Structural and energetic hot-spots for the interaction between a ladder-like polycyclic ether and the anti-ciguatoxin antibody 10C9Fab.

The mechanism by which anti-ciguatoxin antibody 10C9Fab recognizes a fragment of ciguatoxin CTX3C (CTX3C-ABCDE) was investigated by mutational analysis based on structural data. 10C9Fab has an extraordinarily large and deep antigen-binding pocket at the center of its variable region. We mutated several residues located at the antigen-binding pocket to Ala, and kinetic analysis of the interactions between the mutant proteins and the antigen fragment was performed. The results indicate that some residues associated with the rigid antigen-binding pocket are structural hot-spots and that L-N94 is an energetic hot-spot for association of the antibody with the antigen fragment CTX3C-ABCDE, suggesting the importance of structural complementarity and energetic hot-spot interactions for specific recognition of polycyclic ethers.

Inhibitory effects of Schizandrae Fructus on eotaxin secretion in A549 human epithelial cells and eosinophil migration.

Eosinophilia have been implicated in a broad range of diseases, most notably allergic conditions (e.g. asthma, rhinitis and atopic dermatitis) and inflammatory diseases. These diseases are characterized by an accumulation of eosinophils in the affected tissue. Defining the mechanisms that control the recruitment of eosinophil is fundamental to understanding how these diseases progress and identifying a novel target for drug therapy. Accordingly, this study was conducted to evaluate the regulatory effect of Schizandrae Fructus (SF) on the expression of eotaxin, an eosinophil-specific chemokine released in respiratory epithelium following allergic stimulation, as well as its effects on eosinophil migration. To accomplish this, human epithelial lung cells (A549 cell) were stimulated with a combination of TNF-alpha (100ng/ml) and IL-4 (100ng/ml) for 24h. The cells were then restimulated with TNF-alpha (100ng/ml) and IL-1beta (10ng/ml) to induce the expression of chemokines and adhesion molecules involved in eosinophil chemotaxis for another 24h. Next, the samples were treated with various concentrations of Schizandrae Fructus (SF) (1, 10, 100, 1000microg/ml) or one of the major constituents of SF, schizandrin (0.1, 1, 10, 100microg/ml), after which following inhibition effect assay was performed triplicates in three independence. The levels of eotaxin in secreted proteins were suppressed significantly by SF (100 and 1000microg/ml, p<0.01) and schizandrin (10 and 100microg/ml, p<0.01). In addition, SF (1, 10, 100 and 1000microg/ml) decreased mRNA expression levels in A549 cells significantly (p<0.01). Eosinophil recruitment to lung epithelial cells was also reduced by SF, which indicates that eotaxin plays a role in eosinophil recruitment. Furthermore, treatment with SF suppressed the expression of another chemokine, IL-8 (0.1 and 1microg/ml SF, p<0.01), as well as intercellular adhesion molecule-1 (10 and 100microg/ml SF, p<0.01) and vascular cell adhesion molecule-1 (0.1 and 1microg/ml SF, p<0.05), which are all related to eosinophil migration. Taken together, these findings indicate that SF may be a desirable medicinal plant for the treatment of allergic diseases.

How protein recognizes ladder-like polycyclic ethers. Interactions between ciguatoxin (CTX3C) fragments and its specific antibody 10C9.

Ciguatoxins are a family of marine toxins composed of transfused polycyclic ethers. It has not yet been clarified at the atomic level on the pathogenic mechanism of these toxins or the interaction between a polycyclic ether compounds and a protein. Using the crystal structures of anti-ciguatoxin antibody 10C9 Fab in ligand-free form and in complexes with ABCD-ring (CTX3C-ABCD) and ABCDE-ring (CTX3C-ABCDE) fragments of the antigen CTX3C at resolutions of 2.6, 2.4, and 2.3 angstroms, respectively, we elucidated the mechanism of the interaction between the polycyclic ethers and the antibody. 10C9 Fab has an extraordinarily large and deep binding pocket at the center of the variable region, where CTX3C-ABCD or CTX3C-ABCDE binds longitudinally in the pocket via hydrogen bonds and van der Waals interactions. Upon antigen-antibody complexation, 10C9 Fab adjusts to the antigen fragments by means of rotational motion in the variable region. In addition, the antigen fragment lacking the E-ring induces a large motion in the constant region. Consequently, the thermostability of 10C9 Fab is enhanced by 10 degrees C upon complexation with CTX3C-ABCDE but not with CTX3C-ABCD. The crystal structures presented in this study also show that 10C9 Fab recoginition of CTX3C antigens requires molecular rearrangements over the entire antibody structure. These results further expand the fundamental understanding of the mechanism by which ladder-like polycyclic ethers are recognized and may be useful for the design of novel therapeutic agents by antibodies, marine toxins, or new diagnostic reagents for the detection and targeting of members of the polycyclic ether family.

