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1.
Halogenated aromatic hydrocarbons (HAHs) and polynuclear aromatic hydrocarbons (PAHs) are major environmental contaminants. Fish species that are chronically exposed to these compounds can develop resistance to their toxic effects. In all fish species studied to date, toxicant resistance has been accompanied by decreased inducibility of the xenobiotic metabolizing enzyme, cytochrome P450 1A (CYPIA). CYP1A induction is mediated through the Aryl Hydrocarbon Receptor (AHR). Although these compounds mediate their effects through this pathway, there have been resistant populations in which one chemical class cannot induce CYPIA expression (HAHs) while the other (PAHs) can. Resistance to PAHs was examined in a HAH-resistant population of Fundulus heteroclitus collected from a site contaminated with both compound classes (Newark Bay, NJ). Fish were injected intraperitoneally with the HAH 3,4,3',4'-tetrachlorobiphenyl (PCB77), benzo[a]pyrene (B[a]P, a PAH) or vehicle and sacrificed after 2 (B[a]P) or 5 days (PCB77, vehicle). We found no significant increase in CYP1A mRNA levels in resistant Newark Bay F. heteroclitus treated with either B[a]P or PCB77, while there was a 3.9 fold (PCB77) and 4.2 fold (B[a]P) increase in CYP1A mRNA in Flax fish relative to controls. AHR labeling studies revealed significantly (P < 0.05) lower levels of hepatic AHR in Newark fish (1,770 +/- 1,693.2 DPM) relative to Flax fish (6,082.5 +/- 1,709.9 DPM). Overall, these data suggest Newark F. heteroclitus are resistant to both PAHs and HAHs at the level of CYP1A mRNA, which might be mediated, in part, though lower expression of AHR. We are currently studying the promoter sequence to determine its role in chemical resistance. 相似文献
2.
English sole (Pleuronectes vetulus) and starry flounder (Platichthys stellatus) are two sympatric flatfish species which show markedly different responses to chemical contaminant exposure. Whereas English sole develop hepatic neoplasms, the prevalences of which are strongly linked to exposure to polycyclic aromatic hydrocarbons (PAHs), evidence of neoplasia is virtually nonexistent in starry flounder, even those residing in areas with very high levels of PAH in the sediments. Because PAHs are activated to genotoxic forms by the action of cytochrome P450 1A (CYP1A) in teleosts, we are examining the hypothesis that variation in the hepatic expression of this major inducible cytochrome P450 isozyme may contribute to the differential contaminant response. These two species were captured in the Duwamish Waterway, a contaminated area of Puget Sound, Washington. Catalytic activity of CYP1A [determined as aryl hydrocarbon hydroxylase (AHH) activity] was measured in the liver to quantitatively assess the relative induction of CYP1A in these two species, and AHH activity was significantly higher in English sole than in starry flounder (p = 0.015). Cellular expression of CYP1A was determined by immunohistochemical localization of tissues, using an avidin-biotin peroxidase complex method, with polyclonal rabbit anti-cod CYP1A. The results showed a markedly reduced expression of CYP1A in hepatocytes of starry flounder, which is consistent with the apparent resistance of this species to the development of hepatocellular neoplasia. This reduced expression of CYP1A in hepatocytes of contaminant-exposed fish was previously seen in oyster toadfish from the Elizabeth River, Virginia, and this species is also apparently resistant to hepatocellular neoplasia. 相似文献
3.
Newark Bay (NB) killifish (Fundulus heteroclitus) have been chronically exposed to environmental contaminants that activate the aryl hydrocarbon receptor (AHR) and are tolerant to toxic effects and CYP1A induction provoked by AHR ligands. Resistance to CYP1A induction could be due to an epigenetic mechanism such as DNA methylation. We measured in-ovo CYP1A catalytic activity (ethoxyresorufin-O-deethylase, EROD) in NB and reference site killifish embryos aqueously exposed to various concentrations of the de-methylating agent 5-azacytidine, 5-AC (5, 50 and 500 micro(micro)M) with or without 0.2 micro(micro)g/l of the CYP1A inducer 3,3',4,4',5 pentachlorobiphenyl (IUPAC PCB126). Neither PCB126 alone, nor PCB126 plus 5-AC, induced EROD above levels in vehicle treated Newark Bay fish. In reference site fish, the same PCB126 dose provoked a 7.4-fold EROD induction relative to controls. We conclude that Newark Bay killifish are resistant to CYP1A induction by co-planar PCBs during early embryological development and our data suggests that DNA methylation does not play a critical role in resistance to CYP1A induction in this model. 相似文献
4.
