Toxicology
Letters,
71
30 (1986) 71-78
Elsevier
TOXLett.
1528
REDUCED SERUM THYROID HORMONE LEVELS IN HEXACHLOROBENZENE-INDUCED PORPHYRIA (Hexachlorobenzene; induction) K. ROZMANab*, ‘Department Kansas
J.R.
toxicity; hypothyroidism;
GORSKIa,
of Pharmacology,
City,
(U.S.A.)
Umweltforschung
Miinchen,
October
14th, 1985)
received
November 2nd,
26th,
microsomal enzyme
and A. PARKINSON=
and Therapeutics, fiir
8042.Neuherberg
(Revision
December
Toxicology
66103 and bAbteilung
(Received (Accepted
P. ROZMANa
porphyria;
University
Toxikologie
of Kansas Medical
der Gesellschaft
fir
Center,
Strahlen-
und
(F. R. G.)
1985)
1985)
SUMMARY The effect of feeding 0.1% hexachlorobenzene porphyrin
excretion,
serum
in female Sprague-Dawley 33% mortality by dietary
thyroid
rats. This dosage
with a mean time to death
HCB,
whereas
(HCB) for 55 days on mortality,
hormones
non-survivors
and induction regimen,
followed
of 67 k 4 days.
underwent
a rapid
(4-fold)
and a significant
(Ts). When rats were returned prox.
100 times higher
the experiment the
activity
weight loss (wasting)
and
UDP-glucuronosyl
HCB-induced
lethality induction
benzo[a]pyrene
*To whom
c reductase
as substrate)
HCB,
hormones
cytochrome
were significantly hydroxylase
occur by different by HCB,
prior to death.
in the excretion continued
suppressed.
indicator
P-450 and cytochrome
induced,
03.50
whereas
the activity
(2) reduced
T4 and Tj serum levels
of aryl hydrocarbon
hydroxylase
(with
of HCB exposure.
T3, triiodothyronine;
Td, thyroxine;
Science Publishers
B.V. (Biomedical
Division)
of
that (I)
be addressed.
hexachlorobenzene;
0 Elsevier
bs and
aminopyrine-N-
chlorodibenzo-p-dioxin.
0378-4274/86/S
to rise (ap-
At the end of
was not. Results demonstrate
mechanisms,
and (3) induction
At the
of urinary
(Td) and triiodothyronine
porphyrins
remained
in
was not affected
pentoxyresorufin-0-dealkylase,
is not a sensitive
should
of urinary
of liver microsomal
transferase
and porphyria
correspondence
Abbreviations:
and serum thyroid
and benzo[a]pyrene
of porphyria
an increase
urinary
was studied
diet, resulted
of survivors
in the levels of serum thyroxine
diet the excretion
ethoxyresorufin-0-deethylase,
NADPH-cytochrome accompany
than controls)
(day 97), the concentration of
demethylase
decrease
to a regular
enzymes
by 42 days of a regular
Body weight
end of the dosing period (day 55), rats fed the HCB diet exhibited porphyrins
body weight,
of liver microsomal
TCDD,
2,3,7,8-tetra-
72 INTRODUCTION
Chronic exposure of laboratory animals and to HCB elicits a number of effects, such as induction of liver microsomal enzymes, porphyria, hypothyroidism, a wasting syndrome and lethality [l-3]. These manifestations of HCB exposure are quite similar to those seen in laboratory animals intoxicated with polychlorinated biphenyls or TCDD [4-61. The causal relationships between these responses to polyhalogenated aromatic hydrocarbons, as well as the ultimate cause of death, remain largely unknown despite many years of intensive investigation. It has been shown that the toxicity of halogenated aromatic hydrocarbons in rats and mice correlates well with their ability to induce liver microsomal aryl hydrocarbon hydroxylase (benzo~a]pyr~ne) and UDP-glucuronosyl transferase (ff-naphthol) activity [7]. However, the induction of these enzymes is apparently not responsible for the lethal effect of halogenated aromatic hydrocarbons [8]. To gain more insight into the mechanism of toxicity of HCB, this experiment examined the time course of various end points of toxicity (mortality, body weight, porphyria), thyroid hormone status and microsomal enzyme induction in rats chronically exposed to dietary HCB. METHODS
