• <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 ?

    Increasing the appropriate seedling density for higher yield in dry direct-seeded rice sown by a multifunctional seeder after wheatstraw return

    2023-02-03 04:26:40TIANJinyuLIShaopingCHENGShuangLIUQiuyuanZHOULeiTAOYuXINGZhipengHUYajieGUOBaoweiWEIHaiyanZHANGHongcheng
    Journal of Integrative Agriculture 2023年2期

    TIAN Jin-yu ,LI Shao-ping ,CHENG Shuang ,LIU Qiu-yuan ,ZHOU Lei ,TAO Yu ,XING Zhi-peng,HU Ya-jie,GUO Bao-wei,WEI Hai-yan,ZHANG Hong-cheng

    1 Jiangsu Key Laboratory of Crop Cultivation and Physiology/Innovation Center of Rice Cultivation Technology in Yangtze Valley,Ministry of Agriculture and Rural Affairs/Co-Innovation Center for Modern Production Technology of Grain Crops,Yangzhou University,Yangzhou 225009,P.R.China

    2 Agricultural College,Xinyang Agriculture and Forestry University,Xinyang 464000,P.R.China

    Abstract Dry direct-seeded rice (DDR) sown using a multifunctional seeder that performs synchronous rotary tillage and sowing has received increased attention because it is highly efficient,relatively cheap,and environmentally friendly.However,this method of rice production may produce lower yields in a rice-wheat rotation system because of its poor seedling establishment.To address this problem,we performed field experiments to determine the rice yield at five seedling density levels (B1,B2,B3,B4,and B5=100,190,280,370,and 460 seedlings m-2,respectively) and clarify the physiological basis of yield formation.We selected a representative high-quality rice variety and a multifunctional seeder that used in a typical rice-wheat rotation area in 2016 and 2018.The proportion of main stem panicle increased with increasing seedling density.There was a parabolic relationship between yield and seedling density,and the maximum yield (9.34-9.47 t ha-1) was obtained under B3.The maximum yield was associated with a higher total spikelet number m-2 and greater biomass accumulation from heading to maturity.The higher total spikelet number m-2 under B3 was attributed to an increase in panicle number m-2 compared with B1 and B2.Although the panicle numbers also increased under B4 and B5,these increases were insufficient to compensate for the reduced spikelet numbers per panicle.Lower biomass,smaller leaf area,and lower N uptake per plant from the stem elongation stage to the heading stage were partially responsible for the smaller panicle size at higher seedling density levels such as B5.The higher biomass accumulation under B3 was ascribed to the increases in the photosynthetic rate of the top three leaves m-2 of land,crop growth rate,net assimilation rate,and leaf area index.Furthermore,the B3 rice population was marked by a higher grain-leaf ratio,as well as a lower export ratio and transport ratio of biomass per stem-sheath.A quadratic function predicted that 260-290 seedlings m-2 is the optimum seedling density for achieving maximum yield.Together,these results suggested that appropriately increasing the seedling density,and thereby increasing the proportion of panicles formed by the main stem,is an effective approach for obtaining a higher yield in DDR sown using a multifunctional seeder in a rice-wheat rotation system.

    Keywords: seedling density,dry direct-seeded rice sown by a multifunctional seeder,rice-wheat rotation system,yield,biomass,photosynthetic capacity

    1.Introduction

    Dry direct-seeded rice (DDR) is a highly efficient,inexpensive,and environmentally friendly approach for rice establishment that has the potential to alleviate certain rice production problems such as a lack of labor(Chakrabortyet al.2017;Shiet al.2021),limited water resources,and excess greenhouse gas emissions (Burneyet al.2010).DDR requires less labor,time and cost than transplanted rice because some processes such as seedling production,pulling and transplantation can be skipped (Farooqet al.2011;Mahajanet al.2013;Lainget al.2018).Compared with transplanted and wet directseeded rice,DDR consumes less water because it uses dry ploughing,dry harrowing and dry sowing (Liet al.2014;Liuet al.2015).Finally,less methane is emitted with DDR because the lower soil moisture suppresses the growth of soil methanogens and supports the growth of soil methanotrophs relative to transplanted and wet directseeded rice (Hanget al.2014).In the past,DDR was sown after ploughing and harrowing (Kumar and Ladha 2011).In recent years,with the development of multifunctional seeders that perform synchronous rotary tillage and sowing(Wanget al.2017;Zhanget al.2017),DDR sown by multifunctional seeders has developed rapidly due to its labor-and time-saving features,and its planting area has expanded gradually throughout Asia,including China and India (Farooqet al.2011;Kumar and Ladha 2011;Wanget al.2017;Devkotaet al.2020).

    The rice-wheat rotation system is one of the largest agricultural production systems in the world,and it occupies 24 million ha of the most productive land in South Asia and China (Ladhaet al.2003).Under the rice-wheat rotation system,DDR cannot be sown until the wheat has been harvested,and this limits DDR yields by compressing the growing season relative to that of transplanted rice(Xinget al.2017;Huang and Zou 2018).Moreover,the return of wheat-straw is widely used in this rotation system as an important agricultural measure to improve the climate,ambient air quality,and human health relative to the burning of wheat-straw in open fields (Grover and Chaudhry 2019).Wheat-straw return also ameliorates the soil structure,improves the soil organic matter content,and promotes sustainable soil development (Jianget al.2012;Xuet al.2018).Although wheat-straw return has many advantages,it is difficult to carry out high-quality mechanical tillage in large production areas for DDR sown by a multifunctional seeder that performs synchronous rotary tillage and sowing.This limitation is due to the large amounts of wheat-straw returned to the field,the low degree of chopped wheat-straw,and the uneven distribution of wheat-straw (Jianget al.2012).As a result,rice seed germination is constrained by less-than-ideal soil conditions.DDR seedlings also exhibit poor establishment because the returned wheat-straw causes microbial consumption of available soil nutrients (Zhaoet al.2017;Li Het al.2018;Nadeem and Farooq 2019),an accumulation of microbial allelochemicals such as organic acids (Qiet al.2012) and the restriction of rice seedling root development(Xuet al.2018;Wanget al.2019).Together,these production problems cause poor seedling establishment and yield loss in DDR sown by a multifunctional seeder under the rice-wheat rotation system,and rice grown in this manner has been termed “constrained direct-seeded rice”by Zhanget al.(2021).In this study,we call it constrained dry direct-seeded rice (CDDR).

    Higher sowing rates present a problem during largescale production of CDDR.Higher seedling densities can partially compensate for yield loss through higher panicle numbers,but the biomass per plant and spikelet number per panicle decrease due to the effects of competition among individual plants.In addition,higher seedling densities can also aggravate the risk of weak seedlings,seedling heterogeneity,lodging,diseases,and pests(Meulen and Chauhan 2017).Nonetheless,there are also problems associated with lower sowing rates (Qiuet al.2016).Lower seedling densities are beneficial to the growth of individual plants,the accumulation of biomass per plant,and the formation of larger panicles,but it is difficult to improve the yields at low seedling densities because of insufficient panicle numbers.Therefore,determining the optimum seedling density is the most basic and important consideration for achieving higher yields in rice cultivation.Research on transplanted rice has shown that yield generally increases with seedling densities within the range of 5 to 100 seedlings m-2,and the yield remains stable through the balancing of panicle number and spikelet number per panicle at densities greater than 100 seedlings m-2(Fukushimaet al.2011;Clergetet al.2016;Huet al.2020).Previous studies have reported that 100-200 seedlings m-2was a practical optimal plant population (semi-dwarf rice variety) for both aerial-and drill-sowing methods in south-eastern Australia(Dunnet al.2020),70-118 seedlings m-2was a suitable density (hybrid rice variety) for wet direct-seeded rice in South China (Wanget al.2014),240 seeds m-2was found to be an appropriate density (inbred rice variety)for DDR in Central China (Sunet al.2015),and 160-220 seedlings m-2was a suitable density (inbredjaponicarice variety) for direct-seeded rice in rice-wheat rotation systems (Huanget al.2012;Chenet al.2015;Wuet al.2019).Some studies have shown that higher densities of 340-370 seedlings m-2produce good yields and minimize the yield loss caused by weeds (Phuonget al.2005).These previous studies were mainly carried out in soil after intensive tillage,such as puddled soil and soil after multiple rotary tillage,which means that all aspects of the soil tillage conditions were better,and this would be conducive to the growth of rice.However,the less-thanideal soil conditions caused by wheat-straw return and minimum tillage has become a common phenomenon in the large areas of CDDR production.Therefore,the results for optimal seedling density obtained using different systems may not be applicable to CDDR under a rice-wheat rotation system because this kind of rice experiences yield loss associated with poor seedling establishment.The optimum seedling density of CDDR should be re-evaluated for updating the current agronomic management practices in the rice-wheat rotation system.

