• <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 ?

    Solubilization of potassium containing minerals by high temperature resistant Streptomyces sp.isolated

    2016-08-26 07:46:00fromearthwormgut
    Acta Geochimica 2016年3期

    from earthworm's gut

    DianFeng Liu1,2,3·Bin Lian1,3·Bin Wang4

    ?

    Solubilization of potassium containing minerals by high temperature resistant Streptomyces sp.isolated

    from earthworm's gut

    DianFeng Liu1,2,3·Bin Lian1,3·Bin Wang4

    ?Science Press,Institute of Geochemistry,CAS and Springer-Verlag Berlin Heidelberg 2016

    A potassium solubilizing bacterial strain designated EGT,which is tolerant of high temperature,was isolated from an earthworm's gut to obtain a bacterium that can weather potassium-bearing rock effectively through solid-state fermentation.Molecular phylogeny and 16S rRNA gene sequence analysis demonstrated the bacterial strain was a member of the Streptomyces genus.To assess its potential to release potassium from silicate minerals,this strain was used to degrade potassium-bearing rock powder by solid-state fermentation.After fermentation,the amount of water-soluble Al,F(xiàn)e and K of the substrate with active inoculum was higher than those of the control,which had autoclaved inoculum,and those of the fresh substrate.The result indicated that the strain had the ability to weather potassium-bearing rock and could be used as an inoculum in the production of potassium bio-fertilizer,due to its potassium release activity from rock and tolerance to high temperature.

    Weathering·Potassium solubilizing bacteria· Streptomyces

    1 Introduction

    Potassium(K),an element essential for plant growth,plays an essential role for enzyme activation,protein synthesis and photosynthesis(Armengaud et al.2009;Basak and Biswas 2009;Lin 2010).It is one of the three main macronutrients,together with Nitrogen(N)and Phosphorus(P),which are needed for crop growth and crop productionincrease(AmtmannandArmengaud2007;Sugumaran and Janarthanam 2007;Chen et al.2008). Potassium in soil is typically divided into four forms:water-soluble(solution K),exchangeable,non-exchangeable and structural or mineral forms(Jalali 2006;Basak and Biswas 2009).Potassium from the water-soluble pool is directly available for plant uptake.Water-soluble K is readily replenished by the soil exchangeable K,which is held by negatively charged clay minerals and organic matter in soils.Some non-exchangeable K can become exchangeable when the water-soluble and exchangeable K are depleted by plant removal,leaching,or exchange reactions with other cations.Mineral K,which is the major proportion of total K in soils,can only become available very slowly through long-term soil weathering(Peterburgsky and Yanishevsky 1961;Basak and Biswas 2009;Ghiri et al.2010).Total reserves of K in soil are generally large,but more than 98%of them exists in the form of silicate minerals(microcline,muscovite,orthoclase biotite,feldspars,etc.)and can't be directly absorbed by plants (Sugumaran and Janarthanam 2007).However,crops need large amounts of potassium during growth.A large amount ofpotassiumfertilizermustbeaddedintosoiltoadequately supply crops with the potassium needed for sustaining crop production.

    Many countries,such as China,India and Brazil,are important agricultural countries and need large amounts of fertilizers every year,yet they are deficient in potassium fertilizerresources(Sunetal.2009;BasakandBiswas2010). However,thesecountriesarefortunatetoberichinlow-grade potassium-bearing rock(PBR)(Chen 2000;Basak and Biswas2009).Ifthesematerialscanbeconvertedintopotassium fertilizer by some suitable chemical or biological means,the lack of potassium fertilizer resources would be greatly eased inthoseagriculturalcountries.Someresearchershaveproved thatcompostingtechnologycaneffectivelyconvert unavailable K into plant available form because of the acidic environment prevailing during composting,and the product of mineral K compost can increase crop yields(Nishanth and Biswas 2008;Biswas 2010).

    The natural weathering rates of minerals are very low. Some microorganisms must be added into the compost to degrade potassium-bearing minerals and quickly release enough K.It has been found that many microorganisms can enhance the weathering of potassium-bearing minerals,however most of them cannot survive high temperature.The temperatureinsidecompostisgenerallyhigh,oftentimesmore than50°Cduringcomposting.Therefore,somemicrobesthat are tolerant to high temperatures are necessary if weathering potassium-bearing rocks through composting technology.

    Earthworms have been described as ecosystem engineers due to their key role in altering the biological activity and physical structure of soils(Liu et al.2011;Zangerle′ et al.2011).The role of earthworms in promoting the weathering of potassium-bearing minerals have been previously reported,and earthworms'gut microbes may play an important role in increasing the rates of mineral weathering(Basker et al.1994;Carpenter et al.2007,2008;Liu et al.2011).Therefore,earthworms'guts are potential resources from which some potassium solubilizing microorganisms could be isolated.In this study,a potassium solubilizing bacterium,which tolerated high temperature,was isolated from the gut of the earthworms after they fed on potassium-bearing rock powder for 10 days.Subsequently,this strain was used to degrade potassium-bearing rock powder by solid-state fermentation to examine its weathering ability.

    2 Materials and methods

    2.1Preparation of K-bearing minerals,earthworms and other materials

    Potassium-bearing rock resource is rich in Luoyang,Henan Province,China.To develop and utilize the resource,we collected some PBR from Luoyang.The rock was crushed and sieved to pass through a 0.074 mm mesh.The mineral composition and the elemental composition of the rock were determined using the K-value method of X-ray diffraction(Rigaku,D/MAx-2200)(Li et al.2003)and X-ray Fluorescence(Axios,PW4400),respectively,in the Institute of Geochemistry,Chinese Academy of Sciences. Therock'smineralcompositioncontainsfeldspar (70.99%),quartz(23.45%),hematite(3.62%),montmorillonite(1.66%),illite(0.15%)and hornblende(0.13%). The major element oxides of the PBR are K2O(6.36%),Al2O3(11.52%),SiO2(70.36%),F(xiàn)e2O3(0.53%),CaO (0.38%),MgO(0.06%),Na2O(2.53%)and Loss on ignition(LOI,8.02%).

    The earthworms(Eisenia foetida)were purchased from Henan Academy of Agricultural Sciences.Oyster mushroom culture waste was collected from Henan Institute of Science and Technology.Wheat bran and sugar were purchased from the market.

    2.2Isolation of K-solubilizing bacteria

    Seven hundred grams of K-bearing rock powder,mixed with 200 mL of deionized water,was autoclaved at 121°C for 30 min.After cooling,35 earthworms were placed into the mineral powder and fed for 10 days.The feeding containers were covered to avoid light;the laboratory temperature was about 25°C during feeding.The earthworms were sedated,surface sterilized with ethanol(75%)and dissected under sterile conditions after feeding on mineral powder for 10 days.The whole gut content of each specimen without gut wall was extracted with a sterile spatula and transferred into sterile 2 mL tubes.The gut content was immersed with sterile distilled water,and shaken at 200 rpm for 10 min at 28°C to detach the bacteria from the mineral particles.The liquid mixture was allowed to stand for 20 min to obtain the microbe-containing supernatant to isolate the mineral-solubilizing bacteria.The medium for isolating mineral-solubilizing bacteriawasAleksandrov'smedium(sucrose5.0 g,MgSO40.5 g,CaCO30.1 g,Na2HPO4·12H2O2.0 g,F(xiàn)eCl3·6H2O 0.005 g,potassium-bearing rock powders 1.0 g,agar 18.0 g,H2O 1.0 L,pH 7.0-7.2)(Li et al. 2008),a common medium used to isolate silicate-weathering bacteria.The supernatant was serially diluted,and the aliquots of each dilution were spread on plates of Aleksanderov's medium and incubated at 28°C for 2-3 days. Selected colonies were further purified using the same medium.The colonies were stored at 4°C until further use.