Gonadally mature fish display strong sex-related differences in the content and activity of P4501A, the major polynuclear aromatic hydrocarbon-inducible P450 form in teleosts. Such differences appear related to plasma levels of the female sex steroid, estradiol (E2); however, neither the mechanism of estradiol suppression of P4501A nor the capacity for hormonal regulation to overcome P4501A induction by high concentrations of potent inducers are known. Gonadally mature flounder (Pseudopleuronectes americanus) were collected from Fox Island (FI), Rhode Island, a reference site, and New Bedford Harbor (NB), Massachusetts, a site highly contaminated with polychlorinated biphenyls (PCBs). Differences in flounder P4501A expression were determined at the level P4501A catalytic activity (measured as ethoxyresorufin-O-deethylase, EROD), P4501A protein content (immunoquantitated), and P4501A mRNA content (by Northern blot) as they relate to sex, reproductive status, and hepatic PCB content. Our results confirm that suppression of P4501A in gonadally mature female fish is probably due, at least in part, to elevated E2 titers, and demonstrate that such suppression occurs at a pretranslational level and, further, that endogenous regulation of P4501A expression can ‘override’ exogenous regulation by even high concentrations of P4501A inducers. 相似文献
5.
Estrogens appear to have a modulating effect on the expression of cytochrome P4501A (CYP1A) in fish. A number of in vivo studies have demonstrated that hepatic CYP1A expression in females decrease during sexual maturation when plasma levels of 17 beta-estradiol (E2) increase, or in cases when the fish in injected with E2. Since a number of environmental contaminants have weak estrogen-like activities, the question arises if these compounds are able to modulate CYP1A expression as well. In the present study, we used in vitro monolayer cultures of rainbow trout, Oncorhynchus mykiss, liver cells to compare concentration-dependent (10(-9) to 10(-5) M) effects of the natural steroid E2 and the non-steroidal xenoestrogen 4-tert-octylphenol (OP) on CYP1A-catalyzed 7-ethoxyresorufin-O-deethylase (EROD) activity. The concentration dependency of the estrogenic activity of the two test compounds was assessed by determination of hepatocellular vitellogenin (Vg) release into the culture medium. Exposure of hepatocytes to E2 concentrations of 10(-8) M and higher led to a significant inhibition of basal cellular EROD activity. On the contrary, exposure to OP did not result in an inhibition of EROD activity, even at OP concentrations (10(-6) M, 10(-5) M) which were associated with a significant induction of Vg synthesis. 相似文献
6.
Newark Bay (NB) killifish (Fundulus heteroclitus) have been chronically exposed to environmental contaminants that activate the aryl hydrocarbon receptor (AHR) and are tolerant to toxic effects and CYP1A induction provoked by AHR ligands. Resistance to CYP1A induction could be due to an epigenetic mechanism such as DNA methylation. We measured in-ovo CYP1A catalytic activity (ethoxyresorufin-O-deethylase, EROD) in NB and reference site killifish embryos aqueously exposed to various concentrations of the de-methylating agent 5-azacytidine, 5-AC (5, 50 and 500 μ(micro)M) with or without 0.2 μ(micro)g/l of the CYP1A inducer 3,3′,4,4′,5 pentachlorobiphenyl (IUPAC PCB126). Neither PCB126 alone, nor PCB126 plus 5-AC, induced EROD above levels in vehicle treated Newark Bay fish. In reference site fish, the same PCB126 dose provoked a 7.4-fold EROD induction relative to controls. We conclude that Newark Bay killifish are resistant to CYP1A induction by co-planar PCBs during early embryological development and our data suggests that DNA methylation does not play a critical role in resistance to CYP1A induction in this model. 相似文献
7.
