventable causes. Further research is now necessary to examine this hypothesis.


The number of people with Parkinson’s disease (PD) has more than doubled in the past 30 years [1] and, absent change, will double again by 2040 [2]. Numerous genetic causes or risk factors for the disease have been identified, but the vast majority of individuals with PD do not carry any of these mutations [3, 4]. Several environmental toxicants, especially certain pesticides [5], have also been linked to PD, and head trauma is also associated with an increased risk [6]. However, these are insufficient to explain the widespread prevalence of PD. Given the disease’s growing rates— more than can be explained by aging alone [1]— other less visible causes must be contributing to its rise. One of these may be trichloroethylene (TCE), a ubiquitous chemical that has contaminated countless sites and poses health risks to those who are (often unknowingly) exposed via their work or their environment.

The evidence linking TCE to PD to date is based on a handful of case studies [7–12], a small epidemiological study linking exposure to a 500% increased risk of PD [11], and numerous animal studies demonstrating that the chemical leads to the pathological hallmarks of PD [8, 9, 13–17]. Here we introduce the chemical, describe its association to PD and other diseases, detail its widespread use and routes of contamination, and provide circumstantial evidence for its broader role in PD through illustrative cases depicting individuals with the disease who were likely exposed to TCE through their environment or occupation. We conclude with a call for greater research on its effects on PD, protection from and remediation of contaminated sites, and banning of this century-old chemical that has caused immeasurable harm to the public’s health.


TCE is a simple six-atom (two carbons, one hydrogen, and three chlorines) solvent that is clear, colorless, volatile, nonflammable, and environmentally persistent (Fig. 1a) [18]. It was first synthesized in the lab in 1864 (Fig. 1b), and commercial production began in the 1920s [19]. Because of its unique properties, TCE has had countless industrial, commercial, military, and medical applications. Among these are producing other chlorinated compounds (e.g., refrigerants), cleaning electronics, and degreasing engine parts for civilian and military purposes [18]. As it readily evaporates and does not shrink fabrics, TCE was used to dry clean clothes beginning in the 1930s. A closely related chemical called perchloroethylene (PCE), which has one additional chlorine atom in place of the hydrogen atom, largely supplanted TCE in dry cleaning in the 1950s. In anaerobic conditions, PCE often transforms into TCE, and their toxicity may be similar [20].

Fig. 1a

Trichloroethylene (TCE) chemical structure [84].

Trichloroethylene (TCE) chemical structure [84].

Fig. 1b

The history of trichloroethylene (TCE) [15, 85]. EPA, Environmental Protection Agency; FDA, Food and Drug Administration.

The history of trichloroethylene (TCE) [15, 85]. EPA, Environmental Protection Agency; FDA, Food and Drug Administration.

TCE is found in numerous consumer products (Table 1), including typewriter correction fluid, paint removers, and carpet cleaners [18]. Until the 1970s, it was used to decaffeinate coffee [18]. The volatile TCE was also an inhaled anesthetic until the U.S. Food and Drug Administration banned it in 1977 [19].

Table 1

Historical usage of trichloroethylene [19, 72, 73, 85–88]

Commercial &Consumer Products
  Aerosol cleaning products*
  Carpet cleaner*
  Cleaners and solvent degreasers*
  Cleaning wipes*
  Cosmetic glues
  Decaffeinated coffee
  Film cleaners
  Gun cleaner
  Hoof polishes
  Mold release
  Paint and paint removers*
  Pepper spray
  Stain removers*
  Tap and die fluid
  Toner aid
  Tool cleaners
  Typewriter correction fluids*
  Wood finishes*
Industry Usage
  Automotive care
  Dry cleaning*
  Furniture care
 Computer and electronics
 Fat and oil extraction
 Flavor extracts (spices, hops)
 Paint and coating*
  Anesthesia (medical, dental, veterinary)
  Surgical disinfectant
  Treatment (migraines, trigeminal neuralgia)
  Pharmaceutical manufacturing

*Common current uses.


Studies (Table 2) linking TCE exposure to PD and parkinsonism date back to at least 1969 when Huber reported parkinsonism in a 59-year-old man who worked with TCE for over 30 years [7]. Thirty years later, Guehl and colleagues documented PD in a 37-year-old woman who was exposed to the chemical while cleaning houses and again while working in the plastics industry [8]. In 2008, Gash and colleagues reported that among 30 factory workers, three developed PD after using TCE for many years to degrease and clean metal parts [9]. These three workers were stationed closest to an open TCE vat, and 14 of 27 workers who were further from the source “displayed many features of parkinsonism, including significant motor slowing” [9].

Table 2

Clinical studies linking trichloroethylene and parkinsonism or Parkinson’s disease [7–12]

AuthorsYearRefStudy DesignNFindings
Huber1969[7]Case study1A 59-year-old that worked with TCE for 33 years developed parkinsonism. The patient’s brain section showed depigmentation and severe degenerative changes in the substantia nigra.
Guehl et al.1999[8]Case study1A former house cleaner was exposed to TCE for several months, beginning at age 27, in poorly ventilated rooms. She then worked for six years in the plastics industry in a very small, unventilated office exposed to TCE and other volatile compounds. Three years later, she was diagnosed with PD at the age of 37.
Kochen et al.2003[12]Case series3Three workers chronically exposed to TCE developed PD in the post-exposure period.
Gash et al.2008[9]Case series3Three industrial plant workers (ages 49, 76, 56) developed PD after years of dermal and respiratory exposure (exposure duration 25 years, 25 years, 29 years) from cleaning metal gauges in a large, open vat of TCE. An additional 14 coworkers in this cluster that experienced chronic respiratory exposure to TCE exhibited parkinsonism features.
Goldman et al.2012[11]Case-control study in twin pairs discordant for PDBoth occupational and hobby exposure to PCE and TCE among a cohort of twins was studied. TCE was associated with a significantly increased risk of PD (OR 6.1, 95% CI 1.2 – 33; p = 0.034) along with PCE exposure suggestive of an increased risk (OR 10.5, 95% CI 0.97 – 133; p = 0.053).
Reis et al.2016[10]Case study1A former car repairman who worked with products containing TCE for over 40 years was diagnosed with PD at the age of 57.

PD, Parkinson’s disease; TCE, trichloroethylene.

Four years later, researchers found that in twin pairs, the twin with occupational or hobby exposure to TCE had a 500% increased risk of PD (OR 6.1, 95% CI: 1.2–33; p = 0.034) compared to their unexposed twin [11]. Exposure to the closely related solvent PCE also trended toward significance with an odds ratio of 10.5 (95% CI: 0.97–113) [11]. Notably, the researchers found an interval of 10 to 40 years from the time of TCE exposure to PD diagnosis [11].

