Environ. Sci. Technol. 2000, 34, 497-504
Oxidation of Aminodinitrotoluenes
with Ozone: Products and
Pathways
R O N A L D J . S P A N G G O R D , *
C . D A V I D YA O , A N D T H E O D O R E M I L L
SRI International, 333 Ravenswood Avenue,
Menlo Park, California 94025
accelerated with electron-donating groups and retarded with
electron-withdrawing groups. Reaction pathways and prod-
An investigation of the products from the reaction of
ozone with aminodinitrotoluenes (ADNTs) provides information
about the oxidation pathway. Studies conducted at low
conversions of 2- and 4-ADNT show 2:1 ozone/ADNT
stoichiometries, prompt formation of glyoxylic and pyruvic
acids, and NO2- and NO3 (NOx) ions. Reaction schemes
to account for these results involve a 1,3-dipolar cycloaddition
of ozone to selected double bonds of the aromatic ring,
leading to ring cleavage. N-Labeling experiments indicate
that the amino function is not involved in the initial
ozone oxidation and eventually is incorporated into
pyruvamide (2-ADNT) and oxamic acid (4-ADNT) before
being oxidized to nitrate.
-
15
ucts can become complex, depending on the nature and
number of the substituents (3). Both electron-donating
(
amino, methyl) and electron-withdrawing (nitro) groups in
ADNTs create reactive centers for ozonide decomposition in
water and lead to a multiplicity of products. The ADNTs
serve as interesting examples of ozone oxidations in aromatic
systems with multiple reaction sites and the products provide
pathway information in electron-deficient systems. With the
exception of a few simple aromatics and polycyclic aromatics,
detailed characterization of polysubstituted aromatic ozone
reactions has not been done.
Introduction
Aminodinitrotoluenes [2-amino-4,6-dinitrotoluene (2-ADNT)
and 4-amino-2,6-dinitrotoluene (4-ADNT)] are environmen-
tal pollutants that arise from the microbial biotransformation
of 2,4,6-trinitrotoluene (TNT). These chemicals are unique
to soils, lagoons, and groundwaters near TNT production
and handling facilities. In the remediation of such environ-
ments, consideration must be given to the behavior of these
pollutants toward the remediation technology. In the previous
paper (1), we investigated the kinetics of the ozone-hydrogen
peroxide (peroxone) oxidation of 2- and 4-ADNT and found
that, under most peroxone usage conditions, the oxidation
of ADNTs is controlled by ozone. In using an oxidation
remediation process, it becomes important to know the final
end products formed under the treatment conditions. In this
investigation, we determined the products resulting from
ozone oxidation of 2- and 4-ADNT and evaluated products
Experimental Section
Chem icals. 2- and 4-ADNT were prepared in our laboratory
at 99% purity using the method of Zbarskii (4). 15N-Labeled
aminodinitrotoluenes were prepared by the method of
Spanggord and Clizbe (5). The remaining chemicals were
obtained from Aldrich Chemical Co. (Milwaukee, WI) or
synthesized where indicated. An authentic standard of oxamic
acid aldehyde was prepared using the method of Tits and
Bruylant (6); pyruvamide was prepared using the method of
Claison and Shadwell (7). Both standards yielded chromato-
graphic retention volumes and UV spectral data identical to
those for ozonation products from ADNTs.
Ozone Oxidations. Ozone oxidations were conducted in
aqueous solutions adjusted to pH 5.0 with phosphate buffer.
Ozone was generated from a Welsbach ozone generator and
bubbled into water. Ozone concentrations were measured
using the indigo colorimetric method (8).
An ozone stock solution was added in 20 µM increments
to a rapidly stirred stock solution of ADNT (150 µM). After
each addition, the ADNT was analyzed by reverse-phase high-
performance liquid chromatography (HPLC), using a gradient
program developed for aldehydes and ketones as their 2,4-
dinitrophenylhydrazones (DNPHs, 9) and using an Alltech
Altima C18 column (5 µm, 4.6 × 250 mm) and UV detection
at 350 nm. Under these conditions, the ADNTs eluted at 11.4
min. Carboxylic acids were analyzed by ion chromatography
using a Supelcogel 610H column and UV detection at 210
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from oxidation of N-amino-labeled ADNTs, from which
multiple potential oxidation pathways can be advanced.
Many of the mechanistic approaches to the oxidation of
organic compounds by ozone can be described by the Criegee
mechanism (2, 3). The initial steps for ozonation of an
aromatic compound appear to involve sequential formation
of a π-complex (I), an addition product (II), a zwitterion (III),
and an isoozonide (IV) as shown here for benzene.
In aqueous systems, water can play a major role in the
decomposition of intermediates I-IV to form aldehydes or
ketones and hydroxyhydroperoxides (V). If the aromatic ring
has substituents, reaction with ozone will be significantly
*
Corresponding author phone: (650)859-3822; fax: (650)859-4321;
e-mail: ronald.spanggord@sri.com.
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0.1021/es990190h CCC: $19.00
2000 Am erican Chem ical Society
VOL. 34, NO. 3, 2000 / ENVIRONMENTAL SCIENCE & TECHNOLOGY
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Published on Web 12/29/1999