124-58-3C[As](=O)(O)OQYPPRTNMGCREIM-UHFFFAOYSA-NMethylarsonic acid is an organoarsonic acid, a member of arsonic acids and a one-carbon compound. It is a conjugate acid of a methylarsonate(1-).
124-58-3DTXSID4020903CHEMBL1743208CHEBI:29852Monoclinic, spear-shaped plates from absolute alcohol
White, crystalline solid
LEAVES FROM ALCOHOL
Soluble in ethanol
In water, 2.56X10+5 mg/l @ 20 °C.
Solubility in water: very good
160.5 °C
161 °C
0.00162 [mmHg]
<7.5X10-8 mm Hg @ 25 °C
White hygroscopic solid; [ICSC]
Solid
WHITE HYGROSCOPIC SOLID IN VARIOUS FORMS.
安全情報は参考情報です。供給元の安全データシート(SDS)、適用法令、専門家による評価に代わるものではありません。
Danger
H301 (100%): Toxic if swallowed [Danger Acute toxicity, oral]
P261, P264, P270, P271, P273, P301+P316, P304+P340, P316, P321, P330, P391, P403+P233, P405, and P501 (click each P-code to see the statement)
Aggregated GHS information provided per 38 reports by companies from 1 notifications to the ECHA C&L Inventory. Each notification may be associated with multiple companies.
Hazard Traits - Carcinogenicity
Hazard Traits - Carcinogenicity; Cardiovascular Toxicity; Dermatotoxicity; Developmental Toxicity; Neurotoxicity; Other Toxicological Hazard Traits; Respiratory Toxicity
Restricted substance: Methylarsonic acid
Oral LD50 (rat) = 961 mg/kg; [Sax] A mild skin, eye, and respiratory tract irritant; May cause kidney and liver injury; [ICSC] After ingestion of arsenic-rich wine, the majority of the arsenic was excreted in the urine in methylated form (methylarsonic acid & dimethylarsinic acid); Methylarsonic acid (MAA) fed to dairy cows in cottonseed ration had no apparent adverse effects; MAA was poorly absorbed and rapidly excreted in the urine; [HSDB] Arsenic is a known teratogen, but the effects of organic arsenicals is less clear. MAA is not likely to be a reproductive hazard at levels currently found in the environment; [REPROTOX] An irritant; [MSDSonline]
AFTER INGESTION /SRP: BY HUMANS/ OF ARSENIC-RICH WINE, APPROX 10% OF THE ARSENIC WAS EXCRETED AS ARSENITE, BUT THE MAJORITY OF ARSENIC WAS METHYLATED TO METHYLARSONIC ACID & DIMETHYLARSINIC ACID & EXCRETED.
IN THE PRESENCE OF CECAL CONTENT, BUT NOT SMALL INTESTINE, SMALL AMOUNTS OF METHYLARSONIC ACID & DIMETHYLARSINIC ACID WERE FORMED BY THE RAT IN VITRO.
IN FIRST VOID URINE SAMPLES FROM COPPER SMELTER WORKERS EXPOSED TO INORG ARSENIC & FROM NONEXPOSED CONTROLS 20% OF TOTAL ARSENIC WAS EXCRETED AS METHYLARSONIC ACID.
THE HUMAN ORGANISM CAN COPE WITH MODERATE DOSES OF ARSENIC BY A RAPID & EFFICIENT METHYLATION PROCESS GIVING MONOMETHYLARSONIC ACID & DIMETHYLARSINIC ACID WHICH ARE RAPIDLY ELIMINATED IN THE URINE.
For more Metabolism/Metabolites (Complete) data for METHANEARSONIC ACID (6 total), please visit the HSDB record page.
Arsenic is absorbed mainly by inhalation or ingestion, as to a lesser extent, dermal exposure. It is then distributed throughout the body, where it is reduced into arsenite if necessary, then methylated into monomethylarsenic (MMA) and dimethylarsenic acid (DMA) by arsenite methyltransferase. Arsenic and its metabolites are primarily excreted in the urine. Arsenic is known to induce the metal-binding protein metallothionein, which decreases the toxic effects of arsenic and other metals by binding them and making them biologically inactive, as well as acting as an antioxidant. (L20)
Pesticides used to destroy unwanted vegetation, especially various types of weeds, grasses (POACEAE), and woody plants. Some plants develop HERBICIDE RESISTANCE.
