• <tr id="yyy80"></tr>
  • <sup id="yyy80"></sup>
  • <tfoot id="yyy80"><noscript id="yyy80"></noscript></tfoot>
  • 99热精品在线国产_美女午夜性视频免费_国产精品国产高清国产av_av欧美777_自拍偷自拍亚洲精品老妇_亚洲熟女精品中文字幕_www日本黄色视频网_国产精品野战在线观看 ?

    High-resolution mass spectrometric characterization of dissolved organic matter from warm and cold periods in the NEEM ice core

    2018-04-08 00:52:07JianZhongXuAmandaGrannasCunDeXiaoZhiHengDuAmandaWilloughbyPatrickHatcherYanQingAn
    Sciences in Cold and Arid Regions 2018年1期
    關(guān)鍵詞:賢德溫習(xí)曾子

    JianZhong Xu , Amanda Grannas , CunDe Xiao , ZhiHeng Du , Amanda Willoughby ,Patrick Hatcher , YanQing An

    1. State Key Laboratory of Cryospheric Sciences, Northwest Institute of Eco-Environment and Resources, Chinese Academy of Sciences, Lanzhou, Gansu 730000, China

    2. Department of Chemistry, Villanova University, Villanova, PA 19085, USA

    3. Department of Chemistry and Biochemistry, Old Dominion University, Norfolk, VA 23529, USA

    1 Introduction

    Electrospray ionization (ESI) combined with ultra-high resolution Fourier transform ion cyclotron resonance mass spectrometry (ESI-FT-ICR-MS) has recently and effectively been used to characterize the complex molecular composition of DOM because it allows exact molecular weights and formulae of thousands of individual organic molecules to be assigned.Grannaset al. (2006) first used ESI-FT-ICR-MS to analyze DOM in two ice-core samples that had been deposited in approximately 1300 A.D. and 1950 A.D.in Franz Josef Land, Russia. They found that molecules containing sulfur were more abundant in the modern ice than in the older ice and attributed this increase in S incorporation to atmospheric processes occurring in a more SOx-rich environment. Marshet al.(2013) used a nano-ESI-FT-ICR-MS method to analyze small volumes (approximately 90 mL) of meltwater from two ice-core samples, deposited in 1360 A.D.and 1660 A.D., from Greenland. They used two different solid-phase extraction resins (C18 and PPL) to extract and concentrate the DOM and contrasted the molecular composition of the DOM in these two extracts. The results show that PPL had higher extraction efficiency for organic matter (such as CHO components). The DOM in surface snow and ice samples from several sites has been characterized by ESI-FTICR-MS in different studies; and improvements to analytical methods and molecular information about DOM were obtained, such as the importance of DOM sources from terrestrial and microbial input (Bhatiaet al., 2010; Singeret al., 2012; Stubbinset al., 2012;Antonyet al., 2014; Lawsonet al., 2014).

    Ice cores collected from the Greenland ice sheet can contain ice from more than 105 ka ago, which includes ice deposited over a number of glacial-interglacial cycles. DOM in ice cores deposited under different climatic conditions may reflect differences in the provenance of the organic matter (OM) and differences in the chemical, abiotic, and biotic processes that affected the OM under the various conditions, as illustrated from inorganic components (Wolffet al.,2010). Warm and wet interglacial climates, such as during the Holocene, favoured increased plant cover and precipitation; and marine ecosystems would also have been active, meaning that a great deal of phytoplankton metabolism would have occurred. During glacial periods, especially the Last Glacial Maximum(LGM), due to lowering the sea level and exposing continental shelves, ecosystems may have switched to dramatically different states (Farreraet al., 1999;Otto-Bliesneret al., 2006). It is therefore possible that the proportions of aquatic and terrestrial OM in the environment varied as the climate changed. In addition, biological DOM can differ between marine and terrestrial sources; the photochemical processes occurring during the transport of DOM and after deposition may also differ under different climatic conditions. Because of these differences, the molecular composition of DOM samples from ice cores may allow compounds affected by changes in the climate to be "fingerprinted," providing some insight into the factors that controlled the types and reactivity of the DOM compounds.

    In this study, we used ESI-FT-ICR-MS to examine the DOM preserved in two Greenland ice-core samples, comparing glacial and interglacial time periods. Although this work was limited to only two samples, our aim was to give a preliminary assessment of DOM composition in glacial/interglacial ice,which to date has not been assessed in the literature.

    2 Methods

    2.1 Sample collection and pre-analysis processing

    The ice core in this study was collected as part of the North Greenland Eemian Ice Drilling (NEEM)project, and details of the core can be found at http://neem.dk. Briefly, the NEEM ice core, which was 2,540-m long, was taken from the Northwest Greenland ice sheet at 77.45°N, 51.06°W. The core was drilled between 2008 and 2012; and the objective was to retrieve ice from the previous interglacial, the Eemian, which ended about 115,000 years ago. The ice core was cut in the field, and one-quarter of a 20-cm-long subsection of each 10-m section of the ice core was sent to China (one of the members of the NEEM project) for trace-metal analysis using inductively coupled plasma mass spectrometry (ICP-MS).Two melted samples from the core were produced during the ICP-MS measurements by combining parts of several samples into 250-mL Duran glass containers (Schott, Mainz, Germany). The glassware was acid-washed following the procedure used throughout the ICP-MS analysis. The sample details, including the date and depth of each sample, are presented in Table 1. The samples were aged, from the age-depth relationship, to 1692-4379 B.P. before present (Holocene sample: HS) and 21627-24804 B.P. (LGM sample: LS), respectively. The samples were transported to the laboratory, where they were prepared and analyzed in a cooling box at <0 °C.

    Table 1 Concentrations and quality indicators (average for the entire sample) for the DOM isolated from samples from the NEEM ice core, Greenland, and characterized by negative ESI-FT-ICR-MS

    2.2 DOM isolation and analysis

    DOM samples were desalted and concentrated using an established procedure for PPL solid-phase extraction cartridges (Dittmaret al., 2008), and the desalted samples were eluted into LC-MS-grade methanol. Each sample was directly infused into an Apollo II ESI ion source operated in the negative ion mode at a flow rate of 2 μL/min on a Bruker Daltonics 12 Tesla Apex Qe FT-ICR-MS (Bruker, Billerica, MA,USA), housed at the College of Sciences Major Instrumentation Cluster at the Old Dominion University. Spray voltages were optimized for each sample. Ions were accumulated in the hexapole for 3.0 seconds before transfer into the ICR cell, where exactly 300 transients were co-added.

