Human Health Effects:
Human Toxicity Excerpts:
NITRATE SALTS AS SUCH ARE NO MORE TOXIC THAN OTHER NEUTRAL SALTS, BUT IF NOT
PROMPTLY ABSORBED, THEY MAY BE REDUCED TO NITRITES BY BACTERIA IN THE BOWEL.
CYANOSIS AMONG INFANTS WHO DRINK WELL WATER IS A FREQUENTLY ENCOUNTERED CLINICAL
MANIFESTATION OF NITRATE TOXICITY. /NITRATE SALTS/
... WITH LARGE DOSES ... THERE ARISES POSSIBILITY OF SUFFICIENT ABSORPTION TO
PRODUCE DIURESIS ... .
Volunteers, 20 normal and 19 asthmatic, were exposed to clean air and to
ammonium nitrate aerosol under conditions which simulated a worst case ambient
pollution episode. Exposures of 200 ug/cu m lasted for 2 hours with intermittent
exercise and heat stress. No noticeable changes in pulmonary function or overall
reported symptoms were observed due to the ammonium nitrate exposure.
231 normal male human subjects were exposed for 4 hours to ammonium nitrate
aerosols. Each subject had two 15 min exercise sessions on a treadmill at 4 mph
& 20% grade. Temp conditions were 30 deg C and relative humidity was 60%. A
battery of 19 measurements of pulmonary function was performed. No significant
effects from ammonium nitrate aerosol was produced.
Inhalation is irritating to mucous membranes of respiratory tract, causes
severe lung congestion, coughing, and difficult breathing, causes urination and
acid urine.
Inhalation of large amounts causes systemic acidosis and abnormal hemoglobin.
SUMMARY TOXICITY STATEMENT: LOW VIA IRRITATION, ALLERGEN. THERE HAVE BEEN
REPORTS OF FAINTNESS & LOW BLOOD PRESSURE IN WORKERS EXPOSED. THESE SYMPTOMS
COULD BE DUE TO NITRITES PRESENT AS IMPURITIES.
Skin, Eye and Respiratory Irritations:
Irritating to eyes, nose, and throat, and mucous membranes.
Probable Routes of Human Exposure:
As a result of the blasting agent used in mines, ammonium nitrate, workers
are subjected to air pollution in mines which poses an occupational health
hazard.
Animal Toxicity Studies:
Non-Human Toxicity Excerpts:
... FERTILIZERS CONTAINING AMMONIUM NITRATE...CAN CAUSE ILLNESS IN POULTRY.
... /IN/ SHEEP A SINGLE ORAL DOSE OF 2 G/KG CAUSED DEATH IN 12 HR TO 17 DAYS
AFTER ADMIN; REPEATED DOSES OF 0.25 G/KG FOR 30 DAYS OR 0.5 G/KG FOR 10 DAYS
WERE TOLERATED.
CHRONIC POISONING ... CHARACTERIZED BY SWOLLEN & HYPEREMIC MUCOUS
MEMBRANE OF ABOMASUM & CATARRHAL INFLAMMATION OF SMALL INTESTINE. IN SHEEP
... GENERAL PASSIVE HYPEREMIA & PETECHIAE IN MUSCLES, HEART, THYMUS &
LUNGS. CLOUDY SWELLING & NECROTIC FOCI WERE OBSERVED IN KIDNEY TUBULES. IN
GOATS ... /FROM CHRONIC POISONING/ ACUTE CATARRHAL GASTROENTERITIS &
BRONCHITIS, NEPHROSIS, PERI-BRONCHIAL & INTRA-ALVEOLAR HEMORRHAGES, &
CONGESTION, HEMORRHAGES & DEGENERATIVE CHANGES IN CENTRAL NERVOUS SYSTEM
/WERE OBSERVED/.
... AMMONIUM SALTS GENERALLY HAVE SUCH LOW TOXICITY TO CORNEA THAT THEY
PRODUCE NO DAMAGE DURING EXPOSURES OF SEVERAL MIN ... 0.1 MOLAR AMMONIUM ...
NITRATE ... AT PH 7-7.5 MADE UP TO 0.46 OSMOLAR ... BY ADDITION OF NACL OR
SUCROSE & DRIPPED CONTINUOUSLY ON EYES OF RABBITS CAUSED EDEMA OF EPITHELIUM
OF CORNEA WITHIN 3-3.5 HR.
RUMINANTS ... MAY ... DEVELOP METHEMOGLOBINEMIA BY CONSUMPTION OF QUANTITIES
OF NITRATE. THIS IS DUE TO REDUCING ENVIRONMENT OF RUMEN, RESULTING IN RAPID
CONVERSION OF NITRATES TO MORE TOXIC NITRITES. ... CHRONIC NITRATE INTOXICATION
DUE TO LONG-TERM INGESTION OF LOW LEVELS OF NITRATE FROM EITHER WATER OR FEED
SUPPLIES. CHRONIC CONDITION IN CATTLE ... RELATES TO INCR NITRATES IN THE DIET.
CLINICAL SIGNS ARE NONSPECIFIC, BUT OFTEN INVOLVE DECR WT GAIN & FEED
EFFICIENCY, DECR MILK PRODN, POOR REPRODUCTIVE CAPACITY & IMPAIRED HEALTH OF
EPITHELIAL TISSUES AS EXPRESSED BY DIGESTIVE TRACT AND RESPIRATORY DISORDERS.
/NITRATES/
Fertilizers containing ammonium nitrate can cause illness in poultry.
400 mg/l has been suggested as a toxic limit for livestock.
pH and water hardness are important in determining toxicity.
The min lethal toxicity of ... ammonium nitrate ... for Rana temporaria
chensinensis tadpoles was 0.91 g/l, and the max tolerance concn was 0.83 g/l. In
field experiments, ammonium nitrate at concn of 0.25 g/l had no adverse effect
on the tadpoles as reflected by their growth rate.
Acute toxicity was studied of N fertilizers for Daphnia magna, Planaria
tigrina, and Poecilia reticulata in experiments lasting 120 hours in water of pH
6.0-6.5 or 7.5-7.8. With the increasing pH, the effects of preparations with an
NH4+ ion increased. The most sensitive to industrial N fertilizers was P tigrina.
... The order of preparations according to their acute toxicity on the water
animals was: urea much less than Ca(NO3)2 much less than DAM 390 < ammonium
nitrate and (NH4)2SO4. ... DAM 390 is relatively toxic, and ammonium nitrate and
(NH4)2SO4 are toxic.
Ammonium nitrate has caused poisoning in cattle.
Sources of nitrates which may cause intoxication include fertilizers
containing ... ammonium nitrate, well water, swill prepared with contaiminated
water from such sources and commercial dynamite. The principal hazard to
livestock is due to the accumulation of nitrate by certain plants when they grow
on soils containing an excess of this material. These plants include many weeds
and when conditions such as drought are unfavorable for growth, barley, wheat,
rye hay, and other common foodstuffs. Sublethal doses of the herbicide 2,4-D may
also cause an excessive accumulation of nitrate in treated weeds and sugar beet
plants. Due to lowered activity of the enzyme nitrate reductase, the nitrate
levels found in plants are higher on dull days and at night.
