The New Zealand governmet clear the wedicide Glyphosate as perfectly safe for use.
Posted on August 19th, 2016

Chandre Dharmawardana

The New Zealand government, after an long review of the weedicide Glyphosate (Roundup), has now given it the ALL CLEAR signal, confirming that it is VERY SAFE for use.

Here is the report:


Sometime ago there were sensational claims that Glyphosate,  the popular weedicide,  causes kidney diseases, Cancer etc., and that it should be banned.

Fools rush in where angels fear to tread.

Sri Lanka was the first country to ban the herbicide; this was politically lead by Ven. Ratana and the Minsiter Champika Ranawaka who claimed to rid the country of “Toxins”.  It was preceded by a campaign (during the previous government) by Ven Ratana, and by a number of  highly politicized  Kelaniya University academics who claimed that God Natha had revealed that the Rajarata water has arsenic. This was further elaborated  by them and a Sri Lankan Californian doctor to claim that Arsenic combines with glyphosate and hard water to bring the toxin into the human body! This was presented as a “hypothesis” and not a proven fact in a “journal”, but it has been presented as a proven fact when broadcasting  it to the public!

The arsenic is supposed to be found in imported  fertilizers.

So, according to them, agrochemicals- fertilizers and herbicides–  are to blame. Even if they are not to blame, some of the “eco-activists”  advocated banning them as a “precautionary principle“.

Once imported fertilizers are banned, people have to use “organic fertilizers”, i.e., make the fertilizer themselves by composting leaves, and other plant material “like in the olden days”.

Or buy the highly polluted  “organic fertilizer” imported  from India at great cost.

To get the effect of one kilo of inorganic fertilizer, you need to use something like  one TON of organic fertilizer. Such compost is polluted because plants accumulate metal toxins found in trace amounts in the soil.

Remember, this is a country where “Kassipu” and “Kudu” are freely available. All pharmacies sell “viagra” or cortisone drugs without a prescription. Motor vehicles belch out toxins and diesel fumes all over the country. There are mounds of garbage in every street corner. The general pollution levels are high. But the “eco-activists” and “environmental heroes”  (mostly from the affluent strata of Colombo society) are worried about “glyphosate” and arsenic. But their  presence in the water or soil in significant amounts have not been confirmed even though searched for by  several different teams of scientists who carried out chemical analysis. Even the Kelaniya scientists have failed to find significant amounts of them in the soil or water or food consumed by the people.

New Zealand and many other countries use even ten times the agrochemicals used by

Sri Lanka or, say,  Nicaragua. The countries that use agrochemicals  do not have chronic kidney disease nor do they have a high incidence  of diseases. It is the countries like Sri Lanka, Nicaragua, who do  NOT use agrochemicals, and who fail to provide a nutritious diet, clean water and a healthy life to their citizens who have chronic diseases. Chronic diseases and agrochemicals ANT-CORRELATE with each other, where as they should correlate if agrochemicals were significantly responsible for chronic disease.

The New Zealand government, responding to the agitation by eco- extremists in that country and the resulting public fear,  initiated a review of all the available facts. After many months of review of the weedicide Glyphosate (Roundup),  the NZ govt has  given it the ALL CLEAR signal.

I attach here the report of the NZ government’s  review.

Today, in Sri Lanka, a country with an acute shortage of labour, many of the tea estates are struggling to survive. Chicken and other livestock growers have no animal feed because the  Corn (“Bada Iringu”) growers who produced animal feed have given up. Other farming sectors are also in trouble.

Chandre Dharmawardana



(please go to to read it properly).


Review of the Evidence Relating to
Glyphosate and Carcinogenicity
Prepared for the Environmental Protection Authority

Published August 2016
Glyphosate (N-phosphonomethyl glycine; CAS registry #1071-83-6) is the primary active
ingredient in many generic herbicides. Glyphosate is formulated primarily as an
isopropylamine, ammonium, or sodium salt in water soluble concentrates and water soluble
granules. The relevant impurities in glyphosate technical concentrates are formaldehyde, N-
nitrosoglyphosate and N-nitroso-N-phosphonomethylglycine. Surfactants and sulfuric and
phosphoric acids may be added to formulations of glyphosate, with type and concentration
differing by formulation. The United States (US) Environmental Protection Agency (EPA) and
other regulatory agencies around the world have registered this chemical as a broad-
spectrum herbicide for use on multiple food and non-food use crops. Glyphosate-based
herbicides, which have been sold in the US since 1974, are now registered in over 130
Glyphosate is widely considered by regulatory authorities and scientific bodies to have no
carcinogenic potential. The US EPA (1993) has classified glyphosate as a Group E
carcinogen, which is defined as having ‘‘evidence of non-carcinogenicity for humans’’. This
classification was based on ‘‘a lack of convincing evidence of carcinogenicity in adequate
studies with two animal species, rat and mouse’’. Negative results were observed in
genotoxicity studies that were conducted under good laboratory practice conditions and compliant with contemporary regulatory test guidelines.
However since that time, results of further studies have come to light, and the International
Agency for Research on Cancer (IARC) Monograph 112 on glyphosate (released on 29 July
2015) came to the conclusion that glyphosate should now be classified as a carcinogenic
substance in Group 2A (probably carcinogenic to humans). This classification was based on
limited evidence” from human data (regarding non-Hodgkin lymphoma (NHL)) but sufficient
evidence” in animal-experiments. The rationale identifies that the IARC working group (IWG)
also notes mechanistic and other relevant data in support of the conclusion; in particular the
IWG cites strong evidence” that glyphosate can operate by two key characteristics of known
human carcinogens, namely genotoxicity and oxidative stress.
This classification was initially published in a short report by Blair et al, (2015) in the Lancet
Oncology” on 20 March 2015.
This report discusses the relevant data on glyphosate, especially the more recent studies,
and reviews the basis on which the IWG classified it as a probable human carcinogen
(Group 2A). This involves review of the quality of evidence for carcinogenicity in humans and experimental animals and the mechanistic arguments.
Cancer in humans
The IWG found there was limited evidence in humans for the carcinogenicity of glyphosate.
Some case-control studies of occupational exposure in the USA, Canada, and Sweden
reported increased risks for NHL that persisted after adjustment for other pesticide
exposures. However the Agricultural Health Study (AHS) cohort did not show a significantly
increased risk of NHL. These studies are discussed below.

