共查询到17条相似文献，搜索用时 281 毫秒
1.
于2012年7—9月现场测定了北极挪威海和格陵兰海区域海水二甲基硫(DMS)及其前体物质二甲巯基丙酸内盐(DMSP,分溶解态DMSPd和颗粒态DMSPp)的含量,研究了其空间分布格局及其影响因素,探讨了表层海水DMS的生物周转和去除途径。结果表明,表层海水DMS、DMSPd和DMSPp的平均浓度分别为5.36nmol/L、15.63nmol/L和96.73nmol/L,受挪威海流和北极深层水影响,表层海水二甲基硫化物浓度呈现出由低纬度向高纬度海域递减的趋势。DMSPd和DMSPp浓度与Chl a浓度均有显著的相关性,说明浮游植物生物量是影响挪威海和格陵兰海二甲基硫化物生产的重要因素。表层海水DMS生物生产和消费速率平均值分别为18.19nmol/(L·d)、15.67nmol/(L·d)。DMS微生物周转时间变化范围为0.03~1.80d,平均值为0.49d,DMS海-气周转时间是微生物消费时间的90倍,说明夏季挪威海和格陵兰海表层海水中DMS微生物消费过程是比海-气扩散更具优势的去除机制。 相似文献
2.
本研究首次探究了西太平洋雅浦海沟北段从表层到超深渊海水中甲烷（CH4）及二甲基硫（DMS）的前体物质二甲基巯基丙酸内盐（DMSP）的浓度变化情况。结果表明:雅浦海沟海水甲烷浓度变化范围为1.49~3.87 nmol/L。其上层海水甲烷平均浓度最高，有明显的次表层极大现象。雅浦海沟氧最小层海水的甲烷平均浓度最低；在500~1 000 m中层水中甲烷浓度有一定程度的增大，1 000 m以下至底层甲烷浓度继续升高。研究海区溶解态DMSP（DMSPd）和总DMSP（DMSPt）平均浓度的垂直变化随深度呈先增大后减小趋势，颗粒态DMSP（DMSPp）的平均浓度随深度呈波动式变化，在中层达到最大。雅浦海沟CH4和DMSP浓度垂直变化受浮游生物、微生物、光照、温度、压力、大洋环流等的复杂影响。在真光层海水中，CH4浓度与DMSPd、DMSPp和DMSPt浓度表现为负相关关系，在200 m至底层海水中，CH4浓度与DMSPd、DMSPp和DMSPt浓度表现为正相关关系，显示光照条件是造成雅浦海沟不同深度海水CH4和DMSP浓度相关性差异的关键因素。 相似文献
3.
基于中国第7次北极科学考察白令海现场调查资料与数据,分析了2016年夏季白令海海水颗粒态(DMSOp)和溶解态二甲亚砜(DMSOd)浓度的空间变化特征及其影响因素。研究表明,夏季白令海二甲亚砜(DMSO)浓度高于全球多数大洋和近岸海域。夏季白令海DMSOd和DMSOp浓度空间变化相似。表层海水DMSOp浓度为6.47～169.40 nmol/L,平均值为(79.62±56.10) nmol/L;DMSOd浓度的变化范围是20.07～153.70 nmol/L,平均值为(72.67±39.20) nmol/L。平面分布上,白令海表层DMSO浓度由海盆区、中外陆架区至内陆架区依次降低;垂直分布上由表至底随深度增加而降低,表层DMSOd和DMSOp浓度高于55 nmol/L,底层低于25 nmol/L。海盆区DMSOd主要源于DMS氧化和浮游生物直接合成的DMSOp,海盆区深层水团DMSOd浓度主要受控于温度和盐度。中外陆架区表层暖水团DMSO浓度主要受控于温度,陆架冷水团DMSO浓度则受盐度影响较大。内陆架区陆架水团DMSOp浓度和阿拉斯加沿岸水团DMSOd浓度分别受温度和DMS光化学氧化影响。 相似文献
4.