    Here,we performed an experiment in a typical ricewheat rotation area using a widely grown high-qualityjaponicarice variety and a representative multifunctional seeder,and measured relevant indexes of biomass and photosynthetic capacity from the levels of population to individual plants.The objectives of this study were to (1)determine the optimum seedling density for CDDR and(2) clarify the mechanism of the maximized yield at the optimum seedling density.The findings of this study provide theoretical and practical support for high-yield cultivation and regulatory approaches for CDDR in the future.

    2.Materials and methods

    2.1.Experimental site and weather conditions

    The field experiment was performed in Taizhou City,Jiangsu Province,China (32°61′N,120°12′E,3 m altitude)during the rice growing season (from June to October).The cropping system in this region is a rice-wheat rotation system.The field soil was a sandy loam with a viscous texture and 30.36 g kg-1organic matter,1.91 g kg-1total N,31.57 mg kg-1available P,and 153.8 mg kg-1available K.

    Meteorological data were collected at a weather station near the experimental site.The values for the daily mean temperature,sunshine hours,and precipitation during the two rice growing seasons were 25.58 and 25.54°C,679.4 and 857.7 h,and 1 083.9 and 485.5 mm in 2016 and 2018,respectively (Fig.1).

    Fig.1 Daily mean temperature,sunshine hours and precipitation during the rice growth seasons in 2016 and 2018.

    2.2.Rice variety and multifunctional seeder

    The high-qualityjaponicarice variety Nanjing 9108 was selected for this experiment.In the planting area of conventionaljaponicarice,Nanjing 9108 was the fourthranked variety in China and the second in Jiangsu Province (CRDC 2021).A multifunctional seeder with synchronous rotary tillage and sowing (row spacing 25 cm and sowing depth 2-3 cm) was used in this experiment.The multifunctional seeder was developed by the College of Mechanical Engineering,Yangzhou University.This seeder is representative of the seeders used in largescale production to perform the one-time operation of rice sowing and improve sowing efficiency.

    2.3.Experimental design and treatments

    The experiment used a completely randomized design with three replications.Five target seedling density levels were used in 2016 and 2018: 100 seedlings m-2(B1),190 seedlings m-2(B2),280 seedlings m-2(B3),370 seedlings m-2(B4),and 460 seedlings m-2(B5).The sowing date in both years was 20 June.The seedling density levels were achieved by regulating the sowing rate based on the germination rate and the seedling emergence rate measured in a preliminary experiment.The actual seedling density achieved in each treatment was determined during the three-leaf stage (about 2 wk after sowing),and three representative plot areas (5 m×6 m)were selected based on the actual seedling density for each treatment.

    2.4.Crop cultivation

    In both years,wheat was harvested with Kubota machinery (4LBZ-145G(PRO588I-G)),and 100% of the wheat-straw was returned to the field.Next,the rice for each treatment was seeded with the multifunctional seeder.After sowing,wet irrigation management was used during the seedling period to ensure the growth and development of the rice seedlings.Thereafter,moist conditions were maintained until the 5-leaf stage.The field was flooded after the 5-leaf stage,and the water level was maintained at 2-3 cm until the middle tillering stage.The water was then drained for 7-10 d to control unproductive tillers.After the stem elongation stage,a regime of alternating wetting and moderate soil drying irrigation management was used until 1 wk before the final harvest.In this alternating wetting and moderate soil drying irrigation management regime,the fields were not irrigated until the soil water potential reached-15 kPa (soil moisture content 0.170 g g-1) at 15-20 cm depth.The soil water potential was monitored at 15-20 cm soil depth with a tensiometer consisting of a sensor of 5 cm length (Institute of Soil Science,Chinese Academy of Sciences,Nanjing,Jiangsu,China).Four tensiometers were installed in each plot,and readings were recorded at 11:00 a.m.each day.When the soil water potential reached the threshold,plots were flooded with 3 cm of water.The irrigation water level was monitored with a flow meter (LXSG-50 flow meter,Shanghai Water Meter Manufacturing Factory,Shanghai,China) installed in the irrigation pipelines.

    A total of 270 kg N ha-1(as urea with an N content of 45.6%) was applied in three splits at a ratio of 3.5:3.5:3 at pre-sowing,the 4-leaf stage,and the stem elongation stage.Phosphorus (135 kg P ha-1) was applied at presowing using calcium superphosphate with a P2O5content of 12%.Potassium chloride (K2O content: 60%) was used as the potassium fertilizer,and it was applied at presowing (135 kg K ha-1) and again at the panicle initiation stage (135 kg K ha-1).

    Weed,insect,and disease control followed local recommendations throughout the growing season to minimize yield losses over the two years.

    2.5.Sampling and measurements

    To accurately sample and understand the growth process of the rice,we recorded the dates of sowing,the stem elongation stage (panicle initiation),the heading stage,and the maturity stage.In 2018,tiller numbers were measured in each plot from three adjacent and consecutive rows (1 m length) at 5-day intervals from the 3-leaf stage until the number diminished.

    Tiller number (Y) was fit with a logistic equation:

    whereYmis the maximum tiller number,xis days after sowing,andAandBare rate-controlling parameters(Catonet al.2003).The fitting was performed using Origin 9.

    Leaf area and biomass were determined at the stem elongation,heading,and maturity stages.Samples were collected from three adjacent rows (50 cm length) in each plot,and all samples were separated into leaves,stem-sheaths,and panicles (at the heading and maturity stages).Leaf areas were measured with a leaf area meter (LI-3100,LI-COR,USA).Each component of the rice plants was oven-dried separately at 105°C for 30 min and then in bags at 80°C to a constant weight.N uptake per plant was calculated by multiplying the N concentration per plant (%) by the biomass per plant,and N concentration was determined by the semi-micro-Kjeldahl procedure.

    Five representative plants were selected and marked in each plot forin situmeasurement of the photosynthetic rate.Photosynthetic rates of the top first,second,and third leaves were measured at the heading stage and 20 and 40 days after heading.The maximum CO2assimilation rate m-2(i.e.,the photosynthetic rate;μmol m-2s-1) was measured between 9:30 and 11:30 a.m.using an LI-6400 portable photosynthetic system (LICOR,USA).At the same time,10 representative plants were selected for taking measurements of the leaf areas of the top first leaf to the third leaf (LI-3100,LI-COR,USA).

    At the maturity stage,three adjacent rows (1 m length) were sampled randomly from each plot for the measurements of panicle traits and yield components,including spikelet number per panicle (SP),filled-grain percentage,and 1 000-grain weight.Three adjacent rows (5 m length) were sampled randomly from each plot for determination of the panicle number m-2(PN).Total spikelet number m-2(TSP) was calculated as PN multiplied by SP.Yield was determined from a harvest area of 8 m2in each plot and adjusted to the standard moisture content of 0.14 g H2O g-1.

    2.6.Statistical analysis and formula calculations

    The data were analyzed using IBM SPSS Statistics 22,and treatment means were compared by the least significant difference (LSD) test.Graphical representations of the data were produced using Origin 9,Excel 2019,and the R statistical programming language.

    The following equations were used for the calculations:

    where CGR is the crop growth rate,NAR is the net assimilation rate,LAR is the leaf area attenuation rate from heading to maturity,ERBS is the export ratio of biomass per stem-sheath from heading to maturity,TRBS is the transport ratio of biomass per stem-sheath from heading to maturity,and PPR is the photosynthetic rate of the top three leaves m-2of land.W1and W2are the first and second measurements of biomass (kg ha-1),t1and t2are the first and second measurement times (d),LAI1and LAI2are the first and second measurements of leaf area index (m2m-2),Ln indicates the natural logarithm,WHandWMare the stem-sheath weights (after removal of spikes and leaves) at heading and maturity (g),WPis the single panicle weight at maturity (g),Siis the leaf area of theith leaf (from the top) per plant (m2),PRiis the photosynthetic rate of theith leaf per plant (μmol m-2s-1),andkis the number ofith leaves per m2of land (m-2) after heading.

