• <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 ?

    負載納米TiO2石英砂功能集料-水泥石的界面粘結(jié)性能

    2024-05-23 18:14:51王功勛李雄鄧靜祝明橋屈鋒
    土木建筑與環(huán)境工程 2024年2期

    王功勛 李雄 鄧靜 祝明橋 屈鋒

    DOI:?10.11835/j.issn.2096-6717.2022.002

    Received: 2021?08?24

    Foundation items: the State Scholarship Fund (No. 201709480008); Hunan Province Education Scientific Project (No.19A164); National Undergraduate Research and Creative Experiment Project (No. S202010534006)

    Author brief: WANG Gongxun (1979-?), PhD, associate professor, main research interest: new construction materials, E-mail: wanggx@hnust.edu.cn.

    Interfacial bonding characteristics between quartz sand supported nano-TiO2functional aggregates and cement paste

    WANG Gongxuna,b,?LI Xionga,?DENG Jinga,?ZHU Mingqiaoa,b?QU Fenga

    (a. School of Civil Engineering;?b. Hunan Engineering Research Center for Intelligently Prefabricated Passive House, Hunan University of Science and Technology, Xiangtan 411201, Hunan, P. R. China)

    Abstract: Photocatalytic cement-based material is one of the research hotspots of advanced building functional materials, but TiO2cement-based composites prepared by the traditional internal mixing method have low effective utilization rate of TiO2and poor economic benefits. To solve this problem, cement mortar with quartz sand supported TiO2(QST) aggregates were prepared and the effects of the QST aggregates on the drying shrinkage performance of the cement mortar was studied. The interfacial bond strength between the QST aggregates and the cement stone was measured using the pull-out strength method. The effects of the nano TiO2on the hydration products and pore structure of the interfacial transition zone (ITZ) between the aggregates and the cement stone were studied via SEM, EDS and MIP methods. Compared with ordinary quarz sand aggregates, the QST aggregates can reduce the drying shrinkage of the cement mortar and improve the interfacial adhesion between the aggregates and the cement stone. The nano TiO2that was loaded onto the surface of the aggregates promotes the hydration of the cement paste, reduces the enrichment of Ca(OH)2in the ITZ, and refines the pore structure of the ITZ between the cement stone and the aggregates.

    Keywords: functional aggregate;?interfacial bond strength;?interfacial transaction zone (ITZ);?hydration product;?pore structure

    摘要:光催化水泥基材料是先進建筑功能材料的研究熱點之一,但傳統(tǒng)內(nèi)摻法制備的TiO2-水泥基復(fù)合材料中TiO2有效利用率低、經(jīng)濟效益差。針對此問題,采用負載法制備納米TiO2功能集料(QST),并將QST集料負載于普通水泥砂漿表面。研究QST集料對水泥砂漿干縮性能的影響,通過拉拔法測試QST集料與水泥石的界面粘結(jié)力;采用SEM、EDS、MIP等微觀測試方法,研究納米TiO2對集料-水泥石界面過渡區(qū)水化產(chǎn)物、孔結(jié)構(gòu)的影響。結(jié)果表明:與普通石英砂集料相比,表面負載納米TiO2的石英砂功能集料可減少水泥砂漿的干縮,提高集料-水泥石的界面粘結(jié)力。在QST集料-水泥石的界面過渡區(qū),納米TiO2促進了水泥漿體的水化,減少了界面過渡區(qū)Ca(OH)2的富集,細化并改善了界面過渡區(qū)的孔結(jié)構(gòu)。

    關(guān)鍵詞:功能集料;界面黏結(jié)力;界面過渡區(qū);水化產(chǎn)物;孔結(jié)構(gòu)

    中圖分類號:TU528.01 ????文獻標志碼:A ????文章編號:2096-6717(2024)02-0176-12

    1 Introduction

    Photocatalytic properties of nano-TiO2have important and practical significance for air pollution control?[1], therefore, photocatalytic cement-based materials represent a critical industrial opportunity. Nowadays, many researchers have focused on the photocatalytic properties of nano-TiO2cement-based materials used in buildings and pavement?[2-5]. Some investigations have concentrated on the effects of the photocatalyst environment, such as humidity?[6], and illumination intensity of photocatalytic efficiency?[7]. Similarly, the effects of nano-TiO2on the hydration of cement have also been studied?[8-10]. Despite the effectiveness of TiO2as a photocatalyst, its use in practical applications is relatively small. The common application method in construction is to mix nano-TiO2directly into the cement paste or concrete in Fig.1(a)?[11-14]. Since photocatalysis is a surface phenomenon, influenced by the chemistry of the immediate environment, the photocatalytic effects of nano-TiO2can only be effectively activated under exposure to ultraviolet radiation?[15-16]. When TiO2is covered by cement, only a small portion of the TiO2s surface is exposed in the surface layer. This results in a waste of the utilization and economic effectiveness of the relatively expensive nano-TiO2. The concrete surface must be engineered to maximize the photocatalysts accessibility (to reactants) and activation (illumination); therefore, increasing the effective exposure area of the nano-TiO2and improving the photocatalytic efficiency of the nano-TiO2. These are important means in order to solve the above problems and are also an important research direction for nano-TiO2cement-based composite functional materials?[17-19].

    Wang, et al.[20]proposed a surface mounting for a functional aggregate loaded with nano-TiO2in Fig.1(b)???to address these problems. Their research focused on the preparation process and the photocatalytic performance of the loaded nano-TiO2aggregate mortar. The results showed that the photocatalytic efficiency of the loaded TiO2aggregate mortar is considerably higher than that of the traditionally dispersed nano-doped TiO2mortar?[21-22]. The embedding depth (exposed area) of the loaded TiO2aggregates directly affects the photocatalytic efficiency and the bonding strength between the aggregates and the mortar?[23-24].

    (a) Conventional TiO2dispersions in concrete

    (b) Surface-mounted TiO2-aggregate composites on photocatalytic concrete

    Fig. 1 TiO2mixed directly into the concrete and quartz sand supported TiO2(QST)[20]

    Under normal service conditions, the interface between the loaded TiO2aggregates and the cement stone may be considered the weak zone due to the influence of environmental factors such as moisture movement potentially leading to phase precipitation?[25], and expansive crystallization?[26], through variations in temperature, humidity, freezing, and thawing?[27-28]. Nano-TiO2has no pozzolanic activity and does not directly participate in the hydration reaction of the cement?[29-30]; however, its nano particles contain high surface area sites for the nucleation of cement hydration products promoting the hydration of cement, enhancing space filling, and indirectly influencing the bonding characteristics of the interface?[31-34].