《海洋科学进展》2021,39(3)
基于2012年和2014年中国北极科学考察航次白令海现场调查数据,分析白令海东陆架区二甲基硫(DMS)及其前体物质β-二甲基硫巯基丙酸内盐(DMSP)的空间分布特征和年际变化。结果显示,白令海东部陆架区DMS浓度呈自西向东递减的趋势,浓度平均值由2012年0.80 nmol·L~(-1)(范围为0.11～2.27 nmol·L~(-1))增加至2014年1.33 nmol·L~(-1)(范围为0.07～4.49 nmol·L~(-1))。DMSP浓度的空间变化与DMS不一致,高值区位于断面东部,主要受近岸阿拉斯加沿岸流以及育空河淡水输入的影响。2012—2014年,溶解态DMSP(DMSPd)和颗粒态DMSP(DMSPp)浓度平均值分别从4.21 nmol·L~(-1)、16.83 nmol·L~(-1)提高至14.94 nmol·L~(-1)、49.77 nmol·L~(-1),应是冷水团范围缩减以及浮游植物群落变化所引起的。DMS浓度同温度、c_(PO~(3-)_4)、c_(SiO~(2-)_3)显著相关,而DMS和DMSP浓度同无机氮浓度、盐度均存在显著相关性。表层海水DMS和DMSPd的生物生产速率均高于消费速率,且呈现出东高西低的趋势,原因是温度影响了微生物代谢活动。2014年的生产和消费速率均高于2012年的,主要由于表层海水DMS和DMSPd浓度升高和水团的年际变化。2012年和2014年表层海水中DMS微生物消耗速率平均值分别为13.66 nmol·L~(-1)·d~(-1)和33.87 nmol·L~(-1)·d~(-1),海-气通量平均值分别为3.66μmol·m~(-2)·d~(-1)和5.33μmol·m~(-2)·d~(-1),表层海水DMS通过海气扩散去除的周转时间分别是微生物消费的7.4和5.7倍。白令海东部陆架区表层水体中微生物消费是比海气释放更重要的DMS去除途径。 相似文献
5.
秋季东海二甲基硫和二甲巯基丙酸内盐浓度分布及降解速率研究 总被引：1，自引：0，他引：1
于2013年10~11月现场测定了东海中二甲基硫(DMS)及其前体物质二甲巯基丙酸内盐(DMSP,分为溶解态DMSPd和颗粒态DMSPp)的含量,研究其水平分布特征、DMSPp的粒径分布及DMSPd的降解速率,并对DMS的海-气交换通量进行了探讨。研究结果表明,表层海水中DMS、DMSPd和DMSPp的浓度平均值分别为(4.84±0.40)、(5.84±0.93)和(13.01±0.52)nmol·L-1。海水中DMSPd的降解速率在2.59~16.36nmol·L-1·d-1之间,平均值为(6.78±0.84)nmol·L-1·d-1。调查海域范围内,小型浮游植物(20μm)是DMSPp和叶绿素a(Chl a)重要贡献者。此外,秋季东海表层海水DMS的海-气交换通量为0.66~31.73μmol·m-2·d-1,平均值为(11.63±0.71)μmol·m-2·d-1。 相似文献
6.
胶州湾海水中DMS和DMSP的分布及其影响因素 总被引：1，自引：0，他引：1
为了解人为活动对二甲基硫(DMS)和二甲巯基丙酸(DMSP)生物生产的干扰,分别于2005年8月、11月对胶州湾海域进行采样。测定结果表明:胶州湾海水中8月DMS、DMSPd和DMSPp在次表层的平均含量分别为4.89,17.9和23.93nmol·L-1,在微表层中的平均含量分别为4.58,19.98和21.49nmol·L-1,11月DMS、DMSPd和DMSPp在次表层的平均含量分别为2.07,12.99和16.74nmol·L-1,在微表层中的平均含量分别为1.44,16.13和19.62nmol·L-1。DMS和DMSP的水平分布由于受到陆源输入的影响,呈现出自湾内向湾外递降的趋势。DMS和DMSP的含量夏季高于秋季。DMS和Chl-a在每个季节具有一定的相关性。DMS浓度的增加导致DMS通量增加。对海水微表层和次表层的研究表明,DMS和DMSPp并未在微表层中富集,而DMSPd有一定程度的富集。DMS,DMSP,Chl-a在海水微表层和次表层之间浓度分布的相关性体现了2层水体之间存在强烈的交换作用。 相似文献
7.