    3.Results

    3.1.Yield and seedling density

    Data concerning the yields and their components in 2016 and 2018 are shown in Table 1.The B3 density level (280 seedlings m-2) produced the highest yield of 9.34-9.47 t ha-1,which was 6.9-7.5% higher than B1 and 8.1-9.4%higher than B5.The relationship between seedling densityand yield was analyzed with a scatter plot (Fig.2),and in all cases,a parabolic relationship fit the data well.The relationships between grain yield (Y) (kg ha-1) and seedling density (X) (m-2) wereY2016=-0.0292X2+15.5X+7 175.1(R2=0.919) andY2018=-0.0291X2+16.4X+7 059.4 (R2=0.956)in 2016 and 2018,respectively.Based on these quadratic equations,the optimum seedling densities to achieve higher yield were 265 m-2in 2016 and 282 m-2in 2018.

    Table 1 Yield and yield components under five seedling density levels in 2016 and 2018

    Fig.2 The relationships between seedling density and yield in 2016 and 2018.Error bars denote standard error of replicates(n=3).The actual seedling densities are shown in Table 1.

    The yield components were analyzed,and consistent differences were observed in the two years (Table 1).As seedling density increased,panicle number (PN) and the proportion of panicles formed by the main stem also increased.The latter values were 37.4,56.0,70.4,84.0,and 96.4% in B1,B2,B3,B4,and B5,respectively.In contrast,spikelet number per panicle (SP) decreased significantly as seedling density increased.For example,B5 had 21.7% higher PN than B1,but it also had 22.7%lower SP than B1;as a consequence,total spikelet number (TSP) was 1.2% higher in B5 than in B1.Meanwhile,B3 had 15.7% higher PN than B1 but only 10.4% lower SP,and TSP was 6.0% higher in B3 than in B1.Although B3 had 7.2% lower PN than B5,it had 13.9% higher SP,and TSP was therefore 7.0% higher in B3 than in B5.Seedling density had a positive effect on 1 000-grain weight,but this effect was not significant.Seedling density did not have a significant effect on filledgrain percentage.

    The correlation between yield and seedling density was not significant (Fig.3),nor were there significant correlations between yield and the yield components including PN,SP,filled-grain percentage,and 1 000-grain weight.However,there was a significant positive correlation between yield and TSP.Seedling density was significantly positively correlated with PN and 1 000-grain weight,and significantly negatively correlated with SP.There were significant negative correlations of 1 000-grain weight with SP,grain density,and panicle length.

    Fig.3 Correlation analysis among seedling density,yield components and panicle traits (R0.05=0.878 and R0.01=0.959).SD,seedling density;PN,panicle number m-2;SP,spikelet number per panicle;TSP,the total spikelet number m-2;FG,filled-grain percentage;TGW,1 000-grain weight;GD,grain density (spikelets per panicle/PL);PL,panicle length;GWP,grain weight per panicle.

    3.2.Tillering dynamics

    The peak value of tillers m-2increased as seedling density increased,and the value in B5 was 171.3-172.8% and 43.3-51.4% higher than in B1 and B3,respectively.Moreover,the time to achieve maximum tillers m-2was also reduced,and it occurred about 5-10 days earlier in B5 than in B1 (Fig.4,2018).However,after the peak tiller value,it is clear from the slope of the tiller curve that the tiller number declined more rapidly at higher seedling densities (Fig.4,2016).

    Fig.4 Tillering dynamics under five seedling density levels during the growth duration in 2016 and the early growth period in 2018.B1,B2,B3,B4,and B5 represent target seedling density levels of 100,190,280,370,and 460 seedlings m-2,respectively (the actual seedling densities are shown in Table 1).15 DAS,15 days after sowing;MT,middle tillering stage;SE,stem elongation stage;HD,heading stage;MA,maturity stage.Error bars denote standard error of replicates (n=3).

    3.3.Leaf area and N uptake per plant

    Leaf area and N uptake per plant decreased with increasing seedling density in all growth periods (Fig.5).Leaf area per plant in B1 was 15.4-17.7% and 15.8-24.1%higher than in B3 and B5 at the stem elongation stage,11.0-11.6% and 13.0-23.0% higher than in B3 and B5 at heading,and 7.9-11.5% and 17.8-23.2% higher than in B3 and B5 at maturity,respectively.Likewise,N uptake per plant in B1 was 10.8-12.7% and 19.2-21.2% higher than in B3 and B5 at the stem elongation stage,and 17.4-20.7%and 20.7-25.1% higher than in B3 and B5 at heading,respectively.

    Fig.5 Leaf area per plant (A) at the stem elongation (SE),heading (HD),and maturity (MA) stages and N uptake per plant (B) at the SE and HD under the five seedling density levels in 2016 and 2018.B1,B2,B3,B4,and B5 represent target seedling density levels of 100,190,280,370,and 460 seedlings m-2,respectively (the actual seedling densities are shown in Table 1).Error bars show standard error of replicates (n=3).Values followed by different lowercase letters are significantly different at the 0.05 probability level among the different seedling density treatments.

    3.4.LAI and LAR

    As shown in Fig.6,there were differences in LAI among the five seedling densities at the stem elongation,heading,and maturity stages.The LAI in B5 was 17.4-17.5%and 7.2-7.8% higher than in B1 at the stem elongation and heading stages,respectively.However,there were negligible differences in LAI between the higher seedling densities such as B3 and B5 at the heading stage.The LAI in B3 at maturity was 6.6 and 5.2% higher than in B1 and B5,respectively.The LAR increased with increasing seedling density from heading to maturity,and it was 11.4% higher in B5 than in B1.

    Fig.6 Leaf area index (LAI) (A) at the stem elongation (SE),heading (HD),and maturity stages (MA);and leaf area attenuation rate (B) from HD to MA under five seedling density levels in 2016 and 2018.B1,B2,B3,B4,and B5 represent target seedling density levels of 100,190,280,370,and 460 seedlings m-2,respectively (the actual seedling densities shown in Table 1).Error bars show standard error of replicates (n=3).Values followed by different lowercase letters are significantly different at the 0.05 probability level among the different seedling density treatments.

    3.5.Biomass,CGR and NAR

    As seedling density increased,biomass accumulation increased at the stem elongation and heading stages.Specifically,the biomass in B5 was 9.2-15.4% and 6.6-6.7% higher than in B1 at the stem elongation and heading stages,respectively.However,there was a parabolic relationship between seedling density and biomass accumulation from heading to maturity,and biomass in B3 was 8.0-19.5% and 13.3-20.4% higher than in B1 and B5,respectively.Finally,biomass accumulation in B3 at maturity was 5.7-11.3% and 3.2-7.4% higher than in B1 and B5,respectively.Contrary to the trend in biomass accumulation,biomass per plant in B1 was 23.5-26.0%,13.6-23.9% and 16.8-21.1% higher than in B5 at the stem elongation,heading,and maturity stages,respectively (Fig.7-B).

    Fig.7 Biomass accumulation (A) at sowing stage (SO)-stem elongation (SE),SE-heading (HD) and HD-maturity (MA) stages and biomass per plant (B) at SE,HD and MA under the five seedling density levels in 2016 and 2018.B1,B2,B3,B4,and B5 represent target seedling density levels of 100,190,280,370,and 460 seedlings m-2,respectively (the actual seedling densities are shown in Table 1).Error bars show standard error of replicates (n=3).Values followed by different lowercase letters are significantly different at the 0.05 probability level among the different seedling density treatments.

    The crop growth rate and net assimilation rate from heading to maturity initially increased but later decreased with increasing seedling density (Fig.8).In the two years,the crop growth rate in B3 from heading to maturity was 13.7 and 16.9% higher than in B1 and B5,respectively.Similarly,the net assimilation rate in B3 from heading to maturity was 7.9 and 15.7% higher than in B1 and B5,respectively.

