Abstract:Bacterial utilization of dissolved organic matter (DOM) in surface waters is closely linked to photochemical transformations of DOM. Photochemically produced reactive oxygen species (ROS) play a central role in many photochemical reactions, but the role of ROS for the photochemical facilitation of bacterial utilization of DOM is previously not known. We exposed lake water with high DOM concentrations to simulated sunlight, with and without the addition of ROS scavengers, and quantified the effect on the produc… Show more
“…Our results conflict with the recent results of Scully et al (2003a), who attempted to study the effect of photoproduced reactive oxygen species on DOM bioavailability. They found that the use of a ROS scavenger (furfuryl alcohol) during sunlight irradiation increased subsequent bacterial growth (measured as cell abundance only) in incubations, relative to samples irradiated without the scavenger.…”
This study examines the importance of several possible mechanisms causing sunlight-mediated changes in the amounts of bacterial utilization and biomass growth on dissolved organic matter (DOM) from allochthonous sources. Our results demonstrate that, while hydroxyl radical reactions with DOM can be an important process increasing its bioavailability, other photoreactions will cause most of the sunlight-induced increases unless hydroxyl production rates are high (ÏŸÏł7 mol L ÏȘ1 d ÏȘ1 ). Low molecular weight carboxylic acids could not account for most of the observed sunlight and hydroxyl-induced increases in DOM bioavailability. Both sunlight and hydroxyl-mediated reactions significantly decreased the bacterial growth efficiency of DOM, indicating that photochemical reactions affect not only the fraction of the total DOM pool available to bacteria on ecologically relevant timescales but also the substrate quality and ultimately the environmental fate of this material. Extrapolation of these results to field conditions suggests that photochemical and biochemical mineralization could be an important sink of DOC and source of bioavailable carbon in the Plum Island estuary during the summer months.Dissolved organic matter (DOM) is a heterogeneous mixture of natural organic compounds that is present in all natural waters. The sources of this carbon in freshwater systems include both in situ biological production (autochthonous sources) and detrital carbon from the surrounding terrestrial watershed (allochthonous sources). At one time, relatively labile autochthonous material was thought to be the dominant source of substrates for bacterial growth in these systems (Cole et al. 1982). More recently, it has become clear that relatively recalcitrant allochthonous (or humic) organic matter can also be a major source of energy and carbon for bacterial growth in many freshwaters (Tranvik 1988;Moran and Hodson 1990).One important environmental factor that may change the utilization of DOM by bacteria is exposure to light. A variety of studies have shown that irradiation of DOM by natural and/or simulated sunlight can increase both the amount of DOM that is susceptible to bacterial utilization and the abil-
AcknowledgmentsThis research was funded by the National Science Foundation (Chemical Oceanography, grant OCE-9819089) and by postdoctoral fellowships to M.J.P. and S.B. through the National Science Foundation (Earth Sciences) and the Knut and Alice Wallenberg Foundation, respectively. The authors thank Phil Gschwend for the use of the HPLC equipment; Bob Chen, Chuck Hopkinson, and Pete Raymond for assistance in field sampling; Joe Vallino for background information on the Parker River; and Barbara Southworth for lab assistance and estimates of hydroxyl radical production rates.
“…Our results conflict with the recent results of Scully et al (2003a), who attempted to study the effect of photoproduced reactive oxygen species on DOM bioavailability. They found that the use of a ROS scavenger (furfuryl alcohol) during sunlight irradiation increased subsequent bacterial growth (measured as cell abundance only) in incubations, relative to samples irradiated without the scavenger.…”
This study examines the importance of several possible mechanisms causing sunlight-mediated changes in the amounts of bacterial utilization and biomass growth on dissolved organic matter (DOM) from allochthonous sources. Our results demonstrate that, while hydroxyl radical reactions with DOM can be an important process increasing its bioavailability, other photoreactions will cause most of the sunlight-induced increases unless hydroxyl production rates are high (ÏŸÏł7 mol L ÏȘ1 d ÏȘ1 ). Low molecular weight carboxylic acids could not account for most of the observed sunlight and hydroxyl-induced increases in DOM bioavailability. Both sunlight and hydroxyl-mediated reactions significantly decreased the bacterial growth efficiency of DOM, indicating that photochemical reactions affect not only the fraction of the total DOM pool available to bacteria on ecologically relevant timescales but also the substrate quality and ultimately the environmental fate of this material. Extrapolation of these results to field conditions suggests that photochemical and biochemical mineralization could be an important sink of DOC and source of bioavailable carbon in the Plum Island estuary during the summer months.Dissolved organic matter (DOM) is a heterogeneous mixture of natural organic compounds that is present in all natural waters. The sources of this carbon in freshwater systems include both in situ biological production (autochthonous sources) and detrital carbon from the surrounding terrestrial watershed (allochthonous sources). At one time, relatively labile autochthonous material was thought to be the dominant source of substrates for bacterial growth in these systems (Cole et al. 1982). More recently, it has become clear that relatively recalcitrant allochthonous (or humic) organic matter can also be a major source of energy and carbon for bacterial growth in many freshwaters (Tranvik 1988;Moran and Hodson 1990).One important environmental factor that may change the utilization of DOM by bacteria is exposure to light. A variety of studies have shown that irradiation of DOM by natural and/or simulated sunlight can increase both the amount of DOM that is susceptible to bacterial utilization and the abil-
AcknowledgmentsThis research was funded by the National Science Foundation (Chemical Oceanography, grant OCE-9819089) and by postdoctoral fellowships to M.J.P. and S.B. through the National Science Foundation (Earth Sciences) and the Knut and Alice Wallenberg Foundation, respectively. The authors thank Phil Gschwend for the use of the HPLC equipment; Bob Chen, Chuck Hopkinson, and Pete Raymond for assistance in field sampling; Joe Vallino for background information on the Parker River; and Barbara Southworth for lab assistance and estimates of hydroxyl radical production rates.