Case-control studies in the Midwest USA
Three case-control studies were conducted by the U.S National Cancer Institute in Iowa and
Minnesota in the1980s using the same control series, but each investigating a different
lymphohaematopoietic cancer. Brown et al, (1990) found a near null association between
glyphosate exposure and leukaemia among white males residing in the area (OR = 0.9; 95%
CI 0.5–1.6). Among Iowa farmers reporting ever handling glyphosate, there was a slight non-
statistically significant odds ratio for multiple myeloma (OR = 1.7; 95% CI 0.8–3.6) (Brown et
al, 1993). Cantor et al, (1992) found an approximately null association between glyphosate
exposure and NHL among males (OR 1.1; 95% CI 0.7–1.9).
The IWG reviewed a later study by De Roos et al, (2003) who used pooled data from three
case-control studies of NHL conducted in the 1980s in Nebraska (Zahm et al, 1990), Iowa
and Minnesota (Cantor et al, 1992), and Kansas (Hoar et al, 1986). Reported use of
glyphosate as well as several other individual pesticides was associated with an increased
risk of NHL. A total of 650 cases and 1,933 controls were included for the analysis of 47
pesticides. Reporting glyphosate exposure were 36 cases and 61 controls. After adjusting
for other pesticide use, age, and study area, by two regression techniques, odds ratios of 2.1
(1.1–4.0) using logistic regression and 1.6 (0.9–2.8) using hierarchical regression were
In that regard, a later study by De Roos et al, (2005) where they reviewed the AHS cohort
data is significant. They found no association between glyphosate and NHL. The authors
noted that the aforementioned Midwest USA case control studies were retrospective in
design and therefore potentially susceptible to recall bias as regards exposure reporting.
The cross-Canada case – control study
The IWG reviewed a report by McDuffie et al, (2001) who studied the association between
NHL and exposure to specific pesticides in a multicentre population-based study with 517
cases and 1,506 controls among men of six Canadian provinces. The authors reported a
slight, non-statistically significant increased risk for NHL from claimed glyphosate exposure,
the OR being 1.26 (95% CI 0.87–1.80) for analysis adjusted for age and province, and 1.20
(95% CI 0.83–1.74) for analysis adjusted for age, province and high-risk exposures. The
study also assessed the significance of different exposure durations. When stratified by
greater than or less than two days of glyphosate exposure/year (< 2d/year), the values were
2.12 (95% CI 1.20–3.73) for >2d/year relative to those with < 2d/year (assigned OR of 1.0).
The authors commented that although there was not a statistically significant finding for
exposure to glyphosate per se, there was a dose-response relationship.
Case-control studies in Sweden
The IWG reviewed a study by Eriksson et al, (2008) who reported the results of a population-
based case-control study of exposure to pesticides as a risk factor for NHL. Men and women
aged 18–74 years living in Sweden were included from 1 December 1999 to 30 April 2002.
In total, 910 (91%) cases and 1,016 (92%) controls participated. The authors found NHL
associations with exposure to glyphosate. This exposure was reported by 29 cases and 18
controls, giving a reported odds ratio of 2.02 (95% CI 1.10–3.71) in a multivariate analysis.
When restricted to a >10 year latency period the OR became 2.26 (95% CI 1.16–4.40).
Odds ratios were also reported for lymphoma subtypes. For only two of the eight subtypes
were odds ratios statistically significant; likely related to the small numbers. The IWG
considered that this was a large study; that there was possible confounding from the use of
other pesticides including MCPA, but this was controlled for in the analysis. Given the
number of cases studied for glyphosate (29 cases and 18 controls) this study could hardly
be considered as large. Twelve subjects were in a less than 10 days exposure group and 17
in a more than 10 days group. Therefore this study had limited power to detect an effect.
Other findings
In 2014 Schinasi and Leon reported their study of the association between NHL and
occupational exposure to various agricultural pesticide chemical groups. Some findings on
glyphosate were presented; for example the results from the studies by McDuffie et al,
(2001), De Roos et al, (2005) and Eriksson et al, (2008) were given. This review included a
series of meta-analyses, which they asserted showed consistent evidence of positive
associations between NHL and carbamate insecticides, organophosphorus insecticides,
lindane, and MCPA. As regards glyphosate (an organophosphorus herbicide”), in a handful
of papers”, associations between pesticides and NHL subtypes were reported; B cell
lymphoma was positively associated with phenoxy herbicides and glyphosate.
The Agricultural Health Study (AHS) cohort studies
These studies in Ohio and North Carolina involve a large cohort of private and commercial
pesticide applicators (57,311 as at 2004–5). Several studies have been conducted using this
Alavanja et al, (2003) evaluated associations between specific pesticides and prostate
cancer in the AHS. Glyphosate was listed as one of the pesticides with sufficient exposure
data for analysis, but the findings for it were not listed, so that it has been assumed that no
significant positive association was found with prostate cancer.
Flower et al, (2004) evaluated associations between pesticide application by parents and
cancer among children born to Iowa participants in the AHS. There was no positive
association between either maternal or paternal use of glyphosate and risk of childhood
De Roos et al, (2005) evaluated associations between glyphosate exposure and all
cancers” or any cancer site using the AHS cohort. This study did not show a significantly
increased risk of NHL. In the group reportedly exposed to glyphosate, small, non-statistically
significant relative risks of 1.2 (95% CI 0.7–1.9) adjusted for age (only) and 1.1 (95% CI 0.7–
1.9) adjusted for age, demographic and lifestyle factors and other pesticide exposure were
found for NHL, (De Roos 2005). There was no dose (exposure) response relationship.
De Roos et al, (2005) also found a non-statistically significant association between
glyphosate exposure and multiple myeloma, with rate ratios (RR values) of 1.1 (95% CI 0.5–
2.4) adjusted for age only, and 2.6 (95% CI 0.7–9.4) adjusted for age, demographic and
lifestyle factors and other pesticides exposures. Such a finding had not previously been
Comparisons were made between ever-exposed versus never-exposed groups, and
between three equal sized groups (tertiles), formed by subdivision either on the basis of total
days of exposure or intensity-weighted exposure days. In the intensity-weighted analysis of
glyphosate and lung cancer, the relative risk for the highest tertile was only 0.6 (95% CI 0.3–
1.0), for pancreatic cancer the RR for the highest tertile was 0.5, while for multiple myeloma
the RR was 2.1, but the confidence interval was wide (0.6–7.0). None of these findings
reached statistical significance at 95%. Regarding the whole group (ie ever used
glyphosate), the RR for multiple myeloma was 1.1 (95% CI 0.5–2.4) adjusted for age only,
and 2.6 (95% CI 0.7–9.4) adjusted for age, demographic and lifestyle factors and other
pesticide exposures. Unremarkable, non-statistically significant results were found for the
other cancer sites assessed.
Thus as regards this study, there was no evidence of a statistically significant positive
association for any of the cancers for which data were reported (Mink et al, 2012).
Furthermore De Roos et al, (2005) acknowledged in their paper that over 13,000 subjects
were excluded from multivariate analyses because of missing data. In analyses of ever”
versus never” exposed to glyphosate, the age-adjusted relative risk of multiple myeloma
was 1.1. Lash (2007) assessed the study design and concluded that adjustment for
confounders, which resulted in limiting the data set by 25% because of missing data on the
adjustment variables, likely introduced selection bias, which was likely to have been in the