    Fig.8 Crop growth rate (A) and net assimilation rate (B) under the five seedling density levels from the heading to the maturity stages in 2016 and 2018.B1,B2,B3,B4,and B5 represent target seedling density levels of 100,190,280,370,and 460 seedlings m-2,respectively (the actual seedling densities are shown in Table 1).Error bars show standard error of replicates (n=3).Values followed by different lowercase letters are significantly different at the 0.05 probability level among the different seedling density treatments.

    3.6.Photosynthetic rate

    At heading,20 and 40 days after heading,the photosynthetic rates of the top three leaves decreased consistently with increasing seedling density,but the rates did not differ significantly among seedling density levels of B1 to B4 (Fig.9).The photosynthetic rates of the top three leaves were ranked the top first leaf>top second leaf>top third leaf.From heading to 40 days after heading,the photosynthetic rates of the top first,second,and third leaves in B1 were approximately 33.1,30.7 and 45.3% higher than in B5,respectively.

    Fig.9 Photosynthesis rates of the top three leaves at DAH-0 d,DAH-20 d and DAH-40 d under the five seedling density levels in 2018.DAH-0 d,DAH-20 d and DAH-40 d represent 0,20 and 40 days after the heading stage (DAH),respectively.B1,B2,B3,B4,and B5 represent target seedling density levels of 100,190,280,370,and 460 seedlings m-2,respectively (the actual seedling densities are shown in Table 1).Error bars show standard error of replicates (n=3).Values followed by different lowercase letters are significantly different at the 0.05 probability level among the different seedling density treatments.

    The photosynthetic rates of the top three leaves m-2of land (PPR) after heading increased and then decreased with increasing seedling density (Fig.10-A),and PPR was significantly lower at higher seedling density levels such as B5.PPR values in B3 were 3.0,9.1 and 1.1% higher than in B1 at 0,20 and 40 days after heading,respectively.Likewise,PPR levels in B3 were 34.2,29.9 and 27.2% higher than in B5 at 0,20 and 40 days after heading.The mean PPR in B3 across 0,20 and 40 days after heading (PPR at HD-MA) was 5.9 and 30.5% higher in B1 and B5.The scatter plot(Fig.10-B) showed that there was a significant positive correlation between biomass accumulation at HD-MA and PPR at HD-MA.

    Fig.10 Photosynthetic rates (PPR) of the top three leaves m-2 of land (PPR) at DAH-0 d,DAH-20 d,DAH-40 d,and HD-MA (A)and the relationship between biomass accumulation and PPR at HD-MA (B) under the five seedling density levels in 2018.DAH-0 d,DAH-20 d and DAH-40 d represent 0,20 and 40 days after the heading stage (DAH),respectively.HD-MA,from heading to maturity stage.PPR at HD-MA represents the average values of PPR at DAH-0 d,DAH-20 d and DAH-40 d.B1,B2,B3,B4,and B5 represent target seedling density levels of 100,190,280,370,and 460 seedlings m-2,respectively (the actual seedling densities are shown in Table 1).Error bars show standard error of replicates (n=3).Values followed by different lowercase letters are significantly different at the 0.05 probability level among the different seedling density treatments.

    3.7.Source and sink

    The grain-leaf ratio decreased as seedling density increased,but there were no significant differences among B1,B2 and B3.The grain-leaf ratio decreased significantly at higher seedling density levels such as B4 and B5.The grain-leaf ratio in B1 was 7.9-9.4% higher than in B5 (Fig.11).

    Fig.11 Grain-leaf ratio at the heading stage under the five seedling density levels in 2016 and 2018.B1,B2,B3,B4,and B5 represent target seedling density levels of 100,190,280,370,and 460 seedlings m-2,respectively (the actual seedling densities are shown in Table 1).Error bars show standard error of replicates (n=3).Values followed by different lowercase letters are significantly different at the 0.05 probability level among the different seedling density treatments.

    As shown in Fig.12,the export ratio of biomass per stem-sheath (ERBS) and the transport ratio of biomass per stem-sheath (TRBS) differed among seedling densities.There were parabolic relationships between seedling density and both ERBS and TRBS from heading to maturity: ERBS and TRBS first decreased and then increased with increasing seedling density.In both years,ERBS in B3 was 12.4-33.0% and 22.4-25.3% lower than in B1 and B5.Similarly,TRBS in B3 was 8.9-28.0% and 30.7-31.1% lower than in B1 and B5.

    Fig.12 Transport ratio of biomass per stem-sheath (TRBS) (A) and export ratio of biomass per stem-sheath (ERBS) (B) from heading to the maturity stage under the five seedling density levels in 2016 and 2018.B1,B2,B3,B4,and B5 represent target seedling density levels of 100,190,280,370,and 460 seedlings m-2,respectively (the actual seedling densities are shown in Table 1).Error bars show standard error of replicates (n=3).Values followed by different lowercase letters are significantly different at the 0.05 probability level among the different seedling density treatments.

    4.Discussion

    4.1.Yield responses to seedling density

    Seedling density is a critical factor for establishing an appropriate crop population,thereby ensuring high quality and yield (Huanget al.2013;Liet al.2016).Here,we found that yield first increased and then decreased with increasing seedling density,and the maximum yield was obtained at a seedling density level of 280 seedlings m-2(B3).Although some studies have shown that seedling density (sowing rate) has no effect on yield (Ottis and Talbert 2005),sink size,or gross hulled rice yield(Fukushimaet al.2011),they also reported a peak value of yield with increased seedling density.The response curve between yield and seedling density was fitted well by a quadratic function,and the quadratic equation obtained from the two-year experiment predicted that 260-290 seedlings m-2is the optimum seedling density for maximum yield.Previous studies on seedling density of inbredjaponicarice showed that 80-120 seedlings m-2for transplanted rice (Huet al.2020) and 160-220 seedlings m-2for wet direct-seeded rice (Chenet al.2015;Wuet al.2019) were suitable densities in the ricewheat rotation system.However,in this experiment,these seedling density levels (B1 and B2) did not produce the maximum yield.One possible reason is that the poor seedling establishment caused by less-than-ideal soil conditions leads to insufficient tiller numbers and biomass accumulation.Ottis and Talbert (2005) recommended that growers plant twice as many seeds as needed for optimum rice density when planting in a clay soil or under imperfect seedbed conditions.Previously recommended seedling densities would have caused yield loss for CDDR under the conditions of this experiment,and previous seedling density studies are not directly applicable to CDDR in a rice-wheat rotation system.The results of this study preliminary suggest that higher yields for CDDR in the rice-wheat rotation system can be obtained by properly increasing the seedling density.To verify the feasibility of this cultivation model for CDDR,on-farm demonstration experiments were performed in rice-wheat rotation fields of Jiangyan and Yancheng cities,Jiangsu Province in 2020 with another widely used rice variety,Nanjing 5718.The yields reached 10.4 t ha-1in Jiangyan and 10.8 t ha-1in Yancheng.Therefore,appropriately increasing the seedling density is one of the approaches for achieving higher yields of CDDR in the rice-wheat rotation system.

    This study showed that a type of homeostasis was maintained between PN and SP (Table 1).This was consistent with previous studies that reported a compensation effect between PN and SP: if one increased,the other declined (Yinget al.1998;Huanget al.2011).This phenomenon may be linked to plant density.On the one hand,plant density directly determines panicle density (PN) based solely on plant numbers.On the other hand,plant density can determine panicle size (SP) by affecting panicle development and spikelet formation.Differences in planting density change the environment around individual plants,including light quantity (Liet al.2019),canopy temperature,humidity,and carbon dioxide concentration,and these changes can affect gene expression (Lewiset al.2008;Endo-Higashi and Izawa 2011),hormone synthesis (Li Yet al.2018;Wanget al.2020) and growth (Clergetet al.2016)with respect to panicle and spikelet formation.There is also interplant competition for resources such as light and soil nitrogen,and increased competition at higher plant densities will lead to poorer development of individual plants.Thus,previous results have consistently shown positive correlations between SP and biomass (Shiratsuchiet al.2007),nitrogen status (Kamijiet al.2011),panicle neck diameter (Liuet al.2008),stem diameter,and vascular bundle (Xuet al.1998) per plant during panicle development (from stem elongation to heading).Sheehyet al.(2001) reported that source strength was particularly important for the differentiation and development of the sink organ,and Kobayashi and Horie (1994) believed that an increase in plant N significantly increased the number of differentiated spikelets at the panicle development stage by promoting the differentiation of secondary branches on primary branches.Here,we concluded that the smaller panicle size at higher seedling densities was caused by lower biomass (Fig.7-B),smaller leaf area(Fig.5-A),and lower nitrogen uptake (Fig.5-B)per plant from stem elongation to heading.