15 Female Sprague-Dawley rats (Sasco, Omaha, NE) were housed in metabolism cages with free access to feed (Ralston Purina Co., St. Louis, MO) and water (room temperature: 2.5 + 2°C; 12 h light/dark cycle and uncontrolled humidity). After 1 week, rats were divided into 2 groups. 6 rats (271 f 2 g), designated as controls, were maintained throughout this experiment under the conditions described above. For 55 consecutive days, 9 rats (272 + 5 g), were fed a diet containing 0.1 crloHCB (Teklad No. 83147, Madison, WI). HCB was purchased from Aldrich, Milwaukee, WI, and recrystallized from benzene until greater than 99% pure as determined by gas chromatography (Varian No. 3700, electron capture detector, SE-30 column, 30 ml/min nitrogen flow at 200°C). After the 55-day dosing period, the rats were returned to a regular diet for an additional 42 days. Body weight of each rat was measured daily and mortality recorded. 24-h urine samples were collected from 6 rats in each group at 41, 55, 62 and 97 days after the first dose of HCB and total porphyrins were determined. Urine (1 ml) was subjected to anion exchange chromatography (AGI-X8, 50-80 mesh, chloride form, Bio-Rad Laboratories, Richmond, CA) and the absorbance of the 3 N hydrochloric acid eluate was measured at 430, 380 and 403 nm. The absorbance was corrected for the presence of biological material and recovery validated as described by Harmsen and Strik [9]. Blood (1 ml) was drawn from the tail vein of 6 rats in each group at 55, 62 and 97 days after the first dose of HCB, and T4 and T3 levels in serum were determined by radioimmunoassay (Corning Reagents Nos. 474207 and 474209).
73
Survivors of the experiment were killed 97 days after the first dose of HCB and livers were removed and weighed. Liver microsomes were prepared as described by Lu and Levin [lo] and stored as a suspension in 0.25 M sucrose at - 80°C. Protein concentration was measured by the method of Lowry et al. [ll] with bovine serum albumin as standard. Cytochrome P-450 content was determined according to Omura and Sato [ 121; from the carbon monoxide-difference spectrum of dithionite-reduced microsomes based on an extinction coefficient of 91 mM - ‘cm - ‘. The concentration of cytochrome bs was determined by the method of Raw and Mahler [13]; from the difference spectrum between NADH-reduced and oxidized microsomes based on a corrected extinction coefficient of 185 mM - ‘cm - ’ [ 121. The rate of oxidative N-demethylation of aminopyrine was measured essentially as described by Parkinson and Safe with minor modifications [14]; from the production of formaldehyde by measuring absorbance at 412 nm after reaction with Nash reagent [15]. Activities of benzo[a]pyrene hydroxylase [16] and 7-ethyoxyresorufin 0-deethylase [17] were measured as described by Corski et al. [18]. The 0-dealkylation of 7-pentoxyresorufin (Pierce Chemical Company) was measured essentially as described [19]. The 7-pentoxyresorufin was added to the l-ml incubation mixture in 40 ~1methanol at a final concentration of 5 FM. NADPH-cytochrome c reductase activity was measured as described by Phillips and Langdon [20] with lo-20 pg/ml of microsomal protein. UDP-glucuronosyl transferase activity towards I-naphthol was measured according to Otani et al. [21]. Microsomes were solubilized with 10 mM 3[(3-cholamidopropyl)-dimethylammonio]l-propane sulfonate [22] and the reaction mixtures (0.5 ml) were incubated at 37°C in the presence of Tris-HCl (0.2 M, pH 7.4), saccharic acid-1,blactone (2.2 mM), MgC12 (10 mM) and [i4C]naphthol (0.5 mM) (New England Nuclear Corp., Boston, MA) at the final concentrations indicated. Reactions were started by the addition of 2 pmol UDPglucuronic acid. Reagent blanks contained no UDP-glucuronic acid. Reactions were terminated by the addition of 0.5 ml of ice-cold ethanol. In preliminary experiments, conditions were established such that the amount of product formed was proportional to both incubation time and microsomal protein concentration. Statistics were performed by Student’s two-tailed t-test [23]. RESULTS
Of 9 rats fed a diet containing 0.1% HCB for 55 days, 3 died approx. 2 weeks after being returned to a regular diet. As shown in Fig. 1, body weight of survivors and non-survivors was not different from controls at the time HCB administration was discontinued (day 55). However, non-survivors started losing weight at about day 60 in a fashion resembling TCDD-induced ‘wasting syndrome’ [24]. 41 Days after the first dose of HCB, excretion of total urinary porphyrins was not different in control and HCB-treated rats. At the time rats on the HCB diet were
10
20 DAY
30
Fig. 1. Body weight changes hexachlorobenzene treated)
40
AFTER
(HCB)
50
FIRST
DOSE
60
70
OF HCB
in female Sprague-Dawley for 55 days.
