欧美亚洲国产精品久久高清-欧美亚洲国产精品久久第一页-欧美亚洲国产精品第一页-欧美亚洲国产精品-欧美亚洲国产第一页草草-欧美亚洲国产成人综合在线

Leaching and recovery of zinc from leaching residue of zinc calcine based on membrane filter press s

Category.prescription 989

1 Introduction

Zinc sulfide ores are the main source of zmc metal in the world, in which zinc generally exists in forms of sphalerite and marmatite. Currently,more than 80 per cent of the zinc is produced by conventional zinc hydrometallurgical methods, including roasting, leaching and electrowinning processes [1, 2]. % of the zinc is produced by conventional zinc hydrometallurgical methods, including roasting, leaching and electrowinning processes [1, 2]. During the roasting process, ZnS is converted to ZnO, but a significant fraction of ZnO reacts with the iron impurities to form zinc ferrite [3-51]. Zinc ferrite is insoluble in mild acidic conditions, strong Hs. A considerable amount of leaching residue will be produced in the subsequent leaching process [f6, 7]. In addition, the leaching reaction rate decreases over time due to the decreasing acid concentration during the tradifional leaching process in the stirred tank. Consequently, incomplete leaching will OCCur, thereby further increasing the generation of zinc leaching residue (ZLR), leading to a significant waste of resources and a high environmental impact. Consequently, incomplete leaching will OCCur, thereby further increasing the generation of zinc leaching residue (ZLR), leading to a significant waste of resources and a high environmental risk [8, 9]. The high demand for zinc has attracted the interest of industry to utilise the ZLR as a valuable secondary source [1].Hydrometallurgical processes are dely applied to recycle zinc from ZLR due to their significant advantages of lower capital and operating costs, as well as being less harmful to the environment [1, 1]. environment [1, 2]. Currently, the most common hydrometallurgical process is to recover zinc from ZLR in a bath of hot concentrated sulfuric acid [10]. high extraction rate of zinc can be obtained using this process, but incomplete leaching still occurs due to the leaching in the stirred tank.Moreover, the hot concentrated acid leaching process involves a high extraction rate of zinc in a bath of hot concentrated sulfuric acid. Moreover, the hot concentrated acid leaching process involves a long reaction time f4-6¨and consumes an enormous amount of energy and sulfuric acid More importantly, in most electrolytic zinc plants, the ZLRs containing water-soluble zinc with a content of less than 5 per cent of the ZLRs were used to produce the ZLRs in the stirred tank. More importantly,in most electrolytic zinc plants, the ZLRs containing water-soluble zinc with a content of less than 5% are directly discharged or heaped, causing a portion of the zinc losses. The water-soluble zinc can cause soil contamination, water pollution and several other serious environmental pollution through the leachate by rainfall [8, 9]. Therefore, finding a cost effective and environment friendly process to recover zinc from ZLR remains a major challenge. The membrane filter press (MFP), which is a common machine on solid. The membrane filter press (MFP), which is a common machine on solid-liquid separation, has advantages of low cost, high solid content and outstanding efficiency that has been widely used in various industries. years, the washing functionof MFP has also been attracting attention for use in the titanium dioxide, sugar,pigment and electrolytic manganese metal In recent years, the washing functionof MFP has also been attracting attention for use in the titanium dioxide, sugar, pigment and electrolytic manganese metal industries[1b14]. LIU et al[14] recovered 50%of water-soluble manganese from an electrolytic manganese residue fEMR) via a MFP using water. -based water washing technology could be industrially applied because it solves the problem of ''water swelling". swelling", which commonly occurs in previous water washing technologies [1 4, 1 5]. On the basis of the previous work of LIU et al [1 4], we attempted to wash the EMR via a MFP using anolyte. In 2009, the MFP-based technology on the leaching and recovery of manganese from EMR via a combination of anolyte washing with water was developed. combination of anolyte washing with water washing was realized and resulted in a patent application being submitted (No. CN1 024700A) 『1 61.Note that However, the possibility of using this technology in the hydrometallurgical zinc production process has not yet been demonstrated. However, the possibility of using this technology in the hydrometallurgical zinc process has never been investigated previously. The thickening, pulping, second leaching, washing, filtering and pressing would be integrated and realised using a single MFR In addition, the leaching of zinc from ZLR In addition, the leaching of zinc from ZLR in the form of spent electrolyte washing would be performed under constant acid concentration via a continuous flow of spent electrolyte. Hencethe feasibility of leaching and recovery of zinc from ZLR would be improved. feasibility of leaching and recovery of zinc from lcaching residue of zinc calcine based on MFP was investigated, combining spent electrolyte washing with flesh water washing. For this work, the uniformity of filter cakes, which is directly related to the leaching result, was examined. Based on this experimental result, the 1eaching and washing on extracting zinc from ZLR were subsequently studied.