    The coordination of panicle density and panicle size is necessary to optimize the homeostasis between PN and SP,and thereby achieve higher yields.The degree of coordination between panicle density and panicle size is reflected in TSP: the larger the TSP,the better the coordination and the higher the yield.We concluded that the smaller TSP at lower seedling density levels arose mainly from insufficient panicle numbers caused by insufficient tillers in CDDR in the rice-wheat rotation system (Fig.4).Although increasing the seedling density reduced the tiller number per plant,it increased the panicle density,thereby compensating for the yield loss caused by insufficient panicle numbers.The proportions of panicles formed by the main stem increased with increasing seedling density,at levels of 37.4,56.0,70.4,84.0,and 96.4% in B1,B2,B3,B4,and B5,respectively.Therefore,we preliminarily concluded that an effective means for increasing yield in CDDR is to appropriately increase the seedling density,thereby increasing the proportion of panicles formed by the main stem.In this way,a coordinated rice population with higher TSP and yield was produced through sufficient main stem panicle numbers,simultaneously ensuring a sufficient filled-grain percentage and 1 000-grain weight.

    Grain weight is one of the yield components.The results of previous studies have varied regarding the effect of seedling density on grain weight.Yuet al.(1995)believed that reducing seedling density appropriately and establishing an appropriate population structure could effectively improve the plant physiological activity after flowering,increase grain storage capacity and enrich capacity,and increase grain weight.However,some studies have shown that the 1 000-grain weight increases with an increase in seedling density (Xuet al.2008;Huet al.2015).The results of this study showed that increasing seedling density was conducive to increasing 1 000-grain weight (Table 1).The grain weight of rice is closely related to grain filling.The grain filling process depends on two main carbon resources: photosynthetic assimilates and carbohydrates stored during pre-flowering and transported to the grain from the stem-sheath(Ambavaramet al.2014;Xuet al.2016).This study showed that although the ERBS and TRBS decreased(Fig.12),the increase of biomass accumulation after heading (Fig.7) could be conducive to the increase of grain weight at the seedling density levels from B1 to B3 (Table 1).Biomass accumulation after heading decreased at the seedling density levels from B3 to B5(Fig.7),however,the increases in ERBS and TRBS(Fig.12) also promoted the increase in grain weight(Table 1).Previous studies have shown that the grain weight of the main stem panicle is greater than that of the tiller panicle (Quet al.2009).Therefore,the increase in the proportion of main stem panicles could also be one of the reasons for the increase in the 1 000-grain weight with the increase in seedling density (Table 1).Furthermore,correlation analysis showed that the 1 000-grain weight was negatively correlated with grain density and spikelet number per panicle (Fig.3).Therefore,lower grain density and spikelet number per panicle could provide more growth space and material supply for single grain filling,which was also beneficial to the increase in grain weight.

    4.2.Photosynthetic biomass productivity

    Yield is the product of harvest index and biomass accumulation at the maturity stage.Given the current high yield levels,it is difficult to improve the harvest index of rice.Therefore,increasing the harvest index may no longer be the main approach for increasing rice yield,and improving biomass accumulation at the maturity stage may be the key to further improvements in rice yield potential based on a high and stable harvest index(Penget al.1999;Liet al.2009).In particular,increasing biomass accumulation from heading to maturity is critical for high biomass accumulation at maturity (Linget al.1993).However,a higher seedling density does not mean higher biomass accumulation.This study showed that biomass accumulation at maturity was the highest at density B3.Lower biomass accumulation at the seedling density levels recommended (B1 and B2) in previous studies (for transplanting or wet direct-seeded rice)was due to lower plant density (panicle density),which is caused by fewer tillers (Fig.4).The poor seedling establishment and the insufficient growth of the new tiller and main stem were partly responsible for the lack of tillers in B1 and B2.The main reason for the poor seedling establishment compared with wet direct-seeded rice may be the microbial consumption of soil available nutrients and the less-than-ideal soil conditions caused by wheat-straw return and minimum tillage.The main reason for the insufficient growth of the new tiller and main stem compared with transplanting rice may be that the seedling growth time in the vegetative growth period (from sowing to stem elongation) was seriously compressed (i.e.,shorter vegetative growth).For example,the reduced number of days from sowing to the stem elongation stage accounted for more than 60% of the shortened duration of the whole growth period (Xinget al.2017).Therefore,adequate main stems are needed to compensate for the insufficient new tillers for CDDR in the rice-wheat rotation system.Biomass accumulation at maturity decreased with increasing seedling density from B3 to B5,mainly owing to the decrease in biomass accumulation from heading to maturity.Although higher seedling densities improved biomass accumulation before heading,they were not conducive to biomass accumulation after heading because the individual rice plants were thin and weak.Hence,a suitable seedling density is necessary to improve biomass accumulation from heading to maturity.Further analysis showed that the crop growth rate and the net assimilation rate were the highest in B3,perhaps because of its higher LAI and lower LAR from heading to maturity (Fig.6).Therefore,the results of this study suggest that appropriately increasing the seedling density,and thereby increasing the proportion of panicles formed by the main stem,is beneficial for increasing the biomass accumulation of CDDR,especially the biomass accumulation after heading,by increasing the number of sufficient main stem panicles.

    Higher biomass accumulation could be attributed to higher photosynthesis in B3,because the leaf photosynthetic rate plays a crucial role in determining biomass accumulation and yield.Previous research has demonstrated that the leaf photosynthetic rate is based on leaf N content and stomatal conductance (Kanemuraet al.2007;Ohsumiet al.2007).Rice populations with lower plant densities may have higher single-leaf photosynthetic rates owing to higher leaf N content and uptake (Fig.5).However,lower plant densities did not always equate to higher leaf photosynthetic rate m-2of land,because this parameter encompasses the single-leaf photosynthetic rate,single-leaf area,and number of leaves m-2of land(eq.(8)).The top three leaves of rice control about 75%of the yield,and this point was further confirmed through rice simulation models (Hiroeet al.2008;Hiroe and Takeshi 2009).Adachiet al.(2017) also reported that the top three leaves are the main photosynthetic organs in the later growth period.We therefore analyzed the leaf photosynthetic rate m-2of land based on the cumulative photosynthetic rate of the top three leaves m-2of land(PPR) (eq.(8)).There was a positive correlation between PPR and biomass accumulation from heading to maturity(Fig.10-B).The lower PPR at low seedling density levels,such as B1 and B2,was caused by a lower number of top three leaves m-2of land (plant density),although the low seedling densities were characterized by larger single-leaf photosynthetic rates and leaf areas per plant.The lower PPR at high seedling density levels,such as B4 and B5,was caused by lower photosynthetic rates of the top three leaves and smaller leaf areas of the top three leaves per plant,indicating that the increased plant densities could not compensate for the decreases in leaf area and single-leaf photosynthetic rate.The rice population of B3 exhibited a balance between plant density on one hand and single-leaf photosynthetic rate and leaf area on the other,ultimately improving PPR and achieving higher biomass accumulation and yield for CDDR.Therefore,we preliminarily concluded that appropriately increasing the seedling density,and thereby increasing the proportion of panicles formed by the main stem,is beneficial for improving the photosynthetic capacity of the population,which is beneficial for increasing the biomass accumulation after heading in CDDR.

    In this study,the leaf photosynthetic rate m-2of land was determined by measurement and calculation.Although this approach differs from previous methods(Garrityet al.1984;Zhaoet al.2001),it can describe the relationships of both yield and biomass accumulation with leaf photosynthetic rate m-2of land,and it therefore has the value for the study of population photosynthetic productivity.