    2.3 Data processing

    Each mass spectrum was externally calibrated using a polyethylene glycol (PEG) standard. Internal calibration of the acquired mass spectra was achieved using numerous CH2homologous series identified by Kendrick mass defect (KMD) analysis that spanned the m/z range of 200-700. Peaks present in the blank,or those identified as a13C analog or a salt peak (due to a high mass defect) were removed from the peak list prior to molecular-formula assignment. Mass lists(of peaks with a signal-to-noise [S/N] ratio exceeding 4) were processed via a molecular-formula calculator to determine all possible molecular formulae(12C5-801H5-10016O1-3014N0-532S0-531P0-2) for each m/z value, within a maximum error of 1.0 ppm.The formula rules applied by Stubbinset al. (2010)were followed to ensure that chemically possible molecular formulae were assigned to the peaks in each mass spectrum. At higher m/z values, unambiguous formula assignment was not possible in some cases due to several possible molecular formulae existing for the same m/z value. To assist in duplicate removal, the "formula extension" approach (as described in Kujawinski and Behn, 2006) was utilized with homologous series of CH2, CHO, and CH2O groups to determine the appropriate formula. Although it is possible, and even likely, that multiple formulae exist for the same m/z, the formula-extension approach offers support for the presence of certain formulae over formulae not part of a Kendrick mass defects (KMD)series. Peaks that could not be assigned an unambiguous formula were removed from further consideration.Approximately 70% of the peaks were assigned molecular formulae using these constraints.

    The assigned molecular formulae were examined using the van Krevelen diagram, double-bond equivalents (DBEs), KMDs, and aromatic indices (AImod).The O/C and H/C ratios were calculated by dividing the number of O and H atoms, respectively, by the number of C atoms in a formula. DBE analysis was used to determine the number of rings and double bonds in a molecule. The DBE was calculated using Equation(1),

    省是指自我反省、自我警醒、自我省察等。《論語》指出:“曾子曰:‘吾日三省吾身:為人謀而不忠乎?與朋友交而不信乎?傳不習(xí)乎?’”是指,曾子說:“我每天都要對三件事作一番自我反?。禾鎰e人辦事,有不盡心盡力的地方嗎?和朋友交往,有不守信用的地方嗎?老師傳授的學(xué)業(yè),有不溫習(xí)的地方嗎?”“子曰:‘見賢思齊焉,見不賢而內(nèi)自省也。’”是指,孔子說:“看見賢德的人,就要想著向他看齊;看見不賢的人,就要在內(nèi)心做自我反省?!?/p>

    wherec,h,n, andpare the numbers of C, H, N, and P atoms, respectively, in the formula.

    The KMD representation of high-resolution mass spectral data can be used to search for potential oligomeric units (Hugheyet al., 2001). The Kendrick mass(KM) and KMD for CH2series were calculated using Equations(2)and(3),

    where 14 is the nominal mass (NM) of CH2, 14.01565 is the exact mass of CH2, and NM is KM rounded to the nearest integer. A homologous series of compounds differing by only the number of base units form a horizontal line in a plot of KMD against KM.

    AImodis a measure of the probable aromaticity of a molecule, assuming that half the O atoms are double-bonded and half have only σ bonds (Koch and Dittmar, 2006). AImodwas calculated using Equation(4),

    wherec,o,s,h, andpare the number of C, O, S, H,N, and P atoms in the formula. AImodranges from 0 for a purely aliphatic compound to 1, with higher values being found for compounds with more double bonds and that are more aromatic.

    The formulae were plotted on the van Krevelen diagram; then, each was categorized using the stoichiometry of its molecular formula. The groups relevant to this study were identified using AImodand H/C cutoffs, which were AImod≥0.67 for combustion-derived condensed aromatics, 0.67> AImod≥0.5 for highly unsaturated aromatic compounds, AImod<0.5 and H/C ≤1.5 for lignin-like compounds and carboxylic-rich alicyclic molecule (Lignin/CRAM)compounds, and 2.0> H/C >1.5 for aliphatic compounds (Koch and Dittmar, 2006; Hockadayet al.,2009).

    3 Results and discussion

    Molecular formulae with the form CcHhOoNnSsPpwere assigned to the negative-ion ultrahigh-resolution FT-ICR mass spectra of the DOM components extracted from the ice-core meltwater samples. Overall, 80% of the total ion current mass spectra of the samples was assigned. The number of peaks assigned molecular formulae was 919 and 149, for HS and LS,respectively, excluding contributions from compounds containing13C isotopes and peaks with high mass defects, indicative of salts.

    3.1 General FT-ICR-MS characteristics

    Reconstructed mass spectra for the monoisotopic molecular formulae assigned to the samples after blank subtraction are shown in Figure 1. Seven subgroups of the molecular formulae were identified,based on the elements in the formulae. These subgroups were compounds containing only C, H, and O(CHO); compounds containing C, H, O, and N(CHON); compounds containing C, H, O, and S(CHOS); compounds containing C, H, O, and P(CHOP); compounds containing C, H, O, P, and N(CHOPN); compounds containing C, H, O, S, and P(CHOSP); and compounds containing C, H, O, N, and S (CHONS). The most abundant composition in both samples was CHO (contributing 50% of all formulae);and the contributions of the other subgroups decreased in the order of CHOS (13%-19%), CHOP(13%-22%), CHONS (6%-9%), CHON (3%-8%),CHOPN (0%-3%), and CHOSP (0%-3%). The compositions according to these subgroups were very similar to compositions found in snow samples from Mendenhall Glacier, southeastern Alaska (Stubbinset al., 2012), but different from compositions found in aerosol and fog water, in which CHON formulae have sometimes been found to be dominant (Zhaoet al.,2013; Wozniaket al., 2014).

    Figure 1 Negative ESI mass spectra for the DOM in the two NEEM ice-core samples (HS and LS). The pie charts show the contributions of the different compound classes to the totals in the different samples

    Although CHO-containing formulae comprised the majority of the identified OM, a significant portion of the OM contained heteroatoms of varying combinations of S, N, and P. Wozniaket al. (2014)found that water-soluble OM in aerosol particulates collected over a marine environment had primary marine biological sources and was also rich in compounds containing N and P. Lawsonet al. (2014) employed FT-ICR-MS analysis on Greenland Ice Sheet runoff samples and found a high proportion of N-rich DOM. The requirements for N and P are higher for marine phytoplankton and bacteria than for terrestrial vegetation; and dissolved organic N and P have long been known to be enriched in the sea-surface micro-layer,where surface-active OM accumulates after being entrained by bubbles and brought to the surface(Miyazakiet al., 2011; Buchanet al., 2014). The abundance of compounds containing N and P in these Greenland ice-core samples likely indicates that the DOM primarily had a marine biological source.

    3.2 Atomic ratios and aromaticity in the DOM components

    Biological and geochemical classes of organic compounds in DOM can be identified from their distinct elemental ratios using van Krevelen analysis(Grannaset al., 2006; Stubbinset al., 2012). The contributions of different molecular-formula classes to the aliphatic, Lignin/CRAM, aromatic, and condensed aromatic compounds are shown in Figures 2a and 2b. Overall, HS and LS had similar molecular signatures, as determined from the distributions of formulae in the van Krevelen space (Figure 2b), which indicates that the dominant sources of DOM for these two samples were likely similar.