1 Introduction

Zinc sulfide ores are the main source of zmc metal in the world, in which zinc generally exists in forms of sphalerite and marmatite. Currently,more than 80 per cent of the zinc is produced by conventional zinc hydrometallurgical methods, including roasting, leaching and electrowinning processes [1, 2]. % of the zinc is produced by conventional zinc hydrometallurgical methods, including roasting, leaching and electrowinning processes [1, 2]. During the roasting process, ZnS is converted to ZnO, but a significant fraction of ZnO reacts with the iron impurities to form zinc ferrite [3-51]. Zinc ferrite is insoluble in mild acidic conditions, strong Hs. A considerable amount of leaching residue will be produced in the subsequent leaching process [f6, 7]. In addition, the leaching reaction rate decreases over time due to the decreasing acid concentration during the tradifional leaching process in the stirred tank. Consequently, incomplete leaching will OCCur, thereby further increasing the generation of zinc leaching residue (ZLR), leading to a significant waste of resources and a high environmental impact. Consequently, incomplete leaching will OCCur, thereby further increasing the generation of zinc leaching residue (ZLR), leading to a significant waste of resources and a high environmental risk [8, 9]. The high demand for zinc has attracted the interest of industry to utilise the ZLR as a valuable secondary source [1].Hydrometallurgical processes are dely applied to recycle zinc from ZLR due to their significant advantages of lower capital and operating costs, as well as being less harmful to the environment [1, 1]. environment [1, 2]. Currently, the most common hydrometallurgical process is to recover zinc from ZLR in a bath of hot concentrated sulfuric acid [10]. high extraction rate of zinc can be obtained using this process, but incomplete leaching still occurs due to the leaching in the stirred tank.Moreover, the hot concentrated acid leaching process involves a high extraction rate of zinc in a bath of hot concentrated sulfuric acid. Moreover, the hot concentrated acid leaching process involves a long reaction time f4-6¨and consumes an enormous amount of energy and sulfuric acid More importantly, in most electrolytic zinc plants, the ZLRs containing water-soluble zinc with a content of less than 5 per cent of the ZLRs were used to produce the ZLRs in the stirred tank. More importantly,in most electrolytic zinc plants, the ZLRs containing water-soluble zinc with a content of less than 5% are directly discharged or heaped, causing a portion of the zinc losses. The water-soluble zinc can cause soil contamination, water pollution and several other serious environmental pollution through the leachate by rainfall [8, 9]. Therefore, finding a cost effective and environment friendly process to recover zinc from ZLR remains a major challenge. The membrane filter press (MFP), which is a common machine on solid. The membrane filter press (MFP), which is a common machine on solid-liquid separation, has advantages of low cost, high solid content and outstanding efficiency that has been widely used in various industries. years, the washing functionof MFP has also been attracting attention for use in the titanium dioxide, sugar,pigment and electrolytic manganese metal In recent years, the washing functionof MFP has also been attracting attention for use in the titanium dioxide, sugar, pigment and electrolytic manganese metal industries[1b14]. LIU et al[14] recovered 50%of water-soluble manganese from an electrolytic manganese residue fEMR) via a MFP using water. -based water washing technology could be industrially applied because it solves the problem of ''water swelling". swelling", which commonly occurs in previous water washing technologies [1 4, 1 5]. On the basis of the previous work of LIU et al [1 4], we attempted to wash the EMR via a MFP using anolyte. In 2009, the MFP-based technology on the leaching and recovery of manganese from EMR via a combination of anolyte washing with water was developed. combination of anolyte washing with water washing was realized and resulted in a patent application being submitted (No. CN1 024700A) 『1 61.Note that However, the possibility of using this technology in the hydrometallurgical zinc production process has not yet been demonstrated. However, the possibility of using this technology in the hydrometallurgical zinc process has never been investigated previously. The thickening, pulping, second leaching, washing, filtering and pressing would be integrated and realised using a single MFR In addition, the leaching of zinc from ZLR In addition, the leaching of zinc from ZLR in the form of spent electrolyte washing would be performed under constant acid concentration via a continuous flow of spent electrolyte. Hencethe feasibility of leaching and recovery of zinc from ZLR would be improved. feasibility of leaching and recovery of zinc from lcaching residue of zinc calcine based on MFP was investigated, combining spent electrolyte washing with flesh water washing. For this work, the uniformity of filter cakes, which is directly related to the leaching result, was examined. Based on this experimental result, the 1eaching and washing on extracting zinc from ZLR were subsequently studied.

Diaphragm filter press Leaching and recovery of zinc from leaching residue of zinc calcine based on membrane filter pres s-plate and frame chamber membrane filter press

2 Experimental 623

2.1 Materials The experimental study was performed using zinc calcine with a composition of 57% zinc, which was purchased from Hunan Province, China. Spent electrolyte containing 1 60 g/L of H2S04 and 50 g/L of Zn" was used in all of the leaching experiments. under all examined conditions. Under all examined conditions, the zinc concentration was determined based on GB/T 14353.3-2010『17〕, and the hydrogen ion concen仃ation fH+, was measured based on GB 6498.2-2001『181. The membrane filter press (KM470) was from Beijing ZSC Solid-Liquid Separating Technology Co. The membrane filter press (KM470) was from Beijing ZSC Solid-Liquid Separation Technology Co.)

2.2 Experimental procedure The diagram of leaching and recovery of zinc from zinc calcine is presented in Fig. 1.111e proper production process is described briefly as follows. described briefly as follows.1 1 leaching in stirred.tank reactor: Spent electrolyte or sulfuric acid was added to the crashed zinc calcine to leach zinc ions from the ores and to obtain the ZnS04-containing zinc. ions from the ores and to obtain the ZnS04-contained slurry. 2. filtration: the ZnS04-contained slurry was pumped into MFP through central feeding hole and filter pressed to obtain the filter. The ZnS04-contained slurry was pumped into MFP through central feeding hole and filter pressed to obtain the filter cakes (i.e., ZLR); next, the filtrate (1eaching liquor) entered the subsequent production process. 3. 1eaching in Ⅳ[FP: Spent electrolyte at the desired temperature was pumped into the MFP and reacted with filter cakes to leach zinc again and simultaneously recover part of ZnS04. 4) water washing: The filter cakes were washed again with flesh water to further recover ZnS04. 5) pressing: Water with a pressure of 1.5 mL was used for the treatment. with a pressureThe eluate obtained from spent electrolyte washing and flesh water washing steps was then pumped into the membrane plates, which was maintained for 20 min to reduce the water content of filter cakes, and the pressed filter cakes were subsequently discharged from the MFP and transported to landfills. The eluate obtained from spent electrolyte washing and flesh water washing steps were collected and returned to spent electrolyte tank and eluate collection tank. The eluate obtained from spent electrolyte washing and flesh water washing steps were collected and returned to spent electrolyte tank and eluate collection tank, respectively.

3 Results and discussion

3.1 Filter cake formation To obtain a high zinc ex仃action rate and recovery rate using an MFP.the most important step is to obtain uniform filter cakes.the particle size of zinc calcine and sedimentation time.which are directly involved with the width of the filter chambers. particle size of zinc calcine and sedimentation time, which are directly involved with the width of the filter chambers, are the most important parameters regarding the uniformity of filter cake. The particle size of zinc calcine and sedimentation time, which are directly involved with the width of the filter chambers, are the most important parameters regarding the uniformity of filter cake. The five-spot test (upper left, bottom left, centre,upper right, bottom right) was used for estimating the uniformity of the filter cakes by measuring the zinc content. The five-spot test (upper left bottom left, centre, upper right, bottom right) was used for estimating the uniformity of the filter cakes by measuring the zinc content and thickness of the cakes at these selected points. Through observation of the filter cakes formed in the MFP, it is found that triangle cakes were easily formed using raw zinc calcine. The presence of zinc calcine of large particle size inhibits the formation of uniform cakes due to its good The presence zinc calcine of large particle size inhibits the formation of uniform cakes due to its good settleability: thus, small size particles should be selected.Choosing the particle size of zinc calcine less than 106 gm仃,able 1 1. which could be obtained in actual production, a series of experiments regarding the filter cake formation were conducted. and the results are presented in Fig.2. From Fig.2.2, using zinc calcines with particle sizes less than 1 06 gm, the zinc content and filter cake thickness vary clearly at the five tested points when the When the filter chamber width is 40 mln, suggesting that the cake uniformity is poor under this condition, which might be due to long sedimentation time. When the filter chamber width is 30 lnnl, the cake uniformity is improved significantly relative to the chamber width of 40 nun. When the filter chamber width is 20 mm, the cake uniformity is improved significantly. When the filter chamber width is 20 mm, the cake uniformity is similar to the results obtained as the chamber width is 30 mm. Thus. it can be clearly observed that the uniforlTl filter cakes could be formed by choosing the particle size of zinc calcine to be less than 1 06 Bm for filter chamber widths of 20 mm and 30 mill. As a result, the zinc calcines with particle size 1ess than 1 06 Bm were used in the following filter chamber. As a result, the zinc calcines with particle size 1ess than 1 06 Bm were used in the following experiments. The processing capacity of MFP with 20 mm width chamber is 10wer than that with 30 toni width chamber. The processing capacity of MFP with 20 mm width chamber is 10wer than that with 30 toni width chamber.Therefore. combining the results of processing capacity and cake uniformity,the chamber width of 30 finn was selected in the following The chamber width of 30 finn was selected in the following experiments.