    The above microbial strains were inoculated to Aleksanderov's medium and incubated at 50°C for 2 days.The colonies,which grew well at 50°C,were selected and stored onslantsforstudyingthesolubilityofK-bearingrockpowder.

    2.3Morphology and biochemical characterization of the strain

    The mycelia of the isolates,identified as species belonging to the genus Streptomyces by analyzing their morphological characteristics and by biochemical tests,were observed by using the cover slip method,in which sterile square cover slips were inserted at an angle of 45°in sterile Aleksandrov's agar medium in petri dishes.Individual cultures would grow to the intersection of the medium and cover slips.The cover slips were removed after three days of incubation,air-dried and observed with a microscope. Morphological characters were photographed(Thakur et al. 2007).

    Biochemical tests,including Gram staining,nitrate reduction,amylohydrolysis,Voges-Proskauer reaction,and catalase activities,were performed according to the method we used in a previous study(Liu et al.2012).

    2.4DNA extraction,amplification and sequencing

    Cultures for DNA extraction were prepared by inoculating 100 mL of yeast extract medium(YEM)with 100 μL of spore suspension.The YEM medium[sucrose 10.0 g,yeast extract 0.2 g,(NH4)2SO40.5 g,CaCO31.0 g,MgSO40.5122 g,KCl 0.1 g,Na2HPO4·12H2O 2.507 g,H2O 1.0 L,pH 7.0-7.2]was prepared as previously described (Zhou et al.2010).After incubating at 37°C for 48 h on a rotary shaker at the rate of 180 rpm,the culture was transferred to a centrifuge tube(2 mL),and centrifuged at 10,000×g for 10 min to concentrate cells into a pellet for extraction of bacterial genomic DNA.DNA was extracted using a Bacterial Genomic DNA Extraction Kit(Omega,US)according to the manufacturer's instructions.

    The 16S rRNA gene was amplified by polymerase chain reaction(PCR)using bacterial universal primers 16S-fD1 (5′-AGAGTTTGATCCTGGCTCAG-3′)and 16S-rD1(5′-ACGGTTACCTTGTTACGACTT-3′)(Weisburgetal. 1991).The reaction mixture for PCR amplification was prepared as follows:0.4 mM of deoxynucleoside triphosphates,0.4 μM of each primer,1×PCR buffer,2 mM magnesiumchloride,1UofTaqDNApolymerase,and1 μL (about 5-15 ng)of template DNA in a final volume of 30 μL.Amplification was made using a touchdown procedure,as follows:the annealing temperature was set at 65°C and decreased by 1°C every cycle until reaching a‘‘touchdown''at 55°C.The amplification program consisted of 5 min at 94°C,and 10 touchdown cycles of denaturation at 94°C for 1 min,annealing at 65°C(with the temperature decreasing 1°C each cycle)for 1 min,and extension at 72°C for 2 min,followed by 25 cycles of 94°C for 1 min,55°C for 1 min,and 72°C for 2 min.During the last cycle,the length of the extension step was increased to 10 min. After amplification,the PCR product was checked by electrophoresis in 1.5%(w/v)agarose gels.

    The PCR product was excised from 2%low melting point agarose(Sigma,St-Louis,MO)and the DNA was purified using a Gel Isolation Kit following the manufacturer's instructions(Promega,Madison,WI,USA).The purified PCR product was sequenced by Shanghai Sangon Biological Engineering Technology&Services Co.,Ltd.

    2.5Phylogenetic analysis

    The obtained 16S rRNA gene sequence was compared to those in the National Center for Biotechnology Information database using the BLAST procedure(Altschul et al. 1997).The reference sequences with the highest similarities to the query were retrieved from GenBank.The target 16S rRNA gene sequence and the retrieved reference sequences were aligned with the ClustalX program(Larkin et al.2007)with parameters set to its default values. Alignments were improved by comparison to the secondary structures and any regions of uncertain alignment were omitted from the subsequent analyses.

    The best-fit model of nucleotide substitution for the data sets was selected using the program PAUP 4.0b10(Swofford 2002)and Modeltest 3.06(Posada and Crandall 1998). Base composition and sequence variability were examined using the software package MEGA4.0(Tamura et al. 2007).A minimum evolution(ME)phylogenetic tree with 1000 bootstrap was then constructed using the Tamura-Nei model,with the pairwise deletion of gaps by Mega 4.0 package.

    The outgroup used for further phylogenetic analysis was based on the above result of ME.Further phylogenetic analysis,conducted using PAUP 4.0b10 with ME method,was performed using heuristic searches with the random stepwise addition of 10 replicates and tree bisection-reconnection(TBR)rearrangements in effect.The optimal model of nucleotide substitution for the ME analyses,HKY85,was from the result of the best-fit nucleotide substitution model selection.Bootstrap analyses were performed for 1000 replicates to evaluate the robustness of each clade.

    2.6Mineral weathering by the bacterial isolate

    The isolate was revitalized on plates of Aleksanderov's medium and incubated at 37°C for 3-4 days to obtain its spores.The spores and aerial mycelia were scraped off the agar surface,using a sterilized inoculation loop,when a mass of gray spores appeared on the plates.The spore suspension was then prepared in sterile H2O.

    The solid-state medium for the assessment of the effect of bacteria on mineral weathering was prepared as follows:the waste of the oyster mushroom culture(66%)was grounded,dried and mixed with rock powder(16%),wheat bran(16%)and sugar cane dregs(2%).Water was added into the mixture;the ratio of water to mixture was 1.1:1(v/m).The mixed substrate(about 1.5 kg wet wt)was poured into heat resistant polypropylene bags and sterilized(substrate temperature 121°C)for 30 min.

    After the substrate had cooled,it was inoculated with 500 mL of spore suspension(108spore mL-1).Then,the substrate was incubated at 37°C for 14 days.The control,whose substrate components were the same with the above treatment,was inoculated with autoclaved inoculum,and also incubated at 37°C for 14 days.Each treatment was carried out on three biological replicates.The substrates,incubated for 14 days,were sampled to determine their water-soluble elements'content.

    2.7Determination of water-soluble K,Al,F(xiàn)e and Ca

    The samples for determining elemental concentration were prepared by drying them in an oven at 70°C.To assess the isolate's potential for enhancing mineral weathering,concentrations of water-soluble K,Al,F(xiàn)e and Ca of the three samples,including the fresh solid-state medium,the substrate inoculated with autoclaved inoculum and the one inoculated with living bacterium,were determined by inductively coupled plasma atomic emission spectrometry (ICP-AES,Optima 2100 DV,Perkin Elmer,USA).

