the Creative Commons Attribution 4.0 License.
the Creative Commons Attribution 4.0 License.
Estuarine flocculation dynamics of organic carbon and metals from boreal acid sulphate soils
Peter Österholm
Eero Asmala
Abstract. Flocculation of riverine dissolved organic matter to the particulate form in estuaries is an important mechanism for capturing dissolved metals to newly formed organic particles, regulating the metal transport to the sea. The process is particularly relevant for rivers draining boreal acid sulphate soils of western Finland, which are known to deliver large amounts of trace metals with detrimental environmental consequences to the recipient estuaries in the eastern Gulf of Bothnia, northern Baltic Sea. This is the first study to investigate dissolved metal (Al, Fe, Mn, Co and Cu) association with flocculating organic particles in the laboratory, by mixing of acidic metal-rich water from acid sulphate soil-impacted rivers and particle-free artificial seawater. Water samples were collected in April 2021 from the Laihianjoki and Sulvanjoki rivers in western Finland. Experiments with an in situ laser diffraction-based particle size distribution sensor and a multiparameter water quality sonde were run to continuously monitor the development of suspended particle pool over the salinity gradient from 0 to 6, corresponding the salinity range observed in these estuarine systems. Flocculator experiments with discrete salinity treatments were carried out to investigate metal behaviour with the collection of flocculated material on glassfibre filters. Filtrate was analysed for coloured dissolved organic matter absorbance and fluorescence for the characterization of potential changes in the organic matter pool during the flocculation process. Retentate on the filter was subjected to persulfate digestion of organic particles and metal oxyhydroxides (pH <2.3), and the digestion supernatants were analysed for metal concentrations. The laboratory experiments showed strong transfer of Al and Fe already at salinity 0–2 to newly formed organic-dominated flocs that were generally larger than 80 µm. Very strong coupling between the decrease in humic-like fluorescence and the increase in organic-bound Al demonstrated that Al transfer to the flocs was stronger than that of Fe. The flocs in the suspended particle pool were complemented by a smaller population of Al and Fe oxyhydroxide-dominated flocculi (median size 11 µm) after pH exceeded ca. 5.5. Cobalt and Mn transfer to the particle pool was weak, although some transfer to Mn oxyhydroxides as well as Co association with the flocs took place. Up to 50 % of Cu was found to be bound to humic substances in the flocs in the river waters and this proportion did not significantly change during mixing with seawater. The findings of this study demonstrate that salinity and pH are important independent but connected controls of the flocculation behavior of dissolved metals from boreal acid sulphate soils and the seaward transport and environmental consequences of the metals in the marine environment.
Joonas Virtasalo et al.
Status: final response (author comments only)
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RC1: 'Comment on bg-2023-53', Anonymous Referee #1, 19 Apr 2023
This work investigated the estuarine flocculation dynamics of organic carbon and metals from boreal acid sulphate soils. This process is critical for the cycling of OM and metals in aquatic environments. I have several major comments for this manuscript and they are listed below.
Specific comments:
- Introduction: previous studies on estuarine flocculation dynamics of organic carbon and metals should be reviewed.
- Line 140: what is the material of the bucket used? Will it adsorb the metals?
- Line 175: why were different instruments adopted to measure these metals?
- Section 4.1: this section is too short and it need to be merged into the other sections.
- Line 205: ‘The initial DOM concentration, as indicated by humic-like fluorescence’, why not directly measure the DOC?
- Line 310: This paragraph could be deleted as it repeated with previous statements.
- Line 490: ‘The results of the flocculator experiments suggest that climate change will increase the transport of Co, Cu and Mn, and to a smaller spatial extent of Al, to the Gulf of Bothnia, while the Fe transport will be less affected.’, how can this conclusion be obtained?
Citation: https://doi.org/10.5194/bg-2023-53-RC1 -
AC1: 'Reply on RC1', Joonas Virtasalo, 29 Apr 2023
Response to Referee #1
We thank Referee #1 for insightful and constructive comments that help improve the manuscript.
Referee has several Specific Comments, which are well justified, and which we will address as follows.
- We will add more discussion about previous studies on the flocculation dynamics of organic carbon and metals in estuaries in Introduction.
- We will add a mention of the bucket material used. Metal flocculation was studied in the flocculator experiment that used glass beakers, so the bucket material is not important for metal adsorption here.
- We will clarify that ICP-OES was used for Al and Fe, and ICP-MS was used for Co, Cu and Mn, for the highest analytical precision.
- Referee #1 is right that the section is only one sentence. However, we find it is good, for the sake of clarity, that the initial compositions of the river waters are considered separately from the experiment results. Because this is a structural matter, we expect Editor to provide us with guidance if necessary.
- Unfortunately, high-frequency optical sensors for determining DOC concentration are not available. Instead, sensors for measuring DOM fluorescence are commercially available and are time-tested technology. DOM fluorescence has been used as a proxy for DOC concentration widely for the past decades, and we will provide relevant references making this point in case.
