Subchronic Nasal Toxicity of Hexamethylphosphoramide Administered to Rats Orally for 90 Days
FUNDAMENTAL AND APPLIED TOXICOLOGY 40, 1 5 - 2 9 (1997)
ARTICLE NO. FA972375
Subchronic Nasal Toxicity of Hexamethylphosphoramide
Administered to Rats Orally for 90 Days
Douglas A. Keller, Craig E. Marshall, and K. P. Lee
E. I. du Pont de Nemours and Company, Haskell Laboratory for Toxicology and Industrial Medicine,
1090 Elkton Road, P.O. Box 50, Newark, Delaware 19714
Received September 30, 1996; accepted September 3, 1997
the nasal tissue via inhalation. Oral administration of HMPA is a
less potent route for producing nasal lesions than is inhalation.
Subchronic Nasal Toxicity of Hexamethylphosphoramide Administered to Rats Orally for 90 Days. Keller, D. A., Marshall,
C. E., and Lee, K. P. (1997). Fundam. AppL ToxicoL 40, 15-29.
C 1997 Sodety of Tmdcotogy.
Rats were administered hexamethylphosphoramide (HMPA) at
dosages of 10,100, 300, and 1000 ppm in drinking water or at 15,
40, or 120 mg/kg/day by gavage for approximately 90 days. Another group of rats was implanted subcutaneously with HMPAfilled osmotic minipumps, designed to deliver a dosage of 40 mg/
kg/day to prevent the possibility of direct contact of HMPA with
the nasal epithelium. After 90 days at 10 ppm in the drinking
water, some rats had tracheas lined with regenerated epithelium,
but no HMPA-related lesions were present in any other organs
and tissues. At 100 ppm, nasal lesions (epithelial denudation, regeneration, and squamous metaplasia) were mostly in the maxillo
turbinates, tips of nasoturbinates, and the adjacent septum in the
anterior nasal cavity (level I), but the lesions were confined to the
ventral region of the mid-anterior nasal cavity (level II) and to
recesses of the posterior nasal cavity (levels III and IV). At 300
ppm, nasal turbinates in level I were partially adhered to the
nasal septum byfibroustissue. In level II the lesions were mainly
confined to the ventral medial meatus, but were scattered diffusely
in levels HI and IV. Denuded turbinates showed minimal bone
proliferation. At 1000 ppm, the anterior nasal cavity was partially
occluded by extensive adhesion of the turbinates to the nasal septum by granulation tissue and proliferating turbinate bone. The
general architecture of the posterior nasal cavity was obliterated
by the marked proliferation of turbinate bone and fibrous tissue
in the interturbinate spaces. Tracheas showed regenerated epithelium and bronchi had focal epithelial denudation at 100, 300,
and 1000 ppm. Foamy alveolar macrophages (histiocytosis) were
increased in the lungs at 300 and 1000 ppm. Testicular atrophy
occurred at 1000 ppm. No other tissues were affected by HMPA
treatment Nasal lesions in rats given HMPA by gavage were identical in nature to, but sometimes slightly more severe than, the
lesions in rats given HMPA in the drinking water. Rats given 40
mg/kg/day HMPA via an osmotic minipump had slightly less severe nasal lesions than did the rats given the same dosage of
HMPA by gavage. Testicular atrophy was present in the rats given
120 mg/kg/day by gavage. The results of this study show that, with
the exception of bone proliferation, systemic delivery of HMPA or
its metabolites to the nasal tissue following oral administration
causes tissue damage similar to that caused by direct exposure of
15
Hexamethylphosphoramide (HMPA) has unique solvent
properties of being both highly water-soluble and highly
organic soluble and was at one time widely used in organic
and organo-metallic reactions in research laboratories. Industrially, it was used as a processing solvent for aromatic
polyimide fiber, a polymerization catalyst, a stabilizer
against thermal degradation in polystyrene, and an additive
to polyvinyl and polyolefin resins. It also has been tested as
a chemosterilant for insects, as an antistatic agent, a flame
retardant, and a deicing additive for jet fuels (NIOSH, 1975).
Acutely, HMPA has low oral toxicity with an LD50 in
the range of 2500-5000 mg/kg, moderate dermal toxicity
to rabbits with an LD50 of 2600 mg/kg, and moderate inhalation toxicity with a 4-h LC50 of 400 ppm. Subchronically,
severe bronchiectasis and bronchopneumonia were observed
in the lungs of rats fed a dietary concentration of 2000 ppm
HMPA (127-106 mg/kg) over a period of 52-72 days (Kimbrough and Sedlak, 1968). Similarly, exacerbation of murine
pneumonia was observed in rats fed HMPA at 10 and 50
mg/kg for 92 days (Short et ai, 1971). Rhinitis, murine
pneumonia, and/or testicular atrophy were found in rats administered HMPA at 100 mg/kg for 62-100 days (Overcash
etal, 1971).
In a 2-year feeding study in rats at dosages of 6.25, 3.12,
1.56, or 0.78 mg/kg HMPA daily, there were no differences
in the incidence of tumors between treated and control animals (Kimbrough and Gaines, 1973). Nasal tumors were
detected after 6 months in rats exposed by inhalation to 400
and 4000 ppb and after 13 months of exposure to 50 ppb
(Lee and Trochimowicz, 1982a).
Several studies have shown that HMPA is extensively
metabolized by rat and dog nasal epithelium (Dahl et ai,
1982; Hadley and Dahl, 1982; Rickard and Quarels, 1981;
Kuykendall et al, 1995). The only metabolites of HMPA
presently known are the demethylated derivatives penta-
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16
KELLER, MARSHALL, AND LEE
methylphosphoramide and tetramethylphosphoramide and
the demethylation product formaldehyde (Jones and Jackson,
1968).
The potency of the carcinogenic response produced by
inhalation of HMPA in rats has generated much interest in
the mutagenicity of HMPA and its metabolites. HMPA is
mutagenic in several in vivo assays, such as the mouse bone
marrow micronucleus test (Ashby et al., 1985a) and the
Drosophila melanogaster sex-linked recessive lethal assay
(Zijlstra et al., 1989). Results from in vitro tests show weak
activity of HMPA with metabolic activation or, in some
cases, lack of activity (Amacher and Turner, 1985; Ashby
et al., 1985a,b). Most studies indicate a role for metabolism
of HMPA to formaldehyde, a known rat nasal carcinogen, in
the mutagenic process for HMPA (Kuykendall et al., 1995).
HMPA has low volatility and is not uniquely an inhalation
hazard. The high carcinogenic potency of HMPA by inhalation and the lack of overt nasal effects after chronic oral
administration at low doses suggests that more information
is needed about the dose-response relationships in the oral
toxicity of HMPA. The purpose of the present study was to
determine the potential oral toxicity of HMPA in rats, with
respect to the dose-dependence and site-specificity of lesions, by administration in drinking water and by oral gavage. An osmotic minipump implant group was included in
the oral gavage study to preclude definitively direct exposure
of the nasal passages to HMPA (a potential confounding
factor in the drinking water study), and to test the effect of
delivery rate (continuous exposure versus bolus) of HMPA
on the toxici (...truncated)