    Determination of the concentration of water-soluble K,Al,F(xiàn)e and Ca was performed using the methods as previously described(Liu et al.2011)with the following modifications:five grams of a dried sample was mixed with 50 mL of ddH2O in a 250 mL flask followed by 30 min of vigorous shaking.After shaking,the samples were centrifuged at 8000 rpm for 10 min.The supernatants were filtered through a 0.45 μm filter paper to obtain a purified extract.The concentrations of water-soluble K,Al,F(xiàn)e and Ca in the purified extract were determined by ICP-AES.

    3 Results

    3.1Isolation of mineral potassium-solubilizing bacteria tolerant to high temperature

    Afterisolationandrepeatedpurification,sevenfast-growing microbial strains were obtained from the Alexander silicate medium at 28°C.These strains were inoculated into the Alexander silicate medium and cultivated in an incubator at 50°C.One strain was found growing in the medium and forming a strain colony;this strain was labeled‘EGT'. Strain EGT grew well in the solid Alexander silicate medium at 28 and 37°C.At 50°C,however,the rate of growth was reduced and the strain colonies were small.EGT's colonies appeared to be white,dry and intensely woolly. After a while,gray spores appeared on the surface of the colonies(see Fig.1).Furthermore,white mycelium pellets formed when EGT was put into a liquid medium at a constant temperature of 28/37°C for 28 h with agitation at 180 r/min.The Strain EGT was Gram-positive.

    The results of the measurements,including nitrate reduction,amylohydrolysis and catalase activities,were all positive;The Voges-Proskauer reaction,however,produced a negative result.The results of morphological observations were given in Fig.1.After the strain grew on for 3 days,a mass of gray spores appeared on the aerial hyphae.Straight spore chains could be clearly observed with an optical microscope.

    3.2Identification and phylogeny of strain EGT

    Fig.1 Colonies of the strain EGT and optical micrograph(×400)of its mycelium.The top figure showed the colonies of the strain EGT grown on solid Aleksanderov's medium at 28°C for three days.Gray spore had been formed.The bottom figure showed the morphological character of the strain EGT's mycelium observed with an optical microscope

    The 16S rRNA gene sequence of Strain EGT derived from clones has been submitted to GenBank(accession number JF701918).Thegenesequencelengthof16rRNAis1381 bp,among which A occupies 22.3% (308 bp),T 18.0% (249 bp),G 33.8%(467 bp),C 25.9%(357 bp),A+T 40.3%(557 bp)and C+G 59.7%(824 bp).The four base group percentages are similar to those in the 16S rRNA gene sequences of other Streptomyces in the GenBank.

    Fig.2 The divergences of 16S rRNA gene sequences between the strain EGT and some Streptomyces species

    Fig.3 The minimum evolution tree for Tamura-Nei distance matrix of the nearly complete 16S rRNA gene sequences of the strain EGT and some Streptomyces species using the software package MEGA4.0.Numbers on nodes correspond to percentage bootstrap values for 1000 replicates

    The 16S rRNAgenesequencewas analyzedby BLAST in thesequencebaseofGenBank.Theresultsshowthatthemost similar16S rRNAgenesequencesallbelongtoStreptomyces variants,indicating that EGT is one of the Streptomyces.The differences between the EGT and the thirteen 16S rRNAgenesequencesofStreptomycesareshowninFig.2.Itcanbe seen that the sequence difference is negligible.In particular,the divergence from S.griseorubens,S.labedae,S.erythrogriseus,S.variabilis and S.pseudogriseolus is only 0.1%,which is within the criterion 16S rRNA≤3%proposed for agreement(Embley and Stackebrandt 1994).

    Multiple alignments using Clustal X,suggest that the strain's 16S rRNA gene sequence is 1384 bp(including gap),amongwhichA occupies 22.3%,T 18.2%,C 25.8%,G 33.7%,A+T 40.5%and C+G 56.5%.We also observethattheconcentrationofC+Gishigherthanthatof A+T,the average sequence divergence is 0.5%(p-distance),andtheaveragevalueofthetransformation/transversion ratio is 1.273.We note that the disparity between the base groups greatly affects the reconstruction of the phylogeny(Lockhart et al.1994).The results reveal that there are differences in the base groups;these differences must be considered when the phylogeny is analyzed.In addition,when the value of transformation/transversion is less than 2.0,the mutation of the gene sequence is in a saturation state and is easily affected by evolutionary noise. Consequently,errors may occur if extra weights are not added when reconstructing phylogeny(Knight and Mindell 1993;Liu and Jiang 2005).The average value of transformation/transversionintheexperimentis1.273andthishasto beaccountedforduringthephylogenyanalysis.Theresultof a hierarchical likelihood test performed using Model test shows that the best model in the phylogeny analysis is the Hasegawa-Kishino-Yano(HKY)model.This model considers both the differences in the base groups and the transformation/transversion ratio,and is thus suitable for phylogeny analysis of the current data group.

    Figure 3 shows the ME phylogeny based on the Tamura-Nei model derived using MEGA 4.0 software. Four branches are given:the first branch includes S. aureofaciens,S.variabilis,S.erythrogriseus,S.pseudogriseolus,S.griseorubens,S.labedae and the strain EGT;the second branch includes S.xylophagus,S.althioticus,S. matensis and S.almquistii;the third includes S.viridochromogenes;and the fourth S.tendae and S.tritolerans. Figure 3 reveals that these latter,fourth-branch strains are the sister group of the other bacteria.Thus,these two strains have been used as outgroups when the phylogeny was reconstructed using PAUP 4.0 software.

    Fig.4 The minimum evolution tree for HKY85 distance matrix based on nearly complete 16S rRNA gene sequences of the strain EGT and some Streptomyces species using the program PAUP 4.0b10. Numbers on nodes correspond to percentage bootstrap values for 1000 replicates

    The ME phylogeny based on the HKY85 model was established using PAUP 4.0 software(seen in Fig.4).Thetopological features of the phylogeny in this figure are similar to those in Fig.3.In addition to the outgroups,the ingroups of the phylogenetic tree also have three branches that are similar to those in Fig.3.Furthermore,the strain EGT also belongs to the first branch here.These two phylogenetictreesverifythatEGTisoneofthe Streptomyces.

    3.3Effects of strain EGT on weathering of PBR

    After the PBR powders were degraded by EGT through solid-state fermentation,the changes in the aqueous concentrations of major elements were tested to assess the isolate's potential for enhancing mineral weathering.The results are shown in Fig.5 and indicate that the proportions ofwater-solubleAl,F(xiàn)eandKinthesubstrateincubatedwith live inoculum for 14 days were higher than those obtained from the control with autoclaved inoculum and the fresh substrate.Theamounts ofaqueousAl,F(xiàn)eandKintheactive bacterial culture were 23.08%,123.19%and 30.99%,respectively,higher than that of the fresh substrate and were 45.45%,52.48%and9.13%,respectively,higherthanthat of the abiotic control incubated with autoclaved inoculum. The results reveal that EGT has a significant effect on the weathering of potassium-bearing mineral powders.