Immunotoxicity in invertebrates: measurement and ecotoxicological relevance.

Concern is growing regarding the impact of chemicals suspected of altering the function of the immune system in humans and wildlife. There are numerous examples of links between pollution and increased susceptibility to disease in wildlife species, including immunosuppression in harbour seals feeding on fish from contaminated sites, altered immune function in riverine fish and decreased host resistance in birds exposed to pollutants. Laboratory tests have identified potential immunological hazards posed by a range of anthropogenic chemicals in mammals and higher vertebrates. However, few reports have considered the ecological relevance of pollution-induced immunosuppression in invertebrate phyla, which constitute around 95% of all animal species and occupy key structural and functional roles in ecosystems. In this paper effects of chemicals on immune function in invertebrates are briefly reviewed and biomarkers of immunotoxicity are identified. Examples of new approaches for the measurement of immunological inflammatory reactions and stress in molluscan haemocytes are detailed. The relevance of defining the immune system as a target organ of toxicity in invertebrates is discussed and an integrated approach for the use of immunological biomarkers in environment management is proposed, combining measures of immune function and organismal viability at the biochemical, cellular and population level.

Susceptibility to the biological effects of polyaromatic hydrocarbons is influenced by genes of the major histocompatibility complex.

Polyaromatic hydrocarbons are ubiquitous environmental chemicals that are important mutagens and carcinogens. The purpose of this study was to determine whether genes within the major histocompatibility complex (MHC) influence their biological activities. Cell-mediated immunity to dimethylbenz(a)anthracene (DMBA) was investigated in congenic strains of mice. On three different backgrounds, H-2(k) and H-2(a) haplotype mice developed significantly greater contact-hypersensitivity responses to DMBA than H-2(b), H-2(d), and H-2(s) mice. In B10.A(R1) mice, which are Kk and Id, a vigorous contact-hypersensitivity response was present, indicating that the response was governed by class I, rather than class II, MHC genes. C3H/HeN (H-2(k)) and C3H.SW (H-2(s)) strains were also compared for the development of skin tumors and the persistence of DMBA-DNA adducts. When subjected to a DMBA initiation, phorbol 12-tetradecanoate 13-acetate (TPA)-promotion skin-tumorigenesis protocol, C3H/HeN mice, (which develop cell-mediated immunity to DMBA) were found to have significantly fewer tumors than C3H.SW mice (a strain that failed to develop a cell-mediated immune response to DMBA). DMBA-DNA adducts were removed more rapidly in C3H/HeN than in C3H.SW mice. The results indicate that genes within the MHC play an important role in several of the biological activities of carcinogenic polyaromatic hydrocarbons. The observations are consistent with the hypothesis that cell-mediated immunity to chemical carcinogens serves to protect individuals by removing mutant cells before they can evolve into clinically apparent neoplasms.

Metabolic requirements for induction of contact hypersensitivity to immunotoxic polyaromatic hydrocarbons.

Experiments were performed to define the metabolic requirements for induction of contact hypersensitivity to polyaromatic hydrocarbons (PAHs), environmental xenobiotics that are both immunotoxic and carcinogenic. Evidence that conversion of the parent compound to a reactive metabolite was necessary for the development of contact hypersensitivity included the fact 1) that contact hypersensitivity to the polyaromatic hydrocarbon dimethylbenz(a)anthracene (DMBA) only occurred in strains of mice that could metabolize the compound, 2) that among the PAHs, only those that could induce aryl hydrocarbon hydroxylase, the rate-limiting enzyme in the PAH metabolic pathway, were immunogenic, and 3) that inhibitors of PAH metabolism reduced DMBA contact hypersensitivity. Cells from the XS52 Langerhans cell-like dendritic cell line were able to metabolize the PAH benzo(a)pyrene to its diol, quinone, and phenol metabolites. GM-CSF augmented benzo(a)pyrene metabolism in XS52 cells. Finally, in vivo depletion of CD8+, but not CD4+, T cell populations inhibited contact hypersensitivity to DMBA. The implications of these experiments are that at least for some contact allergens, the metabolic status of the host is a key determinant of individual susceptibility to the development of allergic contact dermatitis, and the metabolic pathway of an individual hapten may have ramifications for the T cell subpopulation-CD4 or CD8-that is activated.

Antibodies to carcinogen-DNA adducts in mice chronically exposed to polycyclic aromatic hydrocarbons.