    The formation of crop yield is a process of sourceflow-sink interaction and is related to the production,transport,and accumulation of photosynthate.Previous studies have shown that the sink organ determines the leaf photosynthetic rate,as reductions in the carbon demand of sink tissues eventually limit the photosynthetic rate (Paul and Pellny 2003;McCormicket al.2006;Ainsworth and Bush 2011).However,focusing only on high sink capacity without improving the source supply capacity can lead to insufficient grain filling and declines in filled-grain percentage and grain weight,as has been shown in hybrid rice,and comparable results have been shown in previous studies (Yinget al.1998;Zhanget al.2009).For example,Huanget al.(2019) showed that the higher yield of machine-transplanted doubleseason rice planted after oilseed rape was attributable to improvements in both sink size (spikelet number m-2) and source capacity (total biomass).The grain-leaf ratio has been used as a comprehensive index for measuring the relationship between source and sink (Linget al.1993).Furthermore,the production of photosynthetic substances occurs during photosynthesis in the chloroplasts,and photosynthate can be exported only when the production of carbon compounds exceeds the local demand(Ludewig and Flügge 2013).Similarly,the sink extracts carbon compounds from the stem-sheath when the sink demand cannot be satisfied by photosynthesis (source).The transport of greater amounts of storage material from the stem to the grain is characteristic of low-yield populations (Yanget al.2008).Wuet al.(2010) also reported that the export ratio and the corresponding transport ratio of reserve substances per stem-sheath decrease significantly with increasing rice yield.Hence,the export ratio of biomass per stem-sheath (ERBS)and the transport ratio of biomass per stem-sheath(TRBS) can also reflect the coordination between source and sink.This study showed that the rice population of 260-290 seedlings m-2had lower values for ERBS and TRBS (Fig.12) and higher grain-leaf ratio (Fig.11),source supply capacity (PPR) (Fig.10),and sink capacity(TSP) (Table 1) compared with the other seedling density levels tested.Therefore,the rice population formed at the optimum seedling density showed a coordinated enhancement of sink size and source capacity.

    5.Conclusion

    Dry direct-seeded rice sown by a multifunctional seeder that performs synchronous rotary tillage and sowing in a rice-wheat rotation system tends to experience poor seedling establishment and yield loss because of the less-than-ideal soil conditions caused by wheat-straw return and minimum tillage.The seedling density,a fundamental consideration for high-yield rice cultivation,can regulate panicle density and panicle size.Based on the results presented here,we can preliminarily conclude that appropriately increasing the seedling density,and thereby increasing the proportion of panicles formed by the main stem,is one way to obtain a higher yield for constrained direct-seeded rice in a rice-wheat rotation system.Because,in this system,a coordinated rice population with higher total spikelet number m-2,biomass accumulation,and photosynthetic capacity was produced through sufficient main stem panicle numbers.

    Acknowledgements

    We are grateful for grants from the Jiangsu Agriculture Science and Technology Innovation Fund,China(CX(20)1012),the Jiangsu Demonstration Project of Modern Agricultural Machinery Equipment and Technology,China (NJ2020-58),the Jiangsu Technical System of Rice Industry,China (JATS[2020]432),the National Key Research and Development Program of China (2016YFD0300503),the earmarked fund for China Agriculture Research System (CARS-01-27),and the Yangzhou University Scientific Research and Innovation Program,China (XKYCX20_022).

    Declaration of competing interest

    The authors declare that they have no conflict of interest.

