Death as a Drug Side Effect in FAERS: Is Glyphosate Contamination a Factor?

Abstract

An analysis of selected datasets from the FDA’s drug Adverse Event Reporting System (FAERS) leads us to hypothesize that glyphosate contamination in both food and drugs is a major contributor to chronic and acute kidney failure respectively. In chronic kidney failure, glyphosate-induced pancreatitis results in the release of trypsin, causing a leaky vasculature. The albumin-bound glyphosate escapes into the tissues, protecting the circulatory system and kidneys but resulting in multiple symptoms related to skin, gut, brain, bones, lungs, etc. The rare and poorly understood acute kidney failure response reported for protamine sulfate and Trasylol? is strikingly similar to that associated with glyphosate poisoning. Both drugs are derived from biological tissues that are plausibly contaminated with glyphosate. These drugs protect from haemorrhage, which leads to retention of glyphosate in the vasculature, are followed by circulatory collapse and a high likelihood of death as an outcome. We support our argument by comparing symptom profiles of selected subsets of FAERS with those related to glyphosate poisoning, anomalous reactions to protamine sulfate, and conditions showing strong statistical time-trend correlations with glyphosate.

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Seneff, S., Swanson, N., Li, C. and Koenig, G. (2015) Death as a Drug Side Effect in FAERS: Is Glyphosate Contamination a Factor? Agricultural Sciences, 6, 1742-1501. http://dx.doi.org/10.4236/as.2015.612143

Received 11 November 2015; accepted 23 December 2015; published 28 December 2015

1. Introduction

Adverse drug reactions are common among intravenous medications, especially those administered to intensive care unit (ICU) patients [1] . The incidence of serious and even fatal adverse drug reactions in hospitals in the US is extremely high. An estimate from data in 1994 suggested that adverse reactions were between the fourth and sixth leading cause of death [2] .

The US Food and Drug Administration’s (FDA’s) Adverse Event Reporting System (FAERS) database is a large collection of drug side effect reports dating back to 2004. While it contains a wealth of information, it is difficult to tease out from the data the cause-and-effect relationships. This is mainly because most of the entries contain multiple drugs and multiple side effects, and some of the drugs are long-term maintenance drugs that may be irrelevant to the event. Furthermore, many of the side effects mentioned are likely preconditions such as diabetes or heart disease, which are probably provided to give additional useful information about the patient, but unfortunately they contribute noise to the task of sorting out cause-and-effect relationships.

Given these caveats, we report here on our attempts to critically analyze a specific subset of FAERS, focusing on an important side effect that is undeniably not a precondition: death. Doctors must be able to rely on pharmaceutical purity of drugs. When dealing with complex, unanticipated and inexplicable patient responses to pharmaceutical drugs, doctors need to be aware that the response may not be due to the drug itself, but rather to an inadvertently included contaminant. When drugs are contaminated with unknown harmful ingredients, it may take time for doctors to realize this and recognize the underlying problem. Analyzing drug side effects statistically is one way to begin to explore the possibility of drug contaminations. In this paper, we offer an explanation for an unusual and acute, life-threatening, adverse reaction to certain biological drugs derived from animal products that we believe may be due to unintended contaminants.

Our broadly specified goals are to establish which drugs are most strongly linked to death as an outcome, as well as which other symptoms co-occur with death, and then to try to explain our results by linking them to previous studies in the research literature. Our quest has yielded a most surprising hypothesis: certain biological drugs may carry a high risk of death due to contamination with glyphosate, the active ingredient in the pervasive herbicide, Roundup®. Furthermore, we believe we have identified a class of patients suffering from chronic kidney disease who statistically and collectively exhibit a profile of symptoms that can be explained as a consequence of chronic exposure to glyphosate in the ingested food and water. Our hypothesis is based, in part, on the increasing amounts of glyphosate found in food, air [3] [4] , rain [3] [5] , groundwater [5] , surface water [4] -[6] , soil [5] , seawater [7] , human serum [8] and urine [9] , and even in samples of marijuana [10] . Formal testing of the suspected drugs and ingested foods for glyphosate contamination can and should be done to validate our hypothesis.

We gathered as our first set all the data in FAERS where DEATH was mentioned as a side effect. We then identified the top ten other side effects co-occurring with death. We constructed a second, larger subset of the database by extracting all the entries where at least one of these side effects was mentioned (with or without death). This gives us a contextualized larger population with key symptoms associated with DEATH as a side effect. We then used a formal, mathematical procedure to obtain a short list of drugs most strongly linked to death within this subset population. This allowed us to compare the pooled subsets of our database with and without these particular drugs, and to see which other symptoms occur most frequently in association with the 9 drug classes we identified as potential “High-Death-Association drugs” (HDA DRUGS).

The list of HDA DRUGS was surprising. One noteworthy aspect is that many of them were biologicals derived from animal tissues, such as bovine lung or sturgeon testes, or from blood. This led to the realization that contaminants could be present due to the animals’ exposure to certain toxic chemicals. Since we were aware that glyphosate is pervasive in our environment today, we formulated the hypothesis that severe reactions to these biological drugs could be due to contamination with glyphosate. Exploration of the research literature led us to specific papers where lists of side effects were provided for conditions we suspected to be relevant to our hypothesis. We could then systematically compare the side effects associated with our candidate HDA DRUGS and the reactions reported in these papers.

Manufacturers of drugs are aware that unintended contamination through the manufacturing process is a serious issue. Flaum summarized the situation aptly in a review article on this subject: “In fact, the types of contaminants, their relative hazard to human health, the sources of contamination, and the methods for prevention and detection of such contamination are so varied and numerous as almost to defy compilation” ( [11] , p. 1). For example, in March of 2015, a subsidiary of Johnson & Johnson agreed to pay $25 million in damages due to the discovery of nickel and cadmium contamination in liquid Tylenol® products intended for infants. This is not an isolated occurrence, as a Reuters’ press release concerning this story reported: “There were far-reaching multiple recalls from 2008 to 2010 involving hundreds of millions of bottles and packages of consumer brands such as Tylenol, Motrin, Rolaids, Benadryl and other products due to faulty manufacturing” [12] .

The single drug most strongly linked to death in the FAERS database is Trasylol®, a serine protease inhibitor extracted from bovine lung that is used to protect from haemorrhage during open heart surgery. Red blood cells and protamine sulfate, used to neutralize heparin, were also strongly linked to death in our data analysis. A paper published in 1987 [13] brought the exciting news that aprotinin (Trasylol®) administered during cardiac surgery could reduce the need for transfusions by a factor of eight. Aprotinin was approved by the FDA in 1993 to reduce blood loss during coronary-artery bypass grafting [14] . Aprotinin was widely adopted for this purpose over the following years, but by 2008 it was becoming clear that aprotinin could cause an acute reaction terminating in kidney failure and death [15] -[18] . The FDA took action that year to remove aprotinin from the market, but it was later reinstated.

In an observational study published in 2006, involving 4374 patients, use of aprotinin was associated with twice the risk of renal failure requiring dialysis, a 55% increase in the risk of myocardial infarction or heart failure, and a 181% increase in risk of stroke or encephalopathy [15] . Strikingly, this increased risk was not found in association with tranexamic acid or aminocaprioc acid, two other drugs used similarly to prevent haemorrhage.

An analysis of 8548 patients published in 2008 found a lack of a dose-response relationship between aprotinin and renal failure [19] , which can be explained by varying levels of glyphosate contamination in the administered drug. In 2008, Fergusson et al. [20] compared aprotinin with another antifibrinolytic agent, aminocaproic acid, and found a greater than 50% relative increase for death within the first month linked to aprotinin. The abstract concluded with these harsh words: “Despite the possibility of a modest reduction in the risk of massive bleeding, the strong and consistent negative mortality trend associated with aprotinin, as compared with the lysine analogues, precludes its use in high-risk cardiac surgery”.

In contradiction, a meta-analysis of 211 randomized controlled trials published in 2004 showed no risk of renal failure or death [21] , but this was representing early data before the large increase in the potential of glyphosate contamination. A much later study from 2011 found nearly a 4-fold increase in odds of death one year later for patients administered aprotinin compared to no aprotinin use [22] . So it appears that the risk of death following aprotinin administration is increasing over time, in step with the increased contamination of glyphosate in animal feed. The Environmental Protection Agency (EPA) currently allows between 100 - 300 ppm of glyphosate residues in livestock feed [23] . In 2014, Kruger et al. reported finding 30 ppb of glyphosate residues in bovine lung tissue [9] .

Protamine sulfate was the third most strongly associated with death, after “red blood cells” and Trasylol®. In a case study on protamine sulfate, a rare, unexplained, anomalous reaction was identified that matched well with the symptoms linked to death. We again hypothesized that glyphosate contamination might explain the acute reaction. Protamine sulfate is administered as an antidote to heparin therapy following surgery, to inactivate the heparin and protect from haemorrhage. It was originally isolated from the sperm of salmon and sturgeon, but is now produced primarily through recombinant biotechnology. Like aprotinin, protamine sulfate has also been found to produce an inexplicable acute response in rare cases, manifested as a drop in blood pressure, pulmonary hypertension and noncardiac pulmonary oedema with cardiopulmonary collapse [24] . The severity of the reaction is not dose-related.

Holland et al. reported in 1984 on four unusual cases of an anomalous reaction to protamine sulfate [25] . These four represented only 0.2% of the patient pool exposed to the drug in their population, but their reaction was uniquely different from the usual anaphylaxis due to an antibody-mediated response, well recognized as a risk factor in association with this drug. While protamine sulfate was known to sometimes evoke an allergic reaction, an autoimmune reaction was ruled out for these four cases. Symptoms involved a drop in blood pressure within the first hour following administration associated with profound vascular damage with pulmonary oedema or total vascular collapse. Mortality is high at 30%, with survivors suffering significant morbidity. What is striking to us is that intravenous administration of glyphosate salts to piglets induced a very similar reaction, with a precipitous drop in blood pressure within the first hour and high mortality rate [26] . These symptoms are also remarkably similar to those of acute glyphosate poisoning. We therefore identified a set of symptoms linked to glyphosate exposure following suicide attempts [27] , and showed that these symptoms were over-represented in our death-related dataset.

A very fruitful avenue of exploration was to look specifically at the side effects related to kidney failure, which was the number two (after PAIN) side effect coincident with DEATH. Kidney failure is reaching epidemic proportions worldwide, and kidney failure has been strongly linked to glyphosate exposure among agricultural workers in Sri Lanka [28] , where glyphosate is currently banned from usage on crops for this reason. We hypothesized that the American population with chronic kidney failure had a high likelihood of having experienced chronic exposure to glyphosate during their lifetime. By subselecting for oedema along with conditions relating to the skin and gut, we were able to obtain a subpopulation with kidney failure that also exhibited characteristic symptoms of adrenal insufficiency. Adrenal insufficiency has recently been linked to low-dose glyphosate exposure [29] .

Remarkably, the remaining group with kidney failure but without evidence of adrenal insufficiency has a much higher chance of dying. The two drugs that are most strongly linked to death, Trasylol® and protamine sulfate, are also strongly biased towards the group without the symptoms of adrenal insufficiency. We hypothesize that these drugs interact with glyphosate by interfering with the body’s ability to export the toxic chemical into the tissues via oedema, so as to ultimately eliminate it through the skin or the gut. Instead, glyphosate accumulates in the terminal watershed of the kidneys and brain stem, leading to a characteristic set of mood- disorder symptoms along with acute kidney toxicity, and vascular failure.

Glyphosate is by far the most-used herbicide in the United States today. The use of glyphosate on corn and soy crops has risen steadily in the US following the rise in the adoption of Roundup®-Ready (RR) seeds, first introduced in the mid 1990s [30] , as well as the increasingly popular practice of desiccation with Roundup® right before the harvest, for crops such as sugar cane, grains (especially wheat) and legumes. The increased usage was compounded by the emergence of multiple glyphosate-resistant weeds following the adoption of RR crops [31] . Recently, Swanson et al. [32] published a list of disorders that were rising in step with glyphosate usage on corn and soy crops. We compared those disorders with the two classes of kidney failure events and found that most of these were significantly over-represented in the kidney failure group that included the adrenal insufficiency symptoms.

Today, we face a crisis which is precipitating rapid regulatory approval of mixed herbicides containing two active ingredients, such as glyphosate and 2,4-D or glyphosate and dicamba. This parallels the development of stacked GM crops that harbor resistance to both herbicides. While Monsanto, the inventor of glyphosate, maintains that it is nontoxic to humans, recent evidence has caused the WHO to relabel glyphosate as a “probable carcinogen” in March of 2015 [33] . Multiple biological explanations for how glyphosate could cause cancer are presented in [34] .

2. Materials and Methods

FAERS, containing information on both adverse events and medication errors, is a central part of the FDA’s post-marketing safety surveillance program for drugs and biological products. The system is voluntary for healthcare professionals and consumers, but mandatory for regulated industry and user facilities. The data are made available on the Web for free download. Each report is a structured entry containing the date of the incident, the age, gender and race of the person, a list of drugs that were taken and a list of side effects that were experienced. It is widely acknowledged that spontaneous reporting systems substantially under-represent the actual number of cases of adverse reactions that occur, estimated at only 6% of actual events [35] .

In this work, we have utilized data sets ranging from 2004 to 2012. Our methods are based on a multi-step procedure as outlined in Figure 1. Our goal is to first identify which drugs are most likely linked to death based on death being reported as a side effect. We then attempt to explain the biological link between those particular drugs and death, in part through identifying the other symptoms that co-occur with the drugs which are linked to death.

We began by extracting from the FAERS database all of the records where “DEATH” is a symptom. We then tabulated the number of times symptoms other than death were reported in this dataset, and selected the top-10 most frequent side effects as our focus. We then returned to the database and extracted all cases where at least one of these top-10 symptoms occurred, with or without death. In this way, we obtained a dataset with enrichment in death as a side effect along with death-related symptoms.