direction away from the null (ie exaggerating any possible risk).
It is also known that multiple myeloma is often preceded by monoclonal gammopathy of
undetermined significance (MGUS), a pre-malignant plasma cell disorder (Morgan et al,
2002). It is of interest to note that a decreased risk (albeit not statistically significant) of
MGUS was observed in glyphosate applicators in the AHS.
Engel et al, (2005) evaluated breast cancer risk among wives of farmers in the AHS. No
statistically significant association was found.
In an analysis of colorectal cancer and pesticide use, Lee et al, (2007) found no statistically
significant association between glyphosate use and cancer of the colon or rectum.
Andreotti et al, (2009) reported no significant association of ever” use (versus never use”)
of glyphosate with pancreatic cancer among the combined group of AHS applicators and
spouses (OR 1.1; 95% CI 0.6–1.07), nor was there evidence for a dose-response
Dennis et al, (2010) evaluated associations of 50 pesticides with cutaneous melanoma in the
AHS cohort. Glyphosate was listed as one of the 22 pesticides on the enrolment
questionnaire. The authors commented that none of these 22 pesticides was associated with
None of the AHS cohort study analyses reported statistically significant positive findings for
glyphosate exposure and total cancer or any site-specific cancer, in adults or children. In
particular, the prospective AHS studies did not corroborate the positive association with NHL
reported by the Swedish case-control studies. Analyses of increasing category of glyphosate
exposure days and incidence of NHL produced rate ratios that were below the null value of
1.0 (De Roos et al, 2005 and Mink et al, 2012).
Discussion of review of epidemiological findings
In a review of glyphosate in 2006, the WHO observed that:
widely used pesticides, like glyphosate, have recently become a focus of epidemiological
research. In the past few years several epidemiological studies have been published that
reported weak associations of glyphosate with lymphopoietic cancers, self-reported adverse
reproductive outcomes and self-reported attention deficit hyperactivity disorder in children.
However, the results of these studies do not meet generally accepted criteria from the
epidemiology literature for determining causal relationships. Generally, the associations
were rather weak and rarely statistically significant. Controlling for potential confounding
factors, including other pesticides exposure, was not possible owing to limited available
information and small numbers of subjects”.
Whether or not there was any internal exposure or the extent of such exposure was not
measured and, accordingly, a possible dose–response relationship could not be evaluated.
This seems a fair assessment of several of the studies regarding glyphosate and its
formulations. De Roos et al, (2005) noted that the Midwest USA case control studies were
retrospective in design and therefore potentially susceptible to recall bias as regards
exposure reporting. Certainly a large prospective cohort study (such as that by De Roos et
al, 2005) is much preferable to smaller case-control studies, the latter of which have much
less statistical power to identify causal associations and are subject to more biases,
including those regarding exposure assessment. Therefore much more weight should be
given to the De Roos et al, (2005) cohort study than the much smaller De Roos et al, (2003)
case-control study. In that regard, it is important to note that the cohort study found no
association between glyphosate and NHL. There was, however, a small (non-statistically
significant) increased risk of multiple myeloma in the 2005 study, but the point estimates of
this risk may have been exaggerated. (Lash 2007.)
A re-analysis of some data from the De Roos et al, (2005) study has recently been
undertaken, with a focus on multiple myeloma (Sorahan, 2015). Assessing the same data,
Sorahan found no significant trends of multiple myeloma risk with reported cumulative days
of glyphosate use, and unexceptional point estimates of risk for ever-use of glyphosate. This
was irrespective of whether the analysis had made adjustment for a few basic variables (age
and gender) or made adjustment for many other lifestyle factors or pesticide exposures; as
long as data on all available pesticide applicators was used.
Sorahan (2015) argued that the elevated rate ratios (or relative risks) for multiple myeloma
reported previously by Roos et al, (2005) arose from use of restricted data sets that,
probably by chance, turned out to be unrepresentative. These restrictions were considered
to be unnecessary and undesirable, as potentially informative data on the exposure or
outcome under investigation were discarded. For example, it was asserted that there were a
number of lost cases of multiple myeloma in the group of applicators who had never used
glyphosate, because they were excluded by Roos et al, (2005) due to their not having data
on for example use of alcohol, or smoking. These lost cases in the baseline category gave a
false impression of elevated rates in ever-users. As a result Sorahan gave more weight to
the point estimate of 1.1 as the RR (adjusted for age only) as opposed to the estimate of 2.6
as the RR for ever-use of glyphosate (adjusted for age, demographic and lifestyle factors,
and other pesticides).
Mink et al, (2012) reviewed the epidemiological literature (and relevant methodological and
biomonitoring studies) to evaluate whether exposure to glyphosate is associated causally
with cancer risk in humans. Seven cohort studies and fourteen case-control studies
examining a potential association between glyphosate and one or more cancer outcomes
were subjected to a qualitative analysis.
The cohort studies were all based on analyses of participants or family members of the AHS
cohort. Mink et al (2012), observed that none of the AHS cohort study analyses reported
statistically significant positive findings for glyphosate exposure and total cancer or any site-
specific cancer in adults or children. They found no consistent pattern of positive
associations to suggest a causal relationship between human exposure to glyphosate and
any cancer.
Overall, this 2012 review found no consistent pattern of positive associations between total
cancer (in adults or children) or any site-specific cancer, and exposure to glyphosate. They
suggested a cautious interpretation of the few positive associations reported, and concluded
that the epidemiological data, when considered together, did not support a causal
association between glyphosate exposure and cancer.
Similarly, the latest report of BfR (2015) to the European Food Safety Authority (EFSA)1
based on the evaluation of over 30 epidemiological studies came to the overall assessment
that there is no validated or significant relationship between exposure to glyphosate and an
increased risk of NHL or other types of cancer.
A recent peer review by EFSA2 (2015) essentially confirmed the conclusions in their re-
evaluation of glyphosate. They noted that 10 cohort studies (which included the AHS, the
largest series of prospective studies to date), found that glyphosate did not cause different
types of cancer and did not increase risk of all cancers combined. (As noted earlier, the
findings for NHL were negative in the AHS cohort.) Similarly nine case-control studies did
not indicate an increased risk of carcinogenicity, or did not have sufficient power to assess
this. With regard to NHL, the case-control studies exhibited poor consistency in their results
and small numbers of cases limiting the statistical significance of findings in some studies.
As noted above, case-control studies have less power, are more subject to various biases,
and are less effective at assessing actual exposure levels than are cohort studies. EFSA
concluded that there is very limited evidence for an association between glyphosate
exposure and the occurrence of NHL.
Cancer in experimental animals
Mice studies
Glyphosate was tested in female and male mice by dietary administration in two studies.

