The evidence of clonal evolution with monosomy 7 in aplastic anemia following granulocyte colony-stimulating factor using the polymerase chain reaction

The polycyclic aromatic hydrocarbons (PAH) containing fractions of smoked and charcoal-broiled foods, namely, Sheat fish (Kytopterus apogon), Mimrow (Crossocheilus reba), Freshwater catfish (Clarias batrachus), chicken wings, rice pork sausage and pork, in addition to naphthalene, acenaphthene, anthracene, phenanthrene, fluoranthene, pyrene, benz[a]anthracene, naphthacene, benzo[a]pyrene, benzo[e]pyrene, 9,10-dimethyl-1,2-benzanthracene, dibenz[ah]anthracene, benzo[ghi]perylene and coronene, were evaluated for their mutagenic potential using Salmonella typhimurium strains TA98 and TA100 in the absence of metabolic activation after being treated with nitrite (500 mM) for 4 hr at 37 degrees C and in acid solution pH 3.0-3.5. The presence of N-nitroso compounds was also determined. Results showed that nitrite could convert most samples to direct-acting mutagens towards both strains except for fluoranthene and benzo[ghi]perylene, which exhibit mutagenicity only with TA98. It was demonstrated that treatment of PAHs with nitrite in acid solution produced some non-N-nitroso direct-acting mutagens, suggesting that they might belong to nitro-PAHs. Therefore, the consumption of charcoal-broiled and smoked foods simultaneously with nitrite is not recommended.     

Ability of 16 priority PAHs to be photocytotoxic to a cell line from the rainbow trout gill

Sixteen polycyclic aromatic hydrocarbons (PAHs) were screened for their ability to be photocytotoxic to a cell line from the rainbow trout gill, RTgill-W1. PAHs could be divided into one of three groups: incapable of being photocytotoxic, able to be both photocytotoxic and directly cytotoxic, or capable of being only photocytotoxic. Photocytotoxicity was distinct from direct cytotoxicity in that EC50 values were lower with the neutral red assay immediately after the PAH/UV treatment than with alamar Blue or CFDA-AM, indicating a more specific action on lysosomes. As well, in photocytotoxicity but not in direct cytotoxicity, the three assays showed increased impairment 24 h after treatment. Most PAHs were found to be strictly photocytotoxic; however, only six compounds were photocytotoxic at concentrations theoretically achievable in water. When photocytotoxic PAHs were ranked relative to fluoranthene to establish fluoranthene equivalent factors (FEFs), benzo[a]pyrene and benzo[g,h,i]perylene were found to be most potent. However, when the water solubility of each compound was taken into account in order to calculate the potential environmental photocytotoxic potency (PEPP), fluoranthene and pyrene appeared to have the most potential to impact fish through photocytotoxicity.     

Ceranapril and cerebral blood flow autoregulation

In order to investigate the levels of the polycyclic aromatic hydrocarbons, mainly benzo[a]pyrene because of its carcinogenicity, 55 samples of smoke flavour and smoked foods were analysed. The samples tested included 11 samples of liquid smoke flavour and 44 samples of smoked foods like bacon, loin, turkey, sausage, ox rib, etc. from different brands. A liquid chromatographic method was developed using a fluorescence detector. Benzo[a]pyrene was found in 73% of the liquid smoke flavour samples analysed. The levels varied from 0.1 to 336.6 micrograms/kg. Three liquid smoke flavour samples showed levels of benzo[a]pyrene above the maximum level recommended by FAO/WHO (10 micrograms/kg). From the total of 44 smoked food samples analysed, benzo(a)pyrene was detected in 23 samples (52%). The levels varied from 0.1 to 5.9 micrograms/kg. Anthracene and fluoranthene, non-carcinogenic polycyclic aromatic hydrocarbons, were found in almost all the samples analysed. Benzo[ghi]perylene, 3,4-benzofluoranthene and 1,2,3,4-dibenzopyrene were not found in any of the 55 samples analysed.     