    This work focuses on the bond properties of the interface between loaded nano-TiO2aggregates and cement under the conditions of dry shrinkage, dry and wet cycle, and studies the microstructure of the interface region between the aggregates loaded with nano-TiO2and the cement stone in order to better understand the role of nano-TiO2on the interface between the aggregates and the cement.

    2 Experimental details

    2.1 Raw materials

    The aggregates used as TiO2supports are ISO standard sand (ISO 679:2009) produced from Leucate, France (designated FS). The particle size of the quartz sand is 1-2 mm. Titanium tetra-isopropoxide (TTIP, 99.9%), acetic acid (CH3COOH, 99.6%), absolute ethanol (C2H5OH, 99.9%), NaOH (sodium hydroxide, 0.1 mol/L), were purchased from Sigma-Aldrich. Deionized water (18.2 MΩ·cm) was used throughout the TiO2hydrosol preparation process.

    The sand and CEM I 52,5N (PC) used to produce the mortar conforms to BS EN 196-1 (BSI, 2005) and BS EN 197-1 (BSI, 2011), respectively.

    2.2 Methods

    2.2.1 Preparation of quartz sand supported TiO2(QST) aggregates

    The TiO2hydrosol preparation process and the QST aggregate preparation followed the method previously described by reference [11]. The main steps are summarized here. In order to activate the quartz surface, the sand aggregates were first treated with 0.1 mol/L NaOH for 24 h followed by washing with deionized water three times. The activated sands were then immersed in anatase TiO2hydrosol suspensions for 5 minutes at room temperature. The resulting composites were then separated by filtration and dried at 105 ℃ for 30 minutes. The process above was repeated for the required 6 coating cycles. In the final step, all samples were dried at 105 °C for 24 hours, then washed three times using deionized water before the final drying step. In reference [11], Yang , et al. confirmed that the TiO2 loading increases with the number of coating cycles. This translates to a loading thickness (d) of up to 1 850 nm at a TiO2/SiO2mass fraction of 0.61% after 6 coating cycles. Fig. 2 shows an SEM micrograph of the QST aggregates. TiO2can be observed on the aggregate surface as agglomerated nano-TiO2.

    2.2.2 Preparation of QST cement mortar

    Portland cement-sand-water were mixed in a mass ratio of 1:3:0.5 according to the procedures described in BS EN 196-1:2005[35]. Mortar samples with a size of 100 mm×50 mm×50 mm were prepared for the drying shrinkage test. The process to prepare the aggregate exposed mortar is as follows:

    1) Aggregates were sprinkled onto a 50 mm wide adhesive tape to ensure a specific amount of single layer aggregates were mounted to each test sample, the coated sand was pre-laid onto a 100 mm long adhesive tape. Typically, this enables 9 g to 10 g of the coated sand to be mounted.

    2) Aggregate mounting: the aggregate-coated tape was then placed onto the freshly as-cast surface of the mortar substrate and pressed into the surface under the load of a concrete block to give the specified aggregate exposure (via the depth of embedding). The samples were demoulded after 24 hours and cured under standard conditions in water for 7 days. The tape was then peeled off from the hardened mortar, leaving a single layer of aggregates exposed onto the top surface of the mortar samples.

    2.2.3 Measurement

    1) Drying shrinkage test of the mortar. Lengthlxand massmxof the samples prepared for the drying shrinkage test were measured at various ages (xdays) under 20 ℃ and 50% RH condition;xis the curing day since the samples were moved into the curing room (x=0, 1, 4, 7, 14, 21, and 28).

    2) Dry-wet cycle test of the mortar. After applying the aggregate coating, the samples were demoulded after curing at 20 ℃ and 100% RH conditions for 24 hours, and further cured in water for 6 days. Then, the samples were dried at 20 ℃ for 24 hours and the copper heads were pasted onto the sample ends using Araldite resin. When the resin hardened after 30 minutes, the samples were moved to the curing room (20 ℃,RH=50%) and the initial lengthl0and the massm0were measured before they were immersed in water at 20 ℃. The dry-wet cycle (immersion for 8 hours, followed by drying at 60 ℃ for 8 hours) was repeated 200 times, after which the final length and the mass of sample was measured.

    3) Pull-out strength test between the QST aggregates and the cement paste. Samples were dried at 20 ℃ for 24 hours before the pull-out strength test was performed, as follows: Araldite resin was applied to the mortar and test equipment dolly. The samples were scratched prior to pressing the mortar and the dolly together in Fig. 3. After the resin set, a direct tensile load was applied to measure the bonding strength between the aggregates and the cement paste. The loading rate of the pull-out strength test was 20 psi/s.

    4) Characterization. The samples?morphology was observed using a scanning electron microscope (SEM, Zeiss EVO MA10) equipped with an energy dispersive X-ray spectrometry (EDS, Oxford INCA) for elemental composition analyses.

    The mercury intrusion porosimetry (MIP) method was used to analyze the pore structure of the cement paste samples via the equipment of the AutoPore Ⅳ 9510, Micromeritics. The boundary conditions of the pressure and the pore sizes of the MIP equipment are 0.10-61 000 psia and 5-300 000 nm, respectively.

    3 Results and discussion

    3.1 Drying shrinkage ratio

    The potential effects of nano-TiO2on the hydration process and pore structure in the ITZ of QST and cement paste, along with its super-hydrophilic properties, could have a significant impact on the water transport properties in the ITZ. However, another factor to consider is the consequences of the interfacial bonding strength between the aggregates and the mortar when considering the relative movement of the porous cement matrix and the dimensionally stable aggregates. Based on the influences of nano-TiO2on the hydration properties of the cement-based materials, the drying shrinkage of the hardened cement paste has been investigated and discussed.

    Fig.4 shows the variations in the samples mass of various mortar samples coated by French sand (FS) and quartz sand supported TiO2(QST) aggregates. Fig.5 is the curve of the drying shrinkage rate of different mortar samples coated by French sand (FS) and quartz sand supported TiO2(QST) aggregates.

    It can be concluded that the weight loss of the FS mortar was higher than that of the QST mortar as shown in Fig.4. In Fig.5, the drying shrinkage rate of the QST mortar is smaller than that of the FS mortar. The results match that of Zhang, et al.[36], which concluded that the addition of nano-TiO2can reduce the water loss of the sample. Shimomura, et al.[37], Maekawa, et al.[38], and Shimomura[39], proposed a micromechanical model of drying shrinkage behavior, which was based on pore size distribution and thermodynamic behavior of the water within the pores. Part of the model involved computation of the parameterrs, defined as the radius of the pores where the meniscus forms, i.e., the pores whose radii are smaller thanrsare assumed to be filled with liquid water while pores larger than this are dry. As the drying progresses, the parameterrsdecreases. The researchers hypothesized that the smaller the parameterrs, the larger the capillary tensile forces at the meniscus (the interface between water and air), hence the higher the resulting shrinkage[40].