    The main molecular structures in the samples were aliphatic (68%-74%), the next most common was Lignin/CRAM (12%-19%), and there was a small number of aromatic and condensed aromatic compounds (2%-3%). These contributions were similar to those previously found in snowpack and glacier outflow samples from southeast Alaska (Stubbinset al., 2012). A large contribution of aliphatic compounds has also been found in samples collected far from the coast in Antarctica (Antonyet al., 2014),wherein situmicrobial sources have little influence.

    Figure 2 (a) Van Krevelen plots for Holocene sample (HS) and LGM sample (LS) and (b) a bar chart showing the contributions of each structural class (determined using AImod and H/C ratio) to the total DOM

    The average O/C ratios for both samples were relatively low, 0.29 for HS and 0.27 for LS, respectively,indicating less oxidized aerosols were dominant contributors to DOM. The average O/C ratio observed from aged aerosol in remote areas can be up to 1.0,using aerosol mass spectrometry (Xuet al., 2015);and less than 0.3 for less oxidized aerosol or rainwater samples (Altieriet al., 2009; Wozniaket al.,2014). The O/C ratios in the DOM of snowpack and glacier outflow in the Mendenhall Glacier in southeast Alaska are also close to 0.3 (Stubbinset al.,2012), less than 0.5 in most of the formulae in the Holocene DOM of one Greenland ice core (Marshet al., 2013) and less than 0.4 for the ice core DOM in Franz Josef Land (Grannaset al., 2006).

    Compounds containing N and P were mostly aliphatic, with high H/C ratios (>1.7) and low O/C ratios (<0.4), suggesting the feature of less being oxidized. Wozniaket al. (2014) found that the primary sources of aliphatic CHON compounds in marine aerosol DOM were marine and biological. Most of the CHO compounds were also aliphatic, with higher O/C ratios and lower H/C ratios than the compounds containing N and P. The higher O/C ratios of CHO compounds suggest that a portion of the aerosols were oxidized during transport before deposition (Wozniaketal., 2014). HS was richer in aliphatic S compounds than LS, which may have had primary and/or secondary aerosol sources. Aliphatic compounds rich in S are prevalent in the water-soluble organic carbon fractions of aerosols and probably come from the aqueous oxidation of biogenic volatile organic compounds during the generation of secondary organic aerosols,i.e., organosulfates (Surrattet al., 2007). Organic compounds containing S, such as dimethyl sulfide and dimethylsulfoniopropionate, can also be emitted from marine environments (Andreaeet al., 2003) and influence S-containing DOM. The primary and/or secondary S aerosols can be further distinguished by DBE distribution (Section 3.4). The relatively low abundance of aliphatic S in LS probably means that fresh and aged S aerosol sources were relatively weak during the LGM.

    HS contained a larger number of condensed aromatic formulae than LS. The aromatic compounds mostly contained N and S. Condensed aromatics can be formed only through the heating of OM or through intense photochemical activity (Yeeet al., 2013; Chenet al., 2014), so their presence indicates that HS may contain combusted OM or that the DOM had undergone significant photochemical reactions during transport. The results therefore suggest that terrestrial sources (such as forest fires) of DOM were important in HS.

    3.3 KMD analysis of DOM components

    The homologous groups and homologs within each individual group can be identified using a KMD plot (Mopperet al., 2007). The KMD plots for these two samples are shown in Figures 3a and 3b; and plots for the different compound classes in HS and LS are shown in Figures 3c, 3d, 3e, and 3f. Points forming horizonta, l line corresponds to families of species with formulae CxHyOz(CH2)n, with fixed O-atom contents (x,y, andzare fixed; andnis a variable) and different numbers of CH2groups. A large number of CH2homologous series were found in the CHO,CHOS, CHNO, CHOP, and CHOPN compound classes in HS. The KMD values of these relatively abundant compounds tended to increase as the molecular mass increased, suggesting that increases in the molecular masses were probably caused by increasing numbers of heteroatoms (especially O and S)in the compounds. Overall, no significant families are oberserved in LS due to the smaller number of identified formulae. The most related formulae in the series in CHON compound of HS was the N3O7family, and the next longest were the NO3and N2O8families(Figure 3). On average, more than 98% of the CHON compounds in the sample had O/N ratios >3. The high O/N ratio is consistent with formation of organic nitrate, likely due to the known chemistry of nitrate radicals identified in ambient aerosols (Nget al., 2008).

    Figure 3 Kendrick mass plots of the unique neutral molecular formulae, normalized to CH2 for HS and LS for (a) total HS formulae, (b) total LS formulae, (c) CHO formulae, (d) CHON formulae, (e) CHOP formulae, and (f) CHOS formulae

    3.4 DBE distributions of the DOM components

    The DBEs of DOM molecules also allow assessment of the intensity of different DOM sources and the atmospheric conditions to which the aerosol was exposed (Batemanet al., 2011). The CHO compound DBEs with respect to C of these two samples are shown in Figures 4a and 4b. Most (>90%) of the CHO compounds in both samples had DBEs of <10,and the compounds with high relative abundances had DBEs of 2~7. The most abundant DBEs were 6 in HS and 4 in LS; and the average DBEs were 5.7 and 5.9,respectively. The compounds with the highest relative abundance in both samples had 10~40 C atoms.Compounds with >40 C atoms were also found in HS.The DBEs of CHO compound in HS and LS were similar to those in modern aerosols and fog water(5-7) (Mazzoleniet al., 2010; Zhaoet al., 2013); but the average CHO compound O/C ratios (0.31 and 0.29 for HS and LS, respectively) were lower than in aerosols and fog water (0.4-0.7), suggesting that the CHO compounds in the ice-core samples were less oxidized.

    Higher average DBEs were found for the CHOS compounds in both samples (10 and 14 for HS and LS, respectively), suggesting unsaturated CHOS compounds in these two samples. Two subgroups of CHOS molecular formulae in HS were highlighted,based on H/C value (Figure 4c). The CHOS compounds in subgroup 1 with H/C ≥1.5 are relatively saturated, with DBE values of 0-7. The subgroup 2 CHOS compounds were very unsaturated, with DBEs of 10-20. The O/C ratio was clearly higher in subgroup 1 (0.30) than in subgroup 2 (0.15). The high O content and low DBEs of the CHOS compounds in subgroup 1 suggest these compounds could be organosulfates. However, a large number of S-containing compounds containing reduced forms of S, indicated by the low O content in the molecular formulae,have rarely been reported (Vairavamurthy and Mopper, 1989; Willoughbyet al., 2014). These compounds may have come from fresh emissions rather than being aged products. The average DBEs for CHOP and CHON compounds in HS and LS are all less than 10, similar to DBEs for the CHO compounds.