Polycyclic aromatic hydrocarbons (PAH) and diesel engine emission (elemental carbon) inside a car and a subway train

Significant concentrations of potentially harmful substances can be present in the interior of vehicles. The main sources of PAHs and elemental carbon (EC) inside a car are likely to be combustion emissions, especially from coal and traffic. The same sources can also be important for the interior of a subway train for which there are specific sources in the tunnel system, for example diesel engines. Twice, in summer 1995 and winter 1996 polycyclic aromatic hydrocarbons (PAH) and diesel motor emission (estimated as elemental carbon) were determined in the interior of a car (a 2-year-old VW Golf with a three-way catalytic converter) and in the passenger compartment of a subway train (below ground). On each sampling day (in total 16 daily measurements in the car and 16 in the subway) the substances were determined in the breathing zone of the passengers from 07:00 h to 16:00 h under different meteorologic conditions (winter- and summertime). The car followed the route of the subway from the western Berlin borough of Spandau to the south-eastern borough of Neuk?lln, and back. The sampling represented a realistic exposure model for driving in a high traffic and polluted urban area. The electric subway train (also 2 years in use) connected the same parts of Berlin (31 km underground). The mean values obtained during the two measurement periods (summer/winter) inside the car were 1.0 and 3.2 ng/m3 for benzo[a]pyrene, 10.2 and 28.7 ng/m3 for total-measured-PAHs, 14.1 and 8.2 micrograms/m3 for EC and in the subway 0.7 and 4.0 ng/m3 for benzol[a]pyrene, 30.2 and 67.5 ng/m3 for total PAHs, 109 and 6.9 micrograms/m3 for EC. A comparison between subway and car exposures shows significantly higher concentrations of PAHs in the subway train, which can be explained by relatively high concentrations of fluoranthene and pyrene in the subway. So far a satisfactory explanation has not been found, but one source might be the wooden railway ties which were formerly preserved with tar based products. In wintertime in both transportation systems the concentrations of beno[a]pyrene are three to four times higher than in summer corresponding to the changing of the ambient air concentrations.     

Detoxification of optically active bay- and fjord-region polycyclic aromatic hydrocarbon dihydrodiol epoxides by human glutathione transferase P1-1 expressed in Chinese hamster V79 cells

Dihydrodiol epoxides (DEs) are important carcinogenic metabolites of polycyclic aromatic hydrocarbons (PAHs). The metabolic formation of four stereoisomeric DEs (a pair of optically active diastereomers termed as syn- and anti-form) is possible. Glutathione tranferases (GSTs) have been demonstrated to catalyze the detoxification of DEs. Purified GSTs display remarkable differences in catalytic efficiencies towards bay- and fjord-region DEs along with a high degree of regio- and stereoselectivity. Here we determined to which extent heterologously expressed human GSTP1-1, a major GST isoform in lung, affects the mutagenicity of stereoisomeric bay-region DEs of benzo[a]pyrene in Chinese hamster V79 cells. To evaluate the influence of sterical crowding in the substrate on the activity of GSTP-1, the study was extended to the strongly mutagenic fjord-region (-)-anti-DEs of benzo[c]phenanthrene and dibenzo[a,l]pyrene. GSTP1-1,reduced preferentially the mutagenicity (studied at the hprt locus) of (+)-anti and (+)-syn-DEs of benzo[a]pyrene (by 66 and 67%) as compared with the corresponding (-)-anti- and (-)-syn-enantiomers (by 15 and 13%). These results are in line with previous studies on the enantioselectivity of purified GSTP1-1 towards the DE isomers of benzo[a]pyrene and benzo[c]phenanthrene showing that enantiomers with (R)-configuration at the benzylic oxiranyl carbon are better substrates than those with (S)-configuration. Interestingly, the (-)-anti-DEs of benzo[c]phenanthrene and dibenzo[a,l]pyrene were efficiently detoxified by GSTP-1-1 in the constructed cell line (reduction of mutagenicity by 66 and 64%). This study demonstrates that differences in the caalytic activity seen for purified GST towards individual mutagens do not necessarily reflect the detoxification of DEs by the same enzyme in a living cell and provides further evidence that specific human GSTs play a role in the detoxification of DEs of PAHs.     