skin application in one initiation-promotion study was conducted with male mice.
The IWG found that in male CD-1 mice, glyphosate induced a positive trend in the incidence
of a rare tumour, renal tubule carcinoma. A second study reported a positive trend for
hemangiosarcoma in male mice. A glyphosate formulation promoted skin tumours in an initiation-promotion study in mice.
The IWG noted there was a positive trend in the incidence of renal tubule carcinoma and of
renal tubule adenoma or carcinoma (combined) in male CD-1 mice in a glyphosate feeding
study (0, 1,000, 5,000, or 30,000 ppm glyphosate ad libitum for 24 months). (This study was
conducted prior to the institution of GLP.) The study was submitted to the US EPA which
requested that a pathology working group (PWG) be convened to evaluate the renal
tumours. In this second evaluation, the PWG found that the incidence of adenoma was not
statistically significant but the incidence of carcinoma and the incidence of adenoma and
carcinoma (combined) were significant. The IWG considered that this second evaluation
indicated a significant increase in the incidence of rare tumours, with a dose-related trend,
which could be attributed to glyphosate.
However, this finding is at variance with the US EPA (1993) which reported in their
glyphosate review that the occurrence of these adenomas was spontaneous rather than
compound-induced because the incidence of renal tubular adenomas in males was not
statistically significantly different when compared with the concurrent controls. An
independent group of pathologists and biometricians also conducted extensive evaluations
of these adenomas and reached the same conclusion. The US EPA concluded glyphosate
was not considered to be carcinogenic in this study.
The BfR (2015) report addressing the carcinogenicity of glyphosate is a report of Germany
specifically, as Germany was the lead member state for the EFSA review of glyphosate.
EFSA accepted the conclusion relating to glyphosate and cancer (including NHL), with one
dissenting member state.
The IWG reviewed a second feeding study reported to the FAO/WHO Joint Meeting on
Pesticide Residues (JMPR), and found there was a significant positive trend in the incidence
of hemangiosarcoma in male CD-1 mice. Groups of 50 female and male mice were fed diets
containing glyphosate at a concentration that was adjusted weekly for the first 13 weeks and
every four weeks thereafter to give doses of 0, 100, 300, or 1,000 mg/kg body weight, ad
libitum for 104 weeks.
In contrast JMPR (WHO 2006) found that owing to the lack of a dose-response relationship,
the lack of statistical significance and the fact that the incidences recorded in this study fell
within the historical ranges for controls, these changes were not considered to be caused by
administration of glyphosate. They concluded administration of glyphosate to CD-1 mice for 104 weeks produced no signs of carcinogenic potential at any dose.




