The interactions of five dibenzofurans with the mitochondria from rat liver have been investigated. Results indicate that at low doses all dibenzofurans induce inhibition of ATP synthesis. The efficiency of ATP synthesis is measured from the ratio (R ) between the ADP-stimulated respiratory rate (State 3) and basal respiration (State 4). When R = 1, no ATP synthesis occurs. A comparison between the R values for all investigated dibenzofurans (PCDF) shows that the R values are in the same order of magnitude

A. Iero

G. Perin

M. Bragadin

R. Fabris

S. Manente

V. Rizzoli

Archivio Ricerca Ca'Foscari

Polish Journal of Environmental Studies Vol. 8, No. 3 (1999), 165-168 
 
A Study of the Toxic Effects of Six Dibenzofuranes in 
Mitochondria from Rat Liver 
S. Manente1, A. Iero1, R. Fabris1, G. Perin1, V. Rizzoli2, M. Bragadin1* 
1 Dipartimento di Scienze Ambientali, Univ. Venezia, DD2137 30123 Venezia, Italy 2 
Dipartimento di Chimica Biologica, Universita di Padova, Viale G. Colombo, 3 35121 Padova Italy 
Received 11 January, 1999 
Accepted 15 February, 1999 
Abstract 
The interactions of five dibenzofurans with the mitochondria from rat liver have been investigated. Results 
indicate that at low doses all dibenzofurans induce inhibition of ATP synthesis. The efficiency of ATP 
synthesis is measured from the ratio (R ) between the ADP-stimulated respiratory rate (State 3) and basal 
respiration (State 4). When R = 1, no ATP synthesis occurs. A comparison between the R values for all 
investigated dibenzofurans (PCDF) shows that the R values are in the same order of magnitude. 
Keywords: Dibenzofurans, mitochondria, toxicity. 
Introduction 
Polychlorinated dibenzo-p-dioxins (PCDD), dibenzofu-
rans (DF) and biphenils (PCB) are industrial compounds or 
by-products that have been identified as environmental 
contaminants. Its residues have been detected in fish, wild-
life and humans. Studies have been performed in animals 
to assess the toxic effects in whole organisms, and in tis-
sues, cells and subcellular structures to establish the mole-
cular mechanism or the mechanisms which are responsible 
for the toxic effects observed in whole animals. At the 
present time a considerable body of research establishes 
that in laboratory animals the Ah (aromatic hydrocarbon) 
receptor (AhR) mediated most toxic effects of halogenated 
aromatic hydrocarbons [1-4]. The toxicological pattern, 
however, in whole animals is very complicated and other 
action mechanisms responsible for acute toxicity, in addi-
tion to those alredy proposed, cannot be excluded. 
This paper studies the interactions of five DF with the 
mitochondria from rat liver. The interest of our research on 
the mitochondria is justified from the fact that mitochond-
ria are a possible target for those toxic compounds which 
induce acute toxicity since damage to the mitochondria 
which produce ATP for the cell gives rise to corresponding 
cell damage. Our results indicate that at low doses all DFs 
* Corresponding author. 
induce inhibition of ATP synthesis, thus explaining the 
acute toxicity in whole organisms as rats. A comparison 
with the doses necessary to induce toxic effects in humans 
is complicated since the effects of DFs on humans are not 
well characterized [4]. Different degradation rates are pos-
tulated to explain the different dose-toxicity relation-
ships observed in whole animals and presumably also in 
humans. 
Experimental Procedures 
Mitochondria were prepared from livers of fasted albino 
winstar rats weighing about 300 g. The livers were isolated 
and placed in ice-cold sucrose (0.25 M) solution containing 
Tris-Mops 10 mM pH 7.4 and EGTA 0.1 M (isolation 
medium). The livers were rinsed three times with ice-cold 
medium, cut into small pieces with scissors, and homo-
genized in a glass potter homogeniser equipped with a tef-
lon pestle and kept in an ice-bath, in a volume of 40 
ml/liver. Each liver homogenate was diluted with ice-cold 
medium to 200 ml and intact cells, nuclei and cellular 
debris were sedimented by 10 min centrifugation at 650xg 
in a Sorvall RC2B refrigerated centrifuge kept at 2°C (rotor 
GSA). The supernatant was carefully decanted and cent-
rifuged at 7700xg (rotor SS34) for 10 min. The supernatant 
was discarded and the mitochondrial pellet was carefully 
resuspended in ice-cold isolation medium and centrifuged 
166 Manente S. et al. 
 
