Abstract:
This study analyzed the concentrations of low molecular weight organic acids (LMWOAs) of 74 seawater samples from 4 CTD stations and 5 stations at the seawater-sediment interface in the Southern Yap Trench. Their vertical distribution characteristics and their correlations with various seawater chemical and biological parameters in the Southern Yap Trench were preliminarily explored. The results showed that the seawater in the Southern Yap Trench contained two kinds of LMWOAs, acetic acid (AA) and formic acid (FA), with concentration ranges from 0 to 43.64 and 4.88 to 47.89 μmol/L, respectively. Their average concentrations were (19.18±14.15) and (10.03±9.06) μmol/L, respectively. The low concentration area of LMWOAs appeared around the 1 000 m depth. The concentrations of LMWOAs in the seawater at the east and the west side of the trench was significantly lower than those at the central region of the Southern Yap Trench. In the overlying seawater from the sediment-seawater interface, the AA concentrations were higher, with a range of 18.90-40.63 μmol/L and an average concentration of (33.93±8.22) μmol/L; and the FA concentrations were lower, with a range of 5.09-14.82 μmol/L and an average concentration of (8.48±3.87) μmol/L. The concentration of LMWOAs was higher in the overlying seawater on the west side of the Southern Yap Trench and lower in the overlying seawater on the east side of the trench. The proportions of AA, FA and total organic acids (TOA) in the dissolved organic carbon (DOC) in the seawater of the Southern Yap Trench ranged from 0 to 17.92%, 1.10% to 25.66% and 2.33% to 25.66%, respectively; with mean values of 7.52%, 4.10% and 11.62%, respectively, with an extremely significant positive correlation between AA concentrations and DOC concentrations, and an extremely significant positive correlation between FA concentrations and total organic carbon (TOC) concentrations, and the FA concentrations were more significantly affected by the activity of marine microorganisms. The “ funnel effect” caused by the asymmetric “ V”-shaped topography of the Yap Trench facilitated the accumulation of LMWOAs in its bathypelagic and abyssal seawater layers, resulting in higher concentrations of LMWOAs.