    Figure 4 Isoabundance plot of the double bond equivalents (DBEs) against the number of C atoms in the molecular formulae containing C, H, and O for (a) HS and (b) LS and for the molecular formulae containing C, H, O, and S for (c) HS and(d) LS. The two subgroups shown for HS in (c) were separated using their H/C ratios(H/C <1.5 for subgroup 1 and H/C ≥1.5 for subgroup 2)

    3.5 Limitations and applications

    We performed the first detailed analysis of DOM in LGM and Holocene ice-core samples from Greenland using FT-ICR-MS. The molecular characteristics identified in these samples suggest the present of compounds derived from primarily terrestrial and marine sources and that some secondary processing occurred in the atmosphere. The compounds containing N and P are consistent with marine primary sources. Condensed C compounds in the DOM suggested contributions from terrestrial combustion sources. The presence of organosulfates and organonitrates suggests secondary reactions in the atmosphere influenced this DOM. The concentration and photochemical processes of DOM were higher and stronger during the warm period (HS) than during the cold period (LS); but the chemical compositions are very similar, suggesting the common DOM sources.

    One weakness of this study is that only two samples are used, which means the results could not be representitive; however, the availability of such samples is severly limited. A large sample size is desirable and possible in the future study from multiple ice cores at different sites. In addition, the extraction of DOM using PPL resin can impart loss of exceptionally hydrophillic compounds and small molecules.However, the losses are expected to have minimal negative impact because compounds with m/z less than 200 are not efficiently detected by FT-ICR-MS.PPL is expected to retain 60%-75% of OM (Dittmaret al., 2008; Stubbinset al., 2012). Finally, FT-ICR-MS is providing a picture of only polar compounds ionizable by negative ESI between 200-1,000 m/z. Despite bias, the amount of molecular information provided is still very useful. A combination of a suite of instruments (such as nuclear magnetic resonance spectroscopy, NMR) in future studies is needed to give an even broader characterization of the OM.

    Our results could also help inform future ice-core studies in Northwest Greenland. The chemical characteristics of the DOM showed variations in the importance of marine and terrestrial sources—for example,significant terrestrial sources for HS; and that the high-resolution analysis of ice-core samples is required to allow marine and terrestrial impacts on the aerosols transported to Greenland to be further distinguished. The contributions of compounds formed through atmospheric reactions suggest that atmospheric conditions have strong impacts on the chemical compositions of aerosols, and this may be of interest when interpreting the results of DOM in modern ice cores that contain anthropogenic aerosols.Modern aerosols in Greenland are affected by the sources described above and also by anthropogenic organic compounds that have been transported in the atmosphere over long distances before being deposited. Our results should motivate an expansion of studies of atmospheric DOM to modern times and the determination of the potential for secondary anthropogenic compounds being deposited in remote regions.

    This research was supported by grants from the Hundred Talents Program of the Chinese Academy of Sciences, the Science Fund for Creative Research Groups of the National Natural Science Foundation of China (NSFC) (41425003, 41121001), the Ministry of Science and Technology of China (MoST,2013CBA01804), and the Scientific Research Foundation of the Key Laboratory of Cryospheric Sciences (SKLCS-ZZ-2017-01).

    Altieri KE, Turpin BJ, Seitzinger SP, 2009. Oligomers, organosulfates,and nitrooxy organosulfates in rainwater identified by ultra-high resolution electrospray ionization FT-ICR mass spectrometry. Atmospheric Chemistry and Physics, 9(7): 2533-2542. DOI:10.5194/acp-9-2533-2009.

    Andreae MO, Andreae TW, Meyerdierks D,et al., 2003. Marine sulfur cycling and the atmospheric aerosol over the springtime North Atlantic. Chemosphere, 52(8): 1321-1343. DOI: 10.1016/S 0045-6535(03)00366-7.

    Antony R, Grannas AM, Willoughby AS,et al., 2014. Origin and sources of dissolved organic matter in snow on the East Antarctic Ice Sheet. Environmental Science & Technology, 48(11):6151-6159. DOI: 10.1021/es405246a.

    Bateman AP, Nizkorodov SA, Laskin J,et al., 2011. Photolytic processing of secondary organic aerosols dissolved in cloud droplets.Physical Chemistry Chemical Physics, 13(26): 12199-12212. DOI:10.1039/C1CP20526A.

    Bhatia MP, Das SB, Longnecker K,et al., 2010. Molecular characterization of dissolved organic matter associated with the Greenland ice sheet. Geochimica et Cosmochimica Acta, 74(13): 3768-3784.DOI: 10.1016/j.gca.2010.03.035.

    Buchan A, LeCleir GR, Gulvik CA,et al., 2014. Master recyclers: features and functions of bacteria associated with phytoplankton blooms. Nature Reviews Microbiology, 12(10): 686-698. DOI:10.1038/nrmicro3326.

    Chen HM, Abdulla HAN, Sanders RL,et al., 2014. Production of black carbon-like and aliphatic molecules from terrestrial dissolved organic matter in the presence of sunlight and iron. Environmental Science & Technology Letters, 1(10): 399-404. DOI:10.1021/ez5002598.

    Dittmar T, Koch B, Hertkorn N,et al., 2008. A simple and efficient method for the solid-phase extraction of dissolved organic matter(SPE-DOM) from seawater. Limnology and Oceanography: Methods, 6(6): 230-235. DOI: 10.4319/lom.2008.6.230.

    Farrera I, Harrison SP, Prentice IC,et al., 1999. Tropical climates at the Last Glacial Maximum: a new synthesis of terrestrial palaeoclimate data. I. Vegetation, lake-levels and geochemistry. Climate Dynamics, 15(11): 823-856. DOI: 10.1007/s003820050317.

    Grannas AM, Hockaday WC, Hatcher PG,et al., 2006. New revelations on the nature of organic matter in ice cores. Journal of Geo-physical Research: Atmospheres, 111(D4): D04304. DOI:10.1029/2005jd006251.

    Hockaday WC, Purcell JM, Marshall AG,et al., 2009. Electrospray and photoionization mass spectrometry for the characterization of organic matter in natural waters: a qualitative assessment. Limnology and Oceanography: Methods, 7(1): 81-95. DOI:10.4319/lom.2009.7.81.

    Hughey CA, Hendrickson CL, Rodgers RP,et al., 2001. Kendrick mass defect spectrum: a compact visual analysis for ultrahigh-resolution broadband mass spectra. Analytical Chemistry, 73(19):4676-4681. DOI: 10.1021/ac010560w.

    Kawamura K, Izawa Y, Mochida M,et al., 2012. Ice core records of biomass burning tracers (levoglucosan and dehydroabietic, vanillic andp-hydroxybenzoic acids) and total organic carbon for past 300 years in the Kamchatka Peninsula, Northeast Asia. Geochimica et Cosmochimica Acta, 99: 317-329. DOI: 10.1016/j.gca.2012.08.006.

    Koch BP, Dittmar T, 2006. From mass to structure: an aromaticity index for high-resolution mass data of natural organic matter. Rapid Communications in Mass Spectrometry, 20(5): 926-932. DOI:10.1002/rcm.2386.

    Kujawinski EB, Behn MD, 2006. Automated analysis of electrospray ionization Fourier transform ion cyclotron resonance mass spectra of natural organic matter. Analytical Chemistry, 78(13):4363-4373. DOI: 10.1021/ac0600306.

