From ghegyes@nalusda.gov Thu Jul  7 03:35:07 1994
Date: Wed, 6 Jul 1994 22:54:21 -0400 (EDT)
From: Gabriel Hegyes <ghegyes@nalusda.gov>
To: KATY%smtpgate@earth.wri.org
Cc: SANET-mg <sanet-mg@ces.ncsu.edu>
Subject: Re: Round)Up Breaking Down in Water

>From ghegyes@nalusda.gov Wed Jul  6 22:53:11 1994
Date: Wed, 6 Jul 94 22:52:01 EDT
From: Gabriel Hegyes <ghegyes@nalusda.gov>
Subject: glyphosa.osu

                         E X T O X N E T

                  Extension Toxicology Network

A Pesticide Information Project of Cooperative Extension Offices
of Cornell University, The University of California,  Michigan
State University, and Oregon State University

Extoxnet is a collaborative educational project intended to
convey pesticide-related information in easily understood terms. 
Information is provided in two types of documents:  Pesticide
Information Profiles (PIPs) on the health and environmental
effects of specific pesticides, and Toxicology Information Briefs
(TIBs), short descriptions of a variety of issues that pertain to
pesticides, such as carcinogenicity, ecological effects, and
epidemiology.  The TIBs are intended to assist in the
understanding and interpretation of information in the PIPs. 
Data presented through EXTOXNET documents are not based on an
exhaustive literature search.
                              E X T O X N E T
                       Extension Toxicology Network

                     Source:  Oregon State University
                           January, 1989

GLYPHOSATE

[7mRoundup[m, Rodeo

     A broad-spectrum, non-selective systemic herbicide which is highly 
active on essentially all annual and perennial plants. Glyphosate is 
usually formulated as an isopropylamine salt. While glyphosate can be 
described as an organophosphorus compound, it is not an organophosphate 
ester but a phosphanoglycine, and does not inhibit acetylcholinesterase 
activity(5).

TOXICOLOGICAL EFFECTS

Acute:

     The toxicity of the technical product (glyphosate) and the 
formulated product ([7mRoundup[m) is reported as almost the same value, even 
though the formulated product is only 41% glyphosate. This is unusual. 
For instance, one study of rat oral LD50s showed 4300 to 5600 mg/kg for 
the technical material, 5400 mg/kg for [7mRoundup[m and greater than 4900 
mg/kg for isopropylamine salt. Other oral LD50s for the technical 
material were 1538 to greater than 10,000 mg/kg for mice, rabbits 3500 
mg/kg, and goats 3530 to 5400 mg/kg (1,5).

     The dermal LD50 for [7mRoundup[m to rats is greater than 17,600 mg/kg 
and greater than 5000 in rabbits. In 50 human volunteers, patch tests 
produced no visible skin changes or sensitization. Inhalation LC50 for 
rats after a four-hour exposure was 3200 mg/cubic meter; there was no 
response at 1600 mg/cubic meter(1,5).

Chronic:

     Subchronic and chronic tests with glyphosate have been conducted 
with rats, dogs, mice, and rabbits in studies lasting from 21 days to 
two years. With few exceptions there were no treatment-related gross or 
cellular changes. Rats on levels greater than 5000 ppm for 90 days had 
some lung weight differences which were of uncertain significance in the 
absence of adverse cellular finding in the lungs of the animals(5). Mice 
on diets of 50,000 ppm for 90 days had reduced body weight gains and 
lifetime administration of 300,000 ppm (5400 mg/kg/day) produced a 
slight reduction of body weight and equivocal, microscopic liver and 
kidney changes. Blood chemistry and cellular components, and organ 
function were not effected.

     Neurotoxicity tests with hens fed 7.5 g/kg over three days and 
repeated 21 days later produced no effects. There was no microscopic 
evidence of nerve damage.

Reproductive:

     Two three-generation studies on rats have been performed. In the 
first study there was some reduction of fertility at the 300 ppm 
level(4). However this could not be reproduced in the second study and a 
NOEL of 10 mg/kg/day was established for reproductive effects. Wild deer 
mice suffered no apparent reproductive effects when a coniferous forest 
was sprayed at 2 lbs/acre(4).

Teratogenicity:

     Rabbits receiving 30 mg/kg/day by stomach tube on days 6 through 15 
of gestation had offspring with fetotoxic or teratogenic effects. At 
doses of 350 mg/kg/day on days 6 through 27, the dams suffered numerous 
toxic effects and some death, but no teratogenic effects were noted in 
the offspring.

     Rats given doses up to 3500 mg/kg on days 6 to 19 of gestation had 
offspring with no teratogenic effects but there were maternal and 
fetotoxic effects. No fetotoxic effects occurred at 1000 mg/kg/day.

Mutagenicity:

     Dominant lethal, host-mediated, or rec-assay tests were negative, 
as were tests in seven bacterial and one yeast systems. In human 
lymphocytes, the formulated product may be weakly active(5).

Carcinogenicity:

     Rats and dogs fed 300 ppm in their diets for two years had no 
increase in occurrence, type, or number of benign or malignant tumors. 
Rats showed some increase in microscopic lipid droplets in the liver(5). 
This effect was not seen in a later study at levels up to 600 ppm(4).

     Mice on diets containing up to 3% glyphosate (5400 mg/kg/day) had 
reduced body weights and equivocal liver and kidney changes but no 
carcinogenic effects. Blood samples were taken periodically and a series 
of functions evaluated. All tissues and organs were examined for cancer 
upon death or sacrifice.