TCE and PCE likely mediate their toxicity through a common metabolite [21, 22]. Because they are lipophilic [11], both TCE and PCE readily distribute in the brain and body tissues and appear to cause mitochondrial dysfunction at high doses. This may partially explain the link to PD as dopaminergic neurons are sensitive to mitochondrial neurotoxicants such as MPTP/MPP+, paraquat, and rotenone [23]. Indeed, in animal studies (Table 3), TCE treatment caused selective loss of dopaminergic neurons [8, 9, 13, 15, 16]. In addition, PD-related neuropathology, such as neuroinflammation and α-synuclein phosphorylation and accumulation, was observed in the substantia nigra of rats and mice exposed to 200–1000 mg/kg TCE over chronic time periods (6 weeks to 8 months) [13, 15, 17]. While the specific metabolite or mechanism of TCE-induced neurodegeneration remains unclear, pre-clinical studies with high doses (400–1000 mg/kg) showed that mitochondrial complex I activity is dysregulated in the midbrain of rodents exposed to TCE [9, 13–15]. Mitochondrial function was further reduced in the rat striatum when TCE exposure occurred in conjunction with another PD risk factor, traumatic brain injury. The combined neurotoxic insults resulted in 50% reduction in complex I oxygen consumption [14], a more severe effect than each factor alone. This combined effect provides a key example of how TCE exposure may influence PD risk in certain populations, such as individuals who served in the military where head trauma is morecommon [24].

Table 3

Animal studies involving trichloroethylene and Parkinson’s disease [8, 9, 13–17]

Guehl et al.1999[8]OF1 mice400 mg/kg TCE, 5 days/week for 4 weeksDopaminergic neurodegeneration in the substantia nigra
Gash et al.2008[9]Fisher 344 rats1000 mg/kg TCE, 5 days/week for 6 weeksMitochondrial complex I activity inhibition in substantia nigra, increased complex I activity in striatum, dopaminergic neurodegeneration in nigrostriatal tract
Liu et al.2010[13]Fisher 344 rats200, 500 or 1000 mg/kg TCE, 5 days/week for 6 weeksDose-dependent loss of dopaminergic neurodegeneration in the substantia nigra, motor deficits in 1000 mg/kg TCE-treated rats, mitochondrial complex I inhibition in substantia nigra, elevated oxidative stress markers, activated microglia, and intracellular alpha-synuclein accumulation in dorsal motor nucleus of vagus nerve
Sauerbeck et al.2012[14]Fisher 344 rats1000 mg/kg TCE, daily for 1 or 2 weeks with and without traumatic brain injuryMitochondrial impairment in striatum, with rates of complex I dependent oxygen consumption decreasing by 75%, after two week exposure to TCE and traumatic brain injury. Analysis of one week of TCE exposure and traumatic brain injury indicated a 50% decrease in mitochondrial function. Motor impairment and dopaminergic neurodegeneration in the substantia nigra
Liu et al.2018[15]Male C57BL/6 mice and postnatal day 1–3 Sprague-Dawley rat pups400 mg/kg/day TCE, 5 days a week for 8 monthsProgressive dopaminergic neurodegeneration, decreased dopamine and metabolites, deficits in locomotor activity, mitochondrial complex I inhibition, increased accumulation of phosphorylated a-synuclein, and endogenous formation of toxic metabolite (TaClo)
Keane et al.2019[16]A30P and wild type mice1000 mg/kg TCE, twice weekly for 8 weeksDopaminergic neurodegeneration in the substantia nigra
De Miranda et al.2021[17]Aged, male and female Lewis rats200 mg/kg TCE, daily for 3 or 6 weeksTCE activated LRRK2 kinase activity prior to dopaminergic neurodegeneration in the nigrostriatal tract. Elevated oxidative stress, neuroinflammation, endolysosomal dysfunction and alpha-synuclein accumulation

TCE, trichloroethylene.

In addition to combined environmental factors, evidence from preclinical studies suggests that genetic risk factors may also play a role in TCE-induced neurodegeneration. For example, in a 2021 study, chronic, systemic exposure to 200 mg/kg TCE elevated the kinase activity of LRRK2 (leucine rich repeat kinase 2) in the striatum and substantia nigra of rats after 3 weeks, prior to the loss of dopaminergic neurons at 6 weeks [17]. Inherited variants of LRRK2 are linked to both familial and sporadic PD, the most common of which is the G2019S mutation, that pathogenically elevate LRRK2 kinase activity resulting in dysregulated vesicular trafficking, endolysosomal dysfunction, and oxidative stress [25]. However, despite cellular dysfunction caused by elevated LRRK2 kinase activity, individuals who inherit the LRRK2 G2019S mutation have only a roughly 50% increased risk for PD [26]. Incomplete penetrance of genetic risk factors suggests that possible gene-environment interactions could explain why only some individuals exposed to TCE develop PD and why those with a PD-related genetic predisposition may display variable risk of developing PD. Many other genetic causes of PD (e.g., Parkin, PINK1) also affect mitochondrial function, and an interaction with TCE is conceivable for carriers of mutations in these genes [27]. However, more data on gene-environment interaction between TCE, LRRK2, and other genetic risk factors associated with PD are needed.


TCE was “ubiquitous” in the 1970s [28] when annual U.S. production surpassed 600 million pounds per year, or over two pounds per person [29]. About 10 million Americans worked with the chemical or other organic solvents daily; in the U.K. an estimated 8% of workers have (Table 4) [10]. While domestic use has waned, the U.S. is still the top global exporter of TCE, and since 1990, occupational exposure to TCE has increased by 30% worldwide [30]. Exposure is widespread, and a 1994 study in Italy found TCE at relatively high concentrations in the blood and urine of three quarters of a sample of the general population [31].

Table 4

Example occupations where trichloroethylene exposure may occur [85, 86, 90]

Aircraft maintenance workers
Automotive factory workers
Communications equipment repairers
Computer specialists
Corrosive control technicians
Distillery workers
Dry cleaners
Electronic component manufacturers
Food manufacturers
Insecticide manufacturers
Jet engine mechanics
Leather manufacturers
Machinery installation &assembly workers
Metal treatment workers
Missile technicians
Nautical equipment workers
Oil processors
Pesticide manufacturers
Pharmaceutical manufacturing factory workers
Radar technicians
Refrigerant manufacturers
Resin workers
Rubber cementers
Sewerage workers
Silk screeners
Shoe makers
Systems technicians
Textile manufacturers
Textile and fabric cleaners
Tobacco denicotinizers
Waste treatment workers
Weapons specialists
Varnish workers

Although the European Union and two U.S. states have banned TCE, it is still permitted for vapor degreasing and spot dry cleaning in the U.S. and for authorized industrial uses in the E.U. [32]. Globally, TCE consumption is projected to increase by 3% annually (Fig. 2a) [33], and China, which has the fastest growing rates of PD [1], now accounts for half the global market [34].

Fig. 2a

Top ten exporters and importers of trichloroethylene, 2020 [33].

Top ten exporters and importers of trichloroethylene, 2020 [33].

Fig. 2b

Countries with published studies of sites of groundwater TCE contamination [89].

Countries with published studies of sites of groundwater TCE contamination [89].