“…For example, Febria et al (2006) found that the production of hydrogen peroxide (H 2 O 2 ) in two delta lakes that were also sampled herein (CON and TK) outpaced the rate of removal during a period of uninterrupted sunshine in 2004, leading to an accumulation of H 2 O 2 within the water columns. Production of ROS during previous studies of DOM photodegradation has been observed to inhibit community-level rates of carbon production (Scully et al 2003;Anesio et al 2005;Glaeser et al 2014) and result in changes in bacterial community composition (Glaeser et al 2010(Glaeser et al , 2014. Further, in a prior study by Lund and Hongve (1994), declines in BA of up to 60% were observed after only an hour when UV-irradiated DOM was mixed with bacteria.…”
Section: Photoreactivity Of Mackenzie River Freshet Dommentioning
confidence: 93%
“…These by-products of the photodegradation process are short-lived, but nevertheless inhibit bacterial growth and production (Lund and Hongve 1994;Henle and Linn 1997;Anesio et al 2005). To some extent, therefore, irradiation of DOM by sunlight simultaneously stimulates and inhibits heterotrophic bacterial production (BP) (Scully et al 2003;Ruiz-Gonzalez et al 2013), leading to complex interactions that can result in enhanced, negative, mixed, or no effect on bacterial community metabolism (Lonborg et al 2016). In addition, the bacterial community composition may be altered either by exposure to ROS (Glaeser et al 2010;Glaeser et al 2014) or in response to the increased lability of the pool of DOM substrate (Judd et al 2007;Piccini et al 2009;Paul et al 2012;Ward et al 2017), giving rise to a species assemblage that is better suited to the ambient conditions.…”
“…Indeed, CDOM protects the aquatic biota from exposure to UV radiation [2], which can be very significant during summertime in CDOM-poor environments such as mountain lakes located above the tree-line [3]. Another important issue is that radiation absorption by CDOM yields reactive species, such as âą OH, 1 O 2 and the triplet states 3 CDOM*, which can be involved into transformation of dissolved compounds, including xenobiotics, as well as into the photoprocessing of CDOM itself [4][5][6][7].…”
Water samples from subterranean systems (caves and abandoned mines) and from lake epilimnion were optically characterised and irradiated under simulated sunlight, to study the effects that sunlight exposure before sampling may have on the properties and photochemical behaviour of chromophoric dissolved organic matter (CDOM). Differently from lakes, absorption spectra of subterranean water samples showed variations from the typically observed, featureless exponential decay of absorbance vs. wavelength. Fluorescence spectra suggested that, compared to lake water and with a single exception, subterranean water had higher proportion of aquagenic/autochthonous CDOM (e.g. proteinaceous material) compared to pedogenic/allochthonous one (e.g. humic and fulvic substances). Irradiation of subterranean water produced very significant spectral changes, and finally yielded lakewater-like exponential absorption spectra. In contrast, irradiation of lake water produced photobleaching (decrease of the absorbance) but the shapes of absorption spectra underwent very limited variations. Tyrosine and humic acids were irradiated as proxies of the CDOM fractions identified by fluorescence. Irradiated tyrosine underwent a significant increase of the absorbance and finally yielded an exponential absorption spectrum, with close resemblance to the behaviour of a protein-rich and humic-poor sample of subterranean water. In contrast, irradiated humic acids underwent photobleaching in a similar way as lake water, but they retained their typical exponential spectrum. The present findings suggest that exposure of CDOM to sunlight may play a key role in shaping the exponential absorption spectra that are typically observed in surface waters.3
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