Our next step was to determine which drugs co-occur with death. This task is made more difficult because there are many drug classes with multiple drugs available within the class, such that the frequency of any one of those drugs might be small, but collectively they could become a major factor. We began by finding the top 15 single drugs co-occurring with each of our ten side effects. We pooled these drug lists as a guide to formulate drug classes, and manually produced a set of 34 distinct drug classes, as illustrated in Table 1. We used a web search to identify the major drug names associated with each of the classes. The full list of drugs (a total of 267 distinct drug names) is available online for download from http://people.csail.mit.edu/seneff/DRUG_CLASSES.txt.

Based on this list, we now needed a mechanism to score these drug classes for their potential to induce death. We took our subset of pooled data from our top symptoms linked to death and then divided it into two subsets: those with death as a co-occurring side effect (“DEATH” subset), and the remainder (“NOT DEATH” subset). We computed a score for the bias in the distribution of each drug class between the “DEATH” and “NOT DEATH” subsets. The score we chose will be used throughout this paper to assess biases between different subsets of the data, for both drugs and symptoms.

Let F1 = Count1/N1 = Frequency of drug-class or symptom in subset 1 (target).

Let F2 = Count2/N2 = Frequency of drug-class or symptom in subset 2 (comparison).

(1)

The score ranges from 0 to 1000, with 500 denoting that a drug or symptom occurs with equal frequency in the two datasets. Any score over 800 is highly skewed towards the target set: 800 means that the drug or symptom is four times more frequent in the target score set than in the comparison set (e.g., F1 = 4*F2).
Armed with this method, it was then possible to define a lower cutoff for the score and focus on all the drugs that exceeded this cutoff, which we now label as “High-Death-Association (HDA) DRUGS”. Having identified the drugs of interest, we could then re-sort our entire data set into two new subsets: one containing all the events where at least one of our drugs of interest was mentioned, and the other containing the events where none were mentioned.

Figure 1. Block diagram of our analysis procedures. See text for details.

Table 1. List of representative drug names for the drug classes we investigated in this paper.

The formula we used to select drugs can just as well be used to select symptoms. We can characterize each symptom by a score reflecting its degree of bias towards the HDA DRUGS. This provides a set of symptoms characterizing these drugs. We quantify as a significant result for our discovered symptoms anything which surpasses a 95% confidence interval (CI). Given that our two datasets are of fixed size, it is easy to determine the 95% CI for each frequency count, and from this we can define the minimum count required in the target dataset to assure 95% CI at a given score (from 500 to 1000).

Our targeted dataset of events linked to death-related drugs contained 43,434 entries, with 775,377 entries in the contrastive dataset without those drugs. A chart, presented in Table 2, shows the minimum count required in the target set for each score, over the range from 530 to 675. To compute scores that correspond to non-over- lapping frequency distributions in the two datasets, at the 95% confidence interval level, we started with a fixed count for Count1, e.g., 20, and calculated the 95% interval based on the size of dataset 1. We then varied Count2 until its 95% interval was close to, but did not overlap with the interval of Count1. We then calculated the score from these two counts, and defined this as the minimum score for 95% CI for Count1 = 20. The process was repeated for higher numbers of Count 1. Results are shown in Table 2 over the range from 530 to 675. Since we have discarded any symptoms with a count less than 20 in our target set, due to expected sparse data issues, any score over 675 is automatically significant at the 95% CI level.

An investigation of the research literature can help us define a unique “death syndrome” based on our symptom profile. Our final processing step is to compare symptoms found in association with various health conditions in the research literature with the symptoms we have identified as “death-drug related.” We have hypothesized that glyphosate contamination in the drug is a major factor in a substantial percentage of the acute reactions leading to DEATH as a side effect. We further hypothesize that synergistic toxicity between certain drugs and glyphosate plays an important role. We explain our reasoning for this hypothesis, along with support from the research literature, in the Discussion section.

3. Results

Our results will be illustrated in a series of tables, beginning with the table that lists the set of drug classes we chose to investigate (see Table 1). These include the popular maintenance drug classes such as statin drugs, blood pressure control drugs, and blood thinning drugs, as well as ERYTHROPOIETIN to stimulate red blood cell production, and drugs to treat acid reflux (NEXIUM), or cancer (GLEEVEC), depression (CELEXA), bone density loss (BONIVA), pain (MORPHINE), hormone therapy (YAZ), or inflammation (NSAID). It also includes some unusual and surprising “drugs” such as “RED BLOOD CELLS” and “PLATELETS.” We would not have thought to include these if not for the evidence revealed by our investigations of the most frequent drugs mentioned in our top-10 diseases.

Table 3 lists the top-10 side effects that co-occurred with death in the FAERS database. There are anticipated conditions linked to brain, heart and kidney problems. The list includes three mood-related disorders: “FEAR”, “ANXIETY”, and “ANHEDONIA”. “PAIN” is generally associated with disease, and therefore perhaps not unexpected. “UNEVALUABLE EVENT” is an interesting but vague symptom tag, and we explore this symptom class more fully at the end of this section.

3.1. High-Death-Rate (HDR) DRUGS

Table 4 lists the 9 drug classes that had scores over 750, the cut-off point that we used to select the candidate

Table 2. Table specifying counts required to gain 95% confidence intervals for the scores presented in the tables providing data on frequency distributions for counts in the “death-related drugs” events compared to the “not death-related drugs” events. The scores capture skewed distributions of each side effect over our contrastive datasets, computed as: 1000 * [frequency (Target)/(frequency (Target) + frequency (Control))]. A score of 1000 is the highest achievable score, indicating that all of the cases were in the Target set. With total counts of 43,434 entries in the Target set and 775,377 entries in the Comparison set, any score above 675 is automatically significant at the 95% confidence level (since we have a lower cutoff of 20 for the counts).

Table 3. Ten most frequent side effects co-occurring with death, along with their frequency counts for all cases, and for the subset of cases linked to death. The order is in decreasing frequency of association with death.

Table 4. Nine “death-related” drug classes (“HDA DRUGS”), with average scores for over-representation in the “DEATH” subset above 750 (more than three times more frequent in the DEATH subset).

death-related drugs. A score of 750 means that the drug is three times as common in the DEATH subset compared to the NOT-DEATH subset. The set of drug classes that made the cut was unexpected. The worst-scoring drug was TRASYLOL, a bovine pancreatic trypsin inhibitor, commonly used to reduce bleeding during surgery. As described in the Introduction, it has had a checkered history, and was suspended beginning in May of 2008 [36] , but the suspension was lifted in 2012. PLATELETS, RED BLOOD CELLS, and PROTAMINE SULFATE all scored over 900, which was very surprising, considering that these are all biologicals. ALBUMIN, which scored 881, like PLATELETS and RBCs, is a product of blood. It is normally produced by the liver and is one of the more abundant plasma proteins. VERSED is used to induce sedation before surgery, but also as a sleep aid and to treat epilepsy. VANCOMYCIN is an antibiotic used to treat bacterial infections. HEPARIN is a biological injectible anticoagulant, produced by mast cells. It is derived from mucosal tissues of slaughtered animals such as pig intestines or bovine lungs [37] .

3.2. Symptom Profile

Once we had assigned a set of drugs to investigate, the next step was to determine which symptoms are significantly over-represented in the subset of our events where at least one of these drugs was administered. We identified a total of 1305 symptoms with a biased distribution predicting increased risk associated with the HDA DRUGS, at the 95% CI level. This entire list is available for download from

http://people.csail.mit.edu/seneff/symptoms_linked_to_HDA_drugs.csv. Table 5 provides the most highly significant symptoms, namely, all those with more than 1000 counts and with a score greater than 720.
As can be seen from the table, these symptoms can be grouped into five primary categories, aside from a miscellaneous set of six side effects, one of which is “DEATH”. The blood-related category is likely linked to all the rest, reflecting multiple organ failures consequential to impaired blood flow following a catastrophic effect on the circulation. We hypothesize that hypotension, thrombocytopenia, sepsis, and haemorrhage are the initial response which quickly cascades into a multiple-organ crisis. “OSTEONECROSIS OF JAW”, in the “OTHER” category, is completely unexpected, but it probably has high significance that needs to be explained.

3.3. Comparison between Trasylol® and the Remaining HDA DRUGS

Since Trasylol® was, with a wide margin, the drug that was most strongly associated with death (see Table 4), we thought it would be interesting to compare symptoms associated with Trasylol® with those associated with the remaining HDA DRUGS. There were 11,344 events where TRASYLOL was among the listed drugs, but none of the other HDA DRUGS were present. The number of events where ANY of the HDA DRUGS except TRASYLOL was present was 25,753. These two datasets were highly differentiated by their manifested symptoms. In fact, many of the symptoms associated with death identified in Table 3 were highly skewed between the two datasets, in such a way that symptoms linked to the kidneys, mood disorders, and “other” (including

Table 5. Top scoring side effects linked to HDA DRUGS. This is an exhaustive list of all side effects with counts > 1000 and score > 720.

DEATH) aligned with TRASYLOL, and symptoms related to the vasculature, the lungs, and the heart aligned with the remaining HDA DRUGS (see Table 6).

3.4. Comparison to Anomalous Reaction to Protamine Sulfate

We previously described the rare, unusual reaction to protamine sulfate involving a precipitous drop in blood pressure over the first hour, and a high risk of death, which occurred in only 0.2% of the patient population [25] . These authors identified a specific set of symptoms that could be compared. Table 7 shows the degree of alignment with our symptoms associated with HDA DRUGS (target dataset) and the ones they identified. Our data show significant over-representation of death, as well as symptoms related to pulmonary oedema, vascular damage, vascular collapse, ascites, hypotension, and wheezing, with less support for rashes and a poor match with angioedema.

3.5. Comparison to Attempted Suicide through Glyphosate Ingestion

Table 8 lists a set of symptoms that were identified in a review of 131 cases of attempted suicide by ingesting

Table 6. Comparisons between TRASYLOL (target dataset) and all the other HDA DRUGS (control dataset) with respect to the distributions of selected symptoms most likely to co-occur with death. C1: total number of TRASYLOL events; C2: total number of events with any combination of the other HDA DRUGS; SCORE: score reflecting bias towards TRASYLOL (1000: max), as defined in Equation (1).

Table 7. Evidence from our study of FAERS that the target dataset of HDA DRUGS is associated with increased risk to several side effects that aligned with those observed in four unusual cases where protamine sulfate brought on an unexpected response [25] . The control dataset is all events in FAERS that do NOT include the HDA DRUGS. The values are an indicator of the skewed distribution of each side effect over our contrastive datasets, where the first number is the raw count in the target set and the second number is the score as defined in Equation (1). Key: * = Not significant to 95% confidence level; ** = Symptom is under-represented in target set.

glyphosate [27] . The table shows that these symptoms, for the most part, strongly fit the profile of our target dataset of HDA DRUG symptoms. Symptom classes include respiratory distress, renal failure, shock, altered consciousness, hyperkalaemia, hyperphosphataemia, lowered bicarbonate, pulmonary oedema, hypoxemia, leukocytosis, acidosis, and dysrrhythmia. The only opposing symptom was lactic acidosis which was underrepresented in the HDA DRUGS cases, but many other forms of acidosis were highly significantly positive, including “ACIDOSIS,” “RESPIRATORY ACIDOSIS,” and “METABOLIC ACIDOSIS.” It should be noted that the minerals are highly unstable in association with HDA DRUGS, for example with significant over-representation of both “HYPEKALAEMIA” and “HYPOPHOSPHATAEMIA.”

3.6. Renal Failure and Adrenal Insufficiency

Renal failure was the second most likely symptom associated with DEATH in the FAERS database (second to PAIN). According to Swanson et al. [32] , death due to end stage renal disease (R = 0.958, p ≤ 4.2E-6) and death due to acute renal failure (R = 0.978, p ≤ 5.95E-9) are very strongly correlated in their temporal frequency

Table 8. Evidence from our study of FAERS that the target dataset of HDA DRUGS are strongly associated with side effects of attempted suicide by glyphosate ingestion (see Table 3 of a review of 131 cases of attempted suicide by ingesting glyphosate [27] ). These symptoms were indicators of poor patient outcomes. The score for the distribution of each side effect over our contrastive datasets is computed as defined in Equation (1). The first number in each pair represents the raw count in the target set, and the second number is the score.

Key: * = Not significant to 95% confidence level; ** = Symptom is under-represented in target set. Any unmarked symptoms were significantly over-represented in the Target set, some by a wide margin (no overlap at 99% CI).

curves with the trend upward in glyphosate usage on corn and soy crops. Therefore, we hypothesized that a subset of our database restricted to renal failure would provide a more specific signal of potential chronic or acute glyphosate exposure. There were 127,652 records in the database where renal failure was one of the side effects. We constructed a working hypothesis that chronic renal failure would be linked to chronic exposure to glyphosate prior to the side-effect event, and that acute renal failure might correspond with glyphosate contamination in the administered drug or a direct toxicity of the drug to the kidneys. We further hypothesized that oedema and blood pressure drop immediately following exposure to the drug represented a physiological response aimed to try to flush a toxic exposure out of the blood, likely as a mechanism to protect the terminal watershed (kidneys and brainstem) from further damage. We reasoned that the skin rashes and other skin issues could be a consequence of penetration of the toxic chemical into the skin subsequent to oedema, and sweating could indicate a pathway towards excretion and therefore removal of the noxious chemical. Likewise, nausea, vomiting, diarrhea and gastrointestinal issues could indicate mechanisms to flush the chemical out through the digestive tract.

Thus, we constructed two datasets linked to kidney failure, where one set (KIDNEY-FAILURE1, 38,347 records) included any symptoms which contained a unique substring that was a member of the set: “SKIN”, “RASH”, “GASTRO”, “OESOPH”, “OEDEMA”, “NAUSEA”, and “VOMITING”, and the other set (KID- NEYFAILURE2, 89,306 records) contained none of these substrings among the listed symptoms. This was intended to capture most of the symptoms related to issues of the skin or gut along with oedema.