Workers can inhale or come in dermal contact with TCE, but millions more encounter the chemical unknowingly through outdoor air, contaminated groundwater, and indoor air pollution. In 1987, nearly 56 million pounds of TCE were released into the air in the U.S. alone (Fig. 3) [35]. TCE can also leak from storage tanks or be dumped into the ground where it contaminates up to one-third of the drinking water in the U.S. [36]. TCE has also polluted the groundwater in at least twenty different countries on five continents (Fig. 2b).

Fig. 3a

U.S. cities that released the most TCE into the air, 1987 [35].

U.S. cities that released the most TCE into the air, 1987 [35].

Fig. 3b

U.S. cities that released the most TCE into the air, 2020 [35].

U.S. cities that released the most TCE into the air, 2020 [35].

TCE contaminates countless industrial, commercial, and military sites. TCE is found in half of the 1300 most toxic “Superfund” sites that are part of a federal clean-up program, including 15 in California’s Silicon Valley where TCE was used to clean electronics [37]. The U.S. military has stopped using TCE, but numerous sites have been contaminated, including the Marine Corps base Camp Lejeune in North Carolina. For 35 years, the base— which housed a million Marines, their families, and civilians— had levels of TCE and PCE in the drinking water 280 times safety standards [38].

Beginning in 1978, another route of exposure to TCE and other volatile chemicals was recognized: vapor intrusion (Fig. 4). Researchers found that TCE, much like radon, could evaporate from contaminated soil and groundwater and enter homes, schools, and workplaces [39]. Buildings often have lower air pressure than the outdoor environment and can draw toxic fumes through cracks in the foundation, utility lines, duct work, and elevators [40, 41]. This polluted air can travel upwards to apartments and offices located above plumes, which function as underground rivers of pollutant within the groundwater. TCE has been found in the indoor air of homes, in the butter in their refrigerators (TCE and PCE are fat soluble), and in the breast milk of nursing mothers [42].

Fig. 4

Possible modes of exposure to trichloroethylene in the environment.

Possible modes of exposure to trichloroethylene in the environment.

Since contaminated underground plumes can travel over a mile, individuals who live far from a contaminated site are still at risk. One plume on Long Island, New York, which was associated with an aerospace company, is over four miles long and two miles wide and has contaminated the drinking water of thousands [43]. In Shanghai, China, a village, primary schools, and homes sit atop a TCE-contaminated site where a chemical plant operated for over thirty years [44]. In Newport Beach, California, multi-million dollar homes were built above a former aerospace facility known to be contaminated with TCE and PCE [45, 46]. In Monroe County, New York, where many of the authors of this report live, over a dozen dry cleaners have contaminated the ground with TCE.


Below are seven cases where TCE may have contributed to an individual’s PD. The evidence linking possible exposure to TCE in these cases is circumstantial but raises worrisome questions about the link between the chemical and the disease. The first three cases depict likely environmental exposure contributing to PD. The latter four highlight potential risks from occupational exposure. In some cases, identifying information was changed to protect privacy.

Likely environmental exposure to TCE

Case 1

On May 12, 2006, Mr. Brian Grant played two minutes for the Phoenix Suns in a National Basketball Association (NBA) playoff game. He did not score a point, grab a rebound, or have an assist. However, in the last game of his NBA career, the then 34-year-old power forward made history— he had likely just played an entire basketball season with PD.

Mr. Grant first noticed the symptoms of the disease a season earlier while on the Los Angeles Lakers. There the 6’9”, 250-pound player was puzzled to discover he could no longer jump off of his left leg as he once could. Sometimes the leg would give out. The next season, he developed an intermittent tremor in his left hand [47]. Two years later, he was diagnosed with PD.

The roots of his PD may have been in Camp Lejeune [48]. When Mr. Grant was three years old, his father, then a Marine, was stationed at the base around the time that TCE levels in the water peaked [49]. There, Mr. Grant and his family lived in a trailer park on a dirt road. He enjoyed living on the military base, taking a bus to pre-school, and exploring its fighter planes. Mr. Grant also drank, bathed, and swam in the contaminated water, unaware of its toxicity.

Mr. Grant’s PD did not become apparent until about three decades after his family left Camp Lejeune. No one in his large family has had PD. His younger brother who was born on the base suffered disabling allergies that only resolved after they moved away. In March 2020, Mr. Grant’s father died at age 65 from esophageal cancer, which is linked to TCE [50].

Case 2

From 1984 to 1988, a young Navy captain, Amy Lindberg, was also stationed at Camp Lejeune in Jacksonville, North Carolina. On hot, humid days, Captain Lindberg swam, ran, trained, and outworked her peers. She also drank lots of water. What Captain Lindberg did not know is that the water that she drank, bathed, cooked, swam, and played in was contaminated with TCE, PCE, and other toxicants.

Between active duty and the reserves, Captain Lindberg served for 26 years, before she and her husband retired in northern Virginia. In 2017, thirty years after being stationed at Camp Lejeune, the then 57-year-old Captain Lindberg developed anxiety, depression, and trouble thinking (“brain fog”) and was seen by a neuropsychologist. He asked her about her loss of smell, decreased right arm swing, and dragging of her right leg, all of which she had developed about two years earlier. She also had a mild rest tremor in her right hand and long-standing constipation. She soon saw a neurologist who diagnosed her with PD, which was not present in her family.

Now 63, Captain Lindberg remains an avid runner, boxes regularly, and works out frequently, but is disabled by the disease’s non-motor features including urinary urgency, pain, and mood changes. In 2017, the U.S. Department of Veterans Affairs established PD as having a “presumptive service connection” for those who, like Captain Lindberg, served at Camp Lejeune between 1953 and 1987 [51].

Case 3

Dr. Jesh Mittal is a 48-year-old endocrinologist who was raised in an upstate New York community heavily contaminated by TCE. His first home, where he lived until age 14, was located less than a mile from a Superfund site where TCE, PCE, or both had contaminated 60 residential drinking wells [52]. His second home, where he resided until starting college, was also less than a mile from another Superfund site contaminated by TCE and other solvents used in vapor degreasing [53]. However, his potential exposure did not end at home.

The future physician attended high school adjacent to a large computing firm where his father worked. The soil and groundwater at the manufacturing site were contaminated with TCE and PCE. In 1971, seven years before his freshman year, the well at the high school was found to have “slight contamination” with TCE even after a filtration system was installed [54]. A generation later in 2000, groundwater monitoring found high concentrations of PCE at the manufacturing facility [55]. Neither his homes nor his high school were (to our knowledge) ever checked for vapor intrusion despite their proximity to contaminated sites.

In 2010, after a nurse noticed that his handwriting was becoming smaller, the right-handed physician was diagnosed with writer’s cramp. Two years later, he developed constipation, a “twitch” in his right hand, and dystonia in his right arm. He was subsequently diagnosed with PD at age 38. He had no family history of and no genetic marker for PD. Two years earlier, his mother was diagnosed with breast cancer, and three years after his PD diagnosis, his father was diagnosed with prostatecancer.