    Drying shrinkage of cementitious materials may be due to a higher volume of mesopores causing a higher capillary stress of the water meniscus developed within the capillary pores of the paste, resulting in a higher level of drying shrinkage. Nano-TiO2particles present pore refinement effects on the cement-based materials; thus, resulting in a much denser microstructure and a lower shrinkage value[36,41].

    3.2 Pull-out strength of the mortar

    It is observed that the pull-out strength of the QST mortar is higher than that of the FS mortar during the standard curing and the drying shrinkage conditions; however, the contrary result is observed under the dry-wet cycle condition. Regarding the hygroscopic properties, the increase of TiO2content leads to mortar with higher open porosity and water absorption coefficients?[42]. When the samples were in the dry-wet cycle conditions, the QST mortar absorbed more water and caused a higher open porosity in the bonding area between the QST aggregates and the cement paste; thus, lowering the bonding strength between the QST and the cement paste.

    3.3 Microstructure analysis

    3.3.1 SEM of the QST aggregates dropped from the surface of the mortar

    Fig.7 shows the QST dropped from the surface of the mortar. Hydration products of the binding area between the QST aggregates and the cement paste can be observed by SEM in Fig.7(b) and (c).

    Fig.8(a) shows a QST aggregate partially covered by cement hydration products. Nano-TiO2agglomeration on the surface of QST is observed in Fig.2(a) and is not found in Fig.8(a), indicating that the bonded interface saturated the SiO2surface. The chemical bonding strength between TiO2and the quartz aggregates is stronger than that of TiO2and the cement paste. Ti—O—Si chemical linkages are confirmed in the reference?[11], and TiO2accumulation has been shown on the surface in multiple agglomerated layers. Many needle-like hydration products (AFt) are observed in Fig.8(b); it is deduced that the degree of cement binding with the surface of QST is high. This is due to the nucleation effect of the TiO2accelerating the cement hydration process. In Fig.8(c), hexagonal plate hydration products are observed on the surface and are typical of Ca(OH)2. The size of these Ca(OH)2plates and their proximity to each other suggest regions of fluid filled porosity prior to failure, in which the crystallization of Ca(OH)2could have presented regions prone to cleavage and mechanical weakening.

    Fig.9 shows an SEM micrograph and EDS of a vacated site on the mortar, originally occupied by a QST particle.

    Fig.9(a) shows the recess as well as the massive crystals formed by Ca(OH)2and were observed on the cement coated QST surface. Fig.9(b) shows analytical locations and Fig.9(c) is the EDS elements spectra of the vacated area on the surface of the mortar. The primary elements within this area are Si, O, Ca, Al, and C with only a small quantity of Ti. It can be deduced that some TiO2has debonded from the aggregates, indicating that the bonding strength between TiO2and the quartz is not uniform (as previously indicated by Yang, et al. for coatings of various thicknesses)?[11]. In Fig.2(a), a non-uniform distribution of TiO2on the surface of the quartz aggregates are observed, with the possibility of multiple TiO2layers. In reference [11], Yang, et al. discussed the weaker binding of TiO2in thicker layers but emphasizes the stability of the monolayer closest to the surface.

    3.3.2 EDS of the ITZ between the aggregates and the cement paste

    In order to identify the effects of the nano-TiO2on the microstructure of the interface between the QST and the mortar, SEM images of the FS and the QST mortar were obtained. Fig.10 are the EDS spectra of the ITZ between the FS and the cement paste.

    Fig.10(a) shows the interface and the surrounding regions indicating a significant separation between the FS and the cement. Some separation regions contain a Ca-rich brightly colored substance identified as CaCO3. It is proposed that Ca(OH)2produced in the interface between the FS aggregates and the cement paste during the cement hydration process is readily carbonated within the open/porous microstructure.

    Fig.11(a) shows the scanning line position and Fig.11(b) is a partially enlarged detail of the scanning line area. The microstructure of the gap between the FS particles is loose in Fig.11(a) and (b). The elemental profiles (Fig.11(c) to (h)) indicate the presence at the interface of the primary chemical constituents of the cement, indicating that the aggregates have been squeezed into the mortar forcing the extrusion of the cement fragments into the inter-aggregate region.

    Compared to Fig.10(a), the ITZ between the QST particles and the cement paste is more compact in Fig.12(a) and (b). In Fig.10(a), a significant separation exists between the FS and the cement. In these separations, many pores and Ca-rich substances are identified as CaCO3(in Fig.10(b))and were found between the FS aggregates and the cement paste. However, an enlargement of Area 1 (Fig.12 (a)) confirms a denser microstructure compared with the FS system within the interface region. A large content of Ti (Fig.12 (c) indicates a layer of TiO2which is to be expected on the surface of the aggregates. In Fig.12(d), the content of Ti reduces significantly, Si increases, and the ratio of Ca to Si is minimal; thus, showing that the primary composition within this area is probably SiO2as well as cement hydration products. The compositions in Fig.12(f) are similar to those in Fig.12(d). In Fig.12(e), Ti does not exist, the content of Si is significantly reduced, Ca increases, and the ratio of Ca to Si is high. It shows that the primary composition within this area is more than likely the cement hydration products.

    Compared to Fig.11, the microstructure of the ITZ between the QST and the cement paste is more compact than that of the FS. The micrographs and the elemental analysis indicate a higher level of pore filling by the hydration products at the QST-cement paste interface region than in the FS system. It can be deduced that TiO2coated on the surface of the aggregates improves the degree of hydration of the cement and makes the microstructure and the interface between the aggregates and the cement denser. Hence, the pull-out strength of the QST-cement paste is higher than that of the FS-cement paste under standard curing and drying shrinkage curing conditions in Fig.6. However, the contrary results under the dry-wet cycle conditions still need further investigation.

    Fig.13(a) shows the scanning line position across the QST particle and the ITZ. Fig.13(b) is a partially enlarged detail of the scanning line area. According to Fig.13(f), it can be concluded that a layer of TiO2within the line-scanning range from 4 μm to 8 μm exists in Fig.13(b). It can again be concluded that the interface between the QST and the cement paste is filled with the hydration products of cement as seen in Fig.13. The white particle crossed by the scanning line has a high content of Ca, Al, and Fe, but a lower content of S, which is probably the hydration products of C4AF. The needle-like hydration products are AFt because they have a higher Ca, S, and Al content.

    3.3.3 Mercury intrusion porosimetry (MIP)

    The most probable and average pore sizes are important parameters of the cement pore structure and characterize the pore structure of the overall situation. The pore size distribution of the ITZ between the various aggregates and the cement paste is shown in Fig.14. Table 1 is the pore structural index of the ITZ of the QST-cement paste and the FS-cement paste.

