Use of the Comet assay to assess DNA damage in hemocytes and digestive gland cells of mussels and clams exposed to water contaminated with petroleum hydrocarbons.

Oil spills can result in the deposition of large quantities of petroleum hydrocarbons into intertidal and shallow waters seriously impacting bivalve populations. Petroleum hydrocarbons are enriched in polycyclic aromatic hydrocarbons (PAH) and PAH analogs many of which may have potential to damage DNA. The Comet assay is useful for assessing DNA damage and has been used to a limited degree with aquatic organisms, but mostly with studies in vitro. We have carried out studies with the Comet assay to assess the DNA damaging potential of complex mixtures of petroleum hydrocarbons for bivalves. Experiments were carried out with mussels (Mytilus edulis) and clams (Mya arenaria) with dispersions and water soluble fractions of an Arabian crude oil which was also chemically characterized in detail by GC-MS. Pilot studies were first conducted to evaluate test performance and reproducibility. An interindividual coefficient of variation ranging from 17 to 30% was established for the assay with hemocytes and digestive gland cells of both species. Exposure to hydrocarbon fractions had no significant impact on clams. However, an increase in DNA damage was observed at P < 0.1 with digestive gland cells of mussels exposed to aqueous fractions of a light crude oil. These studies have demonstrated a potential for DNA damage in bivalves exposed to oil spills in inshore waters as well as potential for interspecies sensitivity.

Are metal mining effluent regulations adequate: identification of a novel bleached fish syndrome in association with iron-ore mining effluents in Labrador, Newfoundland.

Water quality guidelines for industrial effluents are in place in many countries but they have generally evolved within a limited ecotoxicological framework. Effluents from iron-ore mines have traditionally been viewed by regulatory bodies as posing little or no risk to the aquatic environment. However, it was recently reported that lake trout taken from a large iron-ore contaminated Lake in Labrador (Wabush Lake) had elevated levels of DNA oxidative damage and were markedly depleted in levels of vitamin A (Payne et al., 1998) in comparison with fish from a Lake (Shabogamo Lake) receiving lesser levels of effluents. Through further observations, it has now been established that the lake trout in Wabush Lake are commonly affected with a marked skin bleaching syndrome in comparison with fish in Shabogamo Lake and a nearby Lake (Ashuanipi) which does not receive effluents. To the authors' knowledge such a syndrome which is characterized by marked reduction in skin pigmentation and overall increase in skin whitening has not been reported before in any fish population in association with contamination. Preliminary information for liver histopathological and blood cell differences have also been obtained in fish in Wabush Lake in comparison with Ashuanipi Lake. It has also been observed through studies on phosphatidyl liposomes that iron-ore leachate contains redox-active material (iron but possibly other transition metals) that has considerable potential for causing oxidative damage to cellular constituents. Using the weight of evidence approach it is indicated that iron-ore effluents may pose more of a risk to the aquatic environment than traditionally considered by regulatory agencies.

Iron ore mines leachate potential for oxyradical production.

The ecotoxicological effects of mining effluents is coming under much greater scrutiny. It appears necessary to explore possible health effects in association with iron ore mining effluents. The present results clearly demonstrate that iron-ore leachate is not an inert media but has the potential to induce lipid peroxidation. Peroxidation was assessed by measuring oxygen consumption in the presence of a reducing agent such as ascorbate or NADPH and a chelator such as EDTA. Labrador iron ore is an insoluble complex crystalline material containing a mixture of metals (Fe, Al, Ti, Mn, Mg,ellipsis, ) in contrast to the iron sources used for normal lipid peroxidation studies. The metal of highest percentage is iron (59. 58%), a metal known to induce oxyradical production. Iron ore powder initiated ascorbic acid-dependent lipid peroxidation (nonenzymatic) in liposomes, lipids extracted from rat and salmon liver microsomes, and intact salmon liver microsomes. It also revealed an inhibitory effect of NADPH-dependent microsomes lipid peroxidation as well as on NADPH cytochrome c reductase activity. However, nonenzymatic peroxidation in rat liver microsomes was not significantly inhibited. Cytochrome P450 IA1- and IIB1-dependent enzymatic activities as well as P450 levels were not affected. The inhibition could be due to one of the other components of iron ore leachate (Mn, Al,ellipsis, ). These effects of iron-ore leachate indicate that a potential toxicity could be associated with its release into lakes. Further studies are necessary to explore in vivo effects on aquatic animals.

