The largest database of trusted experimental protocols

Chrysene

Chrysene is a polycyclic aromatic hydrocarbon (PAH) compound found in various environmental sources, such as fossil fuels and combustion processes.
It has been the subject of extensive research due to its potential toxicity and environmental impact.
PubCompare.ai, an AI-driven platform, can help optimize Chrysene research by quickly locating the best protocols from literature, preprints, and patents.
Leveraging advanced comparisons, PubCompare.ai identifies the most accurate and reproducible methods to drive Chrysene studies forward.
This tool unlocks the key to efficinet and acurate Chrysene research, enabling researchers to explore the power of this AI-driven platform and unlock new insights into this important environmental contaminant.

Most cited protocols related to «Chrysene»

Study population. We conducted a population-based case–control study of NHL in four National Cancer Institute–Surveillance Epidemiology and End Results Program (NCI-SEER) study sites (http://seer.cancer.gov/). The study design has been previously described (Colt et al. 2004 (link); Wheeler et al. 2011 (link)). Briefly, the study was conducted in Iowa, Los Angeles County, California, and the metropolitan areas of Detroit, Michigan (Macomb, Oakland, and Wayne counties) and Seattle, Washington (King and Snohomish counties). Eligible cases were 20–74 years of age, diagnosed with a first primary NHL between July 1998 and June 2000, and uninfected with HIV. In Seattle and Iowa, all consecutive cases were chosen. In Detroit and Los Angeles, all African-American cases and a random sample of white (regardless of Hispanic ethnicity) cases were eligible for study, allowing for oversampling of African-American cases. Of the 2,248 potentially eligible cases, 320 (14%) died before they could be interviewed, 127 (6%) were not located, 16 (1%) had moved away, and 57 (3%) had physician refusals. Of the 1,728 remaining cases, 1,321 (76%) participated. Controls (≥ 65 years of age) were selected from Center for Medicare and Medicaid Services files (http://dnav.cms.gov/) or the general population using random digit dialing (< 65 years of age) and were frequency matched to cases by sex, age (within 5-year groups), race, and study site. Of the 2,409 potentially eligible controls, 2,046 were able to be located and contacted, and 1,057 (52%) of these subjects participated. The study was approved by the human subjects review boards at all participating institutions. Written informed consent was obtained from each participant.
Computer-assisted personal interviews were conducted in the home of each participant. Interviewers asked about demographics including race and education, age of the home, housing type, the presence of oriental rugs, pesticide use in the home and garden, residential and occupational histories, and other factors.
Dust samples and laboratory analysis. As described in detail previously (Colt et al. 2004 (link), 2005 (link)), dust was collected between February 1999 and May 2001 from vacuum cleaners of participants who gave permission (93% of cases, 95% of controls) and who had used their vacuum cleaner within the past year and owned at least half their carpets or rugs for ≥ 5 years [695 cases (57%), 521 controls (52%)]. Dust samples from 682 cases (98%) and 513 controls (98%) were successfully analyzed between September 1999 and September 2001.
Exposure to a mixture of 27 chemicals measured in house dust [5 PCBs, 7 polycyclic aromatic hydrocarbons (PAHs), and 15 pesticides] was of interest. The PCBs were congeners 105, 138, 153, 170, and 180. The PAHs were benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, benzo(k)fluoranthene, chrysene, dibenz(ah)anthracene, and indeno(1,2,3-cd)pyrene. The pesticides were α-chlordane, γ-chlordane, carbaryl, chlorpyrifos, cis-permethrin, trans-permethrin, 2,4-dichlorophenoxyacetic acid (2,4-D), DDE, dichlorodiphenyltrichloroethane (DDT), diazinon, dicamba, methoxychlor, o-phenylphenol, pentachlorophenol, and propoxur. Extraction and analysis were performed on 2-g aliquots of dust samples using gas chromatography/mass spectrometry (GC/MS) in selected ion monitoring mode. Concentrations were quantified using the internal standard method. Usual detection limits were 20.8 ng/g of dust for α-chlordane, γ-chlordane, DDE, DDT, propoxur, o-phenylphenol, PAHs, and PCBs; 42–84 ng/g for chlorpyrifos, diazinon, cis-permethrin, dicamba, pentachlorophenol, and 2,4-D; and 121–123 ng/g for carbaryl and trans-permethrin. Changes in analytic procedures during the study resulted in increased detection limits for methoxychlor (from 20.7 to 62.5 ng/g). A small proportion of samples weighing < 2 g had detection limits that were higher than the usual detection limits.
