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新《生活饮用水卫生标准》GB5749-项目解读:草甘膦(GLYPHOSATE)
2008年09月22日  来源:中国滤材网  [进入论坛讨论]  编辑:ヤo_o灀懵蝶

分子式C3H8NO5P  分子量:169.08

结构式

O     O

    ‖

HOCCH2NHCH2P(OH)2

1.概述

草甘膦为有机磷类除草剂。商品名称为草甘膦(glyphosate)。化学 名称是N-(膦羧甲基)甘氨酸[N-(phosphono methyl)glycine]。

草甘膦主要通过抑制植物体内烯醇丙酮基莽草素磷酸合成酶,从而抑制莽草素向苯丙氨酸、酪氨酸及色氨酸的转化,使蛋白质的合成受到干扰导致植物死亡。草甘膦以内吸传导性强而 著称,且杀草谱很广,但豆科和百合科一些植物对草甘膦的抗性较强。草甘膦入土后很快与铁、铝等金属离子结合而失去活性,对土壤中潜藏的种子和土壤微生物无不良影响。

按我国农药毒性分级标准,草甘膦属低毒除草剂。原粉大鼠急性经口LD50为4300mg /kg,兔急性经皮LD50>5000mg/kg。在试验条件下对动物未见致畸、致突变,致癌作用。大鼠三代繁殖试验未见异常。大鼠两年饲喂试验无作用剂量为34.02(雌)和31.49( 雄)mg/kg/d。草甘膦对鱼和水生物毒性较低,对蜜蜂和鸟类无毒害。

草甘膦制剂有农达41%水剂;10%草甘膦铵盐水剂。进口商品农达41%水剂由草甘膦异丙胺盐41%,表面活性剂和水组成。

农达41%水剂已在我国正式登记,登记号PD73-88,登记作物为柑桔园。登记厂家为美国孟 山都公司(Monsanto Company)。

2.性质

纯品为非挥发性白色固体,约在230℃左右熔化,并伴随分解。25℃时水中溶解度为1.2%,不溶于一般有机溶剂,其异丙胺盐完全溶于水。不可燃、不爆炸 、常温贮存稳定。原药对中炭钢、镀锌铁皮(马口铁)有腐蚀作用。

农达41%水剂外观为琥珀色透明粘性液体,常温下贮存两年内稳定。

3.用途

用于农田、林业、果园及胶园除草。

4.产制

 

5.主要生产国家

美国孟山都公司

6.产品质量规格

进口农达41%水剂:

有效成分:含草甘膦异丙胺盐41%;比重(20℃):1.17;外观:琥珀色透明粘性液体。

7.包装及储运

进口农达41%水剂的包装是用适宜长途运输海运的塑料桶,每桶净容量200L。

8.检验方法

进口农达41%水剂中有效成分含量的测定可采用液相色谱法。流动相为0.0062M KH2PO4水溶液/甲醇(96/4)。草甘膦标样和试样均用流动相溶解,用 250×4.6mm Partisil 10 SAX不锈钢柱分离,用紫外检测器在195nm处检测,根据标样和试样的色谱峰峰面积和质量计算有效成分的含量。

 