    4 Discussion

    4.1Phylogeny and molecular identification of strain EGT

    Streptomyces is the main genus of the actinomycete microorganism.It is the most prevalent among the actinomycetes in soil,and contributes to the soil ecology and circulation of materials(Oskay 2009;Srivibool et al. 2010).Streptomyces have a diverse range of species and metabolism,and are important microbial resource for humans.At present,the number of Streptomyces granted legal names exceeds 600(Ka¨mpfer et al.2008).Since the 1940s,some 55%of the physiologically active substances from 12,000 microorganisms have been produced by Streptomyces(Xu et al.2001).

    Fig.5 Amount of water-soluble elements released by the strain EGT after incubating for 14 days through solid-state fermentation(Each value represented the average of three biological replicates).Fresh substrates were the solid-state medium before composting.Controls were incubated for fourteen days by autoclaved inoculum.Error bars are±SD(n=3)

    Considering its 16S rRNA gene sequence and molecular phylogeny,the strain EGT obtained from the earthworm intestinaltractcanbeidentifiedasaspeciesofStreptomyces.The identification and classification of the microbial strain underliesitsapplication.However,allofthesystemsusedto identify bacteria,regardless of whether they are phenotypic or genotypic,have their limitations,because no single test methodologyprovidesresultsthatare100%accurate(Janda and Abbott 2002).The main approach used for the identificationandclassificationofprokaryoticspeciesisbasedonits 16S rRNA gene sequence and phylogenetic analysis.Bergey's classification system,widely accepted by microbiologists and currently considered as the best approximation to an official classification,is based on the homologous and phylogenetic analysis of 16S rRNA genes and the classical microscopic and biochemical observation of the relatedness of the organisms(Clarridge 2004).Strains whose similarity to the 16S rRNA gene sequence are more than 95%can be classified into a genus(Clarridge 2004),and the strains whose similarity are more than 97%can be classified into a species(Embley and Stackebrandt 1994).

    Despite the EGT being confirmed as one of the Streptomyces by its phylogenetic position and similarity to the 16S rRNA gene sequence with other Streptomyces,the species name of this strain cannot currently be ascertained.The maximum sequence divergence of the 16S rRNA gene between EGT and the thirteen Streptomyces downloaded from GenBank is just 1.2%,among which the sequence divergence between EGT and the five bacteria,including S. griseorubens,S.pseudogriseolus.S.erythrogriseus,S.variabilis and S.labedae,is only 0.1%.This suggests a general lack of suitability for Streptomyces.The strains can however be classified into a species when their 16S rRNA gene has a similarity greater than 97%.This is generally used as a criterion for most prokaryotic species.It seems the 16S rRNA gene does not have sufficient resolution to differentiate the genus and the species(Ka¨mpfer et al.2008).Due to the complexity of the Streptomyces classification and a lack of acknowledged standard,the conception of species for this genus in the systematics has always been a difficult problem (Syed et al.2007).To unequivocally identify the EGT strain,extensive phenotypic and genotypic testing is required.

    4.2Effect of EGT on the weathering of PBR

    Microorganisms play an important role in the process of mineral weathering.They promote the formation of soil and they offer plants nutrients such as phosphorus,potassium and silicon(Banfield et al.1999;Kim et al.2004;Hall et al.2005).For instance,potassium-solubilizing bacteria can release potassium from minerals,promote the growth of plants,improve harvests,strengthen the anti-virus ability of plants and improve soil quality(Sheng 2005a;Basak and Biswas 2009,2010;Youssef et al.2010).It has a wide application in agriculture.

    Many microorganisms have been found to possess this potassium-releasing ability,e.g.Pseudomonas,Burkholderia,Acidithiobacillus ferrooxidans,Bacillus mucilaginosus,B.edaphicus and B.circulans,etc.(Lian et al.2002;Sheng 2005b;Zhaoetal.2008).However,therearestill limitations to the use of these bacteria as microbial fertilizers.First,microbial fertilizers are usually manufactured using composting at a high temperature,often above 50°C.As these bacteria'snormallivingtemperatureisfarlowerthan50°C,they may die at the high temperatures used.In addition to this,althoughsomebacteria,suchasBacillusmucilaginosus,have good potassium-releasing capability,and they also release excessive amounts of polysaccharide during the fermentation,whichmakesthefermentationbrothverythick and viscid.This makes it difficult to produce the required liquid inoculum for microbiological fertilizers that use the liquid state deep-seated fermentation method.

    In contrast,the strain EGT has many advantages.Firstly,it can successfully weather potassium-bearing mineral powders and it can resist high temperatures and survive at 50°C.Secondly,procedures for seed preparation are simple due to the large number of spores yielded by the EGT after the desired incubating time.Therefore,EGT is a good choice for use in microorganism fertilizers.

    AcknowledgmentsThisworkwassupportedbytheNationalNatural Science Foundation of China(41173091,U1204405),Aid Project for theLeadingYoungTeachersinHenanProvincialInstitutionsofHigher Education of China(2012GGJS-284),and Natural Science Foundation of Henan Educational Committee,China(12B180027,14B180010).

    References

    Altschul SF,Madden TL,Scha¨ffer AA,Zhang J,Zhang Z,Miller W,Lipman DJ(1997)Gapped BLAST and PSI-BLAST:a new generation of protein database search programs.Nucleic Acids Res 25:3389-3402

    Amtmann A,Armengaud P(2007)The role of calcium sensorinteracting protein kinases in plant adaptation to potassiumdeficiency:new answers to old questions.Cell Res 17:483-485

    Armengaud P,Sulpice R,Miller AJ,Stitt M,Amtmann A,Gibon Y (2009)Multilevel analysis of primary metabolism provides new insights into the role of potassium nutrition for glycolysis and nitrogenassimilationinarabidopsisroots.PlantPhysiol 150:772-785.doi:10.1104/pp.108.133629

    Banfield JF,Barker WW,Welch SA,Taunton A(1999)Biological impact on mineral dissolution:application of the lichen model to understanding mineral weathering in the rhizosphere.Proc Natl Acad Sci USA 96:3404-3411

    Basak BB,Biswas DR(2009)Influence of potassium solubilizing microorganism (Bacillus mucilaginosus)and waste mica on potassium uptake dynamics by sudan grass(Sorghum vulgare Pers.)grown under two Alfisols.Plant Soil 317:235-255

    Basak BB,Biswas DR(2010)Co-inoculation of potassium solubilizing and nitrogen fixing bacteria on solubilization of waste mica and their effect on growth promotion and nutrient acquisition by a forage crop.Biol Fert Soils 46:641-648. doi:10.1007/s00374-010-0456-x

    Basker A,Kirkman JH,Macgregor AN(1994)Changes in potassium availability and other soil properties due to soil ingestion by earthworms.Biol Fert Soils 17:154-158

    Biswas DR(2010)Nutrient recycling potential of rock phosphate and waste mica enriched compost on crop productivity and changes in soil fertility under potato-soybean cropping sequence in an Inceptisol of Indo-Gangetic Plains of India.Nutr Cycl Agroecosyst,pp.1-16

    Carpenter D,Hodson ME,Eggleton P,Kirk C(2007)Earthworm induced mineral weathering:preliminary results.Eur J Soil Biol 43:S176-S183

    Carpenter D,Hodson ME,Eggleton P,Kirk C(2008)The role of earthworm communities in soil mineral weathering:a field experiment.Mineral Mag 72:33-36