Effect of cytochrome P450 induction on the metabolism and toxicity of ochratoxin A.

Liver microsomes from rats treated with various P450 inducers were examined for their ability to metabolize the mycotoxin ochratoxin A (OTA) to 4(R)-4-hydroxyochratoxin A (4R), the major metabolite, and 4(S)-4-hydroxyochratoxin A (4S), the minor metabolite. Pretreatment of rats with phenobarbital (PB), dexamethasone (DXM), 3-methylcolcanthrene (3MC) and isosafrole (ISF) greatly induced 4R formation. PB, DXM, 3MC, clofibrate (CLF) and ISF treatments also induced 4S formation. Isoniazid (INH) pretreatment primarily induced 4S formation. The pH optimum for 4R formation was found to be 6.0 with 3MC microsomes, and 6.5 with PB and DXM microsomes. For 4S formation, the pH optimum was 7.0. At the optimum pH (compared with pH 7.4), 4R formation increased 40-50% with PB and DXM microsomes but 8.0-fold with 3MC microsomes. Studies using the inhibitors metyrapone and alpha-naphthoflavone as well as monoclonal antibodies against various P450s suggested that at least the P450 isoforms IA1/IA2, IIB1 and IIIA1/IIIA2 are involved in 4R formation. Using urinary excretion of the enzymes alkaline phosphatase and gamma-glutamyl transferase as an index of renal damage, we observed that pretreatment of rats with PB, which induced hepatic P450 (P450II2B1), protected against OTA nephrotoxicity, whereas cobalt-protoporphyrin IX pretreatment, which decreased P450 levels, exacerbated OTA nephrotoxicity. Our results suggest that at least P450IIB1-dependent metabolism of OTA leads to its detoxication and that OTA itself may be toxic in some circumstances or that other pathways are responsible for its activation.

Stimulatory effects of sulfur and nitrogen oxides on carcinogen activation in human polymorphonuclear leukocytes.

The occurrence of inflammatory processes and of cancer in the human respiratory tract is intimately associated. One of the major factors in this is probably the recruitment of and stimulated activity of polymorphonuclear leukocytes (PML) in conjunction with the ability of these cells to convert various carcinogens to their ultimate active metabolites. In this study, we demonstrate that nitrite and sulfite, the major dissolution products of the environmental pollutants nitrogen dioxide and sulfur dioxide in water enhance the metabolic activation of trans-7,8-dihydroxy-7,8-dihydrobenzo[a]pyrene (BP-7,8-dihydrodiol), the proximal carcinogen of benzo[a]pyrene, to trans-7,8-dihydroxy-9,10-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene (BPDE) and tetraols, the corresponding hydrolysis products, in human PML prestimulated with 12-O-tetradecanoylphorbol-13-acetate. Nitrite was more efficient than sulfite in stimulating the formation of reactive intermediates of BP-7,8-dihydrodiol in PML that covalently bind to extracellular DNA and, in particular, to intracellular proteins. The mechanism by which sulfite stimulates the metabolism of BP-7,8-dihydrodiol most probably involves the intermediate formation of a sulfur trioxide radical anion (SO3.-) the subsequent formation of the corresponding sulfur peroxyl radical anion (.OOSO3-) in the presence of oxygen. The mechanism underlying the stimulatory action of nitrite is less clear but the major pathway seems to involve myeloperoxidase. These results offer an explanation for the increased incidence of lung cancer in cigarette smokers living in urban areas. The major glutathione transferase (GST) isoenzyme in human PML is GST P1-1, a Pi-class form. The GST activity of PML was found to be inversely correlated with the extent of binding of BP-7,8-dihydrodiol products to exogenous DNA. These results suggest that individuals exhibiting high GST-activity in the PML may be better protected against the type of carcinogenic dealt with in this study.

Possible role of an iron-oxygen complex in 4(S)-4-hydroxyochratoxin a formation by rat liver microsomes.