Non-Human Toxicity Values:
LD50 Rat oral 4500 mg/kg.
Ecotoxicity Values:
LD50 Aspergillus niger (fungus) 15 mg/l/40 hr (36 deg C).
Metabolism/Pharmacokinetics:
Absorption, Distribution & Excretion:
12 Healthy volunteers ingested orally 7-10.5 g ammonium nitrate in a single
dose & 12 others received 9.5 g of sodium nitrate iv in approx 60 min.
Samples of blood, saliva & urine were collected just before a 24 hr period.
Saliva and urine were analyzed for volatile N-nitrosamines, nitrate &
nitrite. Blood was analyzed for nitrate. Neither in urine nor in saliva were N-nitrosamines
other than N-nitrosodiethylamine detected. Of the 188 urine samples, 13%
contained greater than 0.1 ug N-nitrosodiethylamine/kg the highest level being
0.5 ug/kg. In 92% of the 179 saliva samples, less than 0.5 ug N-nitrosodiethylamine/l
was found. Peak values for nitrate plus nitrite in saliva, which were reached
2-6 hr after intake, varied strongly between individuals, ranging from 4-43 mmol/l.
Nitrite was detected in 26% of the urine samples. An average of 75% of
administered nitrate was excreted in urine in 24 hr. Nitrate contents in blood,
urine & saliva after 24 hr were still higher than before the nitrate intake.
Pharmacology:
Therapeutic Uses:
ACID FORMING SALTS ... ARE EFFECTIVE ONLY IN PROMOTING NET LOSS OF
EXTRACELLULAR ELECTROLYTE & WATER FOR PERIOD OF 1-2 DAYS. ... CHIEF VALUE IS
TO COMPENSATE FOR ALKALOSIS INDUCED BY MERCURIAL DIURETICS, HIGH-CEILING
DIURETICS, & LESS COMMONLY THE THIAZIDES. /SRP: FORMER USE/
MEDICATION (VET): IT HAS BEEN USED AS EXPECTORANT & URINARY ACIDIFIER
Environmental Fate & Exposure:
Probable Routes of Human Exposure:
As a result of the blasting agent used in mines, ammonium nitrate, workers
are subjected to air pollution in mines which poses an occupational health
hazard.
Natural Pollution Sources:
Does not occur in nature
Environmental Fate:
Aquatic: Ammonium nitrate is a nutrient in water. Spills of ammonium nitrate
may cause massive algal blooms in static waters and affect local species
population balance in the aquatic environment.
Ammonium nitrate is quite soluble in water (250 g/100 ml at 20 deg C). Thus,
if precipitation occurs prior to clean up, or if water is used to disperse the
spilled chemical, the solution of
ammonium nitrate produced can infiltrate the soil and migrate downward toward
the groundwater system.
Environmental Biodegradation:
Ammonium nitrate will be taken up by bacteria. Nitrate is more persistent in
water than /the/ ammonium ion; nitrate degradation is fastest in anaerobic
conditions.
Soil Adsorption/Mobility:
When spilled on soil, the liquid form will spread on the surface and
penetrate into the soil at a rate dependent on the soil type and its water
content.
Volatilization from Water/Soil:
The immediate loss of fertilizer nitrogen as nitrous oxide (biochemical &
microbiological) into the atmosphere was determined by in situ measurements of
the nitrous oxide evolution rates from uncultivated Eolian sand. The net loss
was equivalent to 0.1% of the applied fertilizer for ammonium chloride, 0.05%
for ammonium nitrate & 0.01% for sodium nitrate. The total immediate loss of
nitrous oxide-nitrogen after application of mineral fertilizer is estimated to
be 0.004-1.2 teragram/yr.
Sediment/Soil Concentrations:
The effects of nitrogen sources on nitrates and ammonium concn in leachate
& runoff from golf greens were studied. All profiles were equipped with
subsurface tile drains over a plastic sheet and were treated sequentially with
the ammonium nitrate, ureaformaldehyde, 12-12-12, Milorganite &
isobutylenediurea (IBDU). Nitrate concn in leachate from sand, mixed & soil
greens fertilized with quick release materials ranged from 45-326, 8-314 &
8-170 mg/l, respectively & remained in this range for a 3-wk period. Nitrate
nitrogen losses from various sources were in the order of ammonium nitrate
greater than 12-12-12 greater than Milorganite greater than IBDU greater than
ureaformaldehyde. Soluble sources, ammonium nitrate and 12-12-12 exhibited
leaching within 5 days after application.
Atmospheric Concentrations:
The total suspended particulate in the ambient aerosol in the 24 hr period
measurements exceeds the Federal secondary standard, 150 ug/cu m, 10% of the
time. The maximum 4 hr mass measurements for the total mass and fine mass
fractions are 307 and 204 ug/cu m, respectively. The fine fraction of the total
suspended particulate with diameter less than 2.5 mu consisting of organic
carbon 23.7; ammonium nitrate 20.0, elemental carbon 16.8, ammonium sulfate
13.6, & others constitutes 42 to more than 50% of the aerosol.
Environmental Standards & Regulations:
FIFRA Requirements:
Ammonium nitrate is exempted from the requirement of a tolerance when used as
a desiccant or defoliant in the production of cottonseed, grain sorghum,
peppers, potatoes, sweet potatoes.
Ammonium nitrate is exempted from the requirement of a tolerance when used as
a adjuvant/intensifier for herbicides in accordance with good agricultural
practice as inert (or occasionally active) ingredients in pesticide formulations
applied to growing crops only.
FDA Requirements:
Bottled water shall, when a composite of analytical units of equal volume
from a sample is examined by the methods described in paragraph (d)(1)(ii) of
this section, meet the standards of chemical
quality and shall not contain nitrate, as nitrogen, in excess of 10.0 mg/l.
/Nitrate, as nitrogen/
Allowable Tolerances:
Ammonium nitrate is exempted from the requirement of a tolerance when used as
a desiccant or defoliant in the production of cottonseed, grain sorghum,
peppers, potatoes, sweet potatoes.
Ammonium nitrate is exempted from the requirement of a tolerance when used as
a adjuvant/intensifier for herbicides in accordance with good agricultural
practice as inert (or occasionally active) ingredients in pesticide formulations
applied to growing crops only.
Chemical/Physical Properties:
Molecular Formula:
H4-N2-O3
Molecular Weight:
80.06
Color/Form:
COLORLESS RHOMBIC CRYSTALS; MONOCLINIC WHEN TEMP IS GREATER THAN 32.1 DEG C
TRANSPARENT CRYSTALS OR WHITE GRANULES; FIVE SOLID PHASES EXIST AT NORMAL
PRESSURE; ORTHORHOMBIC @ ROOM TEMP
Colorless (pure) to gray or brown (fertilizer grade).