    Chen J(2000)Development and utilization of potassium-bearing rock resource and their prospects.Geol Chem Miner 22:58-64

    Chen HC,Wang SY,Chen MJ(2008)Microbiological study of lactic acid bacteria in kefir grains by culture-dependent and cultureindependent methods.Food Microbiol 25:492-501

    Clarridge JE(2004)Impact of 16S rRNA gene sequence analysis for identification of bacteria on clinical microbiology and infectious diseases.Clin Microbiol Rev 17(4):840-862

    Embley TM,Stackebrandt E(1994)The molecular phylogeny and systematicsoftheActinomycetes.AnnuRevMicrobiol 48:257-289

    Ghiri MN,Abtahi A,Jaberian F,Owliaie HR(2010)Relationship between soil potassium forms and mineralogy in highly calcareous soils of southern Iran.Aust J Basic Appl Sci 4:434-441

    Hall K,Arocena JM,Boelhouwers J,Liping Z(2005)The influence of aspect on the biological weathering of granites:observations fromtheKunlunMountains, China.Geomorphology 67:171-188.doi:10.1016/j.geomorph.2004.09.027

    Jalali M(2006)Kinetics of non-exchangeable potassium release and availability in some calcareous soils of western Iran.Geoderma 135:63-71.doi:10.1016/j.geoderma.2005.11.006

    Janda JM,Abbott SL(2002)Bacterial identification for publication:when is enough enough?J Clin Microbiol 40:1887-1891.doi:10. 1128/jcm.40.6.1887-1891.2002

    Ka¨mpfer P,Huber B,Buczolits S,Thummes K,Gru¨n-Wollny I,Busse HJ(2008)Streptomyces specialis sp.nov.Int J Syst Evol Microbiol 58(11):2602-2606

    Kim J,Dong H,Seabaugh J,Newell SW,Eberl DD(2004)Role of microbes in the smectite-to-illite reaction.Science 303:830-832. doi:10.1126/science.1093245

    Knight A,Mindell DP(1993)Substitution bias,weighting of DNA sequence evolution,and the phylogenetic position of Fea's viper. Syst Biol 42(1):18-31

    Larkin MA et al(2007)Clustal W and Clustal X version 2.0. Bioinformatics23:2947-2948.doi:10.1093/bioinformatics/ btm404

    Li YH,Xu FG,Wang J,Song ZK(2003)Quantitative analysis is of ettringite in cement hydration products by‘‘value K''method of XRD.Chin J Spectrosc Lab 20:334-337

    Li ZG,Luo YM,Teng Y(2008)Research method of soil and environmental microbiology.Science Press,Beijing

    Lian B,F(xiàn)u PQ,Mo DM,Liu CQ(2002)A comprehensive review of the mechanism of potassium releasing by silicate bacteria.Acta Mineral Sin 22:179-183

    Lin YH(2010)Effects of potassium behaviour in soils on crop absorption.Afr J Biotechnol 9:4638-4643

    Liu DF,Jiang GF(2005)Molecular phylogenetic analysis of Acridoidea based on 18S rDNA with a discussion on its taxonomic system.Acta Entomol Sin 48(2):232-241

    Liu D,Lian B,Wang B,Jiang G(2011)Degradation of potassium rock by earthworms and responses of bacterial communities in its gut and surrounding substrates after being fed with mineral. PLoS One 6:e28803.doi:10.1371/journal.pone.0028803

    Liu D,Lian B,Dong H(2012)Isolation of Paenibacillus sp.and assessment of its potential for enhancing mineral weathering. GeomicrobiolJ29:413-421.doi:10.1080/01490451.2011. 576602

    Nishanth D,Biswas DR(2008)Kinetics of phosphorus and potassium release from rock phosphate and waste mica enriched compost and their effect on yield and nutrient uptake by wheat(Triticum aestivum).Bioresour Technol 99:3342-3353

    Oskay M (2009)Comparison of Streptomyces diversity between agricultural and non-agricultural soils by using various culture media.Sci Res Essay 4:997-1005

    Peterburgsky AV,Yanishevsky FV(1961)Transformation of forms of potassium in soil during long-term potassium fertilization. Plant Soil 15:199-210.doi:10.1007/bf01400454

    Posada D,Crandall KA(1998)MODELTEST:testing the model of DNA substitution.Bioinformatics 14:817-818

    Sheng XF(2005)Growth promotion and increased potassium uptake of cotton and rape by a potassium releasing strain of Bacillus edaphicus.Soil Biol Biochem 37:1918-1922

    Srivibool R,Jaidee K,Sukchotiratana M,Tokuyama S,Pathom-aree W (2010)Taxonomic characterization of Streptomyces strain CH54-4 isolated from mangrove sediment.Ann Microbiol 60:299-305.doi:10.1007/s13213-010-0041-4

    Sugumaran P,Janarthanam B(2007)Solubilization of potassium containing minerals by bacteria and their effect on plant growth. World J Agric Sci 3:350-355

    Sun AW,Zhang WF,Du F,Gao LW,Zhang FS,Chen XP(2009)China's development strategy on potash resources and fertilizer. Mod Chem Ind 29(9):10-16

    Swofford DL(2002)PAUP*phylogenetic analysis using parsimony (*and other methods),Version 410b10.Sinauer Associates,Sunderland

    Syed DG,Agasar D,Kim CJ,Li WJ,Lee JC,Park DJ,Xu LH,Tian XP,Jiang CL(2007)Streptomyces tritolerans sp.nov.,a novel actinomycete isolated from soil in Karnataka,India.Antonie van Leeuwenhoek 92(4):391-397

    Tamura K,Dudley J,Nei M,Kumar S(2007)MEGA4:molecular evolutionary genetics analysis(MEGA)software version 4.0. Mol Biol Evol 24:1596-1599

    Thakur D,Yadav A,Gogoi BK,Bora TC(2007)Isolation and screening of Streptomyces in soil of protected forest areas from the states of Assam and Tripura,India,for antimicrobial metabolites.J Mycol Me′d 17:242-249

    Weisburg WG,Barns SM,Pelletier DA,Lane DJ(1991)16S Ribosomal DNA amplification for phylogenetic study.J Bacteriol 173:697-703

    Xu P,Zhang LP,Yu LY(2001)Classification of Streptomyces with theV-2variableregionin16SrDNA.BiodiversSci 9(2):129-137

    Youssef GH,Seddik WMA,Osman MA(2010)Efficiency of natural minerals in presence of different nitrogen forms and potassium dissolving bacteria on peanut and sesame yields.J Am Sci 6:647-660

    Zangerle′A,Pando A,Lavelle P(2011)Do earthworms and roots cooperate to build soil macroaggregates?A microcosm experiment.Geoderma 167-168:303-309.doi:10.1016/j.geoderma. 2011.09.004

    Zhao F,Sheng XF,Huang Z,He LY(2008)Isolation of mineral potassium-solubilizing bacterial strains from agricultural soils in Shandong Province.Biodiver Sci 16:593-600

    Zhou XY,Du Y,Lian B(2010)Effect of different culture conditions on carbonic anhydrase from Bacillus mucilaginosus inducing calciumcarbonatecrystalformation.ActaMicrobiolSin 50:956-962