Rat liver microsomes were examined for their ability to oxidize the mycotoxin ochratoxin A (OTA) to 4(R)-4-hydroxyochratoxin A [(R)-4-OH-OTA] and 4(S)-4-hydroxyochratoxin A [(S)-4-OH-OTA] and to induce OTA-dependent lipid peroxidation. Microsomes isolated from rats pretreated with pregnenolone-16 alpha-carbonitrile greatly induced both (R)-4-OH-OTA and (S)-4-OH-OTA formation whereas isoniazid pretreatment primarily induced (S)-4-OH-OTA. (R)-4-OH-OTA and (S)-4-OH-OTA formation showed significant differences with respect to pH optima, effect of antioxidants, and iron chelators. (R)-4-OH-OTA showed a pH optimum of 6.5 and was not inhibited by the antioxidants butylated hydroxyanisole or N,N-diphenyl-1,4-phenylenediamine or the iron chelators. Desferal or bathophenanthrolinedisulfonic acid. In contrast, both (S)-4-OH-OTA and lipid peroxidation showed a pH optimum of 7.0 and both activities were sensitive to inhibition by the above antioxidants and iron chelators. Lipid peroxidation was not involved in (S)-4-OH-OTA formation since addition of linoleic acid hydroperoxide to microsomes did not give rise to (S)-4-OH-OTA. Cytochrome P450 appeared to be essential since other hemoproteins like horseradish peroxidase and hemoglobin were ineffective in metabolizing OTA in the presence of hydroperoxides. The results suggest that (R)-4-OH-OTA is formed by normal mixed-function oxidation but that (S)-4-OH-OTA formation may involve free iron. It is likely that an active Fe2(+)-oxygen complex, formed via NADPH-cytochrome P450 reductase and cytochrome P450-dependent reduction of free Fe3+ followed by oxygen binding, serves as the species inducing lipid peroxidation and at least part of (S)-4-OH-OTA formation.

Alterations in ATP-dependent calcium uptake by rat renal cortex microsomes following ochratoxin A administration in vivo or addition in vitro.

A disruption of calcium homeostasis, leading to a sustained increase in cytosolic calcium levels, has been associated with cytotoxicity in response to a variety of agents in different cell types. We have observed that administration of a single high dose or multiple lower doses of the carcinogenic nephrotoxin ochratoxin A (OTA) to rats resulted in an increase of the renal cortex endoplasmic reticulum ATP-dependent calcium pump activity. The increase was very rapid, being evident within 10 min of OTA administration and remained elevated for at least 6 hr thereafter. The increase in calcium pump activity was inconsistent with previous observations that OTA enhances lipid peroxidation (ethane exhalation) in vivo, a condition known to inhibit the calcium pump. However, no evidence of enhanced lipid peroxidation was observed in the renal cortex since levels of malondialdehyde and a variety of antioxidant enzymes including catalase, DT-diaphorase, superoxide dismutase, glutathione peroxidase, glutathione reductase and glutathione S-transferase were either unaltered or reduced. In in vitro studies, addition of OTA to cortex microsomes during calcium uptake inhibited the uptake process although the effect was reversible. Preincubation of microsomes with NADPH had a profound inhibitory effect on calcium uptake but inclusion of OTA was able to reverse the inhibition. Changes in the rates of microsomal calcium uptake correlated with changes in the steady-state levels of the phosphorylated Mg2+/Ca(2+)-ATPase intermediate, suggesting that in vivo/in vitro conditions were affecting the rate of enzyme phosphorylation.

Role of cytochrome P-450 in ochratoxin A-stimulated lipid peroxidation.

The role of cytochrome P-450 in the stimulation of lipid peroxidation by the nephrotoxic mycotoxin ochratoxin A has been investigated. Ochratoxin A was previously shown to markedly stimulate lipid peroxidation in a reconstituted system consisting of phospholipid vesicles, NADPH-cytochrome P-450 reductase, Fe3+, ethylenediaminetetraacetic acid (EDTA), and reduced nicotinamide adenine dinucleotide phosphate (NADPH). We now show that purified cytochrome P-450IIB1 could effectively replace EDTA in stimulating lipid peroxidation suggesting that it could mediate the transfer of electrons from NADPH to Fe3+. Cobalt protoporphyrin is known to cause an extensive and long-lasting depletion of hepatic cytochrome P-450 in rats, and it has been used to evaluate the role of hepatic cytochrome P-450 in xenobiotic metabolism and toxicity. We have observed that microsomes isolated from livers of cobalt protoporphyrin-pretreated rats underwent ochratoxin A-dependent lipid peroxidation much more slowly than control microsomes. Also, the level of ethane exhaled (an index of in vivo lipid peroxidation) on ochratoxin A administration was much lower in cobalt protoporphyrin-pretreated rats than in control rats. Taken together, these results provide evidence for the stimulatory role of cytochrome P-450 in ochratoxin A-induced lipid peroxidation in a reconstituted system and strongly implicate its role in microsomal and in vivo ochratoxin A-induced lipid peroxidation.