The laboratory measurements for the 27 analytes contained various types of ‘‘missing data,’’ primarily when the concentration was below the minimum detection level. To a lesser extent, missing data occurred when there was co-elution between the target chemical and interfering compounds. Chemical concentrations were assumed to follow a log-normal distribution, and data were imputed using a “fill-in” approach to create 10 complete data sets for each of the 27 analytes. Details about the imputation of analyte values have been published previously (Colt et al. 2004 (link); Lubin et al. 2004 (link)).
A total of 1,180 subjects with complete dust analysis results and covariate values were included in this analysis. The sample included 508 (43%) controls and 672 (57%) cases, and was predominantly white (88%) with an average age of 60 years (SD = 11.2). Of these 1,180 subjects, 202 (17%) were from the Detroit study site, 340 (29%) from Iowa, 292 (25%) from Los Angeles, and 346 (29%) from Seattle.
Statistical analysis. In previous analyses of individual chemicals in the study population overall, we evaluated NHL risk comparing tertiles or other groupings of levels above the detection limit to those with no detectable level of the chemical (Colt et al. 2005 (link), 2006 (link); Hartge et al. 2005 (link)). Study site–specific risk estimates were not presented in these publications. Here, we used a weighted quartile sum approach in conjunction with nonlinear logistic regression to evaluate the effect of several chemical exposures together on the risk of NHL. Exposure to a mixture of 27 chemicals measured in house dust was evaluated overall and in study site–specific models. All models were adjusted for sex, age at diagnosis (cases)/selection date (controls), race, and level of education. Age was treated as continuous, race was dichotomized as white or non-white, and education was treated as ordinal (grouped as < 12, 12–15, and ≥ 16 years). In the overall model, we also adjusted for study site.
The WQS method (Carrico et al. 2014 (link)) is constrained to have associations in the same direction for chemical exposures and risk, and is designed for variable selection over prediction. WQS regression estimates a weighted linear index in which the weights are empirically determined through the use of bootstrap sampling. The approach considers data with c correlated components scored as ordinal variables into quantiles (here, quartiles) that are reasonable to combine (i.e., all chemicals) into an index and potentially have a common adverse outcome. The weights are constrained to sum to 1 and be between 0 and 1, thereby reducing dimensionality and addressing issues associated with collinearity. For this analysis, the c = 27 chemical concentrations were scored into quartiles based on the case and control data combined and denoted by qi, where qi = 0, 1, 2, or 3 for i = 1 to c. A total of B = 100 bootstrap samples (of the same size as the total sample, n = 1,180) were generated from the full data set and used to estimate the unknown weights, w, that maximized the likelihood for b = 1 to B for the following model
subject to the constraints cΣi=1wi|b  = 1 and 0 ≤ wi ≤ 1 for i = 1 to c. In the above equation, wi represents the weight for the ith chemical component qi, and the term cΣi=1wiqi represents a weighted index for the set of c chemicals of interest. Furthermore, z denotes a vector of covariates determined prior to estimation of the weights, φ are the coefficients for the covariates in z, and g(.) is any monotonic and differentiable link function that relates the mean, μ, to the predictor variables in the right hand side of the equation. Because the outcome variable of interest in this analysis is binary (case status), a logit link was assumed for g.
For each bootstrap sample, the p-value of β1, the parameter estimate for the weighted index, was used to evaluate the statistical significance of the estimated vector of weights (α = 0.10). The weighted quantile score was then estimated as
and nB is the number of bootstrap samples in which β1 was significant. Finally, the significance of the WQS index was determined using the original data set and the model
g(μ) = β0 + β1 WQS + z´φ, [2]
where exp(β1) is the odds ratio (OR) associated with a unit (quartile) increase in the weighted sum of exposure quartiles (WQS index).
Weights estimated from the full data set were used to create a WQS index denoted as WQSF. In addition to WQSF, four site-specific indices [denoted as WQSD (Detroit), WQSI (Iowa), WQSL (Los Angeles), and WQSS (Seattle)] were estimated using data from each site. Differences in the distributions of the chemical concentrations across sites prohibited the use of quantiles based on the full data set in the estimation of site-specific weights; therefore, we used site-specific quartiles based on the combined case–control distribution to estimate site-specific indices. The association between the WQS indices and NHL was examined by testing each index within its respective data set, with statistical significance set at α = 0.05. The primary statistical analysis was performed using one randomly selected imputation data set. A secondary analysis estimated WQS indices for all 10 imputed data sets to assess sensitivity of the results to the data imputation.