Likely occupational exposure to TCE

Case 4

Dr. John Smith was an 85-year-old physicist and industry executive with a family history of PD in his father and two paternal aunts, all of whom grew up on a farm. At age six, the future electrical engineer and his family moved to a farm in upstate New York where the young boy would apply rotenone and DDT to green bean plants as part of his chores. As a graduate student, he used TCE to wash electric parts but wore no personal protective equipment.

Upon completing his PhD, he joined National Aeronautics and Space Administration (NASA) where he cleaned electronics and was “swimming” in TCE. His term at NASA was interrupted by basic training in the army at Fort Gordon, Georgia, which served as a testing site for Agent Orange [56]. He then worked for a large computer manufacturing company in East Fishkill, New York, where TCE, PCE, and other chemicals eventually contaminated the soil and groundwater [57].

In approximately 2010, Dr. Smith was diagnosed with PD. His symptoms included anxiety, decreased energy, anhedonia, diminished initiative, depressed mood, and constipation in addition to a rest tremor, slowed movements, a stooped posture, and a soft voice. Some of these symptoms improved with levodopa, but they subsequently worsened. As part of a physical exam in 2019, an internist found a breast lump in Dr. Smith’s chest. The lump was cancerous. The treatment of his breast cancer, which is associated with TCE exposure [58], required surgery and tamoxifen.

Case 5

Mr. Ethan Jones is a 72-year-old retired teacher who was diagnosed with PD in 2017. He also carries a G2019S mutation in LRRK2.

In his early thirties, Mr. Jones worked for three to four years in a small copy and print shop that required multiple chemicals and solvents. He is unsure whether he was exposed to TCE or PCE, but chlorinated solvents were commonly used in the industry in the 1970s and 1980s [59]. About 35 years later, he noticed that he was moving slower than his peers and was subsequently diagnosed with PD at age 68. His symptoms improved with levodopa, which he continues to take.

Neither of his parents had PD, but his paternal grandfather did and his nephew does. In addition to PD, he was diagnosed with monoclonal gammopathy of undetermined significance, a premalignant state associated with multiple myeloma, which is associated with TCE exposure [60].

Case 6

After serving in the military, Mr. Alex Janssen worked in the construction and automotive industry. In these latter jobs, he worked with degreasing chemicals, such as TCE, for approximately seven years. About five years after his exposure ended, he noticed numbness on the right side of his body followed by difficulty walking up the stairs. He later experienced a stressful event that was followed by involuntary shaking in his right arm and leg and a PD diagnosis at age 33.

The number and intensity of PD symptoms increased significantly over the years, and he eventually had deep brain stimulation (DBS), which improved his symptoms and his quality of life. Three years later, he developed fatigue, headache, and a facial droop. Brain imaging at age 53 revealed a stage IV glioblastoma situated next to a DBS wire.

Case 7

In 2020, Georgians took to the polls to elect two U.S. Senators in a closely watched election that would determine political control of the legislative body. The reason for the unusual election? Parkinson’s disease. The late Senator Johnny Isakson, who was diagnosed with PD in 2015, had stepped down due to “health challenges” in 2019, leading to a special election in 2020 [61].

Senator Johnny Isakson, who died in 2021 at age 76, served for fifteen years in the U.S. Senate during which time he was a staunch advocate for veterans and co-chaired the Congressional Caucus on Parkinson’s Disease [62]. In addition to his PD, Senator Isakson had a two-centimeter renal cell carcinoma removed from his kidney in 2019 [61], a tumor associated with TCE exposure [63].

Nearly fifty years before his PD diagnosis, the future Senator served in the Georgia Air National Guard from 1966 to 1972. The military, including the Air Force, used TCE to degrease airplanes during this period [64], and many military bases, including those in Georgia [65], have been contaminated with the chemical [66].


As depicted by these cases, the adverse health effects associated with TCE extend far beyond PD. Its toxic effects begin shortly after conception. TCE can cross the placenta, [67] and maternal exposure to TCE is associated with low birth weight [68], congenital heart disease [68], and neural tube defects [69]. At the TCE-contaminated Marine Corps Base Camp Lejeune, at least seven babies had anencephaly, and ten had spina bifida [19, 70]. After birth, TCE-linked diseases proliferate as the solvent is linked to conditions affecting nearly every organ system [71] including cancer.

According to the U.S. Environmental Protection Agency (EPA) and World Health Organization, TCE is carcinogenic to humans by all routes of exposure [72, 73]. A meta-analysis found occupational exposure “was associated with excess incidences of liver cancer, kidney cancer, non-Hodgkin’s lymphoma, prostate cancer, and multiple myeloma, with the strongest evidence for the first three cancers” [74]. This is likely only a partial list. At least 78 men who lived at contaminated Camp Lejeune have been diagnosed with breast cancer [49]. In addition, high rates of brain and other central nervous system tumors have been reported in animal studies [19] and in TCE-contaminated communities [75, 76].

TCE’s adverse health effects have long been known. In 1932, Dr. Carey McCord, a physician working for the Chrysler Corporation, wrote a letter to the Journal of the American Medical Association. He said that activities of TCE “frequently fail to disclose the toxic nature of this chemical and the practical dangers that may attend its use.” He then detailed experiments with rabbits in which repeated skin exposure to the chemical caused death in days. Inhalation of TCE “under conditions of trivial exposure” killed the rabbits in days if not hours. Ninety years ago, he concluded that the solvent could be “the source of disaster for exposed workmen” [77].


The cases described demonstrate the potential role that TCE plays in PD. However, they are far from definitive and far from the only ones. The vignettes highlight many of the difficulties in establishing a strong link between the invisible TCE and PD. Among these are the following: 1) many are unaware of their exposure; 2) exposure, if present, was usually unmeasured; 3) previous exposures cannot currently be measured; 4) in many cases, exposure co-occurred with other pollutants; 5) time between exposure and disease is long; 6) underlying genetic risk factors, which are often not assessed, may augment the risk of developing PD following TCE exposure; and 7) diagnosis of PD is often delayed or missed.

In just one of the cases above was the person— a physicist— aware of his exposure to the toxic chemical at the time it occurred, and all were unaware of the health risks associated with the chemical. Those who drank contaminated water or inhaled polluted air outside or inside their workplaces, schools, or homes generally had no idea that they were exposed. Today, sites known to be contaminated with TCE, including many of the most toxic ones in the U.S., have no warning signs, fences, notices, or other public notification of the inherent dangers. As a result, it is challenging to determine whether exposure occurred.

Moreover, if exposure did occur, retrospective exposure assessment of TCE is difficult. Exposure is almost never measured contemporaneously (indeed, we are unaware of any case of PD associated with TCE where it was). Biomarkers of historical TCE exposure do not currently exist. The few studies [9, 20] and case reports [11, 73] available suggest that a dose-response relationship may be present as individuals who work most closely with the chemical have a shorter lag between exposure and disease onset.