3.2 Leaching of zinc from zinc calcine In this lcaching process, 1 00 L of spent electrolyte solution was added to a 300 L stainless steel drum equipped with a variable speed stirrer and then stirred for approximately 1 h at a speed of 60 r/min. Next, the 1eaching solution was adjusted by adding zinc calcine or Next, the 1eaching solution was adjusted by adding zinc calcine or sulfate acid until the final Zn "concentration of electrolyte was in the range of 130-140 g/L and the final H2S04 concentration was in the range of l-2 g/L. Subsequently, the ZnS04-contained slurry was filtered using a MFE The analysis results of zinc calcine and ZLR are presented in 1 'ables 2 and 3. The analysis results of zinc calcine and ZLR are presented in 1, 2 and 3, respectively. As presented in Table 2, the grade of zinc calcine is 57.52%, in which ZnO approximately accounts for 90.06% of total zinc in mass. Table 3 indicates that in this process of leaching, most of the Zn0 is converted to ZnS04, resulting in the dramatic decrease of the content of ZnO. Table 3 indicates that in this process of leaching most of the Zn0 is converted to ZnS04, resulting in the dramatic decrease of the content of ZnO. After solid-liquid separation using the MFP, many insoluble materials are concentrated in the residue. leaching residue is higher than 20%, causing the extraction rate of zinc in this process to be less than 90%. Analysis of ZLR indicates that zinc iS mainly presented in the forills of ZnO. presented in the forills of ZnFe204, ZnO and ZnS04, which in total account for uD to 80% of the zinc iS.(Thus, a secondary leaching process is required to recover the remaining zinc.

3.3 Leaching of zinc from ZLR In this leaching process, the zinc was extracted from ZLR obtained in Section 3.2 in the form of spent electrolyte washing To dissolve ZnFe204 using MFE, strict leaching conditions, such as high temperature (above 90°C, and high concentration of acid solution (100 -200 g/L), were applied. -Under hi. temperature and high acid concentration conditions, the extraction rate of zinc can increase to approximately 97% [19, 20]. approximately 97% [19, 20]. To enable a comparison with the extraction rate obtained in the traditional route, the lcaching conditions in the present work are under a temperature in the range of 0.5 to 0.5°C. The extraction rate of zinc was determined as follows The lcaching conditions in the present work are under a temperature in the range of 90 to 96 oC and an acid concentration in the range of 1 00 to 200 g/L. Becanse alsoe leaching residues of zinc calcine Becanse also e leaching residues of zinc calcine were fixed in the chamber of the MFP. the high reaction temperature condition was realized through heating of the spent electrolyte. Figure 3 shows the Zn "and H2S04 concentrations with the MFP. Figure 3 shows the Zn "and H2S04 concentrations with leaching time under atemperature in the range of 90 to 96 oC during the leaching process based on MFE From Fig. 3, the Zn "concentration is the highest in the chamber. The Zn "concentration is observed to obviously increase during the initial 5 min, followed by a decrease to 55 gui after washing for 60 min and only a slight change around the level of 55 g/L in the following 30 min. Conversely'the H2S04 concentration obviously decreases during the initial 5 min. followed by a decrease to 55 g/L in the following 30 min. Conversely'the H2S04 concentration obviously decreases during the initial 5 min. followed by an increase to 11 7 g/L after washing for 60 min and then slight changes around the level of 120 g/L in next 30 min. Based on these Based on these above results, it can be concluded that the violently reaction of the leaching residue with the hot spent electrolyte only lasts for approximately 60 min. The analysis result of the residue after hot concentrated acid leaching for 90 min is presented in T2lble 4. Clearlv. the zinc content in the residue reduces significantly from over 20% (Table 3) to less than 1 0% (Table 41. As a consequence, the zinc extraction rate 1ncreases to 97%. This result obviously demonstrates that using a MFP as a leaching reactor could not only ensure a high extraction rate but also reduce the leaching time compared with the traditional hot concentrated acid The short leaching time using a MFP might be due to the constant reaction conditions of high temperature and high acid concentration during the whole process when using a MFE Based on the above results. The short leaching time using a MFP might be due to the constant reaction conditions of high temperature and high acid concentration during the whole process when using a MFE Based on the above results. temperatures, such as at 30 oC, 60 to 70 oC, 70 to 80 oC and 80 to 90 oC. to reduce the energy consumption further. The zinc extraction rate at 30 oC is 92.67% and increases to 94.95% at 60 to 70 oC. When the 1eaching temperature is further increased to 80 to 90 oC, the ex仃action ratio increases to 94.95% at 60 to 70 oC. The ex仃action ratio increases to 95.56%. The temperature of spent electrolyte has an obvious effect on t11e zinc extraction ratio. high zinc extraction could be obtained by increasing the temperature of the electrolyte. High zinc extraction could be obtained by increasing the temperature of leaching, which is consistent wim the results of Ref.f191. Under Iow temperatures, the energy consumption is lower,the extraction ratio can be increased by 1.5 per cent. Under Iow temperatures, the energy consumption is lower,the extraction ratio can not reach the traditional result of 97%.In conelusion, the hot acid leaching only at 90 to 96 oC or above can achieve the ideal result(i). achieve the ideal result(i.e., more than 97%,...).

3.4 Recovery of water-soluble zinc

The water-soluble zinc approximately accounts for 3%of the total zinc in the residue after hot acidTo recover this part of the zinc, the leaching residue was further washed with Water. Figure 5 shows that both the Zn2+and H,S04 concentrations of eluate decrease with increasing washing time. Figure 5 shows that both the Zn2+and H,S04 concentrations of eluate decrease with increasing washing time.especially in the initial 5 min. These results indicate that Zn "and H,S04 These results indicate that Zn "and H,S04 in the zinc residue could be quickly washed out by Water using the MFP. After washing for 25 min, the final Znz+and H2S04 concentrations of eluate decrease to 0.05 ki and H2S04 concentrations of eluate. to 0.05 g/l and 1.25 g/l.pectively. The final residue obtained after being washed and pressed merely contains 6% of zinc. in which the water-soluble zinc only accounts for 0.07% (Table 5), suggesting that the majority of water-soluble zinc is recovered during the water washing process. Compared with the traditional hot concentrated acid leaching process, the water-soluble zinc lost in the leaching residue iS very 10 %. The water-soluble zinc lost in the leaching residue iS very 10W. 3.5 Washing uniformity To estimate the washing results, the washing uniformity of MFP was examined by measuring.Both the total zinc and the water-soluble zinc were measured. Both the total zinc and the water-soluble zinc contents in the final residue. As presented in Rlble 6. change slightly at five selected points (upper left, bottom left, centre,upper right, and bottom right) in the residue, indicating that the hot spent The zinc that can be extracted in zinc calcine and the Water-soluble zinc that can be recovered in the residue are completely uniforiil. The zinc that can be extracted in zinc calcine and the Water-soluble zinc that can be recovered in the residue are completely extracted and recovered by USing the MFP.