Characteristics and Reactivity of Algae-Produced Dissolved Organic Carbon

Algae (green, blue–green, and diatom) grown in inorganic media produced particulate and dissolved organic carbon (DOC). DOC produced by a green-alga contains 25% hydrophobic acids. DOC from all algae had specific ultraviolet absorbance values less than 2.0?m?1?(mg/L)?1. Algae-produced DOC was biologically labile; greater than 60% degraded in bioreactors within 5 days. The biodegradable material likely included carbohydrates, amino acids, and amino sugars, which were present in hydrophobic acid isolates. Chlorination of algal DOC formed disinfection by-products; DOC from the green alga, Scenedesmus quadricauda, produced chloroform [0.53?micromole?per?mg?carbon?(μmol/mg?C)], dichloroacetic acid (0.27?μmol/mg?C), and trichloroacetic acid (0.14?μmol/mg?C). This work complements other studies, which focused on algal total organic carbon (DOC and cellular material), and clearly demonstrates the importance of identifying algae-derived sources of DOC in water supplies and removing such DOC in water treatment plants prior to chlorination.     

Exposure to polycyclic aromatic hydrocarbons in occupational versus urban environmental air

OBJECTIVES: To evaluate the balance between occupational and environmental exposure to suspended particulate matter (SPM) and polycyclic aromatic hydrocarbons (PAHs), comparison measurements were performed in a coal-fired power plant and the urban atmosphere from the town nearby. METHODS: The analysis of SPM for PAH content was done according to a high-performance liquid chromatography (HPLC)-based method. The microscopic assessment was performed using scanning electron microscopy (SEM) by silver coverage of the samples derived by air filter. RESULTS: Contrary to expectations, the results showed low levels of particle-bound PAHs in the occupational environment (< 1 ng benzo(a)pyrene/m3 air) and high levels in urban air (range 80-1250 ng benzo(a)pyrene/m3). The SPM collected from the power plant exhibited non-respirable characteristics (particles larger than 10 microm), whereas urban SPM almost exclusively contained respirable airborne particles (<3 microm). CONCLUSIONS: The PAH burden, combined with the enhanced probability of respiratory absorption, confers a much greater hazard potential to the urban SPM. Under these conditions, in areas or countries in which old technologies remain in use, occupational exposure to SPM containing PAHs might represent a severe underestimation of the total risk as it does not take into account the background air pollution.     

Long-term decline of atmospheric and marine pollution by polycyclic aromatic hydrocarbons (PAHS) in Germany

Concentrations of benzo[a]pyrene and benzo[e]pyrene in the atmosphere as markers for the class of PAHs decreased by about 70% within one decade in clean air as well as in industrially polluted areas of Germany when measured with passive samplers (spruce sprouts, poplar and beech leaves). The same trend has been found for East-Germany during 1991-1995. Mussels (Mytilus edulis) were found to accumulate PAHs from the aquatic environment and exhibited a seasonal periodicity of the PAH concentration. After an initial decline from 1985 to 1990, the PAH concentration remained constant until 1995 in the North Sea area investigated.     

Adjuvant activities of pyrene, anthracene, fluoranthene and benzo(a)pyrene in production of anti-IgE antibody to Japanese cedar pollen allergen in mice