Monari M Cattani O Serrazanetti GP Selli A Pagliuca G Zironi E O'Hara SC Livingstone DR 《Marine environmental research》2007,63(3):200-218
The effects of water-borne exposure to benzo[a]pyrene (36 h; celite-bound 0.44 mg L(-1) B[a]P) on cytochrome P450 (CYP) and superoxide dismutases (SODs) were examined in digestive gland of the blood clam, Scapharca inaequivalvis. B[a]P accumulation and elimination were rapid, with maximum whole-body concentrations of 1.78 ng g(-1) wet wt after 12 h of treatment, followed by a progressive decline to 0.89 ng g(-1) at 36 h. The presence of B[a]P resulted in an increase in total CYP of digestive gland microsomes from 54+/-14 to 108+/-21 pmol/mg protein (mean+/-SD; p<0.05, 24 h). Increases were also seen in microsomal CYP1A1/1A2-immunopositive protein (50.5 kDa app. mol. wt; p<0.05), but not CYP2E1-immunopositive protein (49 kDa app. mol. wt.), indicating a specific response of the former isoform. Exposure to B[a]P produced a steady increase in Mn-SOD digestive gland activity (p<0.01; p<0.05) but no significant change in Cu/Zn-SOD activity. The respective proteins, measured by western blotting, were not significant induced after B[a]P exposure. Cu/Zn-SOD and Mn-SOD activities were correlated with total CYP levels (r=0.96 and 0.63, respectively), indicating a role for CYP in reactive oxygen species (ROS) production during exposure. Both 'NADPH-independent' and NADPH-dependent metabolism of B[a]P by digestive gland microsomes was seen, producing mainly 1,6-, 3,6- and 6,12-diones, with some phenols and 7,8-dihydrodiol; putative protein adducts were also formed. Redox cycling of the diones may also have contributed to ROS production, leading to the increased SOD activities. 相似文献
8.
为了了解苯并[a]芘(BaP)对鱼类细胞色素P4501A1(CYP1A1)表达的影响,以褐菖鲉(Sebasticus marmoratus)为实验材料,采用体内实验,研究其在经过不同浓度(0.1、1、10、20、50mg/kg鱼体重量)的BaP诱导后,鱼体肝脏研究CYP1A1基因表达的情况,筛选出后续时间-效应实验中BaP注射的最佳浓度,研究BaP诱导6h、12h、1d、3d、7d后(质量浓度为20mg/kg鱼体重量)鱼体肝脏CYP1A1酶活性、基因表达和蛋白表达的情况。结果表明:剂量-效应实验中,20mg/kg鱼体重量为最佳浓度,此浓度下,基因表达在各组中变化最显著。时间-效应实验中,较空白对照组而言,染毒6h、12h和1d后,EROD酶活性显著增加。3d后开始下降,与对照组相比变化不大,7d后酶活性又发生上调。半定量RT-PCR结果表明,各染毒组与对照组相比,CYP1A1基因表达量都发生了上调,呈现先上升后下降的趋势。其中,6h和12h组相对表达量极显著增加,1d后开始下降且与3d和7d组相比变化不明显。Western blot结果表明,蛋白表达量在染毒12h后表现出显著的诱导效应,随着时间的延长略有回落,但与对照组相比仍有显著性差异。研究表明:BaP对褐菖鲉CYP1A1具有较强的诱导作用。一定质量浓度的BaP注射于褐菖鲉不同的时间后,能诱导褐菖鲉活体EROD酶活性、CYP1A1基因m RNA表达及蛋白表达,并随着时间的延长呈现先诱导后抑制的趋势。这说明BaP作为诱导剂对CYP1A1酶活性和蛋白表达的作用机制可能与调控CYP1A1的转录水平有关。 相似文献
9.
