Restoration experiments in polymetallic nodule areas

Deep‐seabed polymetallic nodule mining can have multiple adverse effects on benthic communities, such as permanent loss of habitat by removal of nodules and habitat modification of sediments. One tool to manage biodiversity risks is the mitigation hierarchy, including avoidance, minimization of impacts, rehabilitation and/or restoration, and offset. We initiated long‐term restoration experiments at sites in polymetallic nodule exploration contract areas in the Clarion‐Clipperton Zone that were (i) cleared of nodules by a preprototype mining vehicle, (ii) disturbed by dredge or sledge, (iii) undisturbed, and (iv) naturally devoid of nodules. To accommodate for habitat loss, we deployed >2000 artificial ceramic nodules to study the possible effect of substrate provision on the recovery of biota and its impact on sediment biogeochemistry. Seventy‐five nodules were recovered after eight weeks and had not been colonized by any sessile epifauna. All other nodules will remain on the seafloor for several years before recovery. Furthermore, to account for habitat modification of the top sediment layer, sediment in an epibenthic sledge track was loosened by a metal rake to test the feasibility of sediment decompaction to facilitate soft‐sediment recovery. Analyses of granulometry and nutrients one month after sediment decompaction revealed that sand fractions are proportionally lower within the decompacted samples, whereas total organic carbon values are higher. Considering the slow natural recovery rates of deep‐sea communities, these experiments represent the beginning of a ~30‐year study during which we expect to gain insights into the nature and timing of the development of hard‐substrate communities and the influence of nodules on the recovery of disturbed sediment communities. Results will help us understand adverse long‐term effects of nodule removal, providing an evidence base for setting criteria for the definition of “serious harm” to the environment. Furthermore, accompanying research is needed to define a robust ecosystem baseline in order to effectively identify restoration success. Integr Environ Assess Manag 2022;18:682–696. © 2021 The Authors. Integrated Environmental Assessment and Management published by Wiley Periodicals LLC on behalf of Society of Environmental Toxicology & Chemistry (SETAC).

[1]  A. Vanreusel,et al.  Potential impacts of polymetallic nodule removal on deep-sea meiofauna , 2021, Scientific Reports.

[2]  A. Gooday,et al.  The Biodiversity and Distribution of Abyssal Benthic Foraminifera and Their Possible Ecological Roles: A Synthesis Across the Clarion-Clipperton Zone , 2021, Frontiers in Marine Science.

[3]  A. Vanreusel,et al.  Potential Impacts of Polymetallic Nodule Removal On Deep-Sea Meiobenthos , 2021 .

[4]  L. Levin,et al.  Eukaryotic Biodiversity and Spatial Patterns in the Clarion-Clipperton Zone and Other Abyssal Regions: Insights From Sediment DNA and RNA Metabarcoding , 2021, Frontiers in Marine Science.

[5]  Tanja Stratmann,et al.  Polymetallic nodules are essential for food-web integrity of a prospective deep-seabed mining area in Pacific abyssal plains , 2021, Scientific Reports.

[6]  Daniëlle de Jonge,et al.  Abyssal food-web model indicates faunal carbon flow recovery and impaired microbial loop 26 years after a sediment disturbance experiment , 2020, Progress in Oceanography.

[7]  A. Metaxas,et al.  Deep-Sea Misconceptions Cause Underestimation of Seabed-Mining Impacts. , 2020, Trends in ecology & evolution.

[8]  Astrid B. Leitner,et al.  Opinion: Midwater ecosystems must be considered when evaluating environmental risks of deep-sea mining , 2020, Proceedings of the National Academy of Sciences.

[9]  L. Levin,et al.  Challenges to the sustainability of deep-seabed mining , 2020, Nature Sustainability.

[10]  A. Boetius,et al.  The contribution of microbial communities in polymetallic nodules to the diversity of the deep-sea microbiome of the Peru Basin (4130–4198 m depth) , 2020, Biogeosciences.

[11]  M. Haeckel,et al.  Assessing the temporal scale of deep-sea mining impacts on sediment biogeochemistry , 2020 .

[12]  A. Boetius,et al.  Effects of a deep-sea mining experiment on seafloor microbial communities and functions after 26 years , 2020, Science Advances.

[13]  A. Denda,et al.  Potential effects of deep seabed mining on pelagic and benthopelagic biota , 2020 .

[14]  A. Koschinsky,et al.  Deep-ocean polymetallic nodules as a resource for critical materials , 2020, Nature Reviews Earth & Environment.

[15]  C. Rodrigues,et al.  Unexpected high abyssal ophiuroid diversity in polymetallic nodule fields of the northeast Pacific Ocean and implications for conservation , 2019, Biogeosciences.

[16]  P. Snelgrove,et al.  The deep sea: The new frontier for ecological restoration , 2019, Marine Policy.

[17]  A. Colaço,et al.  Are seamounts refuge areas for fauna from polymetallic nodule fields? , 2019, Biogeosciences.

[18]  T. Soltwedel,et al.  Recruitment of Arctic deep‐sea invertebrates: Results from a long‐term hard‐substrate colonization experiment at the Long‐Term Ecological Research observatory HAUSGARTEN , 2019, Limnology and Oceanography.

[19]  Geraldine Heng An Ordinary Ship and Its Stories of Early Globalism , 2019, Journal of Medieval Worlds.