We have previously demonstrated that pyrene in diesel-exhaust particles (DEP) has an adjuvant activity on immunoglobulin E (IgE) antibody production in mice immunized with Japanese cedar pollen allergen (JCPA) or ovalbumin (OA) intraperitoneally. The present study is concerned with the adjuvant activity in IgE antibody production against JCPA of pyrene or DEP inoculated intranasally in mice. We show that anthracene, fluoranthene and benzo(a)pyrene in DEP have the ability to enhance anti-JCPA IgE antibody production in mice by intranasal immunization. Mice were grouped, immunized with 10 micrograms of JCPA plus 400 micrograms of pyrene, 10 micrograms of JCPA plus 100 micrograms of DEP, 10 micrograms of JCPA plus 2 mg of aluminum hydroxide and 10 micrograms of JCPA alone intranasally 7 times at 2 week intervals. Mice were also grouped, and immunized with JCPA (10 micrograms) plus 40 micrograms of anthracene, JCPA (10 micrograms) plus 400 micrograms of fluoranthene, JCPA (10 micrograms) plus 40 micrograms of benzo(a)pyrene, and JCPA (10 micrograms) plus 400 micrograms of pyrene and JCPA (10 micrograms) alone. We found that the IgE antibody responses to JCPA in mice immunized with JCPA plus pyrene, JCPA plus DEP or JCPA plus the three chemical organic compounds mentioned above were significantly enhanced compared with those immunized with JCPA alone. In addition, when the intraperitoneal macrophages obtained from the normal mice (unimmunized mice) were incubated with pyrene, anthracene, fluoranthene or benzo(a)pyrene in vitro, an enhanced chemiluminescence (CI) response and interleukin-1 alpha (IL-1 alpha) production of the macrophages was observed in each instance. These results suggest that in the production of IgE antibody to JCPA the adjuvancy of polycyclic aromatic hydrocarbons (PAHs) in DEP may be important in an attack of Japanese cedar pollinosis.     

Cyclodextrin-aided capillary electrophoretic separation and laser-induced fluorescence detection of polynuclear aromatic hydrocarbons (PAHs)

Two neutral cyclodextrins (CDs), hydroxypropyl-beta-CD (HP beta OD) and methyl-beta-CD (M beta CD), and two negatively charged forms, carboxymethyl-beta-CD (CM beta CD) and sulfobutylether-beta-CD (SB beta CD), were used to demonstrate the principle of separation of hydrophobic and non-charged polynuclear aromatic hydrocarbons (PAHs) by capillary electrophoresis (CE) based on differential partitioning of analytes between the CDs. The estimation of the partition coefficient (Ki) confirmed that the PAH components which partitioned most to the negative cyclodextrin (i.e. with the highest Ki) exhibited the longest migration time. The Ki values obtained for the CM beta CD-HP beta CD system are all below 1, indicating that the PAHs prefer to remain in the neutral HP beta CD. The Ki values for the SB beta CD-M beta CD buffer are all greater than 1, and cover a wider range, indicating preference of the PAHs for the anionic derivative. Methods were applied for separation of a PAH mixture containing various important PAHs on the US Environmental Protection Agency priority list. This novel procedure provided much better separation of PAH isomers, including benzo[a]pyrene and benzo[e]pyrene, than has been reported previously using CE. The system was applied to the sensitive determination of nanomolar levels of PAHs in contaminated soil.     

Lack of response of the rat liver "class 3" cytosolic aldehyde dehydrogenase to toxic chemicals, glutathione depletion, and other forms of stress

One of the rat liver "Class 3" cytosolic aldehyde dehydrogenases (EC 1.2.1.3), ALDH3c, is known to be markedly induced by polycyclic aromatic hydrocarbons and 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD; dioxin). In the present study we examined whether hepatic ALDH3c induction is a general response to toxicity. Treatment of Wistar rats for 4 days with known toxic doses of hepatotoxic agents--carbon tetrachloride, dimethylnitrosamine, diethylnitrosamine, aflatoxin B1, and D-ethionine--did not induce ALDH3c enzyme activity. Whereas dimethylaminoazobenzene at 100 mg/kg/day for 4 days did not increase ALDH3c, a 10-fold lower dose of dimethylaminoazobenzene for 4 days produced a 20-fold increase in ALDH3c activity. Treatment with phorone, diethylmaleate or L-buthionine-S,R-sulfoximine--which deplete reduced glutathione (GSH) by different mechanisms--did not affect ALDH3c activity. One dose of benzo[a]pyrene for 24 hr increased ALDH3c activity by 25-fold. Treatment with both the GSH-depleting chemicals and benzo[a]pyrene inhibited ALDH3c induction by 45% to 75%, suggesting a role for GSH during ALDH3c induction. After ALDH3c activity had already been induced by benzo[a]pyrene, however, the GSH-depleting chemicals did not affect ALDH3c activity. No changes in ALDH3c activity were seen 24 or 48 hr after partial hepatectomy, on the fifth day following surgical cholestasis, or after guanethidine-induced sympathectomy. These data indicate that hepatic ALDH3c inducibility in the rat is not a general or direct response to chemical toxicity, or to conditions of GSH depletion or other forms of stress.     