We conducted further analyses of major subtypes of NHL: diffuse large B-cell lymphoma (DLBCL), follicular lymphoma, small lymphocytic lymphoma/chronic lymphocytic leukemia (SLL/CLL), marginal zone lymphomas, other lymphomas, and lymphomas where subtype was not specified/unknown [not otherwise specified (NOS)]. Our study primarily included SLL rather than CLL (Morton et al. 2008 (link)). Other lymphomas consisted of mantle cell lymphoma, lymphoplasmacytic lymphoma, Burkitt lymphoma/leukemia, mycosis fungoides/Sézary syndrome, and peripheral T-cell lymphoma. We fitted WQS regression models separately for each of these groups to determine whether the mixture effect varied by subtype using all 508 controls in each model.
As a comparison to the WQS regression results, we also conducted single chemical analyses (one-by-one) for all of the data (adjusted for study site) and separately within each study site using study site–specific cut points based on the distributions among cases and controls combined. Models were adjusted for sex, age, race, and level of education. ORs comparing each of the three highest quartiles to the first quartile of exposure were estimated for each individual chemical. Given the exploratory nature of these analyses, no adjustments were made for multiple comparisons.
Full text: Click here
Publication 2015

Protocol full text hidden due to copyright restrictions

Open the protocol to access the free full text link

Publication 2015
2,2,4-trimethylpentane acenaphthylene Benzo(a)pyrene chrysene Environmental Pollutants fluoranthene naphthalene Perylene phenanthrene Polycyclic Hydrocarbons, Aromatic Solvents Technique, Dilution
PAH standards (purities ≥ 99%) were obtained from ChemService, Inc. (West Chester, PA, USA). Target analytes included naphthalene (NAP), acenaphthene (ACE), acenaphthylene (ACY), fluorene (FLO), anthracene (ANT), phenanthrene (PHE), fluoranthene (FLA), pyrene (PYR), chrysene (CHR), benz(a)anthracene (BAA), benzo(b)fluoranthene (BBF), benzo(k)fluoranthene (BKF), benzo(a)pyrene (BAP), benzo(ghi)perylene (BPL), and indeno123(cd)pyrene (IPY). Cleanup and extraction solvents were pesticide or Optima® grade from Fisher Scientific (Fairlawn, NJ, USA).
Water quality data included temperature, pH, dissolved oxygen, specific conductivity, oxidative-reductive potential (ORP) and nitrate and ammonium concentrations, and were collected at each site during sampler deployment and retrieval using a YSI® sonde. Additionally, grab samples were also taken at sampler deployment and retrieval at certain sites for analysis of total and dissolved organic carbon (TOC and DOC), as well as total suspended and total dissolved solids (TSS and TDS). The two measurements were averaged for each sampling event and results are summarized in Supporting Information.
SPMD field cleanup and laboratory extraction were performed as previously described (20 (link)) and in accordance with standard operating procedures and standard analytical methods. Quality control consisted of field blanks, trip blanks and field cleanup blanks. Laboratory quality control included reagent blanks, high and low concentration fortifications, and unexposed fortified SPMDs. Quality control resulted in duplicate sites average RSD equaling 15%, and target compounds in blanks were either non-detect or below levels of quantitation.
After extraction, samples were solvent exchanged into acetonitrile and analyzed by HPLC with diode-array and fluorescence detectors. DAD signals were 230 and 254 nm and FLD excitation and emissions were 230 and 332, 405, 460, respectively. Flow was 2.0 mL/min beginning with 40/60% acetonitrile and water and steadily ramping to 100% acetonitrile over a 28 minute run per column maker recommendations. Because the low molecular weight volatile compounds were impacted by the method solvent evaporation steps, SPMD concentrations were recovery corrected with method recovery averages ranging from 35% for NAP to 95% for BPL (Supporting Information Table S1).
The equation established for converting SPMD concentrations (CSPMD) to water concentrations (Cwater) using laboratory sampling rates (Rs) in L/day is:
Cwater=CSPMDVSPMDRst where VSPMD is the volume of the sampler and t is the time in days. Laboratory sampling rates from the literature were used and temperature corrected using a trendline based on rates at three temperatures: 10, 18, and 26° C (9 , 21 (link)). Loads were calculated from the concentrations using USGS flow estimates at the Portland station. Data analysis was performed using Microsoft Excel® 2003, SigmaStat® for t-tests and rank sum tests, S+® for principal component analysis and SigmaPlot® for graphing.