    Lawson EC, Bhatia MP, Wadham JL,et al., 2014. Continuous summer export of nitrogen-rich organic matter from the Greenland Ice sheet inferred by ultrahigh resolution mass spectrometry. Environmental Science & Technology, 48(24): 14248-14257. DOI:10.1021/es501732h.

    Legrand M, Preunkert S, Wagenbach D,et al., 2003. A historical record of formate and acetate from a high-elevation Alpine glacier:Implications for their natural versus anthropogenic budgets at the European scale. Journal of Geophysical Research: Atmospheres,108(D24): 4788. DOI: 10.1029/2003JD003594.

    Legrand M, Preunkert S, Schock M,et al., 2007. Major 20th century changes of carbonaceous aerosol components (EC, WinOC, DOC,HULIS, carboxylic acids, and cellulose) derived from Alpine ice cores. Journal of Geophysical Research: Atmospheres, 112(D23):D23S11. DOI: 10.1029/2006JD008080.

    Marsh JJS, Boschi VL, Sleighter RL,et al., 2013. Characterization of dissolved organic matter from a Greenland ice core by nanospray ionization Fourier transform ion cyclotron resonance mass spectrometry. Journal of Glaciology, 59(214): 225-232. DOI:10.3189/2013JoG12J061.

    Mazzoleni LR, Ehrmann BM, Shen XH,et al., 2010. Water-soluble atmospheric organic matter in fog: exact masses and chemical formula identification by ultrahigh-resolution Fourier transform ion cyclotron resonance mass spectrometry. Environmental Science &Technology, 44(10): 3690-3697. DOI: 10.1021/es903409k.

    Miyazaki Y, Kawamura K, Jung J,et al., 2011. Latitudinal distributions of organic nitrogen and organic carbon in marine aerosols over the western North Pacific. Atmospheric Chemistry and Physics, 11(7): 3037-3049. DOI: 10.5194/acp-11-3037-2011.

    Mopper K, Stubbins A, Ritchie JD,et al., 2007. Advanced instrumental approaches for characterization of marine dissolved organic matter: extraction techniques, mass spectrometry, and nuclear magnetic resonance spectroscopy. Chemical Reviews, 107(2): 419-442.DOI: 10.1021/cr050359b.

    Nebbioso A, Piccolo A, 2013. Molecular characterization of dissolved organic matter (DOM): a critical review. Analytical and Bioanalytical Chemistry, 405(1): 109-124. DOI: 10.1007/s00216-012-6363-2.

    Ng NL, Kwan AJ, Surratt JD,et al., 2008. Secondary organic aerosol(SOA) formation from reaction of isoprene with nitrate radicals(NO3). Atmospheric Chemistry and Physics, 8(14): 4117-4140.DOI: 10.5194/acp-8-4117-2008.

    Otto-Bliesner BL, Brady EC, Clauzet G,et al., 2006. Last glacial maximum and holocene climate in CCSM3. Journal of Climate, 19(11):2526-2544. DOI: 10.1175/JCLI3748.1.

    Singer GA, Fasching C, Wilhelm L,et al., 2012. Biogeochemically diverse organic matter in Alpine glaciers and its downstream fate.Nature Geoscience, 5(10): 710-714. DOI: 10.1038/ngeo1581.

    Stubbins A, Spencer RGM, Chen HM,et al., 2010. Illuminated darkness: Molecular signatures of Congo River dissolved organic matter and its photochemical alteration as revealed by ultrahigh precision mass spectrometry. Limnology and Oceanography, 55(4):1467-1477. DOI: 10.4319/lo.2010.55.4.1467.

    Stubbins A, Hood E, Raymond PA,et al., 2012. Anthropogenic aerosols as a source of ancient dissolved organic matter in glaciers.Nature Geoscience, 5(3): 198-201. DOI: 10.1038/ngeo1403.

    Surratt JD, Kroll JH, Kleindienst TE,et al., 2007. Evidence for organosulfates in secondary organic aerosol. Environmental Science& Technology, 41(2): 517-527. DOI: 10.1021/es062081q.

    Vairavamurthy A, Mopper K, 1989. Mechanistic Studies of organosulfur (Thiol) formation in coastal marine sediments. In: Saltzman ES,Cooper WJ (eds.). Biogenic Sulfur in the Environment. Washington DC: American Chemical Society, pp. 231-242.

    Willoughby AS, Wozniak AS, Hatcher PG, 2014. A molecular-level approach for characterizing water-insoluble components of ambient organic aerosol particulates using ultrahigh-resolution mass spectrometry. Atmospheric Chemistry and Physics, 14(18):10299-10314. DOI: 10.5194/acp-14-10299-2014.

    Wolff EW, Barbante C, Becagli S,et al., 2010. Changes in environment over the last 800,000 years from chemical analysis of the EPICA Dome C ice core. Quaternary Science Reviews, 29(1-2):285-295. DOI: 10.1016/j.quascirev.2009.06.013.

    Wozniak AS, Willoughby AS, Gurganus SC,et al., 2014. Distinguishing molecular characteristics of aerosol water soluble organic matter from the 2011 trans-North Atlantic US GEOTRACES cruise.Atmospheric Chemistry and Physics, 14(16): 8419-8434. DOI:10.5194/acp-14-8419-2014.

    Xu JZ, Zhang Q, Wang ZB,et al., 2015. Chemical composition and size distribution of summertime PM2.5at a high altitude remote location in the northeast of the Qinghai-Xizang (Tibet) Plateau: insights into aerosol sources and processing in free troposphere. Atmospheric Chemistry and Physics, 15(9): 5069-5081. DOI:10.5194/acp-15-5069-2015.

    Yee LD, Kautzman KE, Loza CL,et al., 2013. Secondary organic aerosol formation from biomass burning intermediates: phenol and methoxyphenols. Atmospheric Chemistry and Physics, 13(16):8019-8043. DOI: 10.5194/acp-13-8019-2013.

    Zhao Y, Hallar AG, Mazzoleni LR, 2013. Atmospheric organic matter in clouds: exact masses and molecular formula identification using ultrahigh-resolution FT-ICR mass spectrometry. Atmospheric Chemistry and Physics, 13(24): 12343-12362. DOI: 10.5194/acp-13-12343-2013.