    国产精品福利在线免费观看| 熟女人妻精品中文字幕| 国产伦精品一区二区三区视频9| 亚洲av免费在线观看| 男女视频在线观看网站免费| 欧洲精品卡2卡3卡4卡5卡区| 国产精品亚洲美女久久久| 国产高清视频在线播放一区| 欧美一区二区国产精品久久精品| 欧美色视频一区免费| 又爽又黄无遮挡网站| 亚洲国产精品久久男人天堂| 晚上一个人看的免费电影| 亚洲天堂国产精品一区在线| 欧美最黄视频在线播放免费| 午夜日韩欧美国产| 亚洲人成网站高清观看| 国产探花在线观看一区二区| av专区在线播放| 日日摸夜夜添夜夜添小说| 天堂av国产一区二区熟女人妻| 国产精品不卡视频一区二区| 久久久久免费精品人妻一区二区| 18+在线观看网站| 国产午夜精品论理片| 国内少妇人妻偷人精品xxx网站| 老熟妇仑乱视频hdxx| 一进一出抽搐gif免费好疼| 少妇人妻一区二区三区视频| 久久久久久大精品| 男女视频在线观看网站免费| 男人的好看免费观看在线视频| 久久精品夜色国产| av黄色大香蕉| av在线亚洲专区| av福利片在线观看| 国产av在哪里看| 美女黄网站色视频| 亚洲精品粉嫩美女一区| 99九九线精品视频在线观看视频| 岛国在线免费视频观看| 老司机影院成人| 99久国产av精品| 欧美成人免费av一区二区三区| 午夜免费男女啪啪视频观看 | 中国国产av一级| 日本一二三区视频观看| 国产精品一二三区在线看| 亚洲国产精品国产精品| 亚洲性久久影院| ponron亚洲| 久久中文看片网| 国产成人a∨麻豆精品| 性欧美人与动物交配| 十八禁国产超污无遮挡网站| 日日摸夜夜添夜夜添av毛片| 国产免费一级a男人的天堂| 日本黄大片高清| 波多野结衣高清无吗| av免费在线看不卡| 精品午夜福利在线看| 偷拍熟女少妇极品色| 久久久国产成人免费| 真实男女啪啪啪动态图| 国产伦在线观看视频一区| av福利片在线观看| 在线观看一区二区三区| 嫩草影院精品99| 国模一区二区三区四区视频| 精品午夜福利视频在线观看一区| 中文字幕人妻熟人妻熟丝袜美| 国产乱人偷精品视频| 亚洲丝袜综合中文字幕| 精品不卡国产一区二区三区| 亚洲国产精品sss在线观看| 九九久久精品国产亚洲av麻豆| 一进一出好大好爽视频| 深爱激情五月婷婷| 亚洲成人久久爱视频| 亚洲av成人精品一区久久| 少妇的逼水好多| 亚洲国产日韩欧美精品在线观看| 欧美绝顶高潮抽搐喷水| 你懂的网址亚洲精品在线观看 | 国产精品久久久久久久久免| 天堂影院成人在线观看| 国产在线男女| 亚洲色图av天堂| 亚洲精品亚洲一区二区| 男人舔女人下体高潮全视频| 久久久久久大精品| 极品教师在线视频| 中文亚洲av片在线观看爽| 高清日韩中文字幕在线| 狂野欧美白嫩少妇大欣赏| 波多野结衣巨乳人妻| 男人舔奶头视频| 亚洲性夜色夜夜综合| 啦啦啦啦在线视频资源| h日本视频在线播放| 久久久成人免费电影| 国产成人影院久久av| 午夜精品一区二区三区免费看| 国产免费一级a男人的天堂| 男女边吃奶边做爰视频| 久久精品夜色国产| 国语自产精品视频在线第100页| 丰满的人妻完整版| 国产美女午夜福利| 婷婷亚洲欧美| 亚洲精品粉嫩美女一区| 人妻久久中文字幕网| 老熟妇乱子伦视频在线观看| 亚洲熟妇熟女久久| 欧美成人精品欧美一级黄| 欧美不卡视频在线免费观看| 精品一区二区免费观看| 国产中年淑女户外野战色| 在线播放无遮挡| 精品人妻视频免费看| 99久久久亚洲精品蜜臀av| 97超视频在线观看视频| 国产精品一二三区在线看| 看免费成人av毛片| 在线免费观看的www视频| 麻豆国产av国片精品| 赤兔流量卡办理| 2021天堂中文幕一二区在线观| 天美传媒精品一区二区| 免费黄网站久久成人精品| 国产亚洲精品久久久久久毛片| 亚洲国产欧洲综合997久久,| 免费在线观看成人毛片| 国产高清不卡午夜福利| 久久久久久久久久黄片| aaaaa片日本免费| 亚洲欧美日韩东京热| 色综合亚洲欧美另类图片| 1024手机看黄色片| 欧美绝顶高潮抽搐喷水| 免费高清视频大片| 女的被弄到高潮叫床怎么办| 两个人的视频大全免费| 日本a在线网址| 亚洲不卡免费看| 日本黄色视频三级网站网址| 俄罗斯特黄特色一大片| 乱码一卡2卡4卡精品| 精品人妻偷拍中文字幕| 男女之事视频高清在线观看| 黄色欧美视频在线观看| 国产不卡一卡二| 美女cb高潮喷水在线观看| 麻豆一二三区av精品| 国产午夜精品久久久久久一区二区三区 | 亚洲国产色片| 黄色配什么色好看| 国产国拍精品亚洲av在线观看| 国产精品一二三区在线看| 国产白丝娇喘喷水9色精品| 91麻豆精品激情在线观看国产| 麻豆成人午夜福利视频| 人妻制服诱惑在线中文字幕| 高清日韩中文字幕在线| 干丝袜人妻中文字幕| 黄色配什么色好看| 国产高清视频在线观看网站| 国产精品久久久久久久久免| 亚洲一区二区三区色噜噜| 乱人视频在线观看| 国产 一区 欧美 日韩| 日韩av不卡免费在线播放| 一区二区三区四区激情视频 | 99视频精品全部免费 在线| 国产一区二区亚洲精品在线观看| 九九爱精品视频在线观看| 身体一侧抽搐| 日韩av在线大香蕉| 亚洲人成网站在线观看播放| av免费在线看不卡| 如何舔出高潮| 国内少妇人妻偷人精品xxx网站| 精品免费久久久久久久清纯| 午夜久久久久精精品| 此物有八面人人有两片| 国产精品久久久久久av不卡| 啦啦啦韩国在线观看视频| 亚洲国产精品sss在线观看| 久久久久九九精品影院| 日本熟妇午夜| 麻豆国产97在线/欧美| 久久精品国产99精品国产亚洲性色| 精品不卡国产一区二区三区| 校园人妻丝袜中文字幕| 精品久久久久久久久久免费视频| eeuss影院久久| 国产亚洲精品久久久com| 人人妻人人看人人澡| 一a级毛片在线观看| 99久国产av精品国产电影| 亚洲欧美成人精品一区二区| 97超视频在线观看视频| 亚洲人成网站在线播| 久久久久久九九精品二区国产| 一夜夜www| 观看免费一级毛片| 五月伊人婷婷丁香| 免费在线观看成人毛片| 身体一侧抽搐| videossex国产| 亚洲精华国产精华液的使用体验 | 一边摸一边抽搐一进一小说| 久久精品国产亚洲av涩爱 | 男插女下体视频免费在线播放| 欧美高清成人免费视频www| 国产蜜桃级精品一区二区三区| 成人性生交大片免费视频hd| 欧美激情久久久久久爽电影| 国产精品精品国产色婷婷| 老师上课跳d突然被开到最大视频| 日韩av不卡免费在线播放| 亚洲精品影视一区二区三区av| 一级毛片aaaaaa免费看小| 日韩中字成人| 国产视频内射| 国产女主播在线喷水免费视频网站 | 色尼玛亚洲综合影院| 中文字幕av成人在线电影| 91久久精品国产一区二区成人| 免费人成在线观看视频色| 久久精品国产自在天天线| av女优亚洲男人天堂| 欧美激情久久久久久爽电影| 18禁在线播放成人免费| 麻豆一二三区av精品| 久久99热这里只有精品18| 99热6这里只有精品| 精品不卡国产一区二区三区| 亚洲aⅴ乱码一区二区在线播放| 欧美潮喷喷水| 免费电影在线观看免费观看| 国产69精品久久久久777片| 亚洲一区二区三区色噜噜| 成人午夜高清在线视频| 欧美日本视频| 少妇的逼好多水| 亚洲国产精品久久男人天堂| 精华霜和精华液先用哪个| 人妻少妇偷人精品九色| 变态另类成人亚洲欧美熟女| 欧美性感艳星| 天堂av国产一区二区熟女人妻| www.色视频.com| 色视频www国产| 欧美三级亚洲精品| 亚洲精品影视一区二区三区av| 国产亚洲精品av在线| 国产精品人妻久久久影院| 中文字幕免费在线视频6| 亚洲激情五月婷婷啪啪| 国产欧美日韩一区二区精品| 日本黄色视频三级网站网址| 中国美女看黄片| 国产午夜精品论理片| 亚洲av成人av| 真实男女啪啪啪动态图| 国产成人91sexporn| 久久草成人影院| 12—13女人毛片做爰片一| 嫩草影院入口| 看免费成人av毛片| 国产黄色小视频在线观看| 精品国内亚洲2022精品成人| 丰满人妻一区二区三区视频av| 男人狂女人下面高潮的视频| 免费看光身美女| 久久精品综合一区二区三区| 午夜精品一区二区三区免费看| 国产高清激情床上av| 美女 人体艺术 gogo| 亚洲国产高清在线一区二区三| 女人十人毛片免费观看3o分钟| 国产在线男女| 少妇的逼好多水| 国产在视频线在精品| 亚洲精品成人久久久久久| 国产黄色视频一区二区在线观看 | 看免费成人av毛片| 午夜亚洲福利在线播放| 国产成人一区二区在线| 乱人视频在线观看| 亚洲成av人片在线播放无| 精品午夜福利在线看| 国产精品永久免费网站| 亚洲自拍偷在线| 51国产日韩欧美| 国产午夜福利久久久久久| 亚洲五月天丁香| 亚洲,欧美,日韩| 亚洲精品粉嫩美女一区| 欧美一级a爱片免费观看看| 精品一区二区免费观看| 99热这里只有精品一区| 最新中文字幕久久久久| 色av中文字幕| 亚洲成人中文字幕在线播放| 亚洲精品456在线播放app| 