Publication 2008
acenaphthene acenaphthylene acetonitrile Ammonium anthracene Benzo(a)pyrene benzo(b)fluoranthene benzo(k)fluoranthene chrysene Dissolved Organic Carbon Electric Conductivity fluoranthene fluorene Fluorescence High-Performance Liquid Chromatographies naphthalene Nitrates Oxidation-Reduction Oxygen Perylene Pesticides phenanthrene pyrene Scapuloperoneal Myopathy, MYH7-Related Solvents
During the third trimester of pregnancy, personal monitoring was carried
out as previously described (Perera et al. 2003 (link)). Vapors and particles ≥2.5 μg in diameter were collected
on a precleaned quartz microfiber filter and a pre-cleaned polyurethane
foam cartridge backup. The samples were analyzed at Southwest Research
Institute (San Antonio, TX) for benz[a]anthracene, chrysene, benzo[b]fluroanthene, benzo[k]fluroanthene, BaP, indeno-[1,2,3-cd]pyrene, disbenz[a,h]anthracene, and benzo[g,h,i]perylene as described by Tonne et al. (2004) (link). For quality control, each personal monitoring result was assessed as
to accuracy in flow rate, time, and completeness of documentation. All
of the 183 subjects had samples of acceptable quality.
Full text: Click here
Publication 2006
anthracene chrysene Perylene pyrene Quartz
The inventory was developed using a top-down approach based on the PKU-FUEL-200718 and an updated EFPAHs database. Among the 64 fuel sub-types defined in the PKU-FUEL-2007,18 the category of crude oil (used in petroleum refinery) was replaced with catalytic cracking. In addition, five process emission sources in the iron-steel industry (iron sintering, open hearth furnace, convertor, arc furnace, and hot rolling) were added,23 increasing the total fuel sub-types to 69 (Table S1). They were divided into six categories (coal, petroleum, natural gas, solid wastes, biomass, and an industrial process category) or six sectors (energy production, industry, transportation, commercial/residential sources, agriculture, and deforestation/wildfire). PKU-PAH-2007 covered 222 countries/territories and was gridded to 0.1°× 0.1° resolution for the year 2007. In addition, annual PAH emissions from individual countries were derived from 1960 to 2008 and simulated from 2009 to 2030 based on the six IPCC SRES scenarios.24 The 16 PAHs included in the inventory were: naphthalene (NAP), acenaphthylene (ACY), acenaphthene (ACE), fluorene (FLO), phenanthrene (PHE), anthracene (ANT), fluoranthene (FLA), pyrene (PYR), benz(a)anthracene (BaA), chrysene (CHR), benzo(b)fluoranthene (BbF), benzo(k)fluoranthene (BkF), benzo(a)pyrene (BaP), dibenz(a,h)anthracene (DahA), indeno(l,2,3-cd)pyrene (IcdP), and benzo(g,h,i)perylene (BghiP). In this study, the term “total PAHs” means the sum of the 16 PAHs.
Publication 2013
acenaphthene acenaphthylene anthracene Benzo(a)pyrene benzo(b)fluoranthene benzo(k)fluoranthene Catalysis chrysene Coal Deforestation fluoranthene fluorene Iron naphthalene Perylene Petroleum phenanthrene Polycyclic Hydrocarbons, Aromatic pyrene Steel Wildfires

Most recents protocols related to «Chrysene»

In a 500 mL round-bottom flask, we added 2 g (5.1 mmol) of 6,12-dibromochrysene, 2.85 g (6.2 mmol) of 4,4,5,5-tetramethyl-2-(4-(1,2,2-triphenylvinyl)phenyl)-1,3,2-dioxaborolane (6), 2.5 g (18 mmol) of potassium carbonate, and 0.3 g (0.26 mmol) of tetrakis(triphenylphosphine)palladium(0). This mixture was dissolved in 200 mL of anhydrous o-xylene and 40 mL of distilled water and then stirred. The reaction mixture was heated to 110 °C for 20 h under nitrogen. Upon completion of the reaction, it was extracted with chloroform and distilled water, and the organic layer was dried with anhydrous MgSO4. The product was subsequently purified by silica gel column chromatography using the CHCl3:hexane (1:9) eluent, yielding a white solid (yield: 40%). 1H NMR (400 MHz, DMSO-d6): δ(ppm) = 9.27 (s, 1H), 9.06–8.99 (m, 2H), 8.67 (s, 1H), 8.33 (dd, J = 7.6, 1.9 Hz, 1H), 7.84–7.73 (m, 4H), 7.68–7.62 (m, 1H), 7.40–7.35 (m, 2H), 7.24–7.13 (m, 9H), 7.13–7.05 (m, 6H), 7.03–6.99 (m, 2H).
