Tropical Research Centre for Oceanography, Environment and Natural Resources, The State University of Zanzibar, P.O Box 146, Zanzibar, Tanzania.
Faculty of Science and Marine Environment, Universiti Malaysia Terengganu, 21030 Kuala Nerus, Terengganu, Malaysia.
Environ Sci Pollut Res Int. 2021 Oct;28(37):52247-52257. doi: 10.1007/s11356-021-14424-1. Epub 2021 May 18.
Irgarol 1051 and diuron are photosystem II inhibitors in agricultural activities and antifouling paints in the shipping sector. This study focused on three major ports (western, southern, and eastern) surrounding Peninsular Malaysia to construct the distribution of both biocides on the basis of the seasonal and geographical changes. Surface seawater samples were collected from November 2011 to April 2012 and pretreated using the solid-phase extraction technique followed by quantification with GC-MS and LC-MS-MS for Irgarol 1051 and diuron, respectively. Generally, the distribution of Irgarol 1051 was lowest during November 2011 and highest during April 2012, and similar patterns were observed at all ports, whereas the distribution of diuron was rather vague. The increasing pattern of Irgarol 1051 from time to time is probably related to its accumulation in the seawater as a result of its half-life and consistent utilization. On the basis of the discriminant analysis, the temporal distribution of Irgarol 1051 varied at Klang North Port, Klang South Port, and Pasir Gudang Port, whereas diuron was temporally varied only at Kemaman Port. Furthermore, Irgarol 1051 was spatially varied during November 2011, whereas diuron did not show any significant changes throughout all sampling periods. Ecological risk assessment exhibited a high risk for diuron and Irgarol 1051, but Irgarol 1051 should be of greater concern because of its higher risk compared to that of diuron. Thus, it is recommended that the current Malaysian guidelines and regulations of biocide application should be reevaluated and improved to protect the ecosystem, as well as to prevent ecological risks to the aquatic environment.
依绿草 1051 和敌草隆是农业活动中抑制光系统 II 的物质,也是航运业中防污漆的成分。本研究集中在马来西亚半岛周围的三个主要港口(西部、南部和东部),根据季节和地理位置的变化,构建这两种杀生物剂的分布情况。2011 年 11 月至 2012 年 4 月期间采集了表层海水样本,使用固相萃取技术进行预处理,然后分别使用 GC-MS 和 LC-MS-MS 对依绿草 1051 和敌草隆进行定量。一般来说,依绿草 1051 的分布在 2011 年 11 月最低,2012 年 4 月最高,所有港口都呈现出类似的模式,而敌草隆的分布则较为模糊。依绿草 1051 不时增加的模式可能与其半衰期和持续利用有关,导致其在海水中积累。根据判别分析,依绿草 1051 在巴生北港、巴生南港和巴西古当港的时间分布有所不同,而敌草隆仅在关丹港存在时间差异。此外,依绿草 1051 在 2011 年 11 月存在空间差异,而敌草隆在整个采样期间没有显示出任何显著变化。生态风险评估显示敌草隆和依绿草 1051 的风险较高,但依绿草 1051 的风险更高,应引起更大的关注。因此,建议重新评估和改进马来西亚目前的杀生物剂应用指南和法规,以保护生态系统,防止水生环境面临生态风险。