4 Conclusions

1] The use of a MFP is found to be completely feasible and effective to 1each and recover zinc from leaching residues ofzinc calcine.

2] The zinc calcines with particle size of less than 1 06 gm and MFP chambers with a width of 30 I/IlTI are proper for establishing unifornl filter cakes to obtain acceptable leaching and recovery results.

Diaphragm filter press Leaching and recovery of zinc from leaching residue of zinc calcine based on membrane filter pres s-plate and frame chamber membrane filter press

2 Experimental 623

2.1 Materials The experimental study was performed using zinc calcine with a composition of 57% zinc, which was purchased from Hunan Province, China. Spent electrolyte containing 1 60 g/L of H2S04 and 50 g/L of Zn" was used in all of the leaching experiments. under all examined conditions. Under all examined conditions, the zinc concentration was determined based on GB/T 14353.3-2010『17〕, and the hydrogen ion concen仃ation fH+, was measured based on GB 6498.2-2001『181. The membrane filter press (KM470) was from Beijing ZSC Solid-Liquid Separating Technology Co. The membrane filter press (KM470) was from Beijing ZSC Solid-Liquid Separation Technology Co.)

2.2 Experimental procedure The diagram of leaching and recovery of zinc from zinc calcine is presented in Fig. 1.111e proper production process is described briefly as follows. described briefly as follows.1 1 leaching in stirred.tank reactor: Spent electrolyte or sulfuric acid was added to the crashed zinc calcine to leach zinc ions from the ores and to obtain the ZnS04-containing zinc. ions from the ores and to obtain the ZnS04-contained slurry. 2. filtration: the ZnS04-contained slurry was pumped into MFP through central feeding hole and filter pressed to obtain the filter. The ZnS04-contained slurry was pumped into MFP through central feeding hole and filter pressed to obtain the filter cakes (i.e., ZLR); next, the filtrate (1eaching liquor) entered the subsequent production process. 3. 1eaching in Ⅳ[FP: Spent electrolyte at the desired temperature was pumped into the MFP and reacted with filter cakes to leach zinc again and simultaneously recover part of ZnS04. 4) water washing: The filter cakes were washed again with flesh water to further recover ZnS04. 5) pressing: Water with a pressure of 1.5 mL was used for the treatment. with a pressureThe eluate obtained from spent electrolyte washing and flesh water washing steps was then pumped into the membrane plates, which was maintained for 20 min to reduce the water content of filter cakes, and the pressed filter cakes were subsequently discharged from the MFP and transported to landfills. The eluate obtained from spent electrolyte washing and flesh water washing steps were collected and returned to spent electrolyte tank and eluate collection tank. The eluate obtained from spent electrolyte washing and flesh water washing steps were collected and returned to spent electrolyte tank and eluate collection tank, respectively.

3 Results and discussion

3.1 Filter cake formation To obtain a high zinc ex仃action rate and recovery rate using an MFP.the most important step is to obtain uniform filter cakes.the particle size of zinc calcine and sedimentation time.which are directly involved with the width of the filter chambers. particle size of zinc calcine and sedimentation time, which are directly involved with the width of the filter chambers, are the most important parameters regarding the uniformity of filter cake. The particle size of zinc calcine and sedimentation time, which are directly involved with the width of the filter chambers, are the most important parameters regarding the uniformity of filter cake. The five-spot test (upper left, bottom left, centre,upper right, bottom right) was used for estimating the uniformity of the filter cakes by measuring the zinc content. The five-spot test (upper left bottom left, centre, upper right, bottom right) was used for estimating the uniformity of the filter cakes by measuring the zinc content and thickness of the cakes at these selected points. Through observation of the filter cakes formed in the MFP, it is found that triangle cakes were easily formed using raw zinc calcine. The presence of zinc calcine of large particle size inhibits the formation of uniform cakes due to its good The presence zinc calcine of large particle size inhibits the formation of uniform cakes due to its good settleability: thus, small size particles should be selected.Choosing the particle size of zinc calcine less than 106 gm仃,able 1 1. which could be obtained in actual production, a series of experiments regarding the filter cake formation were conducted. and the results are presented in Fig.2. From Fig.2.2, using zinc calcines with particle sizes less than 1 06 gm, the zinc content and filter cake thickness vary clearly at the five tested points when the When the filter chamber width is 40 mln, suggesting that the cake uniformity is poor under this condition, which might be due to long sedimentation time. When the filter chamber width is 30 lnnl, the cake uniformity is improved significantly relative to the chamber width of 40 nun. When the filter chamber width is 20 mm, the cake uniformity is improved significantly. When the filter chamber width is 20 mm, the cake uniformity is similar to the results obtained as the chamber width is 30 mm. Thus. it can be clearly observed that the uniforlTl filter cakes could be formed by choosing the particle size of zinc calcine to be less than 1 06 Bm for filter chamber widths of 20 mm and 30 mill. As a result, the zinc calcines with particle size 1ess than 1 06 Bm were used in the following filter chamber. As a result, the zinc calcines with particle size 1ess than 1 06 Bm were used in the following experiments. The processing capacity of MFP with 20 mm width chamber is 10wer than that with 30 toni width chamber. The processing capacity of MFP with 20 mm width chamber is 10wer than that with 30 toni width chamber.Therefore. combining the results of processing capacity and cake uniformity,the chamber width of 30 finn was selected in the following The chamber width of 30 finn was selected in the following experiments.

3.2 Leaching of zinc from zinc calcine In this lcaching process, 1 00 L of spent electrolyte solution was added to a 300 L stainless steel drum equipped with a variable speed stirrer and then stirred for approximately 1 h at a speed of 60 r/min. Next, the 1eaching solution was adjusted by adding zinc calcine or Next, the 1eaching solution was adjusted by adding zinc calcine or sulfate acid until the final Zn "concentration of electrolyte was in the range of 130-140 g/L and the final H2S04 concentration was in the range of l-2 g/L. Subsequently, the ZnS04-contained slurry was filtered using a MFE The analysis results of zinc calcine and ZLR are presented in 1 'ables 2 and 3. The analysis results of zinc calcine and ZLR are presented in 1, 2 and 3, respectively. As presented in Table 2, the grade of zinc calcine is 57.52%, in which ZnO approximately accounts for 90.06% of total zinc in mass. Table 3 indicates that in this process of leaching, most of the Zn0 is converted to ZnS04, resulting in the dramatic decrease of the content of ZnO. Table 3 indicates that in this process of leaching most of the Zn0 is converted to ZnS04, resulting in the dramatic decrease of the content of ZnO. After solid-liquid separation using the MFP, many insoluble materials are concentrated in the residue. leaching residue is higher than 20%, causing the extraction rate of zinc in this process to be less than 90%. Analysis of ZLR indicates that zinc iS mainly presented in the forills of ZnO. presented in the forills of ZnFe204, ZnO and ZnS04, which in total account for uD to 80% of the zinc iS.(Thus, a secondary leaching process is required to recover the remaining zinc.