Values
represent
rats fed a regular the mean
f
diet or a diet containing
S.E. of 6 (controls)
0.1%
or 9 (HCB-
rats.
returned to regular rat chow (day 55), excretion of urinary porphyrins was mildly elevated. In spite of cessation of dosing, excretion of urinary porphyrins in survivors of the HCB diet continued to increase and, after 4 weeks, was almost 100 times greater in treated rats than in controls (Table I). At the time of onset of increased porphyrin excretion in urine of HCB-treated rats (day 55), both serum Tq and T3 were significantly reduced (Table II). Serum thyroid hormones remained suppressed during 42 days of subsequent monitoring (Table II). A minor rebound effect appeared to take place between days 62 and 97 in terms of serum T4. At termination (day 97) both total cytochrome P-450 and cytochrome bs content were elevated in liver microsomes from HCB-treated rats compared to controls (Table III). The activity of ethoxyresorufin 0-deethylase (lo-fold), pentoxyresorufin 0-dealkylase (12-fold), aminopyrine N-demethylase (less than 2-fold) and UDP-glucuronosyl transferase (2-fold) were significantly induced in rats fed the HCB-containing diet. In contrast, the activity of liver microsomal NADPHTABLE
I
EXCRETION
OF TOTAL
FED A DIET CONTAINING Day after first dose of HCB
URINARY 0.1%
PORPHYRINS
Total
urinary
Controls
a Mean
f
porphyrins
SPRAGUE-DAWLEY
(HCB)
FOR 55 DAYS
&g/day) HCB
41
3.2 + 0.1”
4.4 f
55 62
3.0 f 0.3 2.9 + 0.5
11.6 + 37.9 +
91
1.5 rt 0.3
SE; n=6.
* Significantly
IN FEMALE
HEXACHLOROBENZENE
different
from controls
(P
120
0.9 1.7* 8.7*
* 21*
RATS
75
TABLE
11
SERUM
LEVELS
OF
SPRAGUE-DAWLEY
THYROXINE
(Td)
AND
TRIIODOTHYRONINE
RATS FED A DIET CONTAINING
0.1%
(Ts)
IN
FEMALE
HEXACHLOROBENZENE
(HCB)
FOR 55 DAYS Day after
first
T, (ng/dl)
T4 (Irg/dl)
dose of HCB Controls
HCB
Controls
HCB
55
3.8 + 0.2a
< 1.0
64.2 * 2.0
48.1 f
62
4.3 + 0.3
74.8 * 2.8
51.3 + 1.5*
4.1 * 0.3
1.5 f 0.3*
75.0 + 5.3
53.0 f 4.1*
97 a Mean
3.2%
& SE; n=6.