Odor:
Odorless
Boiling Point:
210 DEG C AT 11 MM HG
Melting Point:
169.6 DEG C
Density/Specific Gravity:
1.725 @ 25 DEG C
pH:
0.1 M soln in water: 5.43
Solubilities:
118.3 G/100 CC OF H2O @ 0 DEG C, 871 G @ 100 DEG C; 3.8 G/100 CC ETHANOL @ 20
DEG C; SOL IN ACETONE; 17.1 G/100 CC METHANOL @ 20 DEG C; SOL IN AMMONIA; INSOL
IN ETHER
Sol in alkalies
Other Chemical/Physical Properties:
DECOMP ABOUT 210 DEG C MOSTLY INTO WATER AND NITROGEN OXIDE; HYGROSCOPIC,
DELIQUESCENT
Latent heat of fusion 6.110 kJ/mol
Latent heat of sublimation 174.5 kJ/mol at 20 deg C.
Heat of formation -339.9 kJ/mol at 25 deg C.
Heat of solution -27.1 kJ/mol at 18 deg C and infinite dilution.
Heat capacity at constant pressure 139 J/mol deg C at 25 deg C.
Coefficient of thermal expansion 9.82X10-4/deg C.
Thermal conductivity 0.25 J/m X sec X deg C at 20 deg C.
Chemical Safety & Handling:
DOT Emergency Guidelines:
Fire or explosion: These substances will accelerate burning when involved in
a fire. Some may decompose explosively when heated or involved in a fire. May
explode from heat or contamination. Some will react explosively with
hydrocarbons (fuels). May ignite combustibles (wood, paper, oil, clothing,
etc.). Containers may explode when heated. Runoff may create fire or explosion
hazard. /Ammonium nitrate, liquid (hot concentrated solution); Ammonium nitrate
solution, with not more than 0.2% combustible substances; Ammonium nitrate, with
organic coating/
Health: Inhalation, ingestion or contact (skin, eyes) with vapors or
substance may cause severe injury, burns, or death. Fire may produce irritating,
corrosive and/or toxic gases. Runoff from fire control or dilution water may
cause pollution. /Ammonium nitrate, liquid (hot concentrated solution); Ammonium
nitrate solution, with not more than 0.2% combustible substances; Ammonium
nitrate, with organic coating/
Public safety: CALL Emergency Response Telephone Number on Shipping Paper
first. If Shipping Paper not available or no answer, refer to appropriate
telephone number listed on the inside back cover. Isolate spill or leak area
immediately for at least 10 to 25 meters (30 to 80 feet) in all directions. Keep
unauthorized personnel away. Stay upwind. Keep out of low areas. Ventilate
closed spaces before entering. /Ammonium nitrate, liquid (hot concentrated
solution); Ammonium nitrate solution, with not more than 0.2% combustible
substances; Ammonium nitrate, with organic coating/
Protective clothing: Wear positive pressure self-contained breathing
apparatus (SCBA). Structural firefighters' protective clothing will only provide
limited protection. /Ammonium nitrate, liquid (hot concentrated solution);
Ammonium nitrate solution, with not more than 0.2% combustible substances;
Ammonium nitrate, with organic coating/
Evacuation: Large spill: Consider initial downwind evacuation for at least
100 meters (330 feet). Fire: If tank, rail car or tank truck is involved in a
fire, ISOLATE for 800 meters (1/2 mile) in all directions; also, consider
initial evacuation for 800 meters (1/2 mile) in all directions. /Ammonium
nitrate, liquid (hot concentrated solution); Ammonium nitrate solution, with not
more than 0.2% combustible substances; Ammonium nitrate, with organic coating/
Fire: Small fires: Do not use dry chemicals,
CO2, Halon or foams. Use water only. Large fires: Flood fire area with water
from a distance. Move containers from fire area if you can do it without risk.
Do not move cargo or vehicle if cargo has been exposed to heat. Fight fire from
maximum distance or use unmanned hose holders or monitor nozzles. Cool
containers with flooding quantities of water until well after fire is out.
ALWAYS stay away from the ends of tanks. For massive fire, use unmanned hose
holders or monitor nozzles; if this is impossible, withdraw from area and let
fire burn. /Ammonium nitrate, liquid (hot concentrated solution); Ammonium
nitrate solution, with not more than 0.2% combustible substances; Ammonium
nitrate, with organic coating/
Spill or leak: Keep combustibles (wood, paper, oil, etc.) away from spilled
material. Do not touch damaged containers or spilled material unless wearing
appropriate protective clothing. Stop leak if you can do it without risk. Do not
get water inside containers. Small dry spills: With clean shovel place material
into clean, dry container and cover loosely; move containers from spill area.
Small liquid spills: Use a non-combustible material like vermiculite, sand or
earth to soak up the product and place into a container for later disposal.
Large spills: Dike far ahead of liquid spill for later disposal. Following
product recovery, flush area with water. /Ammonium nitrate, liquid (hot
concentrated solution); Ammonium nitrate solution, with not more than 0.2%
combustible substances; Ammonium nitrate, with organic coating/
First aid: Move victim to fresh air. Call emergency medical care. Apply
artificial respiration if victim is not breathing. Administer oxygen if
breathing is difficult. Remove and isolate contaminated clothing and shoes. In
case of contact with substance, immediately flush skin or eyes with running
water for at least 20 minutes. Keep victim warm and quiet. Ensure that medical
personnel are aware of the material(s) involved, and take precautions to protect
themselves. /Ammonium nitrate, liquid (hot concentrated solution); Ammonium
nitrate solution, with not more than 0.2% combustible substances; Ammonium
nitrate, with organic coating/
/Ammonium nitrate, liquid (hot concentrated solution); Ammonium nitrate
solution, with not more than 0.2% combustible substances; Ammonium nitrate, with
organic coating/
Skin, Eye and Respiratory Irritations:
Irritating to eyes, nose, and throat, and mucous membranes.
NFPA Hazard Classification:
Health: 1. 1= Materials that, on exposure, would cause irritation, but only
minor residual injury, including those requiring the use of an approved
air-purifying respirator. These materials are only slightly hazardous to health
and only breathing protection is needed. /Non-fire situation/
Health: 2. 2= Materials that, on intense or continued (but not chronic)
exposure, could cause temporary incapacitation or possible residual injury,
including those requiring the use of respiratory protective equipment that has
an independent air supply. These materials are hazardous to health, but areas
may be entered freely if personnel are provided with full-face mask
self-contained breathing apparatus that provides complete eye protection. /Fire
situation/
Flammability: 0. 0= Includes any material that will not burn.
Reactivity: 3. 3= Includes materials that, in themselves, are capable of
detonation, explosive decomposition, or explosive reaction, but which require a
strong initiating source or heating under confinement. This includes materials
that are sensitive to thermal and mechanical shock at elevated temperatures and
pressures and materials that react explosively with water. Fires involving these
materials should be fought from a protected location.
