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Nearshore sediments using carbon isotopes, A study of the remineralization of organic carbon in

机译:利用碳同位素的近岸沉积物,中国有机碳再矿化的研究

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摘要

A study of the remineralization of organic carbon was conducted in the organic-rich sediments of Buzzards Bay, MA. Major processes affecting the carbon chemistry in sediments are reflected by changes in the stable carbon isotope ratios of dissolved inorganic carbon (XCO2) in sediment pore water. Six cores were collected seasonally over a period of two years. The following species were measured in the pore waters: JC02, &'3 C-2CO2, P04, JH 2S, Alk, DOC, and Ca. Measurements of pore water collected seasonally show large gradients with depth, which are larger in summer than in winter. The 613C (PDB) of IC02 varies from 1.3 o/oo in the bottom water to approximately -10 o/oo at 30 cm. During all seasons, there was a trend towards more negative values with depth in the upper 8 cm due to the remineralization of organic matter. There was a trend toward more positive values below 8 cm, most likely due to biological irrigation of sediments with bottom water. Below 16-20 cm, a negative gradient was re-established which indicates a return to remineralization as the main process affecting pore water chemistry. Using the XC02 depth profile, it was estimated that 67-85 gC/m 2 are oxidized annually and 5 gC/m 2-yr are buried. The amount of carbon oxidized represented remineralization occurring within the sediments. This estimate indicated that approximately 20% of the annual primary productivity reached the sediments. The calculated remineralization rates varied seasonally with the high of 7.5 x 10-' mol/L-sec observed in August 84 and the low (0.6 x 10-) in December 83. The calculated remineralization rates were dependent on the amount of irrigation in the sediments; if the irrigation parameter is known to ±20%, then the remineralization rates are known to this certainty also. The amount of irrigation in the sediments was estimated using the results of a seasonal study of 2 2 2Rn/ 22 'Ra disequilibria at the same study site (Martin, 1985). Estimates of the annual remineralization in the sediments using solid-phase data indicated that the solid-phase profiles were not at steady-state concentrations. The isotopic signature of 2C02 was used as an indicator of the processes affecting IC02 in pore water. During every month, the oxidation of organic carbon to C02 provided over half of the carbon added to the IC02 pool. However, in every month, the 6'"C of XCO2 added to the pore water in the surface sediments was greater than -15 o/oo, significantly greater than the 613C of solid-phase organic carbon in the sediments (-20.6 o/oo). The 613C of IC02 added to the pore water in the sediments deeper than 7 cm was between -20 and -21 o/oo, similar to the organic carbon in the sediments. Possible explanations of the 1 3C-enrichment observed in the surface sediments were: a) significant dissolution of CaC0 3 (613C = +1.7 o/oo) b) the addition of