3.3 Leaching of zinc from ZLR In this leaching process, the zinc was extracted from ZLR obtained in Section 3.2 in the form of spent electrolyte washing To dissolve ZnFe204 using MFE, strict leaching conditions, such as high temperature (above 90°C, and high concentration of acid solution (100 -200 g/L), were applied. -Under hi. temperature and high acid concentration conditions, the extraction rate of zinc can increase to approximately 97% [19, 20]. approximately 97% [19, 20]. To enable a comparison with the extraction rate obtained in the traditional route, the lcaching conditions in the present work are under a temperature in the range of 0.5 to 0.5°C. The extraction rate of zinc was determined as follows The lcaching conditions in the present work are under a temperature in the range of 90 to 96 oC and an acid concentration in the range of 1 00 to 200 g/L. Becanse alsoe leaching residues of zinc calcine Becanse also e leaching residues of zinc calcine were fixed in the chamber of the MFP. the high reaction temperature condition was realized through heating of the spent electrolyte. Figure 3 shows the Zn "and H2S04 concentrations with the MFP. Figure 3 shows the Zn "and H2S04 concentrations with leaching time under atemperature in the range of 90 to 96 oC during the leaching process based on MFE From Fig. 3, the Zn "concentration is the highest in the chamber. The Zn "concentration is observed to obviously increase during the initial 5 min, followed by a decrease to 55 gui after washing for 60 min and only a slight change around the level of 55 g/L in the following 30 min. Conversely'the H2S04 concentration obviously decreases during the initial 5 min. followed by a decrease to 55 g/L in the following 30 min. Conversely'the H2S04 concentration obviously decreases during the initial 5 min. followed by an increase to 11 7 g/L after washing for 60 min and then slight changes around the level of 120 g/L in next 30 min. Based on these Based on these above results, it can be concluded that the violently reaction of the leaching residue with the hot spent electrolyte only lasts for approximately 60 min. The analysis result of the residue after hot concentrated acid leaching for 90 min is presented in T2lble 4. Clearlv. the zinc content in the residue reduces significantly from over 20% (Table 3) to less than 1 0% (Table 41. As a consequence, the zinc extraction rate 1ncreases to 97%. This result obviously demonstrates that using a MFP as a leaching reactor could not only ensure a high extraction rate but also reduce the leaching time compared with the traditional hot concentrated acid The short leaching time using a MFP might be due to the constant reaction conditions of high temperature and high acid concentration during the whole process when using a MFE Based on the above results. The short leaching time using a MFP might be due to the constant reaction conditions of high temperature and high acid concentration during the whole process when using a MFE Based on the above results. temperatures, such as at 30 oC, 60 to 70 oC, 70 to 80 oC and 80 to 90 oC. to reduce the energy consumption further. The zinc extraction rate at 30 oC is 92.67% and increases to 94.95% at 60 to 70 oC. When the 1eaching temperature is further increased to 80 to 90 oC, the ex仃action ratio increases to 94.95% at 60 to 70 oC. The ex仃action ratio increases to 95.56%. The temperature of spent electrolyte has an obvious effect on t11e zinc extraction ratio. high zinc extraction could be obtained by increasing the temperature of the electrolyte. High zinc extraction could be obtained by increasing the temperature of leaching, which is consistent wim the results of Ref.f191. Under Iow temperatures, the energy consumption is lower,the extraction ratio can be increased by 1.5 per cent. Under Iow temperatures, the energy consumption is lower,the extraction ratio can not reach the traditional result of 97%.In conelusion, the hot acid leaching only at 90 to 96 oC or above can achieve the ideal result(i). achieve the ideal result(i.e., more than 97%,...).

3.4 Recovery of water-soluble zinc

The water-soluble zinc approximately accounts for 3%of the total zinc in the residue after hot acidTo recover this part of the zinc, the leaching residue was further washed with Water. Figure 5 shows that both the Zn2+and H,S04 concentrations of eluate decrease with increasing washing time. Figure 5 shows that both the Zn2+and H,S04 concentrations of eluate decrease with increasing washing time.especially in the initial 5 min. These results indicate that Zn "and H,S04 These results indicate that Zn "and H,S04 in the zinc residue could be quickly washed out by Water using the MFP. After washing for 25 min, the final Znz+and H2S04 concentrations of eluate decrease to 0.05 ki and H2S04 concentrations of eluate. to 0.05 g/l and 1.25 g/l.pectively. The final residue obtained after being washed and pressed merely contains 6% of zinc. in which the water-soluble zinc only accounts for 0.07% (Table 5), suggesting that the majority of water-soluble zinc is recovered during the water washing process. Compared with the traditional hot concentrated acid leaching process, the water-soluble zinc lost in the leaching residue iS very 10 %. The water-soluble zinc lost in the leaching residue iS very 10W. 3.5 Washing uniformity To estimate the washing results, the washing uniformity of MFP was examined by measuring.Both the total zinc and the water-soluble zinc were measured. Both the total zinc and the water-soluble zinc contents in the final residue. As presented in Rlble 6. change slightly at five selected points (upper left, bottom left, centre,upper right, and bottom right) in the residue, indicating that the hot spent The zinc that can be extracted in zinc calcine and the Water-soluble zinc that can be recovered in the residue are completely uniforiil. The zinc that can be extracted in zinc calcine and the Water-soluble zinc that can be recovered in the residue are completely extracted and recovered by USing the MFP.

4 Conclusions

1] The use of a MFP is found to be completely feasible and effective to 1each and recover zinc from leaching residues ofzinc calcine.

2] The zinc calcines with particle size of less than 1 06 gm and MFP chambers with a width of 30 I/IlTI are proper for establishing unifornl filter cakes to obtain acceptable leaching and recovery results.

Previous. Next post.
Expand More
Welcome to visit our factory!

loading...