In vitro inhibition of rat platelet aggregation by ochratoxin A.

The mycotoxin ochratoxin A (OA) consists of 5-chloro-3-methyl-3,4-dihydro-8-hydroxyisocoumarin moiety linked by an amide bond to beta-L-phenylalanine. When added to washed rat platelets in vitro, OA caused a dose-dependent inhibition of aggregation induced by agonists such as adenosine diphosphate (ADP) or thrombin. The aggregatory response induced by prior addition of an agonist was also reversed in a dose-dependent manner by OA. Inhibition of aggregation appeared to be irreversible since exposure of platelets to OA followed by several washings removed most of the mycotoxin associated with the platelets but did not diminish the inhibitory response. Serotonin secretion from dense granules and arachidonic acid release from membrane phospholipid (especially phosphatidylcholine) as well as its further metabolism were also inhibited by OA. These results suggest that a disruption of the platelet plasma membrane structure by OA is probably responsible for inhibition of the primary and secondary phases of aggregation.

Alterations in calcium homeostasis as a possible cause of ochratoxin A nephrotoxicity.

Disruption of calcium homeostasis, leading to a sustained increase in cytosolic calcium level, has been associated with cytotoxicity in response to a variety of agents in different cell types. We have observed that a single high dose or multiple lower doses of ochratoxin A administered to rats resulted in an increase in renal endoplasmic reticulum calcium pump activity. The increase was very rapid, being evident within 10 min of ochratoxin A administration and remained elevated for at least 6 h thereafter. Ochratoxin A also decreased renal mitochondrial state-3 respiration and calcium uptake. The latter may lead to an increase in cytosolic calcium level, and the increase in microsomal calcium uptake activity may be an attempt to restore calcium homeostasis. Repeated moderate doses of ochratoxin A led to an eventual decrease in microsomal calcium pump activity, and this could lead to even higher cytosolic calcium levels. Changes in the rate of microsomal calcium uptake correlated with changes in the steady-state levels of the phosphorylated Mg2+/Ca(2+)-ATPase intermediate, indicating that this enzyme is responsible for the calcium pump activity.

NADPH-cytochrome-P-450 reductase promoted hydroxyl radical production by the iron(III)-ochratoxin A complex.

The Fe3+ complex of ochratoxin A has been shown to produce hydroxyl radicals in the presence of NADPH and NADPH-cytochrome-P-450 reductase. ESR spin-trapping experiments carried out in the presence of the hydroxyl radical scavenger ethanol and the spin trap DMPO (5,5-dimethyl-1-pyrroline-1-oxide) produced ESR spectra characteristic of the hydroxyl radial-derived carbon-centered DMPO-alkoxyl radical adduct. Thus hydroxyl radicals produced by the Fe3(+)-ochratoxin A complex in the presence of an enzymatic reductase may be be partly responsible for ochratoxin A toxicity.

Mechanism of ochratoxin A stimulated lipid peroxidation.

Lipid peroxidation, measured as malondialdehyde formation or by oxygen uptake, was stimulated markedly by the mycotoxin ochratoxin A (OTA) in a reconstituted system consisting of phospholipid vesicles, the flavoprotein NADPH-cytochrome P450 reductase, Fe3+, EDTA and NADPH. Deletion of EDTA lowered the extent of lipid peroxidation but did not eliminate it. Fluorometric and spectrophotometric studies demonstrated the formation of a 1:1 Fe3(+)-OTA complex. The rate of reduction of Fe3+ to Fe2+ was enhanced markedly in the presence of OTA, and there was a further increase in the rate when EDTA was also included. The data indicate that OTA stimulates lipid peroxidation by complexing Fe3+ and facilitating its reduction. Subsequent to oxygen binding, an iron-oxygen complex of undetermined nature initiates lipid peroxidation. Free hydroxyl radicals appear not to participate in lipid peroxidation stimulated by Fe3(+)-OTA.