    It shows that the most probable pore diameter of the ITZ between the QST and the cement paste is approximately 41.26 nm, which is smaller than that of the FS. The total porosity of the QST-cement stone ITZ is 17.30%, which is higher than that of the FS-cement stone ITZ. However, the average pore diameter of the QST-cement stone ITZ is smaller than that of the FS. When the aperture is larger than 200 nm, the content of the macropores in the FS-cement ITZ is more than that of the QST. In the range of 50-200 nm aperture, the pore content of the QST-?cement stone ITZ is more than that of the FS, indicating that the aggregate surface loading of TiO2refines the pore size structure of the ITZ. The content of the macropores is reduced as well. Compared with the SEM images of Fig.10(a) and Fig.12(a), it can be concluded that the ITZ of the QST-cement paste is more compact than that of the ITZ of the FS-cement paste. The MIP test proves this result. Chen, et al.[43]and others?study has also shown that nano-TiO2can significantly increase the hydration level during the initial hydration stage with small content. The nucleation effect of nano-TiO2decreases the total porosity of the hardened cement paste, reducing the pore volume primarily occurring within the capillary.

    4 Conclusion

    (1) Weight loss and drying shrinkage of the FS mortar were higher than those of the QST mortar. Nano-TiO2particles present a pore refinement effect on the cement-based materials resulting in a much denser microstructure and lower shrinkage value. Pull-out strength of the QST mortar is higher than that of the FS mortar during the standard curing and the drying shrinkage conditions; however, the contrary result is observed under the dry-wet cycle condition. Further investigation regarding this observation is needed in future research.

    (2) The high Ca(OH)2content and porous microstructure in the FS-cement ITZ reduce the bonding strength between the FS and the cement paste. The microstructure of the ITZ between the QST and the cement paste is more compact than that of the FS. TiO2coated on the surface of the aggregates improves the degree of hydration of the cement and makes the microstructure dense as well as the ITZ between the aggregates and the cement.

    Reference

    [1] ?RAMIREZ A M, DEMEESTERE K, DE BELIE N, et al. Titanium dioxide coated cementitious materials for air purifying purposes: Preparation, characterization and toluene removal potential [J]. Building and Environment, 2010, 45(4): 832-838.

    [2] ?POON C S, CHEUNG E. NO removal efficiency of photocatalytic paving blocks prepared with recycled materials [J]. Construction and Building Materials, 2007, 21(8): 1746-1753.

    [3] ?BALLARI M M, BROUWERS H J H. Full scale demonstration of air-purifying pavement [J]. Journal of Hazardous Materials, 2013, 254/255: 406-414.

    [4] ?BALLARI M M, HUNGER M, H?SKEN G, et al. NOxphotocatalytic degradation employing concrete pavement containing titanium dioxide [J]. Applied Catalysis B: Environmental, 2010, 95(3/4): 245-254.

    [5] ?ZHU Y, ZHANG J P, WANG J X, et al. Distribution and sources of air pollutants in the North China Plain based on on-road mobile measurements [J]. Atmospheric Chemistry and Physics, 2016, 16(19): 12551-12565.

    [6] ?OCHIAI T, FUJISHIMA A. Photoelectrochemical properties of TiO2photocatalyst and its applications for environmental purification [J]. Journal of Photochemistry and Photobiology C: Photochemistry Reviews, 2012, 13(4): 247-262.

    [7] ?XU H, OUYANG S, LIU L Q, et al. Recent advances in TiO2-based photocatalysis [J]. Journal of Materials Chemistry A, 2014, 2(32): 12642-12661.

    [8] ?LAI Y K, HUANG J Y, CUI Z Q, et al. Recent advances in TiO2-based nanostructured surfaces with controllable wettability and adhesion [J]. Small, 2016, 12(16): 2203-2224.

    [9] ?FOLLI A, PADE C, HANSEN T B, et al. TiO2photocatalysis in cementitious systems: Insights into self-cleaning and depollution chemistry [J]. Cement and Concrete Research, 2012, 42(3): 539-548.

    [10] ?LU Z Y, WANG Q, YIN R, et al. A novel TiO2/foam cement composite with enhanced photodegradation of methyl blue [J]. Construction and Building Materials, 2016, 129: 159-162.

    [11] ?YANG L, HAKKI A, WANG F Z, et al. Photocatalyst efficiencies in concrete technology: The effect of photocatalyst placement [J]. Applied Catalysis B: Environmental, 2018, 222: 200-208.

    [12] ?FENG S L, LIU F H, FU X, et al. Photocatalytic performances and durability of TiO2/cement composites prepared by a smear method for organic wastewater degradation [J]. Ceramics International, 2019, 45(17): 23061-23069.

    [13] ?PRAVEENKUMAR T R, VIJAYALAKSHMI M M, MEDDAH M S. Strengths and durability performances of blended cement concrete with TiO2nanoparticles and rice husk ash [J]. Construction and Building Materials, 2019, 217: 343-351.

    [14] ?MORO C, FRANCIOSO V, VELAY-LIZANCOS M. Nano-TiO2effects on high temperature resistance of recycled mortars [J]. Journal of Cleaner Production, 2020, 263: 121581.

    [15] ?JIN Q, SAAD E M, ZHANG W, et al. Quantification of NOxuptake in plain and TiO2-doped cementitious materials [J]. Cement and Concrete Research, 2019, 122: 251-256.

    [16] ?TRYBA B, JAFARI S, SILLANP?? M, et al. Influence of TiO2structure on its photocatalytic activity towards acetaldehyde decomposition [J]. Applied Surface Science, 2019, 470: 376-385.

    [17] ?CHEN K Y, LI Y, MENG X Y, et al. New integrated method to recover the TiO2component and prepare glass-ceramics from molten titanium-bearing blast furnace slag [J]. Ceramics International, 2019, 45(18): 24236-24243.

    [18] ?XU M F, BAO Y, WU K, et al. Influence of TiO2incorporation methods on NOxabatement in Engineered Cementitious Composites [J]. Construction and Building Materials, 2019, 221: 375-383.

    [19] ?YANG L, HAKKI A, ZHENG L, et al. Photocatalytic concrete for NOxabatement: Supported TiO2efficiencies and impacts [J]. Cement and Concrete Research, 2019, 116: 57-64.

    [20] ?WANG F Z, YANG L, WANG H, et al. Facile preparation of photocatalytic exposed aggregate concrete with highly efficient and stable catalytic performance [J]. Chemical Engineering Journal, 2015, 264: 577-586.

    [21] ?YANG L, HAKKI A, WANG F Z, et al. Different roles of water in photocatalytic DeNOxmechanisms on TiO2: Basis for engineering nitrate selectivity [J]. ACS Applied Materials & Interfaces, 2017, 9(20): 17034-17041.