*Significantly
different
from controls
(P
cytochrome c reductase and benzo[a]pyrene hydroxylase was not altered by dietary HCB at termination of the experiment (day 97). DISCUSSION
This experiment confirms an earlier report of Ockner and Schmid [25], that, in TABLE LIVER
111 MICROSOMAL
ENZYME
DIET CONTAINING Microsomal
0.1%
INDUCTION
IN FEMALE
HEXACHLOROBENZENE
enzyme
SPRAGUE-DAWLEY
Enzyme
content/activitya
Controls Cytochrome (nmol/mg
P-450
(nmol/mg
1.01 +
0.09*
bs
0.44 + 0.04
0.69 *
0.02*
0.33 + 0.01
0.32 f 0.07
0.42 t 0.04
0.46 +
protein)
NADPH-cytochrome &mol/mg
c reductase
protein/min)
Benzo[a]pyrene (nmol/mg
hydroxylase
0.05
protein/min)
Ethoxyresorufin (pmol/mg
0deethylase
27.1
f 2.2
260
+ 57*
20
13
240
f 40*
protein/min)
Pentoxyresorufin (pmol/mg
0-dealkylase
protein/min)
Aminopyrine
N-demethylase
6.5
& 0.7
85.6
+ 5.4
10.1
& 0.1*
protein/min)
UDP-glucuronosyl transferase (I-naphthol) (nmol/mg protein/min) a Determined b Mean
HCB
0.70 + 0.05b
protein)
Cytochrome
(nmol/mg
RATS FED A
(HCB) FOR 55 DAYS
97 days after
first dose of HCB.
+ SE; n=6.
* Significantly
different
from controls
(P< 0.05).
161
k 24*
76
rats, the lethal effects of chronic HCB feeding (0.2% of diet for 4 weeks) are poorly correlated with disturbances of porphyrin metabolism. In the present study, we observed that non-survivors with a relative minor disturbance of porphyrin metabolism started wasting away 5 days after discontinuing the HCB diet, whereas survivors did not show any loss of body weight during the 42-day post-exposure period, even though they developed severe porphyria (Fig. 1 and Table I). These findings indicate that the mechanisms of HCB-induced mortality and porphyria are different. Induction of porphyria by HCB occurred as described in more detail by Koss et al. (261. Serum thyroid hormone levels were significantly reduced at the time of onset of porphyria regardless of the survival status of the rats (Table II). Both serum T4 and T3 levels remained suppressed during the 42-day period after cessation of the HCB diet without an apparent adverse effect on rat body weight (Fig. 1). Therefore, reduced serum T4 hormone levels may not necessarily be viewed as a sign of toxicity. However, decreased serum T4 has been shown to occur after exposure of rats to several chlorinated aromatic hydrocarbons that are capable of inducing porphyria [1,5,6,27-291. Based on available data, it is not possible to determine whether reduced serum thyroid hormone levels and porphyria are causally related. The activities of ethoxyresorufin 0-deethylase and pentoxyresorufin 0-dealkylase were extremely sensitive indicators of the effects of dietary exposure to HCB on rat liver microsomal cytochrome P-450. The induction of cytochrome P-450~ by HCB was apparent from a lo-fold induction of ethoxyresorufin 0-deethylase activity, although the activity of benzo[a]pyrene hydroxylase was unaffected by HCB treatment. The difference in the apparent inducibility of these enzyme activities presumably reflects the ability of cytochrome P-450 isozymes other than cytochrome P-450~ to hydroxylate benzo[a]pyrene, but not ethoxyresorufin [30]. The induction of cytochrome P-450b by HCB was apparent from a 1Zfold induction of pentoxyresorufin 0-dealkylase activity, as well as a modest increase in aminopyrine N-demethylase activity. It was shown recently that the dealkylation of pentoxyresorufin is preferentially catalyzed by cytochrome P-450b and is highly inducible by phenobarbital treatment [ 191. These data (Table III) corroborate results of recent immunochemical studies [3 l] indicating that HCB is both a phenobarbitaltype inducer of rat liver microsomal cytochrome P-450b and a 3-methylcholanthrene-type inducer of cytochrome P-450~. In conclusion, these data in conjunction with other experiments [8] suggest that correlations between microsomal enzyme induction and toxicity may be misleading and should not be used without understanding of the underlying mechanism of toxicity.
77
ACKNOWLEDGEMENT
A.P. gratefully acknowledges the financial support Flossie West Foundation and NIH grant ES 03765.
of the PMA, Speas and
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