Carcinogenicity, Category 2
H319 Causes serious eye irritation
H351 Suspected of causing cancer
P203 Obtain, read and follow all safety instructions before use.
P280 Wear protective gloves/protective clothing/eye protection/face protection/hearing protection/...
P318 IF exposed or concerned, get medical advice.
P405 Store locked up.
P501 Dispose of contents/container to an appropriate treatment and disposal facility in accordance with applicable laws and regulations, and product characteristics at time of disposal.
no data available
Fresh air, rest.
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. Give one or two glasses of water to drink.
Toxicity and health hazard of these compounds are low. Contact with eyes causes irritation. (USCG, 1999)
Immediate first aid: Ensure that adequate decontamination has been carried out. If patient is not breathing, start artificial respiration, preferably with a demand-valve resuscitator, bag-valve-mask device, or pocket mask, as trained. Perform CPR as necessary. Immediately flush contaminated eyes with gently flowing water. Do not induce vomiting. If vomiting occurs, lean patient forward or place on left side (head-down position, if possible) to maintain an open airway and prevent aspiration. Keep patient quiet and maintain normal body temperature. Obtain medical attention. Organic acids and related compounds
This chemical is a combustible solid. Use dry chemical, carbon dioxide, water spray, or alcohol foam extinguishers.
Flash point data for this chemical are not available; however, it is probably combustible. (NTP, 1992)
In case of fire in the surroundings, use appropriate extinguishing media.
Personal protection: particulate filter respirator adapted to the airborne concentration of the substance. Do NOT let this chemical enter the environment. 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.
Personal protection: particulate filter respirator adapted to the airborne concentration of the substance. Do NOT let this chemical enter the environment. 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.
This study used acidity, ethylenediaminetetracetic acid and nitrilotriacetic acid treatment processes to explore the removal efficiencies of heavy metals from urban and industrial sludges. The results indicate that the optimum treatment efficiencies of heavy metals extraction from sludge are related to the species of heavy metals in sludge, dosage of extractants and the reaction time. The removal efficiency of a three stage countercurrent process was higher than those of single stage processes... The cost of the acid treatment process per unit weight of heavy metal extracted was lowest in conditions of high heavy metal concentrations, but the ethylenedinitrilotetraacetic process was the cheapest with low heavy metal concentrations.
NO open flames. Closed system, dust explosion-proof electrical equipment and lighting. Prevent deposition of dust. Handling in a well ventilated place. Wear suitable protective clothing. Avoid contact with skin and eyes. Avoid formation of dust and aerosols. Use non-sparking tools. Prevent fire caused by electrostatic discharge steam.
Separated from strong oxidants and strong bases. Well closed.Store in a refrigerator or in a cool, dry place.
MAK: carcinogen category: 3A
no data available
Ensure adequate ventilation. Handle in accordance with good industrial hygiene and safety practice. Set up emergency exits and the risk-elimination area.
Wear safety goggles.
Protective gloves.
Use local exhaust or breathing protection.
no data available
Solid. Flakes.
White.
no data available
242 °C. Atm. press.:Ca. 1 atm.
429 °C. Atm. press.:Ca. 1 atm.
Combustible under specific conditions. Gives off irritating or toxic fumes (or gases) in a fire.
no data available
255 °C. Atm. press.:Ca. 1 atm.
no data available
242°C
pH of saturated aqueous solution = 2.3
no data available
less than 0.1 mg/mL at 73° F (NTP, 1992)
log Pow = -3.81. Temperature:25 °C. Remarks:QSAR.
Ca. 0 Pa. Temperature:25 °C. Remarks:Modified Grain Method.
> 1 g/cm3. Temperature:25 °C.
no data available
no data available
Decomposes on burning. This produces toxic and irritating fumes including nitrogen oxides. The solution in water is a weak acid. Reacts with strong bases and strong oxidants.
no data available
Dust explosion possible if in powder or granular form, mixed with air.NITRILOTRIACETIC ACID is incompatible with strong oxidizers, aluminum, copper, copper alloy and nickel. It is also incompatible with strong bases. (NTP, 1992)
no data available
Violent reaction with strong bases.
When heated to decomposition it emits toxic fumes of /nitrogen oxides/.
no data available
no data available
no data available
no data available
Evaluation: There is inadequate evidence in humans for the carcinogenicity of nitrilotriacetic acid and its salts. There is sufficient evidence in experimental animals for the carcinogenicity of nitrilotriacetic acid and its sodium salts. Overall evaluation: Nitrilotriacetic acid and its salts are possibly carcinogenic in humans (Group 2B).
no data available
The substance is irritating to the eyes, skin and respiratory tract.