    猜你喜歡
    賢德溫習(xí)曾子
    命題作文“溫故”寫作指導(dǎo)與佳作示例
    石塘老嫗
    愛思特美容醫(yī)院集團(tuán)董事長萬賢德:醫(yī)者仁心,為愛前行
    曾子殺豬
    立德樹人是教育的根本
    不溫習(xí)煩惱是人生的智慧
    溫故知新
    曾子殺豬
    快樂語文(2016年29期)2016-02-28 09:03:36
    曾子殺人
    漫畫論語(一)
    日韩电影二区| 少妇人妻一区二区三区视频| 黄色日韩在线| 久久鲁丝午夜福利片| 亚洲三级黄色毛片| 极品教师在线视频| 麻豆成人午夜福利视频| 日韩成人av中文字幕在线观看| 久久久精品欧美日韩精品| 国产亚洲最大av| 高清av免费在线| 日韩制服骚丝袜av| 七月丁香在线播放| 黄片wwwwww| 国产 一区精品| 亚洲精品日韩av片在线观看| 日本与韩国留学比较| 国产乱人视频| 永久免费av网站大全| 国产成人精品一,二区| 亚洲精品中文字幕在线视频 | 美女cb高潮喷水在线观看| 亚洲精品影视一区二区三区av| 欧美激情在线99| 国产成人a∨麻豆精品| 性插视频无遮挡在线免费观看| 久久韩国三级中文字幕| 久久人人爽av亚洲精品天堂 | 青春草亚洲视频在线观看| 久久久成人免费电影| 少妇人妻 视频| 一级毛片 在线播放| 99久久中文字幕三级久久日本| 免费电影在线观看免费观看| 亚洲国产精品专区欧美| 一级片'在线观看视频| 亚洲av福利一区| 91久久精品国产一区二区三区| 久久久精品欧美日韩精品| 国产免费视频播放在线视频| 狂野欧美激情性xxxx在线观看| 99久久中文字幕三级久久日本| 亚洲伊人久久精品综合| 国产伦精品一区二区三区视频9| 国内揄拍国产精品人妻在线| 哪个播放器可以免费观看大片| 久久精品久久久久久噜噜老黄| 九九久久精品国产亚洲av麻豆| 国产伦精品一区二区三区视频9| 18禁裸乳无遮挡动漫免费视频 | 午夜精品国产一区二区电影 | 黄色日韩在线| 午夜福利在线观看免费完整高清在| 成年女人看的毛片在线观看| 午夜福利网站1000一区二区三区| 日韩av不卡免费在线播放| freevideosex欧美| 午夜福利在线在线| 少妇裸体淫交视频免费看高清| xxx大片免费视频| 有码 亚洲区| 国产精品精品国产色婷婷| 日本av手机在线免费观看| 丰满乱子伦码专区| 精品久久久久久久久av| xxx大片免费视频| 亚洲国产欧美在线一区| 亚州av有码| 免费不卡的大黄色大毛片视频在线观看| 我的女老师完整版在线观看| av免费在线看不卡| 国产伦精品一区二区三区视频9| 在线观看三级黄色| 免费不卡的大黄色大毛片视频在线观看| 大片电影免费在线观看免费| 亚洲av福利一区| 有码 亚洲区| 欧美性猛交╳xxx乱大交人| 青青草视频在线视频观看| 视频中文字幕在线观看| 校园人妻丝袜中文字幕| 日日摸夜夜添夜夜爱| 男人和女人高潮做爰伦理| 麻豆乱淫一区二区| 蜜桃亚洲精品一区二区三区| 日日啪夜夜爽| 中文在线观看免费www的网站| 新久久久久国产一级毛片| 国产色爽女视频免费观看| 日韩视频在线欧美| 久久久精品免费免费高清| 精品一区二区三卡| 日韩在线高清观看一区二区三区| 99re6热这里在线精品视频| 亚洲成色77777| 国产精品一区二区性色av| 中文欧美无线码| 亚洲精品色激情综合| 亚洲精品国产成人久久av| 日本爱情动作片www.在线观看| 天美传媒精品一区二区| 欧美zozozo另类| 色播亚洲综合网| 国产淫片久久久久久久久| 男人狂女人下面高潮的视频| 国产大屁股一区二区在线视频| 精品久久久噜噜| 精品少妇黑人巨大在线播放| 久久久久国产网址| 国产有黄有色有爽视频| 男人舔奶头视频| 午夜福利在线在线| 少妇人妻 视频| 日本猛色少妇xxxxx猛交久久| 亚洲最大成人av| 少妇裸体淫交视频免费看高清| 2021少妇久久久久久久久久久| 久久精品夜色国产| 成年av动漫网址| 国产一区有黄有色的免费视频| 成人一区二区视频在线观看| 人人妻人人爽人人添夜夜欢视频 | 免费不卡的大黄色大毛片视频在线观看| 久久精品综合一区二区三区| 国产视频首页在线观看| 欧美zozozo另类| 国内精品宾馆在线| 热re99久久精品国产66热6| 亚洲国产成人一精品久久久| 最近最新中文字幕大全电影3| 美女被艹到高潮喷水动态| 国产一区二区三区综合在线观看 | 亚洲精品成人av观看孕妇| 晚上一个人看的免费电影| 极品少妇高潮喷水抽搐| 免费看不卡的av| 国产白丝娇喘喷水9色精品| 国产成人精品久久久久久| 国产精品偷伦视频观看了| 2021天堂中文幕一二区在线观| 国内揄拍国产精品人妻在线| 丰满人妻一区二区三区视频av| 夫妻午夜视频| 日韩成人av中文字幕在线观看| 亚洲av免费高清在线观看| 少妇熟女欧美另类| 精品亚洲乱码少妇综合久久| 国产精品人妻久久久久久| 色网站视频免费| 国产真实伦视频高清在线观看| 精品午夜福利在线看| 久久精品久久精品一区二区三区| 久久午夜福利片| 久久精品国产亚洲网站| 国产日韩欧美亚洲二区| 久久亚洲国产成人精品v| 99视频精品全部免费 在线| 欧美亚洲 丝袜 人妻 在线| 国产成人91sexporn| 欧美激情在线99| 国产淫片久久久久久久久| 亚洲,一卡二卡三卡| 亚洲精品影视一区二区三区av| 少妇 在线观看| 久久久a久久爽久久v久久| 精品少妇黑人巨大在线播放| 日本免费在线观看一区| 国产一区二区三区av在线| xxx大片免费视频| 嫩草影院入口| 日本黄色片子视频| 丝袜喷水一区| 久久久久久久久久久免费av| 亚洲激情五月婷婷啪啪| 99热网站在线观看| 一级二级三级毛片免费看| 国产精品一区www在线观看| 欧美成人午夜免费资源| 亚洲精华国产精华液的使用体验| 亚洲成人av在线免费| 亚洲精品久久久久久婷婷小说| 最近最新中文字幕免费大全7| 青春草亚洲视频在线观看| av国产久精品久网站免费入址| 久久久久性生活片| 精品人妻一区二区三区麻豆| 秋霞伦理黄片| 高清午夜精品一区二区三区| 免费观看a级毛片全部| 七月丁香在线播放| 超碰av人人做人人爽久久| 好男人在线观看高清免费视频| 在线亚洲精品国产二区图片欧美 | 国产精品.