    13 November 2015/Revised:15 January 2016/Accepted:29 March 2016/Published online:9 April 2016

    ? Bin Lian bin2368@vip.163.com;hn_ldf@126.com
    1Jiangsu Key Laboratory for Microbes and Functional Genomics,Jiangsu Engineering and Technology Research Center for Microbiology,College of Life Sciences,Nanjing Normal University,No.1,Wenyuan Road,Nanjing 210023,People's Republic of China
    2Department of Bioengineering,Puyang Vocational& Technical Institute,Puyang 457000,People's Republic of China
    3State Key Laboratory of Environmental Geochemistry,Institute of Geochemistry,Chinese Academy of Sciences,Guiyang 550081,People's Republic of China
    4Department of Bio-Engineering,Henan Institute of Science and Technology,Xinxiang 453003,People's Republic of China

    久9热在线精品视频| 毛片一级片免费看久久久久 | 色综合婷婷激情| 欧美97在线视频| 别揉我奶头 嗯啊视频| 日本黄色片子视频| 亚洲欧美一区二区三区国产| 天美传媒精品一区二区| 国产亚洲午夜精品一区二区久久 | 亚洲国产成人一精品久久久| 成年免费大片在线观看| 一级黄片播放器| 在现免费观看毛片| 2021少妇久久久久久久久久久| 久久久久久久精品精品| 国产av国产精品国产| 国精品久久久久久国模美| 国产黄片视频在线免费观看| 精品一区在线观看国产| 九色成人免费人妻av| 九色成人免费人妻av| 国国产精品蜜臀av免费| 夫妻午夜视频| 亚洲国产欧美人成| 少妇的逼好多水| 久久久国产一区二区| 国产成人精品婷婷| 国国产精品蜜臀av免费| 亚洲国产欧美人成| 激情五月婷婷亚洲| 国产精品精品国产色婷婷| 日韩成人av中文字幕在线观看| 嫩草影院新地址| 少妇猛男粗大的猛烈进出视频 | 国产毛片在线视频| 亚洲欧美日韩东京热| 三级男女做爰猛烈吃奶摸视频| 国产黄片美女视频| 国产高清不卡午夜福利| 99精国产麻豆久久婷婷| 大话2 男鬼变身卡| 欧美xxⅹ黑人| 天堂中文最新版在线下载 | 日韩不卡一区二区三区视频在线| 日韩伦理黄色片| 国产精品一及| 啦啦啦在线观看免费高清www| 在线观看三级黄色| 男女边吃奶边做爰视频| 国产国拍精品亚洲av在线观看| 97超视频在线观看视频| 久久人人爽人人爽人人片va| 亚洲内射少妇av| 激情 狠狠 欧美| 校园人妻丝袜中文字幕| 天美传媒精品一区二区| av免费观看日本| 欧美日韩精品成人综合77777| 国产精品秋霞免费鲁丝片| 日韩欧美精品v在线| 国产一区二区在线观看日韩| 菩萨蛮人人尽说江南好唐韦庄| 搡女人真爽免费视频火全软件| 成人国产av品久久久| 一级毛片久久久久久久久女| 国产亚洲最大av| 少妇裸体淫交视频免费看高清| 大片免费播放器 马上看| 一级毛片我不卡| 婷婷色综合www| 国产精品99久久99久久久不卡 | 各种免费的搞黄视频| 精品午夜福利在线看| 麻豆国产97在线/欧美| 久久久精品94久久精品| 日本av手机在线免费观看| 卡戴珊不雅视频在线播放| 丰满少妇做爰视频| 亚洲国产最新在线播放| 国产精品一区www在线观看| a级毛色黄片| 一级黄片播放器| 欧美日韩亚洲高清精品| 欧美高清性xxxxhd video| 在线观看人妻少妇| 国产 精品1| 亚洲欧美中文字幕日韩二区| 校园人妻丝袜中文字幕| 高清欧美精品videossex| 精品久久久久久久末码| 六月丁香七月| 亚洲欧美中文字幕日韩二区| 天堂俺去俺来也www色官网| 国产精品蜜桃在线观看| 亚洲国产精品国产精品| 成人午夜精彩视频在线观看| 精品久久久久久久人妻蜜臀av| 99re6热这里在线精品视频| 亚洲av二区三区四区| 日本免费在线观看一区| 成人毛片a级毛片在线播放| 日日啪夜夜撸| 99久久精品热视频| 各种免费的搞黄视频| 舔av片在线| 日本一二三区视频观看| 国产乱来视频区| 免费看日本二区| 亚洲在线观看片| 亚洲精华国产精华液的使用体验| 黄色一级大片看看| 麻豆久久精品国产亚洲av| 深夜a级毛片| 国产欧美另类精品又又久久亚洲欧美| 国产亚洲午夜精品一区二区久久 | 日日摸夜夜添夜夜添av毛片| 国产男女超爽视频在线观看| 久久精品人妻少妇| 看非洲黑人一级黄片| 国产精品人妻久久久影院| 久久久精品欧美日韩精品| 亚洲婷婷狠狠爱综合网| 精品一区二区三区视频在线| 性色av一级| 午夜精品一区二区三区免费看| 欧美人与善性xxx| av.在线天堂| 亚洲激情五月婷婷啪啪| 99久久精品热视频| 欧美另类一区| 亚洲高清免费不卡视频| 欧美xxxx性猛交bbbb| 亚洲精品乱码久久久v下载方式| 日韩一区二区视频免费看| 亚洲精华国产精华液的使用体验| 久久久久久久久久久免费av| 久久热精品热| 美女主播在线视频| 国产亚洲91精品色在线| 中国国产av一级| 亚洲精品影视一区二区三区av| 少妇 在线观看| 日日啪夜夜爽| 80岁老熟妇乱子伦牲交| 欧美日韩综合久久久久久| 免费看a级黄色片| 亚洲av免费在线观看| 啦啦啦中文免费视频观看日本| 久久久久精品性色| 别揉我奶头 嗯啊视频| 大又大粗又爽又黄少妇毛片口| 十八禁网站网址无遮挡 | 青春草国产在线视频| 欧美激情国产日韩精品一区| 亚洲成色77777| 亚洲欧美日韩无卡精品| 国产精品三级大全| 一本久久精品| 国产精品久久久久久精品古装| 久久久久久久亚洲中文字幕| 中文资源天堂在线| 三级国产精品欧美在线观看| 欧美bdsm另类| 久久久精品94久久精品| 