This substance is possibly carcinogenic to humans.
No indication can be given about the rate at which a harmful concentration of this substance in the air is reached on evaporation at 20°C.
AEROBIC: In a river die-away study using Ruhr River water from Germany, nitrilotriacetic acid biodegradation rate constants of 0.30/day (25 deg C) and 0.07/day (2 deg C) were measured which correspond to respective half-lives of 2.3 and 9.9 days(1). In a die-away test Ohio River water, 100% degradation was observed after 12-14 days of incubation which included an 8-10 day lag period(2). In aerobic die-away tests using Detroit and Meramec River water, 100% degradation was observed after 3-15 days of incubation(3). In river die-away tests using river water from both upstream and downstream of the Heath, OH treatment plant, 100% degradation occurred within 10 days in the downstream water and within 16 days in the upstream water(4). In die-away tests using freshwater-sediment from Hamilton Harbor, Lake Erie, 100% degradation occurred in 3-11 days of incubation at input concentrations of 1-12 ppm(5). In CO2 evolution tests using river water inocula from various sites (Fukushima, Japan; Perkinsville, IN; Brantford, Ontario; Cincinnati, OH) located downstream from treatment plants and low concentrations of nitrilotriacetic acid (0.001-1 ppm), rate constants ranging from 0.12 to 1.28/day were measured which correspond to half-lives of 0.54 to 5.8 days(6). Nitrilotriacetic acid was rapidly degraded in river die-away studies using Grand River (Ontario, Can) water and Ohio River water(7); half-lives in the Grand River water ranged from 0.34-0.64 days while the Ohio River water had a 15-day CO2 evolution of 90%(7). Mineralization of nitrilotriacetic acid in Cayuga Lake water (Ithaca, NY) was 90% or greater in 20 days of incubation at concentrations of 1 ug/mL and 10 ng/mL(8); however, at 0.1 ng/L, mineralization was much slower (about 15% in 60 days)(8).
BCFs of <9 to 24 and 109 were measured in carp (Cyprinus carpio) exposed for 28 days at nitrilotriacetic acid concentrations of 3 and 0.3 mg/L, respectively(1). According to a classification scheme(2), these BCFs suggest the potential for bioconcentration in aquatic organisms is low to moderate(SRC).
The Koc of nitrilotriacetic acid is estimated as <286(SRC), using a measured Kd value of <10 in a creek sediment containing 3.5% organic carbon(1). According to a classification scheme(2), this Koc suggests that nitrilotriacetic acid is expected to have high to moderate mobility in soil(SRC). Soil Rf values of 0.33-0.41 that were measured by thin-layer chromatography also suggest moderate to high soil mobility of nitrilotriacetic acid(3). Nitrilotriacetic acid had a reported Kd of 0.3 giving a half-life of 5 days(4). The pKa1 of nitrilotriacetic acid is 3.03(5), indicating that this compound will exist almost entirely in anion form in the environment and anions generally do not adsorb more strongly to soils containing organic carbon and clay than their neutral counterparts(6).
no data available
The material can be disposed of by removal to a licensed chemical destruction plant or by controlled incineration with flue gas scrubbing. Do not contaminate water, foodstuffs, feed or seed by storage or disposal. Do not discharge to sewer systems.
Containers can be triply rinsed (or equivalent) and offered for recycling or reconditioning. Alternatively, the packaging can be punctured to make it unusable for other purposes and then be disposed of in a sanitary landfill. Controlled incineration with flue gas scrubbing is possible for combustible packaging materials.
ADR/RID: Not dangerous goods. (For reference only, please check.)
IMDG: Not dangerous goods. (For reference only, please check.)
IATA: Not dangerous goods. (For reference only, please check.)
ADR/RID: Not dangerous goods. (For reference only, please check.)
IMDG: Not dangerous goods. (For reference only, please check.)
IATA: Not dangerous goods. (For reference only, please check.)
ADR/RID: Not dangerous goods. (For reference only, please check.)
IMDG: Not dangerous goods. (For reference only, please check.)
IATA: Not dangerous goods. (For reference only, please check.)
ADR/RID: Not dangerous goods. (For reference only, please check.)
IMDG: Not dangerous goods. (For reference only, please check.)
IATA: Not dangerous goods. (For reference only, please check.)
ADR/RID: No
IMDG: No
IATA: No
no data available
no data available