久久久久久九九精品二区国产| 一本久久中文字幕| 国产精品久久久久久久电影| 国产成人a∨麻豆精品| 久久精品国产亚洲av涩爱 | 国产高潮美女av| 18禁在线无遮挡免费观看视频 | 性色avwww在线观看| 色综合色国产| 成人午夜高清在线视频| 国产精品国产高清国产av| 天堂动漫精品| 久久久国产成人免费| 俄罗斯特黄特色一大片| 欧美极品一区二区三区四区| 久久久久国产精品人妻aⅴ院| 免费不卡的大黄色大毛片视频在线观看 | 女生性感内裤真人,穿戴方法视频| 91精品国产九色| 欧美不卡视频在线免费观看| 国产一区亚洲一区在线观看| 少妇熟女欧美另类| 日产精品乱码卡一卡2卡三| 乱系列少妇在线播放| 精品熟女少妇av免费看| 国产精华一区二区三区| 亚洲国产高清在线一区二区三| 欧美xxxx黑人xx丫x性爽| 成年版毛片免费区| 性插视频无遮挡在线免费观看| 久久鲁丝午夜福利片| 日韩成人av中文字幕在线观看 | 少妇猛男粗大的猛烈进出视频 | 黄片wwwwww| 久久精品国产99精品国产亚洲性色| 免费看a级黄色片| 少妇熟女欧美另类| 人人妻人人澡欧美一区二区| 欧美3d第一页| 日韩欧美精品v在线| 午夜老司机福利剧场| 人人妻人人看人人澡| 99热网站在线观看| 51国产日韩欧美| 国产精品一区二区三区四区免费观看 | 亚洲国产精品成人综合色| 啦啦啦韩国在线观看视频| 午夜a级毛片| 最近2019中文字幕mv第一页| 欧美+日韩+精品| 国产精品久久久久久精品电影| 国产黄色视频一区二区在线观看 | 一级黄片播放器| 三级男女做爰猛烈吃奶摸视频| 国产精品三级大全| 一卡2卡三卡四卡精品乱码亚洲| 国产精品综合久久久久久久免费| 69av精品久久久久久| 看片在线看免费视频| 草草在线视频免费看| 最近2019中文字幕mv第一页| 一个人看的www免费观看视频| 久久久精品94久久精品| 免费黄网站久久成人精品| 久久热精品热| 国产片特级美女逼逼视频| 国产一级毛片七仙女欲春2| 亚洲精品国产av成人精品 | 午夜激情欧美在线| 午夜影院日韩av| a级毛色黄片| 午夜影院日韩av| 免费看av在线观看网站| 欧美日韩精品成人综合77777| 精品午夜福利视频在线观看一区| 热99在线观看视频| 国产又黄又爽又无遮挡在线| 国产高清视频在线观看网站| 麻豆一二三区av精品| 成人特级av手机在线观看| 中文字幕av在线有码专区| 噜噜噜噜噜久久久久久91| 亚洲成av人片在线播放无| 偷拍熟女少妇极品色| 欧美绝顶高潮抽搐喷水| av卡一久久| 国产高清不卡午夜福利| 亚洲av免费高清在线观看| 国产精品一区二区性色av| 国产淫片久久久久久久久| 日韩欧美 国产精品| 亚洲人与动物交配视频| 久久精品人妻少妇| 又爽又黄无遮挡网站| 精品久久久久久久久亚洲| 人妻久久中文字幕网| 亚洲欧美成人综合另类久久久 | 性欧美人与动物交配| 搡老岳熟女国产| 成年av动漫网址| 亚洲欧美成人综合另类久久久 | 如何舔出高潮| www.色视频.com| 久久久a久久爽久久v久久| 十八禁网站免费在线| 国产欧美日韩精品一区二区| 嫩草影院精品99| 国产探花极品一区二区| 亚洲婷婷狠狠爱综合网| 国内精品美女久久久久久| 国产精品一区www在线观看| 97碰自拍视频| 极品教师在线视频| 久久久久久久久大av| 久久久精品大字幕| 国产精品爽爽va在线观看网站| 日韩在线高清观看一区二区三区| 嫩草影院新地址| 99久久九九国产精品国产免费| 97热精品久久久久久| 国产极品精品免费视频能看的| 国产真实乱freesex| 人人妻,人人澡人人爽秒播| 麻豆av噜噜一区二区三区| 亚洲国产精品sss在线观看| 国产精品久久电影中文字幕| 色吧在线观看| 精品久久久久久久人妻蜜臀av| 俄罗斯特黄特色一大片| 三级经典国产精品| 亚洲欧美日韩高清专用| 亚洲av中文av极速乱| 色视频www国产| 一a级毛片在线观看| 日本 av在线| 老司机福利观看| 免费av毛片视频| 久久久久久久亚洲中文字幕| 亚洲av美国av| 在线国产一区二区在线| 欧美激情在线99| 精品不卡国产一区二区三区| 男人和女人高潮做爰伦理| 午夜福利高清视频| 国产精品久久久久久久久免| 我的女老师完整版在线观看| 麻豆一二三区av精品| 我要搜黄色片| 小说图片视频综合网站| 国产成人aa在线观看| 亚洲乱码一区二区免费版| 午夜精品国产一区二区电影 | 国产一区二区亚洲精品在线观看| 国产精品人妻久久久久久| av在线播放精品| 精品不卡国产一区二区三区| 亚洲成人久久爱视频| 国产精品无大码| 亚洲久久久久久中文字幕| 色吧在线观看| 免费av观看视频| 成人午夜高清在线视频| 永久网站在线| 国产日本99.免费观看| 男女下面进入的视频免费午夜| 国产aⅴ精品一区二区三区波| 麻豆国产97在线/欧美| 成人永久免费在线观看视频| 亚洲精品久久国产高清桃花| 又粗又爽又猛毛片免费看| 亚洲精品456在线播放app| 久久久久久伊人网av| 啦啦啦韩国在线观看视频| 久久综合国产亚洲精品| 欧美日韩综合久久久久久| 成人性生交大片免费视频hd| 日本色播在线视频| 久久久久久久亚洲中文字幕| av在线天堂中文字幕| 婷婷亚洲欧美| 精品一区二区三区视频在线| 国产 一区精品| 国产aⅴ精品一区二区三区波| 久久精品综合一区二区三区| 日韩精品中文字幕看吧| 好男人在线观看高清免费视频| 亚洲精品一区av在线观看| 欧美另类亚洲清纯唯美| 国产av不卡久久| 欧美激情国产日韩精品一区| 久久久久九九精品影院| 亚洲真实伦在线观看| 蜜桃久久精品国产亚洲av| 免费高清视频大片| 国产成人freesex在线 | 日日啪夜夜撸| 如何舔出高潮| 免费高清视频大片| 搞女人的毛片| 国内精品宾馆在线| 国产三级在线视频| 精品久久久久久久久久久久久| 97在线视频观看| 久久久久国产网址| 国产精品嫩草影院av在线观看| 国产精品福利在线免费观看| 国产aⅴ精品一区二区三区波| 日韩强制内射视频| 人人妻人人澡人人爽人人夜夜 | 99视频精品全部免费 在线| 午夜激情欧美在线| 久久这里只有精品中国| 麻豆一二三区av精品| 卡戴珊不雅视频在线播放| 人妻夜夜爽99麻豆av| 亚洲一区高清亚洲精品| 久久久久久久久久黄片| 国产午夜精品论理片| 久久久久九九精品影院| 2021天堂中文幕一二区在线观| 亚洲天堂国产精品一区在线| 黄色视频,在线免费观看| 亚洲成人av在线免费| 一级黄片播放器| 国产蜜桃级精品一区二区三区| 午夜视频国产福利| 夜夜爽天天搞| 嫩草影视91久久| 欧洲精品卡2卡3卡4卡5卡区| 久久精品综合一区二区三区| 黄色日韩在线| 国产成人影院久久av| 寂寞人妻少妇视频99o| 麻豆成人午夜福利视频| 一进一出抽搐gif免费好疼| 亚洲欧美日韩高清专用| 三级国产精品欧美在线观看| 给我免费播放毛片高清在线观看| 久久精品91蜜桃| 午夜精品在线福利| 精品一区二区三区人妻视频| 亚洲av免费高清在线观看| 精品一区二区三区人妻视频| 久久午夜亚洲精品久久| 精品熟女少妇av免费看| 午夜免费激情av| 国产极品精品免费视频能看的| 久久6这里有精品| 国产高清不卡午夜福利| 午夜免费激情av| 国产高清不卡午夜福利| 18禁裸乳无遮挡免费网站照片| 国内精品一区二区在线观看| 偷拍熟女少妇极品色| 日韩,欧美,国产一区二区三区 | 国内精品美女久久久久久| 国产成人aa在线观看| 日产精品乱码卡一卡2卡三| 欧美成人免费av一区二区三区| 日韩精品青青久久久久久| 97超视频在线观看视频| 青春草视频在线免费观看| 男女边吃奶边做爰视频| 国产 一区 欧美 日韩| 五月玫瑰六月丁香| 中文字幕久久专区| 亚洲国产欧美人成| 欧美人与善性xxx| 欧美xxxx黑人xx丫x性爽| 九九在线视频观看精品| 国产精品美女特级片免费视频播放器| 国产精品综合久久久久久久免费| 又爽又黄无遮挡网站| 亚洲精品在线观看二区| 欧美成人精品欧美一级黄| 久久久久久伊人网av| 99热精品在线国产| 一级毛片久久久久久久久女| 伦理电影大哥的女人| 春色校园在线视频观看| 国产免费一级a男人的天堂| 国产黄色视频一区二区在线观看 | 别揉我奶头 嗯啊视频| 嫩草影院精品99| 不卡一级毛片| 高清毛片免费看| av在线天堂中文字幕| 精品一区二区三区人妻视频| 高清毛片免费看| 深爱激情五月婷婷| 成人av一区二区三区在线看| 欧洲精品卡2卡3卡4卡5卡区| 成人漫画全彩无遮挡| 国产精品一区二区性色av| 亚洲图色成人| 一级毛片久久久久久久久女| 国产高清视频在线播放一区| 又爽又黄a免费视频| 一夜夜www| 亚洲精品亚洲一区二区| 亚洲人成网站高清观看| 一个人观看的视频www高清免费观看| 蜜臀久久99精品久久宅男| 精品久久久噜噜| 亚洲婷婷狠狠爱综合网| 亚洲国产精品sss在线观看| 麻豆一二三区av精品| 国产精华一区二区三区|