Guided by a recent paper studying the effects of small doses of Roundup® on rats [29] , we decided to investigate how our two renal failure subsets distributed with respect to symptoms related to adrenal insufficiency. Pandey et al. [29] showed that 10 mg/kg doses of Roundup® administered over a two-week period to male rats resulted in a marked drop in steroidogenesis in the adrenal glands. They showed that this was related to a reduced supply of adrenocorticotrophic hormone (ACTH) from the pituitary gland, which caused reduced expression of steroidogenic acute regulatory protein (StAR) in the adrenal glands. Further evidence comes from a study on sublethal exposures of fish to glyphosate, which showed a significant reduction in the amount of cortisol produced in response to a stress stimulus (P < 0.01) [38] . The StAR protein controls the rate-limiting step in steroidogenesis. It was indicated in an earlier paper that testosterone synthesis was sharply reduced in testicular Leydig cells exposed to Roundup®, an effect that was linked to marked reduction in the expression of StAR [39] . The fact that “BLOOD TESTOSTERONE DECREASED” was strongly over-represented in KIDNEY- FAILURE1 (score = 942) was encouraging in this respect. Pandey et al. wrote: “The findings that Roundup® treatment down-regulates endogenous ACTH, is similar to the condition known as adrenal insufficiency in humans. This condition manifests as fatigue, anorexia, sweating, anxiety, shaking, nausea, heart palpitations and weight loss.” ( [29] , p. 1084). Based on this list, we created a table showing how these symptoms distributed among KIDNEYFAILURE1 and KIDNEYFAILURE2. We constructed a significance chart similar to Table 2 for the new kidney failure datasets. It is remarkable, as shown in Table 9, that all of these symptoms, as well as ADRENAL INSUFFICIENCY itself, ADDISON’S DISEASE (chronic adrenal insufficiency) and SJOGREN’S SYNDROME were strongly over-represented in the KIDNEYFAILURE1 subset. Sjögren’s syndrome is a pathology of the salivary glands but it is linked to low pituitary function and reduced expression of ACTH (adrenocorticotrophic hormone) [40] . We will henceforth refer to the KIDNEYFAILURE1 subset as the “adrenal insufficiency dataset.”

3.7. Comparison to Conditions Correlated with Glyphosate Usage

A list of conditions whose incidence has been increasing alarmingly in the past two decades, in step with the increasing use of glyphosate on corn and soy crops was obtained from Swanson et al. [32] . The conditions and the associated p-values for their correlations with the temporal trends in glyphosate usage are shown in the headings of Table 10. We analyzed a set of symptoms which are more likely in the adrenal insufficiency group and which are representative of the conditions identified in Swanson et al. The acute renal failure and acute myeloid leukaemia do not pass our significance test, which is in agreement with our hypothesis that KIDNEYFAILURE1 and adrenal insufficiency are associated with chronic exposure to glyphosate.

“UNEVALUABLE EVENT” is an unusual category which, statistically, closely characterizes the reaction that we are detecting in our studies. We hypothesize this is linked to glyphosate exposure from the administered biologicals (blood products), along with the administration of other drugs that protect from haemorrhage, which includes protamine and Trasylol®, but also AMICAR (aminocaproic acid). TRASYLOL is remarkably over-

Table 9. Counts and scores for the KIDNEYFAILURE1 set (kidney failure with associated oedema, skin, or gut issues), compared to KIDNEYFAILURE2 (the remainder of the KIDNEY FAILURE cases), for various symptoms linked to adrenal insufficiency, as defined in [29] . The scores are computed as previously defined. Key: * = Not significant at 95% confidence level.

Table 10. Evidence that the adrenal insufficiency kidney failure dataset is associated with increased risk to several diseases and conditions that correlate in temporal patterns with glyphosate usage on corn and soy crops. The values are an indicator of the skewed distribution of each side effect over the contrastive dataset (KIDNEYFAILURE2). The first number is the raw counts in the adrenal insufficiency dataset and the second number is the SCORE as defined in Equation (1). The p-values associated with the diseases are taken from Table 3 in Swanson et al. [32] , and reflect the strength of the correlation with glyphosate usage.

Key: * = Not significant at 95% confidence level.

represented within the UNEVALUABLE EVENT dataset, with over 16,000 cases and a score of 996. AMICAR is also one of the drugs that is highly over-represented (403 count, with a score of 986). Both HEPARIN and PROTAMINE SULFATE score over 950, as do RED BLOOD CELLS, PLATELETS, and PLASMA. Other drugs that are highly associated with UNEVALUABLE EVENT are drugs used in anaesthesia and drugs used to treat heart failure.

Table 11 lists side effects that are linked to UNEVALUABLE EVENT, contrasted with side effects linked to adrenal insufficiency. Among other side effects, UNEVALUABLE EVENT is highly inverse correlated with the symptoms linked to adrenal insufficiency. OSTEONECROSIS OF JAW, on the other hand, obtained a score of 974 in our adrenal insufficiency dataset, and a score of only 53 in the UNEVALUABLE EVENT subgroup. Other disorders related to jaw and also to bone, more generally, were similarly skewed towards adrenal insufficiency and away from UNEVALUABLE EVENT. Conditions related to the lung were highly over-represented in association with adrenal insufficiency and highly under-represented with UNEVALUABLE EVENT. Brain disorders such as dementia, Parkinson’s disease, depression, and attention deficit hyperactivity disorder were all strongly over-represented in the adrenal insufficiency data set.

The most highly linked symptom to UNEVALUABLE EVENT was RENAL INJURY. MULTI-ORGAN FAILURE also scored very highly, along with MULTIPLE INJURIES and RENAL IMPAIRMENT. Symptoms related to brain stem disorder include FEAR, ANHEDONIA, TARDIVE DYSKINESIA, EXTRAPYRAMIDAL DISORDER, and EMOTIONAL DISTRESS. DEATH is also highly correlated with UNEVALUABLE EVENT, with 8421 cases and a score of 941.

Since we have reached the working hypothesis that Trasylol® is the most potent of our HDA DRUGS, and that UNEVALUABLE EVENT best characterizes an acute reaction to glyphosate, we decided to use the subset of our database where both of these were present along with DEATH as a side effect to characterize trends over time of DEATH as a side effect. The results are shown in Table 12. As might be expected if glyphosate contamination is increasing over time, the death toll steadily rises until 2008, when Trasylol® was temporarily removed from the market. However, by 2010, the number of DEATHS recorded had risen to surpass the highest count before 2010.

4. Discussion

“Death” as a drug side effect listed in the FAERS database represents a unique opportunity to investigate acute and unusual drug reactions. In many of the reports culminating in death, it is likely that the patient already had a

Table 11. Comparison of typical symptoms linked to UNEVALUABLE EVENT contrasted with those of the adrenal insufficiency dataset. See text for discussion.

Table 12. Number of events where DEATH and UNEVALUABLE EVENT were both listed as side effects, and TRASYLOL was the only one of the HDA DRUGS that was administered.

life-threatening disease such as cancer or renal failure. However, the fact that “death” was recorded as an adverse reaction implies that the circumstances surrounding the death were unexpected in the context of the disease. The fact that “UNEVALUABLE EVENT” as a side effect is strongly linked to DEATH supports this contention. Our investigation into the specific drugs and other side effects that co-occur with death have led to a novel hypothesis that, in some cases, an acute reaction to an unintended contaminant in the drug may explain death as an outcome. We hypothesize, based on its pervasiveness, that this contaminant is usually glyphosate.

Our investigations focused mainly on comparisons among two pairs of datasets. The first pair is contrastive for HDA DRUGS among the listed side effects, which we subdivided into two groups: one that includes death as a side effect and one that does not. The second pair concerns only the subset where renal failure was a side effect, divided into two groups reflecting a distinction we have related to the presence or absence of adrenal insufficiency and associated symptoms. Within this second set, DEATH as a side effect and TRASYLOL or PROTAMINE SULFATE as a drug all linked strongly to the set without adrenal insufficiency. We propose that renal failure with adrenal insufficiency captures chronic renal failure and associated symptoms due to chronic glyphosate exposure from food, and that the TRASYLOL-associated renal failure subset is far more likely to reflect glyphosate contamination in the drug, especially when the drug in question (TRASYLOL and PROTA- MINE SULFATE) protects from haemorrhage.

The symptoms derived from the research literature involving glyphosate poisoning through suicide attempts [27] and a rare but unusual reaction to protamine sulfate [25] are over-represented in the HDA DRUGS data set. We propose that these are associated with acute glyphosate poisoning. The list of symptoms associated with the diseases and conditions that have been found to be rising in frequency in step with glyphosate usage on corn and soy crops [32] are significantly over-represented in the adrenal insufficiency subset of the renal failure database. It is instructive to compare the scores for these symptoms to those in the HDA DRUGS dataset. In the case of Swanson et al. [32] , the conditions with weak support in the HDA DRUGS dataset are multiple sclerosis, Parkinson’s disease, inflammatory bowel disease and viral infection.

We propose that these conditions, all of which are well supported in the adrenal insufficiency dataset, are linked to chronic exposure of the gut microbiome to glyphosate via an oral delivery pathway, whereas intravenous administration of glyphosate through drug contamination would by-pass the gut. For instance, in [41] , it was proposed that glyphosate could be causal in Parkinson’s disease through manganese toxicity in the brain stem, consequential to manganese accumulation in the liver through disrupted bile flow. Manganese then traverses the vagus nerve to accumulate in the brain stem.

In two independent life-long rat studies, liver and kidney disease are strongly linked to chronic exposure to Roundup® in small environmentally plausible doses [42] [43] . Mesnage et al. [42] identified over 4000 genes related to liver and kidney function whose expression rates were significantly altered, and this was consistent with anatomical and histological changes as well as blood and urine biochemical pathologies identified by Séraliniet al. for rats similarly exposed [43] . Mesnage et al. [42] wrote in the abstract: “Observed alterations in gene expression were consistent with fibrosis, necrosis, phospholipidosis, mitochondrial membrane dysfunction and ischemia.”

UNEVALUABLE EVENT: We hypothesize that the most common situation where UNEVALUABLE EVENT occurs is in cardiac surgery relating to heart disease and heart failure, where drugs are administered to protect from haemorrhage. This leads to an increased risk to death consequential to glyphosate contamination in the administered biologicals, in part due to an inability to flush the toxic chemical out of the blood into the tissues. This results in kidney toxicity due to the large concentration of glyphosate that reaches the kidney, and to increased exposure in the brainstem, which, like the kidney, is a highly perfused terminal watershed area. Thus, we are hypothesizing synergistic action between glyphosate and drugs used to prevent haemorrhage, which results in an inability to reduce the toxic burden in the vasculature.

The side effect, FEAR is significant, and it suggests excitation of the NMDA receptors in the amygdala [44] [45] . FEAR was hugely overexpressed in association with UNEVALUABLE EVENT, as it was listed as a side effect in over half of the events, with over 15,000 cases and a score of 978. NMDA receptors respond to simultaneous presence of glutamate and glycine ligands [46] . Studies on rats exposed to glyphosate have shown that its mechanism of action in the hippocampus is over-stimulation of NMDA receptors [47] , likely due to glyphosate’s chelation of manganese interfering with glutamate recycling [48] coordinated with its direct action as a glycine mimetic to act as the second ligand.

A Role for Toxic Metals? Toxic metals such as aluminum and cadmium may also play a role in the drug reactions investigated here. Albumin and heparin are especially effective at extracting aluminum from glass, and this has brought up a concern for aluminum toxicity in these products following a long storage time in a glass vial [49] . It has been proposed that aluminum may be synergistically toxic with glyphosate [50] , and this would be particularly true under conditions of kidney failure when aluminum tends to be stored in the body due to failed kidney function [51] . Parathyroid hormone dramatically increases the retention of aluminum in the brain of rats fed dietary aluminum [52] . Elevated PTH through secondary hyperparathyroidism is a common feature of renal failure [53] . This is supported by the adrenal insufficiency analysis, where there were five side effects related to elevated parathyroid, and they scored in the range from 814 to 957.

It is plausible that these biological pharmaceuticals could also extract cadmium from glass, as cadmium can be leached from glass in acidic environments [54] . Glyphosate is both acidic and a strong chelating agent, so its presence could compound the problem. Both arsenic [28] and cadmium [55] have been proposed as possible causes of chronic kidney disease. Cadmium exposure is a growing problem, and studies on children have shown that it is linked to impaired bone mineralization [56] , which is a key feature of our adrenal insufficiency profile. It was hypothesized in [28] that arsenic is synergistically toxic with glyphosate due to glyphosate’s action as a chelating agent. Glyphosate could be expected to unload its arsenic cargo in the acidic environment of the terminal watershed in the kidney. Thus it is possible that glyphosate contamination in a biological drug such as heparin could enhance the effectiveness in extracting toxic metals from the vial and then carrying them to the terminal watershed areas of the kidneys and brain stem nuclei to cause harm.

A high rate of kidney failure was reported in a small agricultural community in India which was linked to toxic metal contamination, mainly cadmium and lead, in the soil [57] . Symptoms included oedema, anemia, proteinuria, anorexia, hypertension, glycosuria, haematuria and renal calculi. All of these symptoms were over- represented in our adrenal insufficiency dataset.

Glyphosate Formulations: Glyphosate formulations generally contain buffering salts such as isopropylamine salt to increase glyphosate’s solubility in water. Furthermore, a surfactant is added such as polyoxyethylenea- mine (POEA) to increase uptake of glyphosate into the cells of the weeds, and POEA is itself also highly toxic [58] . In fact, glyphosate formulations have been found to be up to 125 times more toxic to animals than glyphosate by itself [59] .

A study in Korea from 2010 involving 76 patients who ingested glyphosate formulations revealed respiratory failure, hypotension, acute pancreatitis, acute kidney injury, hyperkalemia and seizures as common symptoms [60] . A study involving over 600 patients with acute poisoning from glyphosate-containing herbicides in two hospitals in Sri Lanka between 2002 and 2007 found a 3.2% fatality rate, with a median time to death of 20 hours [61] . Symptoms linked to death included gastrointestinal symptoms, respiratory distress, hypotension, altered level of consciousness, and oliguria. Plasma levels of glyphosate above 734 μg/mL were detected. All of the symptoms listed above for both studies were significantly over-represented in our adrenal insufficiency dataset.