    [22] ?HAKKI A, YANG L, WANG F, et al. The effect of interfacial chemical bonding in TiO2-SiO2composites on their photocatalytic NOxabatement performance [J]. Journal of Visualized Experiments, 2017(125): 56070.

    [23] ?BOCCI E, RIDERELLI L, FAVA G, et al. Durability of NO oxidation effectiveness of pavement surfaces treated with photocatalytic titanium dioxide [J]. Arabian Journal for Science and Engineering, 2016, 41(12): 4827-4833.

    [24] ?GUO M Z, LING T C, POON C S. Photocatalytic NOxdegradation of concrete surface layers intermixed and spray-coated with nano-TiO2: Influence of experimental factors [J]. Cement and Concrete Composites, 2017, 83: 279-289.

    [25] ?DANTAS S R A, SERAFINI R, DE OLIVEIRA ROMANO R C, et al. Influence of the nano TiO2dispersion procedure on fresh and hardened rendering mortar properties [J]. Construction and Building Materials, 2019, 215: 544-556.

    [26] ?RECHES Y, THOMSON K, HELBING M, et al. Agglomeration and reactivity of nanoparticles of SiO2, TiO2, Al2O3, Fe2O3, and clays in cement pastes and effects on compressive strength at ambient and elevated temperatures [J]. Construction and Building Materials, 2018, 167: 860-873.

    [27] ?WANG D, HOU P K, ZHANG L N, et al. Photocatalytic activities and chemically-bonded mechanism of SiO2@TiO2nanocomposites coated cement-based materials [J]. Materials Research Bulletin, 2018, 102: 262-268.

    [28] ?KARTHIKEYAN B, DHINAKARAN G. Influence of ultrafine TiO2and silica fume on performance of unreinforced and fiber reinforced concrete [J]. Construction and Building Materials, 2018, 161: 570-576.

    [29] ?GUO X, RAO L, WANG P F, et al. Photocatalytic properties of P25-doped TiO2composite film synthesized via Sol-gel method on cement substrate [J]. Journal of Environmental Sciences, 2018, 66: 71-80.

    [30] ?GUO M Z, CHEN J, XIA M, et al. Pathways of conversion of nitrogen oxides by nano TiO2incorporated in cement-based materials [J]. Building and Environment, 2018, 144: 412-418.

    [31] ?MISHRA A, MEHTA A, BASU S M. Clay supported TiO2nanoparticles for photocatalytic degradation of environmental pollutants: A review [J]. Journal of Environmental Chemical Engineering, 2018, 6(5): 6088-6107.

    [32] ?BINAS V, PAPADAKI D, MAGGOS T, et al. Study of innovative photocatalytic cement based coatings: The effect of supporting materials [J]. Construction and Building Materials, 2018, 168: 923-930.

    [33] ?PAUL S C, VAN ROOYEN A S, VAN ZIJL G P A G, et al. Properties of cement-based composites using nanoparticles: A comprehensive review [J]. Construction and Building Materials, 2018, 189: 1019-1034.

    [34] ?DANIYAL M, AKHTAR S, AZAM A. Effect of nano-TiO2on the properties of cementitious composites under different exposure environments [J]. Journal of Materials Research and Technology, 2019, 8(6): 6158-6172.

    [35] ?Methods of testing cement. Part 1: Determination of strength: BS EN 196-1:2005 [S]. London, UK: British Standards Institution, 2005.

    [36] ?ZHANG R, CHENG X, HOU P K, et al. Influences of nano-TiO2on the properties of cement-based materials: Hydration and drying shrinkage [J]. Construction and Building Materials, 2015, 81: 35-41.

    [37] ?SHIMOMURA T, MAEKAWA K. Micromechanical model for drying shrinkage of concrete based on the distribution function of porosity [C]// BAZANT Z P, CAROL I. Proc. 5th International RILEM Symposium on Creep and Shrinkage of Concrete, Barcelona, Spain, E & FN Spon, London, 1993: 133-139.

    [38] ?SHIMOMURA T, MAEKAWA K. Analysis of the drying shrinkage behaviour of concrete based on the micropore structure of concrete using a micromechanical model [J]. Magazine of Concrete Research, 1997, 49(181): 303-322.

    [39] ?SHIMOMURA T. Modelling of initial defect of concrete due to drying shrinkage [C]//Proc. CONSEC '98 Concrete Under Severe Conditions, Norway, 1998, 3: 2071-2083.

    [40] ?COLLINS F, SANJAYAN J G. Effect of pore size distribution on drying shrinking of alkali-activated slag concrete [J]. Cement and Concrete Research, 2000, 30(9): 1401-1406.

    [41] ?DUAN P, YAN C J, LUO W J, et al. Effects of adding nano-TiO2on compressive strength, drying shrinkage, carbonation and microstructure of fluidized bed fly ash based geopolymer paste [J]. Construction and Building Materials, 2016, 106: 115-125.

    [42] ?POZO-ANTONIO J S, DION?SIO A. Physical-mechanical properties of mortars with addition of TiO2nanoparticles [J]. Construction and Building Materials, 2017, 148: 261-272.

    [43] ?CHEN J, KOU S C, POON C S. Hydration and properties of nano-TiO2blended cement composites [J]. Cement and Concrete Composites, 2012, 34(5): 642-649.

    (編輯??胡英奎)