亚洲欧美清纯卡通| 国产精品久久久久久精品古装| 久久久精品免费免费高清| av福利片在线观看| 国产精品福利在线免费观看| 777米奇影视久久| 欧美成人a在线观看| 狂野欧美白嫩少妇大欣赏| 尤物成人国产欧美一区二区三区| 少妇的逼水好多| 日本-黄色视频高清免费观看| av免费观看日本| 欧美另类一区| 热99国产精品久久久久久7| 蜜桃久久精品国产亚洲av| 亚洲在久久综合| 中文天堂在线官网| 一本色道久久久久久精品综合| 亚洲欧美日韩卡通动漫| 亚洲精品第二区| 日本一本二区三区精品| 在线精品无人区一区二区三 | 男女啪啪激烈高潮av片| 免费播放大片免费观看视频在线观看| 亚洲欧洲日产国产| 99久国产av精品国产电影| 亚洲美女搞黄在线观看| av在线亚洲专区| 两个人的视频大全免费| 国产成人91sexporn| av国产精品久久久久影院| 最近2019中文字幕mv第一页| 日本一本二区三区精品| 99视频精品全部免费 在线| 男女下面进入的视频免费午夜| 午夜激情久久久久久久| 亚洲婷婷狠狠爱综合网| 欧美日韩亚洲高清精品| 日韩成人伦理影院| 国产高清不卡午夜福利| 少妇丰满av| 激情 狠狠 欧美| 成年人午夜在线观看视频| 亚洲美女搞黄在线观看| 黄色配什么色好看| 国产精品国产三级专区第一集| 亚洲自偷自拍三级| 午夜老司机福利剧场| av线在线观看网站| 国产成人freesex在线| 91午夜精品亚洲一区二区三区| 少妇人妻久久综合中文| 久久久久久久精品精品| 99热全是精品| 久久精品熟女亚洲av麻豆精品| av.在线天堂| 欧美bdsm另类| 校园人妻丝袜中文字幕| 国产69精品久久久久777片| 日韩一区二区视频免费看| 制服丝袜香蕉在线| 久久久久久伊人网av| 午夜免费鲁丝| a级毛色黄片| 午夜免费男女啪啪视频观看| 亚洲欧美一区二区三区黑人 | 激情五月婷婷亚洲| 日韩亚洲欧美综合| 高清毛片免费看| 亚洲性久久影院| 亚洲激情五月婷婷啪啪| 国产精品久久久久久精品电影| av国产精品久久久久影院| 色视频www国产| 看免费成人av毛片| 国产在线男女| 在线天堂最新版资源| 亚洲国产精品专区欧美| 亚洲色图综合在线观看| 欧美成人精品欧美一级黄| 久久久久久久久久成人| 在线观看av片永久免费下载| 在线观看三级黄色| 欧美成人一区二区免费高清观看| 成年免费大片在线观看| 欧美日本视频| 日韩一本色道免费dvd| 免费不卡的大黄色大毛片视频在线观看| 大片免费播放器 马上看| 欧美极品一区二区三区四区| 十八禁网站网址无遮挡 | 免费观看的影片在线观看| 别揉我奶头 嗯啊视频| 国产欧美亚洲国产| 成人黄色视频免费在线看| 久久ye,这里只有精品| 亚洲四区av| 夜夜爽夜夜爽视频| 永久网站在线| 国产精品国产三级国产av玫瑰| 亚洲国产最新在线播放| 乱码一卡2卡4卡精品| 人体艺术视频欧美日本| 草草在线视频免费看| 丰满少妇做爰视频| 国产黄色视频一区二区在线观看| 久久精品熟女亚洲av麻豆精品| 大话2 男鬼变身卡| av又黄又爽大尺度在线免费看| 男男h啪啪无遮挡| 久久精品国产a三级三级三级| 女人久久www免费人成看片| 亚洲天堂av无毛| 亚洲av一区综合| 性色av一级| 免费看光身美女| 久久99精品国语久久久| 黄色怎么调成土黄色| 人妻系列 视频| 中文资源天堂在线| 亚洲精品,欧美精品| 欧美日韩视频高清一区二区三区二| 干丝袜人妻中文字幕| 国产一区二区三区综合在线观看 | 久久人人爽人人片av| 亚洲丝袜综合中文字幕| 天天躁夜夜躁狠狠久久av| 丰满乱子伦码专区| 黄色视频在线播放观看不卡| 国产成人a区在线观看| 我的老师免费观看完整版| 精品午夜福利在线看| 亚洲精品日本国产第一区| 一级毛片aaaaaa免费看小| 久久热精品热| 国产精品精品国产色婷婷| 亚洲精品中文字幕在线视频 | 国产午夜精品久久久久久一区二区三区| 免费不卡的大黄色大毛片视频在线观看| 各种免费的搞黄视频| 成人黄色视频免费在线看| 精品一区二区三卡| 18禁裸乳无遮挡动漫免费视频 | 国产日韩欧美在线精品| 少妇的逼水好多| av在线蜜桃| xxx大片免费视频| 国产中年淑女户外野战色| 国产精品麻豆人妻色哟哟久久| 亚洲国产高清在线一区二区三| 国产成人福利小说| 久久人人爽人人片av| 人妻一区二区av| 街头女战士在线观看网站| 日本av手机在线免费观看| 久久精品国产鲁丝片午夜精品| 精品国产露脸久久av麻豆| 精品午夜福利在线看| 51国产日韩欧美| a级一级毛片免费在线观看| 国产极品天堂在线| 久久精品久久精品一区二区三区| 中文字幕免费在线视频6| 在线a可以看的网站| 久久国产乱子免费精品| 性插视频无遮挡在线免费观看| av线在线观看网站| 欧美日韩一区二区视频在线观看视频在线 | 一个人看的www免费观看视频| 中国三级夫妇交换| 男人和女人高潮做爰伦理| 欧美变态另类bdsm刘玥| 亚洲av国产av综合av卡| 国产高清有码在线观看视频| 免费黄频网站在线观看国产| 亚洲av国产av综合av卡| 亚洲最大成人av| 国产精品蜜桃在线观看| av福利片在线观看| 大片电影免费在线观看免费| 亚洲精品成人av观看孕妇| 一个人看视频在线观看www免费| 精品久久久久久久久亚洲| 丰满少妇做爰视频| 日韩电影二区| 免费看a级黄色片| 性插视频无遮挡在线免费观看| 涩涩av久久男人的天堂| 国内精品美女久久久久久| 久久精品综合一区二区三区| 蜜桃亚洲精品一区二区三区| 色网站视频免费| 国产国拍精品亚洲av在线观看| 免费在线观看成人毛片| 少妇高潮的动态图| 黑人高潮一二区| 国产精品一二三区在线看| 白带黄色成豆腐渣| 国产黄a三级三级三级人| 婷婷色av中文字幕| 精品国产一区二区三区久久久樱花 | a级一级毛片免费在线观看| 91aial.com中文字幕在线观看| 亚洲精品影视一区二区三区av| 男女无遮挡免费网站观看| 久久久久精品久久久久真实原创| 18禁裸乳无遮挡免费网站照片| 成人午夜精彩视频在线观看| 日韩伦理黄色片| 国产老妇伦熟女老妇高清| 欧美日本视频| 免费av毛片视频| 少妇 在线观看| 成人免费观看视频高清| 2018国产大陆天天弄谢| 国产69精品久久久久777片| 99精国产麻豆久久婷婷| 噜噜噜噜噜久久久久久91| 精品99又大又爽又粗少妇毛片| 免费观看av网站的网址| 一级毛片电影观看| 别揉我奶头 嗯啊视频| 