 
Fig. 1. A typical experiment of mitochondrial respiration in va-
rious conditions (the respiratory rate is the slope of oxygen con-
centration against time): State 4 is basal respiration. In the presen-
ce of 100 µM ADP and Phosphate (Pi), the respiration is stimula-
ted (State 3). When all ADP is consumed and ATP is synthetized, 
the system returns to State 4. In this condition, the respiratory rate 
can be stimulated adding an uncoupler (FCCP) is added. Medium 
composition: sucrose 0.25 M, Hepes pH 7.4 10 mM, succinate 
2 mM, acetate 10 mM. Mitochondria 1 mg/ml. 
as above. The resulting mitochondrial pellet was resuspen-
ded in 0.25 M sucrose containing 10 mM Tris-Mops, pH 
7.4 at approximately 200 mg protein/ml and stored in an 
ice-bath until use. Mitochondrial proteins were measured 
using Lowry's method [5]. 
Mitochondrial oxygen consumption was measured with 
a Clark oxygen electrode (Yellow Springs Instruments, 
OH, U.S.A.) fitted in a thermostated, closed chamber equ-
ipped with magnetic stirring. 
All chemicals were of the higest purity commercially 
available. 
Dibenzofurans were a gift from dr. A. Orio. 
FCCP (Carbonyl Cyanide p-Trifluoromethoxyphenyl-
hydrazone) was furnished by Sigma. 
Results 
In respiring mitochondria, State 4 is the rate of basal 
respiration (Fig. 1) (the respiratory rate or respiration is the 
slope of oxygen concentration against time). State 3 is the 
respiratory rate when ADP and Pi are added: when ADP 
and Pi are added, a stimulation in respiratory rate occurs 
since ATP is synthetized. When all ADP have reacted, the 
respiratory rate returns in State 4. If in this condition FCCP 
(a potent uncoupler of oxidative phosphorylation) is added, 
the respiratory rate is stimulated up to the maximal value. 
 
Fig. 2. Respiratory rates of mitochondria in the presence of vary-
ing amounts of 2,3,7,8 DF in State 4 (•), State 3 (x) and by 
FCCP-stimulated respiration (o). In the upper side the R values at 
any DF concentration are reported. Medium and conditions are 
those indicated in Fig. 1. 
Fig. 3. Respiratory rates of mitochondria in the presence of vary-
ing amounts of 1,2,3,4,7,8,9 DF. Medium and conditions as in 
Figs. 1 and 2. 
A Study of the Toxic Effects ... 167 
 
