The influence of different pretreatment methods on theδ13C value of dissolved inorganic carbon in water
-
摘要: 为探明不同的样品前处理方法对水中溶解无机碳同位素的影响,寻找最佳的样品前处理方法,本文系统研究了不同样品采集方法(顶空样品瓶和聚乙烯瓶)和保存方法(不同的温度和是否加饱和氯化汞)以及储存时间对不同类型水样溶解无机碳同位素值的影响。结果表明:在水样类型相同的情况下,顶空瓶法较聚乙烯瓶法采集的水样δ13CDIC值更稳定;用聚乙烯瓶采集水样,加入饱和氯化汞能抑制微生物生长,不加饱和氯化汞的水样δ13CDIC值变化无规律且幅度大,而加了饱和氯化汞的水样δ13CDIC值更接近初始值,但随保存温度的升高和保存时间的推移,其δ13CDIC值逐渐偏重,主要受温度升高有利于HCO3-水解并释放CO2的影响;不同类型水样在不加饱和氯化汞条件下,随保存时间加长,岩溶水的δ13CDIC值较初始值偏重,混合水和非岩溶区水δ13CDIC值较初始值偏轻。实验表明,用顶空样品瓶采集的水样保存100天,δ13CDIC最大变化值为0.42‰;用顶空样品瓶采集的水样保存时间长,δ13CDIC值变化小,最能反映样品的初始值,是最佳的样品前处理方法。用聚乙烯瓶采集的水样加饱和氯化汞并保存在5 ℃能满足样品短时间的保存。Abstract: In order to research the influence of different sample preparation methods on the dissolved inorganic carbon isotope in water samples, and to establish the best sample preparation method, this paper systematically study the sample collection (headspace vial and polyethylene bottle) methods, storage temperature, saturation mercuric chloride and storage duration which affect the dissolved inorganic carbon isotope value in different types of water samples. The results show that δ13CDIC headspace vial collection method is more stable than the polyethylene bottle collection method for the same water type. Using polyethylene bottle collection method and adding saturated mercury chloride may inhibit the growth of microorganisms. The δ13CDIC value irregularly varies in a big range in case of no saturated mercury chloride added. In contrast, the δ13CDIC value roughly stabilizes at its initial value. The value increased in the case of the relative high temperature or long duration, which is mainly attributed to the release of CO2 in this condition of sample preservation. Different types of water samples without saturated mercuric chloride and with prolonged preservation, the karst water δ13CDIC was more positive than the original value, and the mixed water and non- karst water was negative than the original value. The experiment results show, the maximum difference of δ13C value was merely 0.42‰ after 100 days of storage by using headspace vial sample collection, which is proved to be the best way of sample collection and preservation. In the meantime, the water sampled by polyethylene bottle collection method and stored in a 5 ℃ condition can last a short time to maintain the reliable δ13CDIC value.
-
[1] 赖冬蓉, 严兆彬, 陈益平,等. 南昌市湖水可溶解无机碳与碳同位素特征及其影响因素分析[J]. 东华理工大学学报(自然科学版), 2012, 35(2):143-147. [2] Parker S R, Gammons C H, Smith M G, et al. Behavior of stable isotopes of dissolved oxygen, dissolved inorganic carbon and nitrate in groundwater at a former wood treatment facility containing hydrocarbon contamination[J]. Applied Geochemistry, 2012, 27:1101-1110. [3] Abongwa P T, Atekwana E A. Assessing the temporal evolution of dissolved inorganic carbon in waters exposed to atmospheric CO2(g): A laboratory approach[J].Journal of Hydrology, 2013, 250-265. [4] Gustafsson E, M?rth C M, Humborg C, et al. Modelling the 13C and 12C isotopes of inorganic and organic carbon in the Baltic Sea[J].Journal of Marine Systems,2015,148:122-130. [5] Porowska D. Determination of the origin of dissolved inorganic carbon in groundwater around a reclaimed landfill in Otwock using stable carbon isotopes[J].Waste Management, 2015, 39:216-225. [6] Leng M G,Marshal J D. Palaeoclimate interpretation of stable isotope data from lake sediment archives[J].Quaternary Science Reviews, 2004, 23, 811-831. [7] Eastwood W J, Leng M J, Roberts N, et al. Holocene Climate Change in the Eastern Mediterranean Region: a Comparison of Stable Isotope and Pollen Data from a Lake Record in Southwest Turkey[J].Journal of Quaternary Science, 2007, 22(4):327-341. [8] 焦树林,陶贞,高全洲,等. 西江河口段溶解无机碳稳定同位素组成的时空变化[J]. 地理学报, 2008, 63(5): 553-560. [9] Parker S R, Gammons C H, Poulson S R, et al. Diel behavior of stable isotopes of dissolved oxygen and dissolved inorganic carbon inrivers over a range of trophic conditions, and in a mesocosm experiment[J]. Chemical Geology, 2010, 269:22-32. [10] 贾国东, 陈法锦, 邓文锋. 北江河水溶解无机碳同位素的季节变化[J].地球科学(中国地质大学学报),2012,37(2):365-369. [11] Das A, Krishnaswami S,Bhattacharya S K. Carbon isotope ratio of dissolved inorganic carbon (DIC)in rivers draining the Deccan Traps, India:Sources of DIC and their magnitudes[J].Earth and Planetary Science Letters, 2005, 236: 419-429. [12] Górka M, Sauer P E, Lewicka-Szczebak D, et al. Carbon isotope signature of dissolved inorganic carbon (DIC) in precipitationand atmospheric CO2[J].Environmental Pollution, 2011, 159:294-301. [13] 王华, 张春来, 杨会,等.利用稳定同位素技术研究广西桂江流域水体中碳的来源[J]. 地球学报, 2011, 32(6): 691-698. [14] 吴夏, 涂林玲, 杨会,等.水样中溶解性无机碳同位素测试前处理方法对比研究[J]. 岩矿测试, 2013, 32(4): 659-664. [15] Taipale S J, Sonninen E. The Influence of Preservation Method and Time on the δ13C Value of Dissolved Inorganic Carbon inWater Samples [J].Rapid Communications in Mass Spectrometry,2009,23: 2507-2510. [16] Kusakabe M. A simple method for sampling total dissolved carbonate in carbonaterich natural waters and CO2preparation forδ13C determination[J]. Geochemical Journal, 2001, 35:459-464. [17] Li X Z,Liu W G. Effect of preservation on the δ13C value of dissolved inorganic carbon indifferent types of water samples[J].Isotopes in Environmental and Health Studies,2011, 47(3):379-389. [18] Atekwana E A, Krishnamurthy R V. Seasonal variations of dissolved inorganic carbon and δ13C of surface waters: application of a modified gas evolution technique [J]. Journal of Hydrology, 1998, 205(3): 265-278. [19] 唐伟, 曹建华, 杨会,等.外源水对碳酸盐侵蚀速率研究:以桂林毛村地下河为例[J].地球与环境, 2014,42(2):207-212. [20] 杨涛, 蒋少涌, 赖鸣远, 等. 连续流同位素质谱测定水中溶解无机碳含量和碳同位素组成的方法研究[J].地球化学, 2006, 35(6): 675-680. [21] Tang Y, Lian B, Dong H L, et al. Endolitliic bacterial connnmuties in dolomite and limestone rocks from the Nanjiang Canyon in Guizboukarst area (China)[J]. Geomicrobiology Journal, 2012,29:213-225.
点击查看大图
计量
- 文章访问数: 1722
- HTML浏览量: 382
- PDF下载量: 1954
- 被引次数: 0