An agent that causes the production of physical defects in the developing embryo.
...DAIRY COWS /WERE FED/ COTTONSEED RATION CONTAINING MAA. THE MAA HAD NO EFFECT ON COWS, WITH VERY LITTLE RESIDUE ACCUMULATING IN TISSUES OR MILK. THE MAA APPEARED TO BE POORLY ABSORBED FROM INTESTINAL TRACT & WAS RAPIDLY EXCRETED IN URINE.
ARSENIC CONTENT OF MILK OR EDIBLE TISSUES OF COWS FED FOR 9 WK WITH 5 LB COTTONSEED MEAL CONTAINING 30 PPM OF ACID WAS NOT SIGNIFICANTLY INCREASED; NOR WAS ARSENIC CONTENT OF EGGS AND MEAT OF HENS RECEIVING DIETS CONTAINING UP TO 3 PPM OF METHANEARSONIC ACID.
現在のフィルター条件では反応記録がありません。
読み込み中…
Strong dibasic acid.
Water high in calcium, magnesium and iron may cause precipitation; these cations form insoluble methane arsonate salts.
化学的特性Plates from EtOH or Me2CO.Sol in H 2O and EtOH.
REVIEW OF THE CHEMICAL, PHYSICAL, & BIOL PROPERTIES & METHODS OF ANALYSIS FOR MONOMETHYLARSONIC ACID, CACODYLIC ACID, & THEIR SODIUM SALTS.[DIETZ EA JR, MOORE LO; MONOMETHYLARSONIC ACID, CACODYLIC ACID, AND THEIR SODIUM SALTS; ANAL METHODS PESTIC PLANT GROWTH REGUL 10: 385-401 (1978)]
If material involved in fire: Extinguish fire using agent suitable for type of surrounding fire. (Material itself does not burn or burns with difficulty.) Use water in flooding quantities as fog. Use foam, dry chemical, or carbon dioxide. /Arsenical cmpd, liquid, NOS/
If material involved in fire: Extinguish fire using agent suitable for type of surrounding fire. (Material itself does not burn or burns with difficulty.) Use water in flooding quantities as fog. Use foam, dry chemical, or carbon dioxide. /Arsenical cmpd, solid, NOS/
Listed as a hazardous air pollutant (HAP) generally known or suspected to cause serious health problems. The Clean Air Act, as amended in 1990, directs EPA to set standards requiring major sources to sharply reduce routine emissions of toxic pollutants. EPA is required to establish and phase in specific performance based standards for all air emission sources that emit one or more of the listed pollutants. Methanearsonic acid is included on this list.
(a) The owner or operator of an existing glass melting furnace subject to the provisions of this subpart shall comply with either paragraph (a)(1) or (a)(2) of this section ... (1) Uncontrolled total arsenic emissions from the glass melting furnace shall be less than 2.5 Mg (2.7 ton) per year, or ... (2) Total arsenic emissions from glass melting furnace shall be conveyed to a control device and reduced by at least 85%. /Total arsenic/
(b) The owner or operator of a new or modified glass melting furnace subject to the provisions of this subpart shall comply with either paragraph (b)(1) or (b)(2) of this section ... (1) Uncontrolled total arsenic emissions from the glass melting furnace shall be less than 0.4 Mg (0.44 ton) per year, or ... (2) Total arsenic emissions from glass melting furnace shall be conveyed to a control device and reduced by at least 85%. /Total arsenic/
The owner or operator of each copper converter subject to the provisions of this subpart shall reduce inorganic arsenic emissions to the atmosphere by meeting the following design, equipment, work practice, and operational requirements: (1) Install, operate, and maintain a secondary hood system on each copper converter. Each secondary hood system shall consist of a hood enclosure, air curtain fan(s), exhaust system fan(s), and ductwork that conveys the captured emission to a control device ... (2) Optimize the capture of secondary inorganic arsenic emission by operating the copper converter and secondary hood systems at all times ... . /Inorganic arsenic/
D004; A waste containing arsenic may or may not be characterized as a hazardous waste following testing by the Toxicity Characteristic Leaching Procedure as prescribed by the Resource Conservation and Recovery Act (RCRA) regulations. /Arsenic/
Fresh air, rest. Refer for medical attention.
Remove contaminated clothes. Rinse and then wash skin with water and soap.
First rinse with plenty of water for several minutes (remove contact lenses if easily possible), then refer for medical attention.