A study on piglets is especially relevant to our results because it examined the effects of glyphosate infusion as well as the infusion of the isopropylamine salt of glyphosate (IPAG) and the commonly used surfactant, POEA [26] . The latter two were found to be much more toxic than glyphosate alone. A 35 minute intravenous infusion of IPAG resulted in a precipitous drop in blood pressure, over the course of about an hour, highly reminescent of the rare and unusual reaction to protamine sulfate described earlier [25] . Half of the 6 piglets died immediately following the blood pressure drop, along with indications of ventricular arrhythmia. This was associated with lowered cardiac contractility and heart failure. Only 2 of the 6 piglets recovered, with a mortality rate therefore of 66.7%. POEA was also found to be toxic, causing metabolic acidosis, pulmonary vasoconstriction, left ventricular dysfunction and circulatory collapse, ultimately leading to death within a few hours of exposure for all 6 exposed piglets. A woman who drank a formulation containing glyphosate and POEA developed acute respiratory distress with circulatory collapse, renal failure, disseminated intravascular coagulopathy and aseptic meningitis, suggesting brain involvement [62] .

The symptoms of both IPAG and POEA exposure are strongly linked to the HDA DRUGS dataset, with consistently high scores for HYPOTENSION (770) VENTRICULAR ARRHYTHMIA (747), LEFT VEN- TRICULAR FAILURE (812), METABOLIC ACIDOSIS (709), CIRCULATORY COLLAPSE (712), PUL- MONARY VASCULAR DISORDER (872), RESPIRATORY DISTRESS (793), DISSEMINATED INTRA- VASCULAR COAGULATION (723) and DEATH (933). This might suggest that the additional components of glyphosate formulations could also be present in the administered biological drugs.

Remarkably, there was only one case of “ARRHYTHMIA” of any sort in the kidney failure set without adrenal insufficiency, while there were 2382 cases reported in the adrenal insufficiency subset of the kidney failure database. HYPOTENSION was also strongly linked to adrenal insufficiency (785) as well as CIR- CULATORY COLLAPSE (756). Patients with adrenal insufficiency have been shown to be at increased risk to lethal arrhythmias when exposed to excessive stress [63] .

OSTEONECROSIS OF JAW: OSTEONECROSIS OF JAW is an unusual side effect highly correlated with DEATH in our analysis (see Table 5). Furthermore, the kidney failure set with adrenal insufficiency had 2199 cases where OSTEONECROSIS OF JAW was a listed side effect, as compared to only 140 in the comparison set of kidney failure without adrenal insufficiency. There were no cases of OSTEONECROSIS OF JAW when TRASYLOL was a listed drug and none of the other HDA DRUGS were present. This type of event (TRA- SYLOL only) was not uncommon, with over 11,000 cases listed, so it is quite striking that none included OSTEONECROSIS OF JAW.

OSTEONECROSIS OF JAW may seem at first glance unrelated to glyphosate exposure, and certainly there are other known risk factors, including tooth removal, bisphosphonates, chemotherapy, multiple myeloma, low blood protein levels, and renal impairment [64] . Avascular necrosis of the jaw [64] is associated with persistent bacterial infection (generally Actinomyces colonization) and increased oxidative stress and glutathione depletion [65] . Glyphosate both decreases glutathione and increases oxidative stress. In addition, many items on this list can plausibly be linked to glyphosate. A complex formed by two glyphosate molecules chelating aluminum [50] may behave much like a bisphosphonate to interfere with pyrophosphate-based activities in the cell [66] . Such a complex would be very similar to bisphosphonates in that both molecules contain two phosphonyl groups. Glyphosate has been linked to multiple myeloma [67] and to multiple other cancers and therefore to chemotherapy [33] [34] , and there is strong support in the literature for glyphosate causing renal impairment [28] [43] . Low plasma proteins, such as serum albumin and transferrin, are associated with pulmonary vascular permeability [68] . A good indicator of systemic transvascular leaks is microalbuminurea [69] , and it is also linked with chronic kidney disease [70] .

There is a plausible link among jaw necrosis, pancreatitis, and adrenal insufficiency. Salivary albumin levels are elevated in association with frailty in the elderly [71] , and this suggests loss of albumin through vascular leakage eventually terminating in the saliva (as a mechanism to export the toxic chemicals bound to albumin?). Autoimmune chronic pancreatitis is associated with impaired biliary flow and salivary gland dysfunction, and is treatable with corticosteroids, suggesting a role for adrenal insufficiency [72] . Adrenal insufficiency is also common in association with acute pancreatitis [73] [74] . In a prospective cohort study on patients with biliary pancreatitis, insufficient adrenal cortisol secretion, i.e., primary adrenal insufficiency, in response to a corticotropin stimulus was strongly correlated with severity of disease and mortality risk [75] . One third of the patients in the study suffered from adrenal insufficiency.

In vitro studies have suggested that glyphosate binds to serum albumin [76] , and so albumin lost from the blood through vascular leakage may be carrying glyphosate out of the vasculature into the tissues, including the salivary glands, where it could gain access to and harm the jaw, perhaps through a bisphosphonate-like mechanism. SALIVARY GLAND DISORDER was highly over-represented in the adrenal insufficiency dataset, with a score of 958. Glyphosate exposure has been shown to negatively impact the salivary glands. In a study where mice were exposed to glyphosate via their feed, the weight of the salivary glands, especially the parotid gland, increased significantly following exposure to glyphosate, and this was associated with cytoplasmic changes of acinar cells (basophilic change, fine vacuolation, swelling, and loss of the normal periodic acid-Schiff (PAS)- positive reactivity of the secretory granules) [77] . Industry-sponsored toxicology reports for glyphosate often mention salivary problems. These include excess and/or foamy salivation; cellular alterations, lesions, and enlargement of the salivary gland; ulceration of the tongue and oral mucosa [78] .

Acinar cells are also implicated in pancreatic toxicity due to glyphosate. Diseases of the pancreas were highly over-represented in the adrenal insufficiency subset of the kidney failure dataset, including CHRONIC PANCREATITIS (820) and PANCREATIC CARCINOMA (833). Excessive stimulation of pancreatic acinar cells activates trypsin synthesis and the production of cytokines, both of which result in cellular damage [79] . Acinar cell damage has been implicated in glyphosate exposure in multiple studies involving rodents [80] , and acinar cell carcinoma is the second most common type of pancreatic cancer [81] . The incidence of pancreatic cancer is sharply on the rise in step with glyphosate usage on corn and soy crops (R = 0.918, p < 4.6E−7) [32] . Glyphosate, in a monotonic dose-response relationship, substantially increased the levels of digestive enzymes, including trypsin, chymotrypsin, amylase and acid protease, in the gut of fish exposed to low doses [82] .

4.1. Evidence of Glyphosate Contamination in Specific HDA DRUGS

RED BLOOD CELLS, PLATELETS, SERUM ALBUMIN, PLASMA: Glyphosate contamination in blood products is plausible. There is no question that ingested glyphosate can cross the gut barrier. A study of 13 cases of acute glyphosate toxicity in humans confirmed that ingested glyphosate penetrates past the gut barrier and infiltrates the blood. Glyphosate was found present in the blood in all 13 cases, with the highest detected level being 7480 mg/L for one of the fatal cases [83] . A study by Krüger et al. in 2014 showed that humans in Europe have detectable amounts of glyphosate in their urine, and those consuming an organic diet had less than those eating conventional food [9] . Since red blood cells, platelets and serum albumin are all blood products, they can be expected to sometimes be contaminated with glyphosate, given its pervasiveness in our food supply. Studies have shown that glyphosate likely binds to serum albumin [76] .

There are many different potential adverse reactions to transfusion, most of which probably have nothing to do with glyphosate contamination. However, one that is of special interest to us in the context of our studies is acute hypotensive transfusion reaction (AHTR). It is characterized by an abrupt drop in blood pressure along with haemolysis and acute lung injury. Sometimes, hypotension is the only manifestation. Angiotensin-con- verting enzyme inhibitors (ACE inhibitors) may have a synergistic role, likely because they also reduce blood volume [84] . In a typical case study of a 12 year-old girl, blood pressure began to drop during the transfusion, and an increase in the rate of transfusion to try to maintain blood pressure only made the situation worse. Brain swelling and diffuse oozing followed, with red blood cells appearing in the urine 30 minutes later. It was confirmed that there were no blood incompatibilities. [85] .

Up to half of the critically ill children in pediatric intensive care units receive at least one red blood cell transfusion, often due to severe anaemia. Low serum transferrin levels are especially problematic when packed RBC units are delivered intravenously, especially in the case of premature babies, and particularly following long-term storage [86] -[88] , Oxidized free heme accumulates in the extracellular fluid of aged packed RBC units, while at the same time antioxidant defenses such as vitamin C and glutathione become depleted. The preparation process of these units involves the removal of most plasma proteins that could bind and sequester iron, such as transferrin and albumin.

However, RBC transfusions can also cause an acute reaction independent of storage time. A study by Reddy et al. in 2011 of 100 critically ill pediatric patients found that 20% of those administered red blood cells experienced an adverse reaction resulting in extravascular haemolysis, linked to an increase in the acute phase response, along with excess free (non-transferrin-bound) iron associated with high serum bilirubin, indicative of haemolysis [89] . They tested for and ruled out any relationship with the length of storage of the transfusion [89] . Hyperbilirubinemia was strongly correlated with the HDA DRUGS in our analysis, suggesting that red blood cells are incurring damage. Glyphosate has been shown to cause severe damage to exposed red blood cells, both in in vivo studies on fish [90] and in vitro studies on human red blood cells [91] . Red blood cells depend on glucose-6-phosphate dehydrogenase (G6PD) to maintain the antioxidant glutathione in the reduced state, and glyphosate has been shown to suppress G6PD activity in experiments on E. coli [92] and on goldfish [93] . Glyphosate can be expected to lead to free serum iron and depleted antioxidant proteins due in part to its destructive effect on red blood cells [90] and human cell membranes [94] .

Sickle cell disease (SCD) is the most prevalent inherited disorder in African Americans [95] . RBC transfusion is the cornerstone treatment for complications of SCD [96] , and most patients require blood transfusions starting in early childhood [97] . Fatal pulmonary complications, including interstitial abnormalities, impaired pulmonary function, and pulmonary hypertension, are a significant cause of mortality associated with SCD [98] [99] . The mechanism leading to pulmonary hypertension is unknown and typically explained as “multifactorial” [100] . In a study in a single hospital in the U.S. of 141 patient deaths from SCD between 1976 and 2001, it was noted that pulmonary hypertension as cause of death was more than twice as common after 1992 (36.2%) compared to before 1992 (16.6%) (P < 0.01) [95] . This temporal increase could be explained by increased glyphosate residue in the transfusions. INTERSTITIAL LUNG DISEASE (736), PULMONARY OEDEMA (769) and PULMONARY HYPERTENSION (854) were all significantly over-represented in the adrenal insufficiency dataset.

HEPARIN and TRASYLOL: Pharmaceutical-grade heparin is derived from mucosal tissues of slaughtered animals such as pig intestines and bovine lungs [37] . Both pigs and cattle are typically fed genetically engineered RR corn and soy feed, particularly in the US. Studies on glyphosate contamination in chickens found the highest concentrations in the gut, as might be expected given the oral source. But the second-highest levels were found in the lungs [101] . Interestingly, a study on cows in Germany and Denmark found the highest levels in the lungs, with glyphosate showing up in all the organs tested [9] . Monsanto’s own studies showed that radioactively labelled carbon in orally administered glyphosate can be recovered from carbon dioxide in the expelled breath [102] . We hypothesize that the high scores for multiple lung disorders associated with the adrenal insufficiency subset links to chronic glyphosate poisoning in the lungs. Heparin is a highly cationic peptide, which increases its likelihood of electrostatic binding to the negatively charged molecule, glyphosate.

Trasylol® (aprotinin) is a natural protease inhibitor obtained from bovine lung, administered intravenously. Hydrochloric acid and/or sodium hydroxide is used to adjust the pH to 4.5 - 6.5. These buffering agents will increase the solubility of glyphosate, increasing the likelihood of its contamination due to glyphosate residues in the lung tissues. It is even likely that aprotinin expression is stimulated in the cow in the context of glyphosate exposure, due to the release of trypsin by the pancreas and its escape into the lung tissue following vascular leaks, as will be more fully discussed later in this paper.

PROTAMINE SULFATE: Protamine is used increasingly to reverse heparin anticoagulation during cardiac catheterization, vascular surgery procedures, dialysis, and leukapheresis. Protamine sulfate is a basic protein extracted from fish sperm heads, mainly sturgeon and salmon [103] , although in recent years recombinant technology through microbial cultures such as E. coli is increasingly being used [104] [105] . We discussed in the introduction studies showing anomalous reactions to protamine sulfate therapy involving lung complications and a high risk of death [24] [25] .

Iran has been the second-highest producer of sturgeon-derived products, coming mainly from fish living in the Caspian Sea. However, the native sturgeon population has declined by 90% over the past three decades, and all sturgeon species in the Caspian Sea are now critically endangered. Coastal habitats are being widely exposed to herbicides, especially glyphosate, from large farms and paddy fields nearby [106] . Glyphosate is acutely toxic to fish [107] . Reproductive failure due to glyphosate exposure is hypothesized to be an important contributor to their decline in the Caspian Sea [106] . It is therefore not unreasonable to suppose that products derived from sturgeon testes might be contaminated with glyphosate.

Recombinant methods are also not necessarily free from glyphosate contamination. There is no awareness that glyphosate might be an issue, and so it remains an open question as to whether the medium on which the microbes are grown might contain glyphosate. A highly productive choice for nutrition for the microbes to induce high yield of the recombinant protein is a mixture of glucose, lactose and glycerol [104] [105] . Glucose could be obtained from GM RR sugar beets, or sugar cane sprayed with Roundup® right before the harvest, or from high fructose corn syrup derived from RR corn. Lactose is derived from milk, likely produced by cows exposed to high doses of glyphosate in their GM corn and soy feed. Glycerol is now a major by-product of the production of biofuel from soybeans, and most of the soybeans grown in the US are genetically engineered to be glyphosate resistant, and therefore highly exposed to glyphosate.