Full text: Click here
Publication 2024
New blue-emitting materials, 4-(12-([1,1′:3′,1″-terphenyl]-5′-yl)chrysen-6-yl)-N,N-diphenylaniline (TPA-C-TP) and 6-([1,1′:3′,1″-terphenyl]-5′-yl)-12-(4-(1,2,2-triphenylvinyl)phenyl)chrysene (TPE-C-TP), were described in Scheme 1 and Scheme 2 and were reported in a previous study [29 (link),30 (link),31 (link)]. The relevant NMR data are presented in Figures S1–S3.
Full text: Click here
Publication 2024
In a 250 mL round-bottom flask, we added 1.3 g (2 mmol) of compound (7), 0.62 g (2.2 mmol) of [1,1′:3′,1″-terphenyl]-5′-ylboronic acid, 0.91 g (6.5 mmol) of potassium carbonate, and 0.11 g (0.09 mmol) of tetrakis(triphenylphosphine)palladium(0). This mixture was dissolved in 140 mL of anhydrous o-xylene and 30 mL of distilled water and then stirred. The reaction mixture was heated to 110 °C for 20 h under nitrogen. Upon completion of the reaction, it was extracted with dichloromethane and distilled water, and the organic layer was dried with anhydrous MgSO4. The product was subsequently purified by silica gel column chromatography using the CHCl3:hexane (2:8) eluent, yielding a white solid (yield: 62%). 1H NMR (400 MHz, DMSO-d6): δ(ppm) = 9.13 (d, J = 8.2 Hz, 1H), 9.04 (d, J = 8.6 Hz, 1H), 8.93 (s, 1H), 8.72 (s, 1H), 8.07 (d, J = 8.2 Hz, 1H), 8.03 (s, 1H), 7.89 (s, 2H), 7.87 (s, 4H), 7.79 (d, J = 9.3 Hz, 1H), 7.75–7.62 (m, 4H), 7.49 (t, J = 7.6 Hz, 4H), 7.43–7.37 (m, 4H), 7.25–7.14 (m, 9H), 7.13–7.07 (m, 6H), 7.02 (s, 2H).
Full text: Click here
Publication 2024
All the DFT calculations
for chrysene-based Z-shaped compounds
were performed via the Gaussian 09,87 program.
From the literature, we found out that Khan et al.88 (link) reported the photovoltaic properties of the FCIC chromophore via the DFT approach. In that report, they selected
the MW1PW91/6-311G(d,p) functional89 (link),90 (link) through the
benchmark study between experimental and DFT values of λmax at various functionals of the FCIC compound.
Therefore, to investigate the nonlinear optical properties of FCIC, which is named DTMR1, utilized as a reference
in the current study and its derivatives, we used the MW1PW91/6-311G(d,p)
level. First of all, the geometrical optimization of all the studied
compounds was done at the aforementioned functional and the lack of
imaginary frequencies was assured for local minima, which confirmed
the optimization of the structure. To uncover the electronic and optical
characteristics of DTMR1 and DTMD2DTMD6, various analyses such as DOSs, NBOs, HOMO/LUMO band
gaps, NPA, GRPs, UV–vis, TDM, and NLO were computed at the
aforementioned functional. To interpret the data from outputs, different
kinds of software like the Gauss View 5.0 program,91 Avogadro,92 (link) Chemcraft,93 Multiwfn,94 (link) and Origin95 were used. Further, eqs 36 were employed
to determine the dipole moment (μtotal),81 (link) linear polarizability ⟨α⟩,82 (link),96 (link) hyperpolarizability (βtotal),97 (link) and second hyperpolarizability (γtotal)8 (link) behavior of DTMR1 and DTMD2DTMD6.
Ten hyperpolarizability
total) tensors were
aligned across the x, y, and z axes: βxxx, βxyy, βxzz, βyyy, βxxy, βyzz, βzzz, βxxz, βyyz, and βxyz by analyzing Gaussian output files.83 (link) where .