The literature reports that in well coupled mitochondria, 
the ratio between State 3 and State 4 respiratory rate (R ) is 
about 5 [6], while when R = 1 no ATP synthesis occurs. 
On the basis of these arguments, we have examined the 
interactions of five DF with the mitochondria. As Fig. 
2 shows, when the mitochondria are incubated in the pre-
sence of increasing amounts of 2,3,7,8 DF, a significantive 
increase of State 4 occurs, while State 3 is not substantially 
modified. As the concentration of 2,3,7,8 DF rises, R value 
decreases (upper side of Fig. 1). At about 60 ppb DF, 
R= 1. In this condition, no ATP synthesis occurs. In the 
figure, the reducing substrate is succinate. The figure also 
shows that to obtain a complete inhibition of the respiratory 
chain (FCCP stimulated), the DF dose has to be higher than 
60 ppb. This data indicate that the prevailing (more toxic) 
effect of 2,3,7,8 DF is not an inhibitory effect on the re-
spiratory chain carriers (carriers responsible for the trans-
port of ATP, ADP, Pi or electron carriers as the cytochro-
mes), but an increased State 4 respiratory rate. This effect, 
as discussed below, has been analyzed in a previous paper 
[7]. 
The experiments of Fig. 2 have been performed by suc-
cinate as substrate. If glutamate/mahte as reducing sub-
strates are utilized, the same results about the R values are 
obtained (not shown), but the inhibition of the FCCP-sti-
mulated respiratory rate occurs at higher doses, thus in-
dicating that the first site of the respiratory chain is not the 
prevailing target of 2,3,7,8 DF. Since the effective toxic 
effect is the effect with the lowest dose, this aspect has not 
been further analyzed. 
The experiments as in Figs. 1 and 2 have been 
performed with other four DFs: 1,2,3,4,7,8,9 DF, 
1,2,3,4,7,8 DF, 2,3,4,7,8 DF and 2,3,4,6,7,8 DF. Figs. 3-6 
report the interactions of the various PCDFs with the 
respiratory states. The corresponding R values are reported 
in the upper side of each figure. 
Discussion 
Results indicate that all DFs inhibit ATP synthesis. This 
effect occurs at doses lower than that necessary to inhibit 
the maximal respiratory rate, thus indicating that the preva-
iling effect on mitochondria is not the inhibition of the 
respiratory chain. In this regard, the effect on State 4 is 
similar to an uncoupling effect, but all DF do not possess 
any acid-base group which is typical of uncouplers. As 
suggested in a previous paper [7], we suggest therefore that 
the enhancement in the respiratory rate is a detergent ef-
fect. This behaviour could explain many of the different 
hystopathological behaviours observed in exposed animals 
such as progressive weight loss and general debilitation and 
the very extended hystopathological pattern: if low doses 
of DF cause membrane leaks, this behaviour is not peculiar 
only to mitochondrial membranes, but a characteristic of 
all membranes, inducing an effect which is similar to an 
aging mechanism. 
Similar behaviours have also been observed with PCB 
compounds [8]. 
Furthermore, data indicate that the doses of DF neces-
sary to inhibit ATP synthesis are all included in the same 
 
 
Fig. 4. Respiratory rates of mitochondria in the presence of vary-
ing amounts of 1,2,3,4,7,8 DF. Medium and conditions as in Figs. 
1 and 2. 
Fig. 5. Respiratory rates of mitochondria in the presence of vary-
ing amounts of 2,3,4,7,8 DF. Medium and conditions as in Figs. 
1 and 2. 
168 Manente S. et al. 
 