Organ Toxicity:

     A disputed study where glyphosate was administrated into the 
stomach cavity of rats at doses up to 60 mg/kg for 28 days showed weight 
gain effects and blood effects. These are effects similar to those 
caused by materials which alter mitochondrial energy transformation(1).

Fate in Humans and Animals:

     Glyphosate is poorly absorbed from the digestive tract and is 
excreted unchanged by mammals. Rats excreted 99% and rabbits excreted 
about 90% of a single oral dose in 120 hours. Ten days after treatment 
there was 0.1 ppm or less in the tissues of rats fed 100 ppm for 19 
days. No single tissue showed accumulated(3).

     Cows, chickens, and pigs fed up to 75 ppm had undetectable levels 
(less than 0.05 ppm) in muscle tissue and fat. Levels in milk and eggs 
were also undetectable (less than 0.025 ppm).


ECOLOGICAL EFFECTS

     Mallards and bobwhite quail both had an LC50 of greater than 4640 
ppm. Hatchability or time to hatch of domestic chicken eggs dipped in a 
solution of 5% had no effect. The bioaccumulation factor in chicken 
muscle, fat, eggs, and liver was as low as 1/10,000 of the environmental 
concentration(4).

     In fish the formulated product, [7mRoundup[m, was more toxic than 
glyphosate. In rainbow trout, for instance, the 96-hour LC50 was 8.3 ppm 
with [7mRoundup[m and 38 ppm with glyphosate. For bluegill the 96-hour LC50 
was 5 ppm, 78 ppm for glyphosate. The surfactant used in the [7mRoundup[m 
formulation (a modified tallow amine) is apparently somewhat more toxic 
to fish than many common surfactants. For this reason, the formulation 
for use in aquatic situations (Rodeo) omits the surfactant. There is a 
bioconcentration factor of 0.1 to 0.3 (fish/water).

     Bees have both an oral and dermal LD50 of greater than 100 ug/per 
bee.

ENVIRONMENTAL FATE

     Glyphosate is highly adsorbed on most soils especially those with 
high organic content. One study showed 7% of the applied material in the 
leachate from 30 centimeter columns. Microbial action is responsible for 
degradation with a half-life of 3 to 130 days. The primary metabolite 
aminomethyl phosphonic acid (AMPA), degrades somewhat slower than the 
parent.

     Glyphosate is strongly adsorbed to both organic and mineral matter 
and is degraded primarily by microorganisms in water to AMPA. Half-lives 
in ponds range from 12 days to 10 weeks. Because glyphosate is so 
tightly bound to the soil, not much is picked up by rain or irrigation 
water. One estimate had 1.85% of the applied chemical lost to runoff(4). 
Photodecomposition plays a minor role in environmental breakdown.

     The prime mode of action in plants is on the shikimic acid pathway. 
It appears that glyphosate may be extensively metabolized by some plants 
while remaining intact in others(2). Once in the plant tissue, the 
chemical is translocated throughout the plant including the roots. The 
half-time in forest vegetation is less than four weeks.


BASIC MANUFACTURER

Monsanto Company         Telephone: 314/694-1000
800 N Lindbergh Blvd
St Louis, MO 63167       Emergency: 314/694-4000

                                <continued>
PHYSICAL PROPERTIES
Common name               glyphosate
CAS # 1071-83-6           N-(phosphonomethyl)glycine
Chemical class/use        phosphanoglycine compound/herbicide
Solubility in water       10,000 ppm
Solubility in solvent     insoluble in common organics
Melting Point             200 degrees C
Vapor Pressure            "negligible" (Monsanto)
Dissociation values       2.27 (pKa)
Partition Coefficient     0.17 X 10 to the minus 2 at 20 ppm
                          0.6 X 10 to the minus 3 at 100 ppm

Exposure Guidelines
  NOEL
     rat                  10 mg/kg (ppm); renal; three generation
  HA                      700 ug/l (ppb) (lifetime)
  ADI                     0.03 mg/kg (ppm) (EPA)
                          0.3 mg/kg (ppm) (WHO)

                                <continued>
REFERENCES

1. National Library of Medicine (1987). Hazardous Substances Databank.
   TOXNET, Medlars Management Section, Bethesda, MD.

2. Grossbard, E. and D. Atkinson, Editors (1985). The Herbicide
   Glyphosate, Butterworths, Boston, MA.


3. U. S. Environmental Protection Agency (1987). Health Advisory, Office
   of Drinking Water.

4. Forest Service, (1984). Pesticide Background Statements, Vol. I
   Herbicides. United States Dept.of Agriculture, Agriculture Handbook
   No. 633.

5. Monsanto Company (1985). Toxicology of Glyphosate and [7mRoundup[m
   Herbicide, Department of Medicine and Environmental Health, St.
   Louis, MO.


DISCLAIMER:  The information in this profile does not in any way replace 
or supersede the information on the pesticide product label/ing or other 
regulatory requirements.  Please refer to the pesticide product 
label/ing.
------------------
Gabriel A. Hegyes
Sustainable Agriculture Network
ghegyes@nalusda.gov


 



On Wed, 6 Jul 1994 KATY%smtpgate@earth.wri.org wrote:

> If this request does not follow proper netiquette, please let me
> know:  Does anyone have any information as to whether or not
> Round-Up breaks down in water?  Thanks very much :)
> 
> 
> 
> 
