File Download
There are no files associated with this item.
Links for fulltext
(May Require Subscription)
- Publisher Website: 10.1016/j.ecss.2010.02.018
- Scopus: eid_2-s2.0-77951024048
- WOS: WOS:000278245900014
- Find via
Supplementary
- Citations:
- Appears in Collections:
Article: Bulk organic δ13C and C/N as indicators for sediment sources in the Pearl River delta and estuary, southern China
Title | Bulk organic δ13C and C/N as indicators for sediment sources in the Pearl River delta and estuary, southern China | ||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Authors | |||||||||||||||
Issue Date | 2010 | ||||||||||||||
Publisher | Academic Press. The Journal's web site is located at http://www.elsevier.com/locate/ecss | ||||||||||||||
Citation | Estuarine, Coastal And Shelf Science, 2010, v. 87 n. 4, p. 618-630 How to Cite? | ||||||||||||||
Abstract | Preservation of organic matter in estuarine and coastal areas is an important process in the global carbon cycle. This paper presents bulk δ13C and C/N of organic matter from source to sink in the Pearl River catchment, delta and estuary, and discusses the applicability of δ13C and C/N as indicators for sources of organic matter in deltaic and estuarine sediments. In addition to the 91 surface sediment samples, other materials collected in this study cover the main sources of organic material to estuarine sediment. These are: terrestrial organic matter (TOM), including plants and soil samples from the catchment; estuarine and marine suspended particulate organic carbon (POC) from both summer and winter. Results show that the average δ13C of estuarine surface sediment increases from -25.0 ± 1.3‰ in the freshwater environment to -21.0 ± 0.2‰ in the marine environment, with C/N decreasing from 15.2 ± 3.3 to 6.8 ± 0.2. In the source areas, C3 plants have lower δ13C than C4 plants (-29.0 ± 1.8‰ and -13.1 ± 0.5‰ respectively). δ13C increases from -28.3 ± 0.8‰ in the forest soil to around -24.1‰ in both riverbank soil and mangrove soil due to increasing proportion of C4 grasses. The δ13CPOC increases from -27.6 ± 0.8‰ in the freshwater areas to -22.4 ± 0.5‰ in the marine-brackish-water areas in winter, and ranges between -24.0‰ in freshwater areas and -25.4‰ in brackish-water areas in summer. Comparison of the δ13C and C/N between the sources and sink indicates a weakening TOM and freshwater POC input in the surface sedimentary organic matter seawards, and a strengthening contribution from the marine organic matter. Thus we suggest that bulk organic δ13C and C/N analysis can be used to indicate sources of sedimentary organic matter in estuarine environments. Organic carbon in surface sediments derived from anthropogenic sources such as human waste and organic pollutants from industrial and agricultural activities accounts for less than 10% of the total organic carbon (TOC). Although results also indicate elevated δ13C of sedimentary organic matter due to some agricultural products such as sugarcane, C3 plants are still the dominant vegetation type in this area, and the bulk organic δ13C and C/N is still an effective indicator for sources of organic matter in estuarine sediments. © 2010 Elsevier Ltd. All rights reserved. | ||||||||||||||
Persistent Identifier | http://hdl.handle.net/10722/151303 | ||||||||||||||
ISSN | 2023 Impact Factor: 2.6 2023 SCImago Journal Rankings: 0.760 | ||||||||||||||
ISI Accession Number ID |
Funding Information: This research was part of the PhD project sponsored by NERC/EPSRC (UK) through the Dorothy Hodgkin Postgraduate Award (to FY). This research was also supported by the University of Durham through a special research grant (to YZ), the NERC (UK) Radiocarbon Laboratory Steering Committee (1150.1005) (to YZ) and the NERC Isotope Geosciences Facilities Steering Committee through the organic isotope analyses awarded (IP/883/1105) (to YZ). We also acknowledge support from the Quaternary Research Association, the Durham Geography Graduates Association, University College of Durham University and the British Sediment Research Group for grants awarded to FY to complete fieldwork and laboratory visits. This research was also supported by the Research Grants Council of the Hong Kong SAR through research grants HKU7058/06P and HKU7052/08P (to W.W.-S. Yim). The authors also thank the director of the Environmental Protection Department, Hong Kong SRA for the collection of surface sediment samples and water salinity from the Hong Kong area. | ||||||||||||||
References |
DC Field | Value | Language |
---|---|---|
dc.contributor.author | Yu, F | en_HK |
dc.contributor.author | Zong, Y | en_HK |
dc.contributor.author | Lloyd, JM | en_HK |
