Two treatment methods on Ulva prolifera bloom result in distinctively different ecological effects in coastal environment

Green tides Ulva prolifera have broken out in the Yellow Sea for more than 10 years, becoming a periodic ecological disaster. The largest-ever green tide that occurred in 2021 promoted innovation in treatment methods. Different from the traditional harvest-disposal method, a microbial complex formulation was firstly sprayed on the harvest U. prolifera that promotes rapid degradation, and then fermented and disposed into the sea. At present, little was known about the ecological effects of those different treatment methods. In order to examine this hypothesis, we run an in-lab incubation of 60 days to simulate the two methods to degrade U. prolifera, with focuses on the degradation ensued impacts on water quality. The degradation process of fresh U. prolifera over two months was dominated by the continuous and slow release of DOM, and the concentration of DOM in the water column was hardly observed to decrease within two months. The pre-discomposed-disposal method also significantly altered microbial community structure. The pre-decomposing treatment with microbial complex formulations destroyed U. prolifera cell tissues and changed its physical state in seawater from floating to fast depositing, and increased the degradation rate by about 14 times. The rapid decomposition of the released bioactive organic matter consumed a substantial amount of dissolved oxygen in local seawater, which has the potential risk of causing local hypoxia and acidification in a short-term. The pre-decomposition treatment of U. prolifera could be a practical and efficient countermeasures to U. prolifera blooming. After the complete degradation of the pre-decomposed U. prolifera, the resulting dissolved organic matter could increase TA to resist acidification. Overall, compared with traditional harvest-packing-disposal method, the pre-decomposing-disposal treatment is an efficient and environmental-friendly disposal method to deal with the U. prolifera “green tide”, but it should be used cautiously.

[1]  N. Jiao,et al.  Green Tides Significantly Alter the Molecular Composition and Properties of Coastal DOC and Perform Dissolved Carbon Sequestration. , 2022, Environmental science & technology.

[2]  W. Liu,et al.  Environmental and Economic Impacts of Different Disposal Options for Ulva prolifera Green Tide in the Yellow Sea, China , 2022, ACS Sustainable Chemistry & Engineering.

[3]  Zhihua Xu,et al.  Public's preference for the treatment of Ulva prolifera blooms: A choice experiment study in China , 2022, Algal Research.

[4]  Jinlin Liu,et al.  Prevention strategies for green tides at source in the Southern Yellow Sea. , 2022, Marine pollution bulletin.

[5]  W. Cai,et al.  Responses of the marine carbonate system to a green tide: A case study of an Ulva prolifera bloom in Qingdao coastal waters. , 2021, Harmful algae.

[6]  S. Powtongsook,et al.  Dynamics of Microbial Community During Nitrification Biofilter Acclimation with Low and High Ammonia , 2021, Marine Biotechnology.

[7]  Na Yang,et al.  Active dissolved organic nitrogen cycling hidden in large river and environmental implications. , 2021, The Science of the total environment.

[8]  Xiaohua Zhang,et al.  Succession of marine bacteria in response to Ulva prolifera-derived dissolved organic matter. , 2021, Environment international.

[9]  Hong Xu,et al.  Controlling the source of green tides in the Yellow Sea: NaClO treatment of Ulva attached on Pyropia aquaculture rafts , 2021 .

[10]  Zilin Song,et al.  Effects of phosphogypsum and medical stone on nitrogen transformation, nitrogen functional genes, and bacterial community during aerobic composting. , 2021, The Science of the total environment.

[11]  Gui‐Peng Yang,et al.  Emissions of biogenic sulfur compounds and their regulation by nutrients during an Ulva prolifera bloom in the Yellow Sea. , 2020, Marine pollution bulletin.

[12]  Pengyang Zhang,et al.  Integrated effects of Ulva prolifera bloom and decay on nutrients inventory and cycling in marginal sea of China. , 2020, Chemosphere.

[13]  J. Chen,et al.  DOC dynamics and bacterial community succession during long-term degradation of Ulva prolifera and their implications for the legacy effect of green tides on refractory DOC pool in seawater. , 2020, Water research.

[14]  W. H. M. Wan Mohtar,et al.  Dataset on specific UV absorbances (SUVA254) at stretch components of Perak River basin , 2020, Data in brief.

[15]  S. Shen,et al.  Comparative transcriptome analysis between floating and attached Ulva prolifera in studying green tides in the Yellow Sea , 2019 .

[16]  K. Murphy,et al.  staRdom: Versatile Software for Analyzing Spectroscopic Data of Dissolved Organic Matter in R , 2019, Water.

[17]  Dongyan Liu,et al.  Ulva prolifera green-tide outbreaks and their environmental impact in the Yellow Sea, China , 2019, National science review.

[18]  Zhigang Yu,et al.  Physical-biogeochemical interactions and potential effects on phytoplankton and Ulva prolifera in the coastal waters off Qingdao (Yellow Sea, China) , 2019, Acta Oceanologica Sinica.

