General Description
A colorless liquid with a peculiar odor. Slightly denser than water. Contact may irritate to skin, eyes, and mucous membranes. May be toxic by ingestion. Used to make other chemicals.
Reactivity Profile
QUINOLINE(91-22-5) is hygroscopic. QUINOLINE(91-22-5) absorbs as much as 22% water. QUINOLINE(91-22-5) is sensitive to light and moisture. QUINOLINE(91-22-5) darkens on storage. This chemical is a weak base. A potentially explosive reaction may occur with hydrogen peroxide. QUINOLINE(91-22-5) reacts violently with dinitrogen tetraoxide. QUINOLINE(91-22-5) also reacts violently with perchromates. QUINOLINE(91-22-5) is incompatible with (linseed oil + thionyl chloride) and maleic anhydride. QUINOLINE(91-22-5) is also incompatible with strong oxidizers and strong acids. This chemical can be unpredictably violent. QUINOLINE(91-22-5) dissolves sulfur, phosphorus and arsenic trioxide. QUINOLINE(91-22-5) may attack some forms of plastics. QUINOLINE(91-22-5) is a preparative hazard.
Air & Water Reactions
Hygroscopic. Soluble in water.
Health Hazard
Vapors are irritating to nose and throat and may cause headaches, dizziness, and nausea if inhaled. Ingestion causes irritation of mouth and stomach; vomiting may occur. Contact with eyes or skin causes irritation.
Potential Exposure
In manufacture of quinoline deriva-
tives (dyes and pesticides); in synthetic fuel manufacture.
Occurs in cigarette smoke.
First aid
Move victim to fresh air. Call 911 or emergency
medical service. Give artificial respiration if victim is not
breathing. Do not use mouth-to-mouth method if victim
ingested or inhaled the substance; give artificial respiration
with the aid of a pocket mask equipped with a one-way valve
or other proper respiratory medical device. Administer oxy-
gen if breathing is difficult. Remove and isolate contami-
nated clothing and shoes. In case of contact with substance,
immediately flush skin or eyes with running water for at
least 20 minutes. For minor skin contact, avoid spreading
material on unaffected skin. Keep victim warm and quiet.
Effects of exposure (inhalation, ingestion or skin contact) to
substance may be delayed. Ensure that medical personnel
are aware of the material(s) involved and take precautions to
protect themselves. Medical observation is recommended
for 24 to 48 hours after breathing overexposure, as pulmo-
nary edema may be delayed. As first aid for pulmonary
edema, a doctor or authorized paramedic may consider
administering a drug or other inhalation therapy.
Shipping
UN2656 Quinoline, Hazard Class: 6.1; Labels:
6.1-Poisonous materials.
Incompatibilities
Reacts, possibly violently, with strong
oxidants, strong acids; perchromates, nitrogen tetroxide;
and maleic anhydride. Keep away from moisture, steam,
and light. Contact with hydrogen peroxide may cause
explosion. Unpredictably violent, this substance has been
the source of various plant accidents.
Chemical Properties
colourless to brown liquid
Chemical Properties
Quinoline has a heavy, penetrating and nauseating, yet sweet odor of good tenacity.
Chemical Properties
Quinoline is a colorless liquid with a penetrating
amine odor. Turns brown on exposure to light.
Waste Disposal
Dissolve or mix the material
with a combustible solvent and burn in a chemical incinera-
tor equipped with an afterburner and scrubber. All federal,
state, and local environmental regulations must be observed.
Occurrence
Quinoline was discovered in coal tar distillate in 1834 by Runge. It is released to
the environment through natural combustion processes and has been isolated from
air particulates (Dong et al 1977). Quinoline may be a significant aqueous
byproduct of synthetic fuel production (shale oil, coal processing) and from wood
preservation production and use facilities. Small amounts also have been detected
in tobacco smoke (Schmeltz and Hoffmann 1977).
Definition
A
colorless two-ring heterocyclic compound
with an unpleasant odor, which acts as a
base and forms salts with acids. First made
from the alkaloid quinine, it is found in
bone oil and coal tar and used for making
drugs and dyestuffs.
Definition
ChEBI: The simplest member of the quinoline class of compounds, comprising a benzene ring ortho fused to C-2 and C-3 of a pyridine ring.
Definition
quinoline: A hygroscopic unpleasant-smelling colourless oily liquid,C9H7N; b.p. 240°C. Its molecules consistof a benzene ring fused to a pyridinering. It occurs in coal tar andbone oil, and is made from phenylamineand nitrobenzene. Quinolineis a basic compound, forming saltswith mineral acids and forming quaternaryammonium compounds withhaloalkanes. It is used for makingmedicines and dyes. In quinoline, thenitrogen atom is one atom awayfrom the position at which the ringsare fused. In an isomer, isoquinoline,the nitrogen atom is positioned twoatoms away from the fused ring.