NITROGLYCERIN and VANCOMYCIN: Nitroglycerin and vancomycin were the weakest of the HDA DRUGS in terms of their score for association with death. Nitroglycerin is administered in multiple ways, including as an intravenous solution, a transdermal patch, and sublingual sprays and tablets. Vancomycin must be given intravenously for systemic therapy, since it is not absorbed from the intestine. Nitroglycerin is an antihypertensive agent that releases nitric oxide, a vasoactive gas that relaxes the vessel wall. An antihypertensive agent might work synergistically with glyphosate to increase risk in a situation where blood pressure is dropping precipitously.

Vancomycin is a popular antibiotic that’s most effective against gram-positive bacteria. A known adverse effect of vancomycin, in less than 1% of patients, is thrombocytopenia. Confirming this adverse reaction, we obtained highly significant scores of 762 for THROMBOCYTOPENIA and 916 for ESSENTIAL THROMBO- CYTHAEMIA, when comparing a subset of our HDA DRUGS dataset where vancomycin was the ONLY HDA DRUG present to the opposing set where vancomycin was not among the HDA DRUGS. Nephrotoxicity is another issue with VANCOMYCIN, and we obtained a score of 908 for “NEPHROPATHY TOXIC” when comparing these two sets.

Since it is not obvious how these two drugs might be contaminated with glyphosate, we hypothesize that their link to DEATH may be through other mechanisms directly linked to the drug’s biological effects. However, the highly significant scores for the known side effects of these drugs show that our method has merit.

VERSED: VERSED, a benzadiazepine, is a low-toxicity drug, and it is therefore anomalous on the HDA DRUGS list. It is often used as a premedication for sedation, and it is likely that surgery is commonly associated with “DEATH” as an outcome. Therefore, it may be “guilty by association” with the other death-related drugs. We can easily test this by separating out those events where VERSED, but none of the other HDA DRUGS, was administered. This occurred in only 399 of the HDA DRUG events (out of 43,434) (fewer than 1%). When these 399 events are compared with the remainder of the HDA DRUG events, all of the side effects that were linked to death (see Table 3) get a score < 500, meaning that they are under-represented in association with VERSED only. Therefore, we highly suspect that VERSED is anomalously tagged as an HDA DRUG. It is probably highly significant that “UNEVALUABLE EVENT” was hugely under-represented with VERSED only: the number of cases was more than 12-fold fewer than would be predicted based on the frequency in the other HDA DRUG events.

4.2. Possible Biological Mechanisms

It should be clear by now that we are proposing two ideas in this paper: (1) People are chronically exposed to glyphosate in their food and water, and this is leading to a disease profile that is captured in our adrenal insufficiency dataset linked to kidney failure, and (2) Certain biological pharmaceuticals may be contaminated with glyphosate which is inadvertently administered intravenously, leading to an acute symptom profile that is quite distinct from the one resulting from chronic glyphosate exposure.

Our research has led us to propose a hypothesis for a systemic reaction to chronic glyphosate exposure from food and water. This reaction likely initiates with pancreatitis, leading to a leaky vasculature due in part to increased trypsin synthesis, resulting in the escape of blood plasma along with trypsin and glyphosate, likely bound to serum albumin, into the extracellular space. This causes chronic damage to multiple organs, but spares the vasculature and the kidneys. It follows that death as a side effect is more likely when glyphosate exposure is concurrent with drugs that protect from haemorrhage, such as Trasylol® and protamine sulfate, due to the fact that glyphosate stays in the blood and fatally damages the kidneys.

GGT, Adrenal Insufficiency, Vitamin C Deficiency and Pancreatitis: Multiple studies on plants have demonstrated that glyphosate induces glutathione-S-transferase activity [108] -[110] . It is not clear that glyphosate itself is detoxified through glutathionylation, but, rather, it is perhaps more likely that glyphosate interferes with other conjugations of xenobiotics in general, such as with sulfate or glucuronate, that depend on CYP enzymes, leaving glutathionylation as the preferred pathway for detoxification when CYP enzymes are suppressed. This will also lead over time to a depletion of glutathione bioavailability in the liver, a source of oxidative stress.

Gamma glutamyltransferase (GGT) is a widely expressed enzyme, especially in the liver. Since GGT is needed to break down glutathionylated xenobiotics, such as polycyclic aromatic hydrocarbons [111] , it can be expected to be induced in the presence of glutathionylated xenobiotics. Increased GGT expression is linked to glyphosate through multiple animal studies. Its over-expression is associated with many diseases related to hepatobiliary and pancreatic disorders [112] -[114] . Kids born from goats fed GM RR soy had elevated liver expression of GGT [115] . GGT was found to be enhanced up to 5.4-fold in the liver in Séralini et al.’s long-term study of rats exposed to GMO’s plus Roundup® [43] . Lum and Gambino found extremely high levels of GGT in cases of acute pancreatitis, primary carcinoma of the head of the pancreas, and adenocarcinoma of the bile duct [113] . GGT levels were higher than the upper limit of normal for 100% of cases of pancreatitis, with an average value of ten times the upper limit.
A retrospective study on over half a million hospitalized cancer patients, between 1995 and 2003, showed that the administration of both red blood cells and platelets led to increased risk to thrombosis and death compared to no transfusion [116] . It was proposed that a factor could be the presence of redox-active iron in the transfusion, leading to an increase in iron-catalyzed free radical-mediated oxidative stress [117] . Elevated GGT would greatly enhance this effect, because GGT has a pro-oxidant effect by promoting iron reduction and the peroxidation of lipids [118] [119] .

21-Hydroxylase is a CYP enzyme that catalyzes the synthesis of cortisol and aldosterone in the adrenal glands. Women with adrenal insufficiency due to 21-hydroxylase deficiency generally have elevated expression of GGT, along with increased risk to non-alcoholic fatty liver disease [120] . This may be linked to a deficiency in ascorbate. The adrenal glands have an unusually high concentration of ascorbate, which is a cofactor both in catecholamine biosynthesis and in steroidogenesis [121] . It also plays an essential role in protecting them from oxidative damage. Red blood cells use a glutathione-dependent dehydroascorbate reductase to maintain vitamin C in the reduced state in the vasculature, and this function could be impaired in the presence of glyphosate, due to both glutathione depletion and oxidative stress. Furthermore, the suppression of G6PD by glyphosate impairs the glucose-mediated reducing capacity of RBCs [92] [93] . The liver also reduces dehydroascorbate to ascorbate, but this burden induces loss of glutathione and oxidative stress as well [122] .

The symptoms of severe vitamin C deficiency (scurvy) were listed in [123] as “anorexia, anaemia, arthralgia, bleeding gums, coiled hair, depression, dry eyes and mouth (Sjögren’s Syndrome), ecchymosis, follicular hyperkeratosis, fatigue, frequent infections, impaired wound healing, inflamed gums, joint effusions, myalgia, muscle weakness, perifollicular hemorrhages, and petechiae.” We found 51 side effects that were highly over-repre- sented in the adrenal insufficiency dataset which collectively matched with all of the above symptoms except coiled hair: scores for all but 5 of them were above 900, and those 5 were all above 800.

Pancreatitis and Trypsin: Acute pancreatitis has been observed in a case study of a reaction to glyphosate exposure through a suicide attempt [124] . Pancreatitis on the first day was followed by chemical pneumonitis and respiratory failure, likely due in part to the release of glyphosate into the pleural cavity, along with blood plasma and serum proteins. Acute haemorrhagic pancreatitis induces increased lung vascular permeability, an effect that is linked to overexpression of proteases such as trypsin [125] . Trypsin induces platelet activation [126] , and platelet-rich blood clots release cytokines and inflammatory mediators such as vascular endothelial growth factor, which can increase capillary permeability leading to exudative pleural effusion [127] . The cytokines, interleukin-1β (IL-1β) and interferon γ (IFN-γ) have been shown to significantly increase vascular permeability, allowing neutrophils to penetrate the endothelial layer [128] .

Pretreatment with Trasylol® protects from this effect of trypsin [125] [129] , making it attractive in the context of open heart surgery. Tahamont et al. [129] proposed that the increases in pulmonary lymph flow and transvascular protein clearance after pancreatitis is the result of the release of proteases such as trypsin. They wrote: “The release of proteases into the circulation after acute pancreatitis may be the initiating event mediating the pulmonary vascular injury” ( [129] , p. 15). Trasylol® protects more generally from exudative pleural effusion. In a study on dogs with experimentally induced myocardial infarction, it was demonstrated that Trasylol® administered 30 minutes after ligation with cobra venom factor significantly reduces the inflammatory response and tissue exudate in the myocardium [130] [131] .

Astonishingly, if we compare counts for all side effects related to pancreatitis and pancreatic cancer between HDA DRUGS not including TRASYLOL and HDA DRUGS including TRASYLOL, we get a score of 994; i.e., pancreatic dysfunction is hugely over-represented in the HDA DRUGS when TRASYLOL is omitted. What is most interesting, however, is that TRASYLOL-containing HDA DRUG events are much more strongly linked to DEATH, with a score of 934, when compared to HDA DRUGS omitting TRASYLOL. This suggests to us that protection from vascular leakage and haemorrhage in the context of glyphosate poisoning is very risky, because it prevents the escape of glyphosate from the blood and results in kidney injury leading to death.

Pathological Sequelae Leading to Death: Thus, a story emerges from the data analysis we have performed, and it suggests that a signaling cascade launched by pancreatitis leads to pancreatic release of digestive enzymes, which then both degrade ACTH [132] and erode the vascular wall in the major vessels sufficiently to induce migration of serum and even whole blood into the pleural and abdominal cavities. The loss of ACTH can plausibly induce secondary adrenal insufficiency, whereas primary adrenal insufficiency develops in part due to Roundup®’s suppression of StAR and reduced supply of ascorbate. The intended use of the anti-trypsin agent, aprotinin (Trasylol®) is to break down trypsin only after it has breached the artery wall. This is sensible in order to prevent trypsin from digesting lung tissue and causing major damage to the lung. Administering of Trasylol® intravenously during open heart surgery has the desired effect of preventing the escape of blood into the pleural cavity during the operation by neutralizing the trypsin while it is still in the arteries, but this then does not protect the glomeruli from a high dose of the toxic chemical that launched the signaling cascade in the first place. Thus, while multiple organs, such as the lungs, the gut, the bones, the skin, the brain, the eyes, the ears, etc., are spared, the kidney suffers acute injury and the patient has a much higher chance of death as an outcome.

If we are right, then there is good news in that Trasylol® and heparin could be sourced from grass fed cows rather than cows fed GM RR corn and soy feed. Trasylol® may be an outstanding drug for protection from haemorrhage during open heart surgery if we can prevent the rare acute reaction leading to death that may in fact be largely due to a contaminant rather than to the drug itself.

We end this section with a quote from a recent paper discussing data mining from FAERS: “A report in the FAERS database is a story, sometimes only a rumor, but numerous reports can reflect reality. With larger numbers of faithful reports, the FAERS database and other spontaneously reported databases should help to optimize pharmacotherapy.” ( [133] , p. 6). We hope that the analysis we report here will lead to further investigation into the theory we have presented concerning glyphosate exposure in food and drugs.

5. Conclusions

In this paper, we have presented evidence that a toxic chemical contamination might explain the high risk of death as a side effect associated with certain biologically derived drugs, including multiple blood products as well as drugs extracted from bovine lung and sturgeon testes. We theorize that the contaminant causing this acute reaction is glyphosate, the active ingredient in Roundup®. We show that events in FAERS which include drugs that are strongly linked to death exhibit side effects that are well correlated with symptoms related to glyphosate toxicity in suicide attempts as well as to a rare but unique reaction to protamine sulfate. This reaction is highly reminiscent of the reaction of piglets exposed to glyphosate salts intravenously [26] . From this we hypothesize that these biologically derived drugs may be contaminated with glyphosate and it is the glyphosate that is causing the acute reactions. We further hypothesize that glyphosate adjuvants such as POEA and various toxic metals, including iron, aluminum and cadmium, may play a synergistic role.

Based on knowledge that glyphosate is causative in kidney failure, we undertook a separate investigation into the subset of the FAERS database with renal failure as one of the symptoms. This yielded interesting insight into the underlying pathology associated with chronic kidney disease. By separating the renal failure dataset into two contrastive subgroups, we are able to show that adrenal insufficiency characterizes a chronic form of kidney failure that we believe is a reflection of chronic glyphosate exposure from food sources. Symptoms of diseases whose rising frequency over time correlates with the rising use of glyphosate on corn and soy crops were well- matched with the adrenal insufficiency dataset. We note that those side effects related to glyphosate toxicity that are under-represented in our HDA DRUGS database are linked to gut dysbiosis, and we suggest that the intravenous route rather than the oral route serves to minimize gut exposure.

We have developed a hypothesis to explain the symptom patterns observed in the context of kidney failure and adrenal insufficiency. We propose that the pancreas is highly susceptible to damage from glyphosate, and that pancreatitis induces vascular leakage mediated by trypsin over-expression and platelet activation. Vascular leakage results in a flushing of blood products, including glyphosate, into the pleural and abdominal cavities, causing conditions such as pulmonary oedema and ascites. The two drugs that were most strongly linked to death as an outcome, Trasylol® and protamine sulfate, both are administered to protect from haemorrhage. They therefore interfere with the flushing of glyphosate into the tissues, sparing the lungs, gut, skin, heart, brain and other organs from major damage, but ultimately leading to an increased risk to death due to kidney failure.

Acknowledgements

This work was funded in part by Quanta Computers, Taiwan, under the auspices of the Qmulus Project. We thank Marlene Beggelman, Bob Davidson, Ann Lauritzen, Judy Hoy, James Beecham, Steve Kette and Anthony Samsel for insightful discussion related to this work.

Conflicts of Interest

The authors declare no conflicts of interest.