[19]  Guang Gao,et al.  Physiological acclimation of the green tidal alga Ulva prolifera to a fast-changing environment. , 2018, Marine environmental research.

[20]  Yuan Yuan,et al.  Microwave assisted hydrothermal extraction of polysaccharides from Ulva prolifera: Functional properties and bioactivities. , 2018, Carbohydrate polymers.

[21]  Yan Li,et al.  Effect of the large-scale green tide on the species succession of green macroalgal micro-propagules in the coastal waters of Qingdao, China. , 2017, Marine pollution bulletin.

[22]  P. Glibert,et al.  Eutrophication, harmful algae and biodiversity - Challenging paradigms in a world of complex nutrient changes. , 2017, Marine pollution bulletin.

[23]  Kefeng Yu,et al.  The fast expansion of Pyropia aquaculture in “Sansha” regions should be mainly responsible for the Ulva blooms in Yellow Sea , 2017 .

[24]  Chuanmin Hu,et al.  Remote estimation of biomass of Ulva prolifera macroalgae in the Yellow Sea , 2017 .

[25]  Guang Gao,et al.  Expected CO2-induced ocean acidification modulates copper toxicity in the green tide alga Ulva prolifera , 2017 .

[26]  Guang Gao,et al.  Changes in morphological plasticity of Ulva prolifera under different environmental conditions: A laboratory experiment. , 2016, Harmful algae.

[27]  Chuanmin Hu,et al.  Long-term trend of Ulva prolifera blooms in the western Yellow Sea. , 2016, Harmful algae.

[28]  Y. Ko,et al.  Organic alkalinity produced by phytoplankton and its effect on the computation of ocean carbon parameters , 2016 .

[29]  E. L. Luherne,et al.  Fish community responses to green tides in shallow estuarine and coastal areas , 2016 .

[30]  James C. Stegen,et al.  The reduced genomes of Parcubacteria (OD1) contain signatures of a symbiotic lifestyle , 2015, Front. Microbiol..

[31]  Brian C. Thomas,et al.  Unusual biology across a group comprising more than 15% of domain Bacteria , 2015, Nature.

[32]  Adriana Zingone,et al.  Green and golden seaweed tides on the rise , 2013, Nature.

[33]  Natalia N. Ivanova,et al.  Insights into the phylogeny and coding potential of microbial dark matter , 2013, Nature.

[34]  Junhai Liu,et al.  Microwave-assisted direct liquefaction of Ulva prolifera for bio-oil production by acid catalysis. , 2012, Bioresource technology.

[35]  Julian L Fairey,et al.  Improving on SUVA 254 using fluorescence-PARAFAC analysis and asymmetric flow-field flow fractionation for assessing disinfection byproduct formation and control. , 2012, Water research.

[36]  Xiao-Song He,et al.  Fluorescence excitation-emission matrix spectroscopy with regional integration analysis for characterizing composition and transformation of dissolved organic matter in landfill leachates. , 2011, Journal of hazardous materials.

[37]  N. Ye,et al.  ‘Green tides’ are overwhelming the coastline of our blue planet: taking the world’s largest example , 2011, Ecological Research.

[38]  Treavor H. Boyer,et al.  Effect of landfill characteristics on leachate organic matter properties and coagulation treatability. , 2010, Chemosphere.

[39]  R. Jaffé,et al.  Acclimation to elevated carbon dioxide and ultraviolet radiation in the diatom Thalassiosira pseudonana : Effects on growth , photosynthesis , and spectral sensitivity of photoinhibition , 2008 .

[40]  Treavor H. Boyer,et al.  Removal of dissolved organic matter by anion exchange: effect of dissolved organic matter properties. , 2008, Environmental science & technology.

[41]  P. Morand,et al.  How Brittany and Florida coasts cope with green tides , 2008 .

[42]  A. Zirino,et al.  Estimating the contribution of organic bases from microalgae to the titration alkalinity in coastal seawaters , 2007 .

[43]  P. Lozovik Contribution of Organic Acid Anions to the Alkalinity of Natural Humic Water , 2005 .

[44]  B. Roe,et al.  Metagenomic Analysis of the Microbial Community at Zodletone Spring (Oklahoma): Insights into the Genome of a Member of the Novel Candidate Division OD1 , 2005, Applied and Environmental Microbiology.

[45]  C. Stedmon,et al.  Resolving the variability in dissolved organic matter fluorescence in a temperate estuary and its catchment using PARAFAC analysis , 2005 .

[46]  Scott T. Kelley,et al.  New Perspective on Uncultured Bacterial Phylogenetic Division OP11 , 2004, Applied and Environmental Microbiology.

[47]  W. Cai,et al.  Acid-Base Properties of Dissolved Organic Matter in the Estuarine Waters of Georgia, USA , 1998 .

[48]  P. H. Nienhuis,et al.  Marine Benthic Vegetation , 1996, Ecological Studies.

[49]  A. C. Redfield The biological control of chemical factors in the environment. , 1960, Science progress.