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PAHs

The synthesis of PAHs is generally thought not to occur within the clouds themselves, but in the envelopes of old carbon-rich stars. These stars possess large envelopes in which material expands outward and cools as it expands. In the inner [Pg.36]


Esaulov A V 1986 Electron detachment from atomic negative ions Ann. Phys., Pahs 11 493-592... [Pg.823]

Ireland J F and Wyatt PAH 1976 Acid-base properties of electronically excited states of organic molecules Adi/. Rhys. Org. Chem. 12 131-221... [Pg.2969]

Chesnoy J and Gale G M 1984 Vibrational energy relaxation in liquids Ann. Phys., Pahs 9 893-949... [Pg.3049]

Stabilizing resonances also occur in other systems. Some well-known ones are the allyl radical and square cyclobutadiene. It has been shown that in these cases, the ground-state wave function is constructed from the out-of-phase combination of the two components [24,30]. In Section HI, it is shown that this is also a necessary result of Pauli s principle and the permutational symmetry of the polyelectronic wave function When the number of electron pairs exchanged in a two-state system is even, the ground state is the out-of-phase combination [28]. Three electrons may be considered as two electron pairs, one of which is half-populated. When both electron pahs are fully populated, an antiaromatic system arises ("Section HI). [Pg.330]

In this work, relativistic effects are included in the no-pah or large component only approximation [13]. The total electronic Hamiltonian is H (r R) = H (r R) + H (r R), where H (r R) is the nom-elativistic Coulomb Hamiltonian and R) is a spin-orbit Hamiltonian. The relativistic (nomelativistic) eigenstates, are eigenfunctions of R)(H (r R)). Lower (upper)... [Pg.452]

We briefly summarize what we found in this Nj = 5 case We revealed six different contours that led to the sign flip of six (different) pahs of functions and one contour that leads to a sign flip of all four functions. The analysis of Eq. (87) shows that indeed we should have seven different cases of sign flip and one case without sign flip (not surrounding any conical intersection). [Pg.675]

Fig. 20. Improved packing parameters ( ) for liquid mass transfer (a) ceramic Raschig rings (b) metal Raschig rings (c) ceramic Bed saddles (d) metal PaH... Fig. 20. Improved packing parameters ( ) for liquid mass transfer (a) ceramic Raschig rings (b) metal Raschig rings (c) ceramic Bed saddles (d) metal PaH...
Euture Prospectsfor the Tine Chemicals Business, ECOPLAN Int., Pahs, 1992. [Pg.442]

Polycychc aromatic hydrocarbons (PAHs) are carcinogens produced by the thermal breakdown of organic materials. These are widely distributed in both food and the environment, and are some of the principal carcinogens in cigarette tar and air pollution. Of over 20 PAHs isolated, benzopyrene and quinoline compounds are the most commonly encountered in foods, particularly those which are broiled or fried (111). Shellfish living in petroleum contaminated waters may also contain PAHs (112). [Pg.481]

Epidemiologic studies in Japan indicate an increased risk of stomach cancer owing to consumption of broiled fish and meats (116). In the United States, stomach cancer incidence has steadily declined since the 1940s, whereas consumption of broiled food has increased (108). In addition, the average human intake of PAHs is only 0.002 of that required to produce cancer in half of animals fed. Test results are often contradictory (117) and many components of food, such as vitamin A, unsaturated fatty acids, thiols, nitrites, and even saUva itself, tend to inhibit the mutagenic activity of PAHs (118—120). Therefore, the significance of PAHs in the human diet remains unknown (121,109). [Pg.481]

Fig. 2. Overall schematic of solid fuel combustion (1). Reaction sequence is A, heating and drying B, solid particle pyrolysis C, oxidation and D, post-combustion. In the oxidation sequence, left and center comprise the gas-phase region, tight is the gas—solids region. Noncondensible volatiles include CO, CO2, CH4, NH, H2O condensible volatiles are C-6—C-20 compounds oxidation products are CO2, H2O, O2, N2, NO, gaseous organic compounds are CO, hydrocarbons, and polyaromatic hydrocarbons (PAHs) and particulates are inerts, condensation products, and solid carbon products. Fig. 2. Overall schematic of solid fuel combustion (1). Reaction sequence is A, heating and drying B, solid particle pyrolysis C, oxidation and D, post-combustion. In the oxidation sequence, left and center comprise the gas-phase region, tight is the gas—solids region. Noncondensible volatiles include CO, CO2, CH4, NH, H2O condensible volatiles are C-6—C-20 compounds oxidation products are CO2, H2O, O2, N2, NO, gaseous organic compounds are CO, hydrocarbons, and polyaromatic hydrocarbons (PAHs) and particulates are inerts, condensation products, and solid carbon products.
The fused 3+ ring aromatics in petroleum include both cata- and peri-condensed stmctures (see Table 4, Fig. 8). The cata-condensed species are those stmctures where only one face is shared between rings, the peri-condensed molecules are those that share more than one face. The fused ring aromatics form the class of compounds known as polynuclear aromatic hydrocarbons (PAH) which includes a number of recognized carcinogens in the 4+ ring family (33). Because of the potential health and environmental impact of PAH, these compounds have been studied extensively in petroleum. [Pg.171]