Rinse mouth. Refer for medical attention .
At the time of review, criteria for land treatment or burial (sanitary landfill) disposal practices are subject to significant revision. Prior to implementing land disposal of waste residue (including waste sludge), consult with environmental regulatory agencies for guidance on acceptable disposal practices.
Personal protection: particulate filter respirator adapted to the airborne concentration of the substance. Sweep spilled substance into covered containers. If appropriate, moisten first to prevent dusting. Carefully collect remainder. Then store and dispose of according to local regulations.
Tolerances for total residues of combined arsenic (calculated as As) in food are established as follows: (a) In edible tissues & in eggs of chickens & turkeys: 0.5 ppm in uncooked muscle tissue; 2 ppm in uncooked edible by-products; & 0.5 ppm in eggs. (b) In edible tissues of swine: 2 ppm in uncooked liver & kidney; 0.5 ppm in uncooked muscle tissue & by-products other than liver & kidney. /Arsenic/
Arsenic poisoning can be treated by chelation therapy, using chelating agents such as dimercaprol, EDTA or DMSA. Charcoal tablets may also be used for less severe cases. In addition, maintaining a diet high in sulfur helps eliminate arsenic from the body. (L20)
EVOLUTION OF DIMETHYLARSINE & TRIMETHYLARSINE FROM GRASSES TREATED WITH SODIUM ARSENITE, METHYLARSONIC ACID, DIMETHYLARSINIC ACID, OR PHENYLARSONIC ACID CONFIRMED THE IDEA OF NATURAL BIOMETHYLATION.
Strongly adsorbed to soil; fixed by Fe and Al hydrous oxides in soil. Sorption increases as size of clay fraction decreases.
DECR IN PHYTOTOXICITY IS A RESULT OF FIXATION...MAINLY BY IRON & ALUMINUM HYDROUS OXIDES IN THE SOIL.
NINETEEN SAMPLES REPRESENTING 13 VARIETIES OF RED & WHITE DOMESTIC TABLE WINES WERE ANALYZED FOR ARSENITE, ARSENATE, METHYLARSONIC ACID & DIMETHYLARSINIC ACID. THE CONCN OF ARSENITE RANGED FROM LESS THAN 1 TO 420 PPB, & THE CONCN OF ARSENATE RANGED FROM 1 TO 110 PPB. METHYLARSONIC ACID WAS BELOW LIMIT OF DETECTION OF 1 PPB.
The substance can be absorbed into the body by inhalation of its aerosol and by ingestion.
Oral (L2) ; inhalation (L2); dermal (L2)
Arsenic and its metabolites disrupt ATP production through several mechanisms. At the level of the citric acid cycle, arsenic inhibits pyruvate dehydrogenase and by competing with phosphate it uncouples oxidative phosphorylation, thus inhibiting energy-linked reduction of NAD+, mitochondrial respiration, and ATP synthesis. Hydrogen peroxide production is also increased, which might form reactive oxygen species and oxidative stress. Arsenic's carginogenicity is influenced by the arsenical binding of tubulin, which results in aneuploidy, polyploidy and mitotic arrests. The binding of other arsenic protein targets may also cause altered DNA repair enzyme activity, altered DNA methylation patterns and cell proliferation. (T1, A17)
Cough. Sore throat.
Redness.
Redness.
Abdominal pain. Diarrhoea. Vomiting.
Exposure to lower levels of arsenic can cause nausea and vomiting, decreased production of red and white blood cells, abnormal heart rhythm, damage to blood vessels, and a sensation of burn (T1).
Methylarsenic acid was evaluated for clastogenicity in groups of 20 male Long-Evans rats injected intraperitoneally with total dose levels of 0 or 500 mg/kg bw, in three equal increments at 2 day intervals. Blood and bone marrow samples were obtained from each rat at 1 and 30 days after treatment, for determination of chromosomal abnormalities. The treatment increased the frequency of 1 type of chromosomal aberration (gap/break) in bone marrow cells obtained on day 1, indicating that the test compound was positive for clastogenicity in rats under the conditions of this assay. Positive control treatment with a single intraperitoneal injection of 0.3 mg/kg triethylenemelamine produced a significant increase in the frequency of chromosomal aberrations in bone marrow cells collected on day 1; bone marrow cells collected from positive control rats on day 30 and blood cells collected on day 1 or 30 were similar to negative controls in frequency of chromosomal aberrations.