en_GBEN
主站蜘蛛池模板: 色哟哟哟www精品视频观看软件 | 国产精品黄色网 | 永久免费毛片在线播放 | 亚洲 激情 | 国产乱码精品一区二区三区中文 | 免费av在线播放 | 免费人成在线观看 | 国产亚洲精品久久久久的角色 | 日韩成人自拍 | 国内自拍视频一区二区三区 | 日本美女极度性诱惑卡不卡 | 亚洲国产毛片aaaaa无费看 | 久久中文字幕一区 | 97视频人人| 野外做受又硬又粗又大视频 | 欧美性淫爽www视频免费播放 | 久久久久久一区二区三区 | 依依成人综合网 | 91精品一区二区 | 中文字幕一区在线观看视频 | 男女三级视频 | 久久影院午夜理论片无码 | 男女啪啪免费体验区 | 成人在线午夜视频 | 99热欧美 | 中文字幕一区日韩精品 | 牛牛a级毛片在线播放 | 手机在线免费看av | 8090理论片午夜理伦片 | 色又黄又爽18禁免费网站现观看 | 91精品国产99久久久久久红楼 | 黄色a免费看 | av免费在线播放网站 | 成人爽a毛片一区二区免费 成人爽爽爽 | 亚洲精品一区二区三区不卡 | 久久精品一本到东京热 | 日韩高清片 | 亚洲va欧美va国产va黑人 | 成人网址在线观看 | 97干婷婷 | 921国产乱码久久久久久 | 日韩午夜理论免费tv影院 | 国产精品久久久一区二区 | 中文天堂最新版在线www | 在线看欧美 | av免费网址在线观看 | 国模自拍视频 | 性荡视频播放在线视频 | 亚洲乱淫| 成人av免费看 | 国产午夜精品视频免费不卡69堂 | 狠狠色视频 | 风间由美性色一区二区三区 | 亚洲欧美日韩另类精品一区二区三区 | 99久久99久久久精品棕色圆 | 91福利社区在线观看 | 可以看的av网站 | 老汉色av影院 | 大尺度做爰床戏呻吟舒畅 | 在线观看亚洲天堂 | 91成人国产| 有码在线 | 亚洲深深色噜噜狠狠网站 | 理论片午午伦夜理片影院 | 香蕉久久av一区二区三区 | 国产精品乱码一区二区三区四川人 | 国产午夜不卡片免费视频 | 欧美性猛片aaaaaaa做受 | 国产人与禽zoz0性伦免费视频 | 国产人妻精品午夜福利免费 | 天堂va蜜桃一区二区三区 | 欧美最爽乱淫视频播放 | 国产亲子乱弄免费视频 | 亚洲深夜视频 | 中字幕人妻一区二区三区 | 国产超碰人人做人人爱ⅴa 日韩人妻无码精品久久久不卡 | 欧美性免费 | 精品久久久久久亚洲精品 | 久久草草精品入口av | 在线不卡日本v二区到六区 免费又黄又爽又猛的毛片 特级西西人体444www高清大胆 | 91麻豆精品传媒一二三区 | 动漫羞羞 | 亚洲特黄视频 | 国产一区二区不卡老阿姨 | 伊人久久大香线蕉av超碰演员 | 91看片在线| 色诱久久久久综合网ywww | 免费看成人av | 无码内射成人免费喷射 | 欧美视频a | 亚洲精品网站在线观看 | 九色首页 | 国产美女一区二区三区 | 直接看av的网站 | 色一情一狱一爱一乱 | 激情中文网 | 九色丨porny丨喷水 | 日韩中文字幕2019 | 肉丝美足丝袜一区二区三区四 | 一本色道久久hezyo加勒比 | 国产情侣草莓视频在线 | 能直接看的av | 精品一区二区不卡无码av | ass东方小嫩模pics | 天天玩天天干 | 久久久麻豆 | 五月av在线| 国产特黄aaaaa毛片 | 男女啪啪猛烈无遮挡猛进猛出 | 天堂综合久久 | 国产一区二区三区内射高清 | 久操国产在线 | 男人边吃奶边揉好爽免费视频 | 四虎在线免费观看视频 | 国产无套粉嫩白浆内精品 | 亚洲天堂av一区二区三区 | 国产麻豆一区二区三区精品 | 久久人人看 | 青青色在线观看 | 精品国产国产综合精品 | 亚洲韩欧美第25集完整版 | 国产伦精品一区二区三区在线 | 亚洲免费看黄 | 国产精品成av人在线视午夜片 | 男女操操操 | 污污的视频在线免费观看 | 久久久午夜爽爽一区二区三区三州 | 国产一级片免费看 | 日批视频免费看 | 亚洲精品久久久久午夜福禁果tⅴ | 久久久99国产精品免费 | 国产伦精品一区二区三区免.费 | 夜夜躁很很躁日日躁2020 | 欧美 日韩 国产在线 | 久久久久久亚洲精品a片成人 | 怡红院av久久久久久久 | 成人免费视频一区二区 | 91视频在线观看网站 | 国语自产免费精品视频在 | 国产寡妇xxxxxxxx性开放 | 99热这里只有精 | 毛片毛片毛片毛片毛片毛片毛片毛片毛片毛片 | 午夜激情综合网 | 中文字幕三区 | 国产精品亚洲а∨无码播放麻豆 | 久久视频免费在线观看 | 日本19禁啪啪吃奶大尺度 | 爱高潮www亚洲精品 爱搞国产 | 午夜成人理论无码电影在线播放 | 午夜免费片 | 粉嫩一区| 久久久91精品国产一区二区精品 | 老熟妻内射精品一区 | 91精品国模一区二区三区 | 91精品视频一区二区三区 | 国产精品sm| 日本艹逼视频 | 欧美成人精品第一区 | 免费又黄又爽又猛大片午夜 | 深夜福利啪啪片 | 老妇激情毛片视频 | 久青草视频在线 | 久久国产乱子伦免费精品 | 波多一区| 欧美性在线观看 | jizz4国产| 偷拍精偷拍精品欧洲亚洲网站 | 久久久久久久久久久影院 | 精品粉嫩超白一线天av | 亚洲精品久久久蜜桃 | 影音先锋资源av不撸 | 人妻熟女av一区二区三区 | 亚洲一区二区三区在线观看视频 | 久草在线中文888 | 午夜精品久久久久久99热小说 | brazzers欧美极品少妇 | 挺进美女教师的蜜桃肥臀视频 | 91精品国产高清91久久久久久 | 亚洲激情自拍 | 日本最新免费二区三区 | 亚洲在线观看免费 | 国产亚洲成av人片在线观看下载 | 无码精品一区二区三区在线 | av免费网站在线观看 | 亚洲精品久久久久久久久久久久久久 | 人妻少妇一区二区三区 | 久久一区二区三区视频 | 久久影音先锋 | 亚洲色偷偷男人的天堂 | 色一情一乱一伦一视频免费看 | 日韩和欧美一区二区 | 丰满少妇被猛烈进入无码 | 少妇精品无码一区二区免费视频 | 国产情侣激情在线对白 | 日本xxxwww| 国产色在线 | 天天综合在线视频 | 农村妇女做爰偷拍视频 | 成人黄色激情视频 | 国产98色在线 | 国 | 丝袜性爱视频 | 蜜臀久久99静品久久久久久 | 综合激情亚洲 | 