Like other environmental toxicants (e.g., smoking, pesticides), exposure to TCE is often combined with other exposures. Many TCE-contaminated sites are polluted with PCE and other toxic hydrocarbons such as benzene and carbon tetrachloride, which itself may be associated with PD.

The effect of each individual compound has often not been assessed, and research into the risk of exposure to mixtures of toxicants is needed [78, 79].

The time between exposure and disease onset may be decades. Individuals, if they were aware of their exposure to the chemical, may have long since forgotten about it. Those who worked with the solvent or who lived near a contaminated site may have changed jobs or moved, making retrospective evaluation of potential clusters challenging.

Finally, while TCE’s effects on cancer are well-documented, its effects on PD are only recently coming to light. Gash’s study of factory workers who developed PD after degreasing metal parts with TCE was published in 2008 [9]. The twin study quantifying the high degree of association between occupational or hobby exposure to TCE and PD is only ten years old [11]. Many individuals who know they were exposed to TCE and subsequently developed PD have no reason to link the two. Today, most clinicians are unaware of TCE’s deleterious health effects even though they have been documented for over ninety years [77].


To address the large role TCE (and other chlorinated solvents) may play in fueling the rise of PD, we need to do the following:

  • 1. Conduct more research – Given the widespread environmental contamination by TCE, the authors of the twin study linking TCE to PD concluded, “the potential public health implications are substantial” [11]. Unfortunately, that prescient warning has largely gone unheeded. A search of TCE and PD on PubMed yields only 15 papers in the past decade [80]. By contrast, a search of the genetic risk factor GBA and PD returns more published papers in just the last two months [81]. Among the pressing research needs are evaluating cohorts (ideally prospectively) of individuals (likely) exposed to TCE, identifying biological markers of prior exposure, better understanding the mechanisms of injury, and assessing gene-environment interactions including those affecting TCE’s metabolism. Further work is also needed to estimate the risk of TCE exposure in conjunction with other known neurotoxicants, such as pesticides, and risk factors like traumatic brain injury.

  • 2. Clean and contain contaminated sites – Hundreds of thousands of sites are contaminated across the U.S. and globally. They are found in strip malls where dry cleaners used to operate, on military bases where use was widespread, in cities near old manufacturing sites (especially those near rivers or streams), and in rural areas where landfills were created to dump hazardous waste. Fortunately, contaminated sites can be remediated, and homes, schools, and workplaces can be protected by vapor intrusion mitigation systems like those used for radon [82]. Until they are cleaned, existing contaminated sites must be contained, limiting exposure for humans and nature. Local, regional, and national authorities should take responsibility in overseeing rapid control of contaminated sites.

  • 3. Monitor TCE levels and publicly communicate risk – Most databases monitor emissions, not current levels, and monitoring tends to be sporadic and reactive. TCE testing in groundwater, drinking water, soil, and in outdoor and indoor air should be widespread, frequent, and part of routine water quality testing. The results should be readily and publicly available. Polluted sites need to be marked as such, and the dangers to health clearly communicated to all parties at risk.

  • 4. Ban trichloroethylene – In many ways, the long-established health risks of TCE dwarf its relationship with PD. TCE causes cancer, increases the risk of miscarriages, contributes to birth defects, and is associated with diseases in nearly every organ system. The chemical is over a century old. We do not fly airplanes from the days of the Wright brothers or drive cars from Henry Ford’s era; engineers have developed safer ones. Chemists can do the same for solvents. Some companies now advertise safer alternatives to TCE [83]. They are needed as the use of TCE continues to rise globally.

  • 5. Listen to our patients – Finally, we should listen to our patients more. In medicine, we often move from diagnosis to treatment without considering the cause. The vast majority of individuals with PD do not have a family history of the disease or carry an identifiable genetic risk factor. Listening to their life stories or occupational histories can help identify TCE or other factors contributing to PD and could help develop etiology-specific treatments. This information can also inform their care (e.g., cancer screening), provide guidance to family members, co-workers, and classmates, and advance our understanding of the potential causes of this debilitating and likely very preventable disease.


For more than a century, TCE has threatened workers, polluted the air we breathe— outside and inside— and contaminated the water we drink. Global use is waxing, not waning. Most of this has been invisible, all of it is unacceptable, and none of it will stop until we act.


Thank you to those who contributed their stories, including Mr. Brian Grant, Captain Amy Lindberg, and several anonymous individuals.


Dr. Dorsey has received honoraria for speaking at American Academy of Neurology, American Neurological Association, Excellus BlueCross BlueShield, International Parkinson’s and Movement Disorders Society, National Multiple Sclerosis Society, Northwestern University, Physicians Education Resource, LLC, PRIME Education, LLC, Stanford University, Texas Neurological Society, and Weill Cornell; received compensation for consulting services from Abbott, Abbvie, Acadia, Acorda, Bial-Biotech Investments, Inc., Biogen, Boehringer Ingelheim, California Pacific Medical Center, Caraway Therapeutics, Curasen Therapeutics, Denali Therapeutics, Eli Lilly, Genentech/Roche, Grand Rounds, Huntington Study Group, Informa Pharma Consulting, Karger Publications, LifeSciences Consultants, MCM Education, Mediflix, Medopad, MedRhythms, Merck, Michael J. Fox Foundation, NACCME, Neurocrine, NeuroDerm, NIH, Novartis, Origent Data Sciences, Otsuka, Physician’s Education Resource, Praxis, PRIME Education, Roach, Brown, McCarthy & Gruber, Sanofi, Seminal Healthcare, Spark, Springer Healthcare, Sunovion Pharma, Theravance, Voyager and WebMD; research support from Biogen, Biosensics, Burroughs Wellcome Fund, CuraSen, Greater Rochester Health Foundation, Huntington Study Group, Michael J. Fox Foundation, National Institutes of Health, Patient-Centered Outcomes Research Institute, Pfizer, PhotoPharmics, Safra Foundation, and Wave Life Sciences; editorial services for Karger Publications; stock in Included Health, stock in Mediflix and ownership interests in SemCap.

Dr. Schneider has received compensation for consulting services from Escape Bio and Parkinson’s Foundation; research support from Acadia Pharmaceuticals, Biohaven Pharmaceuticals, the Michael J. Fox Foundation for Parkinson’s Research, National Institutes of Health, Parkinson Study Group, and CHDI Foundation.

Dr. Kieburtz has research support from NIH (NINDS, NCATS) and the Michael J Fox Foundation. He is paid to serve on DSMBs of studies for Janssen, Lilly, and Roche/Genentech. He receives payments from Hoover Brown LLC and Clintrex Research Corp, and has equity interests in both. He also has equity interests in Biohaven, Inhibikase, Modality.AI and Safe Therapeutics LLC.

Dr. Tanner has received has received grant support from the NIH, the Michael J Fox Foundation, the Department of Defense, the Parkinson Foundation, the Marcus Program in Precision Medicine, Gateway LLC, Roche-Genentech, Biogen, Bioelectron Technology Corporation; personal compensation as a consultant/scientific advisory board /data & safety monitoring board member for CNS Ratings, Cadent, Adamas, Biogen, Neurocrine, Kyowa Kirin, Jazz/Cavion, Lundbeck and the Australian Parkinson’s Mission.