significant amounts of carbonate ion from bottom water to pore water c) an isotopic difference between the carbon oxidized in the sediments and that remaining in the sediments. The effect of CaC0 3 dissolution was quantified using measured dissolved Ca profiles and was not large enough to explain the observed isotopic enrichment. An additional source of 13C-enriched carbon was bottom water carbonate ion. In every month studied, there was a net flux of 2C0 2 from pore water to bottom water. The flux of pore water 2C02 to bottom water ranged from a minimum of 10 x 10-12 mol/cm 2 -sec in December 83 to a maximum of 50 x 10-12 mol/cm2-sec in August 84. However, because the pH of bottom water was about 8 while that of the pore water was less than or equal to 7, the relative proportion of the different species of inorganic carbon (H2CO, HCO-, C0~) was very different in bottom water and pore water. Thus, while there was a net flux of IC0 2 from pore water to bottom water, there was a flux of carbonate ion from bottom water to pore water. Because bottom water JC02 was more 13C-enriched than pore water JC0 2, the transfer of bottom water carbonate ion to pore water was a source of 13C-enriched carbon to the pore water. If the &'3C of CO2 added to the pore water from the oxidation of organic carbon was -20.6 o/oo, then the flux of C3% from bottom water to pore water must have been 10-30% of the total flux of 2C02 from pore water to bottom water. This is consistent with the amount calculated from the observed gradient in carbonate ion. Laboratory experiments were conducted to determine whether the 613C of C02 produced from the oxidation of organic carbon (613C-OCOX) was different from the 613C of organic carbon in the sediments (613C-SOC). In the laboratory experiments, mud from the sampling site was incubated at a constant temperature. Three depths were studied (0-3, 10-15, and 20-25 cm). For the first study (IEl), sediment was stirred to homogenize it before packing into centrifuge tubes for incubation. For the second study (IE2), sediment was introduced directly into glass incubation tubes by subcoring. The second procedure greatly reduced disturbance to the sediment. Rates of C02 production were calculated from the concentrations of 2C02 measured over up to 46 days. In both studies, the values of Re in the deeper intervals were about 10% of the surface values. This was consistent with the field results, although the rates decreased more rapidly in the field. In all cases, the remineralization rates during the beginning of IEl were much greater than those at the beginning of IE2. The sediment for IEl was collected in February 84. The measured value of Rc in the surface sediment of the laboratory experiment (24 x 10- mol/L-sec) was much greater than the value of Rc observed in the field in another winter month, December 83 (.62 x 10~9). The sediment for IE2 was collected in August 85. The measured values of Re in the surface sediment (6.6-12 x 10~9 mol/L-sec) were consistent with the field values from August 84 (7.5 x 10-9). The XC02 results indicated that IE2 