国产精品网站在线 | 影音先锋亚洲资源 | 国产黄色片免费在线观看 | 18禁超污无遮挡无码免费网站国产 | 尹人成人| www中文字幕av | 成人免费视频观看视频 | 国产精品嫩草影院av | 高潮内射免费看片 | 国产91精品激烈高潮白浆 | 黄色片链接 | 97精品久久久午夜一区二区三区 | 亚洲男人天堂网址 | 最新免费黄色网址 | 操mm影院| 国产av无码久久精品 | 亚洲人成伊人成综合网久久久 | 国产精品无码av天天爽播放器 | 亚洲v在线观看 | 无码中文字幕人妻在线一区二区三区 | 杨思敏全身裸体毛片看 | 色88888久久久久久影院 | 小早川怜子xxxxaⅴ在线 | 免费观看一区二区三区视频 | 日本不卡视频在线 | 天堂va欧美va亚洲va老司机 | 成人精品视频在线 | 国产最新精品 | 久久成人国产精品免费软件 | 国产人妻丰满熟妇嗷嗷叫 | 91久久国产露脸精品国产 | 一级黄色在线观看 | 国产又黄又爽又色的免费视频白丝 | 一区二区三区日韩视频在线观看 | 精品无人国产偷自产在线 | 免费国产自产一区二区三区四区 | 色欲av无码一区二区人妻 | 亚洲精品一区久久久久久 | 中文字幕无码乱码人妻系列蜜桃 | 天天爽夜夜爽人人爽 | 粉嫩一区 | 亚洲网站在线观看 | 久久日精品 | 涩涩的视频在线观看 | 又粗又黑又大的吊av | 在线中文字幕一区 | 欧洲人妻丰满av无码久久不卡 | 懂色av中文一区二区三区天美 | 俄罗斯老熟妇色xxxx | 亚洲人成在线观看 | 老司机伊人 | 亚洲二区在线视频 | 欧美美女性视频 | 中国小鲜肉xvideoscom | 五月伊人网| 国产免费无码一区二区 | 日日鲁鲁夜夜狼狼视频 | 亚洲天堂网在线视频 | 中文字幕一区二区视频 | 91精品中文字幕 | 激情av| 国产偷v国产偷∨精品视频 国产偷v国产偷v精品视频 | 欧洲高潮三级做爰 | 在线观看成人 | 国产人妻大战黑人第1集 | 特级毛片爽www免费版 | 无码人妻av免费一区二区三区 | 国产成人一区在线观看 | 欧美xxxxx高潮喷水 | 66亚洲一卡2卡新区成片发布 | julia中文字幕久久亚洲蜜臀 | 少妇高潮太爽了中文字幕 | 国产精品一区二区三区视频免费 | 伊人色综合久久天天小片 | 日本乳奶水流出来高清xxxx | 人人妻人人澡人人爽人人精品av | 成人动态视频 | 国产精品99久久免费黑人人妻 | 亚洲成人a v | 北条麻妃一区二区免费播放 | 欧洲美一区二区三区亚洲 | 婷婷色九月 | 高清毛片aaaaaaaaa郊外 | 真人祼交二十三式视频 | 精品无码专区久久久水蜜桃 | 国产调教av | 99视频偷窥在线精品国自产拍 | 亚洲 欧美 制服 综合 另类 | 亚洲熟妇无码乱子av电影 | 久久99热久久99精品 | 国产大片中文字幕在线观看 | 精品国产99久久久久久 | 麻豆三级 | 日本舌吻大尺度呻吟视频 | 亚洲午夜一区二区 | www.青青草.com | 99久久精品日本一区二区免费 | 中文字幕日本精品一区二区三区 | 一级特黄aaa毛片在线视频 | 香港三级午夜理伦三级 | 日本丰满熟妇videossexhd 午夜福利影院私人爽爽 | 色噜噜狠狠一区二区三区狼国成人 | 国产农村一国产农村无码毛片 | h网站免费在线观看 | 日本三级视频在线播放 | 国产九九在线 | 国产强伦姧在线观看无码 | 高清视频在线观看一区二区三区 | 女女同性女同一区二区三区91 | 国产精品视频播放 | 欧美日韩一二三四 | 秋霞福利网| 午夜尤物丰满大乳美女 | 高清人人天天夜夜曰狠狠狠狠 | 无码纯肉视频在线观看 | 尤物综合网 | 在线精品国产成人综合 | 草草免费视频 | 亚洲国产成人精品无码区在线观看 | 99免费精品 | 久久精品成人无码观看免费 | 国产高清亚洲 | 欧美一区二区三区四区在线观看 | 亚洲中文字幕无码爆乳 | 超碰在线小说 | 综合久久给合久久狠狠狠97色 | 日本囗交一级视频 | 伊人春色av | 中文字幕乱码亚洲无线三区 | 大尺度福利视频 | 日韩视频免费在线观看 | 久久久久夜色精品国产老牛91 | 3344成人 | 黄色片xxxx| 午夜婷婷在线观看 | 亚洲精品国产福利 | 国产精品日日夜夜 | 医生强烈淫药h调教小说阅读 | 豆麻视频在线免费观看 | 欧美一区二区福利视频 | 成人av网站免费观看 | 国产japanhdxxxx麻豆 | 国产精品久久久久久久久久免费 | 红杏av在线| 77777亚洲午夜久久多人 | 亚洲4444| 国产新婚夫妇白天做个爱 | 国产91一区 | 四虎国产精品免费观看视频优播 | 美美女高清毛片视频免费观看 | 夜夜躁狠狠躁夜躁2021鲁大师 | 欧美精品福利 | 人妖另类巨茎双性人欧美视频 | 66m66成人摸人视频 | 亚洲国产精品无码久久电影 | 狠狠综合 | 超级碰碰色偷偷免费视频 | 就爱啪啪网站 | 十八女人水多三级 | 久久69精品久久久久久国产越南 | 亚洲小说春色综合另类 | av在线手机观看 | 乱淫的女高中暑假调教h | 中文字幕在线播放日韩 | 91亚洲国产成人精品一区二区三 | 国产精品一区二区久久乐夜夜嗨 | a级黄色毛片三 | 黑人性视频 | 亚洲欧美日韩精品 | 爱逼综合网| 国产精品国产三级国产普通话三级 | 大学生一级一片全黄 | 999这里只有是极品 999资源站 | 女优中文字幕 | 久久免费在线视频 | 欧美顶级丰满另类xxx | 国产一级特黄毛片 | 成人羞羞网站入口免费 | 99精品福利 | 亚洲精品久久区二区三区蜜桃臀 | 在线视频激情小说 | 99re6这里只有精品 | 久草蜜桃| 狠狠撸视频 | 精品一区二区三区免费 | 曰韩中文字幕 | 精品欧美色视频网站在线观看 | √天堂资源8在线官网 | 亚洲s色大片在线观看 | 欧美最猛性xxxx | 中文字幕在线网站 | 日韩动漫av | 国产亚洲第一伦理片在线c 国产亚洲精品久久久久动 国产亚洲精品久久久久久大师 | 久久精品国产99国产精品导航 | 国产女主播在线喷水呻吟 | 欧美在线免费播放 | 亚洲性无码av中文字幕 | 国产亚洲视频在线播放香蕉 | 黑人干亚洲人 | 在线精品一区二区 | 青青草免费观看视频 | 国产精品成人无码久久久 | 激情欧美日韩一区二区 | 欧美成人精品第一区二区三区 | 怡红院一区二区 | 四虎永久在线视频 | 婷婷丁香五月天综合东京热 | 国产午夜精品一区二区理论影院 | 亚洲拍拍 | 五月天中文字幕mv在线 | 波多野结衣导航 | 成人韩免费网站 | 国产淫语对白粗口video | 美日韩一区二区三区 | 亚洲国产精品久久久天堂不卡 | 又爽又大又黄a级毛片在线视频 | 亚洲天天操| 国产成人久久 | 国产出轨一区 | 日日摸夜夜添夜夜添一区二区 | 五月婷婷开心网 | 91成人精品视频 | 亚洲国产一区二区三区日本久久久 | 97caoav| www.