    亚洲国产看品久久| 国产欧美日韩一区二区三| 午夜免费成人在线视频| 午夜视频精品福利| 少妇 在线观看| 变态另类成人亚洲欧美熟女 | 99re在线观看精品视频| 人人妻人人澡欧美一区二区 | 欧美日韩福利视频一区二区| 久9热在线精品视频| 精品欧美国产一区二区三| 丝袜人妻中文字幕| 久久久久九九精品影院| 久久性视频一级片| 午夜精品在线福利| 后天国语完整版免费观看| 久9热在线精品视频| 制服诱惑二区| 国产熟女午夜一区二区三区| 在线观看免费午夜福利视频| 99久久国产精品久久久| 性少妇av在线| 国产单亲对白刺激| 91麻豆av在线| 午夜久久久在线观看| av天堂久久9| 人妻丰满熟妇av一区二区三区| 成人欧美大片| 亚洲午夜理论影院| 又黄又粗又硬又大视频| 欧美乱色亚洲激情| 欧美日韩精品网址| 国产亚洲av高清不卡| 在线观看免费视频日本深夜| 欧美成人免费av一区二区三区| 免费不卡黄色视频| 性少妇av在线| 一卡2卡三卡四卡精品乱码亚洲| 色av中文字幕| 国产片内射在线| 久久久久久久久免费视频了| 啦啦啦韩国在线观看视频| 午夜日韩欧美国产| 日韩国内少妇激情av| 免费无遮挡裸体视频| 亚洲三区欧美一区| 女人被躁到高潮嗷嗷叫费观| 久久人人97超碰香蕉20202| 国产成人系列免费观看| 免费av毛片视频| 老汉色av国产亚洲站长工具| 亚洲人成77777在线视频| 欧美日韩乱码在线| 亚洲五月天丁香| 如日韩欧美国产精品一区二区三区| 日韩有码中文字幕| 国产麻豆成人av免费视频| 极品人妻少妇av视频| 一卡2卡三卡四卡精品乱码亚洲| 制服人妻中文乱码| 啦啦啦韩国在线观看视频| 亚洲av片天天在线观看| 天天一区二区日本电影三级 | 日本 欧美在线| 国产av又大| 欧美色欧美亚洲另类二区 | 巨乳人妻的诱惑在线观看| 日韩精品免费视频一区二区三区| 国产欧美日韩一区二区三| www.999成人在线观看| 视频区欧美日本亚洲| 午夜亚洲福利在线播放| 国产精品久久久久久人妻精品电影| 一本久久中文字幕| 国产成人av教育| 大码成人一级视频| 在线播放国产精品三级| 看免费av毛片| 国产精品野战在线观看| 熟妇人妻久久中文字幕3abv| 国产精品1区2区在线观看.| 99久久久亚洲精品蜜臀av| 亚洲国产毛片av蜜桃av| 亚洲视频免费观看视频| 国产精品日韩av在线免费观看 | 一本大道久久a久久精品| 又紧又爽又黄一区二区| 老熟妇仑乱视频hdxx| 国产精品久久久av美女十八| 88av欧美| 俄罗斯特黄特色一大片| 一级,二级,三级黄色视频| 日韩有码中文字幕| 成熟少妇高潮喷水视频| 国内精品久久久久精免费| 一本综合久久免费| 亚洲欧美日韩另类电影网站| 丝袜在线中文字幕| 亚洲 欧美 日韩 在线 免费| 黑人巨大精品欧美一区二区mp4| 成年版毛片免费区| 欧美精品亚洲一区二区| 午夜精品国产一区二区电影| 巨乳人妻的诱惑在线观看| 中文字幕人妻丝袜一区二区| 丝袜美腿诱惑在线| 在线观看午夜福利视频| 国产麻豆69| 欧洲精品卡2卡3卡4卡5卡区| 丁香六月欧美| 岛国在线观看网站| 每晚都被弄得嗷嗷叫到高潮| 97人妻精品一区二区三区麻豆 | 成人国产一区最新在线观看| 精品国产一区二区三区四区第35| 一二三四社区在线视频社区8| 91成年电影在线观看| 中国美女看黄片| 国产麻豆69| 中文字幕最新亚洲高清| 91九色精品人成在线观看| 亚洲欧美激情在线| 神马国产精品三级电影在线观看 | 国产精品野战在线观看| 成年版毛片免费区| 大型黄色视频在线免费观看| 欧美黑人精品巨大| 精品久久久久久久毛片微露脸| 色播亚洲综合网| 久99久视频精品免费| 欧美日韩亚洲国产一区二区在线观看| 国内精品久久久久精免费| 无限看片的www在线观看| 国产一区二区三区视频了| 亚洲国产精品sss在线观看| 88av欧美| 亚洲av熟女| 嫩草影院精品99| 亚洲七黄色美女视频| 欧美成狂野欧美在线观看| 国产成人欧美在线观看| 制服人妻中文乱码| 日韩国内少妇激情av| 日本免费一区二区三区高清不卡 | 老司机午夜福利在线观看视频| 黄色a级毛片大全视频| 欧美激情久久久久久爽电影 | 欧美色视频一区免费| 色综合欧美亚洲国产小说| 一区二区三区国产精品乱码| 又紧又爽又黄一区二区| 久久国产乱子伦精品免费另类| 人人妻人人爽人人添夜夜欢视频| 国产亚洲精品久久久久5区| 欧美色视频一区免费| 色尼玛亚洲综合影院| 国产熟女xx| 999久久久精品免费观看国产| 啦啦啦免费观看视频1| 99在线人妻在线中文字幕| 日韩av在线大香蕉| 热99re8久久精品国产| 日韩欧美国产在线观看| 免费在线观看视频国产中文字幕亚洲| 国产一区二区三区视频了| 日韩欧美一区视频在线观看| 国产av精品麻豆| 久久久国产成人免费| svipshipincom国产片| 亚洲一区二区三区不卡视频| 身体一侧抽搐| 丰满的人妻完整版| 亚洲七黄色美女视频| x7x7x7水蜜桃| 午夜免费鲁丝| 9热在线视频观看99| 女人高潮潮喷娇喘18禁视频| www.999成人在线观看| 亚洲五月天丁香| 亚洲一区高清亚洲精品| 中文字幕av电影在线播放| 久久精品91蜜桃| 午夜福利一区二区在线看| 国产伦人伦偷精品视频| 国产精品美女特级片免费视频播放器 | 亚洲五月天丁香| 狂野欧美激情性xxxx| 亚洲国产欧美网| 成人av一区二区三区在线看| 久久中文看片网| 亚洲黑人精品在线| 久久久久久亚洲精品国产蜜桃av| 中文字幕av电影在线播放| 精品一区二区三区视频在线观看免费| av欧美777| 午夜亚洲福利在线播放| 极品人妻少妇av视频| 一级毛片精品| 国产99白浆流出| 欧美午夜高清在线| 国产成人精品无人区| 女人精品久久久久毛片| 黄色毛片三级朝国网站| 黄网站色视频无遮挡免费观看| 午夜a级毛片| 少妇裸体淫交视频免费看高清 | 