The IWG found that in a study involving 20 male Swiss mice which had a glyphosate based
formulation applied to their skin, it appeared to be a tumour promoter, but they concluded
that this was an inadequate study because its design was poor, with short duration of
treatment, no solvent controls, small numbers of animals, and a lack of histopathological
However the BfR (2015) considered that generally testing of formulations should not be used
for the toxicological evaluation of active substances because co-formulants may extensively
alter the outcome. The BfR deemed that this IWG finding was not considered by the
institutions in the EU to be evidence for the carcinogenic properties of glyphosate per se.
Review articles – mice studies
The IWG noted that Griem et al, (2015) had published a review article which included
discussion of five long-term glyphosate feeding studies in mice. Two of the studies were
discussed in the IARC monograph. The working group summarised the other three studies
but claimed that it was unable to fully evaluate the other three studies because of the limited
experimental data provided in the review article and supplemental information.
Griem et al, (2015) noted that the five mouse studies that they reviewed were submitted to
support glyphosate renewal in the EU. They considered that all but the oldest study were
reliable without restriction and were performed under conditions of GLP and OECD
During the EFSA peer-review process for the renewal of the approval of glyphosate, EFSA
also received a complementary mandate from the EU to consider the findings by IARC
regarding the potential carcinogenicity of glyphosate (EFSA 2015).
The EFSA peer review (2015) also evaluated the five mice studies. Only one of these
suggested a potential carcinogenic effect, as evidenced by a statistically significant
increased evidence of malignant lymphomas at the top dose level of 1,460 mg/kg/day.
However the validity of the study was questioned, due to the occurrence of viral infection
which could have influenced survival rates and the incidence of lymphomas. No carcinogenic
effects were observed at the highest dose levels in any of the other studies. The IWG
evaluated two of these studies and asserted positive trends in males for renal tubular
carcinomas in one study and for hemangiosarcoma in the other. However EFSA took a
weight-of-evidence approach; with considerations including the statistical significance being
only found in trend analysis but not in pairwise comparison, lack of consistency in multiple
animal studies, the fact that the slightly increased incidences only occurred at doses higher
than those recommended for the oral route in carcinogenicity studies, incidences in test
animals generally being within the historical range for control groups, and the lack of pre-neoplastic lesions.
Rat studies
Five feeding studies in rats and two drinking water studies with glyphosate were reviewed by the IWG.
Drinking water
One study in Sprague-Dawley rats was considered by the IWG to be inadequate for
evaluation because of its short exposure duration.
A glyphosate containing drinking water study with Wistar rats did not show any significant increase in tumour incidence.
Dietary administration
Two studies in Sprague-Dawley rats showed a significant increase in the incidence of
pancreatic islet cell adenoma in male rats. One of these studies also showed a significant
positive trend in the incidence of hepatocellular adenoma in males and of the thyroid C-cell
adenoma in females. However two studies (one in Sprague-Dawley and one in Wistar rats)
found no significant increase in tumour incidence at any site.
The IWG reviewed a chronic feeding study (provided by the US EPA) in which groups of 60
female and male Sprague Dawley rats were given diets containing glyphosate at a
concentration of 0, 2,000, 8,000 or 20,000 ppm ad libitum for 24 months. In males at the
lowest dose, there was a statistically significant increase in the incidence of pancreatic islet
cell adenoma compared with controls. Additional analyses by the US EPA revealed a
statistically significant higher incidence of pancreatic islet cell carcinoma in males at the
lowest and highest doses compared with controls: lowest dose, 8/45 (18%); intermediate
dose, 5/49 (10%); highest dose, 7/48 (15%) versus controls, 1/43 (2%). The range for
historical controls for pancreatic cancer islet cell carcinoma reported in males at this
laboratory was 1.8–8.5%. The IWG concluded that this study demonstrated a significant
increase in the incidence of pancreatic islet cell adenoma in male rats.
However the US EPA (1993) had concluded that:
these adenomas were not treatment-related and glyphosate was not considered to be
carcinogenic in this study. With respect to pancreatic islet cells adenomas, there was no
statistically significant positive dose-related trend in their occurrence; there was no
progression to carcinomas; and the incidence of pancreatic hyperplasia (non-neoplastic
lesion) was not dose-related. With respect to hepatocellular adenomas, the increased
incidence of these neoplasms was not statistically significant in comparison with the controls;
the incidence was within the historical control range; there was no progression to
carcinomas; and the incidence of hyperplasia was not compound-related. With respect to
thyroid C-cell adenomas, there was no statistically significant dose-related trend in their
occurrence; the increased incidence was not statistically significant; there was no
progression to carcinomas; and there was no significant dose-related increase in severity or
incidence of hyperplasia in either sex”.
Also, in the JMPR (WHO 2006) review of this study they reported:
The historical-control range for this tumour at the testing laboratory was 1.8–8.5%, but a
partial review of studies reported recently in the literature revealed a prevalence of 0–17% in
control males with several values being ³ 8%. More importantly, the incidences of islet cell
adenomas clearly did not follow a dose-related trend in the treated groups of males. There
was no evidence of dose-related pancreatic damage or pre-neoplastic lesions. The only
pancreatic islet cell carcinoma found in this study occurred in a male in the control group,
thus indicating a lack of treatment-induced neoplastic progression. Taken together, the data
support the conclusion that the occurrence of pancreatic islet cell adenomas in male rats
was spontaneous in origin and unrelated to administration of glyphosate”.
Review articles – rat studies
The IWG noted that Griem et al, (2015) had published a review article containing
assessments of nine long-term glyphosate feeding studies in rats. Five of these studies were
reviewed by the IWG. The remaining four studies were not evaluated by the IWG which
stated that there was limited experimental data provided in the review article. These four
studies had been submitted to various organisations for registration purposes. There was no
evidence of a carcinogenic effect related to glyphosate treatment.
Its long-term toxicity and carcinogenicity was assessed in nine rat studies. The EFSA peer
review concluded that no significant increase in tumour incidence was apparent. Three of
these studies were not evaluated by the IARC panel. In two studies, increased incidences of
pancreatic islet cell adenomas were found but were not dose-related. EFSA also noted that
the significance of these findings depended on the statistical analysis: using a pairwise
comparison (as planned for in the study protocol) no significant effect is observed, whereas
a trend analysis performed by the IWG identified significant changes. EFSA noted that
deviations from the statistical analysis used by the study authors should be limited and
properly justified.
Other relevant data
The IWG group noted that soil microbes degrade glyphosate to aminomethylphosphonic acid
(AMPA). Blood AMPA detection after glyphosate poisoning incidents suggests intestinal
microbial metabolism in humans.
Glyphosate has been detected in the blood and urine of agricultural workers, indicating
absorption. Neimann et al, (2015) published a critical review and comparison of data
obtained in a total of seven studies from Europe and the US. They concluded that no health
concern was revealed because the resulting exposure estimates were several magnitudes
lower than the acceptable daily intake (ADI) or the acceptable operator exposure level
The measured internal exposure was clearly below the worst-case predictions made in the
evaluation of glyphosate as performed for the renewal of its approval within the European Union.