亚洲视频| 久久精品国产一区二区 | 国产色欲av一区二区三区 | 成人国产精品免费观看视频 | 亚洲 欧美 日韩 国产综合 在线 | 亚洲午夜精品在线观看 | 亚洲精品乱码久久久久久日本蜜臀 | 亚洲一区二区三区四区 | 欧美a级网站| 久久不见久久见免费影院 | 亚洲欧美在线观看 | 精品久久久久久乱码天堂 | 国产区一区二区三 | 一本到亚洲网 | 久久伊人网站 | 爱情岛论坛自拍 | 超碰人人99 | 日本边添边摸边做边爱喷水 | 久久久久国产精 | 韩国av在线免费观看 | 成人性做爰 | 午夜天堂影院 | 免费动漫av | 九九九九热精品免费视频点播观看 | 精品美女在线 | 四虎国产精品免费观看视频优播 | 少妇疯狂做受xxxx高潮台湾 | 欧美三级黄色大片 | av无码精品一区二区三区四区 | 最近更新中文字幕第一页 | 国产无遮挡又黄又爽免费网站 | 肉丝美足丝袜一区二区三区四 | 久久亚洲二区 | 亚洲中字 | 四虎永久地址www成人 | 1000部啪啪未满十八勿入 | 国产精品久久无码一区二区三区网 | 欧美午夜精品久久久久久人妖 | 老熟女重囗味hdxx69 | 无码人妻久久一区二区三区蜜桃 | 国产欧美视频一区 | 一区二区久久久 | 性囗交免费视频观看 | 久在线观看福利视频 | 国产成人综合色在线观看网站 | 免费美女毛片 | 国产性色αv视频免费 | 国产日韩一级 | 国产成人av一区二区三区在线 | 久久精品99国产精品日本 | 农村末发育av片四区五区 | 国产ts人妖一区二区 | 国产精品久久久久久久龚玥菲 | 第九色婷婷 | 亚洲永久精品在线观看 | 婷婷伊人久久大香线蕉av | 色偷偷噜噜噜亚洲男人 | 国产一区二区三区在线观看免费 | 日韩视频一区二区 | 中文字幕无码视频专区 | 日韩五月天 | 中文字幕久久综合 | 亚洲成人免费网站 | 日本wwwxxxx| 女被男啪到哭的视频网站 | 欧美最猛黑人xxxxx猛交 | 国产高清在线观看 | 成人毛片在线观看 | 久久中文字幕一区二区 | 91麻豆精品国产91久久久无需广告 | 一级做a视频在线观看 | 一本色道久久99一综合 | 久久久一级黄色片 | 国产又大又硬又爽免费视频试 | 狠狠色噜噜狠狠狠狠黑人 | 欧美三级在线观看视频 | 色猫成人网 | 揄拍成人国产精品视频99 | 欧美日韩人成综合在线播放 | 国产剧情av网站 | 少妇高潮惨叫久久久久久 | 久久不见久久见免费影院www日本 | 狠狠干天天爱 | 一个色av| 日韩一区二区三区精品 | 久久久久人妻一区精品性色av | 奇米777四色在线精品 | 夹得我好紧好爽日出了水视频 | avt天堂网 | 天天干狠狠操 | 丰满少妇弄高潮了www | 天堂中文在线播放 | 99精品国产在热久久 | 亚洲自拍成人 | 秋霞欧美视频 | 动漫av纯肉无码免费播放 | 日本人jizz | 亚洲第一成年免费网站 | 夜夜嗨av一区二区三区 | 久久综合久久88 | 亚洲第一a在线观看网站 | 亚洲精品色综合av网站 | 国产一区不卡 | 亚洲在线不卡 | 天堂成人在线观看 | 国产精品www伦之荡艳岳 | 精品国内自产拍在线观看 | 熟妇人妻久久中文字幕 | 亚洲成熟女人毛毛耸耸多 | 丰满少妇大力进入av亚洲 | 热久久精品免费视频 | 午夜视频在线瓜伦 | 亚洲国产97色在线张津瑜 | 另类综合二 | 欧美图片在线观看 | 天天射天天干天天舔 | 在线观看污视频网站 | 国产无遮挡又黄又爽免费网站 | 97在线视频免费人妻 | 精品国产一区二区三区久久 | 亚洲 欧美 日韩 国产综合 在线 | 亚洲欧美国产精品久久久久久久 | 2021国产精品 | 国产大学生粉嫩无套流白浆 | 少妇三级 | 国产无套内射又大又猛又粗又爽 | 婷婷嫩草国产精品一区二区三区 | 99久久久无码国产精品不卡 | 色久阁 | 林雅儿欧洲留学恋爱日记在线 | 午夜视频在线免费观看 | 国产欧美日韩高清 | 欧美日本精品一区二区三区 | 国产精品入口66mio | 日韩av在线免费看 | 免费国产成人高清在线观看网站 | wwwxxx在线播放| 69看片| 男女一进一出粗大楱视频 | 天天爽夜夜爽夜夜爽 | 久草成人在线 | h色在线观看 | 亚洲中文字幕无码中文字在线 | 豆花av在线| 在线免费av观看 | 玩弄japan白嫩少妇hd小说 | 18禁美女裸体无遮挡网站 | 国产精品一级视频 | 午夜影院在线免费观看 | 99re视频精品 | 国产亚av手机在线观看 | 69视频污 | 一本一道无人区 | 婷婷四房综合激情五月在线 | 国产一级二级视频 | 欧美日韩在线一区二区三区 | 四虎永久在线精品免费一区二区 | 人妻熟妇乱又伦精品视频 | 女性向h片在线观看 | 国产乱淫av片免费观看 | 丰满的继牳3中文字幕系列 丰满的少妇xxxxx人伦理 | 欧美大片一区二区 | 日本三级日本三级韩国三级视 | 成人性视频网站 | 8090yy亚洲精品久久 | 亚洲精品视频观看 | 成人网免费 | 天天摸天天干天天操 | 91精品国产91久久久久久最新 | 天天狠狠色噜噜 | 久久久亚洲欧洲日产国码aⅴ | 欧美二区乱c黑人 | 国产精品日韩欧美一区二区三区 | 日韩国产精品一区二区 | 91香蕉在线看 | 三级无遮挡 | 搡女人真爽免费视频大全 | 91插插插视频 | 国产福利萌白酱在线观看视频 | 国产99在线 | 欧美 | 国产精品白丝喷水在线观看 | 亚洲熟妇无码一区二区三区导航 | 日韩在线一区二区三区 | 嫩草在线观看视频 | 欧美69视频| 中文字幕乱码一区二区三区四区 | 国内精品视频一区二区三区 | 久久亚洲精品国产亚洲老地址 |