Dr. De Miranda is funded by the National Institutes for Environmental Health Sciences (R00ES029986).

Dr. Goldman has received research support from the Michael J. Fox Foundation, the National Institutes of Health, the Agency for Toxic Substances and Disease Registry (ATSDR), the Health Resources and Services Administration (HRSA), the US Department of Defense, and the Veterans Health Administration.

Prof. Bloem currently serves as co-Editor in Chief for the Journal of Parkinsons Disease but was not involved in any way in the peer review process of this editorial. He serves on the editorial board of Practical Neurology and Digital Biomarkers, has received honoraria from serving on the scientific advisory board for Abbvie, Biogen and UCB, has received fees for speaking at conferences from AbbVie, Zambon, Roche, GE Healthcare and Bial, and has received research support from the Netherlands Organization for Scientific Research, the Michael J Fox Foundation, UCB, Not Impossible, the Hersenstichting Nederland, the Parkinson’s Foundation, Verily Life Sciences, Horizon 2020 and the Parkinson Vereniging (all paid to the institute).



Dorsey ER , Elbaz A , Nichols E , Abbasi N , Abd-Allah F , Abdelalim A , Adsuar JC , Ansha MG , Brayne C , Choi J-YJ , Collado-Mateo D , Dahodwala N , Do HP , Edessa D , Endres M , Fereshtehnejad S-M , Foreman KJ , Gankpe FG , Gupta R , Hamidi S , Hankey GJ , Hay SI , Hegazy MI , Hibstu DT , Kasaeian A , Khader Y , Khalil I , Khang Y-H , Kim YJ , Kokubo Y , Logroscino G , Massano J , Mohamed Ibrahim N , Mohammed MA , Mohammadi A , Moradi-Lakeh M , Naghavi M , Nguyen BT , Nirayo YL , Ogbo FA , Owolabi MO , Pereira DM , Postma MJ , Qorbani M , Rahman MA , Roba KT , Safari H , Safiri S , Satpathy M , Sawhney M , Shafieesabet A , Shiferaw MS , Smith M , Szoeke CEI , Tabarés-Seisdedos R , Truong NT , Ukwaja KN , Venketasubramanian N , Villafaina S , weldegwergs Kg , Westerman R , Wijeratne T , Winkler AS , Xuan BT , Yonemoto N , Feigin VL , Vos T , Murray CJL ((2018) ) Global, regional, and national burden of Parkinson’s disease, 1990-2016: A systematic analysis for the Global Burden of Disease Study 2016. Lancet Neurol 17: , 939–953.


Dorsey ER , Bloem BR ((2018) ) The Parkinson pandemic— a call to action. JAMA Neurol 75: , 9–10.


Klein C , Westenberger A ((2012) ) Genetics of Parkinson’s disease. Cold Spring Harb Perspect Med 2: , a008888.


Bloem BR , Okun MS , Klein C ((2021) ) Parkinson’s disease. Lancet 397: , 2284–2303.


Tanner CM , Kamel F , Ross GW , Hoppin JA , Goldman SM , Korell M , Marras C , Bhudhikanok GS , Kasten M , Chade AR , Comyns K , Richards MB , Meng C , Priestley B , Fernandez HH , Cambi F , Umbach DM , Blair A , Sandler DP , Langston JW ((2011) ) Rotenone, paraquat, and Parkinson’s disease. Environ Health Perspect 119: , 866–872.


Gardner RC , Byers AL , Barnes DE , Li Y , Boscardin J , Yaffe K ((2018) ) Mild TBI and risk of Parkinson disease. Neurology 90: , e1771.


Huber F ((1969) ) Clinical aspects and neuropathology of trichloroethylene poisoning. Z Unfallmed Berufskr 62: , 226–267.


Guehl D , Bezard E , Dovero S , Boraud T , Bioulac B , Gross C ((1999) ) Trichloroethylene and parkinsonism: A human and experimental observation. Eur J Neurol 6: , 609–611.


Gash DM , Rutland K , Hudson NL , Sullivan PG , Bing G , Cass WA , Pandya JD , Liu M , Choi D-Y , Hunter RL , Gerhardt GA , Smith CD , Slevin JT , Prince TS ((2008) ) Trichloroethylene: Parkinsonism and complex 1 mitochondrial neurotoxicity. Ann Neurol 63: , 184–192.


Reis J , Benbrick E , Bonneterre V , Spencer PS ((2016) ) Parkinson’s disease and solvents: Is there a causal link? Rev Neurol 172: , 761–765.


Goldman SM , Quinlan PJ , Ross GW , Marras C , Meng C , Bhudhikanok GS , Comyns K , Korell M , Chade AR , Kasten M , Priestley B , Chou KL , Fernandez HH , Cambi F , Langston JW , Tanner CM ((2012) ) Solvent exposures and Parkinson disease risk in twins. Ann Neurol 71: , 776–784.


Kochen W , Kohlmüller D , De Biasi P , Ramsay R ((2003) ) The endogeneous formation of highly chlorinated tetrahydro-β-carbolines as a possible causative mechanism in idiopathic Parkinson’s disease. In Developments in Tryptophan and Serotonin Metabolism, AllegriG, CostaCVL, RagazziE, SteinhartH, VaresioL, eds. Springer US, Boston, MA, pp. 253–263.


Liu M , Choi D-Y , Hunter RL , Pandya JD , Cass WA , Sullivan PG , Kim H-C , Gash DM , Bing G ((2010) ) Trichloroethylene induces dopaminergic neurodegeneration in Fisher 344 rats. J Neurochem 112: , 773–783.


Sauerbeck A , Hunter R , Bing G , Sullivan PG ((2012) ) Traumatic brain injury and trichloroethylene exposure interact and produce functional, histological, and mitochondrial deficits. Exp Neurol 234: , 85–94.


Liu M , Shin E-J , Dang D-K , Jin C-H , Lee PH , Jeong JH , Park S-J , Kim Y-S , Xing B , Xin T , Bing G , Kim H-C ((2018) ) Trichloroethylene and Parkinson’s disease: Risk assessment. Mol Neurobiol 55: , 6201–6214.


Keane PC , Hanson PS , Patterson L , Blain PG , Hepplewhite P , Khundakar AA , Judge SJ , Kahle PJ , LeBeau FEN , Morris CM ((2019) ) Trichloroethylene and its metabolite TaClo lead to degeneration of substantia nigra dopaminergic neurones: Effects in wild type and human A30P mutant α-synuclein mice. Neurosci Lett 711: , 134437.


De Miranda BR , Castro SL , Rocha EM , Bodle CR , Johnson KE , Greenamyre JT ((2021) ) The industrial solvent trichloroethylene induces LRRK2 kinase activity and dopaminergic neurodegeneration in a rat model of Parkinson’s disease. Neurobiol Dis 153: , 105312.