Fig. 6. Respiratory rates of mitochondria in the presence of vary-
ing amounts of 2,3,4,6,7,8 DF. Medium and conditions as in 
Figs. 1 and 2. 
order of magnitude. Comparisons with the doses necessary 
to obtain toxic effects in whole animals, however, are com-
plicated. As suggested by many authors, in humans, the 
responses dose-effect and the body burdens associated with 
such effects requires more research [1,3, 4]. Therefore, the 
proposal which establishes that the toxicity is due to a bin-
ding to Ah receptors may not be the only mechanism re-
sponsible for toxicity. Therefore, we propose that DFs 
could contribute to the whole acute toxicity. This hypo- 
thesis is supported by the fact that their effect is a memb-
rane permeability enhancement effect [7] since all DFs are 
membrane-soluble and all membranes show the same cha-
racteristics. A possible discrepancy between "in vitro" and 
"in vivo" experiments could be explained, postulating dif-
ferents degradation rates for the various DFs. By this mo-
del, the major toxicity observed "in vivo" with some DFs is 
due to their high persistence in the cell, while the low 
toxicity observed in animals treated with some DFs could 
be due to a fast degradation of the parent compounds. This 
different behaviour toward degradation has recently been 
observed in microorganisms [2]. 
References 
1. DE VITO M.J., BIRNBAUM L.S. Dioxins: model chemicals 
for assessing receptor-mediated toxicity.  Toxicology.   102, 
115, 1995. 
2. TAKADA S. NAKAMURA M, MATSUEDA T., KONDO 
R., SAKAI K. Degradation of polychlorinated dibenzo-p-di- 
oxins and polychlorinated dibenzofurans by the whiteot fun 
gus Phanerochaete  sordida.  Appl.  Environ.  Microbiol.  62, 
4323, 1996. 
3. VAN DEN BERG M, DE LONGHI J., POIGER H., OLSON 
G.R. The toxicocinetics and methabolism of polychlorinated 
dibenzo-p-dioxins (PCCDs) and dibenzofurans (PCDFs) and 
their relevance for toxicity. Crit. Rev. Toxicol. 24, 1, 1994. 
4. VANDEN-HEUVEL J.P., LUCIER G. Environmental toxico 
logy of polychlorinated dibenzo-p-dioxins and polychlorinated 
dibenzofurans. Environ. Health Perspect. 100, 189, 1993. 
5. LOWRY OH., Rosenbrough N.J., Farr D.L. Randall R.J. Pro 
tein measurement with the folin phenol reagent. J. Biol. Chem. 
193, 265, 1951. 
6. SHANNON R.D., BOARDMANN G.D., DIETRICH A.M. 
Mitochondrial responses to chlorophenols as a short-term toxi 
city assay. Environ. Toxicol. Chem. 10, 57, 1991. 
7. BRAGADIN M., PERIN G., MANENTE S., RACCANELLI 
S. Mitochondrial permeability to ions induced by dibenzodi- 
oxines and dibenzofurans. A simple method to measure ion 
permeability in membranes. Polish J. Environ. Studies 6, 35, 
1997. 
8. NISHIHARA Y. Effects of polychlorinated biphenyls (Kane- 
chlor-400) on isolated rat liver mitochondria. Arch. Environ. 
Contam. Toxicol. 12, 517, 1984. 


A study of the toxic effects of six dibenzofuranes in mitochondria from rat liver

Archivio Istituzionale della Ricerca

MANENTE, Sabrina

PERIN, Guido

BRAGADIN, Marcantonio

Archivio istituzionale della ricerca - Università degli Studi di Venezia Ca' Foscari

