Optimizing the use of quicklime (CaO) for sea urchin management — A lab and field study

Mass blooms of sea urchins sometimes cause kelp forest collapses that can last for decades. Quicklime has historically been used to reverse those conditions, but the efficacy of liming has varied along latitudinal and temperature gradients for reasons that are not fully understood. To evaluate the f...

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Published in:Ecological Engineering: X
Main Authors: Strand, Hans Kristian, Christie, Hartvig C, Fagerli, Camilla With, Mengede, Martin, Moy, Frithjof Emil
Format: Article in Journal/Newspaper
Language:English
Published: 2020
Subjects:
Online Access:https://hdl.handle.net/11250/2719554
https://doi.org/10.1016/j.ecoena.2020.100018
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spelling ftimr:oai:imr.brage.unit.no:11250/2719554 2023-05-15T17:43:42+02:00 Optimizing the use of quicklime (CaO) for sea urchin management — A lab and field study Strand, Hans Kristian Christie, Hartvig C Fagerli, Camilla With Mengede, Martin Moy, Frithjof Emil 2020 application/pdf https://hdl.handle.net/11250/2719554 https://doi.org/10.1016/j.ecoena.2020.100018 eng eng Ecological Engineering: X. 2020, 6:100018 1-11. https://hdl.handle.net/11250/2719554 https://doi.org/10.1016/j.ecoena.2020.100018 cristin:1852479 1-11 6:100018 Ecological Engineering: X Peer reviewed Journal article 2020 ftimr https://doi.org/10.1016/j.ecoena.2020.100018 2021-09-23T20:16:11Z Mass blooms of sea urchins sometimes cause kelp forest collapses that can last for decades. Quicklime has historically been used to reverse those conditions, but the efficacy of liming has varied along latitudinal and temperature gradients for reasons that are not fully understood. To evaluate the feasibility and ecological impacts of liming in a high latitude area in Northern Norway (70°N), we conducted a field pilot study in 2008–2011, a follow-up lab study in 2017, and a further field study in 2018–2019, with the latter evaluating and implementing the previous results in a site high in refuges. It was found that liming can reduce sea urchin densities sufficiently for macroalgal revegetation to occur, and that the mobile fauna species richness and abundance increased in the re-vegetated in comparison to the barren control fields. Also, the remaining sea urchins in the treated fields increased their roe content to commercial levels after 2 years. The lab experiments in 2017 indicated that the liming method is season/temperature-independent, as mortality remained at the same level irrespective of whether treatment started in the spring, when the sea temperatures were 2 °C, or in autumn when the temperatures were closer to 10 °C. The most important factor in treatment efficacy in the lab was particle size. With similar doses, the particles in the smallest size range (0–0.5 mm) caused 100% mortality, while the 0.5–2 mm and 2–4 mm fractions caused only 13% and 2% mortality respectively. In 2018–2019 we tested the fine CaO fraction (0.1–0.6 mm) and the medium fraction (0.5–2 mm) in a field experiment in areas characterized by high levels of refuges. Within 11 days, the sea urchin densities in the three fields treated with the fine lime were reduced to levels that theoretically should allow revegetation, but only in one of those fields was that potential partly realized after 1 year. The lack of effect in the two other fields was probably due to urchins protected by the substrate during treatment reappearing in sufficient numbers to prevent macroalgal regrowth, demonstrating that CaO treatment can be less effective on substrates where part of the sea urchin population hides among stones. Of the three variables held up as potential explanations for the different effects of CaO treatment in previous studies, we conclude based on our experiments that the presence of refuges and particle size were probably more important than temperature. Further improvements for larger scale treatments are discussed. publishedVersion Article in Journal/Newspaper Northern Norway Institute for Marine Research: Brage IMR Norway Ecological Engineering: X 6 100018
institution Open Polar
collection Institute for Marine Research: Brage IMR
op_collection_id ftimr
language English
description Mass blooms of sea urchins sometimes cause kelp forest collapses that can last for decades. Quicklime has historically been used to reverse those conditions, but the efficacy of liming has varied along latitudinal and temperature gradients for reasons that are not fully understood. To evaluate the feasibility and ecological impacts of liming in a high latitude area in Northern Norway (70°N), we conducted a field pilot study in 2008–2011, a follow-up lab study in 2017, and a further field study in 2018–2019, with the latter evaluating and implementing the previous results in a site high in refuges. It was found that liming can reduce sea urchin densities sufficiently for macroalgal revegetation to occur, and that the mobile fauna species richness and abundance increased in the re-vegetated in comparison to the barren control fields. Also, the remaining sea urchins in the treated fields increased their roe content to commercial levels after 2 years. The lab experiments in 2017 indicated that the liming method is season/temperature-independent, as mortality remained at the same level irrespective of whether treatment started in the spring, when the sea temperatures were 2 °C, or in autumn when the temperatures were closer to 10 °C. The most important factor in treatment efficacy in the lab was particle size. With similar doses, the particles in the smallest size range (0–0.5 mm) caused 100% mortality, while the 0.5–2 mm and 2–4 mm fractions caused only 13% and 2% mortality respectively. In 2018–2019 we tested the fine CaO fraction (0.1–0.6 mm) and the medium fraction (0.5–2 mm) in a field experiment in areas characterized by high levels of refuges. Within 11 days, the sea urchin densities in the three fields treated with the fine lime were reduced to levels that theoretically should allow revegetation, but only in one of those fields was that potential partly realized after 1 year. The lack of effect in the two other fields was probably due to urchins protected by the substrate during treatment reappearing in sufficient numbers to prevent macroalgal regrowth, demonstrating that CaO treatment can be less effective on substrates where part of the sea urchin population hides among stones. Of the three variables held up as potential explanations for the different effects of CaO treatment in previous studies, we conclude based on our experiments that the presence of refuges and particle size were probably more important than temperature. Further improvements for larger scale treatments are discussed. publishedVersion
format Article in Journal/Newspaper
author Strand, Hans Kristian
Christie, Hartvig C
Fagerli, Camilla With
Mengede, Martin
Moy, Frithjof Emil
spellingShingle Strand, Hans Kristian
Christie, Hartvig C
Fagerli, Camilla With
Mengede, Martin
Moy, Frithjof Emil
Optimizing the use of quicklime (CaO) for sea urchin management — A lab and field study
author_facet Strand, Hans Kristian
Christie, Hartvig C
Fagerli, Camilla With
Mengede, Martin
Moy, Frithjof Emil
author_sort Strand, Hans Kristian
title Optimizing the use of quicklime (CaO) for sea urchin management — A lab and field study
title_short Optimizing the use of quicklime (CaO) for sea urchin management — A lab and field study
title_full Optimizing the use of quicklime (CaO) for sea urchin management — A lab and field study
title_fullStr Optimizing the use of quicklime (CaO) for sea urchin management — A lab and field study
title_full_unstemmed Optimizing the use of quicklime (CaO) for sea urchin management — A lab and field study
title_sort optimizing the use of quicklime (cao) for sea urchin management — a lab and field study
publishDate 2020
url https://hdl.handle.net/11250/2719554
https://doi.org/10.1016/j.ecoena.2020.100018
geographic Norway
geographic_facet Norway
genre Northern Norway
genre_facet Northern Norway
op_source 1-11
6:100018
Ecological Engineering: X
op_relation Ecological Engineering: X. 2020, 6:100018 1-11.
https://hdl.handle.net/11250/2719554
https://doi.org/10.1016/j.ecoena.2020.100018
cristin:1852479
op_doi https://doi.org/10.1016/j.ecoena.2020.100018
container_title Ecological Engineering: X
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