以胶州湾及青岛近海为研究区域,利用吹扫-捕集气相色谱法研究了二甲基硫(DMS)和二甲巯基丙酸(DMSP,分为溶解态DMSPd和颗粒态DMSPp)在微表层与次表层中的浓度以及它们在微表层中的富集行为。结果表明,DMS、DMSPd和DMSPp在微表层中的浓度高于次表层,它们在微表层中的富集因子分别为1.17、1.84和1.51。研究发现,DMS及DMSPp浓度与叶绿素a(Chl-a)浓度有很好的相关性,但它们的周日变化与Chl-a并不完全同步。DMS/Chl-a和DMSPp/Chl-a的比值在次表层和微表层分别为4.35、13.47mmol/g和3.99、15.88mmol/g。胶州湾及青岛近海生态环境受人为活动干扰严重,使本海域DMS含量较高,从而贡献出较大的DMS海-气通量。 相似文献
8.
秋季东海二甲基亚砜的分布与影响因素研究 总被引：1，自引：0，他引：1
2010年11月对东海进行了大面调查,研究了秋季东海表层水中颗粒态和溶解态二甲基亚砜(DMSOp和DMSOd)的水平分布和PN断面的垂直分布特征及其影响因素。结果显示,表层海水中DMSOp和DMSOd的浓度范围分别为2.49~85.5nmol/L和2.27~86.6nmol/L,平均值分别为(17.2±1.40)nmol/L和(15.3±1.29)nmol/L。DMSOp水平分布与叶绿素a(Chl a)相类似,呈现近岸高、远海低的趋势,而DMSOd浓度高值区主要集中在东海西南部上升流区域。分析PN断面的垂直分布可见,DMSOp在近岸底层水中浓度较高,而DMSOd浓度在表层出现高值。相关性分析的结果表明,DMSOp与颗粒态二甲巯基丙酸内盐(DMSPp)以及DMSOp/Chl a比值与盐度分别存在一定的相关性,说明DMSOp与DMSPp具有相似的来源及生理功能。此外,DMSOd与二甲基硫(DMS)浓度具有正相关关系,说明DMS的氧化是东海DMSOd的一个重要来源途径。 相似文献
9.
于2013年10~11月和2014年5~6月调查测定了东海陆架区海水中二甲亚砜(DMSO)的浓度,探讨了溶解态二甲亚砜(DMSOd)和颗粒态二甲亚砜(DMSOp)的水平和垂直分布、季节变化及其影响因素;此外,对沉积物间隙水中DMSOd的浓度以及表层海水中不同粒径的DMSOp和叶绿素a(Chl a)进行了分析。结果显示,秋季和夏初表层海水中DMSOd和DMSOp的平均浓度分别为(10.52±7.16)、(8.99±6.34)nmol·L^-1和(17.51±9.90)、(16.96±10.73)nmol·L^-1,存在明显的季节差异。秋季表层海水中DMSOp的高值区出现在Chl a较低的远岸海域,而夏初表层海水中DMSO的浓度从近岸到远海逐渐降低。间隙水中DMSOd的浓度明显高于底层海水中DMSOd的浓度,说明沉积物中存在DMSO的生产释放,可能是底层海水DMSO的重要来源。此外,粒径分布结果表明较大微型浮游植物(5~20μm)是秋季东海表层海水中DMSOp的主要贡献者。 相似文献
10.
海水温度对衰亡期浒苔释放生源硫影响的模拟研究 总被引：1，自引：0，他引：1
为研究浒苔释放生源硫的特征，本文对采集于黄海绿潮中期和末期的浒苔进行了实验室模拟培养，探讨了不同温度对衰亡期浒苔释放生源硫化物的影响。实验结果表明，在10~25℃温度范围内，温度升高能够加速浒苔的衰亡。二甲基硫（DMS）的平均释放速率范围为2.79~150.70 nmol/（L·g·d），二甲基硫基丙酸内盐（DMSP）的平均释放速率范围为2.16~113.26 nmol/（L·g·d）。温度升高能够使DMS和DMSP的释放速率加快，释放量增加，DMS最大平均释放速率在25℃条件下比10℃条件下升高了约60%，培养液中DMS浓度升高了2~3倍。采集于绿潮末期的浒苔培养液中的DMS和DMSP和采集于绿潮中期的浒苔相比，浓度有所增加，采集于浒苔绿潮末期浒苔培养液中DMS的最高平均浓度为418.41 nmol/L，约为中期的4倍；DMSP的最高平均浓度为316.14 nmol/L，是中期的3倍。浒苔绿潮的爆发会对水体中的硫体系循环产生影响，进而影响该海域生态环境。 相似文献
11.