Effect of a Prudhoe Bay crude oil on hepatic and renal peroxisomal beta-oxidation and mixed-function oxidase activities in rats.

The effect of oral administration of a Prudhoe Bay crude oil (PBCO) to male rats (PBCO, 2.6 g/kg body weight, daily) for 5-12 days on hepatic and renal microsomal monooxygenase activities and peroxisomal beta-oxidation has been investigated. PBCO administration leads to liver enlargement. This is associated with induction of microsomal cytochrome P-450 levels (1.6- to 2.0-fold) and dependent mixed-function oxidase activities (7-ethoxyresorufin-O-deethylase and 7-pentoxyresorufin-O-depentylase, representing cytochrome P-450I and cytochrome P-450IIB isoenzymes respectively, 9- to 15-fold; omega-oxidation of lauric acid representing the cytochrome P-450IVA1 isoenzyme, 1.4- to 1.5-fold) along with peroxisomal beta-oxidation (palmitoyl CoA oxidation, 2- to 5-fold). It was observed that rats exposed to PBCO showed an increase in renal microsomal cytochrome P-450 content (1.6- to 2.3-fold), cytochrome P-450I activity (5- to 8-fold) and omega-oxidation activity (1.3- to 1.4-fold). However, renal peroxisomal beta-oxidation was unaltered. Serum total triglycerides were lowered by 41-46% after PBCO exposure. These results suggest that induction of peroxisomal beta-oxidation and possibly mono-oxygenases may be related to the carcinogenic/tumorigenic potential of crude oil.

Perturbation of liver microsomal calcium homeostasis by ochratoxin A.

The effect of ochratoxin A on hepatic microsomal calcium sequestration was studied both in vivo and in vitro. The rate of ATP-dependent calcium uptake was inhibited by 42-45% in ochratoxin A intoxicated rats as compared to controls. In the presence of NADPH, addition of ochratoxin A (2.5 to 100 microM) caused a concentration-dependent inhibition of calcium uptake (28-94%) by untreated rat liver microsomes. The rate of NADPH-dependent lipid peroxidation, measured as malondialdehyde formed, was also greatly enhanced by ochratoxin A. Various agents that inhibited ochratoxin A enhanced lipid peroxidation were also able to block the destruction of calcium uptake activity. Lipid peroxidation enhanced by ochratoxin A was also accompanied by leakage of calcium from calcium-loaded microsomes. These results suggest that ochratoxin A disrupts microsomal calcium homeostasis by an impairment of the endoplasmic reticulum membrane probably via enhanced lipid peroxidation.

Lipid peroxidation as a possible cause of ochratoxin A toxicity.

Addition of the mycotoxin ochratoxin A (OA), a nephrotoxic carcinogen, to rat liver microsomes greatly enhanced the rate of NADPH or ascorbate-dependent lipid peroxidation as measured by malondialdehyde formation. NADPH-dependent lipid peroxidation in kidney microsomes was similarly enhanced by OA. The process required the presence of trace amounts of iron but cytochrome P-450 and free active oxygen species appeared not to be involved. The efficiency of several ochratoxins (ochratoxins A, B, C, alpha and O-methyl-ochratoxin C) to enhance lipid peroxidation was related to the presence and reactivity of the phenolic hydroxyl group. Furthermore, the ability of these ochratoxins to enhance lipid peroxidation in microsomes correlated precisely with their known toxicities in chicks. Administration of ochratoxin A to rats also resulted in enhanced lipid peroxidation in vivo as evidenced by a seven-fold increase in the rate of ethane exhalation. These results suggest that lipid peroxidation may play a role in the observed toxicity of ochratoxin A in animals; a mechanism is proposed. (Formula: see text). Ochratoxin A: X = Cl; R1 = R2 = R3 = R4 = H Ochratoxin B: X = H; R1 = R2 = R3 = R4 = H Ochratoxin C: X = Cl; R1 = R2 = R3 = H; = R4 = CH3 O-Methyl-ochratoxin C: X = Cl; R2 = R3 = H; R1 = R4 = CH3 (4R)-4-hydroxyochratoxin A: X = Cl; R1 = R3 = R4 = H; R2 = OH (4S)-4-hydroxyochratoxin A: X = Cl; R1 = R2 = R4 = H; R3 = OH Fig. 1. Chemical structures of the various ochratoxins.