Agency for Toxic Substances and Disease Registry, Public Health Service, U.S. Department of Health and Human Services (2019) Toxicological profile for trichloroethylene. U.S. Departmentof Health and Human Services, p. 511.


IARC Working Group on the Evaluation of Carcinogenic Risks to Humans (2014) Trichloroethylene, Tetrachloroethylene, and Some Other Chlorinated Agents. IARC Monographs on the Evaluation of Carcinogenic Risks to Humans, No. 106. International Agency for Research on Cancer, Lyon (FR).


Agency for Toxic Substances and Disease Registry, Public Health Service, U.S. Department of Health and Human Services (2019) Toxicological profile for tetrachloroethylene. U.S. Department of Health and Human Services, p. 435.


Riederer P , Foley P , Bringmann G , Feineis D , Brückner R , Gerlach M ((2002) ) Biochemical and pharmacological characterization of 1-trichloromethyl-1,2,3,4-tetrahydro-β-carboline: A biologically relevant neurotoxin? Eur J Pharmacol 442: , 1–16.


De Miranda BR , Greenamyre JT ((2020) ) Trichloroethylene, a ubiquitous environmental contaminant in the risk for Parkinson’s disease. Environ Sci Process Impacts 22: , 543–554.


Risiglione P , Leggio L , Cubisino SAM , Reina S , Paternò G , Marchetti B , Magrì A , Iraci N , Messina A ((2020) ) High-resolution respirometry reveals MPP+ mitochondrial toxicity mechanism in a cellular model of Parkinson’s disease. Int J Mol Sci 21: , 7809.


McKee AC , Robinson ME ((2014) ) Military-related traumatic brain injury and neurodegeneration. Alzheimers Dement 10: , S242–S253.


Rocha EM , Keeney MT , Di Maio R , De Miranda BR , Greenamyre JT ((2022) ) LRRK2 and idiopathic Parkinson’s disease. Trends Neurosci 45: , 224–236.


Healy DG , Falchi M , O’Sullivan SS , Bonifati V , Durr A , Bressman S , Brice A , Aasly J , Zabetian CP , Goldwurm S , Ferreira JJ , Tolosa E , Kay DM , Klein C , Williams DR , Marras C , Lang AE , Wszolek ZK , Berciano J , Schapira AHV , Lynch T , Bhatia KP , Gasser T , Lees AJ , Wood NW ((2008) ) Phenotype, genotype, and worldwide genetic penetrance of LRRK2-associated Parkinson’s disease: A case-control study. Lancet Neurol 7: , 583–590.


Ge P , Dawson VL , Dawson TM ((2020) ) PINK1 and Parkin mitochondrial quality control: A source of regional vulnerability in Parkinson’sdisease. Mol Neurodegener 15: , 20.


Barringer F ((2011) ) E.P.A. Charts Risks of a Ubiquitous Chemical. The New York Times.


Doherty RE ((2014) ) History of TCE. In Trichloroethylene: Toxicity and Health Risks, GilbertKM, BlossomSJ, eds. Springer London, London, pp. 1–14.


Li N , Zhai Z , Zheng Y , Lin S , Deng Y , Xiang G , Yao J , Xiang D , Wang S , Yang P , Yang S , Xu P , Wu Y , Hu J , Dai Z , Wang M ((2021) ) Association of 13 occupational carcinogens in patients with cancer, individually and collectively, 1990-2017. JAMA Netw Open 4: , e2037530.


Brugnone F , Perbellini L , Giuliari C , Cerpelloni M , Soave M ((1994) ) Blood and urine concentrations of chemical pollutants in the general population. Med Lav 85: , 370–389.


European Chemicals Agency (2022) Case study: Impacts of REACHauthorisation of trichloroethylene.


(2020) C2 Chlorinated Solvents S&P Global’s Chemical Economics Handbook.


Fact.MR, Trichloroethylene Market,, Accessed October 27, 2022.


Toxics Release Inventory Explorer,, Accessed October 27, 2022.


Environmental Working Group Tap Water Database. Trichloroethylene,, Accessed October 28, 2022.


EPA, Superfund Site Search Query: California, Santa Clara County, Trichloroethylene, U.S. Environmental Protection Agency,


(2010) Camp Lejeune: Contamination and Compensation, Looking Back, Moving Forward. Committee on Science and Technology, House of Representatives.


Beck EC ((1979) ) The love canal tragedy. EPA J.


Nazaroff WW , Lewis SR , Doyle SM , Moed BA , Nero AV ((1987) ) Experiments on pollutant transport from soil into residential basements by pressure-driven airflow. Environ Sci Technol 21: , 459–466.


Shen R , Suuberg EM ((2016) ) Impacts of changes of indoor air pressure and air exchange rate in vapor intrusion scenarios. Build Environ 96: , 178–187.


Beamer PI , Luik CE , Abrell L , Campos S , Martínez ME , Sáez AE ((2012) ) Concentration of trichloroethylene in breast milk and household water from Nogales, Arizona. Environ Sci Technol 46: , 9055–9061.


LaRocco PS , David M ((2020) ) Grumman knew its toxic chemicals were polluting groundwater. It kept the facts secret. Newsday,


Geng C , Luo Q , Chen M , Li Z , Zhang C ((2010) ) Quantitative risk assessment of trichloroethylene for a former chemical works in Shanghai, China. Hum Ecol Risk Assess 16: , 429–443.


Community Fact Sheet No. 9 Former Ford Aeronutronics Facility– Newport Beach, CA,, Accessed January 13, 2023.


Ford Newport Beach Project,, Accessed January 13, 2023.


Laliberte R ((2016) ) Former NBA player Brian Grant combats Parkinson’s with exercise. Brain&Life.


Grant BB , Ric ((2021) ) Rebound: Soaring in the NBA Battling Parkinson’s, and Finding What Really Matter, Triumph Books.


Ruckart PZ , Bove FJ , Shanley E , Maslia M ((2015) ) Evaluation of contaminated drinking water and male breast cancer at Marine Corps Base Camp Lejeune, North Carolina: A case control study. Environ Health 14: , 74.


Hansen J , Raaschou-Nielsen O , Christensen JM , Johansen I , McLaughlin JK , Lipworth L , Blot WJ , Olsen JH ((2001) ) Cancer incidence among Danish workers exposed to trichloroethylene. J Occup Environ Med 43: , 133–139.


(2017) Diseases associated with exposure to contaminants in the water supply at Camp Lejeune. U.S. Department of Veterans Affairs.


Shenandoah Road Groundwater Contamination East Fishkill, NY, United States Environmental Protection Agency,, Accessed September 21, 2022.


Hopewell Precision Hopewell Junction, NY, U.S. Environmental Protection Agency,, Accessed September 22, 2022.


Klapp D ((1981) ) IBM is paying about $140,000 for well tests. Poughkeepsie J 3.