研究了夏季东海海水中和大气中一氧化碳(CO)的浓度分布、海-气通量和表层海水中CO的微生物消耗。夏季东海大气中CO的体积分数范围为63×10-9~120×10-9,平均值为87×10-9(SD=18×10-9,n=37),呈现出近岸高,远海低和北高南低的特点。夏季东海表层海水中CO的浓度范围为0.24~5.51nmol/L,平均值为1.48nmol/L(SD=1.46,n=37),CO的浓度受太阳辐射影响明显;CO在垂直分布上表现出浓度随深度增加迅速减小的特征,浓度最大值出现在表层。调查期间表层海水中CO相比大气处于过饱和状态,过饱和系数变化范围为3.65~113.55,平均值为23.63(SD=24.56,n=37),这表明调查海域是大气中CO的源。CO的海-气通量变化范围为0.25~78.50μmol/(m2·d),平均值为9.97μmol/(m2·d)(SD=14.92,n=37)。在CO的微生物消耗培养实验中,CO的浓度随时间增长呈指数降低,消耗过程表现出一级反应的特点,速率常数KCO范围为0.043~0.32/h,平均值为0.18/h(SD=0.088,n=9),KCO与盐度之间存在负相关关系。 相似文献
12.
A chemoreduction-purge-and-trap gas chromatographic method has been developed for the determination of trace dimethylsulfoxide (DMSO) in seawater. In the analysis procedure, DMSO was first reduced to dimethylsufide (DMS) by sodium borohydride and then the produced DMS was analyzed using the purge-and-trap technique coupled with gas chromatographic separation and flame photometric detection. Under the optimum conditions, 97% DMSO was reduced in the standard solution samples with a standard deviation of 5% (n=5). The detection limit of DMSO was 2.7 pmol of sulfur, corresponding to a concentration of 0.75 nmol/L for a 40 ml sample. This method was applied to determine the dissolved DMSO (DMSOd) and particulate DMSO (DMSOp) concentrations in the surface seawater of the Jiaozhou Bay, and the results showed that the DMSOd and DMSOp concentrations varied from 16.8 to 921.1 nmol/L (mean:165.2 nmol/L) and from 8.0 to 162.4 nmol/L (mean:57.7 nmol/L), respectively. The high concentrations of DMSOp were generally found in productive regions. Consequently, a significant correlation was found between the concentrations of DMSOp and chlorophyll a, suggesting that phytoplankton biomass might play an important role in controlling the distribution of DMSOp in the bay. Moreover, in the study area, the concentrations of DMSOd were significantly correlated with the levels of DMS, implying that the production of DMSOd is mainly via photochemical and biological oxidation of DMS. 相似文献
13.
春秋季南黄海二甲基硫(DMS)与二甲巯基丙酸(DMSP)的浓度分布研究 总被引：2，自引：0，他引：2
Temporal distributions of dimethylsulfide(DMS) and dimethylsulfoniopropionate(DMSP) were studied in the southern Yellow Sea(SYS) during April and September 2010. The mean concentrations(range) of DMS, dissolved and particulate DMSP(DMSPd and DMSPp) in the surface waters in spring are 1.69(0.48–4.92), 3.18(0.68–6.75)and 15.81(2.82–52.33) nmol/L, respectively, and those in autumn are 2.80(1.33–5.10), 5.45(2.19–11.30) and 30.63(6.24–137.87) nmol/L. On the whole, the distributions of DMS and DMSP in spring are completely different from those in autumn. In the central part of the SYS, the concentrations of DMS and DMSP in spring are obviously higher than those in autumn, but the opposite situation is found on the south of 34°N, which can be attributed to the differences in nutrients and phytoplankton biomass and composition between spring and autumn. Besides,the seasonal variations of water column stability and the Changjiang diluted water also have significant impact on the distributions of DMS and DMSP in spring and autumn on the south of 34°N. DMS and DMSPp concentrations coincide well with chlorophyll a(Chl a) levels in the spring cruise, suggesting that phytoplankton biomass may play an important role in controlling the distributions of DMS and DMSPp in the study area. Annual DMS emission rates range from 0.015 to 0.033 Tg/a(calculated by S), respectively, using the equations of Liss and Merlivat(1986) and Wanninkhof(1992). This result implies a significant relative contribution of the SYS to the global oceanic DMS fluxes. 相似文献
14.