[20]  A. Purser,et al.  Potential Mitigation and Restoration Actions in Ecosystems Impacted by Seabed Mining , 2018, Front. Mar. Sci..

[21]  A. Koschinsky,et al.  Natural spatial variability of depositional conditions, biogeochemical processes and element fluxes in sediments of the eastern Clarion-Clipperton Zone, Pacific Ocean , 2018, Deep Sea Research Part I: Oceanographic Research Papers.

[22]  A. Koschinsky,et al.  Biogeochemical Regeneration of a Nodule Mining Disturbance Site: Trace Metals, DOC and Amino Acids in Deep-Sea Sediments and Pore Waters , 2018, Front. Mar. Sci..

[23]  L. Levin,et al.  Deep-Sea Mining With No Net Loss of Biodiversity—An Impossible Aim , 2018, Front. Mar. Sci..

[24]  A. Boetius,et al.  Mind the seafloor , 2018, Science.

[25]  P. Johnston,et al.  An Overview of Seabed Mining Including the Current State of Development, Environmental Impacts, and Knowledge Gaps , 2018, Front. Mar. Sci..

[26]  A. Gooday,et al.  Novel benthic foraminifera are abundant and diverse in an area of the abyssal equatorial Pacific licensed for polymetallic nodule exploration , 2017, Scientific Reports.

[27]  Jens Greinert,et al.  Biological responses to disturbance from simulated deep-sea polymetallic nodule mining , 2017, PloS one.

[28]  Matthew J. Church,et al.  Polymetallic nodules, sediments, and deep waters in the equatorial North Pacific exhibit highly diverse and distinct bacterial, archaeal, and microeukaryotic communities , 2016, MicrobiologyOpen.

[29]  A. Boetius,et al.  Association of deep-sea incirrate octopods with manganese crusts and nodule fields in the Pacific Ocean , 2016, Current Biology.

[30]  Cindy Lee Van Dover,et al.  Defining “serious harm” to the marine environment in the context of deep-seabed mining , 2016 .

[31]  Adrian G. Glover,et al.  Insights into the abundance and diversity of abyssal megafauna in a polymetallic-nodule region in the eastern Clarion-Clipperton Zone , 2016, Scientific Reports.

[32]  Ann Vanreusel,et al.  Threatened by mining, polymetallic nodules are required to preserve abyssal epifauna , 2016, Scientific Reports.

[33]  Alan Williams,et al.  The impacts of deep-sea fisheries on benthic communities: a review , 2016 .

[34]  T. Kuhn,et al.  Mineralogical characterization of individual growth structures of Mn-nodules with different Ni+Cu content from the central Pacific Ocean , 2015 .

[35]  A. Gooday,et al.  Abyssal foraminifera attached to polymetallic nodules from the eastern Clarion Clipperton Fracture Zone: a preliminary description and comparison with North Atlantic dropstone assemblages , 2015, Marine Biodiversity.

[36]  P. Masqué,et al.  Impact of Bottom Trawling on Deep-Sea Sediment Properties along the Flanks of a Submarine Canyon , 2014, PloS one.

[37]  Roberto Danovaro,et al.  Ecological restoration in the deep sea: Desiderata , 2014 .

[38]  D. Freese,et al.  Recolonisation of new habitats by meiobenthic organisms in the deep Arctic Ocean: an experimental approach , 2012, Polar Biology.

[39]  P. M. Arbizu,et al.  Deep-sea nematode assemblage has not recovered 26 years after experimental mining of polymetallic nodules (Clarion-Clipperton Fracture Zone, Tropical Eastern Pacific) , 2011 .

[40]  F. Colijn,et al.  Experimental settlement study in the Eastern Mediterranean deep sea (Ionian Sea) , 2011 .

[41]  F. D. De Leo,et al.  Abyssal food limitation, ecosystem structure and climate change. , 2008, Trends in ecology & evolution.

[42]  Stace E. Beaulieu,et al.  Colonization of habitat islands in the deep sea: recruitment to glass sponge stalks , 2001 .

[43]  I. Konig A geochemical model of the Peru Basin deep-sea floor and the response of the system to technical impacts , 1999 .

[44]  H. Kitazato Recolonization by deep-sea benthic foraminifera: possible substrate preferences , 1995 .

[45]  H. Thiel,et al.  Manganese nodule crevice fauna , 1993 .

[46]  L. Mullineaux,et al.  Recruitment of encrusting benthic invertebrates in boundary-layer flows: A deep-water experiment on Cross Seamount , 1990 .

[47]  L. Mullineaux Vertical distributions of the epifauna on manganese nodules: implications for settlement and feeding , 1989 .

[48]  L. Mullineaux The role of settlement in structuring a hard-substratum community in the deep sea , 1988 .

[49]  J. Grassle,et al.  Macrofaunal colonization of disturbed deep-sea environments and the structure of deep-sea benthic communities , 1987 .

[50]  R. Hessler,et al.  Colonization and succession in deep-sea ecosystems. , 1987, Trends in ecology & evolution.

[51]  M. Lyle Estimating growth rates of ferromanganese nodules from chemical compositions: implications for nodule formation processes , 1982 .

[52]  J. Grassle,et al.  Slow recolonisation of deep-sea sediment , 1977, Nature.