Publication 2024
To explore the formation of metal-organic precursors comprising chrysene tectons, we used the coarse-grained MC model developed previously [24 (link),25 (link),26 (link),27 (link)]. Specifically, the chrysene molecules, abbreviated here as ch, were represented by flat rigid collections of four interconnected segments, each corresponding to one benzene ring, as shown in Figure 1. These monomers were equipped with two differently distributed active interaction centers imitating the halogen substituents (red arrows therein). The molecules were placed on a triangular lattice of equivalent adsorption sites mimicking the catalytically active (111) metallic surface (e.g., gold, silver, copper). For convenience, the lattice constant of the adsorbing surface a was assumed to be equal to 1. A single segment of ch was allowed to occupy one adsorption site (lattice vertex), and the consecutive segments of ch were centered at the next neighbor sites of the lattice (i.e., they were separated by a distance of a3 ). The active centers of chrysene tectons provided directional interactions with the coadsorbed metal atoms modeled as single segments. The range of these metal–organic interactions was limited to nearest neighbor sites, measuring from the vertices 1–12 of the polyhexagonal contour shaded in Figure 7. The formation of metal–organic links sustaining the precursors was possible only when the interaction directions of the contributing molecules were collinear, as illustrated in the figure. In this case, the energy of interaction assumed for a single link was equal to 2ε, where ε stands for the energy of elementary metal–monomer interaction. Nonlinear 120° linker-metal-linker configurations contributed with energy ε, reflecting the effect of repulsive interactions between active molecular segments located too close to each other. Figure S4 in the Supporting Information section shows the possible one- and bi-molecular metal-linker configurations along with their corresponding energies.
In the calculations, the conventional canonical MC method with Metropolis sampling was used, where the total number of species N, temperature T, and system size A (here area of the adsorbing surface) were fixed [38 ]. To eliminate edge effects, periodic boundary conditions in both planar directions were imposed. The simulations started with a mixture of Nl molecules of a given isomer and Nm metal atoms distributed randomly on a rhombic fragment of a triangular lattice with side L equal to 200a (i.e., 200 by 200 adsorption sites); N=Nl+Nm . Next, the adsorbed overlayer was equilibrated in a series of trial moves, each of which corresponded to a single MC step. During one MC step, a molecule or metal atom was picked up at random, and its potential energy in the current position, Uo, was calculated by reckoning the elementary directional interactions (ε) and taking into account the geometric conditions discussed previously (preferred linear →•← links). Next, the selected component was translated to a new random position on the lattice. In the case of chrysene isomers, these units were additionally rotated in-plane by a multiple of 60 degrees. If in the new position, there was enough space (sufficient number of unoccupied adsorption sites), the selected component was inserted therein; otherwise, it was returned to its original site, and the calculation started again. The potential energy of the new configuration, Un, was determined using the same procedure as for Uo. To accept this configuration, the Metropolis criterion was used with the acceptance probability p=min[1,expUkT] , where U=UnUo and k stands for the Boltzmann constant. The calculated value of p was compared with a uniformly distributed random number r(0,1) . If r<p , the new configuration was accepted; in the opposite case, the selected atom or molecule was moved back to the initial (old) position on the lattice and the next MC step was performed. In the simulation, typically, N×105 steps were made at a given T, the last 10% of which were used for the calculation of average values. Moreover, to minimize the risk of trapping the modeled systems in metastable states, gradual cooling of the adsorbed overlayer was implemented. During this procedure, the temperature was linearly decreased from 0.51 to 0.01 using 500 steps of equal length.
Surface coverage θ was defined as the average number of adsorbed segments per lattice site, that is, (4Nl+Nm)/L2 . Quantitative descriptors of the simulated systems presented here, including coordination functions, cluster size distributions, and order parameters, are averages over ten independent replicas.
Energies and temperatures of our model were expressed in the units of ε and ε/k , respectively. Precisely, the values of system energy and temperature are dimensionless and have no physical units. Instead, they are real numbers that specify how many times the elementary portion of energy, ε, and the temperature, |ε|/k, fit into the simulated values of energy and temperature, T, respectively. Note that ε can be given in any energy units (J, cal, eV), so that the units of temperature |ε|/k are automatically adjusted. To maintain the broad applicability of the model, we decided to use only numerical values for the parameters and leave the choice of units to the reader, depending on the specific system. For that reason, our model is dependent on just one working parameter, ε, which describes the single metal–linker interaction and whose numerical value was assumed to be −1. Accordingly, the reduced Boltzmann constant, k, was set to 1 to make temperature, T, dimensionless.