Production Methods
Quinoline may be synthesized by heating aniline with glycerol and nitrobenzene in
sulfuric acid (Skraup method) or by reacting aniline, acetaldehyde, and a formaldehyde
hemiacetal (Windholz et al 1983). Commercial production is by isolation
from coal tar with greater than 100,000 lbs being produced in 1977. Production of
refined quinoline has almost ceased due to low demand (Parris et al 1983).
Aroma threshold values
Detection: 710 ppb
Taste threshold values
Taste characteristics at 2 to 10 ppm: earthy, musty, nutty, coumarinic with a chemical nuance.
Flammability and Explosibility
Nonflammable
Chemical Reactivity
Reactivity with Water No reaction; Reactivity with Common Materials: Attacks some forms of plastics; Stability During Transport: Stable; Neutralizing Agents for Acids and Caustics: Not pertinent; Polymerization: Not pertinent; Inhibitor of Polymerization: Not pertinent.
Industrial uses
Quinoline is used as a solvent for resins and terpenes. It also is used as an
antimalarial, an antioxidant, a catalyst and as an intermediate in the manufacture
of various products (Parris et al 1983).
Carcinogenicity
Liver tumors were observed in
rats administered diets containing 0.05–0.25% quinoline.
The incidence of hepatocellular carcinomas was 3/11 at
0.05%, 3/16 at 0.1%, and 0/19 at 0.25% versus 0/6 in controls.
At 0.25%, most of the rats died within 40 weeks. The
incidences of hemangioendotheliomas were 6/11, 12/16,
18/19, and 0/6, respectively. Hepatocellular carcinomas
and hemangioendotheliomas were seen in livers of rats
fed 500, 1000, or 2500 ppm for 16–40 weeks. Typical
hyperplasias were also observed in the liver.
Environmental Fate
biodegradative processes occur under aerobic conditions. Anaerobic degradation
is minimal (Mill et al 1981). Breakdown of quinoline in natural waters has been
correlated with bacterial concentration (Rogers et al 1984). Adsorption was high in
acidic soils (pH<6) and low in basic soils (pH>7). The presence of pyridine
decreased quinoline adsorption on acidic, but not basic, soils. Sorption did not
correlate with organic carbon or clay content (Felice et al 1984). Soil bacteria have
been grown with quinoline as the sole carbon source (Grant and Al-Najjar 1976).
Quinoline did not bioconcentrate to a significant extent in fathead minnows
(Southworth et al 1980).
Purification Methods
Dry quinoline with Na2SO4 and distil it from zinc dust in a vacuum. It has also been dried by boiling with acetic anhydride, then fractionally distilled. Calvin and Wilmarth [J Am Chem Soc 78 1301 1956] cooled redistilled quinoline in ice and added enough HCl to form its hydrochloride. Diazotization removed aniline, the diazo compound being broken down by warming the solution to 60o. Non-basic impurities were removed by ether extraction. Quinoline was then liberated by neutralising the hydrochloride with NaOH, then dried with KOH and fractionally distilled at low pressure. Addition of cuprous acetate (7g/L of quinoline) and shaking under hydrogen for 12hours at 100o removed impurities due to the nitrous acid treatment. Finally the hydrogen was pumped off, and the quinoline was distilled. Other purification procedures depend on conversion to the phosphate (m 159o, precipitated from MeOH solution, filtered, washed with MeOH, then dried at 55o) or the picrate (m 201o) which, after recrystallisation, were reconverted to quinoline. The method using the picrate [Packer et al. J Am Chem Soc 80 905 1958] is as follows: quinoline is added to picric acid dissolved in the minimum volume of 95% EtOH, giving yellow crystals which were washed with EtOH, air-dried and crystallised from acetonitrile. These were dissolved in dimethyl sulfoxide (previously dried over 4A molecular sieves) and passed through a basic alumina column, onto which the picric acid is adsorbed. The free base in the effluent is extracted with n-pentane and distilled under vacuum. Traces of solvent can be removed by vapour-phase chromatography. [Moonaw & Anton J Phys Chem 80 2243 1976.] The ZnCl2 and dichromate complexes have also been used [Cumper et al. J Chem Soc 1176 1962]. [Beilstein 20 H 339, 20 I 134, 20 II 222, 20 III/IV 3334, 20/7 V 276.]
Toxicity evaluation
Quinoline undergoes Phase I metabolism to form an enamine
oxide, a rapid transitional epoxide, which can then form DNA
adducts. This epoxide is formed on the pyridine moiety of
quinoline. Fluorination at position 3 completely prevents the
mutagenicity of quinoline. The major metabolic enzyme is the
CYP2E1 isoform with the primary end product from this
reaction being 3-hydroxyquinoline. Refer to the sections on ‘Genotoxicity’ and ‘Carcinogenicity’ for more specific descriptions
of quinoline toxicity. The primary and most severe, toxic
outcome following quinoline exposure is genotoxicity followed
by tumor formation.