Food poisoning and infections in 1992

The concentration of heavy metals and polycyclic aromatic hydrocarbons (PAH) were determined in the soils obtained from various traffic roads in Cracow including surroundings of steel works. The method of atom absorption spectrometry was using to determination of Ca, Mg, Pb, Fe, Zn, Cd, Cu. PAH (fluoranthene, pyrene, benz(a)anthracene + chryzene, benz(a)pyrene, benz(ghi)perylene, fenanthrene and perylene) were determined by gas chromatography. The highest concentration of heavy metals was found in zone of steel works. A steep fall concentration of Fe was observed in the soils with increasing distance from the works. It seems that the variety in concentration of metals don't depend only on vehicular traffic. The highest mean PAH concentration exceeding 800 micrograms/kg of dried soils was found in soil samples taken from roads where the traffic is the highest.     

Immediate and Time-Dependent Compression of Tire Derived Aggregate

This paper examines immediate and time-dependent compression of tire derived aggregate (TDA) and TDA-soil composites. To accommodate large particle sizes, modified experimental devices were developed and used to test tire chips and tire shreds. Immediate compression of TDA, which results almost entirely from the reduction of pore volume, increases with TDA content and tire particle size. The secant constrained modulus (Msec) of TDA defined over the stress range of 0–50?kPa varied from a low of 255?kPa (100% tire shreds) to a high of 1,320?kPa (50% tire chips). A characteristic relationship between strain and time exists for TDA and TDA composites under one-dimensional confined compression. Time-dependent deformation is well described by the modified secondary compression index (Cαε), which ranged from 0.0010 (50% tire chips) to 0.0074 (100% tire chips). Time-dependent deformation was inversely proportional to sand content, with the most significant changes resulting from the addition of 15% sand. Both applied stress and tire particle size appear to have a negligible effect on time-dependent compression of TDA. Based on the findings of this study it is recommended that practitioners assess time-dependent settlement when designing a TDA structure and if necessary incorporate design features to accommodate these settlements.     

Elution of benzo[alpha]pyrene from carbon particles in the respiratory tract of mice

The effect of carrier particle size on the rate of dissociation of benzo[alpha]pyrene (BaP) from carrier particles deposited in the respiratory tract of mice was studied. BaP-coated carbon particles (in two size ranges, 0.5-1.0 and 15-30 mum) plus 103Ru-tagged carbon tracer particles were intratracheally instilled in mice. The clearance of carbon particles and the simultaneous rate of elimination of BaP from the respiratory tract was measured. BaP adsorbed to 15- to 30-muM carbon particles was eliminated from the lung at essentially the same rate as the carbon particles were cleared. In contrast, BaP adsorbed to 0.5- to 1.0-muM carbon particles was eliminated from the lung approximately 4 times faster than the carbon particles were cleared. The persistence of carcinogens and their rates of elution from carrier particles are discussed in relation to the pathogenesis of lung cancer in animals treated with carcinogen-carrier particle preparations.     