Relative potency of PAHs and heterocycles as aryl hydrocarbon receptor agonists in fish 总被引：6，自引：0，他引：6
The relative potency of polycyclic aromatic compounds as aryl hydrocarbon receptor (AhR) agonists in fish was determined using data on CYP1A induction or AhR binding for 74 polycyclic aromatic hydrocarbons (PAHs) and heterocycles in teleost, avian, or mammalian systems from 18 published papers. Each PAH was assigned a fish potency factor relative to the potency of 2,3,7,8-tetrachlorodibenzo-p-dioxin as an AhR agonist. Two and three ring unsubstituted PAHs were generally inactive in fish, avian, and mammalian systems. Benzo[k]fluoranthene and indeno[1,2,3-cd]pyrene were consistently the most potent PAHs, with fish potency factors of 0.001-0.002. Common structural features associated with higher potency PAHs included 4-6 rings containing fluoranthene or phenanthrene structures with an exposed bay region. These results show that PAHs can have similar potency as many dioxin-like PCBs, and AhR mediated toxicity should be considered in assessing the risks of PAHs in fish. 相似文献
10.
外源激素对养殖牙鲆血浆睾酮和雌二醇含量的影响研究 总被引：7，自引：0，他引：7
雄性牙鲆单独注射促黄体激素释放激素类似物(LHRH-A)(每千克质量的注射量,下同)25μg/kg或人绒毛膜促性腺激素(hCG)1 000 IU/kg,血浆睾酮(T)含量在注射后6 h大幅度降低,12h时达到最低值,以后逐渐回升;LHRH-A与hCG联合注射[LHRH-A(12.5μg/kg)+hCG(500 IU/kg)],注射后6 h血浆T含量剧烈下降,24 h时达到最低点,以后缓慢回升;对照组雄鱼血浆T含量随着采样进行而呈现降低趋势.雌鱼单独LHRH-A后,血浆雌二醇(E2)水平逐渐下降,24 h时达到最低值,30 h后略有回升;单独注射hCG后,血浆E2含量缓慢下降,30 h达到最低值;LHRH-A与hCG联合注射,注射后6 h血浆E2含量逐渐下降,24 h时达到最低点,30 h时缓慢回升.对照组雌鱼血浆E2水平也随着采样的进行而逐渐降低.结果表明:单独或联合注射LHRH-A和hCG降低了雌、雄牙鲆血浆E2和T含量,与对照组结果相同. 相似文献
11.
Despite the fact that BaP is a carcinogen, mammalian immunosuppressant, and ubiquitous aquatic pollutant, knowledge regarding the effects of BaP on the immune system of fish is still lacking. To begin to fill this gap, studies were conducted in medaka to examine the effects and mechanisms by which BaP exposure might alter host immunocompetence. Fish, exposed by IP injection of BaP (2-600 microg/g BW), were examined after 48 h for effects upon immune function and CYP1A expression/activity. Benzo[a]pyrene, at a concentration below that which increased levels of CYPIA expression/activity (2 microg BaP/g BW) suppressed lymphocyte proliferation. Concentrations of BaP at 20 and 200 microg/g BW. suppressed antibody-forming cell (AFC) numbers, superoxide production, and host resistance against bacteria. In contrast, exposure to the low affinity aryl hydrocarbon receptor (AhR) agonist, benzo[e]pyrene (BeP), neither induced CYP1A expression nor altered immune function. Given the lack of immunosuppressive effects produced by BeP, and the fact that exposure to the AhR antagonist (and CYP1A inhibitor) alpha-naphthoflavone (ANF) ameliorated the suppressive effects of BaP upon AFC numbers, the AhR pathway (including CYP1A-mediated production of reactive BaP metabolites) appears important in mediating BaP-induced immunotoxicity in fish, as in mammals. In the past, the medaka has proven a successful model for assessing carcinogenic agents. These studies have demonstrated its utility for also determining the immunosuppressive effects of an important aquatic contaminant. 相似文献
12.