Antibodies specific for polycyclic aromatic hydrocarbon (PAH)-DNA adducts have previously been reported in human sera. In this study, we examined the association between mixed PAH exposure and PAH-DNA adduct specific antibodies in BALB/c mice. Mice were treated either by i.p. injection or by intragastric (i.g.) intubation with a mixture of seven different PAHs [benzo(a)pyrene (BP), benz(a)anthracene (BA), fluoranthene (FA), dibenz(a,h)anthracene (DBA), 3-methyl-cholanthrene (MC), chrysene (Ch), benzo(b)fluoranthene (BF)] at three doses (0, 15, 150 micrograms of each PAH) twice a week for 8 weeks. Sera were screened by direct ELISA for antibodies recognizing DNA modified by diolepoxides or epoxides of each PAH injected. In i.p. treated mice, the sera were slightly more reactive to DNAs modified with diolepoxides of BP, BA, or Ch or an epoxide of DBA than to unmodified DNA. In i.g. treated mice, the sera were more reactive to DNAs modified with diolepoxides of BA or BF than to unmodified DNA. For some PAHs, a dose-response effect was observed between sera reactivity to PAH metabolites and the dose of PAH administered. However, there was considerable variation in the immune responses among individual mice within each treatment group. When tested by competitive ELISA, none of the sera could discriminate between modified and unmodified DNA. This animal study suggests that an assessment of previous carcinogen exposure by measuring DNA adduct-specific antibodies requires further validation prior to its application to the human monitoring of carcinogen exposure.

Immunologic measurement of polycyclic aromatic hydrocarbon-albumin adducts in foundry workers and roofers.

Roofers and iron foundry workers with high exposure to polycyclic aromatic hydrocarbons (PAH) were monitored for levels of covalent PAH serum albumin adducts, quantitated in enzymatically digested samples by a sensitive competitive enzyme-linked immunosorbent assay. Albumin adducts were higher in the foundry workers (5.22 fmol/micrograms, 0.314 mmol/mol) than in the reference group (4.07 fmol/micrograms, 0.245 mmol/mol), but only of borderline significance probably due to the small sample size. In a subset of foundry workers, a significant difference in adduct levels was observed for samples collected immediately after vacation and after six weeks of workplace exposure. The roofers also showed higher levels of adducts (5.19 fmol/micrograms, 0.312 mmol/mol) than their reference group (3.28 fmol/micrograms, 0.197 mmol/mol). These results demonstrate the feasibility of PAH protein adduct measurement as a marker of human exposure to this class of chemicals.

Postlabeling and immunoassay analysis of polycyclic aromatic hydrocarbons--adducts of deoxyribonucleic acid in white blood cells of foundry workers.

Blood samples were obtained from volunteers who were occupationally exposed to polycyclic aromatic hydrocarbons in a Finnish iron foundry and from referents not known to be occupationally exposed to this class of chemical carcinogens. Aromatic adducts were determined in the deoxyribonucleic acid of white blood cells from the exposed workers with the 32P-postlabeling and immunologic techniques. There was a correlation between the estimated exposure in a particular job and the adduct levels. Jobs of men with high adduct levels (greater than 1 adduct/10(7) nucleotides in the postlabeling assay) included sand preparation, molding, shake-out, and transport. The adduct levels were low in men in pattern making, melting, and fettling. This study suggests that 32P-postlabeling and immunoassay may be useful in monitoring human exposure to known and previously unidentified environmental genotoxic agents.

Molecular mechanics and antibody binding in the structural analysis of polycyclic aromatic hydrocarbon-diol-epoxide--DNA adducts.

Analysis of polycyclic aromatic hydrocarbon (PAH)-DNA adducts using monoclonal antibodies raised against DNA that had been modified with (+-)-r-7-,t-8-dihydroxy-t-9,10-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene in an enzyme-linked immunosorbent assay, as well as analysis using human serum antibodies and antibodies raised in laboratory animals, have suggested the presence on these adducts of both common and unique immunological epitopes. The molecular mechanics studies reported here establish a model for the analysis of PAH-DNA adducts through the identification of energetically favored binding conformations and they further reveal structural alterations in DNA due to the presence of carcinogen adducts. The data explain the antibody reactivity patterns by defining different molecular presenting surfaces that are available for antibody binding. The preferred orientation of the aromatic portions of the adducts, which align either 3' or 5' in the minor groove, were found to be correlated with antibody reactivity patterns. Examination of the topographical characteristics of the adducts facilitated correlation of adduct-antibody recognition and adduct presenting surface. Significant differences were found between benzo[a]pyrene-diol-epoxide (BPDE)-DNA adducts, which align 5' in the minor groove, and benz[a]anthracene-diol-epoxide (BADE)-DNA and dibenz[a,c]anthracene-diol-epoxide-DNA adducts, which align 3' within the minor groove. Chrysene-diol-epoxide-DNA adducts were found to have only a weak preference for 5' alignment and therefore share topographical characteristics with both BPDE-DNA and BADE-DNA adducts.