Trace elements in human scalp hair and soil in Irian Jaya

Benzo[a]pyrene (BaP) and other polycyclic aromatic hydrocarbons (PAHs) which are present in cigarette smoke, are common air and food genotoxic contaminants and possible human carcinogens. We measured the following PAH levels: benzo[a]anthracene, benzo[b]fluoranthene, benzo[k]fluoranthene, BaP, dibenzo[a,h]anthracene, benzo[g,h,i]perylene as well as (+/-) syn and anti BaP diol-epoxide (BPDE) DNA adducts in autopsy samples from the lungs of non-smokers, ex-smokers and smokers who had lived in Florence, Italy. PAH levels in lung tissue were similar in all groups, with the exception of dibenzo[a,h]anthracene (DBA), which was higher in lung samples from smokers (n = 10, 0.18+/-0.17 ng/g d.w, mean +/- S.D.) compared to non-smokers (n = 15, 0.046+/-0.025 ng/g d.w) (P < 0.05), whereas ex-smokers (n = 5), had intermediate levels (0.07+/-0.03 ng/g d.w). The average level of total BPDE-DNA adducts was 4.46+/-5.76 per 10(8) bases in smokers, 4.04+/-2.37 per 10(8) in ex-smokers and 1.76+/-1.69 per 10(8) in non-smokers. The levels of non-smokers were significantly different (P < 0.05) from the levels of the smokers and ex-smokers combined. Total BPDE-DNA adducts were correlated with BaP levels in the lung samples in which both determinations were obtained (r = 0.63). Our results demonstrate that the biological load of PAHs due to environmental pollution is similar in individuals who smoke and those who do not, but BPDE-DNA adducts are higher in smokers and ex-smokers compared to non-smokers. This study further confirms the usefulness of BPDE-DNA adduct levels determination in the lungs from autopsy samples for monitoring long-term human exposure to BaP, a representative PAH.     

Effect of polycyclic aromatic hydrocarbons on the elimination kinetics of pyrene and the urinary excretion profile of 1-hydroxypyrene in the rat

Pyrene was chosen as a noncarcinogen model of polycyclic aromatic hydrocarbons (PAHs). Groups of male Wistar rats were dosed with pyrene and with mixture of pyrene and fluoranthene, pyrene and benz[a]anthracene, or pyrene, fluoranthene, and benz[a]anthracene at 20 mg/kg by intravenous or oral routes. Blood samples were taken at 0.25, 0.5, 1, 2, 3, 4, and 5 h after administration. The concentration of pyrene was determined by gas chromatography. The toxicokinetic parameters for pyrene were determined from the time course of blood concentration. A significant increase in the bioavailability of pyrene after treatment with other PAHs was observed. Urinary 1-hydroxypyrene excretion was analyzed after pretreatment with acenaphthene, naphthalene, chrysene, phenanthrene, benz[a]anthracene, and benzo[a]pyrene. The urine from rats was collected for 3 d and the concentration of 1-hydroxypyrene was determined using high-performance liquid chromatography (HPLC). Most compounds examined caused a decrease in the urinary excretion of the metabolite of pyrene.     

cDNA cloning, sequence analysis, and induction by aryl hydrocarbons of a murine cytochrome P450 gene, Cyp1b1

C3H mouse embryo fibroblast cells, designated 10T1/2, can be transformed by physical and chemical agents including polycyclic aromatic hydrocarbons. In a previous report (Shen et al., Proc. Natl. Acad. Sci. USA 90, 11483-11487, 1993), we identified a cytochrome P450 gene induced by polycyclic aromatic hydrocarbons (PAHs) that is different from 1A1 or 1A2, and which we tentatively named P450CMEF. Here, we report the entire cDNA sequence of P450CMEF (5,128 bp) and the amino acid sequence deduced from it (543 residues). A comparison of the latter sequence with known cytochrome P450s indicates that P450CMEF is in a new subfamily of family 1 of the P450 superfamily. Accordingly, the Committee on Standardized Cytochrome P450 Nomenclature designated the gene Cyp1b1. Exposure to various aryl hydrocarbons (2.5 hr) induced Cyp1b1 mRNA in 10T1/2 cells to different degrees: 2,3,7,8-tetrachlorodibenzo-p-dioxin, 7,12-dimethylbenz[a]anthracene, benz[a]anthracene, benzo[a]pyrene, and beta-naphthoflavone were strong inducers; alpha-naphthoflavone and 3-methylcholanthrene, were moderate inducers; and benzo[e]pyrene was a weak inducer.     