This is consistent with the risk-based approach that regulatory agencies use when
considering realistic dosages and real-life conditions. Those studies show that farmers and
farm families are exposed to significantly lower doses of the herbicide than some model
estimates would suggest.
It is also in keeping with an earlier review (Williams et al, 2000) of the animal data, in which
dose levels from animal toxicity tests were compared to conservative, upper-limit estimates
of human exposure to glyphosate, to give a margin of exposure (MOE) value. MOE analyses
compare the lowest NOAELs determined from animal studies to worst-case levels of human
exposure; with MOEs of greater than 100 indicating confidence that no adverse health
effects would occur. These authors found in their review that the MOEs for worst-case
chronic exposure to glyphosate ranged from 3,370 to 5,420, and concluded that under
present and expected conditions of use, Roundup herbicide does not pose a health risk to humans”.
The IWG claimed that there is strong evidence that glyphosate is genotoxic. They tabulated
numerous reports of tests relating to the genotoxicity of glyphosate and its formulations, with
some showing a positive association, and some a negative association.
The evaluation of the large volume of genotoxicity data available requires consideration of
assay system validation, test system species used, relevance of the endpoint to heritable
mutation, reproducibility and consistency of effects and dose-response, and relationship of
effects to toxicity. The guidelines for genetic toxicology tests developed for the OECD are a
pre-eminent source of internationally agreed guidelines.
There were often inconsistent results reported (both positive and negative) from the same
test systems in different laboratories. The relevance of many of the assays in test system
species (fish, oysters, insects, snails, worms and caimans) which have never been validated
for the assessment of genotoxicity in humans for regulatory purposes, is questionable.
Additionally the intraperitoneal route of exposure for many of the mammalian in vivo studies
is not appropriate since it does not reflect normal human exposure, with doses exceeding
occupational exposure by orders of magnitude.
Kier and Kirkland (2013) published a review of the genotoxicity of glyphosate and
glyphosate-based formulations. This review concluded that there was a strong weight of
evidence that glyphosate and its formulations are predominantly negative in well-conducted,
core bacterial reversion and in vivo mammalian micronucleus and chromosomal aberration
assays. Although some positive results for glyphosate and glyphosate-based formulations
were reported in DNA damage assays, and for the micronucleus endpoint for formulations in
non-mammalian studies, the positive results were associated with high dose levels and/or
overt toxic effects. The preponderance of negative results in core assays supports the
conclusion that reports of DNA damage or non-mammalian micronucleus effects are likely to
be secondary to cytotoxicity rather than indicative of DNA-reactive mechanisms.
The IWG found that glyphosate and glyphosate formulations induced DNA and chromosomal
damage in mammals, and in human and animal cells in vitro. They referred to one study
(Bolognesi, 2009) reporting increases in blood markers of chromosomal damage
(micronuclei) in residents of several communities after spraying of glyphosate formulations,
to support this contention of genotoxicity.
However, the authors of the Bolognesi (2009) study concluded that overall, data suggesting
that genotoxic damage (as evidenced by the micronuclei test) associated with glyphosate
spraying for control of illicit crops is slim, and any such effect appears to be transient.
Evidence indicates that the genotoxic risk potentially associated with exposure to glyphosate
in the areas where the herbicide is applied for coca and poppy eradication is low. The
attribution of a genotoxic effect due to glyphosate exposure rather than a multitude of other
demographic and environmental causes seems rather tenuous given the uncertainty of
actual exposure.
In a recent communication, EFSA summarised their appraisal of the genotoxicity studies. In
vitro tests of mutagenicity gave consistently negative results. In vitro tests of mammalian
chromosome aberration (all of those which had been performed under GLP conditions) were
also negative. Positive results were found in some published in vitro studies of chromosomal
aberrations, but these were not confirmed by in vivo studies addressing the appropriate
endpoints, such as the micronucleus test.
As regards in vivo tests, all studies conducted according to internationally validated
guidelines for good laboratory practice (GLP) and some non-GLP published studies gave
negative results. Two non-GLP studies were positive in mice treated intraperitoneally, but at
levels close to or above the LD503 (possibly suggestive that this is a secondary effect), and
one study had major flaws. No genotoxic effects on germ cells have been detected in rats or
mice treated orally at dose levels up to 2,000 mg/kg/day (the maximum dose level
recommended for such studies). EFSA concluded that, considering the weight of evidence,
glyphosate is unlikely to be genotoxic in vivo.
As regards glyphosate-based commercial formulations, a number of formulations with
unknown composition have given positive results when tested in vitro and in vivo. However
some of the test systems are not validated and/or interpretation is difficult due to possible
confounding, such as cytotoxicity, specific organ toxicity or unclear relevance to humans
(such as tests in fish, amphibians, or invertebrates). Some of the co-formulants (such as
polyethoxylated tallow amine (often abbreviated to POEA)) may be more systemically toxic
than glyphosate. However EFSA concluded that the genotoxic potential of such complete
formulations should be further assessed.
Kier (2015) reviewed genotoxicity biomonitoring studies of glyphosate-based formulations.
He found that most of the human biomonitoring studies were not informative because there
was either a very low frequency of exposure to glyphosate formulations or exposure to a
large number of pesticides in addition to glyphosate without analysis of specific pesticide
effects. One pesticide sprayer biomonitoring study indicated there was no statistically
significant relationship between frequency of exposure to glyphosate formulations reported
for the last spraying season and oxidative DNA damage. There were three studies of human
populations in regions of glyphosate formulation aerial spraying. One study found increases
for the cytokinesis-block micronucleus endpoint but these increases did not show statistically
significant associations with self-reported spray exposure and were not consistent with
application rates. A second study found increases for the blood cell comet endpoint at high
exposures causing toxicity. However, a follow-up to this study two years after spraying did not indicate chromosomal effects.
Oxidative stress
The IWG found that glyphosate, glyphosate formulations, and AMPA induced oxidative stress in rodents and in vitro.
Oxidative stress was only found in one study in rats administered intraperitoneal glyphosate active ingredient (Astiz et al, 2009), and in numerous studies using intraperitoneal administration or in vitro methods with glyphosate-based formulations. However, these studies used doses that exceeded normal occupational exposures by orders of magnitude
and the intraperitoneal route of exposure is not appropriate for evaluating human exposure.
Glyphosate has low gastrointestinal absorption and poor dermal absorption. It therefore
[LD50 is the dose of the substance required (usually expressed in relation to body weight) that
is estimated to kill 50% of the test population].
seems unlikely that human exposure would produce the sort of tissue levels used in the
oxidative stress tests. There was also some inconsistency in results.
Most effects were seen when whole glyphosate formulations were tested. EFSA considered
that generally testing of formulations should not be used for the toxicological evaluation of
active substances because co-formulants may extensively alter the outcome. Thus any
effects found cannot then be attributed to the glyphosate active ingredient present.
The IARC WG (IWG) classified glyphosate as probably carcinogenic to humans (Group 2A)”
as the overall evaluation.
As set out in their evaluation section, this was based on:
· limited evidence” in humans for the carcinogenicity of glyphosate, and