Synonyms Glyphosate
N-(Phosphonomethyl)glycine, isopropylamine salt
Roundup
Molecular Formula C3H8NO5P
Use NON-SELECTIVE, NON-RESIDUAL POST-EMERGENCE HERBICIDE. Very effective on deep-rooted perennial species. Non-selective systemic herbicide, for control of a great variety of annual, biennial, and perennial grasses, sedges, broad-leaved weeds, and woody shrubs. Used in fruit orchards, vineyards, conifer plantations, and many plantation crops (eg coffee, tea, bananas, rubber, coconut, palms, cocoa, mangoes); post-weed emergence but pre-crop-emergence in a wide range of crops (including vegetables, beet, lucerne, okra, soya beans, figs, kiwi fruit, olives, cucurbits, cereals, cotton, etc); on non crop areas; immediately pre-harvest in ripened cereals; in cereal stubble; and in pasture renovation. Also used for pre-harvest desiccation of cotton, cereals, peas, beans, etc; for destruction of rye sown to prevent wind erosion of the soil; for control of suckers on fruit trees; and for aquatic weed control.
Apparent Color WHITE SOLID; Colorless crystals
Odor Odorless
Melting Point 230 DEG C (DECOMP)
Molecular Weight 169.07
Density 0.5 G/CU CM
Environmental Impact Glyphosate is released to the environment in its use as a non-selective, post emergent herbicide for controlling woody and herbaceous weeds on forestry, right-of-way, cropped and non-cropped sites. It is applied as a spray of the isopropylamine salt and is removed from the atmosphere by gravitational settling. After glyphosate is applied to forests, fields, and other land by spraying, it is strongly adsorbed to soil, remains in the upper soil layers, and has a low propensity for leaching. Glyphosate readily and completely biodegrades in soil. Its average half-life in soil is about 60 days. Biodegradation in foliage and litter is somewhat faster. In field studies, residues are often found the following year. Glyphosate may enter aquatic systems through accidental spraying, spray drift, or surface runoff. It dissipates rapidly from the water column as a result of adsorption and possibly biodegradation. The half-life in water is a few days. Sediment is the primary sink for glyphosate. After spraying, glyphosate levels in sediment rise and then decline to low levels in a few months. Glyphosate does not bioconcentrate in aquatic organisms or bioaccumulate in species in higher tropic levels. Occupational workers and home gardeners may be exposed to glyphosate by inhalation and dermal contact during spraying, mixing, and cleanup. They may also be exposed by touching soil and plants to which glyphosate was applied. Occupational exposure may also occur during glyphosate's manufacture, transport storage, and disposal.
Environmental Fate TERRESTRIAL FATE: APPLIED AT 2.6 KG/HA FOR QUACKGRASS ON LOAM & FINE SILT SOILS, GLYPHOSATE WAS IMMEDIATELY DETECTABLE BY GAS CHROMATOGRAPHY AFTER APPLICATION AS WELL AS AT 28 DAYS & 8 MO LATER. UNCHANGED GLYPHOSATE & AMINOMETHYLPHOSPHONIC ACID WERE IDENTIFIED BY GC IN THE SOILS. TERRESTRIAL FATE: After 16 wk, <3% of the starting material is detectable. Strong soil adsorption, slight washing-out or displacement. Would not be expected to persist from one growing season to the next. TERRESTRIAL FATE: Half-life in soil is normally less than 60 days. TERRESTRIAL FATE: After glyphosate is applied to forests, fields, and other land by spraying, its mobility in soil is limited and is affected by pH and phosphate levels, as well as by soil type . In addition to binding to organic matter and clay in soil, it may also form insoluble complexes with metal ions in the soil. Distribution data for glyphosate after spraying in a coastal forest ecosystem indicate that glyphosate is strongly adsorbed to the upper layers of soil and has a low propensity for leaching . Glyphosate residues dissipated with a half-life of 45-60 days. After 360 days, residues levels were 6-18% of initial levels . Field studies on eleven different soils covering a full range of soil types and geographical areas indicates an avg half-life of 60 days for glyphosate in soil . Other sources also report an avg half-life of 60 days from literature surveys(1,5). TERRESTRIAL FATE: The half-life of glyphosate applied to forest foliage was 14.4 days and that applied to two Finnish agricultural fields were 69 and 127 days, respectively . Persistence studies with glyphosate in sandy test sites in a boreal forest in Ontario, Canada indicate that the half-life of glyphosate was 24 days and residues were reduced to <10% of that applied after 78 days . More than 95% of residues were found in the upper organic layer of soil. In aerially treated forest brush fields in the Oregon coast range, the half-life of glyphosate ranged from 10.4-26.6 days in foliage and litter. The half-life of glyphosate on exposed soil and litter-covered soil was 40.2 and 29.2 days, respectively . Glyphosate degrades even under low temperature conditions. TERRESTRIAL FATE: In a Finnish study where the glyphosate was applied to two agricultural fields in September to control quackgrass and the fields plowed after six days, 76% and 10% remained in the field containing loam soil after 28 days and 8 months, respectively . The corresponding values for the field with fine silt was 92% and 53%. The loam soil in which degradation was more rapid had a higher respiration rate. In a similar study in eight forest soils in Sweden at higher temperatures, an avg 20% of the glyphosate applied in August was present in samples taken the following May . AQUATIC FATE: When glyphosate enters water as runoff or inadvertent overspray or spray drift, it adsorbs strongly to sediment and particulate matter in the water column. It may also form insoluble complexes with metal ions and precipitate. Evidence from microcosm studies suggests that sediment adsorption and/or biodegradation represents the major dissipation process in aquatic systems . Glyphosate levels in sediment rise at first and then fall to very low or undetectable levels . After glyphosate was sprayed over two streams in the rainy coastal watershed of British Columbia, glyphosate levels in the streams rose dramatically after the first rain event, 27 hr postapplication, and fell to undetectable levels 96 hr postapplication . The highest residues were associated with sediments, indicating that they were the major sink for glyphosate. Residues persisted throughout the 171 day monitoring period. Suspended sediment is not a major mechanism for glyphosate transport in rivers . The half-lives of glyphosate in three forest ponds in Manitoba, Canada that were aerially spray in August was 1.51 to 1.99 days and glyphosate was not detected in any sample by day 38 . The pond in which glyphosate had the longest half-life had much higher levels of calcium and magnesium than the other ponds. AQUATIC FATE: In aerially treated forest brush fields in the Oregon Coast range, the concentration in streamwater peaked at 0.28 ppm shortly after spraying and declined sharply to undetectable levels in about 6 days . Concentrations in sediment increased slowly to a peak value of 0.55 ppm after 14 days and then slowly declined; at the end of the 55 day study the level was about 0.1 ppm. The concn pattern for aminomethylphosphonic acid, a glyphosphate metabolite in sediment was similar to that of glyphosate, but at much lower levels. Sediments adsorb glyphosate from flowing water; once adsorbed, it is not readily eluted. In experiments where glyphosate was added to water in two irrigation canals, the fractional reduction in load was 13 and 27% per km with uptake by the benthic sediment being 365 and 603 g/km . In two other experiments in which glyphosate was added to flowing water to simulate contamination during foliar spaying, 63% of the glyphosate was scavenged by sediment in 14 km and 43% was removed in 14 km . In a field study, glyphosate was sprayed on sediment in an irrigation channel in spring and 4 days afterwards the channel was filled with water. Based on the observed concentration levels, less than 7% of the applied glyphosate eluted with water . ATMOSPHERIC FATE: Glyphosate will be released into the atmosphere as an aerosol during spraying and removed by gravitational settling. It will occur in the atmosphere only as an aerosol and may degrade by photolysis.
Drinking Water Impact GROUNDWATER: Glyphosate was detected in groundwater and water supply monitoring programs in Texas . The concn and site details were not reported . In a survey of farm wells in Ontario, Canada, 103 in 1986 and 76 in 1987, glyphosate was not detected in any wells . However, glyphosate was only used on crops on 28 farms in 1986 and 1987 .