Fire Fighting Procedures:
If fire becomes uncontrollable, evacuate for a radius of 5,000 feet.
Cool exposed containers with water. Continue cooling after fire has been
extinguished.
Use flooding quantities of water. Fight fire from protected location or
maximum possible distance. Approach fire from upwind to avoid hazardous vapors
and toxic decomposition products. Fire situations may require evacuation.
Toxic Combustion Products:
[Bureau of Explosives; Emergency Handling of Haz Matl in Surface Trans p.30
(1981)] Toxic oxides of nitrogen are produced in fires involving this material.
Explosive Limits & Potential:
MAY EXPLODE UNDER CONFINEMENT AND HIGH TEMPERATURES. EXPLOSIONS HAVE OCCURRED
IN SHIP'S HOLDS, ETC. THERE HAVE BEEN WAREHOUSE FIRES THAT DID NOT DETONATE.
IN THE PURE STATE IT REQUIRES A COMBINATION OF AN INITIATOR AND A HIGH
EXPLOSIVE. THIS COMBINATION IS KNOWN AS A REINFORCED DETONATOR. ...IN
COMBINATION WITH NITRO COMPOUNDS (EG TNT) FORMS ONE OF THE MAJOR HIGH EXPLOSIVES
FOR MILITARY USE.
A mixture of these chemicals is
used as an explosive. /Sodium perchlorate & ammonium nitrate/
Strong oxidizer. If heated under confinement, material may explode. Ammonium
nitrate of any grade, including fertilizer, when contaminated with oil,
charcoal, or other organic materials should be considered an explosive capable
of detonation by combustion or by explosion of adjacent explosive materials.
Combustion by-products include oxides of nitrogen, ammonia. Closed containers
may rupture violently when heated.
Hazardous Reactivities & Incompatibilities:
The decomposition of ammonium nitrate in the presence of ammonium chloride
(0.1%) becomes violent around 175 deg C. The gases liberated contain chlorine.
With ammonium chloride, (barium nitrate), water, zinc: Addition of water to
an intimate mixture of zinc powder and the metal salts causes spontaneous
ignition and a mixture of ammonium nitrate and ammonium chloride...sprinkled
with zinc dust ignites vigorously when moistened.
Mixtures of ammonium nitrate with charcoal and metal oxides: The pelleted
explosive ("ammonpulver", containing 10% charcoal) normally ignites at
160-165 deg C, but presence of rust, or copper or zinc oxides, lowers the
temperature to 80-120 deg C.
With fertilizer materials: Mixtures of ammonium nitrate, superphosphate and
organic materials stored in bulk may ignite if the internal temperature exceeds
90 deg C. This is owing to the free acid in the superphosphate, and may be
prevented by neutralization with ammonia.
During the flame cutting of a pipeline plugged with impure ammonium nitrate,
the pipe contents exploded violently.
Fused ammonium nitrate with powdered metal is often a violent and sometimes
an explosive reaction. Zinc, cadmium, copper, magnesium, lead, cobalt, nickel,
bismuth, chromium, and antimony are the metals that reacted in this way.
A mixture of white (or yellow) phosphorus & ammonium nitrate can be
exploded by percussion.
A mixture of ammonium sulfate and ammonium nitrate can easily be exploded by
potassium or sodium-potassium alloy.
Sodium and ammonium nitrate react through a series of reductions to form a
yellow explosive substance believed to be disodium nitrite.
The two substances /zinc and ammonium nitrate/ are mixed intimately and
wetted with 3 or 4 drops of water. After a short time, a violent reaction occurs
with the evolution of steam and zinc oxide.
Explodes more readily if contaminated with combustible /materials/.
With copper iron (II) sulfide: During preparations for blasting the sulfide
mineral copper pyrites, ammonium nitrate based cartridges exploded prematurely
in the blast holes. This was attributed to exothermic interaction of acid
groundwater with the sulfide-oxidant combination.
With metals: Shock sensitivity of mixtures of ammonium nitrate and powdered
metals decreases in the order titanium, tin, aluminum, magnesium, zinc, lead,
iron, antimony, and copper.
With urea: concentrated solutions of ammonium nitrate and urea exploded
during large scale mixing operations. Although the cause was not established,
hazards /associated with/ these operations are discussed in relation to the
circumstances.
With potassium permanganate: Admixture of 0.5% potassium permanganate with an
ammonium nitrate explosive caused an explosion 7 hr later. This was /due/ to
formation and exothermic decomposition of ammonium permanganate leading to
ignition.
Reacts violently with reducing agents, strong acids, powdered metals, organic
materials.
Hazardous Decomposition:
Decomposes @ 210 deg C, with evolution of nitrous oxide.
When heated to decomp ... emits highly toxic fumes of /nitrogen oxides/.
Prior History of Accidents:
Explosions ascribed to ammonium nitrate occurred in 1947 at Texas City and at
Brest.
Protective Equipment & Clothing:
PERSONAL PROTECTIVE EQUIPMENT ... SHOULD BE PROVIDED FOR NORMAL PROCESS WORK
AS PROTECTION AGAINST EYE SPLASHES, ACID BURNS, DERMATITIS & SKIN ABSORPTION
... PERSONAL HYGIENE IS PARTICULARLY IMPORTANT WHEN HARMFUL NITRO-COMPD ARE
BEING PRODUCED & MANIPULATED. /EXPLOSIVES/
Wear boots, protective gloves, and goggles.
Preventive Measures:
Do not handle broken packages without protective equipment.
Eliminate sources of ignition including traffic and equipment.
Restrict access to spill site. Issue warning: "Oxidizer".
Overheating during manufacture (above 121 deg C) must be avoided due to
explosion potential.
Store on clean concrete floors, or on wooden pallets, dunnage or on any type
of clean floor. When stored directly on a concrete floor, the floor should be
covered first with a moisture insulator such as polyethylene sheet. Bags of
ammonium nitrate should be stored not less than 30 inches away from the walls of
a storage building. The bags should be stacked, and made accessible, with proper
ventilation provided. Stacks should be not more than 8 ft wide and 7 ft high.
Where applicable, the bags should be kept at least 36 inches from the eaves and
from support beams and rafters overhead. Open flames, sparks and other sources
of heat should be kept 50 ft away from storage areas of bags. Smoking within 50
ft of storage areas must be prohibited. Emptied bags should be disposed of
promptly and properly.
SRP: The scientific literature for the use of contact lenses in industry is
conflicting. The benefit or detrimental effects of wearing contact lenses depend
not only upon the substance, but also on factors including the form of the
substance, characteristics and duration of the exposure, the uses of other eye
protection equipment, and the hygiene of the lenses. However, there may be
individual substances whose irritating or corrosive properties are such that the
wearing of contact lenses would be harmful to the eye. In those specific cases,
contact lenses should not be worn. In any event, the usual eye protection
equipment should be worn even when contact lenses are in place.