sufficient evidence” in experimental animals for carcinogenicity of glyphosate.
The rationale identifies that the IWG also notes mechanistic and other relevant data in
support of the conclusion; in particular the IWG cites strong evidence” that glyphosate can operate by two key characteristics of known human carcinogens, namely genotoxicity and oxidative stress.
This discussion section of the report will consider each of these sources of evidence in turn as contributing factors to the IWG’s overall evaluation.
Human epidemiological evidence
The key cited studies in support of the limited evidence” in humans for carcinogenicity of glyphosate consisted of three case-control investigations. The odds ratios (OR) for cases of
NHL and glyphosate exposures are summarised in the following table.
Odds ratios (OR) for cases of NHL and glyphosate exposures
Study area
OR1 and 95% CI2
Study reference
Midwest, USA
2.1 (1.1–4.0) [logistic
De Roos et al, 2003
1.6 (0.9–2.8) [hierarchical
1.26 (0.87–1.8)
McDuffie et al, 2001
1.20 (0.83–1.74) [adjusted for
medical variables]
2.02 (1.1–3.71) [univariate]
Erikson et al, 2008
1.51 (0.77–2.94) [multivariate]
1. OR is the odds ratio of outcome of interest between the relevant case group and the reference or control
2. The 95% CI are the confidence intervals round the OR representing the limits within which there is 95%
confidence that the true value falls.
The first important observation is that depending on the statistical tests used only two
studies (Midwest USA and Sweden) show OR values indicating statistical significance at the
95% level. In the Midwest USA, however, this is only true using logistic regression, while in
the Swedish study only the univariate analysis showed statistical significance.
Some case control studies assessed data using dose (exposure)/response or
intensity/response to determine whether or not there is a trend to a higher incidence of
tumours in persons categorised as having higher exposures to glyphosate. While these
approaches are desirable, the criteria of exposure seem low. For one case-control study, the
criterion for high or lower glyphosate use was greater than or less than two days of
glyphosate use/year (McDuffie et al, 2001), whereas in another the criterion was greater
than or less than 10 days of glyphosate use/year (Eriksson et al, 2008). While the
distribution of use category was not given in either study, 2–10 days of use per year seems a
low benchmark for exposure comparisons. The direct glyphosate exposure findings with
respect to NHL was not significant in the McDuffie et al, 2001 study, but they reported a
dose response based on this dose comparison and quoted the OR for exposure >2 day/year
as 2.12 (95% CI 1.20–3.73).
The direct glyphosate exposure findings with respect to NHL were significant in the Swedish
study using univariate evaluation, and the effect of dose-response in the Swedish study
appears to only be statistically significant using this approach (considering the data
presented in the IARC Monograph in Table 2.2, p23) which reported a higher OR for heavy”
users (>10 days/year) of 2.36 (95% CI 1.04–5.37). It is noteworthy that the paper reports the
highest OR, 2.81 (95% CI 1.27–6.22), for the association between exposure to MCPA and
NHL. This may be the explanation for the difference between the results using univariate and
multivariate evaluation. When considering the latency period, >10 years exposure to
glyphosate had an OR of 2.26 (95% CI 1.16–4.4) in comparison to ≤ 10 years with an OR of
1.11 (95% CI 0.24–5.08), but these findings may be confounded by exposure to MCPA or
other phenoxy herbicide exposures. There could be residual confounding from MCPA
exposure if the participants under-reported earlier MCPA exposure. The apparent increased
risk with latency for glyphosate exposure could be because participants who had sprayed
pesticides for longer were more likely to have used the phenoxy herbicides (including
MCPA) earlier in their working lives.
The AHS cohort study (De Roos, et al, 2005) had a more detailed assessment at different
exposure intensities as they used cumulative lifetime days of use and an intensity measure
(years of use x days/year x estimated exposure level). The data (presented in Table 2.1 of
the IARC Monograph on p12) for this cohort study showed no statistically significant
difference for the trend to increased exposure with exposure bands at 0–20, 21–56 and 57–
2,678 cumulative days of exposure, despite the higher exposure levels in comparison to the case-control studies.
It is important in these circumstances to consider the overall data set. Rather than only
highlighting the three case-control studies which identified a marginally statistically
significant association between reported glyphosate use and NHL, the overall assessment needs to take into account other studies which did not demonstrate such an association.
Also, it is particularly important to note the lack of significant finding in a large cohort study
(the AHS) where the potential for recall bias is greatly reduced and should therefore be given
greater weight than the case control studies. Cohort studies are generally considered more
reliable than case-control studies, because the population is defined and the exposure
parameters and the potential confounding exposures and lifestyle factors are established
prior to the adverse outcome of interest so that the potential for recall bias is less likely.
Given the lack of confirmation of the small number of positive findings from case-control
studies in the more powerful cohort study, the epidemiological support for the conclusion limited evidence” in humans is not convincing.
Experimental animal studies
The key cited studies in support of the sufficient evidence” in experimental animals for carcinogenicity of glyphosate consisted of three studies in mice. These comprised one oral study demonstrating a positive trend for increased incidence of renal tubule carcinoma, one oral study in mice demonstrating a positive trend for increased incidence of hemangiosarcoma; and a supporting skin study demonstrating tumour promotion using a
glyphosate formulation. In addition, one rat study demonstrated an increased incidence of
pancreatic islet cell adenomas.
In assessing these data, the IWG used different statistical tests to those in the original
analysis (trend analysis rather than a pairwise comparison against controls). The original
studies were designed with the intention to assess statistical significance by means of a
pairwise comparison between the test and control groups, so use of the trend assessment
by IARC to assess these data requires justification. IARC’s use of the trend assessment
gave a positive response, but in none of the studies are the positive effects statistically
significant using the original statistical approaches. Also, the IWG did not take into account
the generally accepted assessment of the same data by international panels of experts,
which took into account additional historical incidence data for hepatocellular adenomas in
the rats and the presence of a viral infection in the mouse study which could have influenced
survival rates and the incidence of lymphomas.
The promotion study using a glyphosate-based formulation should not be used as support
for the carcinogenicity of glyphosate per se, since the test substance contains other
components which might influence the outcome.
The IWG did not evaluate some other studies which have been used by other regulators.
These did not support the view that exposure to glyphosate in long-term feeding studies was
associated with an increase in tumours at any sites. While the IWG approach is consistent
with the IARC pre-amble and policy on the selection of study data, in the current
circumstances this attributes inappropriate weight to the three studies which IWG considered
and for which their analysis found an increase in tumours. Firstly because other studies
which other reputable bodies found to be negative were not considered, and secondly
because the reasons why the above findings were not relied upon by other assessments
were not taken into account by the IWG. In particular a lack of consistency (dose-response) in multiple studies, slight increases in incidence at the maximum tested dose only, or incidences within the historical control range.
Taking into account that the positive findings cited by the IWG were not assessed as
evidence of a carcinogenic effect in the view of other reputable bodies, and that the total
data set of long-term carcinogenicity bioassays were consistently negative, it is concluded