Polish Journal of Environmental Studies Vol. 8, No. 3 (1999), 165-168  A Study of the Toxic Effects of Six Dibenzofuranes in Mitochondria from Rat Liver S. Manente1, A. Iero1, R. Fabris1, G. Perin1, V. Rizzoli2, M. Bragadin1* 1 Dipartimento di Scienze Ambientali, Univ. Venezia, DD2137 30123 Venezia, Italy 2 Dipartimento di Chimica Biologica, Universita di Padova, Viale G. Colombo, 3 35121 Padova Italy Received 11 January, 1999 Accepted 15 February, 1999 Abstract The interactions of five dibenzofurans with the mitochondria from rat liver have been investigated. Results indicate that at low doses all dibenzofurans induce inhibition of ATP synthesis. The efficiency of ATP synthesis is measured from the ratio (R ) between the ADP-stimulated respiratory rate (State 3) and basal respiration (State 4). When R = 1, no ATP synthesis occurs. A comparison between the R values for all investigated dibenzofurans (PCDF) shows that the R values are in the same order of magnitude. Keywords: Dibenzofurans, mitochondria, toxicity. Introduction Polychlorinated dibenzo-p-dioxins (PCDD), dibenzofu-rans (DF) and biphenils (PCB) are industrial compounds or by-products that have been identified as environmental contaminants. Its residues have been detected in fish, wild-life and humans. Studies have been performed in animals to assess the toxic effects in whole organisms, and in tis-sues, cells and subcellular structures to establish the mole-cular mechanism or the mechanisms which are responsible for the toxic effects observed in whole animals. At the present time a considerable body of research establishes that in laboratory animals the Ah (aromatic hydrocarbon) receptor (AhR) mediated most toxic effects of halogenated aromatic hydrocarbons [1-4]. The toxicological pattern, however, in whole animals is very complicated and other action mechanisms responsible for acute toxicity, in addi-tion to those alredy proposed, cannot be excluded. This paper studies the interactions of five DF with the mitochondria from rat liver. The interest of our research on the mitochondria is justified from the fact that mitochond-ria are a possible target for those toxic compounds which induce acute toxicity since damage to the mitochondria which produce ATP for the cell gives rise to corresponding cell damage. Our results indicate that at low doses all DFs * Corresponding author. induce inhibition of ATP synthesis, thus explaining the acute toxicity in whole organisms as rats. A comparison with the doses necessary to induce toxic effects in humans is complicated since the effects of DFs on humans are not well characterized [4]. Different degradation rates are pos-tulated to explain the different dose-toxicity relation-ships observed in whole animals and presumably also in humans. Experimental Procedures Mitochondria were prepared from livers of fasted albino winstar rats weighing about 300 g. The livers were isolated and placed in ice-cold sucrose (0.25 M) solution containing Tris-Mops 10 mM pH 7.4 and EGTA 0.1 M (isolation medium). The livers were rinsed three times with ice-cold medium, cut into small pieces with scissors, and homo-genized in a glass potter homogeniser equipped with a tef-lon pestle and kept in an ice-bath, in a volume of 40 ml/liver. Each liver homogenate was diluted with ice-cold medium to 200 ml and intact cells, nuclei and cellular debris were sedimented by 10 min centrifugation at 650xg in a Sorvall RC2B refrigerated centrifuge kept at 2°C (rotor GSA). The supernatant was carefully decanted and cent-rifuged at 7700xg (rotor SS34) for 10 min. The supernatant was discarded and the mitochondrial pellet was carefully resuspended in ice-cold isolation medium and centrifuged 166 Manente S. et al.   