References

[1] Nuckols, T.K., Paddock, S.M., Bower, A.G., Rothschild, J.M., Fairbanks, R.J., Carlson, B., Panzer, R.J. and Hilborne, L.H. (2008) Costs of Intravenous Adverse Drug Events in Academic and Nonacademic Intensive Care Units. Medical Care, 46, 17-24.
http://dx.doi.org/10.1097/MLR.0b013e3181589bed
[2] Lazarou, J., Pomeranz, B.H. and Corey, P.N. (1998) Incidence of Adverse Drug Reactions in Hospitalized Patients: A Meta-Analysis of Prospective Studies. The Journal of the American Medical Association, 279, 1200-1205.
http://dx.doi.org/10.1001/jama.279.15.1200
[3] Majewski, M.S., Coupe, R.H., Foreman, W.T. and Capel, P.D. (2014) Pesticides in Mississippi Air and Rain: A Comparison between 1995 and 2007. Environmental Toxicology and Chemistry, 33, 1283-1293.
http://dx.doi.org/10.1002/etc.2550
[4] Chang, F.C., Simcik, M.F. and Capel, P.D. (2011) Occurrence and Fate of the Herbicide Glyphosate and Its Degradate Aminomethylphosphonic Acid in the Atmosphere. Environmental Toxicology and Chemistry, 30, 548-555.
[5] Scribner, E.A., Battaglin, W.A., Gilliom, R.J. and Meyer, M.T. (2007) Concentrations of Glyphosate, Its Degradation Product, Aminomethylphophonic Acid, and Glufosinate in Ground- and Surface-Water, Rainfall, and Soil Samples Collected in the United States, 2001-06S. Geological Survey Scientific Investigations Report 2007-5122.
[6] Coupe, R.H., Kalkhoff, S.J., Capel, P.D. and Gregoire, C. (2012) Fate and Transport of Glyphosate and Aminomethylphosphonic Acid in Surface Waters of Agricultural Basins. Pest. Management Science, 68, 16-30.
http://dx.doi.org/10.1002/ps.2212
[7] Mercurio, P., Flores, F., Mueller, J.F., Carter, S. and Negri, A.P. (2014) Glyphosate Persistence in Seawater. Marine Pollution Bulletin, 85, 385-390.
http://dx.doi.org/10.1016/j.marpolbul.2014.01.021
[8] Aris, A. and Leblanc, S. (2011) Maternal and Fetal Exposure to Pesticides Associated to Genetically Modified Foods in Eastern Townships of Quebec, Canada. Reproductive Toxicology, 31, 528-533.
http://dx.doi.org/10.1016/j.reprotox.2011.02.004
[9] Krüger, M., Schledorn, P., Schrödl, W., Hoppe, H.-W., Lutz, W. and Shehata, A.A. (2014) Detection of Glyphosate Residues in Animals and Humans. Journal of Environmental & Analytical Toxicology, 4, 2.
[10] Lanaro, R., Costa, J.L., Cazenave, S.O., Zanolli-Filho, L.A., Tavares, M.F. and Chasin, A.A. (2015) Determination of Herbicides Paraquat, Glyphosate and Aminomethylphosphonic Acid in Marijuana Samples by Capillary Electrophoresis. Journal of Forensic Sciences, 60, S241-S247.
http://dx.doi.org/10.1111/1556-4029.12628
[11] Flaum, I. (1977) Contamination of Pharmaceutical Products. Journal of Pharmaceutical Sciences, 67, 1-11.
http://dx.doi.org/10.1002/jps.2600670104
[12] Dunsmuir, L. (2015) Tylenol Maker to Pay $25 mln for Selling Metal-Contaminated Drugs. Reuters Press, March 10. Last accessed September 10, 2015.
http://www.reuters.com/article/2015/03/10/johnson-johnson-tylenol-idUSL1N0WC2E420150310
[13] Royston, D., Bidstrup, B.P., Taylor, K.M. and Sapsford, R.N. (1987) Effect of Aprotinin on Need for Blood Transfusion after Repeat Open-Heart Surgery. The Lancet, 2, 1289-1291.
http://dx.doi.org/10.1016/S0140-6736(87)91190-1
[14] Ray, W.A. and Stein, C.M. (2008) The Aprotinin Story—Is BART the Final Chapter? The New England Journal of Medicine, 358, 2398-2400.
http://dx.doi.org/10.1056/NEJMe0803514
[15] Mangano, D.T., Tudor, I.C. and Dietzel, C. (2006) The Risk Associated with Aprotinin in Cardiac Surgery. The New England Journal of Medicine, 354, 353-365.
http://dx.doi.org/10.1056/NEJMoa051379
[16] Mangano, D.T., Miao, Y., Vuylsteke, A., Tudor, I.C., Juneja, R., Filipescu, D,, Hoeft, A., Fontes, M.L., Hillel, Z., Ott E, Titov, T., Dietzel, C. and Levin, J., Investigators of the Multicenter Study of Perioperative Ischemia Research Group and Ischemia Research and Education Foundation (2007) Mortality Associated with Aprotinin during 5 Years Following Coronary Artery Bypass Graft Surgery. The Journal of the American Medical Association, 297, 471-479.
[17] Schneeweiss, S., Seeger, J.D., Landon, J. and Walker, A.M. (2008) Aprotinin during Coronary-Artery Bypass Grafting and Risk of Death. The New England Journal of Medicine, 358, 771-783.
http://dx.doi.org/10.1056/NEJMoa0707571
[18] Shaw, A.D., Stafford-Smith, M., White, W.D., Phillips-Bute, B., Swaminathan, M.D., Milano, C., Welsby, I.J., Aronson, S., Mathew, J.P., Peterson, E.D. and Newman, M.F. (2008) The Effect of Aprotinin on Outcome after Coronary-Artery Bypass Grafting. The New England Journal of Medicine, 358, 784-793.
http://dx.doi.org/10.1056/NEJMoa0707768
[19] Dietrich, W., Busley, R. and Boulesteix, A.L. (2008) Effects of Aprotinin Dosage on Renal Function: An Analysis of 8,548 Cardiac Surgical Patients Treated with Different Dosages of Aprotinin. Anesthesiology, 108, 189-198.
http://dx.doi.org/10.1097/01.anes.0000299428.55062.67
[20] Fergusson, D.A., Hébert, P.C., Mazer, C.D., Fremes, S., MacAdams, C., Murkin, J.M., Teoh, K., Duke, P.C., Arellano, R., Blajchman, M.A., Bussiéres, J.S., Côté, D., Karski, J., Martineau, R., Robblee, J.A., Rodger, M., Wells, G., Clinch, J. and Pretorius, R., BART Investigators (2008) A Comparison of Aprotinin and Lysine Analogues in High-Risk Cardiac Surgery. The New England Journal of Medicine, 358, 2319-2331.
http://dx.doi.org/10.1056/NEJMoa0802395
[21] Sedrakyan, A., Treasure, T. and Elefteriades, J.A. (2004) Effect of Aprotinin on Clinical Outcomes in Coronary Artery Bypass Graft Surgery: A Systematic Review and Meta-Analysis of Randomized Clinical Trials. The Journal of Thoracic and Cardiovascular Surgery, 128, 442-448.
http://dx.doi.org/10.1016/j.jtcvs.2004.03.041
[22] Schloss, B., Gulati, P., Yu, L., Abdel-Rasoul, M., O’Brien, W., Von Visger, J. and Awad, H. (2011) Impact of Aprotinin and Renal Function on Mortality: A Retrospective Single Center Analysis. Journal of Cardiothoracic Surgery, 6, 103.
http://dx.doi.org/10.1186/1749-8090-6-103
[23] EPA (2013) Electronic Code of Federal Regulations, Title 40: Protection of Environment. PART 180 Tolerances and Exemptions for Pesticide Chemical Residues in Food. Subpart C: Specific Tolerances. Environmental Protection Agency, Washington DC.
[24] Just-Viera, J.O., Fischer, C.R., Gago, O. and Morris, J.D. (1984) Acute Reaction to Protamine. Its Importance to Surgeons. The American Surgeon, 50, 52-60.
[25] Holland, C.L., Singh, A.K., McMaster, P.R.B. and Fang, D.W. (1984) Adverse Reactions to Protamine Sulfate Following Cardiac Surgery. Clinical Cardiology, 7, 157-162.
http://dx.doi.org/10.1002/clc.4960070305
[26] Lee, H.L., Kan, C.D., Tsai, C.L., Liou, M.J. and Guo, H.R. (2009) Comparative Effects of the Formulation of Glyphosate-Surfactant Herbicides on Hemodynamics in Swine. Clinical Toxicology (Philadelphia), 47, 651-658.
http://dx.doi.org/10.1080/15563650903158862
[27] Lee, H.L., K.W., Chen, Chi, C.H., J.J., Huang and Tsai, L.M. (2000) Clinical Presentations and Prognostic Factors of a Glyphosate-Surfactant Herbicide Intoxication: A Review of 131 Cases. Academic Emergency Medicine, 7, 906-910.
http://dx.doi.org/10.1111/j.1553-2712.2000.tb02069.x
[28] Jayasumana, C., Gunatilake, S. and Senanayake, P. (2014) Glyphosate, Hard Water and Nephrotoxic Metals: Are They the Culprits behind the Epidemic of Chronic Kidney Disease of Unknown Etiology in Sri Lanka? International Journal of Environmental Research and Public, 11, 2125-2147.
http://dx.doi.org/10.3390/ijerph110202125
[29] Pandey, A. and Rudraiah, M. (2015) Analysis of Endocrine Disruption Effect of Roundup in Adrenal Gland of Male Rats. Toxicology Reports, 2, 1075-1085.
http://dx.doi.org/10.1016/j.toxrep.2015.07.021
[30] Livingston, M., Fernandez-Cornejo, J., Unger, J., Osteen, C., Schimmelpfennig, D., Park, T. and Lambert, D. (2015) The Economics of Glyphosate Resistance Management in Corn and Soybean Production. U.S. Department of Agriculture, Economic Research Service, April 2015, No. ERR-184.
[31] Benbrook, C.B. (2012) Impacts of Genetically Engineered Crops on Pesticide Use in the U.S.—The First Sixteen Years. Environmental Sciences Europe, 24, 2190-4715.
[32] Swanson, N.L., Leu, A., Abrahamson, J. and Wallet, B. (2014) Genetically Engineered Crops, Glyphosate and the Deterioration of Health in the United States of America. Journal of Organic Systems, 9, 6-37.
[33] Guyton, K.Z., Loomis, D., Grosse, Y., El Ghissassi, F., Benbrahim-Tallaa, L., Guha, N., Scoccianti, C., Mattock, H. and Straif, K., The International Agency for Research on Cancer Monograph Working Group (2015) Carcinogenicity of Tetrachlorvinphos, Parathion, Malathion, Diazinon, and Glyphosate. The Lancet Oncology, 16, 490-491.
http://dx.doi.org/10.1016/s1470-2045(15)70134-8
[34] Samsel, A. and Seneff, S. (2015) Glyphosate, Pathways to Modern Diseases IV: Cancer and Related Pathologies. The Journal of Biological Physics and Chemistry, 15, 121-159.
http://dx.doi.org/10.4024/11sa15r.jbpc.15.03
[35] Hazell, L. and Shakir, S.A. (2006) Under-Reporting of Adverse Drug Reactions: A Systematic Review. Drug Safety, 29, 385-396.
http://dx.doi.org/10.2165/00002018-200629050-00003
[36] Kristeller, J.L., Roslund, B.P. and Stahl, R.F. (2008) Benefits and Risks of Aprotinin Use during Cardiac Surgery. Pharmacotherapy, 28, 112-124.
http://dx.doi.org/10.1592/phco.28.1.112
[37] Linhardt, R.J. and Gunay, N.S. (1999) Production and Chemical Processing of Low Molecular Weight Heparins. Seminars in Thrombosis and Hemostasis, 3, 5-16.
[38] Cericato. L., Neto, J.G., Fagundes, M., Kreutz, L.C., Quevedo, R.M., Finco, J., da Rosa, J.G., Koakoski, G., Centenaro, L., Pottker, E., Anziliero, D. and Barcellos, L.J. (2008) Cortisol Response to Acute Stress in Jundi Rhamdiaquelen Acutely Exposed to Sub-Lethal Concentrations of Agrichemicals. Comparative Biochemistry and Physiology C-Toxicology & Pharmacology, 148, 281-286.
[39] Walsh, L.P., McCormick, C., Martin, C. and Stocco, D.M. (2000) Roundup Inhibits Steroidogenesis by Disrupting Steroidogenic Acute Regulatory (StAR) Protein Expression. Environmental Health Perspectives, 108, 769-776.
http://dx.doi.org/10.1289/ehp.00108769
[40] Johnson, E.O., Vlachoyiannopoulos, P.G., Skopouli, F.N., Tzioufas, A.G. and Moutsopoulos, H.M. (1998) Hypofunction of the Stress Axis in Sjögren’s Syndrome. The Journal of Rheumatology, 25, 1508-1514.
[41] Samsel, A. and Seneff, S. (2013) Glyphosate’s Suppression of Cytochrome P450 Enzymes and Amino Acid Biosynthesis by the Gut Microbiome: Pathways to Modern Diseases. Entropy, 15, 1416-1463.
http://dx.doi.org/10.3390/e15041416
[42] Mesnage, R., Arno, M., Costanzo, M., Malatesta, M., Séralini, G.-E. and Antoniou, M.N. (2015) Transcriptome Profile Analysis Reflects Rat Liver and Kidney Damage Following Chronic Ultra-Low Dose Roundup Exposure. Environmental Health, 14, 70.
http://dx.doi.org/10.1186/s12940-015-0056-1
[43] Séralini, G.-E., Clair, E., Mesnage, R., Gress, S., Defarge, N., Malatesta, M., Hennequin, D. and Spiroux de Vendômois, J. (2014) Republished Study: Long-Term Toxicity of a Roundup Herbicide and a Roundup-Tolerant Genetically Modified Maize. Environmental Sciences Europe, 26, 14.
http://dx.doi.org/10.1186/s12302-014-0014-5
