L. Zhang's research while affiliated with Xiamen University and other places

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Publications (1)


Special guest paper
  • Article

April 1995

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17 Reads

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203 Citations

Marine Pollution Bulletin

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L. Xu

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L. Zhang

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[...]

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T. S. M. Wan

Sediment samples were collected from Xiamen Harbour, the People's Republic of China, and Victoria Harbour, Hong Kong, and were analysed for non-aromatic hydrocarbons (NAHs), long-chain linear alkylbenzenes (LABs), polycyclic aromatic hydrocarbons (PAHs), organochlorine pesticides (HCHs, DDTs) and polychlorinated biphenyls (PCBs). In Xiamen Harbour, concentrations varied from 3.1–32.9 μg g−1 for NAH, 2.9–61 μg g−1 for PAHs, 0.14–1.12 ng g−1 for HCHs, 4.45–311 ng g−1 for DDTs and 0.05–7.24 ng g−1 for PCBs. In Victoria Harbour, the concentration ranges of those pollutants were 60–646 μg g−1, 1.2–14.0 μg g−1, undetectable to 2.3 ng g−1, 1.38–30.3 ng g−1 and 3.2–16.0 ng g−1, respectively. The distribution patterns of various organic pollutants in the sediments are discussed. The NAH levels present in Victoria Harbour indicated that there was significant petroleum contamination in the harbour. Xiamen Harbour was slightly more contaminated by DDTs. LABs could be used as synthetic detergent tracers. From the data available, it is concluded that Victoria Harbour is more polluted than Xiamen Harbour. The structure of the benthic community provides further evidence to support this claim.

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Citations (1)


... Sewage is a large source of pollutants and pathogens (Kennish, 1997), and molecular markers of sewage, i.e., sewage markers, are important. Coprostanol, derived from human feces (Leeming et al., 1996), and linear alkylbenzenes (LABs) contained in synthetic detergents (Takada and Ishiwatari, 1987) have been used as sewage markers since the 1960s (e.g., Murtaugh and Bunch, 1967;Goodfellow et al., 1977;Readman et al., 1986;Leeming et al., 1996;Peng et al., 2005;Martins et al., 2014) and 1980s (e.g., Eganhouse et al., 1983;Takada and Ishiwatari, 1987;Hong et al., 1995;Gustafsson et al., 2001;Ni et al, 2009;Wang et al., 2012;Thomes et al., 2019;Alkhadher et al., 2023), respectively. Although coprostanol and LABs are persistent, they can be removed through sewage treatment and adsorption by soil because of their hydrophobic and particle-reactive nature. ...

Reference:

Artificial sweeteners in surface waters from Asian, African and Middle Eastern countries: Utility as molecular markers and water pollution status in 2010–2019
Special guest paper
  • Citing Article
  • April 1995

Marine Pollution Bulletin