M. McArdle A. Elskus A. McElroy B. Larsen W. Benson D. Schlenk 《Marine environmental research》2000,50(1-5):175-179
Recent studies demonstrating feminization of effluent-exposed wild-caught male fish in the UK have prompted much research regarding the estrogenic activity of effluent from municipal sewage treatment plants (MSTPs). To investigate the estrogenicity and cytochrome P450 1A (CYP1A) induction potency of MSTP effluent, two species of fish, adult male mummichogs, Fundulus heteroclitus, and juvenile sunshine bass, Morone saxatilis x Morone chrysops, were exposed to un-chlorinated effluent (75% effluent, 25% seawater) from a large MSTP in Yonkers, NY, USA. After a 21-day static-daily (75%) renewal exposure, significant elevations over controls were observed in levels of vitellogenin (VtG) in plasma (1730%) and liver (131%) in effluent-exposed sunshine bass. In contrast, hepatic VtG was not elevated in mummichogs; plasma VtG was not measured in this species. Effluent exposure elevated hepatic CYP1A protein (140-145%) and ethoxyresorufin-O-deethylase (EROD) activity (408-598%) in both species. These findings suggest ontogenetic and/or species differences in response to estrogenic compounds in MSTP effluent. Furthermore, the elevation of CYP1A in response to sewage effluent exposure indicates the presence of additional compounds that may alter xenobiotic and/or steroid biotransformation in fish. 相似文献
13.
Hepatic CYP1A levels and EROD activity in English sole: biomonitoring of marine contaminants in Vancouver Harbour 总被引：4，自引：0，他引：4
To assess chemical contaminant stress in the marine environment, ethoxyresorufin-O-deethylase (EROD) activity and cytochrome P450 1A (CYP1A) expression were measured in 88 English Sole (Pleuronectes vetulus) collected during May and June 1999 from four sites in Vancouver Harbour and at an expected reference site outside the harbour. Hepatic microsomes were prepared from the fish and analyzed for total CYP content, EROD activity, and CYP1A protein levels. Hepatic EROD activity and CYP1A protein levels were elevated in fish from two sites in the inner harbour. A comparison with sediment chemistry data showed that fish with increased EROD activity and CYP1A levels came from sites containing relatively high levels of polycyclic aromatic hydrocarbons and polychlorinated biphenyls. Unexpectedly high levels of EROD activity and CYP1A protein were also found in fish from a reference site near Gibsons, in Howe Sound. The elevated EROD activity and CYP1A expression in fish from this site cannot be explained by the chemical analysis data collected. 相似文献
14.
Chronic exposure to organic contaminants such as polychlorinated biphenyls (PCBs) can lead to the development of resistance to these chemicals, a condition associated with reduced response of CYP1A1, a pollutant-inducible biomarker. We measured CYP1A activity (ethoxyresorufin o-deethylase, EROD) and PCB concentrations in feral fish from the Town Branch/Mud River system (Logan County, KY), a stream historically contaminated with PCBs and partially remediated. As a first step in evaluating the possible development of resistant populations in this system, we measured CYP1A expression and PCB body burdens in resident fish from sites we previously characterized as containing biologically significant levels of CYP1A inducing compounds. Mean PCB concentrations in edible flesh ranged from 75.2 to 16.7 microg/g in fish collected from Town Branch remediated sites and were relatively low (1.23 microg/g) in Town Branch reference site fish. However, hepatic CYP1A activity was similar among individuals of most species collected from reference and contaminated/remediated sites. The absence of elevated CYP1A levels in resident fish species despite the presence of significant PCB body burdens may indicate these fish have developed reduced sensitivity to CYP1A induction, a condition associated with acquired resistance to toxicants. 相似文献
15.