Activated Carbon Addition to a Submerged Anaerobic Membrane Bioreactor: Effect on Performance, Transmembrane Pressure, and Flux

This study examined the effect of the addition of activated carbon to three, 3 L submerged anaerobic membrane bioreactors (SAMBRs) in terms of chemical oxygen demand (COD) removal, flux, and transmembrane pressure (TMP). The feed was a synthetic substrate with a COD of 460?mg?L?1, with one reactor run as a control, one with 1.7?g?L?1 of powdered activated carbon (PAC), and the third with 1.7?g?L?1 of granular activated carbon (GAC). While COD removal was high in all reactors (>90%), in comparison to the control (SAMBR1), the average COD removal in SAMBR2 (PAC) increased by 22.4%, while SAMBR3 with GAC was not significantly better. Because PAC has a significantly greater surface area per mass than GAC, it is probable that this difference was primarily due to the greater absorbance of fine colloidal particles and high molecular weight organics onto the carbon surface. These effects manifested themselves by SAMBR2 having lower TMPs and higher fluxes than both SAMBR3 and SAMBR1. Volatile fatty acids in the effluent from all three SAMBRs were extremely low (<18?mg?L?1), even during step changes in hydraulic retention tune, and most of the soluble COD in the effluent was soluble microbial products. Biochemical methane potential assays showed that biomass in the SAMBRs was less active than the seed sludge, and it appears that the addition of activated carbon to Reactors SAMBR2 and SAMBR3 provided a solid support for growth, and hence reduced floc breakage.     

Adsorption of Polycyclic Aromatic Hydrocarbons in Aged Harbor Sediments

Polycyclic aromatic hydrocarbons (PAHs) are a group of hydrophobic organic contaminants which have low aqueous solubilities and are common pollutants in harbor sediments. Adsorption and desorption isotherms for PAHs are conducted to study the abiotic sorption of PAHs in uncontaminated harbor sediments in contact with the natural overlaying water. Representative 2-, 3-, and 4-ring PAHs are used to obtain PAH adsorption/desorption data. Linear adsorption onto sediment is obtained for the following PAHs: Naphthalene and 2-methyl naphthalene (2 ring), acenaphthene, anthracene, and phenanthrene (3 ring), and fluoranthene and pyrene (4 ring). Linear adsorption is followed by a significant hysteresis in desorption from sediment, due to strong retention by the aged sediment organic carbon. Sediment organic carbon–water partition coefficients (log?Koc) for the seven PAHs range from 2.49 to 4.63. Based on the sorption data for these representative PAHs, sediment organic carbon–water partition coefficients may be predicted for other PAH compounds, particularly the less soluble and the more hydrophobic PAHs (5 or more rings).     

Treatment of Aluminum Plant Hazardous Wastes Containing Fluorides and PAH

Aluminum industry wastes are solid residues contaminated with polycyclic aromatic hydrocarbons (PAHs) and fluorides. The aluminum industry waste used in this study contained 1,129?mg?kg?1 of benzo(b,j,k)fluoranthene. On application of toxicity characteristic leaching procedure (TCLP), a leachate containing 448?mg?L?1 of fluoride ions was obtained. The decontamination of aluminum industry wastes was carried out in cycles and included a stage of flotation, followed by stabilization and neutralization. The flotation treatment in the cell containing wastes contaminated with a concentration of 15% (w?v?1) in the presence of surfactant cocamydopropyl hydroxysultaine (0.25% w?w?1) allowed 47 to 83% removal of benzo(b,j,k) fluoranthene. The subsequent step of lime stabilization (8% w?v?1) allowed production of nonhazardous wastes. The concentration of fluoride ions resulting from the TCLP test (67?mg?L?1) remained lower than the permissible level (150?mg?L?1).