Detection and ecological threats of PSII herbicide diuron on coral reefs around the Ryukyu Archipelago, Japan.
Detection and ecological threats of PSII herbicide diuron on coral reefs around the Ryukyu Archipelago, Japan.
复制标题
PSII 除草剂敌草隆对日本琉球群岛周围珊瑚礁的检测和生态威胁。
DOI:
10.1016/j.marpolbul.2009.09.010
复制
发表时间:
2009
影响因子:
5.8
通讯作者:
T. Oomori
中科院分区:
文献类型:
--
作者:
M. Sheikh;H. Fujimura;T. Miyagi;Y. Uechi;T. Yokota;S. Yasumura;T. Oomori
Coral reefs are mostly found in shallow coastlines of tropical and subtropical areas (Suzuki and Kawahata, 2003; Inoue et al., 2004). They are among of the world’s most valuable natural resources that provide food, medicines, ecological services and source of income for the coastal residences. However, in recent years, the sustainability of the coral reef ecosystems has been thrown into doubt by a number of threats including marine pollution, global environmental changes, outbreaks of crown-of-thorns starfish (Hughes et al., 2003) and disease (Santavy and Peters, 1997). It has been estimated that about 27% of the world’s coral reefs have already been lost and 31% have been projected to be degraded by 2030 (Wilkinson, 2000). More integrated efforts and new conservation approaches are necessary to minimize the threats facing coral reefs in future (Downs et al., 2005). Ryukyu Archipelago composed of Okinawa Islands has a unique marine ecological importance hosting about 90% of Japan’s coral reefs. However, the health of coral reefs around the Ryukyu Archipelago steadily deteriorates due hazardous chemical pollution from domestic, agricultural, industrial and shipping activities (Kitada et al., 2008; Sheikh et al., 2007; Tanabe et al., 2008), terrestrial run-off (Omija, 2004; Sakai, 2004; West and van Woesik, 2001), developmental projects (Nakano, 2004) and natural disturbance (Sano, 2001).Diuron,[N0-(3, 4-dichlorophenyl)-N, N-dimethyl-urea] is a photosystem II (PSII) herbicide derived from urea. It is considered a priority hazardous substance by the European Commission (Malato et al., 2002). Countries including the UK, Sweden, Denmark and France have restricted the use of diuron in antifouling paints (Konstantinou and Albanis, 2004; Giacomazzi and Cochet, 2004). In Japan, diuron has been extensively used in antifouling paints in shipping and agricultural activities (Okamura et al., 2003). In 2004 alone, around 11 tons of diuron was used for agricultural purposes in the Okinawa Prefecture, which was the highest amount of this toxic substance used in Japan outside of the Tokyo metropolitan region. In addition, the urban areas of Okinawa mainland, apply a significant amount of diuron as a weed control (Kitada, 2007).