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seaward enrichment <strong>of</strong> d 15 N value could also be seen. Nevertheless,<br />

similar to stable <strong>carbon</strong> isotope, d 15 N <strong>in</strong> <strong>surface</strong> sediments <strong>of</strong><br />

coastal Bohai Bay has more complex spatial fluctuations (Fig. 8),<br />

which <strong>in</strong>dicates that additional factors have significant <strong>in</strong>fluences<br />

on the distributions <strong>of</strong> d 15 N <strong>in</strong> sedimentary <strong>organic</strong> matter. Nitrogen<br />

isotopic compositions could be easily modified by a series <strong>of</strong><br />

complex biogeochemical processes on some time scales. Dynamic<br />

cycl<strong>in</strong>g <strong>of</strong> <strong>nitrogen</strong> is subject to k<strong>in</strong>etic isotope fraction effects<br />

especially dur<strong>in</strong>g the biogenic transformation <strong>and</strong> recycl<strong>in</strong>g <strong>of</strong> dissolved<br />

<strong>and</strong> particulate <strong>nitrogen</strong> compounds (Cifuentes et al., 1988,<br />

1996; Wu et al., 2003). Liu et al. (2006) reported that heavier d 15 N<br />

values significantly corresponded with higher C/N ratios <strong>in</strong> <strong>in</strong>tertidal<br />

sediments from the Yangtze Estuary, Ch<strong>in</strong>a, <strong>and</strong> the authors<br />

ascribed this relationship to the result <strong>of</strong> <strong>organic</strong> matter diagenesis.<br />

It has also been reported that <strong>nitrogen</strong> isotopic enrichment<br />

dur<strong>in</strong>g <strong>organic</strong> decomposition was relative to heterotrophic microorganisms<br />

(Macko <strong>and</strong> Estep, 1984). The effects <strong>of</strong> heterotrophs<br />

were documented by Caraco et al. (1998) who found that the<br />

d 15 N <strong>of</strong> microbially reworked terrestrial particulates <strong>in</strong>creased<br />

from 4‰ to 9‰. As microbial m<strong>in</strong>eralization proceeds, the total<br />

amount <strong>of</strong> <strong>nitrogen</strong> present <strong>in</strong> the <strong>organic</strong> substrates reduces with<br />

14 N be<strong>in</strong>g preferentially lost. Consequently, higher decomposed <strong>organic</strong><br />

matter will conta<strong>in</strong> little <strong>nitrogen</strong> enriched <strong>in</strong> d 15 N. However,<br />

it is shown that, like d 13 C, d 15 N aga<strong>in</strong>st C/N ratios also has no pronounced<br />

relationship <strong>in</strong> this study (Fig. 9b). Although d 13 C <strong>and</strong><br />

d 15 N <strong>of</strong> sediments can be modified by microbial rearrangement,<br />

isotopic fractionation specifically associated with early diagenesis<br />

is negligible (Lehmann et al., 2004) <strong>and</strong> the isotopic composition<br />

<strong>of</strong> sedimentary <strong>organic</strong> matter is fairly conservative, mirror<strong>in</strong>g<br />

the isotopic signatures <strong>of</strong> the sources (Di Leonardo et al., 2009).<br />

Thus, it implies that <strong>organic</strong> matter <strong>in</strong> <strong>surface</strong> sediments <strong>of</strong> the<br />

studied area is relatively fresh <strong>and</strong> the <strong>nitrogen</strong> cycl<strong>in</strong>g <strong>in</strong> early<br />

diagenesis processes has no obvious effect on the <strong>nitrogen</strong> isotopic<br />

composition.<br />

3.2.4. Contribution <strong>of</strong> terrigenous <strong>and</strong> autogenous <strong>organic</strong> <strong>carbon</strong><br />

To assess the relative proportions <strong>of</strong> terrigenous <strong>and</strong> mar<strong>in</strong>e<br />

autogenous <strong>organic</strong> <strong>carbon</strong> (AOC) present <strong>in</strong> the sediments, a simple<br />

d 13 C-based two end-member mix<strong>in</strong>g model based on the work<br />

<strong>of</strong> Calder <strong>and</strong> Parker (1968) <strong>and</strong> adopted by other researchers such<br />

as Schlunz et al. (1999) <strong>and</strong> Hu et al. (2006) was applied to this<br />

area. We took 27.0‰ as the d 13 C value <strong>of</strong> terrestrial end-member<br />