Stability/Shelf Life:
Stability during transport: If heated strongly, decomposes, giving off toxic
gases and gases which support combustion. Undergoes detonation if heated under
confinement.
Shipment Methods and Regulations:
No person may /transport,/ offer or accept a hazardous material for
transportation in commerce unless that person is registered in conformance ...
and the hazardous material is properly classed, described, packaged, marked,
labeled, and in condition for shipment as required or authorized by ... /the
hazardous materials regulations (49 CFR 171-177)./
The International Air Transport Association (IATA) Dangerous Goods
Regulations are published by the IATA Dangerous Goods Board pursuant to IATA
Resolutions 618 and 619 and constitute a manual of industry carrier regulations
to be followed by all IATA Member airlines when transporting hazardous
materials.
The International Maritime Dangerous Goods Code lays down basic principles
for transporting hazardous chemicals.
Detailed recommendations for individual substances and a number of
recommendations for good practice are included in the classes dealing with such
substances. A general index of technical names has also been compiled. This
index should always be consulted when attempting to locate the appropriate
procedures to be used when shipping any substance or article.
Storage Conditions:
KEEP WELL CLOSED.
Separate from acids, alkalies, reducing agents, combustible materials. Store
in a cool, dry well ventilated location.
Cleanup Methods:
AIR OR WASTE GAS FROM MFR OF GRANULATED AMMONIUM NITRATE ARE TREATED WITH
ATOMIZED WATER & STEAM TO DISSOLVE AMMONIUM NITRATE DUST. MIST CONTAINING
AMMONIUM NITRATE IN SOLN IS REMOVED FROM AIR OR WASTE GAS IN DEMISTERS.
AMMONIUM NITRATE PRILLING TOWERS EMIT FUME CONTAINING AMMONIUM NITRATE
PARTICLES LESS THAN 1 MU. THIS WASTE GAS IS TREATED BY MIST OF AMMONIUM NITRATE
SOLN IN VENTURI SCRUBBER & AGGLOMERATED PARTICLES ARE FILTERED. THE AMMONIUM
NITRATE IS RECOVERED.
Stop the flow and contain spill, if safe to do so.
Spills on land: Contain if necessary by forming mechanical and/or chemical
barriers to prevent spreading and shovel spilled material into non- combustible
containers for disposal.
Spills on land: Spilled material can be dissolved in large amounts of water,
soda ash added and mixed. The mixture is then neutralized with 6M hydrogen
chloride.
Spills in water: Activated carbon can be applied, at 10% the spill amount,
over the region occupied by 10 mg/l or greater concentration. Mechanical dredges
or lifts may be used to remove immobilized masses of pollutants.
An ion exchange process has been used successfully to treat waste streams
ranging in solute concn from 1,700 to 11,000 ppm. The process uses a classical
demineralization system.
Disposal Methods:
Remove slowly into a large container of water. Add Na2CO3 /sodium carbonate/
slightly by stirring. After 24 hr, decant or siphon into another container.
Neutralize with 6 M-HCL /6 M-hydrochloric acid/ and drain into the sewer with
abundant water. Recommendable methods: Landfill, discharge to sewer, chemical
treatment, sea disposal. Not recommendable method: Thermal destruction.
Peer-review: Care. Ammonia nitrate can explode if heated. Do not mix with
organic material. Small amounts only: Landfill. Dilute with much water and
discharge to sewer. Large amounts of ammonia in landfill leachate may make
disposal of leachate difficult. Treatment with sodium or calcium hydroxide will
liberate ammonia which should be collected, dissolved in water and reused.
Residue to sewer well diluted. Sea disposal is an option for large amounts of
this material. (Peer-review conclusions of an IRPTC expert consultation (May
1985))
If incinerated, scrubbers are required for nitrogen dioxide and oxidation or
reduction process for nitrogen oxide.
Following treatment either at the spill site or at a waste management
facility, the resultant sludge can be disposed in a secure landfill.
Occupational Exposure Standards:
Manufacturing/Use Information:
Major Uses:
IN FREEZING MIXTURES; MFR OF MATCHES & PYROTECHNICS
DIRECT APPLICATION NITROGEN FERTILIZER; CHEM INT FOR NITROUS OXIDE; COMPONENT
OF MIXT WITH FUEL OIL FOR INDUST EXPLOSIVES & BLASTING AGENTS
IN COSMETIC PREPN
HERBICIDES & INSECTICIDES; ABSORBENT FOR NITROGEN OXIDES; OXIDIZER IN
SOLID ROCKET PROPELLANTS; NUTRIENT FOR ANTIBIOTICS & YEAST; CATALYST
Used as a desiccant for cotton.
/As a propellant oxidizer/, ammonium nitrate has been used in slow burning
propellants and where smokeless exhaust is required.
The extensive use of ammonium nitrate in ammonium nitrate fuel oil (ANFO) and
water based commercial explosives has revolutionized the industry and displaced
the nitroglycerin based dynamites.
AMMONIUM NITRATE IS FOUND IN HAIR DYES, TINTS, & COLORINGS.
Used in military explosives such as amatols, ammonals, manols, and amatexes
as a partial replacement for alpha-2,4,6-trinitrotoluene (TNT) or
cyclotrimethylenetrinitramine (RDX).
