Jaffrennou C, Stephan L, Giamarchi P, Cabon J Y, Burel-Deschamps L, Bautin F
Chemistry Department, University of Brest, Brest, France.
J Fluoresc. 2007 Sep;17(5):564-72. doi: 10.1007/s10895-007-0216-y. Epub 2007 Jun 29.
Whenever immersed in seawater after a collier accident, a fossil fuel such as coal could become a source of pollution to the marine environment. To study the effect of such a contamination, four coal samples from different origins were used. A first analysis on those coals enabled us to determine the content of polycyclic aromatic hydrocarbons. Seawater was then mixed with coal to study the organic matter released from coal into seawater. Fluorescence was used for its sensitivity to aromatic compounds, with the additional purpose of evaluating the relevance of using an immersed fluorescence probe to monitor water pollution. Excitation-emission matrices were recorded and the excitation-emission wavelength range corresponding to the highest fluorescence intensity was 230 nm/[370 nm; 420 nm]. The samples with coal happened to fluoresce more than the coal-free samples, the difference depending on the coal origin. The fluorescence intensity increased with coal mass, up to some limit. The particle size also influenced the fluorescence intensity, the finest particles releasing more fluorescing substances, due to their higher exchange surface. When seawater percolated through coal, the samples fluoresced highly at the beginning, and then the fluorescence intensity decreased and reached the seawater level. However, even with a 10 ns acquisition time shift, the fluorescence spectra were not specific enough to show the presence of PAHs in the samples, which were too diluted to be detected, whenever released from coal into seawater. The lifetimes of the seawater and of the coal samples were respectively 4.7 and 3.8 ns, indicating that the substances released from coal mainly consisted of short-lived fluorescing substances, such as natural humic or fulvic substances. Consequently, the presence of coal does not seem to be too detrimental to the marine environment, and a direct fluorescence probe could be used to monitor the seawater organic charge increase due to the immersion of coal in seawater.
在煤矿事故后,每当煤炭等化石燃料浸入海水中时,都可能成为海洋环境污染的一个来源。为了研究这种污染的影响,使用了来自不同产地的四个煤样。对这些煤进行的首次分析使我们能够确定多环芳烃的含量。然后将海水与煤混合,以研究从煤中释放到海水中的有机物。由于荧光对芳香族化合物敏感,因此还用于评估使用浸入式荧光探头监测水污染的相关性。记录了激发-发射矩阵,对应于最高荧光强度的激发-发射波长范围为230 nm/[370 nm;420 nm]。含有煤的样品碰巧比不含煤的样品荧光更强,差异取决于煤的产地。荧光强度随着煤的质量增加而增加,直至达到某个极限。颗粒大小也影响荧光强度,最细的颗粒由于其更大的交换表面而释放出更多的荧光物质。当海水渗过煤时,样品一开始荧光很强,然后荧光强度下降并达到海水水平。然而,即使采集时间偏移10 ns,荧光光谱也不够特异,无法显示样品中多环芳烃的存在,因为从煤释放到海水中的多环芳烃被稀释得太厉害而无法检测到。海水和煤样的寿命分别为4.7 ns和3.8 ns,这表明从煤中释放的物质主要由短寿命的荧光物质组成,如天然腐殖质或富里酸物质。因此,煤的存在似乎对海洋环境没有太大危害,并且可以使用直接荧光探头来监测由于煤浸入海水中而导致的海水有机负荷增加。