(d 13 Cterrestrial) based on the d 13 C value <strong>of</strong> coastal sediments <strong>of</strong> Bohai<br />

Bay. This value is close to that <strong>of</strong> C 3 plants. Likewise, we assumed<br />

20.5‰ as the d 13 C value <strong>of</strong> mar<strong>in</strong>e end-member (d 13 Cmar<strong>in</strong>e) (Jia<br />

<strong>and</strong> Peng, 2003). The calculation <strong>of</strong> terrestrial <strong>organic</strong> <strong>carbon</strong> contribution<br />

(f) was ga<strong>in</strong>ed by the follow<strong>in</strong>g equation:<br />

f ð%Þ ¼ðd 13 Cmar<strong>in</strong>e d 13 CmeasuredÞ=ðd 13 Cmar<strong>in</strong>e d 13 CterrestrialÞ 100<br />

AOC concentration (%)<br />

2.0<br />

1.8<br />

1.6<br />

1.4<br />

1.2<br />

1.0<br />

0.8<br />

0.6<br />

0.4<br />

0.2<br />

0.0<br />

M-1<br />

M-2<br />

M-3<br />

M-4<br />

M-5<br />

Then the contribution <strong>of</strong> mar<strong>in</strong>e algae (f 0 ) to the TOC could be<br />

estimated by the follow<strong>in</strong>g expression:<br />

X. Gao et al. / Mar<strong>in</strong>e Pollution Bullet<strong>in</strong> 64 (2012) 1148–1155 1153<br />

Terrestrial Autogenous<br />

K-1<br />

K-2<br />

K-3<br />

K-4<br />

K-5<br />

K-6<br />

K-7<br />

K-8<br />

Station ID<br />

T-1<br />

T-2<br />

T-3<br />

T-4<br />

T-5<br />

f 0 ð%Þ ¼100 f<br />

The content <strong>of</strong> AOC was obta<strong>in</strong>ed from the follow<strong>in</strong>g equation:<br />

AOC ¼ TOC f 0 %<br />

Consider<strong>in</strong>g the obvious anthropogenic disturbance to the <strong>organic</strong><br />

matter composition <strong>in</strong> the river<strong>in</strong>e region as discussed above,<br />

only the data <strong>of</strong> the mar<strong>in</strong>e region were calculated. As shown <strong>in</strong><br />

Fig. 10, the AOC concentrations generally descend seaward along<br />

transects M, K <strong>and</strong> U. This might be expla<strong>in</strong>ed by the flourish <strong>of</strong><br />

mar<strong>in</strong>e primary producers respond<strong>in</strong>g to the <strong>in</strong>put <strong>of</strong> nutrients<br />

from l<strong>and</strong> to this area by surround<strong>in</strong>g rivers. The result<strong>in</strong>g estimates<br />

for the contribution <strong>of</strong> the terrestrial <strong>and</strong> autogenous <strong>organic</strong><br />

<strong>carbon</strong> <strong>in</strong> mar<strong>in</strong>e sediments <strong>of</strong> coastal Bohai Bay are also<br />

summarized <strong>in</strong> Fig. 10. Tak<strong>in</strong>g as a whole, the <strong>surface</strong> sediments<br />

<strong>in</strong> the mar<strong>in</strong>e region <strong>of</strong> coastal Bohai Bay are dom<strong>in</strong>ated by mar<strong>in</strong>e<br />

derived <strong>organic</strong> <strong>carbon</strong>, which on average accounts for 62 ± 11% <strong>of</strong><br />

their TOC concentrations. Although the highest proportion <strong>of</strong> AOC<br />

up to 87% <strong>of</strong> TOC is recorded at site M-5, the contribution <strong>of</strong> AOC to<br />

TOC <strong>in</strong> nearly all samples from the northern two transects is lower<br />

than that <strong>in</strong> a majority <strong>of</strong> samples from the southern two transects.<br />

Except for site T-2, AOC accounts for 67–79% <strong>of</strong> TOC <strong>in</strong> <strong>surface</strong> sediments<br />

from the rest sites <strong>of</strong> transects T <strong>and</strong> U, while it accounts for<br />

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