亚洲成人免费电影在线观看| 亚洲片人在线观看| 一夜夜www| 夜夜夜夜夜久久久久| 热re99久久国产66热| 午夜福利高清视频| www.999成人在线观看| 午夜免费激情av| 色尼玛亚洲综合影院| 免费无遮挡裸体视频| 巨乳人妻的诱惑在线观看| 俄罗斯特黄特色一大片| 精品一区二区三区四区五区乱码| 一级毛片精品| ponron亚洲| 长腿黑丝高跟| 欧美乱妇无乱码| 9色porny在线观看| 精品少妇一区二区三区视频日本电影| 99re在线观看精品视频| а√天堂www在线а√下载| 日本撒尿小便嘘嘘汇集6| 波多野结衣巨乳人妻| 女人被躁到高潮嗷嗷叫费观| 午夜福利,免费看| 亚洲五月婷婷丁香| 久久人妻av系列| 国产亚洲精品久久久久久毛片| 久久精品国产亚洲av香蕉五月| 免费人成视频x8x8入口观看| 一卡2卡三卡四卡精品乱码亚洲| 欧美国产精品va在线观看不卡| 在线视频色国产色| 黄色视频,在线免费观看| 极品人妻少妇av视频| 热re99久久国产66热| 伊人久久大香线蕉亚洲五| 国产黄a三级三级三级人| 亚洲一卡2卡3卡4卡5卡精品中文| 久久国产精品人妻蜜桃| 中文亚洲av片在线观看爽| 国产精品久久久久久精品电影 | 男人操女人黄网站| 淫妇啪啪啪对白视频| 999久久久精品免费观看国产| 人人妻人人爽人人添夜夜欢视频| 国产精华一区二区三区| 9色porny在线观看| 精品一区二区三区视频在线观看免费| 激情在线观看视频在线高清| 亚洲少妇的诱惑av| 黄色视频,在线免费观看| 亚洲成a人片在线一区二区| 香蕉久久夜色| 人人妻人人澡欧美一区二区 | 好看av亚洲va欧美ⅴa在| 韩国精品一区二区三区| 视频区欧美日本亚洲| 久久这里只有精品19| 国产成人精品久久二区二区免费| 韩国精品一区二区三区| 极品教师在线免费播放| 性欧美人与动物交配| 欧美 亚洲 国产 日韩一| 亚洲国产精品sss在线观看| 国产高清有码在线观看视频 | 亚洲精品一区av在线观看| 亚洲性夜色夜夜综合| 在线av久久热| 老司机深夜福利视频在线观看| 久久国产精品男人的天堂亚洲| 亚洲一码二码三码区别大吗| 色av中文字幕| 变态另类成人亚洲欧美熟女 | 午夜久久久久精精品| 亚洲 欧美 日韩 在线 免费| 亚洲熟妇中文字幕五十中出| 日韩有码中文字幕| 亚洲国产欧美网| 在线视频色国产色| 国产成人精品无人区| 日本在线视频免费播放| 在线观看免费视频日本深夜| 黄片小视频在线播放| 香蕉国产在线看| 日日夜夜操网爽| 亚洲专区中文字幕在线| 99国产综合亚洲精品| 精品久久蜜臀av无| 午夜激情av网站| 一进一出好大好爽视频| 欧美乱妇无乱码| 真人做人爱边吃奶动态| 91成人精品电影| 两个人视频免费观看高清| 欧美国产日韩亚洲一区| 午夜两性在线视频| 老汉色av国产亚洲站长工具| 午夜老司机福利片| 欧美 亚洲 国产 日韩一| 婷婷六月久久综合丁香| 在线观看午夜福利视频| 看免费av毛片| 亚洲av成人不卡在线观看播放网| 亚洲无线在线观看| 精品久久蜜臀av无| 精品少妇一区二区三区视频日本电影| 中文字幕人妻丝袜一区二区| 精品国产一区二区久久| 不卡av一区二区三区| 日韩欧美一区二区三区在线观看| 香蕉国产在线看| 男男h啪啪无遮挡| 美女大奶头视频| 日韩高清综合在线| 一级毛片女人18水好多| 人人妻,人人澡人人爽秒播| 男女之事视频高清在线观看| 高清在线国产一区| 国产99白浆流出| 国产成人精品在线电影| 欧美丝袜亚洲另类 | 精品国内亚洲2022精品成人| 久久人人97超碰香蕉20202| 免费女性裸体啪啪无遮挡网站| 色尼玛亚洲综合影院| 亚洲精品中文字幕在线视频| 黄色视频,在线免费观看| www.精华液| 麻豆久久精品国产亚洲av| 国产精品精品国产色婷婷| 亚洲avbb在线观看| 国产午夜福利久久久久久| 国产成人精品在线电影| 人妻久久中文字幕网| 成人特级黄色片久久久久久久| 女生性感内裤真人,穿戴方法视频| 欧美黄色淫秽网站| 亚洲欧美日韩另类电影网站| 国产精品九九99| 中出人妻视频一区二区| 亚洲成人免费电影在线观看| 成人亚洲精品一区在线观看| 中出人妻视频一区二区| 日本黄色视频三级网站网址| 淫秽高清视频在线观看| 99久久综合精品五月天人人| 亚洲三区欧美一区| 91成年电影在线观看| 国产精品久久电影中文字幕| 每晚都被弄得嗷嗷叫到高潮| 免费女性裸体啪啪无遮挡网站| 91大片在线观看| 人人妻,人人澡人人爽秒播| 一个人观看的视频www高清免费观看 | 亚洲精华国产精华精| 亚洲精品av麻豆狂野| 美女免费视频网站| 桃红色精品国产亚洲av| 亚洲中文日韩欧美视频| av在线播放免费不卡| 久久九九热精品免费| 久久精品亚洲精品国产色婷小说| av视频免费观看在线观看| 国产精品美女特级片免费视频播放器 | 黑人操中国人逼视频| 午夜福利欧美成人| 亚洲色图 男人天堂 中文字幕| 又黄又粗又硬又大视频| 欧美黄色片欧美黄色片| 欧美黄色淫秽网站| 亚洲电影在线观看av| av在线天堂中文字幕| 久久影院123| av天堂在线播放| 久久精品91无色码中文字幕| 真人做人爱边吃奶动态| 日本 av在线| 美女 人体艺术 gogo| 麻豆成人av在线观看| 国产成人精品在线电影| 欧美成人性av电影在线观看| 两个人看的免费小视频| 亚洲成人精品中文字幕电影| 大香蕉久久成人网| 亚洲自偷自拍图片 自拍| 88av欧美| 中出人妻视频一区二区| 国产成人欧美| 亚洲国产欧美一区二区综合| 亚洲国产欧美网| 亚洲熟妇中文字幕五十中出| 校园春色视频在线观看| 女人高潮潮喷娇喘18禁视频| 久久久国产成人免费| 激情在线观看视频在线高清| 国产一区二区三区综合在线观看| 精品日产1卡2卡| 纯流量卡能插随身wifi吗| 人成视频在线观看免费观看| 精品久久久久久久人妻蜜臀av | 最近最新免费中文字幕在线| 亚洲午夜理论影院| 天堂动漫精品| 成人三级做爰电影| 亚洲全国av大片| 日本 欧美在线| 好看av亚洲va欧美ⅴa在| 国产成年人精品一区二区| 国产单亲对白刺激| 身体一侧抽搐| 母亲3免费完整高清在线观看| 男男h啪啪无遮挡| 久久精品国产清高在天天线| 亚洲一区高清亚洲精品| 欧美亚洲日本最大视频资源| 久久精品国产亚洲av高清一级| 日日摸夜夜添夜夜添小说| 精品国产美女av久久久久小说| 久久久久久亚洲精品国产蜜桃av| 欧美亚洲日本最大视频资源| 母亲3免费完整高清在线观看| 色播在线永久视频| 亚洲,欧美精品.