亚洲激情五月婷婷啪啪| 好男人视频免费观看在线| 美女被艹到高潮喷水动态| 欧美bdsm另类| 日韩 亚洲 欧美在线| 搞女人的毛片| 国产男人的电影天堂91| 香蕉精品网在线| 国产永久视频网站| 三级男女做爰猛烈吃奶摸视频| 色吧在线观看| 亚洲欧美日韩另类电影网站 | 国产成人精品一,二区| 国产 一区精品| 国产精品熟女久久久久浪| 不卡视频在线观看欧美| 精品午夜福利在线看| 婷婷色av中文字幕| 亚洲第一区二区三区不卡| 欧美一区二区亚洲| 免费黄频网站在线观看国产| 免费高清在线观看视频在线观看| 精品久久久精品久久久| 少妇的逼水好多| 日韩不卡一区二区三区视频在线| 国产片特级美女逼逼视频| 欧美+日韩+精品| 日韩三级伦理在线观看| 国产乱来视频区| 国产有黄有色有爽视频| 青春草亚洲视频在线观看| 老师上课跳d突然被开到最大视频| 亚洲精品,欧美精品| 国产亚洲精品久久久com| 亚洲在久久综合| 国产亚洲午夜精品一区二区久久 | 亚洲欧洲国产日韩| 日韩 亚洲 欧美在线| 老司机影院毛片| 一级二级三级毛片免费看| 亚洲人成网站高清观看| 99热国产这里只有精品6| 99热6这里只有精品| 国产高清不卡午夜福利| 在线观看国产h片| 在线观看一区二区三区激情| 国产 一区精品| 亚洲人与动物交配视频| 欧美区成人在线视频| 欧美一区二区亚洲| 大又大粗又爽又黄少妇毛片口| 搡女人真爽免费视频火全软件| 国产成人aa在线观看| 成人亚洲欧美一区二区av| 国产亚洲最大av| 乱码一卡2卡4卡精品| 日产精品乱码卡一卡2卡三| 亚洲四区av| 看十八女毛片水多多多| 色哟哟·www| 午夜精品国产一区二区电影 | 日韩强制内射视频| 免费少妇av软件| 亚洲美女视频黄频| 午夜激情福利司机影院| av.在线天堂| 亚洲精品影视一区二区三区av| 特级一级黄色大片| 国产亚洲91精品色在线| av线在线观看网站| 婷婷色综合大香蕉| 最近2019中文字幕mv第一页| 波野结衣二区三区在线| 久久ye,这里只有精品| 丝袜喷水一区| 免费观看a级毛片全部| 日韩 亚洲 欧美在线| 国产精品一区二区在线观看99| 国产淫语在线视频| 日韩av不卡免费在线播放| 最近手机中文字幕大全| 黄色一级大片看看| 深爱激情五月婷婷| 久久这里有精品视频免费| 国产一区亚洲一区在线观看| 国产精品蜜桃在线观看| 国产精品国产三级专区第一集| 国产精品嫩草影院av在线观看| 五月开心婷婷网| 国产精品女同一区二区软件| 99久久精品一区二区三区| 777米奇影视久久| 中文在线观看免费www的网站| 国产一区二区在线观看日韩| 性色av一级| 亚洲精品乱码久久久久久按摩| 国产亚洲精品久久久com| 国产精品.久久久| 午夜亚洲福利在线播放| 波多野结衣巨乳人妻| 777米奇影视久久| 久久久久久久久久久丰满| 欧美bdsm另类| 婷婷色av中文字幕| 亚洲精品视频女| 国产片特级美女逼逼视频| 九九在线视频观看精品| 国精品久久久久久国模美| 久久久久久久久久成人| 麻豆国产97在线/欧美| 免费少妇av软件| 日日撸夜夜添| 伊人久久国产一区二区| 看非洲黑人一级黄片| 91精品国产九色| 国产真实伦视频高清在线观看| 黄色视频在线播放观看不卡| 亚洲国产高清在线一区二区三| 卡戴珊不雅视频在线播放| 人妻制服诱惑在线中文字幕| 美女xxoo啪啪120秒动态图| 午夜免费男女啪啪视频观看| 高清av免费在线| 国产色爽女视频免费观看| 亚洲av成人精品一二三区| 性色av一级| 神马国产精品三级电影在线观看| 国产老妇伦熟女老妇高清| 国产av码专区亚洲av| 国模一区二区三区四区视频| 成人免费观看视频高清| 嫩草影院新地址| 看免费成人av毛片| 亚洲,一卡二卡三卡| 精品少妇黑人巨大在线播放| 国产精品女同一区二区软件| a级一级毛片免费在线观看| 大片电影免费在线观看免费| 免费少妇av软件| 免费电影在线观看免费观看| 国产色爽女视频免费观看| 国产精品一及| 老师上课跳d突然被开到最大视频| 99热国产这里只有精品6| 成人亚洲精品av一区二区| 婷婷色综合大香蕉| 欧美日韩亚洲高清精品| 五月伊人婷婷丁香| 又爽又黄无遮挡网站| 国产精品成人在线| 国产精品国产三级国产专区5o| 国产亚洲5aaaaa淫片| 国产亚洲一区二区精品| 国产极品天堂在线| 久久精品夜色国产| 天天躁夜夜躁狠狠久久av| 亚洲欧美中文字幕日韩二区| 欧美精品人与动牲交sv欧美| 久久久色成人| 我的老师免费观看完整版| 亚洲av免费高清在线观看| 国产免费福利视频在线观看| 久久久色成人| 纵有疾风起免费观看全集完整版| 国产淫片久久久久久久久| 我的老师免费观看完整版| 精品人妻熟女av久视频| 精品人妻偷拍中文字幕| 五月天丁香电影| 不卡视频在线观看欧美| 亚洲国产精品专区欧美| 亚洲美女搞黄在线观看| 一区二区av电影网| 久久久久久久国产电影| 亚洲欧美日韩无卡精品| 在线 av 中文字幕| 永久网站在线| 最近手机中文字幕大全| 在线天堂最新版资源| 毛片女人毛片| 亚洲欧美一区二区三区黑人 | 国产精品久久久久久精品电影| 最近最新中文字幕大全电影3| 国产av不卡久久| 看黄色毛片网站| 久久ye,这里只有精品| 久久亚洲国产成人精品v| 精品久久久久久久久av| 老女人水多毛片| 免费电影在线观看免费观看| 新久久久久国产一级毛片| 99热国产这里只有精品6| 九九爱精品视频在线观看| 99久久精品热视频| 久久久a久久爽久久v久久| 日韩av免费高清视频| 亚洲精品一二三| av国产精品久久久久影院| 日韩国内少妇激情av| 日韩强制内射视频| 国产在线男女| 91久久精品国产一区二区三区| 成人欧美大片| 久久久精品94久久精品| 99久久精品一区二区三区| 97在线视频观看| 日韩成人伦理影院| 在线观看美女被高潮喷水网站| 人人妻人人爽人人添夜夜欢视频 | 国产69精品久久久久777片| 婷婷色综合大香蕉| 中文字幕人妻熟人妻熟丝袜美| 亚洲av免费在线观看| 又黄又爽又刺激的免费视频.| 精品久久久久久久久av| 免费看不卡的av| 丰满乱子伦码专区| a级一级毛片免费在线观看| 少妇裸体淫交视频免费看高清| 成人高潮视频无遮挡免费网站| 国产成人a∨麻豆精品| 少妇高潮的动态图| 久久久久九九精品影院| 男的添女的下面高潮视频| 性色av一级| 少妇人妻 视频| 波多野结衣巨乳人妻| 午夜福利视频1000在线观看| 日韩精品有码人妻一区|