Consumer Factsheet on: GLYPHOSATE

EPA

As part of the Drinking Water and Health pages, this fact sheet is part of a larger publication:
National Primary Drinking Water Regulations

This is a factsheet about a chemical that may be found in some public or private drinking watersupplies. It may cause health problems if found in amounts greater than the health standard set bythe United States Environmental Protection Agency (EPA).

What is Glyphosate and how is it used?

Glyphosate is an organic solid of odorless white crystals. It is a non-selective herbicide used onmany food and non-food crops as well as non-crop areas such as roadsides. When applied atlower rates, it serves as a plant growth regulator. The most common uses include control ofbroadleaf weeds and grasses in: hay/pasture, soybeans, field corn; ornamentals, lawns, turf, forestplantings, greenhouses, rights-of-way.

 

The list of trade names given below may help you find out whether you are using this chemical athome or work.

Trade Names and Synonyms:

Glialka
Roundup
Sting
Rodeo
Spasor
Muster
Tumbleweed
Sonic
Glifonox
Glycel
Rondo
 

Why is Glyphosate being Regulated?

In 1974, Congress passed the Safe Drinking Water Act. This law requires EPA to determine safelevels of chemicals in drinking water which do or may cause health problems. Thesenon-enforceable levels, based solely on possible health risks and exposure, are called MaximumContaminant Level Goals.

 

The MCLG for glyphosate has been set at 0.7 parts per million (ppm) because EPA believes thislevel of protection would not cause any of the potential health problems described below.

Based on this MCLG, EPA has set an enforceable standard called a maximum Contaminant Level(MCL). MCLs are set as close to the MCLGs as possible, considering the ability of public watersystems to detect and remove contaminants using suitable treatment technologies.

The MCL has been set at 0.7 ppm because EPA believes, given present technology and resources,this is the lowest level to which water systems can reasonably be required to remove thiscontaminant should it occur in drinking water.

These drinking water standards and the regulations for ensuring these standards are met, arecalled National Primary Drinking Water Regulations. All public water supplies must abide bythese regulations.

What are the Health Effects?

Short-term: EPA has found glyphosate to potentially cause the following health effects whenpeople are exposed to it at levels above the MCL for relatively short periods of time: congestionof the lungs; increased breathing rate.

 

Long-term: Glyphosate has the potential to cause the following effects from a lifetime exposure atlevels above the MCL: kidney damage, reproductive effects.

How much Glyphosate is produced and released to the environment?

Glyphosate is released to the environment in its use as a herbicide for controlling woody andherbaceous weeds on forestry, right-of-way, cropped and non-cropped sites. These sites may bearound water and in wetlands.

 

It may also be released to the environment during its manufacture, formulation, transport, storage,disposal and cleanup, and from spills. Glyphosate is among the most widely used pesticides byvolume. Usage in 1990 was estimated to be 11,595,000 pounds. It ranked eleventh amongconventional pesticides in the US during 1990-91. In recent years, 13 to 20 million acres weretreated with 18.7 million lbs. annually.

What happens to Glyphosate when it is released to the environment?

Glyphosate is strongly adsorbed to soil, with little potential for leaching to ground water.Microbes in the soil readily and completely degrade it even under low temperature conditions. Ittends to adhere to sediments when released to water. Glyphosate does not tend to accumulate inaquatic life.

 

How will Glyphosate be Detected in and Removed from My Drinking Water?

The regulation for glyphosate became effective in 1994. Between 1993 and 1995, EPA requiredyour water supplier to collect water samples every 3 months for one year and analyze them to findout if glyphosate is present above 6 parts per billion. If it is present above this level, the systemmust continue to monitor this contaminant.

 

If contaminant levels are found to be consistently above the MCL, your water supplier must takesteps to reduce the amount of glyphosate so that it is consistently below that level. The followingtreatment methods have been approved by EPA for removing glyphosate: Granular activatedcharcoal.

How will I know if Glyphosate is in my drinking water?

If the levels of glyphosate exceed the MCL, 0.7 ppm, the system must notify the public vianewspapers, radio, TV and other means. Additional actions, such as providing alternativedrinking water supplies, may be required to prevent serious risks to public health.

 

Drinking Water Standards:

Mclg: 0.7 ppm

Mcl: 0.7 ppm

 
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