- Referee #1 is right that the first paragraph of Discussion briefly restates the study aim and methodological approach. The purpose of the paragraph is to help the busy reader who may wish to jump to Discussion section and, therefore, we would like to keep it as it does not take up much space. Because this is a structural matter, we expect Editor to provide us with guidance if necessary.
- Climate change is likely to increase the acidic runoff and metal loading from AS soils to the Gulf of Bothnia as shown by the previous studies. We expect this effect to influence Co, Cu and Mn, which remained largely in the dissolved phase in our experiments and may, therefore, be transported out to the sea. Aluminum and Fe transferred strongly to the particulate phase, so they are expected to be deposited close to the river mouths, which is also confirmed by our previous study of seafloor metal distribution (Virtasalo et al., 2020). We will clarify the reasoning in the paragraph in question.
Kind regards on behalf of all co-authors,
Joonas Virtasalo, Geological Survey of Finland
Citation: https://doi.org/10.5194/bg-2023-53-AC1
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RC2: 'Comment on bg-2023-53', Anonymous Referee #2, 20 Apr 2023
In this study, Virtasao et al. use laboratory experiments to simulate the flocculation of several metals during the drainage of boreal acid sulfate soils into seawater. They used a combination of bucket experiment with continuous, in situ monitoring, and smaller-scale flocculator with more detailed chemical analysis. The results have clear implications for the export of dissolved metals from terrestrial to marine environments.
In general, I found that the results were presented very clearly and the conclusions were well-supported.
My only potential major concern is that the approach to replication needs to be clarified. Line 162 indicates that at the end of the flocculator experiments, suspended material was collected on triplicate filters. As written, this sounds like psuedoreplication (repeated sampling of a single, unreplicated experiment).
It doesn’t appear that the bucket experiments were replicated, which is probably okay given the nature and purpose of these experiments, but that should be clarified in the text.
Other comments:
Lines 87-91: comparison between the two rivers is an important aspect of the study. I suggest adding an object and/or hypothesis related to this comparison.
Lines 134-151: a few details are missing in the setup of the bucket experiment: what was the initial volume of artificial seawater, what was the rate of river water addition, and what was the total duration of the experiment?
Line 335: “already at very low salinities” this sentence is not clear.
Lines 391-402: I don’t think the data demonstrate selective removal of aromatic or humic-like DOM. To demonstrate selectivity you would need to show that these fractions are removed at a higher rate than bulk DOM. Figure 6 shows that aromatics and humics are removed, but not necessarily selectively.
Line 430: “longer experiment time…” this is why it is important to clarify the length of the experiment in the methods section!
Line 436: what is meant by the local background level here?
Figures: panel letters are provided for Figure 1 but not the rest of figures. In general, it would be helpful to include these in all figures and refer to them in the text.
Figure 4: the text indicates these results are from the flocculator experiments but the caption indicates bucket experiment.
Figure 9: several of the data points and error bars seem to indicate a negative percentage of the metals are found in the particulates. How is this possible?
Citation: https://doi.org/10.5194/bg-2023-53-RC2 -
AC2: 'Reply on RC2', Joonas Virtasalo, 29 Apr 2023
Response to Referee #2
We thank Referee #2 for insightful and constructive comments that help improve the manuscript.
Referee’s comments are well justified and we will address them as follows.
Referee #2 correctly points out the difference between experiment replication and analysis replication. We will clarify this in the text.
Other comments.
Lines 87-91: We will include a hypothesis related to the differences between the studied rivers.
Lines 134-151: We will add the missing details about the bucket experiment: the initial volume of river water, the rate of seawater addition, and the total duration of the experiment.
Line 335: We will state the relevant 0-2 salinity range.
Lines 391-402: We have other optical parameters (such as CDOM absorbance at 440 nm and protein-like DOM fluorescence), that show clearly how humic and aromatic compounds are removed most efficiently from the DOM pool. We did not include this data in the original submission, but we will add new figures to supplementary material and elaborate this in the text.
Line 430: We agree. We will clarify the experiment duration in Methods.
Line 436: Referee probably means line 456. The determination of the local background level is described in the paper cited in that sentence. We will add a mention of the approach used in the sentence.
Figures: We will add panel letters to all the figures and use them when referring to the figures.
Figure 4: We thank Referee for pointing this out. The results in the figure indeed are from the flocculator experiment. We will correct this.
Figure 9: We had a blank subtraction error regarding manganese, resulting in values slightly below zero for two samples with very low concentration. This will be corrected, and does not affect the overall results or interpretation. It is correct that when mean values are close to zero, large standard deviation will cause error bars to indicate negative values. This is of course not true, as reviewer correctly points out. This is however a plotting issue, and we will update the figure by removing error bars altogether and showing each observation as points instead of means and error bars.
Kind regards on behalf of all co-authors,
Joonas Virtasalo, Geological Survey of Finland
Citation: https://doi.org/10.5194/bg-2023-53-AC2
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AC2: 'Reply on RC2', Joonas Virtasalo, 29 Apr 2023
Joonas Virtasalo et al.
Joonas Virtasalo et al.
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