[44] Walker, D.L. and Davis, M. (2002) The Role of Amygdala Glutamate Receptors in Fear Learning, Fear-Potentiated Startle and Extinction. Pharmacology Biochemistry and Behavior, 71, 379-392.
http://dx.doi.org/10.1016/s0091-3057(01)00698-0
[45] Falls, W.A., Miserendino, M.J. and Davis, M. (1992) Extinction of Fear-Potentiated Startle: Blockade by Infusion of an NMDA Antagonist into the Amygdala. The Journal of Neuroscience, 12, 854-863.
[46] Wilcox, K.S., Fitzsimonds, R.M., Johnson, B. and Dichter, M.A. (1996) Glycine Regulation of Synaptic NMDA Receptors in Hippocampal Neurons. Journal of Neurophysiology, 76, 3415-3424.
[47] Cattani, D., de Liz Oliveira Cavalli, V.L., Heinz Rieg, C.E., Domingues, J.T., Dal-Cim, T., Tasca, C.I., Mena Barreto Silva, F.R. and Zamoner, A. (2014) Mechanisms Underlying the Neurotoxicity Induced by Glyphosate-Based Herbicide in Immature Rat Hippocampus: Involvement of Glutamate Excitotoxicity. Toxicology, 320, 34-45.
http://dx.doi.org/10.1016/j.tox.2014.03.001
[48] Samsel, A. and Seneff, S. (2015) Glyphosate, Pathways to Modern Diseases III: Manganese Neurological Diseases, and Associated Pathologies. Surgical Neurology International, 6, 45.
[49] Bohrer, D., do Nascimento, P.C., Binotto, R. and Pomblum, S.C. (2001) Influence of the Glass Packing on the Contamination of Pharmaceutical Products by Aluminium. Part I: Salts, Glucose, Heparin and Albumin. Journal of Trace Elements in Medicine and Biology, 15, 95-101.
http://dx.doi.org/10.1016/S0946-672X(01)80050-X
[50] Seneff, S., Swanson, N. and Li, C. (2015) Aluminum and Glyphosate Can Synergistically Induce Pineal Gland Pathology: Connection to Gut Dysbiosis and Neurological Disease. Agricultural Science, 6, 42-70.
http://dx.doi.org/10.4236/as.2015.61005
[51] Alfrey, A.C. (1993) Aluminum Toxicity in Patients with Chronic Renal Failure. Therapeutic Drug Monitoring, 15, 593-597.
http://dx.doi.org/10.1097/00007691-199312000-00025
[52] Mayor, G.H., Sprague, S.M., Hourani, M.R. and Sanchez, T.V. (1980) Parathyroid Hormone-Mediated Aluminum Deposition and Egress in the Rat. Kidney International, 17, 40-44.
http://dx.doi.org/10.1038/ki.1980.5
[53] Cozzolino, M., Brancaccio, D., Gallieni, M., Galassi, A., Slatopolsky, E. and Dusso, A. (2005) Pathogenesis of Parathyroid Hyperplasia in Renal Failure. Journal of Nephrology, 18, 5-8.
[54] Sinha, P.K., Mandal, S. and Kundu, D. (2007) Leaching of Lead and Cadmium from Glass Dinnerware. Journal of Environmental Science and Engineering, 49, 58-61.
[55] Wanigasuriya, K.P., Peiris-John, R.J. and Wickremasinghe, R. (2011) Chronic Kidney Disease of Unknown Aetiology in Sri Lanka: Is Cadmium a Likely Cause? BMC Nephrology, 12, 32.
http://dx.doi.org/10.1186/1471-2369-12-32
[56] Sughis, M., Penders, J., Haufroid, V., Nemery, B. and Nawrot, T.S. (2011) Bone Resorption and Environmental Exposure to Cadmium in Children: A Cross-Sectional Study. Environmental Health, 10, 104.
http://dx.doi.org/10.1186/1476-069X-10-104
[57] Bawaskar, H.S., Bawaskara, P.H. and Bawaskara, P.H. (2010) Chronic Renal Failure Associated with Heavy Metal Contamination of Drinking Water: A Clinical Report from a Small Village in Maharashtra. Clinical Toxicology, 48, 768-769.
http://dx.doi.org/10.3109/15563650.2010.497763
[58] Mesnage, R., Bernay, B. and Séralini, G.-E. (2013) Ethoxylated Adjuvants of Glyphosate-Based Herbicides Are Active Principles of Human Cell Toxicity. Toxicology, 313, 122-128.
http://dx.doi.org/10.1016/j.tox.2012.09.006
[59] Mesnage, R., Defarge, N., Spiroux de Vendômois, J. and Séralini, G.-E. (2014) Major Pesticides Are More Toxic to Human Cells than Their Declared Active Principles. BioMed Research International, 2014, Article ID: 179691.
http://dx.doi.org/10.1155/2014/179691
[60] Moon, J.M. and Chun, B.J. (2010) Predicting Acute Complicated Glyphosate Eintoxication in the Emergency Department. Clinical Toxicology, 48, 718-724.
http://dx.doi.org/10.3109/15563650.2010.488640
[61] Roberts, D.M., Buckley, N.A., Mohamed, F., Eddleston, M.E., Goldstein, D.A., Mehrsheikh, A., Bleeke, M.S. and Dawson, A.H. (2010) A Prospective Observational Study of the Clinical Toxicology of Glyphosate-Containing Herbicides in Adults with Acute Self-Poisoning. Clinical Toxicology, 48, 129-136.
http://dx.doi.org/10.3109/15563650903476491
[62] Sato, C., Kamijo, Y., Yoshimura, K. and Ide, T. (2011) Aseptic Meningitis in Association with Glyphosate-Surfactant Herbicide Poisoning. Clinical Toxicology (Philadelphia), 49, 118-120.
http://dx.doi.org/10.3109/15563650.2011.552065
[63] Komuro, J., Kaneko, M., Ueda, K., Nitta, S., Kasao, M. and Shirai, T. (2015) Adrenal Insufficiency Causes Life-Threatening Arrhythmia with Prolongation of QT Interval. Heart and Vessels, Epub ahead of Print.
http://dx.doi.org/10.1007/s00380-015-0660-6
[64] Carter, G., Goss, A.N. and Doecke, C. (2005) Bisphosphonates and Avascular Necrosis of the Jaw: A Possible Association. Medical Journal of Australia, 182, 413-415.
[65] Bagan, J., Sáez, G.T., Tormos, M.C., Gavalda-Esteve, C., Bagan, L., Leopoldo-Rodado, M. and Camps, C. (2014) Oxidative Stress in Bisphosphonate-Related Osteonecrosis of the Jaws. Journal of Oral Pathology & Medicine, 43, 371-377.
http://dx.doi.org/10.1111/jop.12151
[66] Rodan, G.A. and Fleisch, H.A. (1996) Bisphosphonates: Mechanisms of Action. The Journal of Clinical Investigation, 97, 2692-2696.
http://dx.doi.org/10.1172/JCI118722
[67] De Roos, A.J., Blair, A., Rusiecki, J.A., Hoppin, J.A., Svec, M., Dosemeci, M., Sandler, D.P. and Alavanja, M.C. (2005) Cancer Incidence among Glyphosate-Exposed Pesticide Applicators in the Agricultural Health Study. Environmental Health Perspectives, 113, 49-54.
http://dx.doi.org/10.1289/ehp.7340
[68] Aman, J., van der Heijden, M., van Lingen, A., Girbes, A.R., van NieuwAmerongen, G.P., van Hinsbergh, V.W. and Groeneveld, A.B. (2011) Plasma Protein Levels Are Markers of Pulmonary Vascular Permeability and Degree of Lung Injury in Critically Ill Patients with or at Risk for Acute Lung Injury/Acute Respiratory Distress Syndrome. Critical Care Medicine, 39, 89-97.
http://dx.doi.org/10.1097/CCM.0b013e3181feb46a
[69] Jensen, J.S., Borch-Johnsen, K., Jensen, G. and Feldt-Rasmussen, B. (1995) Microalbuminuria Reflects a Generalized Transvascular Albumin Leakiness in Clinically Healthy Subjects. Clinical Science, 88, 629-633.
http://dx.doi.org/10.1042/cs0880629
[70] Sarafidis, P.A. and Bakris, G.L. (2006) Microalbuminuria and Chronic Kidney Disease as Risk Factors for Cardiovascular Disease. Nephrology Dialysis Transplantation, 21, 2366-2374.
http://dx.doi.org/10.1093/ndt/gfl309
[71] Meurman, J.H., Rantonen, P., Pajukoski, H. and Sulkava, R. (2002) Salivary Albumin and Other Constituents and Their Relation to Oral and General Health in the Elderly. Oral Surgery, Oral Medicine, Oral Pathology, Oral Radiology and Endodontology, 94, 432-438.
http://dx.doi.org/10.1067/moe.2002.122345
[72] Kamisawa, T., Tu, Y., Egawa, N., Sakaki, N., Inokuma, S. and Kamata, N. (2003) Salivary Gland Involvement in Chronic Pancreatitis of Various Etiologies. American Journal of Gastroenterology, 98, 323-326.
http://dx.doi.org/10.1111/j.1572-0241.2003.07230.x
[73] De Waele, J.J., Hoste, E.A.J., Baert, D., Hendricks, K., Rijckaert, D., Thibo, P., Van Biervliet, P., Blot, S.I. and Colardyn, F. (2007) Relative Adrenal Insufficiency in Patients with Acute Pancreatitis. Intensive Care Medicine, 33, 1754-1760.
http://dx.doi.org/10.1007/s00134-007-0747-3
[74] De Waele, J.J., Hoste, E., Decruyenaere, J. and Colardyn, F. (2003) Adrenal Insufficiency in Severe Acute Pancreatitis. Pancreas, 27, 244-246.
http://dx.doi.org/10.1097/00006676-200310000-00009
[75] Peng, Y.-S., Wu, C.-S., Chen, Y.-C., Lien, J.-M., Tian, Y.-C., Fang, J.-T., Yang, C., Chu, Y.-Y., Hung, C.-F., Yang, C.-W., Chen, P.-C. and Tsai, M.-H. (2009) Critical Illness-Related Corticosteroid Insufficiency in Patients with Severe Acute Biliary Pancreatitis: A Prospective Cohort Study. Critical Care, 13, R123.
http://dx.doi.org/10.1186/cc7978
[76] Yue, Y., Zhang, Y., Zhou, L., Qin, J. and Chen, X. (2008) In Vitro Study on the Binding of Herbicide Glyphosate to Human Serum Albumin by Optical Spectroscopy and Molecular Modeling. Journal of Photochemistry and Photobiology B, 90, 26-32.
http://dx.doi.org/10.1016/j.jphotobiol.2007.10.003
[77] Chen, P.O. and Mahler, J.F. (1992) NTP Technical Report on Toxicity Studies of Glyphosate (CAS No. 1071083-6) Administered in Dosed Feed to F344/N Rats and B6C3F1 Mice. National Toxicology Program, Research Triangle Park, NC, USA. NTP Toxicity Report Series No. 16, NIH Publication 92-3135, July 1992. Submitted to WHO by Monsanto In. Services SA, Brussels, Belgium.
[78] Glyphosate Renewal Assessment Report (RAR). Volume 3CA-CP B-6, Toxicology and Metabolism, 2013-12-18. Draft Report Submitted by Federal Institute for Risk Assessment (BfR, Germany) to the European Food Safety Authority. Last Accessed October 1, 2015.
http://www.scribd.com/doc/238089929/Glyphosate-RAR-08-Volume-3CA-CP-B-6-2013-12-18-San
[79] Hirota, M., Ohmuraya, M. and Baba, H. (2006) The Role of Trypsin, Trypsin Inhibitor, and Trypsin Receptor in the Onset and Aggravation of Pancreatitis. Journal of Gastroenterology, 41, 832-836.
http://dx.doi.org/10.1007/s00535-006-1874-2
[80] Malatesta, M., Caporaloni, C., Rossi, L., Battistelli, S., Rocchi, M.B., Tonucci, F. and Gazzanelli, G. (2002) Ultrastructural Analysis of Pancreatic Acinar Cells from Mice Fed on Genetically Modified Soybean. Journal of Anatomy, 201, 409-415.
http://dx.doi.org/10.1046/j.0021-8782.2002.00103.x
[81] Klimstra, D.S., Heffess, C.S., Oertel, J.E. and Rosai, J. (1992) Acinar Cell Carcinoma of the Pancreas: A Clinicopathologic Study of 28 Cases. The American Journal of Surgical Pathology, 16, 815-837.
http://dx.doi.org/10.1097/00000478-199209000-00001
[82] Salbego, J., Pretto, A., Machado da Silva, V.M., Loro, V.L., Lazzari, R., Gioda, C.R. and Baldisserotto, B. (2014) Glyphosate on Digestive Enzymes Activity in Piava (Leporinus obtusidens). Ciência Rural, 44, 1603-1607.
http://dx.doi.org/10.1590/0103-8478cr20131399
[83] Zouaoui, K., Dulaurent, S., Gaulier, J.M., Moesch, C. and Lachatre, G. (2013) Determination of Glyphosate and AMPA in Blood and Urine from Humans: About 13 Cases of Acute Intoxication. Forensic Science International, 226, e20-e25.
http://dx.doi.org/10.1016/j.forsciint.2012.12.010
[84] Kalra, A., Palaniswamy, C., Patel, R., Kalra, A. and Selvaraj, D.R. (2012) Acute Hypotensive Transfusion Reaction with Concomitant Use of Angiotensin-Converting Enzyme Inhibitors: A Case Report and Review of the Literature. American Journal of Therapeutics, 19, e90-e94.
http://dx.doi.org/10.1097/MJT.0b013e3181e4ddb2
[85] Raddy, M., Sriganesh, K., Bhadrinarayan, V. and Raghavendra, B.S. (2011) Unusual Manifestation of Blood Transfusion Reaction as Diffuse Operative Site Oozing, Hypotension and Brain Swelling. Journal of Anaesthesiology Clinical Pharmacology, 27, 130-131.
[86] Dumaswala, U.J., Zhuo, L., Jacobsen, D.W., Jain, S.K. and Sukalski, K.A. (1999) Protein and Lipid Oxidation of Banked Human Erythrocytes: Role of Glutathione. Free Radical Biology and Medicine, 27, 1041-1049.
http://dx.doi.org/10.1016/S0891-5849(99)00149-5