In summary, the input parameters in our model are L, ε, N, and T, with the first two being fixed in all of the calculations, that is L=200 and ε=1 . The targeted parameters include the orientational parameters δa and δc, the fractions of homochiral (S-S and R-R) and heterochiral (R-S) metal-mediated links, and the statistics of aggregate size. The parameters δa and δc were determined by counting the number of molecules with their arms (a) and cores (c) oriented in the three primary directions of the triangular lattice. Figure S5 in the Supporting Information section illustrates the definitions of the core- and arm-based orientation directions. The determined numbers of molecules with distinct orientations were inserted into Equation (S1) in that section. The fraction of homo- and heterochiral links was calculated by accounting for metal atoms coordinated with two enantiomers of the same type for homochiral links and of opposite types for heterochiral links. These numbers were divided by the total number of metal atoms in the system (Nm) to yield the corresponding fractions. Examples of bimolecular configuration of the aforementioned types are presented in Figure S4 in the Supporting Information Section. The statistics of aggregate size were determined based on the number of clusters consisting of a specific number of molecules (ranging from 1 to Nl), which were calculated using a suitably modified Hoshen–Kopelman algorithm for cluster identification [39 (link)].
The algorithm employed in our calculations implemented the conventional Metropolis sampling in the canonical ensemble [39 (link)]. The lattice of adsorption sites was represented as a square L × L table, with each cell being characterized by the occupation variable s, which could take on values of 0 (representing an unoccupied site), 1 (indicating occupancy by a molecular segment), or 2 (denoting occupancy by a metal atom). The nearest neighbors of a specific cell in the table were redefined to include six cell sites, corresponding to the topology of a triangular lattice. The simulation began with a collection of randomly distributed molecules (collections of cells with s=1 ) and metal atoms (single cells with s=2 ) in quantities Nl and Nm, respectively. To adsorb a molecule, a cluster of four sites matching the shape of a given chrysene tecton was selected, as illustrated in Figure 7. The distance between any pair of neighboring segments of the molecule was equal to a3 , corresponding to the next-nearest-neighbor distance on a triangular lattice. The occupation variables s of the cells corresponding to these sites were all set to 1. In the case of a metal atom, a single cell was chosen, and the associated value of s was updated to 2. To determine if there exists an effective interaction between an adsorbed molecule and a metal atom, the active molecular segments were probed. To that end, the next-nearest-neighbor site of a selected active segment was searched out in the direction determined by the specific position of the halogen substituent. If the occupation variable s of this site was equal to 2, then a further search in the same direction was made at the next step of a3 , aiming to determine if a second molecule could be linked with the metal atom. If for that site s was zero, then the first molecule interacted with the metal atom with energy ε , providing single metal coordination. If s was equal to one, the match between the interaction directions (halogen substituents) of the first and second molecule was checked. If the interaction directions were collinear (→←), the second molecule contributed with an additional input of ε, resulting in double coordination of the metal atom with energy 2ε. If the interaction directions were not collinear, the energy of this configuration was reduced and equal to ε. For all other situations in which the occupation variables associated with neighboring segments were not equal to 1 (linker) and 2 (metal), the interaction energy was zero. An analogous scheme was used for a metal atom if this component was selected in the equilibration procedure. In this case, a single lattice site was considered, so the occupation variable for an adsorbed metal atom was set to 2.
To account for the interactions with neighboring molecules, six next-nearest-neighbor sites of the metal atom were checked (at a distance of a3 each). If any of these sites were occupied by an active molecular segment, the directionality of the interaction provided by this molecular segment (halogen position) was inspected. If the interaction direction assigned to the segment pointed towards the metal atom, a single link was formed with energy ε. Then, the second site of the six surrounding the metal atoms was examined, and if this site was occupied by an active molecular segment, the same procedure was used to determine the corresponding interaction direction. If this interaction direction was collinear with that of the first molecule, the second link was formed, contributing to ε. For the 120° alignment of interaction directions, the energy was equal to ε. No more than two linkers were allowed to link with a single metal atom, and this condition was always checked when updating the coordination of a metal atom. The energy of a selected molecule or a metal atom was determined using the method described above, and it served as the input Uo (old configuration) or Un (new configuration) for the previously mentioned Metropolis acceptance criterion.
All computer programs utilized in this study were developed from scratch using the FORTRAN programming language. The calculations were carried out on a computer cluster running the Linux operating system. Executable files were generated using the gfortran GNU compiler.