Seasonal and spatial distributions of dissolved and particulate dimethylsulfoxide(DMSOd,DMSOp)were measured in the East China Sea and the Yellow Sea during March–April 2011 and October–November 2011.The concentrations of DMSOd and DMSOp in the surface water were 20.6(5.13–73.8)and 8.90(3.75–29.6)nmol/L in spring,and 13.4(4.17–42.7)and 8.18(3.44–22.6)nmol/L in autumn,respectively.Both DMSOd and DMSOp concentrations revealed similar seasonal changes with higher values occurring in spring,mainly because of the higher phytoplankton biomass observed in spring.Moreover,the ratios of DMSOp/chlorophyll a also exhibited an apparent seasonal change with higher values in autumn(35.7 mmol/g)and lower values in spring(23.4 mmol/g),thereby corresponding with the seasonal variation in the proportion of DMSO producers in the phytoplankton community between spring and autumn.In addition,DMSOd and DMSOp concentrations in the surface seawater revealed obvious diurnal variations with the maxima appearing in the afternoon. 相似文献
15.
The distributions of DMS and its precursor dimethylsulfoniopropionate, in both dissolved (DMSPd) and particulate fractions (DMSPp) were determined in the seasurface microlayer and corresponding subsurface water of the Jiaozhou Bay, China and its adjacent area in May and August 2006. The concentrations of all these components showed a clear seasonal variation, with higher concentrations occurring in summer. This can be mainly attributed to the higher phytoplankton biomass observed in summer. Simultaneously, the enrichment extents of DMSPd and DMSPp in the microlayer also exhibited seasonal changes, with higher values in spring and lower ones in summer. Higher water temperature and stronger radiant intensity in summer can enhance their solubility and photochemical reaction in the microlayer water, reducing their enrichment factors (the ratio of concentration in the microlayer to that in the corresponding subsurface water). A statistically significant relationship was found between the microlayer and subsurface water concentrations of DMS, DMSP and chlorophyll a, demonstrating that the biogenic materials in the microlayer come primarily from the underlying water. Moreover, our data show that the concentrations of DMSPp and DMS were significantly correlated with the levels of chlorophyll a, indicating that phytoplankton biomass might play an important role in controlling the distributions of biogenic sulfurs in the study area. The ratios of DMS/chlorophyll a and DMSPp/chlorophyll a varied little from spring to summer, suggesting that there was no obvious change in the proportion of DMSP producers in the phytoplankton community. The mean sea-to-air flux of DMS from the study area was estimated to be 5.70 μmol/(m2·d), which highlights the effects of human impacts on DMS emission. 相似文献
16.
17.
In the present study, we report N_2 fixation rate(~(15)N isotope tracer assay) and the diazotroph community structure(using the molecular method) in the western tropical North Pacific Ocean(WTNP)(13°–20°N, 120°–160°E). Our independent evidence on the basis of both in situ N_2 fixation activity and diazotroph community structure showed the dominance of unicellular N_2 fixation over majority of the WTNP surface waters during the sampling periods.Moreover, a shift in the diazotrophic composition from unicellular cyanobacteria group B-dominated to Trichodesmium spp.-dominated toward the western boundary current(Kuroshio) was also observed in 2013. We hypothesize that nutrient availability may have played a major role in regulating the biogeography of N_2 fixation.In surface waters, volumetric N_2 fixation rate(calculated by nitrogen) ranged between 0.6 and 2.6 nmol/(L·d) and averaged(1.2±0.5) nmol/(L·d), with 10 μm size fraction contributed predominantly(88%±6%) to the total rate between 135°E and 160°E. Depth-integrated N_2 fixation rate over the upper 200 m ranged between 150 μmol/(m~2·d)and 480 μmol/(m~2·d)(average(225±105) μmol/(m~2·d). N_2 fixation can account for 6.2%±3.7% of the depthintegrated primary production, suggesting that N_2 fixation is a significant N source sustaining new and export production in the WTNP. The role of N_2 fixation in biogeochemical cycling in this climate change-vulnerable region calls for further investigations. 相似文献