[87] Collard, K., White, D. and Copplestone, A. (2014) The Influence of Storage Age on Iron Status, Oxidative Stress and Antioxidant Protection in Paediatric Packed Cell Units. Blood Transfusion, 12, 210-219.
[88] Collard, K.J. and White, D.L. (2014) On the Source of the Non-Transferrin-Bound Iron Which Accumulates in Packed Red Blood Cell Units during Storage. Blood Transfusion, 12, 527-532.
[89] L’Acqua, C., Bandyopadhyay, S., Francis, R.O., McMahon, D.J., Nellis, M., Sheth, S., Kernie, S.G., Brittenham, G.M., Spitalnik, S.L. and Hod, E.A. (2015) Red Blood Cell Transfusion Is Associated with Increased Hemolysis and an Acute Phase Response in a Subset of Critically Ill Children. American Journal of Hematology, 90, 915-920.
http://dx.doi.org/10.1002/ajh.24119
[90] Cavas, T. and Könen, S. (2007) Detection of Cytogenetic and DNA Damage in Peripheral Erythrocytes of Goldfish (Carassius auratus) Exposed to a Glyphosate Formulation Using the Micronucleus Test and the Comet Assay. Mutagenesis, 22, 263-268.
http://dx.doi.org/10.1093/mutage/gem012
[91] Kwiatkowska, M., Huras, B. and Bukowska, B. (2014) The Effect of Metabolites and Impurities of Glyphosate on Human Erythrocytes (in Vitro). Pesticide Biochemistry and Physiology, 109, 34-43.
[92] Lu, W., Li, L., Chen, M., Zhou, Z., Zhang, W., Ping, S., Yan, Y., Wang, J. and Lin, M. (2013) Genome-Wide Transcriptional Responses of Escherichia coli to Glyphosate, a Potent Inhibitor of the Shikimate Pathway Enzyme 5-Enolpyruvylshikimate-3-Phosphate Synthase. Molecular BioSystems, 9, 522-530.
http://dx.doi.org/10.1039/c2mb25374g
[93] Lushchak, O.V., Kubrak, O.I., Storey, J.M., Storey, K.B. and Lushchak, V.I. (2009) Low Toxic Herbicide Roundup Induces Mild Oxidative Stress in Goldfish Tissues. Chemosphere, 76, 932-937.
http://dx.doi.org/10.1016/j.chemosphere.2009.04.045
[94] Benachour, N. and Séralini, G.-E. (2009) Glyphosate Formulations Induce Apoptosis and Necrosis in Human Umbilical, Embryonic and Placental Cells. Chemical Research in Toxicology, 22, 97-105.
http://dx.doi.org/10.1021/tx800218n
[95] Darbari, D.S., Kple-Faget, P., Kwagyan, J., Rana, S., Gordeuk, V.R. and Castro, O. (2006) Circumstances of Death in Adult Sickle Cell Disease Patients. American Journal of Hematology, 81, 858-863.
http://dx.doi.org/10.1002/ajh.20685
[96] Vichinsky, E.P., Haberkern, C.M., Neumayr, L., Earles, A.N., Black, D., Koshy, M., Pegelow, C., Abboud, M., Ohene-Frempong, K. and Iyer, R.V. (1995) A Comparison of Conservative and Aggressive Transfusion Regimens in the Perioperative Management of Sickle Cell Disease. The New England Journal of Medicine, 333, 206-213.
http://dx.doi.org/10.1056/NEJM199507273330402
[97] Ballas, S.K. (2001) Iron Overload Is a Determinant of Morbidity and Mortality in Adult Patients with Sickle Cell Disease. Seminars in Hematology, 38, 30-36.
[98] Platt, O.S., Brambilla, D.J., Rosse, W.F., Milner, P.F., Castro, O., Steinberg, M.H. and Klug, P.P. (1994) Mortality in Sickle Cell Disease. Life Expectancy and Risk Factors for Early Death. The New England Journal of Medicine, 330, 1639-1644.
http://dx.doi.org/10.1056/NEJM199406093302303
[99] Haynes Jr, J. and Allison, R.C. (1986) Pulmonary Edema: Complication in the Management of Sickle Cell Pain Crisis. American Journal of Medicine, 80, 833-840.
http://dx.doi.org/10.1016/0002-9343(86)90624-8
[100] Siddiqui, A.K. and Ahmed, S. (2003) Pulmonary Manifestations of Sickle Cell Disease. Postgraduate Medical Journal, 79, 384-390.
http://dx.doi.org/10.1136/pmj.79.933.384
[101] Shehata, A.A., Schrödl, W., Schledorn, P. and Krüger, M. (2014) Distribution of Glyphosate in Chicken Organs and Its Reduction by Humic Acid Supplementation. The Journal of Poultry Science, 51, 333-337.
http://dx.doi.org/10.2141/jpsa.0130169
[102] Ridley, W.P. and Mirly, K. (1988) The Metabolism of Glyphosate in Sprague-Dawley Rats-Part I. Excretion and Tissue Distribution of Glyphosate and Its Metabolites Following Intravenous and Oral Administration. (Unpublished Study MSL-7215 Conducted by Monsanto Company Environmental Health Laboratory and Submitted to the US EPA July 1988) MRID#407671-01.
[103] Horrow, J.C. (1988) Protamine Allergy. Journal of Cardiothoracic Anesthesia, 2, 225-242.
http://dx.doi.org/10.1016/0888-6296(88)90277-3
[104] Studier, F.W. (2005) Protein Production by Auto-Induction in High Density Shaking Cultures. Protein Expression and Purification, 41, 207-234.
http://dx.doi.org/10.1016/j.pep.2005.01.016
[105] Studier, F.W. (2014) Stable Expression Clones and Autoinduction for Protein Production in E. coli. Methods in Molecular Biology, 1091, 17-32.
http://dx.doi.org/10.1007/978-1-62703-691-7_2
[106] Filizadeh, Y. and Zolfinejad, K. (2011) Toxicity Determination on Three Sturgeon Species Exposed to the Glyphosate. Iranian Journal of Fisheries Sciences, 10, 383-392.
[107] Antón, F.A., Laborda, E. and Ariz, M. (1994) Acute Toxicity of the Herbicide Glyphosate Tofish. Chemosphere, 28, 745-753.
http://dx.doi.org/10.1016/0045-6535(94)90228-3
[108] Uotila, M., Gullner, G. and Kömives, T. (1995) Induction of Glutathione S-Transferase Activity and Glutathione Level in Plants Exposed to Glyphosate. Physiologia Plantarum, 93, 689-694.
[109] Basantani, M., Srivastava, A. and Sen, S. (2011) Elevated Antioxidant Response and Induction of Tau-Class Glutathione S-Transferase after Glyphosate Treatment in Vigna radiata (L.). Wilzek. Pesticide Biochemistry and Physiology, 99, 111-117.
http://dx.doi.org/10.1016/j.pestbp.2010.11.007
[110] Jain, M. and Bhalla-Sarin, N. (2001) Glyphosate-Induced Increase in Glutathione S-Transferase Activity and Glutathione Content in Groundnut (Arachis hypogaea L.). Pesticide Biochemistry and Physiology, 69, 142-152.
http://dx.doi.org/10.1006/pest.2000.2535
[111] Lee, D.H. and Jacobs, D.R. (2009) Is Serum Gamma-Glutamyltransferase an Exposure Marker of Xenobiotics? Empirical Evidence with Polycylic Aromatic Hydrocarbon. Clinical Chemistry and Laboratory Medicine, 47, 860-862.
http://dx.doi.org/10.1515/CCLM.2009.197
[112] Lum, G. and Gambino, S.R. (1972) Serum Gamma-Glutamytranspeptidase Activity as an Indicator of Disease of Liver, Pancreas, or Bone. Clinical Chemistry, 18, 358-362.
[113] Lum, G. (1974) Gamma-Glutamyl Transpeptidase in Cancer Diagnosis. Annals of Clinical & Laboratory Science, 4, 13-18.
[114] Miyazaki, S. and Okumura, M. (1992) Change of Serum Glutamyltranspeptidase Level and Isoenzyme Pattern in Hepatobiliary Pancreatic Disease. Clinica Chimica Acta, 40, 193-197.
[115] Mastellone, V., Tudisco, R., Monastra, G., Pero, M.E., Calabrò, S., Lombardi, P., Grossi, M., Cutrignelli, M.I., Avallone, L. and Infascelli, F. (2013) Gamma-Glutamyltransferase Activity in Kids Born from Goats Fed Genetically Modified Soybean. Food and Nutrition Sciences, 4, 50-54.
http://dx.doi.org/10.4236/fns.2013.46A006
[116] Khorana, A.A., Francis, C.W., Blumberg, N., Culakova, E., Refaai, M.A. and Lyman, G.H. (2008) Blood Transfusions, Thrombosis and Mortality in Hospitalized Patients with Cancer. Archives of Internal Medicine, 168, 2377-2381.
http://dx.doi.org/10.1001/archinte.168.21.2377
[117] Zacharski, L.R. (2005) Hypercoagulability Preceding Cancer. The Iron Hypothesis. Journal of Thrombosis and Haemostasis, 3, 585-588.
http://dx.doi.org/10.1111/j.1538-7836.2005.01178.x
[118] Dominici, S., Paolicchi, A., Lorenzini, E., Maellaro, E., Comporti, M., Pieri, L., Minotti, G. and Pompella, A. (2003) Gamma-Glutamyltransferase-Dependent Prooxidant Reactions: A Factor in Multiple Processes. Biofactors, 17, 187-198.
[119] Koenig, G. and Seneff, S. (2015). Gamma-Glutamyltransferase: A Predictive Biomarker of Cellular Antioxidant Inadequacy and Disease Risk. Disease Markers, 2015, Article ID: 818570.
http://dx.doi.org/10.1155/2015/818570
[120] Falhammar, H., Filipsson, H., Holmdahl, G., Janson, P.-O., Nordenskjöld, A., Hagenfeldt, K. and Thorén, M. (2009) Increased Liver Enzymes in Adult Women with Congenital Adrenal Hyperplasia due to 21-Hydroxylase Deficiency. Endocrine Journal, 56, 601-608.
http://dx.doi.org/10.1507/endocrj.K08E-312
[121] Patak, P., Willenberg, H.S. and Bornstein, S.R. (2004) Vitamin C Is an Important Cofactor for Both Adrenal Cortex and Adrenal Medulla. Endocrine Research, 30, 871-875.
http://dx.doi.org/10.1081/erc-200044126
[122] Song, J.H., Simons, C., Cao, L., Shin, S.H., Hong, M. and Chung, I.M. (2003) Rapid Uptake of Oxidized Ascorbate Induces Loss of Cellular Glutathione and Oxidative Stress in Liver Slices. Experimental & Molecular Medicine, 35, 67-75.
http://dx.doi.org/10.1038/emm.2003.10
[123] Olabisi, A.O. (2005) The Chemistry of L-Ascorbic acid Derivatives in the Asymmetric Synthesis of C2- and C3-Substituted Aldonolactones. Ph.D. Dissertation, College of Liberal Arts and Sciences, Wichita State University, Wichita.
[124] Hsiao, C.T., Lin, LJ., Hsiao, K.Y., Chou, M.H. and Hsiao, S.H. (2008) Acute Pancreatitis Caused by Severe Glyphosate-Surfactant Oral Intoxication. The American Journal of Emergency Medicine, 26, 384.e3-384.e5.
http://dx.doi.org/10.1016/j.ajem.2007.06.024
[125] Garcia-Szabo, R.R. and Malik, A.B. (1984) Pancreatitis-Induced Increase in Lung Vascular Permeability. Protective Effect of Trasylol. American Review of Respiratory Disease, 129, 580-583.
[126] Mao, Y. and Kunapuli, S.P. (2013) Trypsin Causes Platelet Activation Independently of Known Protease-Activated Receptors. Thrombosis and Haemostasis, 110, 1241-1249.
http://dx.doi.org/10.1160/th13-03-0189
[127] Bradshaw, M., Mansfield, A. and Peikert, T. (2013) The Role of Vascular Endothelial Growth Factor in the Pathogenesis, Diagnosis and Treatment of Malignant Pleural Effusion. Current Oncology Reports, 15, 207-216.
http://dx.doi.org/10.1007/s11912-013-0315-7
[128] Martin, S., Maruta, K., Burkart, V., Gillis, S. and Kolb, H. (1988) IL-1 and IFN-Gamma Increase Vascular Permeability. Immunology, 64, 301-305.
[129] Tahamont, M.V., Barie, P.S., Blumenstock, F.A., Hussain, M.H. and Malik, A.B. (1982) Increased Lung Vascular Permeability after Pancreatitis and Trypsin Infusion. The American Journal of Pathology, 109, 15-26.
[130] Hartmann, J.R., Robinson, J.A. and Gunnar, R.M. (1977) Chemotactic Activity in the Coronary Sinus after Experimental Myocardial Infarction: Effects of Pharmacologic interventions on Ischemic Injury. American Journal of Cardiology, 40, 550-555.
http://dx.doi.org/10.1016/0002-9149(77)90070-4
[131] Roxvall, L., Sennerby, L., Johansson, B.R. and Heideman, M. (1990) Trypsin-Induced Vascular Permeability and Leukocyte Accumulation in Hamster Cheek Pouch: The Role of Complement Activation. Journal of Surgical Research, 49, 504-513.
http://dx.doi.org/10.1016/0022-4804(90)90175-2
[132] Loh, Y.P. and Gainer, H. (1980) Evidence That Glycosylation of Pro-Opiocortin and ACTH Influences Their Proteolysis by Trypsin and Blood Proteases. Molecular and Cellular Endocrinology, 20, 35-44.
http://dx.doi.org/10.1016/0303-7207(80)90092-1
[133] Sakaeda, T., Tamon, A., Kadoyama, K. and Okuno, Y. (2013) Data Mining of the Public Version of the FDA Adverse Event Reporting System. International Journal of Medical Sciences, 10, 796-803.
http://dx.doi.org/10.7150/ijms.6048

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