久久久| 一区二区三区精品91| 免费电影在线观看免费观看| 免费大片18禁| 午夜激情福利司机影院| 97在线人人人人妻| 日日摸夜夜添夜夜添av毛片| 亚洲欧美精品自产自拍| 国产精品秋霞免费鲁丝片| 国产亚洲午夜精品一区二区久久 | 国产成人一区二区在线| 交换朋友夫妻互换小说| 日日撸夜夜添| 一二三四中文在线观看免费高清| 青春草国产在线视频| 欧美高清成人免费视频www| 日本-黄色视频高清免费观看| 欧美日韩在线观看h| 日韩强制内射视频| 久久久久网色| 涩涩av久久男人的天堂| 国产黄片美女视频| 深夜a级毛片| 青青草视频在线视频观看| 久久久久精品性色| 亚洲不卡免费看| 日韩在线高清观看一区二区三区| 欧美三级亚洲精品| 精品久久久久久电影网| 青春草亚洲视频在线观看| 简卡轻食公司| videos熟女内射| 国产成人精品福利久久| 亚洲欧美精品自产自拍| 婷婷色麻豆天堂久久| 亚洲美女视频黄频| 国产精品av视频在线免费观看| 观看美女的网站| 亚洲欧美一区二区三区国产| 精品人妻一区二区三区麻豆| 国产白丝娇喘喷水9色精品| 精品久久久久久久久亚洲| 青青草视频在线视频观看| 欧美丝袜亚洲另类| 97超碰精品成人国产| 欧美亚洲 丝袜 人妻 在线| 色哟哟·www| 国产精品嫩草影院av在线观看| 日本三级黄在线观看| 91狼人影院| 欧美亚洲 丝袜 人妻 在线| 啦啦啦在线观看免费高清www| 国模一区二区三区四区视频| 在线亚洲精品国产二区图片欧美 | 精品熟女少妇av免费看| 亚洲欧洲国产日韩| 久久97久久精品| 极品教师在线视频| 看免费成人av毛片| 久久精品久久久久久噜噜老黄| 日日摸夜夜添夜夜爱| 免费看日本二区| 精品酒店卫生间| 少妇人妻一区二区三区视频| 激情 狠狠 欧美| 简卡轻食公司| 波多野结衣巨乳人妻| 亚洲一区二区三区欧美精品 | av在线app专区| 女人久久www免费人成看片| av免费观看日本| 一级毛片久久久久久久久女| 欧美3d第一页| 亚洲在久久综合| 国产真实伦视频高清在线观看| 午夜免费鲁丝| 国产视频内射| 色5月婷婷丁香| 亚洲精品乱码久久久久久按摩| 一级a做视频免费观看| 最近2019中文字幕mv第一页| 国产淫语在线视频| 欧美精品人与动牲交sv欧美| 91久久精品国产一区二区三区| 熟女人妻精品中文字幕| 18禁在线播放成人免费| 最近的中文字幕免费完整| 赤兔流量卡办理| 日日啪夜夜撸| 久久ye,这里只有精品| 中文乱码字字幕精品一区二区三区| av在线老鸭窝| av.在线天堂| 九九久久精品国产亚洲av麻豆| 97热精品久久久久久| 国产久久久一区二区三区| 人人妻人人澡人人爽人人夜夜| 亚洲怡红院男人天堂| 久久6这里有精品| 国产爽快片一区二区三区| 三级经典国产精品| 美女主播在线视频| 国产高清有码在线观看视频| 性色av一级| 内射极品少妇av片p| 亚洲成人中文字幕在线播放| 久久99热这里只频精品6学生| 蜜桃亚洲精品一区二区三区| 九草在线视频观看| 国产精品一及| 国产免费一区二区三区四区乱码| 日日啪夜夜爽| 三级国产精品欧美在线观看| 一边亲一边摸免费视频| 最近的中文字幕免费完整| av在线亚洲专区| 日本午夜av视频| 国产成人免费无遮挡视频| 狠狠精品人妻久久久久久综合| 国产黄片美女视频| www.色视频.com| 精品久久久久久久末码| 老师上课跳d突然被开到最大视频| 亚洲国产高清在线一区二区三| 国产男人的电影天堂91| 日本欧美国产在线视频| a级一级毛片免费在线观看| av在线观看视频网站免费| 青青草视频在线视频观看| 女的被弄到高潮叫床怎么办| 波野结衣二区三区在线| 成人国产av品久久久| 国产精品无大码| 综合色av麻豆| 久久99热6这里只有精品| 欧美激情久久久久久爽电影| 精品一区二区免费观看| 色视频在线一区二区三区| 久久精品综合一区二区三区| 精华霜和精华液先用哪个| 亚洲无线观看免费| 晚上一个人看的免费电影| 男女国产视频网站| 噜噜噜噜噜久久久久久91| 老司机影院成人| 波多野结衣巨乳人妻| 国产一区二区三区av在线| 91精品伊人久久大香线蕉| tube8黄色片| 亚洲一区二区三区欧美精品 | 久热这里只有精品99| 亚洲欧美日韩无卡精品| 在线观看免费高清a一片| 国产大屁股一区二区在线视频| 22中文网久久字幕| 观看美女的网站| av黄色大香蕉| 我的老师免费观看完整版| av在线天堂中文字幕| 美女高潮的动态| 国产精品一区二区在线观看99| 18禁裸乳无遮挡动漫免费视频 | 22中文网久久字幕| 国产综合精华液| 丝瓜视频免费看黄片| 中文天堂在线官网| 美女xxoo啪啪120秒动态图| 久久精品国产a三级三级三级| 插逼视频在线观看| 国产一区二区亚洲精品在线观看| 成年免费大片在线观看| 国产精品一区二区在线观看99| 国产成人精品婷婷| 欧美3d第一页| 制服丝袜香蕉在线| 欧美性猛交╳xxx乱大交人| 国产久久久一区二区三区| 午夜福利网站1000一区二区三区| 国产精品精品国产色婷婷| 亚洲av在线观看美女高潮| 亚洲精品久久久久久婷婷小说| 日本av手机在线免费观看| 最近最新中文字幕大全电影3| 两个人的视频大全免费| 丝袜美腿在线中文| 成人亚洲精品av一区二区| 边亲边吃奶的免费视频| 综合色丁香网| 极品少妇高潮喷水抽搐| 制服丝袜香蕉在线| 亚洲av一区综合| 男人添女人高潮全过程视频| 国产一区二区三区av在线| 国产在视频线精品| 97超碰精品成人国产| 日本wwww免费看| 国产精品99久久99久久久不卡 | 最后的刺客免费高清国语| 亚洲天堂国产精品一区在线| 国产黄色免费在线视频| 亚洲aⅴ乱码一区二区在线播放| 亚洲在线观看片| 日韩中字成人| 日韩免费高清中文字幕av| 国产精品国产av在线观看| 精品国产三级普通话版| 