Actual water treatment challenges are multicomponent. For example, contamination of groundwater by creosote [8021-39-4], a wood (qv) preservative, is a recurring problem in the vicinity of wood-preserving faciUties. Creosote is a complex mixture of 85 wt % polycycHc aromatic hydrocarbons (PAHs) 10 wt % phenohc compounds, including methylated phenols and the remaining 5 wt % N—, S—, and O— heterocycHcs (38). Aqueous solutions of creosote are therefore, in many ways, typical of the multicomponent samples found in polluted aquifers. [Pg.402]

The ratio of tire numbei of e + (3 pahs to the niimher of y-iays emitted. [Pg.452]

Some of the methods used for deterrnination of organic pollutants in the environment foUow (118). The most notable are polyaromatic hydrocarbons (PAHs) and volatile organic compounds (VOCs). [Pg.248]

Aerobic, Anaerobic, and Combined Systems. The vast majority of in situ bioremediations ate conducted under aerobic conditions because most organics can be degraded aerobically and more rapidly than under anaerobic conditions. Some synthetic chemicals are highly resistant to aerobic biodegradation, such as highly oxidized, chlorinated hydrocarbons and polynuclear aromatic hydrocarbons (PAHs). Examples of such compounds are tetrachloroethylene, TCE, benzo(a)pyrene [50-32-8] PCBs, and pesticides. [Pg.170]

Fig. 21. Random packing elements for distillation columns (a), Raschig ring (metal) (b). Bed saddle (ceramic) (c), Intalox saddle (ceramic) (d), PaH ring... Fig. 21. Random packing elements for distillation columns (a), Raschig ring (metal) (b). Bed saddle (ceramic) (c), Intalox saddle (ceramic) (d), PaH ring...
Typical experimental values of HETP for a random packing such as 50-mm PaH rings, and a stmctured packing, such as Intalox 2T of Norton Co., under the same system conditions, are shown in Figure 25. Many designers of packed columns prefer the use of HETP instead of but the latter is more fundamental and discrirninates between Hquid- and vapor-phase resistances. It should be noted that terms such as H and N are based on... [Pg.173]


See other pages where PAHs is mentioned: [Pg.34]    [Pg.476]    [Pg.105]    [Pg.586]    [Pg.586]    [Pg.717]    [Pg.779]    [Pg.392]    [Pg.481]    [Pg.523]    [Pg.55]    [Pg.57]    [Pg.158]    [Pg.171]    [Pg.171]    [Pg.172]    [Pg.197]    [Pg.197]    [Pg.252]    [Pg.404]    [Pg.226]    [Pg.242]    [Pg.247]    [Pg.248]    [Pg.248]    [Pg.248]    [Pg.249]    [Pg.249]    [Pg.170]    [Pg.222]    [Pg.171]    [Pg.171]   
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ATMOSPHERIC FATES OF PARTICLE-ASSOCIATED PAHs HETEROGENEOUS REACTIONS

Activation of PAH and Tumorigenesis

Activation of PAHs

Adsorption of PAH

Alkyl PAHs

All-benzenoid Graphitic PAHs Larger than HBCs

All-benzenoid PAHs - Synthesis, Structural Characterizations and Electronic Properties

Amino-PAH

Analysis of PAH

Another Challenge Large Molecules, the Case of PAHs

Anthropogenic PAH

Aqueous solubility of PAH

Aza-PAHs

Bay region PAHs

Bioaccumulation factors , PAHs

Bioconcentration factors , PAHs

Bioconcentration, PAH

Boston Harbor , PAHs

Carcinogenic effects of PAHs

Carcinogenicity of PAH

Case Study Quick Turnaround Analysis of PAHs by HPLC in Multimedia Samples

Chlorinated PAHs

Chlorinated polycyclic aromatic hydrocarbons Cl-PAHs)

Coal identifying PAHs

Combustion-produced PAHs

Complex mixtures, PAHs

Complex pahs

Covalent PAH o-Quinone-DNA Adducts

Dendritic Poly(phenylene)s and Giant Polyaromatic Hydrocarbons (PAHs)