Fig. 1. A typical experiment of mitochondrial respiration in va-rious conditions (the respiratory rate is the slope of oxygen con-centration against time): State 4 is basal respiration. In the presen-ce of 100 µM ADP and Phosphate (Pi), the respiration is stimula-ted (State 3). When all ADP is consumed and ATP is synthetized, the system returns to State 4. In this condition, the respiratory rate can be stimulated adding an uncoupler (FCCP) is added. Medium composition: sucrose 0.25 M, Hepes pH 7.4 10 mM, succinate 2 mM, acetate 10 mM. Mitochondria 1 mg/ml. as above. The resulting mitochondrial pellet was resuspen-ded in 0.25 M sucrose containing 10 mM Tris-Mops, pH 7.4 at approximately 200 mg protein/ml and stored in an ice-bath until use. Mitochondrial proteins were measured using Lowry's method [5]. Mitochondrial oxygen consumption was measured with a Clark oxygen electrode (Yellow Springs Instruments, OH, U.S.A.) fitted in a thermostated, closed chamber equ-ipped with magnetic stirring. All chemicals were of the higest purity commercially available. Dibenzofurans were a gift from dr. A. Orio. FCCP (Carbonyl Cyanide p-Trifluoromethoxyphenyl-hydrazone) was furnished by Sigma. Results In respiring mitochondria, State 4 is the rate of basal respiration (Fig. 1) (the respiratory rate or respiration is the slope of oxygen concentration against time). State 3 is the respiratory rate when ADP and Pi are added: when ADP and Pi are added, a stimulation in respiratory rate occurs since ATP is synthetized. When all ADP have reacted, the respiratory rate returns in State 4. If in this condition FCCP (a potent uncoupler of oxidative phosphorylation) is added, the respiratory rate is stimulated up to the maximal value.  Fig. 2. Respiratory rates of mitochondria in the presence of vary-ing amounts of 2,3,7,8 DF in State 4 (•), State 3 (x) and by FCCP-stimulated respiration (o). In the upper side the R values at any DF concentration are reported. Medium and conditions are those indicated in Fig. 1. Fig. 3. Respiratory rates of mitochondria in the presence of vary-ing amounts of 1,2,3,4,7,8,9 DF. Medium and conditions as in Figs. 1 and 2. A Study of the Toxic Effects ... 167  The literature reports that in well coupled mitochondria, the ratio between State 3 and State 4 respiratory rate (R ) is about 5 [6], while when R = 1 no ATP synthesis occurs. On the basis of these arguments, we have examined the interactions of five DF with the mitochondria. As Fig. 2 shows, when the mitochondria are incubated in the pre-sence of increasing amounts of 2,3,7,8 DF, a significantive increase of State 4 occurs, while State 3 is not substantially modified. As the concentration of 2,3,7,8 DF rises, R value decreases (upper side of Fig. 1). At about 60 ppb DF, R= 1. In this condition, no ATP synthesis occurs. In the figure, the reducing substrate is succinate. The figure also shows that to obtain a complete inhibition of the respiratory chain (FCCP stimulated), the DF dose has to be higher than 60 ppb. This data indicate that the prevailing (more toxic) effect of 2,3,7,8 DF is not an inhibitory effect on the re-spiratory chain carriers (carriers responsible for the trans-port of ATP, ADP, Pi or electron carriers as the cytochro-mes), but an increased State 4 respiratory rate. This effect, as discussed below, has been analyzed in a previous paper [7]. The experiments of Fig. 2 have been performed by suc-cinate as substrate. If glutamate/mahte as reducing sub-strates are utilized, the same results about the R values are obtained (not shown), but the inhibition of the FCCP-sti-mulated respiratory rate occurs at higher doses, thus in-dicating that the first site of the respiratory chain is not the prevailing target of 2,3,7,8 DF. Since the effective toxic effect is the effect with the lowest dose, this aspect has not been further analyzed. The experiments as in Figs. 1 and 2 have been performed with other four DFs: 1,2,3,4,7,8,9 DF, 1,2,3,4,7,8 DF, 2,3,4,7,8 DF and 2,3,4,6,7,8 DF. Figs. 3-6 report the interactions of the various PCDFs with the respiratory states. The corresponding R values are reported in the upper side of each figure. Discussion Results indicate that all DFs inhibit ATP synthesis. This effect occurs at doses lower than that necessary to inhibit the maximal respiratory rate, thus indicating that the preva-iling effect on mitochondria is not the inhibition of the respiratory chain. In this regard, the effect on State 4 is similar to an uncoupling effect, but all DF do not possess any acid-base group which is typical of uncouplers. As suggested in a previous paper [7], we suggest therefore that the enhancement in the respiratory rate is a detergent ef-fect. This behaviour could explain many of the different hystopathological behaviours observed in exposed animals such as progressive weight loss and general debilitation and the very