根据2010年春季对台湾海峡中部日本鲭的生物学测定数据及怀卵量计数结果,对其产卵群体的生物学特征进行了研究.结果表明：日本鲭产卵群体性比符合1∶1的雌雄性比关系;叉长范围212.00～271.00 mm,平均244.76 mm,优势组230.00～260.00 mm;雌鱼最小性成熟叉长225.00 mm,雄鱼最小性成熟叉长221.00 mm;体质量范围110.99～242.00 g,平均170.97 g,优势组130.00～220.00 g.雌雄个体的性腺成熟度均以Ⅳ～Ⅴ期为主,摄食强度均较高,雌鱼平均摄食强度为2.00,雄鱼平均摄食强度为2.25;雌鱼的平均摄食强度随性腺成熟度的提高呈下降趋势,而雄鱼正好相反;在达到完全性成熟前,雌雄鱼的性腺指数GSI都随着性腺的发育而增加,雌鱼的平均性腺指数GSI略高于雄鱼;绝对怀卵量5.283 5万～16.884 7万粒,平均10.405 0万±0.611 8万粒;叉长相对怀卵量227～625粒/mm,平均423±22粒/mm.随着叉长的增加,怀卵量也持续增加.叉长250.00 mm以上个体怀卵量相对于250.00 mm以下个体出现大幅增加趋势.与20世纪80年代研究结果相比,目前该海域日本鲭的大量性成熟年龄由2龄提前为1龄,最小性成熟年龄即为大量性成熟年龄;产卵群体年龄组成由1～5龄转变为1～2龄,优势组由2～3龄下降为1龄;产卵群体平均绝对怀卵量下降了33.23%.因此,为了保护该海域日本鲭资源并提高种群数量和年龄结构,应该首先制定合理的最小开捕叉长,同时在其春汛产卵期采取必要的休渔措施及在主要产卵场设立保护区. 相似文献
16.
17.
Haasch ML 《Marine environmental research》2002,54(3-5):297-301
The mummichog (Fundulus heteroclitus) has been shown to be responsive to peroxisome proliferating agents (PPAs). Peroxisomes function as important sites for fatty acid beta-oxidation. Peroxisome proliferation by PPAs or starvation can lead to changes in the size and number of peroxisomes and the expression of omega-hydroxylases (CYP2K1/2M1 in rainbow trout). Mummichogs were subjected to 96 h fasting or 96 h recovery from fasting. Expression of PMP70- and CYP2K1/2M1-like proteins in vehicle-treated or non-treated controls was compared in both males and females. Fasting and vehicle produced decreases in PMP70- and CYP2K1/2M1-like proteins in both males and females. In reproductive females, decreases due to fasting and vehicle treatment were greater than in female fish that were not gravid. Recovery from fasting resulted in levels of CYP2K1/2M1 near control levels in males while in recovered females, about 2-fold higher levels compared to controls were noted. These results indicate that gender, reproductive status and diet can produce changes in the expressed levels of peroxisomal PMP70 and microsomal CYP2K1/2M1-like proteins in the mummichog. 相似文献
18.
The biotransformation of xenobiotics by microsomal cytochromes P450 is known to be pivotal in the effects of some compounds, and thought to be so for many. A knowledge of CYP gene diversity and CYP function and regulation in aquatic species is pursued, expecting that it will disclose mechanisms, allow predictions regarding species differences in susceptibility, and provide markers for exposure to xenobiotics. As well, it is hoped that such knowledge will provide clues to CYP endogenous functions, and to the origin and functional significance of CYP gene diversity. The knowledge of CYP in marine and other aquatic species is expanding rapidly. The diversity of CYP genes in non-mammalian vertebrates may approximate that in mammals. At present, cloning studies have identified members of gene families 1 to 4 have been cloned from one or more fish species. Where known, the gene structures of fish CYP genes are like those of mammalian homologues. Only one CYP1A gene has been identified in most fish species examined. Fish CYP1As, including multiple forms from recent divergence in some genera, have structural and catalytic properties more like CYP1A1, but also have properties that are 1A2-like, consistent with fish CYP1As representing the CYP ancestral to both CYP1A1 and CYP1A2. A number of genes cloned from several species have been classified in the 3A subfamily. Fish CYP3As catalyze steroid 6β-hydroxylase, and have other properties consistent with mammalian 3As. Recently identified CYP4 genes classify to novel subfamilies but apparently are homologues of mammalian CYP4 genes, and may act on similar substrates. The greatest diversity of fish CYP genes is in family 2; there are now six fish CYP2 subfamilies known. Four of these are novel subfamilies, although cladistic analysis suggests distinct relationships to mammalian CYP2 subfamilies. Heterologous expression and characterization of some of these CYP have identified similar functions among genes in different subfamilies. For example, fish CYP2Ns and CYP2Ps are related to mammalian CYP2Js, and CYP2P3 and CYP2J2 have strikingly similar functions as fatty acid epoxygenases and hydroxylases, with nearly identical regio- and enantioselectivity for metabolism of arachidonic acid. In addition to sequence and catalytic similarities, there also are indications that CYP regulation, tissue and cellular localization are similar between fish and mammals. Yet even in cases where orthology is strongly suggested, e.g. CYP1A, there