Desorption of PAHs

Diesel emissions, PAHs

Diesel emissions, PAHs particulate

EPA-PAHs

Electrokinetic Removal of PAHs

Electrokinetic Removal of PAHs Using Facilitating Agents

Extraction PAHs from soil

Extraction efficiencies several PAHs

Fast GC Quantification of 16 EC Priority PAH Components

Fate of PAH

Fluoranthene PAHs

Generated PAHs and PACs

Hemoglobin PAHs oxidation

Hetero-PAHs

Human Cell Mutagenicities of PAHs and PACs

Hydrolysis and PAH Carcinogenicity

Introduction PAHs)

Isomeric PAHs

Isomeric PAHs identification

LiChrospher PAH

Metabolic Activation of PAHs

Methylene-bridged PAHs

Microbial oxidation, PAHs

Molecular clouds with PAHs

Monitoring-PAH

Multidisciplinary Approach Towards Investigating Structure-Function Relationships in the NER of Bulky PAH-DNA Adducts

Nitro-PAH

Nitro-PAHs

Nonalternant PAHs

Nonplanar PAHs

OH-PAH

Oxidative DNA Lesions from PAH o-Quinones

PAH

PAH (index)

PAH (polycyclic aromatic

PAH Carcinogenicity and Theoretical Models

PAH Exposure and Cancer

PAH and Soot Formation

PAH carbocations

PAH carcinogenicity

PAH compounds

PAH degradation

PAH derivatives

PAH emissions

PAH metabolism

PAH o-quinone

PAH o-quinone DNA adduct

PAH polyanhydride

PAH profiles

PAH quinones

PAH remediation

PAH stability

PAH toxicity

PAH transport

PAH-DNA adducts

PAH-PEDOT-S multilayer films

PAH-induced cancer

PAHs (polycyclic aromatic

PAHs (polycyclic aromatic synthesis

PAHs , in atmospheric

PAHs From Benzene by Shock Reaction

PAHs distribution variations

PAHs in sediment

PAHs in sewage sludge

PAHs interstellar dust

PAHs oxidation

PAHs peri-condensed

PAHs pyrolytic

PAHs with Five-membered Rings

PAHs with Three or More Rings

PAHs with Varying Peripheries

PAHs world hypothesis

PAHs, Cancer Potencies, and Potency Equivalence Factors

PAHs, abbreviations

PAHs, bioconcentration factors BCFs)

PAHs, carcinogenic

PAHs, defined

PAHs, electron-poor

PAHs, in house dust

PAHs, noncarcinogenic

PAHs, octanol-water partition coefficients

PAH—See Polycyclic aromatic hydrocarbons

PFPA-HFIP (PAH)

Particle Size Distribution of PAHs and Mutagenicity

Particle-Associated. PAHs in Ambient Air

Partitioning of PAHs

Photochemical Reactions of Particle-Associated PAHs

Pollution PAHs)

Polyallylamine hydrochloride (PAH

Polyaromatic hydrocarbons (PAH

Polyaromatic hydrocarbons PAHs

Polycyclic Aromatic Hydrocarbons PAH PNA POM

Polycyclic aromatic hydrocarbons (PAHs degradation

Polycyclic aromatic hydrocarbons (PAHs discharge

Polycyclic aromatic hydrocarbons (PAHs emission

Polycyclic aromatic hydrocarbons (PAHs in sediment

Polycyclic aromatic hydrocarbons (PAHs in soil

Polycyclic aromatic hydrocarbons (PAHs in water

Polycyclic aromatic hydrocarbons (PAHs properties

Polycyclic aromatic hydrocarbons (PAHs results

Polycyclic aromatic hydrocarbons (PAHs solubility

Polycyclic aromatic hydrocarbons (PAHs sources

Polycyclic aromatic hydrocarbons PAHs)

Polycyclic aromatic hydrocarbons PAHs) adsorption

Polycyclic aromatic hydrocarbons interstellar PAHs

Polycylic aromatic hydrocarbons PAHs)

Polyelectrolyte PAH

Polymeric materials PAHs)

Polynuclear aromatic hydrocarbon, PAH:

Polynuclear aromatic hydrocarbons PAHs)

Pyrene PAHs)

Sediments, PAHs

Solvent PAHs using

Synthesis of PAHs

The Enantioselective Toxicities of Polyaromatic Hydrocarbons (PAHs)

Time - Concentration Profiles of Particle-Phase PAHs during Transport across an Air Basin

Toluene, PAHs

Unsubstituted PAH

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