Comparison of the inhibitory effects of some compounds present in crude oils on rat platelet aggregation: role of intra- and extra- cellular calcium.

In vitro addition of some representative aliphatic, aromatic or heterocyclic compounds present in petroleum crude oils to washed rat platelets resulted in a concentration-dependent inhibition of aggregation induced by ADP or thrombin. Increasing concentration of extracellular Ca2+ did not alter the pattern of inhibition. ADP-induced intracellular Ca2+ mobilization was unaffected by most of the compounds tested. However, Ca2+ uptake was significantly inhibited when platelets were preincubated with these agents. This suggests that some components of crude oil may inhibit platelet aggregation by bringing about alterations in the platelet plasma membrane.

Effect of a Prudhoe Bay crude oil on hepatic and placental drug metabolism in rats.

Administration of a Prudhoe Bay crude oil (PBCO) to pregnant rats resulted in induction of hepatic microsomal P-450 levels and various monooxygenases in a dose-dependent manner. The activities of aniline hydroxylase, benzo[a]pyrene hydroxylase, aminopyrine-N-demethylase, ethoxyresorufin-O-deethylase, and pentoxyresorufin-O-depentylase were increased 2-3-fold, 12-15-fold, 1.4-1.8-fold, 20-24-fold, and 6-8-fold, respectively, on gestation day 18, when a single dose of PBCO (5-10 mL/kg body weight, p.o.) had been administered 24 h earlier. Glutathione-S-transferase, UDPG transferase, and DT-diaphorase activities were also increased; however, maximum induction was noticed when crude oil was given 72 h earlier. Repeated exposure (day 6-day 17, daily) of crude oil at lower levels was able to produce similar induction patterns in enzyme systems at day 18 of gestation. The xenobiotic-metabolizing enzyme systems were also induced transplacentally: treatment of pregnant rats with PBCO induced both placental and fetal hepatic enzyme systems. Liver microsomal P-450 contents, benzo[a]pyrene hydroxylase, and ethoxyresorufin-O-deethylase activities were increased 2-fold, 2-3-fold, and 10-12-fold, respectively in 18-day-old fetuses. Similar trends were noticed in placenta. Activities of phase II enzymes such as glutathione-S-transferase, UDPG transferase, and DT-diaphorase were also significantly elevated. It is suggested that crude oil induces maternal hepatic drug metabolism and that some of its constituents (mainly aromatic hydrocarbons) and (or) their metabolites pass through the placenta and thus induce drug-metabolizing enzymes transplacentally. The practical importance of the results in relation to human and environmental health is also discussed.

The hepatotoxic potential of a Prudhoe Bay crude oil: effect on mouse liver weight and composition.

The hepatotoxic properties of a Prudhoe Bay Crude Oil (PBCO) were evaluated in mice. Administration of PBCO (5.0 ml/kg body wt, daily for 2 days) to mice resulted in an increase in (i) liver wet and dry weight, (ii) hepatic total proteins, RNA, glycogen and total lipids, and (iii) individual lipids such as cholesterol, triglycerides and phospholipids. Hepatic protein biosynthesis, determined in vivo by administration of L-[14C]leucine was increased in PBCO exposed mice. The rate of 3H incorporation from 3H2O was significantly enhanced in liver fatty acids, cholesterol, triglycerides and thus ultimately in total lipids. Also, an increase in 3H incorporation was noticed in hepatic glycogen after PBCO administration. The results suggest that PBCO may induce hepatotoxicity by altering the intermediary metabolism of biochemical constituents.

Embryotoxic evaluation of a Prudhoe Bay crude oil in rats.

The embryotoxic potential of a Prudhoe Bay crude oil (PBCO) was investigated in rats. PBCO was administered orally to pregnant rats as (i) a single dose on various gestation days, (ii) a single variable dose on gestation day 6, or (iii) as daily doses from day 6 to day 17 of pregnancy. PBCO administered during the earlier stages of pregnancy (day 3, 6 or 11) but not during the later stages, affected the reproductive performance of pregnant rats by significantly increasing the number of resorptions including fetal death and by decreasing the fetal weight. A dose-dependent increase in fetomortality was also observed. Multiple exposure to low levels of crude oil also caused a significant reduction in maternal body weight besides other embryotoxic changes.