Hazardous Waste Cleanup: IBM Corporation, Former in Hopewell Junction, New York,U.S. Environmental Protection Agency, November 29, 2021.


(2014) Department of Veterans Affairs Board of Veterans’ Appeals. Citation Nr 1434404.


Wilkie HG, Keith, Region 2 RCRA Corrective Action Facility Fact Sheet,, Accessed October 28, 2022.


Laouali N , Pilorget C , Cyr D , Neri M , Kaerlev L , Sabroe S , Gorini G , Richiardi L , Morales-Suárez-Varela M , Llopis-Gonzalez A , Ahrens W , Jöckel K-H , Afonso N , Eriksson M , Merletti F , Olsen J , Lynge E , Guénel P ((2018) ) Occupational exposure to organic solvents andrisk of male breast cancer: A European multicenter case-controlstudy. Scand J Work Environ Health 44: , 310–322.


Perchloroethylene, International Agency for Research on Cancer,, Accessed October 1, 2022.


US Department of Veterans Affairs, Camp Lejeune water contamination health issues,, Accessed March, 2022.


Booker B, Citing ‘Health Challenges,’ Republican Sen. Johnny Isakson To Retire At End Of Year, National Public Radio (NPR),, Accessed July 1, 2022.


Blymire C, Tribute: Honoring Senator Johnny Isakson,, Accessed July 1, 2022.


Moore LE , Boffetta P , Karami S , Brennan P , Stewart PS , Hung R , Zaridze D , Matveev V , Janout V , Kollarova H , Bencko V , Navratilova M , Szeszenia-Dabrowska N , Mates D , Gromiec J , Holcatova I , Merino M , Chanock S , Chow W-H , Rothman N ((2010) ) Occupational trichloroethylene exposure and renal carcinoma risk: Evidence of genetic susceptibility by reductive metabolism gene variants. Cancer Res 70: , 6527–6536.


U.S. Government Accountability Office (2007) Environmental Contamination: Department of Defense Activities Related to Trichloroethylene, Perchlorate, and Other Emerging Contaminants. Subcommittee on Readiness, Committee on Armed Services, House of Representatives.


EPA, Superfund Site Search Query: Trichloroethene, Department of Defense, U.S. Environmental Protection Agency,


(1995) Environmental Impact Statement for Proposed Wing Conversion and Airspace Modification. Air National Guard Environmental Division.


Elkin ER , Harris SM , Su AL , Lash LH , Loch-Caruso R ((2020) ) Placenta as a target of trichloroethylene toxicity. Environ Sci Process Impacts 22: , 472–486.


Forand Steven P , Lewis-Michl Elizabeth L , Gomez Marta I ((2012) ) Adverse birth outcomes and maternal exposure to trichloroethylene and tetrachloroethylene through soil vapor intrusion in New York State. Environ Health Perspect 120: , 616–621.


Desrosiers TA , Lawson CC , Meyer RE , Richardson DB , Daniels JL , Waters MA , van Wijngaarden E , Langlois PH , Romitti PA , Correa A , Olshan A , and the National Birth Defects Prevention Study ((2012) ) Maternal occupational exposure to organic solvents during early pregnancy and risks of neural tube defects and orofacial clefts. Occup Environ Med 69: , 493.


Ruckart PZ , Bove FJ , Maslia M ((2013) ) Evaluation of exposure to contaminated drinking water and specific birth defects and childhood cancers at Marine Corps Base Camp Lejeune, North Carolina: Acase– control study. Environ Health 12: , 104.


Chiu WA , Jinot J , Scott CS , Makris SL , Cooper GS , Dzubow RC , Bale AS , Evans MV , Guyton KZ , Keshava N , Lipscomb JC , Barone S Jr , Fox JF , Gwinn MR , Schaum J , Caldwell JC ((2013) ) Human health effects of trichloroethylene: Key findings and scientific issues. Environ Health Perspect 121: , 303–311.


(2011) Toxicological review of trichloroethylene. U.S. Environmental Protection Agency, xlii .


Trichloroethylene, International Agency for Research on Cancer,, Accessed October 1, 2022.


(2000) Trichloroethylene CAS No. 79-01-6. Report on Carcinogens, Eleventh Edition.


Hasan F (2002) Residents near old semiconductor plant worry about toxic exposure Mountain View Voice.


DeBolt D (2011) TCE causes cancer, other health problems, EPA says. Mountain View Voice.


McCord CP ((1932) ) Toxicity of trichloroethylene. JAMA 99: , 409–409.


Van Der Ven Leo TM , Van Ommeren P , Zwart Edwin P , Gremmer Eric R , Hodemaekers Hennie M , Heusinkveld Harm J , van Klaveren Jacob D , Rorije E ((2022) ) Dose addition in the induction of craniofacial malformations in zebrafish embryos exposed to a complex mixture of food-relevant chemicals with dissimilar modes of action. Environ Health Perspect 130: , 047003.


Paul KC , Krolewski RC , Moreno EL , Blank J , Holton K , Ahfeldt T , Furlong M , Yu Y , Cockburn M , Thompson LK , Bronstein J , Rubin LL , Khurana V , Ritz B ((2022) ) Coupling comprehensive pesticide-wide association study to iPSC dopaminergic screening identifies and classifies Parkinson-relevant pesticides. bioRxiv, 2022.2002.2006.479305.


Search query “trichloroethylene +parkinson’s” PubMed,, Accessed October 1, 2022.


Search query “GBA + parkinson’s”, PubMed,, Accessed October 1, 2022.


(2015) Assessment of Mitigation Systems on Vapor Intrusion: Temporal Trends, Attenuation Factors, and Contaminant Migration Routes under Mitigated And Non-mitigated Conditions. U.S. Environmental Protection Agency.


Safe, sustainable n-Propyl Bromide and TCE replacement,, Accessed October 1, 2022.


Trichloroethylene sketch, NIH PubChem Sketcher,, Accessed October 5, 2022.


Bakke B , Stewart PA , Waters MA ((2007) ) Uses of and exposure to trichloroethylene in U.S. industry: A systematic literature review. J Occup Environ Hyg 4: , 375–390.


Who is at Risk for Exposure to Trichloroethylene? Agency for Toxic Substances and Disease Registry, Centers for Disease Control,, Accessed October 5, 2022.


(2017) Preliminary Information on Manufacturing, Processing, Distribution, Use, and Disposal: Trichloroethylene. U.S. Environmental Protection Agency.


Hansen J , Sallmén M , Seldén AI , Anttila A , Pukkala E , Andersson K , Bryngelsson I-L , Raaschou-Nielsen O , Olsen JH , McLaughlin JK ((2013) ) Risk of cancer among workers exposed totrichloroethylene: Analysis of three Nordic cohort studies. JNatl Cancer Inst 105: , 869–877.


Search query “trichloroethylene + contaminated + site” Web of Science (,, Accessed June, 2022.


Trichloroethylene (TCE) Exposure and VA Disability, Chisholm Chisholm & Kilpatrick LTD,, Accessed October 6, 2021.