that the overall weight of evidence does not indicate that glyphosate is carcinogenic.
Mechanism of action
The IWG cites what is described as strong evidence” that glyphosate can operate by two
key characteristics of known human carcinogens – genotoxicity and oxidative stress.
The studies used in support of this conclusion were primarily in vitro mammalian cell studies.
In such studies the mammalian cells are directly exposed to the test substance (glyphosate
or a glyphosate-based formulation) at high concentrations which would not be reasonably
achieved in an in vivo exposure whether in animals or humans. All studies done according to
internationally validated guidelines gave negative results, while studies using unvalidated
test method/species, or with glyphosate-containing formulations or using high intraperitoneal
doses are inappropriate for assessment of genotoxicity to humans.
Other supporting evidence for this conclusion included DNA damage and micronuclei in
various populations allegedly exposed to glyphosate from sprays. Attributing the effects
found to the exposure to glyphosate is questionable when the exposure, if any, was to
glyphosate-based formulations and unidentified demographic, geographical or lifestyle
factors that could be responsible for the DNA damage.
In relation to oxidative stress this was only found in one study in rats administered
intraperitoneal glyphosate active ingredient (Astiz et al, 2009), and in numerous studies
using intraperitoneal administration or in vitro methods with glyphosate-based formulations.
The intraperitoneal route of administration is not considered relevant to human exposures.
Glyphosate has low gastrointestinal absorption and poor dermal absorption. There was also some inconsistency in results. So the evidence for glyphosate causing oxidative stress is considered weak.
The overall conclusion is that – based on a weight of evidence approach, taking into account the quality and reliability of the available data – glyphosate is unlikely to be genotoxic or carcinogenic to humans and does not require classification under HSNO as a carcinogen or mutagen.
Alavanja MC, Samanic C, Dosemeci M, et al. Use of agricultural pesticides and prostate
cancer risk in the Agricultural Health Study cohort. American Journal of Epidemiology 157:
Andreotti G, Freeman LE, Hou L, et al, (2009). Agricultural pesticide use and pancreatic
cancer risk in the Agricultural Health Study Cohort. Int J Cancer 124: 2495–2500.
Astiz M, de Alaniz MJ, Marra CA (2009). Antioxidant defense system in rats simultaneously
intoxicated with agrochemicals. Environ toxicol pharmacol 28:465–473.
Blair A, et al. Carcinogenicity of tetrachlorvinphos, parathion, malathion, diazinon, and
glyphosate. Lancet Oncology 2015; 16: 49–1.
BfR (2015) Does glyphosate cause cancer? BfR Communication No 007/2015, 23 March
Bolognesi C, Carrasquila G, Volpi S, Solomon KR, Marshall EJ (2009). Biomonitoring of
genotoxic risk in agricultural workers from five Columbian regions: association to
occupational exposure to glyphosate. J Toxicol Environ Health A, 72(15–16):986–97.
Brown LM, Blair A, Gibson R, et al (1990). Pesticide exposures and other agricultural risk
factors for leukemia among men in Iowa and Minnesota. Cancer Res 50: 6585–91.
Brown LM, Burmeister LF, Everett G, et al (1993). Pesticide exposures and multiple
myeloma in Iowa men. Cancer Causes Control 4: 153–6.
Cantor KP, Blair A, Everett G, et al (1992). Pesticides and other agricultural risk factors for
non-Hodgkin’s lymphoma among men in Iowa and Minnesota. Cancer Res 52: 2447–55.
Dennis LK, Lynch CF, Sandler DP, et al (2010). Pesticide use and cutaneous melanoma in
pesticide applicators in the agricultural health study. Environ Health Perspect 118: 812–7.
De Roos AJ, Zahm SH, Cantor KP, Weisenburger DD, Holmes FF, Burmeister LF et al,
(2003). Integrative assessment of multiple pesticides as risk factors for non-Hodgkins
lymphoma among men. Occup Environ Med, 60(9):E11.
De Roos AJ, Blair A, Rusiecki JA, Hoppin JA, Svec M, Dosemeci M et al, (2005). Cancer
incidence among glyphosate-exposed pesticide in the Agricultural Health Study. Environ
Health Perspect, 113(1):49–54.
Engel LS, Hill DA, Hoppin JA, et al, (2005). Pesticide use and breast cancer risk among
farmers’ wives in the agricultural health study. Am J Epidemiol 161: 121–35.
Erikkson M, Hardell L, Carlberg M, Akerman M (2008). Pesticide exposure as risk factor for
non-Hodgkin lymphoma including histopathological subgroup analysis. Int J Cancer,
European Food Safety Authority. EFSA explains the carcinogenicity assessment of
glyphosate. 12 November 2015.
EFSA (European Food Safety Authority), 2015. Peer review of the pesticide risk assessment
of the active substance glyphosate. EFSA Journal 2015;13(11):4302, 107 pp.
Flower KB, Hoppin JA, Lynch CF, et al. Cancer risk and parental pesticide application in
children of Agricultural Health Study participants. Environ Health Perspect 2004; 112: 631–5.
Greim H, Saltmiras D, Mostert V, Strupp C (2015). Evaluation of carcinogenic potential of the
herbicide glyphosate, drawing on tumor incidence data from fourteen chronic/carcinogenicity
rodent studies. Crit Rev Toxicol, 45(3):185–208.
Hoar SK, Blair A, Holmes FF, et al. Agricultural herbicide use and risk of lymphoma and soft
tissue sarcoma. JAMA 1986; 256: 1141–7.
International Agency for Research on Cancer Volume 112: Some organophosphate
insecticides and herbicides: tetrachlorvinphos, parathion, malathion, diazinon and
glyphosate. IARC Working Group. Lyon; 3–10 March 2015. IARC Monographs on the
Evaluation of Carcinogenic Risks to Humans (in press).
Kier LD, Kirkland DJ (2013). Review of genotoxicity studies of glyphosate and glyphosate-
based formulations. Crit Rev Toxicol. 43(4):283–315.
Kier LD (2015). Review of genotoxicity biomonitoring studies of glyphosate-based
formulations. Crit Rev Toxicol. 45(3):209–18.
Lash TL (2007). Bias analysis applied to Agricultural Health Study publications to estimate
non-random sources of uncertainty. J Occup Med Toxicol 2; 15.
Lee WJ, Sandler DP, Blair A, et al, (2007). Pesticide use and colorectal cancer risk in the
Agricultural Health Study. Int J Cancer 121: 339–46.
McDuffie, HH, Pahwa, P, McLaughlin, JR, Spinelli, JJ, Fincham, S, Dosman, JA, Robson, D,
Skinnider, LF & Choi, NW (2001) Non-Hodgkin’s lymphoma and specific pesticide exposure
in men: Cross-Canada study of pesticides and health. Cancer Epidemiol. Biomark. Prev., 10,
Mink PJ, Mandel JS, Sceurman BK, Lundin JI. (2012). Epidemiologic studies of glyphosate
and cancer: a review. Regul Toxicol Pharmacol, 63,440–52.
Morgan GJ, Davies FE, Linet M. Myeloma aetiology and epidemiology. Biomedicine and
Pharmacotherapy 2002; 56(5): 223–34.
L Niemann, C Sieke, R Pfeil and R Solecki (2015). A critical review of glyphosate findings in
human urine samples and comparison with the exposure of operators and consumers. J.
Verbr. Lebensm, 10:3–12.
Schinasi L, Leon ME. 2014. Non-Hodgkin lymphoma and occupational exposure to
agricultural pesticide chemical groups and active ingredients: a systematic review and meta-
analysis. Int J Environ Res Public Health 11(4): 4449–527.
Sorahan T. Multiple myeloma and glyphosate use: a re-analysis of US Agricultural Health
Study (AHS) data. Int J Environ Res Public Health 2015; 12: 1548–59.
US EPA (1993) Reregistration eligibility decision (RED): glyphosate
WHO (2006) Joint Meeting of the FAO Panel of Experts on Pesticides Residues in Food and
the Environment and the WHO Core Assessment Group (2004 : Rome, Italy) Pesticide
residues in food : 2004 : toxicological evaluations : part II / Joint Meeting of the FAO Panel of
Experts on Pesticides Residues in Food and the Environment and the WHO Core
Assessment Group, Rome, Italy 20–29 September 2004.
Williams GM, Kroes R, Munro IC (2000). Safety evaluation and risk assessment of the
herbicide Roundup and its active ingredient, glyphosate, for humans. Reg Toxicol Pharmacol
31: 117–65.
Zahm SH, Weisenburger DD, Babbitt PA, et al. A case-control study of non-Hodgkin’s
lymphoma and the herbicide 2,4-dichlorophenoxyacetic acid (2,4-D) in eastern Nebraska.
Epidemiology 1990; 1: 349–56.
Dr Michael Beasley MBChB, DComH, MSc, DIH, FFOM (I) for valuable assistance
with the preparation of this review.

One Response to “The New Zealand governmet clear the wedicide Glyphosate as perfectly safe for use.”

  1. NAK Says:

    Several times I tried to read this but fell asleep. So I decided to skip this thinking that our former registrar of pesticides must have got a posting in NZ!

Leave a Reply

You must be logged in to post a comment.



Copyright © 2024 All Rights Reserved. Powered by Wordpress