Immunologic methods for the detection of carcinogen adducts in humans.

Monoclonal antibodies have been developed which recognize a number of carcinogen-DNA and protein adducts. These antibodies can be used in highly sensitive competitive enzyme linked immunosorbent assays (ELISA) to detect femtomole levels of adducts in human samples. With the most sensitive antibodies, DNA adducts in the range of 1/10(8) nucleotides can be measured. In addition, antibodies to DNA adducts can be used to investigate immunohistochemically the localization of adducts in specific cell and tissue types. Antibodies recognizing benzo(a)pyrene diol epoxide-DNA have been used to monitor adducts in white blood cell DNA of foundry workers and placental and white blood cell DNA of smokers and nonsmokers. Because of antibody crossreactivity with structurally related adducts of other polycyclic aromatic hydrocarbons, this assay is not specific for benzo(a)pyrene adducts. Antibodies to the stable guanine imidazole ring opened aflatoxin-B1-DNA adduct have been used to detect elevated levels of adducts in liver tissue from Taiwanese hepatocellular cancer patients. Monoclonal antibodies against 8-methoxypsoralen-DNA have been used to monitor adducts in psoriasis and cancer patients treated with psoralen plus UVA light. These patients have also served as model systems for the development of immunofluorescence methods for adduct detection. Immunohistochemical staining of skin biopsies from psoriasis patients demonstrated specific staining of epidermal cells. With further increases in sensitivity, this method should be applicable to the detection of adducts in other human tissues. Adduct detection in humans is now established as a viable method for determination of exposure to certain chemical carcinogens. However, the relationship of adduct measurements to individual risk requires further investigation.

Detection and characterization of human serum antibodies to polycyclic aromatic hydrocarbon diol-epoxide DNA adducts.

The presence of serum antibodies to the diol-epoxide DNA adducts of representative polycyclic aromatic hydrocarbons (PAH), chrysene, benz[a]anthracene and benzo[a]pyrene, was determined by ELISA using serum samples obtained from normal healthy individuals. Antibodies that reacted against PAH adducted-DNA, but not against PAH-adducted protein, were found in the serum of approximately 40% of the test individuals. Specificity analysis of the antibodies demonstrated that serological cross-reactions between the benzo[a]pyrene and the chrysene diol-epoxide adducts were present. Similar cross-reactivity between the benz[a]anthracene and the chrysene adducts was observed. Sera containing antibodies that were apparently specific for each of the three PAH-DNA adducts were also identified. The presence of antibodies to PAH-DNA adducts indicates both past exposure to these carcinogenic PAH and their metabolic activation to the DNA damaging metabolites. These antibodies may prove to be useful in both retrospective and prospective epidemiological studies of various diseases associated with PAH exposure.

The application of immunoassays and fluorometry to the detection of polycyclic hydrocarbon-macromolecular adducts and anti-adduct antibodies in humans.

The metabolic activation of polycyclic aromatic hydrocarbons (PAH) to chemical species that form covalent adducts with cellular macromolecules (DNA and protein) is central to theories of carcinogenesis. Assays are currently being developed that will accurately reflect human macromolecular exposure to these carcinogens. Immunoassays are capable of detecting low levels of PAH-DNA adducts and antibodies directed against these adducts in humans and HPLC/spectrophotofluorimetry allows the detection of carcinogen-DNA or carcinogen-protein adducts in human peripheral blood. Both types of method have inherent advantages and disadvantages, and the use of more than one type of corroborative assay is a feature in our work. Simplified but highly specific synchronous fluorescence spectra have been obtained for BP-tetrols after mild acid hydrolysis and HPLC of sample materials. When using a wavelength difference of 34 nm to drive the excitation and emission monochromators simultaneously, the pyrene fluorophore, when present, has a signature peak at 345 nm (excitation). The results of immunoassays demonstrate human exposure to PAH as a class of carcinogen, since serological cross-reactivity of antibodies does not limit detection in this system to a single chemical compound. In addition the formation in humans of anti-PAH-DNA antibodies has been shown, presumably in response to both past and present exposure to the parent compounds. In summary the results of each assay can indicate human exposure to PAH and have the potential for molecular dosimetry of this exposure.