水蜜桃什么品种好| 五月开心婷婷网| 自拍欧美九色日韩亚洲蝌蚪91 | 国产大屁股一区二区在线视频| 国内少妇人妻偷人精品xxx网站| 午夜福利视频精品| 成人欧美大片| 在线观看一区二区三区| 麻豆成人午夜福利视频| 天天一区二区日本电影三级| 国产av不卡久久| 美女视频免费永久观看网站| 亚洲av日韩在线播放| 天美传媒精品一区二区| 欧美潮喷喷水| 亚洲欧洲国产日韩| 久久人人爽人人片av| 九九在线视频观看精品| 深爱激情五月婷婷| 免费黄频网站在线观看国产| freevideosex欧美| 春色校园在线视频观看| 免费看光身美女| 一边亲一边摸免费视频| 蜜桃久久精品国产亚洲av| 国产爱豆传媒在线观看| 亚洲精品影视一区二区三区av| 免费av观看视频| 亚洲自偷自拍三级| 美女视频免费永久观看网站| av在线蜜桃| 免费观看无遮挡的男女| 国产在线男女| 亚洲自偷自拍三级| 狠狠精品人妻久久久久久综合| 欧美精品一区二区大全| videossex国产| 内射极品少妇av片p| 日本猛色少妇xxxxx猛交久久| 国产乱人偷精品视频| 亚洲av国产av综合av卡| 国产精品嫩草影院av在线观看| 成人亚洲精品一区在线观看 | av在线观看视频网站免费| 日本欧美国产在线视频| 国产毛片a区久久久久| 国产精品三级大全| 人妻 亚洲 视频| 尤物成人国产欧美一区二区三区| 1000部很黄的大片| 校园人妻丝袜中文字幕| 日韩一区二区视频免费看| 少妇人妻 视频| 超碰97精品在线观看| 交换朋友夫妻互换小说| 王馨瑶露胸无遮挡在线观看| 麻豆成人av视频| 精品一区在线观看国产| 午夜精品一区二区三区免费看| 日韩制服骚丝袜av| 嘟嘟电影网在线观看| 亚洲激情五月婷婷啪啪| 毛片女人毛片| 少妇高潮的动态图| 久久久精品94久久精品| 日本一本二区三区精品| 国产一区二区在线观看日韩| 狂野欧美白嫩少妇大欣赏| 在线a可以看的网站| 听说在线观看完整版免费高清| 男女那种视频在线观看| eeuss影院久久| 美女高潮的动态| 国产成人精品久久久久久| 国产黄a三级三级三级人| 中文字幕免费在线视频6| 九九在线视频观看精品| 亚洲一级一片aⅴ在线观看| 久久精品久久久久久久性| 国内少妇人妻偷人精品xxx网站| 欧美日韩国产mv在线观看视频 | 亚洲av不卡在线观看| 亚洲精品视频女| 亚洲精品国产av成人精品| 精品酒店卫生间| 观看美女的网站| 久久亚洲国产成人精品v| 一级a做视频免费观看| 久久精品国产亚洲av天美| 久久99蜜桃精品久久| 国产乱来视频区| 三级国产精品欧美在线观看| 日韩欧美精品免费久久| 看免费成人av毛片| 欧美日韩视频高清一区二区三区二| 久久久欧美国产精品| 日韩av免费高清视频| 高清在线视频一区二区三区| 3wmmmm亚洲av在线观看| 亚洲成人一二三区av| 国产精品偷伦视频观看了| 国产乱来视频区| 免费高清在线观看视频在线观看| 人妻少妇偷人精品九色| 国内精品美女久久久久久| 亚洲综合精品二区| 精品国产露脸久久av麻豆| 亚洲国产最新在线播放| 国产黄片美女视频| 欧美激情在线99| 不卡视频在线观看欧美| 欧美一区二区亚洲| 色5月婷婷丁香| 久久精品综合一区二区三区| 在线观看一区二区三区激情| 成人国产麻豆网| 18禁动态无遮挡网站| 亚洲成人精品中文字幕电影| 久久精品夜色国产| 亚洲欧美一区二区三区黑人 | 日韩视频在线欧美| 七月丁香在线播放| 内地一区二区视频在线| 亚洲成人中文字幕在线播放| 女人被狂操c到高潮| 中文欧美无线码| 欧美3d第一页| 亚洲精品,欧美精品| 韩国av在线不卡| 日韩欧美 国产精品| 日韩免费高清中文字幕av| 大陆偷拍与自拍| 国产成人a∨麻豆精品| 午夜免费男女啪啪视频观看| 成人特级av手机在线观看| 成人午夜精彩视频在线观看| 九色成人免费人妻av| 日韩视频在线欧美| 亚洲内射少妇av| 日韩一区二区视频免费看| 色哟哟·www| 小蜜桃在线观看免费完整版高清| 欧美另类一区| 日韩欧美一区视频在线观看 | 午夜爱爱视频在线播放| 国产精品久久久久久久电影| 亚洲av免费高清在线观看| 两个人的视频大全免费| 在线免费十八禁| 国产精品国产三级专区第一集| 精品人妻熟女av久视频| 男女边摸边吃奶| 成年免费大片在线观看| 欧美日韩视频精品一区| 蜜桃久久精品国产亚洲av| 在线观看一区二区三区| 亚洲国产精品国产精品| 一级毛片 在线播放| av黄色大香蕉| 国产欧美另类精品又又久久亚洲欧美| 欧美一级a爱片免费观看看| 亚州av有码| 国产探花在线观看一区二区| 中文精品一卡2卡3卡4更新| 可以在线观看毛片的网站| 国产亚洲最大av| 91精品一卡2卡3卡4卡| 日韩强制内射视频| 国产在线男女| 久久人人爽av亚洲精品天堂 | 看免费成人av毛片| 国产成人免费无遮挡视频| av天堂中文字幕网| 一区二区三区乱码不卡18| 夜夜看夜夜爽夜夜摸| 久久久久网色| 亚洲精品视频女| 亚洲精品456在线播放app| 成人国产麻豆网| 丝袜喷水一区| 午夜激情久久久久久久| 少妇的逼水好多| 青青草视频在线视频观看| 亚洲最大成人中文| 日日摸夜夜添夜夜爱| 一级毛片黄色毛片免费观看视频| 久久久久网色| 汤姆久久久久久久影院中文字幕| 男人狂女人下面高潮的视频| 看非洲黑人一级黄片| 中文字幕人妻熟人妻熟丝袜美| 久久久国产一区二区| 另类亚洲欧美激情| 色视频在线一区二区三区| 成年版毛片免费区| 18禁在线无遮挡免费观看视频| 亚洲成人av在线免费| 亚洲精品日本国产第一区| 亚洲av国产av综合av卡| 又爽又黄无遮挡网站| 精品国产三级普通话版| 国产乱人偷精品视频| 国产成人精品婷婷| 18+在线观看网站| 午夜亚洲福利在线播放| 成年版毛片免费区| 18禁裸乳无遮挡免费网站照片| 在线看a的网站| 99热6这里只有精品| 视频区图区小说| 国产精品麻豆人妻色哟哟久久| 欧美国产精品一级二级三级 | 国产免费一区二区三区四区乱码| 国产高清不卡午夜福利| 日韩亚洲欧美综合| 欧美亚洲 丝袜 人妻 在线|