SKIN IRRITATION OF THESE VARIOUS ARSENICALS VARY FROM VERY-MILD TO NONE, DEPENDING ON ACIDITY OR ALKALINITY OF EACH PREPN, & SKIN SENSITIVITY OF EXPOSED INDIVIDUAL. SYMPTOMS OF...SUBACUTE POISONING WITH ARSENICALS.../INCL METHANEARSONIC ACID/ SALTY TASTE, BURNING IN THROAT, & COLICKY PAINS IN STOMACH & INTESTINES. GARLICKY ODOR OF BREATH & SKIN IS FREQUENTLY PRESENT. SYMPTOMS OF ACUTE POISONING...HEADACHE, VOMITING, DIARRHEA, DIZZINESS, STUPOR, CONVULSIONS, GENERAL PARALYSIS, & DEATH.
THE METABOLISM OF MAA TO INORGANIC ARSENIC IS THE MAIN MECHANISM OF HERBICIDE DEGRADATION... THE ASSOC OF HERBICIDAL BREAKDOWN WITH THE GENERAL MICROBIOLOGICAL ACTIVITY SUGGESTS THAT THE OXIDATION OF MAA /METHANEARSONIC ACID/ OCCURRED COINCIDENTALLY WITH THE METAB OF SOIL ORG MATTER. ON THE OTHER HAND, BOTH NORFOLK LOAMY SAND SAMPLES (WITH & WITHOUT ORGANIC MATTER ADDED) SHOWED AN INCREASED DSMA /DISODIUM SALT OF MAA/ DECOMPOSITION RELATIVE TO SOIL ORGANIC MATTER. THIS SUGGESTED AN ADAPTATION OF THE MICROBIAL POPULATION TO METABOLIZE THE METHYL CARBON OF MAA. /INVESTIGATORS/...EXAM THE DEGRADATION OF MSMA /MONOSODIUM SALT OF MAA/ ON 4 SOILS. THEY CONCLUDED THAT SOIL MICROORGANISMS APPEARED TO PLAY SOME ROLE IN THE DECOMPOSITION PROCESS. A FUNGUS, SEVERAL ACTINOMYCETES, & SEVERAL BACTERIA WERE ISOLATED USING SOIL ENRICHMENT TECHNIQUES. THE ORGANISMS DEGRADED 3, 13 OR 9, & 20% OF THE MSMA IN 11 DAYS, RESPECTIVELY. HOWEVER, IN THE ABSENCE OF AN ENERGY SOURCE, MICROBIAL METABOLISM OF THE ORGANIC ARSENICAL WAS NONEXISTENT. THE PRODUCTS OF METABOLISM WERE CARBON DIOXIDE & ARSENATE. NO ARSENITE COULD BE DETECTED.
If material involved in fire: Extinguish fire using agent suitable for type of surrounding fire. (Material itself does not burn or burns with difficulty.) Use water in flooding quantities as fog. Use foam, dry chemical, or carbon dioxide. /Arsenical cmpd, liquid, NOS/
If material involved in fire: Extinguish fire using agent suitable for type of surrounding fire. (Material itself does not burn or burns with difficulty.) Use water in flooding quantities as fog. Use foam, dry chemical, or carbon dioxide. /Arsenical cmpd, solid, NOS/
Listed as a hazardous air pollutant (HAP) generally known or suspected to cause serious health problems. The Clean Air Act, as amended in 1990, directs EPA to set standards requiring major sources to sharply reduce routine emissions of toxic pollutants. EPA is required to establish and phase in specific performance based standards for all air emission sources that emit one or more of the listed pollutants. Methanearsonic acid is included on this list.