| 欧美成人免费av一区二区三区| 久久人人97超碰香蕉20202| 18禁裸乳无遮挡免费网站照片 | 天堂影院成人在线观看| 涩涩av久久男人的天堂| 久久久国产成人免费| 一级黄色大片毛片| 搡老妇女老女人老熟妇| 久久国产亚洲av麻豆专区| 黄片小视频在线播放| 成人三级做爰电影| 亚洲伊人色综图| 麻豆国产av国片精品| 久热爱精品视频在线9| 亚洲九九香蕉| 成人欧美大片| 午夜福利,免费看| www.精华液| 日韩成人在线观看一区二区三区| 欧美日韩福利视频一区二区| 国产精品免费视频内射| 中文字幕另类日韩欧美亚洲嫩草| 国内精品久久久久久久电影| 国产成人av激情在线播放| 在线观看免费视频网站a站| 国产亚洲欧美98| 午夜精品国产一区二区电影| 黄片大片在线免费观看| 亚洲色图av天堂| 国产亚洲精品久久久久5区| 精品久久久久久久人妻蜜臀av | 男人操女人黄网站| 国产精品亚洲一级av第二区| cao死你这个sao货| 午夜福利影视在线免费观看| 亚洲精品美女久久久久99蜜臀| 国产av一区在线观看免费| 亚洲第一av免费看| 99久久精品国产亚洲精品| 午夜福利高清视频| 日韩大码丰满熟妇| 在线观看舔阴道视频| 国产精品香港三级国产av潘金莲| 成人手机av| 变态另类成人亚洲欧美熟女 | 老司机午夜福利在线观看视频| 嫩草影视91久久| 别揉我奶头~嗯~啊~动态视频| 国产亚洲av高清不卡| 一级片免费观看大全| 久久精品亚洲熟妇少妇任你| 久久中文字幕一级| 丝袜美足系列| 美女高潮到喷水免费观看| 50天的宝宝边吃奶边哭怎么回事| 亚洲视频免费观看视频| 亚洲国产精品久久男人天堂| 成人三级黄色视频| 国产97色在线日韩免费| 91字幕亚洲| 欧美日韩一级在线毛片| 亚洲精品国产区一区二| 亚洲五月婷婷丁香| 亚洲三区欧美一区| 一边摸一边抽搐一进一小说| 亚洲欧美精品综合一区二区三区| 日韩av在线大香蕉| 少妇熟女aⅴ在线视频| 国产成人精品在线电影| 日日摸夜夜添夜夜添小说| 久久精品影院6| 亚洲在线自拍视频| 精品乱码久久久久久99久播| 多毛熟女@视频| 精品国产一区二区三区四区第35| 老司机午夜福利在线观看视频| 午夜影院日韩av| 日韩一卡2卡3卡4卡2021年| 亚洲专区中文字幕在线| 亚洲人成电影免费在线| 老熟妇仑乱视频hdxx| 久久香蕉激情| 黄色 视频免费看| 久久午夜亚洲精品久久| 精品一区二区三区视频在线观看免费| 午夜免费激情av| 亚洲成人免费电影在线观看| 18禁裸乳无遮挡免费网站照片 | 国产1区2区3区精品| 88av欧美| 人妻丰满熟妇av一区二区三区| 91精品三级在线观看| 看免费av毛片| 一二三四社区在线视频社区8| 高潮久久久久久久久久久不卡| 欧美黄色片欧美黄色片| 欧美一级a爱片免费观看看 | 欧美国产精品va在线观看不卡| 亚洲欧美一区二区三区黑人| 老司机深夜福利视频在线观看| 精品免费久久久久久久清纯| 国产精品乱码一区二三区的特点 | 美女国产高潮福利片在线看| 亚洲精品中文字幕一二三四区| 不卡av一区二区三区| 国产成人精品无人区| 亚洲国产欧美网| 美女高潮到喷水免费观看| 国产1区2区3区精品| 亚洲av日韩精品久久久久久密| 可以在线观看毛片的网站| 国产午夜精品久久久久久| 黄片播放在线免费| 久久精品影院6| 怎么达到女性高潮| 国产三级黄色录像| 日日摸夜夜添夜夜添小说| 久久精品人人爽人人爽视色| 色播在线永久视频| 精品国产乱码久久久久久男人| 两性午夜刺激爽爽歪歪视频在线观看 | 国产日韩一区二区三区精品不卡| 国产成年人精品一区二区| 国产99久久九九免费精品| 国产一区二区激情短视频| 一区二区三区国产精品乱码| 嫩草影院精品99| 国产免费男女视频| 久久久久久久精品吃奶| 变态另类成人亚洲欧美熟女 | 日韩中文字幕欧美一区二区| 国产av又大| 12—13女人毛片做爰片一| 女警被强在线播放| 久久欧美精品欧美久久欧美| 女人精品久久久久毛片| 美女午夜性视频免费| www.精华液| 亚洲第一青青草原| 亚洲色图综合在线观看| 国产一区二区三区在线臀色熟女| 又黄又粗又硬又大视频| 久久久久久久精品吃奶| 久久国产精品影院| 91国产中文字幕| 亚洲成人久久性| 免费在线观看亚洲国产| 天天躁狠狠躁夜夜躁狠狠躁| 免费久久久久久久精品成人欧美视频| 午夜免费观看网址| 看免费av毛片| 午夜福利免费观看在线| 一本综合久久免费| 老鸭窝网址在线观看| 亚洲 欧美 日韩 在线 免费| 亚洲人成电影免费在线| 人人妻人人澡欧美一区二区 | 一级a爱片免费观看的视频| 多毛熟女@视频| 深夜精品福利| 窝窝影院91人妻| 亚洲九九香蕉| 午夜激情av网站| 制服诱惑二区| 国产精品影院久久| 婷婷丁香在线五月| 1024香蕉在线观看| 黄色毛片三级朝国网站| 国内毛片毛片毛片毛片毛片| 国产乱人伦免费视频| 成年人黄色毛片网站| 久久欧美精品欧美久久欧美| 老司机福利观看| 亚洲男人天堂网一区| 国产成人精品久久二区二区免费| 两个人视频免费观看高清| 亚洲成人免费电影在线观看| 操出白浆在线播放| 美女大奶头视频| 最近最新中文字幕大全电影3 | 乱人伦中国视频| 国产亚洲欧美精品永久| 国产精品,欧美在线| 免费一级毛片在线播放高清视频 | 超碰成人久久|