dc.contributor.author | Huang, G | en_HK |
dc.contributor.author | Leng, MJ | en_HK |
dc.contributor.author | Kendrick, C | en_HK |
dc.contributor.author | Lamb, AL | en_HK |
dc.contributor.author | Yim, WWS | en_HK |
dc.date.accessioned | 2012-06-26T06:20:19Z | - |
dc.date.available | 2012-06-26T06:20:19Z | - |
dc.date.issued | 2010 | en_HK |
dc.identifier.citation | Estuarine, Coastal And Shelf Science, 2010, v. 87 n. 4, p. 618-630 | en_HK |
dc.identifier.issn | 0272-7714 | en_HK |
dc.identifier.uri | http://hdl.handle.net/10722/151303 | - |
dc.description.abstract | Preservation of organic matter in estuarine and coastal areas is an important process in the global carbon cycle. This paper presents bulk δ13C and C/N of organic matter from source to sink in the Pearl River catchment, delta and estuary, and discusses the applicability of δ13C and C/N as indicators for sources of organic matter in deltaic and estuarine sediments. In addition to the 91 surface sediment samples, other materials collected in this study cover the main sources of organic material to estuarine sediment. These are: terrestrial organic matter (TOM), including plants and soil samples from the catchment; estuarine and marine suspended particulate organic carbon (POC) from both summer and winter. Results show that the average δ13C of estuarine surface sediment increases from -25.0 ± 1.3‰ in the freshwater environment to -21.0 ± 0.2‰ in the marine environment, with C/N decreasing from 15.2 ± 3.3 to 6.8 ± 0.2. In the source areas, C3 plants have lower δ13C than C4 plants (-29.0 ± 1.8‰ and -13.1 ± 0.5‰ respectively). δ13C increases from -28.3 ± 0.8‰ in the forest soil to around -24.1‰ in both riverbank soil and mangrove soil due to increasing proportion of C4 grasses. The δ13CPOC increases from -27.6 ± 0.8‰ in the freshwater areas to -22.4 ± 0.5‰ in the marine-brackish-water areas in winter, and ranges between -24.0‰ in freshwater areas and -25.4‰ in brackish-water areas in summer. Comparison of the δ13C and C/N between the sources and sink indicates a weakening TOM and freshwater POC input in the surface sedimentary organic matter seawards, and a strengthening contribution from the marine organic matter. Thus we suggest that bulk organic δ13C and C/N analysis can be used to indicate sources of sedimentary organic matter in estuarine environments. Organic carbon in surface sediments derived from anthropogenic sources such as human waste and organic pollutants from industrial and agricultural activities accounts for less than 10% of the total organic carbon (TOC). Although results also indicate elevated δ13C of sedimentary organic matter due to some agricultural products such as sugarcane, C3 plants are still the dominant vegetation type in this area, and the bulk organic δ13C and C/N is still an effective indicator for sources of organic matter in estuarine sediments. © 2010 Elsevier Ltd. All rights reserved. | en_HK |
dc.language | eng | en_US |
dc.publisher | Academic Press. The Journal's web site is located at http://www.elsevier.com/locate/ecss | en_HK |
dc.relation.ispartof | Estuarine, Coastal and Shelf Science | en_HK |
dc.title | Bulk organic δ13C and C/N as indicators for sediment sources in the Pearl River delta and estuary, southern China | en_HK |
dc.type | Article | en_HK |
dc.identifier.email | Zong, Y: yqzong@hku.hk | en_HK |
dc.identifier.email | Yim, WWS: wwsyim@hku.hk | en_HK |
dc.identifier.authority | Zong, Y=rp00846 | en_HK |
dc.identifier.authority | Yim, WWS=rp01746 | en_HK |
dc.description.nature | link_to_subscribed_fulltext | en_US |
dc.identifier.doi | 10.1016/j.ecss.2010.02.018 | en_HK |
dc.identifier.scopus | eid_2-s2.0-77951024048 | en_HK |
dc.identifier.hkuros | 171036 | - |
dc.relation.references | http://www.scopus.com/mlt/select.url?eid=2-s2.0-77951024048&selection=ref&src=s&origin=recordpage | en_HK |
dc.identifier.volume | 87 | en_HK |
dc.identifier.issue | 4 | en_HK |
dc.identifier.spage | 618 | en_HK |
dc.identifier.epage | 630 | en_HK |
dc.identifier.isi | WOS:000278245900014 | - |
dc.publisher.place | United Kingdom | en_HK |
dc.identifier.scopusauthorid | Yu, F=35747418400 | en_HK |
dc.identifier.scopusauthorid | Zong, Y=7005203454 | en_HK |
dc.identifier.scopusauthorid | Lloyd, JM=7402365382 | en_HK |
dc.identifier.scopusauthorid | Huang, G=7403425099 | en_HK |
dc.identifier.scopusauthorid | Leng, MJ=7006497331 | en_HK |
dc.identifier.scopusauthorid | Kendrick, C=35210597000 | en_HK |
dc.identifier.scopusauthorid | Lamb, AL=7102445484 | en_HK |
dc.identifier.scopusauthorid | Yim, WWS=7007024728 | en_HK |
dc.identifier.citeulike | 6834646 | - |
dc.identifier.issnl | 0272-7714 | - |