MEDICATION (VET)
Manufacturers:
Air Products and Chemicals, Inc, Hq,
Allentown, PA 18195-1501, (215) 481-4911; Chemicals
Group, (800) 345-3148; Industrial Chemicals
Division; Production site: Pace, FL 32571
Arcadian Corp, Hq, 6750 Poplar Ave, Suite 600, Memphis, TN 38138, (901)
758-5200; Production sites: Geismar, LA 70734; Augusta, GA 30903; Clinton, IA
52732; La Platte, NE 68005; Savannah, GA 31418; Wilmington, NC 28402
Apache Nitrogen Products Co, Hq, PO Box 700, Bensen, AZ 85602, (602)
720-2217; Production site: Benson, AZ 85602
BP America, Inc, Hq, 200 Public Sq, Cleveland, OH 44114-2375, (216) 586-4141;
Subsidiary: BP Chemicals America, Inc;
Production site: Lima, OH 45802
CF Industries, Inc, Hq, Salem Lake
Dr, Long Grove, IL 60047, (708) 438-9500; Production site: Donaldsonville, LA
70346
Chevron Corporation, Hq, 225 Bush
St, San Francisco, CA 94104, (415) 894-7700; Subsidiary: Chevron Chemical
Company; Chevron Fertilizer Division, 6001 Bollinger Canyon Rd, San Ramon, CA
94583-0947; Production sites: Kennewick, WA 99336; St Helens, OR 97051;
Richmond, CA 94804
The Coastal Corp, Hq, Coastal Tower, 9 Greenway Plaza, Houston, TX 77046,
(713) 877-1400; Subsidiary: Coastal Natural Gas Co; Subsidiary: Coastal Chemical
Inc; Production site: Cheyenne, WY 82003
Cominco American Incorporated, Hq, 601 West Riverside, Spokane, WA 99201,
(509) 747-6111; Cominco Fertilizer Division, Production site: Beatrice, NE 68310
Explosives Technologies International, Hq, Rockwood Office Park, 501 Carr Rd,
Suite 200, Wilmington, Delaware 19802, (302) 761-1900; Production site: Seneca,
IL 61360
Farmland Industries, Inc, Hq, 3315 North Oak Trafficway, PO Box 7305, Kansas
City, MO 64116, (816) 459-6000; Production sites: Dodge City, KS 67801;
Lawrence, KS 66044; Beatrice, NE 68310
Inspiration Resources Corporation,
Hq; Subsidiary: Terra International, Inc, Terra Centre, 600 Fourth St, Sioux
City, IA 51101, (712) 277-1340; Production site: Sergeant Bluff, IA 51054;
Woodward, OK 73801
IRECO Inc, Hq, 11th floor, Crossroads Tower, Salt Lake
City, UT 84144, (801) 364-4800; Production sites: Donora, PA 15033; Louisiana,
MO 63353
La Roche Holdings Inc, Hq, La Roche Industries, Inc, Perimeter 400 Center,
1100 Johnson Ferry Rd NE, Atlanta, GA 30342, (404) 851-0300; Production sites:
Cherokee, AL 35616; Crystal City, MO 63019; Geneva, UT 84601
LSB Industries, Hq, 16 S Pennsylvania Ave, PO Box 754, Oklahoma City, OK
73101, (405) 235-4546; Subsidiary: El Dorado
Chemical Co, Production site: El
Dorado, AR 71730
Mississippi Chemical Corporation,
Hq, PO Box 388, Yazoo City, MS 39194, (601) 746-4131; Production site: Yazoo
City, MS 39194
Nitram, Inc, Hq, 5321 Hartford St, PO Box 2968, Tampa, FL 33601, (813)
626-2181 Production site: Tampa, FL 83601
J R Simplot Co, Hq, PO Box 912, Pocatello, ID 83204, (208) 238-2700; Minerals
and Chemical Division; Production
sites: Helm, CA 93627; Pocatello, ID 83204
TradeMark Nitrogen Corp, Hq, 1216 Old Hopewell Rd, PO Box 1750, Brandon, FL
33509, (813) 626-1181; Production site: Tampa, FL 33619
Unocal Corporation, Hq, 1201 W
Fifth St, PO Box 7600, Los Angeles, CA 90051, (213) 977-7600; Unocal Minerals
and Chemicals Division; Agricultural
Products Group Production sites: Brea, CA 92621; West Sacramento, CA 95691
Willard Grain and Feed, Hq, Route 2, Box 41, Celina, TX 75009, (214)
382-2367; Wil-Gro Fertilizer, Inc, division, PO Box 2129 Pryor, OK 74362;
Production site: Pryor, OK 74362
Methods of Manufacturing:
REACTION OF NITRIC ACID & AMMONIA IN THE PRESENCE OF WATER
Reacting calcium nitrate by-product from nitrophosphate plants with nitric
acid and carbon dioxide.
General Manufacturing Information:
FERTILIZER INSTITUTE STATES THAT FERTILIZER GRADE OF AMMONIUM NITRATE IS NOT
EXPLOSIVE.
Very greatly accelerated use of a combustible sensitized ammonium nitrate
started in 1955 when mixtures were packaged in plastic, waterproof bags for use
in large diameter boreholes, mainly in coal mining stripping operations. Within
3 yr, porous prilled ammonium nitrate, a product of the fertilizer industry,
which had a rather large particle size, was tested extensively in both Canada
and the USA in approx a 94/6 ammonium nitrate and fuel oil mixture. The mixture
known as AN/FO was not desensitized by moderately damp conditions, and in wet
operations was often protected adequately by enclosure in polyethylene bags.
Later on, the majority of blasting in the USA was done with AN/FO and similar
nitrate types of explosives. /Explosives/
WITH AMMONIUM CHLORIDE OR AMMONIUM THIOSULFATE
Ammonium nitrate changes its crystal form every time it passes through a
temperature of 90 deg F. It also absorbs moisture rapidly from the air when the
humidity exceeds about 60%. The exact percent varies with the temperature. In
dry atmospheres the material dries out. Both these processes cause the particles
to knit together. The tendency to cake can be greatly reduced by coating the dry
material with 2-4% of a conditioning agent such as kieselguhr, kaolin, clay, or
tricalcium phosphate, and storing in moisture proof bags.
The ammonium salt of nitric acid is prepared by treating the acid with
ammonia, removing essentially all of the water, and prilling or granulating the
resulting melt. Various processes have been developed and used to prepare the
solid product. These include crystallization, flaking, prilling, and
granulation. Prilling is the predominant practice. Two types of prills are
produced: (1) low- density prills are formed by cooling droplets of concentrated
solution (95%) of ammonium nitrate as they fall through upcoming air in a prill
tower, and (2) high-density prills are produced by using a melt (99+%) of
ammonium nitrate in a similar system but with a shorter prill tower.
With cyanoguanidine (dicyandiamide): Mixtures of cyanoquanidine with ammonium
nitrate were formerly proposed for use as powerful explosives.
Nitric acid, initially derived from ammonia, is the starting material for
ammonium nitrate, and other nitrogen compounds used in the manufacture of
explosives.
May be made resistant to flame and detonation by proprietary process
involving addition of 5 - 10% ammonium phosphate.
Formulations/Preparations:
Grades: usually expressed in percent of nitrogen, as 20.5% nitrogen; 33.5%
nitrogen. FGAN is fertilizer grade, prilled & usually coated with kieselguhr.
Also avail as 83% soln. Temp stabilized grade is ... available which inhibits
breakdown of prills due to crystalline changes.
Fertilizer grade: 33.5% nitrogen.
Granular ammonium nitrate can be produced in almost any desired size range
and has greater crushing strength than prills.
Fertilizer nitrates including high grade or straight ammonium nitrate, AN
(33-34% N); ammonium sulfate-nitrate, ASN (26%N), and calcium-ammonium nitrate,
CAN (20.5-28% N)
ANFO consists of 94% ammonium nitrate prills coated with an anti-caking agent
and 6% absorbed fuel oil.
For use in explosives-99% purity, water content of not more than 0.15%,
should contain only small amounts of ether-soluble and water insoluble
materials, sulfates & chlorides; 99.5% purity for nitrous oxide manufacture,
ammonium phosphate is sometimes introduced as a stabilizer in the amount of a
fraction of a percent.
Impurities:
Ammonium nitrate fertilizer contains no more than 2% carbon.
Ammonium nitrate, solution contains not less than 15% water.
Consumption Patterns:
84% IN FERTILIZER APPLICATIONS; 16% IN PRODN OF EXPLOSIVES & BLASTING
AGENTS; LESS THAN 1% AS A CHEMICAL
INTERMEDIATE FOR NITROUS OXIDE (1975)
Demand 14.4 B lb (1978), up 2.3%/yr from 1968.