Full text: Click here
Publication 2024

Top products related to «Chrysene»

Sourced in United States, Germany, United Kingdom, Spain, Sao Tome and Principe, Macao, Canada, France
Benzo[a]pyrene is a polycyclic aromatic hydrocarbon commonly used as a reference compound in various laboratory applications. It serves as a standard for analytical techniques and is often employed in research, environmental monitoring, and regulatory compliance testing.
Sourced in United States
Chrysene is a polycyclic aromatic hydrocarbon (PAH) compound. It is a solid crystalline material at room temperature. Chrysene is commonly used as a reference standard in analytical chemistry and environmental monitoring applications.
Sourced in United States, United Kingdom, Germany, Australia, France, China, Spain
Phenanthrene is a polycyclic aromatic hydrocarbon that consists of three fused benzene rings. It is a crystalline solid at room temperature. Phenanthrene is commonly used as a laboratory reagent and in the synthesis of other chemical compounds.
Sourced in United States
Benzo(b)fluoranthene is a polycyclic aromatic hydrocarbon compound. It is used as a reference standard and analytical reagent in laboratory settings.
Sourced in United States, Canada
Acenaphthylene is a chemical compound used as a laboratory reagent. It is a polycyclic aromatic hydrocarbon with the molecular formula C₁₂H₈. Acenaphthylene is a colorless crystalline solid with a distinct odor.
Sourced in United States, Germany, Canada
Fluoranthene is a polycyclic aromatic hydrocarbon (PAH) compound. It is a solid, crystalline substance used as a chemical standard and reference material in various analytical and research applications.
Sourced in United States, Germany, United Kingdom
Naphthalene is a crystalline compound with the chemical formula C₁₀H₈. It is a common organic chemical used in various industrial and laboratory applications. Naphthalene is a colorless, volatile solid with a distinctive odor. It is known for its high melting and boiling points. The core function of naphthalene is as a chemical building block and intermediate in the production of other organic compounds.
Sourced in Germany, United States, Italy, India, China, United Kingdom, France, Poland, Spain, Switzerland, Australia, Canada, Brazil, Sao Tome and Principe, Ireland, Belgium, Macao, Japan, Singapore, Mexico, Austria, Czechia, Bulgaria, Hungary, Egypt, Denmark, Chile, Malaysia, Israel, Croatia, Portugal, New Zealand, Romania, Norway, Sweden, Indonesia
Acetonitrile is a colorless, volatile, flammable liquid. It is a commonly used solvent in various analytical and chemical applications, including liquid chromatography, gas chromatography, and other laboratory procedures. Acetonitrile is known for its high polarity and ability to dissolve a wide range of organic compounds.
Sourced in United States, Germany, Australia
Acenaphthene is a chemical compound that is commonly used in laboratory equipment. It is a polycyclic aromatic hydrocarbon with the chemical formula C₁₂H₁₀. Acenaphthene is a crystalline solid at room temperature and is typically used as a reference standard or in various analytical techniques.
Sourced in United States
Benzo(k)fluoranthene is a polycyclic aromatic hydrocarbon (PAH) compound. It is a crystalline solid at room temperature. Benzo(k)fluoranthene can be used as a standard reference material in analytical chemistry and environmental monitoring applications.

More about "Chrysene"

Chrysene is a polycyclic aromatic hydrocarbon (PAH) compound found in various environmental sources, such as fossil fuels and combustion processes.
It is closely related to other PAHs like Benzo[a]pyrene, Phenanthrene, Benzo(b)fluoranthene, Acenaphthylene, Fluoranthene, Naphthalene, Acenaphthene, and Benzo(k)fluoranthene.
Chrysene has been the subject of extensive research due to its potential toxicity and environmental impact, with a focus on its detection, quantification, and mitigation.
The analysis of Chrysene often involves techniques like acetonitrile extraction, gas chromatography, and mass spectrometry.
Researchers utilize advanced comparisons and optimization tools like PubCompare.ai to quickly locate the most accurate and reproducible methods from literature, preprints, and patents.
This AI-driven platform helps drive Chrysene studies forward by identifying the best protocols and unlocking new insights into this important environmental contaminant.
By leveraging the power of PubCompare.ai, researchers can explore efficient and accurate ways to study Chrysene, leading to a better understanding of its sources, distribution, and potential mitigation strategies.
This tool serves as a key to unlocking the secrets of Chrysene and its impact on the environment, enabling scientists to make significant advancements in this field of study.