extended hystopathological pattern: if low doses of DF cause membrane leaks, this behaviour is not peculiar only to mitochondrial membranes, but a characteristic of all membranes, inducing an effect which is similar to an aging mechanism. Similar behaviours have also been observed with PCB compounds [8]. Furthermore, data indicate that the doses of DF neces-sary to inhibit ATP synthesis are all included in the same   Fig. 4. Respiratory rates of mitochondria in the presence of vary-ing amounts of 1,2,3,4,7,8 DF. Medium and conditions as in Figs. 1 and 2. Fig. 5. Respiratory rates of mitochondria in the presence of vary-ing amounts of 2,3,4,7,8 DF. Medium and conditions as in Figs. 1 and 2. 168 Manente S. et al.  Fig. 6. Respiratory rates of mitochondria in the presence of vary-ing amounts of 2,3,4,6,7,8 DF. Medium and conditions as in Figs. 1 and 2. order of magnitude. Comparisons with the doses necessary to obtain toxic effects in whole animals, however, are com-plicated. As suggested by many authors, in humans, the responses dose-effect and the body burdens associated with such effects requires more research [1,3, 4]. Therefore, the proposal which establishes that the toxicity is due to a bin-ding to Ah receptors may not be the only mechanism re-sponsible for toxicity. Therefore, we propose that DFs could contribute to the whole acute toxicity. This hypo- thesis is supported by the fact that their effect is a memb-rane permeability enhancement effect [7] since all DFs are membrane-soluble and all membranes show the same cha-racteristics. A possible discrepancy between "in vitro" and "in vivo" experiments could be explained, postulating dif-ferents degradation rates for the various DFs. By this mo-del, the major toxicity observed "in vivo" with some DFs is due to their high persistence in the cell, while the low toxicity observed in animals treated with some DFs could be due to a fast degradation of the parent compounds. This different behaviour toward degradation has recently been observed in microorganisms [2]. References 1. DE VITO M.J., BIRNBAUM L.S. Dioxins: model chemicals for assessing receptor-mediated toxicity.  Toxicology.   102, 115, 1995. 2. TAKADA S. NAKAMURA M, MATSUEDA T., KONDO R., SAKAI K. Degradation of polychlorinated dibenzo-p-di- oxins and polychlorinated dibenzofurans by the whiteot fun gus Phanerochaete  sordida.  Appl.  Environ.  Microbiol.  62, 4323, 1996. 3. VAN DEN BERG M, DE LONGHI J., POIGER H., OLSON G.R. The toxicocinetics and methabolism of polychlorinated dibenzo-p-dioxins (PCCDs) and dibenzofurans (PCDFs) and their relevance for toxicity. Crit. Rev. Toxicol. 24, 1, 1994. 4. VANDEN-HEUVEL J.P., LUCIER G. Environmental toxico logy of polychlorinated dibenzo-p-dioxins and polychlorinated dibenzofurans. Environ. Health Perspect. 100, 189, 1993. 5. LOWRY OH., Rosenbrough N.J., Farr D.L. Randall R.J. Pro tein measurement with the folin phenol reagent. J. Biol. Chem. 193, 265, 1951. 6. SHANNON R.D., BOARDMANN G.D., DIETRICH A.M. Mitochondrial responses to chlorophenols as a short-term toxi city assay. Environ. Toxicol. Chem. 10, 57, 1991. 7. BRAGADIN M., PERIN G., MANENTE S., RACCANELLI S. Mitochondrial permeability to ions induced by dibenzodi- oxines and dibenzofurans. A simple method to measure ion permeability in membranes. Polish J. Environ. Studies 6, 35, 1997. 8. NISHIHARA Y. Effects of polychlorinated biphenyls (Kane- chlor-400) on isolated rat liver mitochondria. Arch. Environ. Contam. Toxicol. 12, 517, 1984. 

The interactions of five dibenzofurans with the mitochondria from rat liver have been investigated. Results indicate that at low doses all dibenzofurans induce inhibition of ATP synthesis. The efficiency of ATP synthesis is measured from the ratio (R) between the ADP-stimulated respiratory rate (State 3) and basal respiration (State 4). When R = 1, no ATP synthesis occurs. A comparison between the R values for all investigated dibenzofurans (PCDF) shows that the R values are in the same order of magnitude

A study of the toxic effects of six dibenzofuranes in mitochondria from rat liver

Abstract

Similar works

Full text

Available Versions

Archivio Ricerca Ca'Foscari

Archivio Istituzionale della Ricerca

Archivio istituzionale della ricerca - Università degli Studi di Venezia Ca' Foscari

CiteSeerX