U. S. Production:
(1972) 6.4X10+12 GRAMS
(1975) 6.78X10+12 G
(1985) 6.27X10+12 g
(1990) 14.16 billion lb
(1991) 14.62 billion lb
(1991) 2.82X10+6 metric tons
(1992) 15.66 billion lb
(1993) 16.79 billion lb
U. S. Imports:
(1972) 3.29X10+11 GRAMS (EST)
(1975) 1.82X10+11 GRAMS (EST)
(1984) 1.14x10+11 g
U. S. Exports:
(1972) 2.54X10+10 GRAMS (EST)
(1975) 3.18X10+10 GRAMS (EST)
Laboratory Methods:
Analytic Laboratory Methods:
GRAINS, MEALS, SUPPLEMENTS, DRIED PLANTS, HAYS, GRASSES, SILAGES &
PRODUCTS; COLORIMETRIC DETERMINATION. /NITRATES/
Ion chromatography: An aliquot is injected into a suitable ion chromatograph
and the retention time and peak height noted. Nitrate is then determined using a
standard curve. Operating conditions for the ion chromatograph are: 3.1 ml/min
eluent flow rate, ambient column temperature, standard eluent which is 0.003
molar sodium bicarbonate and 0.0024 molar sodium carbonate, 100 ul sample loop,
conductivity meter setting at 10uMHO full scale, and a chart speed of 40 cm/hr.
A range of 0.1 to 25.4 ppm nitrate in the extract may be determined using ion
chromatography. This is equivalent to between 28 and 7,055 ug/cu m (0.01 to 2.16
ppm in air) of 0.1 to 25.4 ppm in water.
Analysis in Soil: A 5 g sample of 2 mm soil is shaken for 60 min with 50 ml
of 2M potassium chloride solution. The solution is boiled for 15 min with solid
magnesium oxide to remove any ammonia, cooled, filtered, and diluted to 50 ml. A
suitable aliquot of extract is transferred to a distillation flask. A boric acid
solution is prepared by dissolving 20 g boric acid in 900 ml of water and adding
20 ml mixed indicator. The indicator is prepared by dissolving 0.1 g
bromocrescol green and 0.07 g methyl red in 100 ml of ethanol. Sodium hydroxide
(O.1M) is then added drop-wise until a reddish-purple color is obtained. The
column is then brought up to 1 liter. A 5 ml aliquot of the boric acid solution
is transferred to a suitable conical flask beneath the condenser which is
attached to the distillation flask. 0.5 g of magnesium oxide is added to the
sample extract and and the flask is stopped. The contents are steam distilled
into the boric acid solution. A 35 ml volume of distillate is collected and
discarded. A 1 ml volume of 2% aqueous sulfuric acid is added and the solution
is swirled. 0.2 g of Devarda's alloy is added to the distillation flask.
Devarda's alloy is prepared by combining 50 g copper, 45 g aluminum, and 5 g
zinc. The contents are steam distilled into a fresh 5 ml portion of boric acid
solution. A 30 ml volume of distillate is collected and titrated with
standardized hydrochloric acid.
EPA Method 9200. Colorimetric Method for the determination of nitrate in
ground water, drinking, surface, and saline waters, and domestic and industrial
wastes. Modification can be made to remove or correct for turbidity, color,
salinity, or dissolved organic compounds in the sample. The method is based upon
the reaction of the nitrate ion with the brucine sulfate in a 13 N sulfuric acid
solution at a temperature of 100 deg C. The color of the resulting complex is
measured at 410 nm. Temperature control of the color extremely critical. The
applicable range of concentration is 0.1 to 2 mg nitrate nitrogen/l of sample.
Twenty-seven analysts in fifteen laboratories analyzed natural-water samples
containing increments of inorganic nitrate with the following results: For the
increments of the exact 0.16, 0.19, 0.08, and 1.24 mg/l, the standard deviation
was 0.092, 0.083, 0.245, and 0.214 mg/l, respectively and the accuracy was
-0.01, +0.02, +0.04, and +0.04 mg/l, respectively. /Nitrate/
Method 4500-Nitrate Ion E. Cadmium Reduction Method for the determination of
nitrate nitrogen in water and wastewater. This method uses commercially
available cadmium granules treated with copper sulfate to form a copper coating.
The nitrite produced is determined by diazotizing with sulfanilamide and
coupling with N-(1-naphthyl)ethylenediamine to form a highly colored azo dye
that is measured colorimetrically. Interferences include iron, copper and other
metals at concentrations above 1 mg/l, and residual chlorine. The appliable
range of this method is 0.01 to 1.0 mg nitrate-nitrogen/l. The method is
especially recommended for nitrate levels below 0.1 mg nitrogen/l where other
methods lack adequate sensitivity. /Nitrate/
Method 418 D. Chromotropic Acid Method for determination of nitrate nitrogen
in water and wastewater. Nitrate /ion/ reacts with one mole of chromotropic acid
to form a yellow reaction product with maximum absorbance at 410 nm.The maximum
color develops within 10 min and is stable for 24 hr. The method is recommended
for the concn range 0.1 to 5 mg nitrate nitrogen/l. A synthetic sample
containing 1.00 mg nitrate nitrogen/l was analyzed by 5 laboratories with a
relative standard deviattion of 8% and relative error of 3%. /Nitrate/
Determination of nitrate in cheese by modified Jones reduction method.
Applicable to cheeses containing greater than or equal to 1 ppm nitrate.
/Nitrate/
Determination of nitrogen (nitrate) in fertilizers by using Jones
modification of Robertson method. Applicable when water soluble newton (10
dynes) need to be determined. /Nitrate/
Determination of nitrogen (nitrate) in water by brucine colorimetric method.
Nitrate ion reacts with brucine in sulfuric acid at 100 deg to form colored cmpd
whose absorbance is measured at 410 nm. Temperature control of reaction is
critical. /Nitrate/
Method 418E. Dvarda's Alloy Reduction Method for the determination of nitrate
nitrogen in water and wastewater. This method is recommended for oxidized
nitrogen concn greater than 2 mg/l. In this technique, nitrate ion and nitrite
ion are reduced to ammonia under hot alkaline conditions in the presence of a
reducing agent, Devarda's alloy (an alloy of 50% copper, 45% aluminum and 5%
zinc). Under hot alkaline conditions, the ammonia formed distills and is trapped
in a receiving flask containing boric acid. The ammonia can be determined either
by direct nesslerization or acidimetrically. For the determination of nitrate
nitrogen. A separate determination of nitrogen dioxide should be made and
subtracted, otherwise the result is reported as "total oxidized
nitrogen." The recovery of 200 to 400 ug nitrate nitrogen from partially
treated effluents was found to average 96% with a coefficient of variation of
7.7%. /Nitrate/
Sampling Procedures:
A known volume of air is drawn through a 37 mm diameter cellulose-ester
filter of 0.8 um pore size or a minimum volume of 2 liters of liquid is
collected. A sample size of 90 liters is recommended at a flow rate between 1.5
and 2.0 liters per min. The sample filter is then transferred to a 60 ml
container with tweezers and extracted with 25 ml of distilled water by gentle
swirling.