(a) The owner or operator of an existing glass melting furnace subject to the provisions of this subpart shall comply with either paragraph (a)(1) or (a)(2) of this section ... (1) Uncontrolled total arsenic emissions from the glass melting furnace shall be less than 2.5 Mg (2.7 ton) per year, or ... (2) Total arsenic emissions from glass melting furnace shall be conveyed to a control device and reduced by at least 85%. /Total arsenic/
(b) The owner or operator of a new or modified glass melting furnace subject to the provisions of this subpart shall comply with either paragraph (b)(1) or (b)(2) of this section ... (1) Uncontrolled total arsenic emissions from the glass melting furnace shall be less than 0.4 Mg (0.44 ton) per year, or ... (2) Total arsenic emissions from glass melting furnace shall be conveyed to a control device and reduced by at least 85%. /Total arsenic/
The owner or operator of each copper converter subject to the provisions of this subpart shall reduce inorganic arsenic emissions to the atmosphere by meeting the following design, equipment, work practice, and operational requirements: (1) Install, operate, and maintain a secondary hood system on each copper converter. Each secondary hood system shall consist of a hood enclosure, air curtain fan(s), exhaust system fan(s), and ductwork that conveys the captured emission to a control device ... (2) Optimize the capture of secondary inorganic arsenic emission by operating the copper converter and secondary hood systems at all times ... . /Inorganic arsenic/
Toxic pollutant designated pursuant to section 307(a)(1) of the Federal Water Pollution Control Act and is subject to effluent limitations. /Arsenic & cmpd/
For the maximum protection of human health from the potential carcinogenic effects due to exposure of arsenic through ingestion of contaminated water & contaminated aquatic organisms, the ambient water concn should be zero based on the nonthreshold assumption for this chemical. However, zero level may not be attainable at the present time. Therefore, the levels which may result in incremental increase of cancer risk over the lifetime are estimated at 1X10-5, 1X10-6, & 1X10-7. The corresponding criteria are 22 ng/l, 2.2 ng/l, & .22 ng/l, respectively .... For consumption of aquatic organisms only, excluding consumption of water, the levels are 175 ng/ml, 17.5 ng/l, & 1.75 ng/l, respectively. /Arsenic/
D004; A solid waste containing arsenic may or may not become characterized as a hazardous waste when subjected to the Toxicity Characteristic Leaching Procedure listed in 40 CFR 261.24, and if so characterized, must be managed as a hazardous waste.
(AZ) ARIZONA 10 ug/L /Arsenic/
(CT) CONNECTICUT 10 ug/l /Arsenic/
/COTTON/ COTYLEDONS ABSORBED MAA /METHANEARSONIC ACID/ & MSMA /MONOSODIUM METHANEARSONIC ACID/ MORE READILY THAN DSMA. ... ABSORPTION OF (14)C DSMA TENDED TO INCREASE WITH TEMPERATURE. /METHANEARSONIC ACID, DISODIUM SALT/
Used as herbicide in the past; [Merck Index] Not currently registered with the EPA for use in the US; [HSDB]
Farming (Pesticides) [Category: Industry]
For Methanearsonic acid (USEPA/OPP Pesticide Code: 128876) there are 0 labels match. /SRP: Not registered for current use in the U.S., but approved pesticide uses may change periodically and so federal, state and local authorities must be consulted for currently approved uses./
Herbicide /Former use/
Methylarsonic acid, disodium salt is used as an herbicide and pesticide. (L389)
Prepared from sodium arsenite and methyl iodide: Quick, Adams, J Am Chem Soc 44, 809 (1922). The disodium salt is...prepared by treating sodium arsenite with dimethyl sulfate at 85 °C... other routes are by reaction of methyl chloride with sodium arsonate under pressure: Miller et al, US patent 2,442,372 (1948); by the reaction of dimethyl sulfate with soln of arsenic trioxide in sodium hydroxide: Schwerdle, US patent 2,889,347 (1959).
解説メチルアルソン酸.亜ヒ酸ナトリウムとクロロメタンとを反応させると得られる.分解点130 ℃.水和物は白色の結晶.融点113~116 ℃.pK1 3.61,pK2 8.25.水,エタノールに可溶,エーテルに不溶.塩化水素と二酸化硫黄を作用させるとジクロロ(メチル)アルシンを与える.金属イオンの沈殿剤,ワタ畑,芝生,非農耕地用除草剤として用いられる.LD50 700 mg/kg(ラット,経口).
用途有機合成用。
説明Salts of methanearsonic acid,CH3AsO(OH)2, especially the iron ammonium salt, Neoasozin, used as a fungicide in rice growing and the sodium, ammonium, and diethanolam monium salts used as herbicides in cotton growing.
使用Methylarsonic acid is used as herbicide.
純化方法Recrystallise this herbicide from Me2CO or absolute EtOH (white plates; its solubility is 28g/100mL EtOH). [Quick & Adams J Am Chem Soc 44 809 1922, Beilstein 4 H 613, 4 I 577, 4 II 996, 4 III 1822, 4 IV 3682.]