appear to be taxonomic differences in active site structure suggesting potential differences in involvement of CYP1A in toxicity. In contrast to fish, CYP diversity and functions in aquatic invertebrates are poorly known. Investigators have identified novel gene families and subfamilies in crustaceans (CYP2L; CYP45), molluscs (CYP30, CYP10) and sponges (CYP38). CYP4C genes occur in crustaceans, molluscs and echinoderms, and a new subfamily (CYP4Y) in molluscs. The future? There is no doubt that new CYP will continue to be discovered in non-mammalian vertebrates; some (e.g. CYP51) can be predicted confidently. And, there is no doubt that the numbers known in invertebrates will expand greatly. In insects and C. elegans the numbers are very high, and even slime molds have 18 CYP genes. It is virtually certain that CYP genes with unique functions will be discovered. While the knowledge of CYP genes is increasing, knowledge of CYP function and regulation lag well behind. Technical approaches to speed the aquisition of such knowledge are available. The information will be essential to discern the role that CYP play in the disposition and toxicity of xenobiotics, during development as well as in adults. Yet, when such data are in hand, we may have to face the paucity of information on the diversity, function and regulation other enzymes, notably the glutathione S-transferases, glucuronyl transferases and sulfotransferases, in aquatic species. Discerning orthologous relationships among CYP genes, as well as those for phase II enzymes, could highlight gene lineages associated with conserved and endogenous functions. Understanding CYP endogenous functions, as well as their metabolism of xenobiotics, may reveal fully the ways that chemicals cause toxicity. [Support: Sea Grant NA46RG0470-R/P61, EPA R-829890, NIH ES07381]. 相似文献
19.
In a controlled laboratory experiment, fish in two treatment groups were exposed to B(a)P or B(a)P+PCB77 repeatedly over 1 year. Fish were held in a flow-through system and sampled on day 0, week 3, and on months 3, 6, 9, and 12. Each sampling (except week 3) was followed by exposure in water under static conditions. Exposure was terminated by restoring the flow-through within a maximum period of 24 h. Hepatic CYP1A remained significantly induced in juveniles even 3 months after the first exposure. The induction response in liver was more persistent in comparison to the gill response in juveniles. Sex influenced CYP1A expression in both organs of control fish and in both exposure groups. Suppression of CYP1A occurred in females even under repeated exposure. Liver GST activity showed sex differences, control females having higher activities than control males on the same sampling day. GST activity showed increases and decreases under both exposures possibly indicating the overriding influence of some other factors. Increased levels of fluorescent aromatic compounds (FACs) were detected in bile only in females exposed to B(a)P and PCB77 for 9 months. Liver UDPGT activity, length, weight, and condition showed no differences related to exposure or gender. The study was supported by Norwegian Research Council and the Ministry of Oil and Energy in Norway. 相似文献
20.
The gulf killifish, Fundulus grandis, was used to determine the influence of biological rhythms on three biomarker responses. We first developed monoclonal antibodies against the model's immunoglobulins and vitellogenin in order to measure antibody responses and vitellogenesis, respectively. We then treated adults with 10, 1, 1, and 10 ppm of Aroclor 1254, tribuyltin, 3-methylcholanthrene, and nonyl-phenol, respectively, in mixtures over a 16-week period. The study followed Vibrio anguillarum-specific antibody responses, hepatic CYP1A, and plasma vitellogenin levels in the morning and again in the evening at 2-week intervals. The contaminated diet suppressed secondary antibody responses, but only in the morning. The contaminated diet also altered CYP1A, but not vitellogenesis. In addition, fish in the control group exhibited daily and seasonal differences in specific antibody levels and CYP1A induction. Moreover, circulating vitellogenin levels in control males sampled in the morning increased throughout the exposure, but remained below those of females. This study underscores the need to consider normal physiological rhythms when employing biomarkers in toxicology. 相似文献