Special References:
Special Reports:
Environment Canada; Tech Info for Problem Spills: Ammonium Nitrate (Draft)
(1981)
Synonyms and Identifiers:
Synonyms:
AMMONIUM (I) NITRATE (1:1)
**PEER REVIEWED**
Caswell No. 045
**PEER REVIEWED**
EPA Pesticide Chemical Code 076101
**PEER REVIEWED**
German saltpeter
**PEER REVIEWED**
HERCO PRILLS
**PEER REVIEWED**
Merco Prills
**PEER REVIEWED**
Nitram
**PEER REVIEWED**
Nitrate d'ammonium (French)
**PEER REVIEWED**
Nitrate of ammonia
**PEER REVIEWED**
Nitrato amonico (Spanish)
**PEER REVIEWED**
Nitric acid, ammonium salt
**PEER REVIEWED**
Norway saltpeter
**PEER REVIEWED**
VARIOFORM I
**PEER REVIEWED**
Formulations/Preparations:
Grades: usually expressed in percent of nitrogen, as 20.5% nitrogen; 33.5%
nitrogen. FGAN is fertilizer grade, prilled & usually coated with kieselguhr.
Also avail as 83% soln. Temp stabilized grade is ... available which inhibits
breakdown of prills due to crystalline changes.
Fertilizer grade: 33.5% nitrogen.
Granular ammonium nitrate can be produced in almost any desired size range
and has greater crushing strength than prills.
Fertilizer nitrates including high grade or straight ammonium nitrate, AN
(33-34% N); ammonium sulfate-nitrate, ASN (26%N), and calcium-ammonium nitrate,
CAN (20.5-28% N)
ANFO consists of 94% ammonium nitrate prills coated with an anti-caking agent
and 6% absorbed fuel oil.
For use in explosives-99% purity, water content of not more than 0.15%,
should contain only small amounts of ether-soluble and water insoluble
materials, sulfates & chlorides; 99.5% purity for nitrous oxide manufacture,
ammonium phosphate is sometimes introduced as a stabilizer in the amount of a
fraction of a percent.
Shipping Name/ Number DOT/UN/NA/IMO:
UN 2426; Ammonium nitrate, solution (containing 35% water); Ammonium nitrate,
liquid (not concentrated solution)
UN 0223; Ammonium nitrate fertilizers: which is more liable to explode than
ammonium nitrate with 0.2% combustible substances, including any organic
substances calculated as carbon, to the exclusion of any other added substances.
IMO 5.1; Ammonium nitrate fertilizers, Type A, uniform non segregating
mixtures of ammonium nitrate with added matter which is inorganic and chemically
inert towards ammonium nitrate, containing not less than 90% of ammonium nitrate
and not more than 0.2% of combustible material (including organic material
calculated as carbon), or containing less than 90% but more than 70% of ammonium
nitrate and not more than 0.4% of total combustible material; Uniform non
segregating mixtures of nitrogen/phosphate or nitrogen/potash types or complete
fertilizers of nitrogen/phosphate/potash type, containing more than 70% but less
than 90% of ammonium nitrate and not more than 0.4% of total combustible
material.
IMO 1.1; Ammonium nitrate fertilizer, which is more liable to explode than
ammonium nitrate, with more than 0.2% by weight of combustible substances,
including any organic substance calculated as carbon, to the exclusion of any
other added substance.
IMO 9.0; Ammonium nitrate fertilizers, Type B. Uniform non-segregating
mixtures of nitrogen/phosphate or nitrogen potash types or complete fertilizers
of nitrogen/phosphate/potash type, containing not more than 70% of ammonium
nitrate and not more than 0.4% of total added combustible material or
containing, not more than 45% of ammonium nitrate with unrestricted combustible
material.
UN 1942; Ammonium nitrate, with not more than 0.2% of combustible substance
including any organic substance calculated as carbon, to the exclusion of any
other added substance.
UN 2067; Ammonium nitrate fertilizers, Type A, uniform non segregating
mixtures of ammonium nitrate with added matter which is inorganic and chemically
inert towards ammonium nitrate, containing not less than 90% of ammonium nitrate
and not more than 0.2% of combustible material (including organic material
calculated as carbon), or containing less than 90% but more than 70% of ammonium
nitrate and not more than 0.4% of total combustible material.
UN 2068; Ammonium nitrate fertilizers: Uniform non segregating mixtures of
ammonium nitrate with calcium carbonate and/or dolomite, containing more than
80% but less than 90% of ammonium nitrate and not more than 0.4% of total
combustible material; Ammonium nitrate - carbonate mixture.
UN 2069; Ammonium nitrate fertilizers: Uniform non segregating mixtures of
ammonium nitrate/ammonium sulfate, with more than 45% but not more than 70% of
ammonium nitrate and not more than 0.4% of total combustible material.
UN 2070; Ammonium nitrate fertilizers: Uniform non segregating mixtures of
nitrogen/phosphate or nitrogen/ potash types or complete fertilizers of
nitrogen/phosphate/potash type, containing more than 70% but less than 90% of
ammonium nitrate and not more than 0.4% of total combustible material.
UN 2071; Ammonium nitrate fertilizers, Type B. Uniform non segregating
mixtures of nitrogen/phosphate or nitrogen/potash types or complete fertilizers
of nitrogen/phosphate/potash type, containing not more than 70% of ammonium
nitrate and not more than 0.4% of total added combustible material or
containing, not more than 45% of ammonium nitrate with unrestricted combustible
material.
UN 0222; Ammonium nitrate, with more than 0.2% by weight of combustible
substances, including any organic substance calculated as carbon, to the
exclusion of any other added substance.
NA 1942; Ammonium nitrate, (no organic coating)
UN 2072; Ammonium nitrate fertilizers, not otherwise specified
Standard Transportation Number:
49 183 12; Ammonium nitrate, organic coating
49 183 10; Ammonium nitrate fertilizer, containing no more than 0.2% carbon
49 187 05; Ammonium nitrate mixed fertilizer
49 187 74; Ammonium nitrate, solution, containing not less than 15% water
49 183 11; Ammonium nitrate (no organic coating)
49 187 34; Ammonium nitrate-carbonate mixture
49 029 10; Ammonium nitrate-fuel oil mixture (containing only prilled
ammonium nitrate and fuel oil)
49 187 04; Ammonium nitrate-phosphate
49 187 03; Ammonium nitrate, magnesia, and pulp mixture (oxidizing material)
49 187 02; Ammonium nitrate, sodium nitrate mixture (oxidizing material)
RTECS Number:
NIOSH/BR9050000
Administrative Information:
Hazardous Substances Databank Number: 475
Last Revision Date: 20020114
Last Review Date: Reviewed by SRP on 11/30/1992