reproduced field conditions more accurately than IEl did. The isotopic results from the experiments strongly suggested that 613C-OCOX in the surface sediments (-17.8 o/oo ± 1.9 o/oo) was greater than 6'3C-SOC (-20.6 ± 0.2 o/oo). The magnitude of the observed fractionation was small enough that the observed values of 613C-C02 in the pore waters could be explained by fractionated oxidation coupled with the diffusion of carbonate ion from bottom water to pore water. The observed fractionation was most likely due to the multiple sources of organic carbon to coastal sediments. A study of the natural levels of radiocarbon in these sediments indicated that the carbon preserved in the sediments is approximately 30% terrestrial while the rest is from phytoplankton.
机译:在马萨诸塞州巴扎德斯湾富含有机物的沉积物中进行了有机碳再矿化的研究。沉积物孔隙水中溶解的无机碳(XCO2)的稳定碳同位素比的变化反映了影响沉积物中碳化学的主要过程。在两年的时间内,季节性收集了六个岩心。在孔隙水中测量了以下物种:JCO2、3 C-2CO2,PO4,JH 2S,Alk,DOC和Ca。季节性收集的孔隙水的测量结果显示,深度的梯度较大,夏季比冬季大。 IC02的613C(PDB)从底部水中的1.3 o / oo到30 cm处的大约-10 o / oo不等。在所有季节中,由于有机物的再矿化,在上部8厘米处的深度有向负值更大的趋势。在8厘米以下,有一个趋于正值的趋势,这很可能是由于用底水对沉积物进行了生物灌溉。在16-20厘米以下,将重新建立负梯度,这表明重新矿化是影响孔隙水化学的主要过程。使用XCO2深度剖面,估计每年氧化67-85 gC / m 2,并掩埋5 gC / m 2年。碳的氧化量表示沉积物中发生了再矿化。这一估计表明,每年初级生产力的大约20%到达了沉积物。计算的再矿化率随季节变化,84年8月的最高值是7.5 x 10-mol / L-sec,83年12月的最低值是(0.6 x 10-sec)。计算的再矿化率取决于灌溉量。沉积物如果灌溉参数已知为±20%,则再矿化率也可以确定。使用在同一研究地点进行的2 2 2Rn / 22'Ra不平衡的季节性研究结果,估算沉积物中的灌溉量(Martin,1985年)。使用固相数据对沉积物的年度再矿化程度进行的估算表明,固相分布不在稳态浓度下。 2CO 2的同位素标记用作影响孔隙水中IC02的过程的指标。在每个月中,有机碳被氧化为CO2的过程中,有一半以上的碳被添加到了IC02库中。但是,每个月添加到表层沉积物中孔隙水中的XCO2的6'“ C大于-15 o / oo,显着大于沉积物中固相有机碳的613C(-20.6 o /在深于7 cm的沉积物中孔隙水中添加的IC02的613C在-20和-21 o / oo之间,类似于沉积物中的有机碳。表面沉积物是:a)CaCO 3的显着溶解(613C = +1.7 o / oo)b)从底部水到孔隙水中添加了大量的碳酸根离子c)沉积物中被氧化的碳与氧化碳之间的同位素差异通过测量溶解的Ca曲线来量化CaCO 3溶解的影响,其作用还不足以解释所观察到的同位素富集;另外13 C富集碳的来源是底水碳酸盐离子。是来自孔隙的2C0 2净通量水到底水。孔隙水2CO2到底部水的通量范围从83年12月的最低10 x 10-12 mol / cm 2 -sec到84年8月的最高50 x 10-12 mol / cm2-sec。底水的pH约为8,而孔隙水的pH小于或等于7,底水和孔隙水中不同种类的无机碳(H2CO,HCO-,CO〜)的相对比例差异很大。因此,尽管有IC 0 2从孔隙水到底部水的净通量,但有碳酸根离子从底部水到孔隙水的通量。因为底部水JCO 2比孔隙水JCO 2富集13C,所以底部碳酸盐离子向孔隙水的转移是向孔隙水富集13 C的碳的来源。如果由于有机碳的氧化而添加到孔隙水中的CO2的'3C为-20.6 o / oo,则从底部水到孔隙水的C3%通量必须为2C02总通量的10-30%从孔隙水到底部水。这与从观察到的碳酸根离子梯度计算出的量一致。进行实验室实验以确定由有机碳氧化产生的CO2 613C(613C-OCOX)是否与沉积物中的有机碳613C(613C-SOC)不同。在实验室实验中,将采样部位的泥浆在恒温条件下孵育。研究了三个深度(0-3、10-15和20-25厘米)。对于第一个研究(IE1),将沉淀物搅拌均匀,然后包装到离心管中进行孵育。对于第二项研究(IE2)通过沉淀将沉淀物直接引入玻璃培养管中。第二步大大减少了对沉积物的干扰。根据在长达46天的时间内测得的2CO2浓度,计算出CO2产生率。在这两项研究中,在较深的时间间隔内的Re值约为表面值的10%。这与田间结果一致,尽管在田间比率下降得更快。在所有情况下,IEI初期的再矿化率都比IE2初期的高。 IEl的沉积物是在84年2月收集的。实验室实验的表面沉积物中Rc的测量值(24 x 10 mol / L-sec)远大于另一个冬季月份在野外观察到的Rc值。 ,十二月83(.62 x 10〜9)。 IE2的沉积物是在85年8月收集的。表层沉积物中Re的测量值(6.6-12 x 10〜9 mol / L-sec)与8月84日的田间测量值(7.5 x 10-9)一致。 XC02结果表明IE2比IE1更准确地再现了田间条件。实验的同位素结果强烈表明,表面沉积物中的613C-OCOX(-17.8 o / oo±1.9 o / oo)大于6'3C-SOC(-20.6±0.2 o / oo)。观察到的分馏的大小足够小,以致于孔隙水中613C-CO2的观察值可以通过分馏氧化和碳酸盐离子从底部水到孔隙水的扩散来解释。观察到的分馏最有可能是由于沿海沉积物中有多种有机碳源。对这些沉积物中自然放射性碳含量的研究表明,沉积物中保存的碳大约占陆地的30%,而其余的则来自浮游植物。

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    McNichol, Ann P., 1956-;

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  • 年度 1986
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