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. 2022 Oct 28;5:1143. doi: 10.1038/s42003-022-04107-z

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© The Author(s) 2022

Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made. The images or other third party material in this article are included in the article’s Creative Commons license, unless indicated otherwise in a credit line to the material. If material is not included in the article’s Creative Commons license and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this license, visit http://creativecommons.org/licenses/by/4.0/.

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Fig. 4 — a CAP with time relative to the Blob (before: 2008–2013, during: 2014–2015, and after: 2016–2021) as a constraining variable. Points represent the average species composition across four sites for each sampling season. Lines represent (b) prominent species with correlations >0.6; (1) Actinostella californica (Phylum Cnidaria) (2) Bugula neritina (Phylum Bryozoa) (3) Thylacodes squamigerus (Phylum Mollusca) (4) Watersipora subatra (Phylum Bryozoa) (5) Diaperoforma californica (Phylum Bryozoa) (6) Phragmatopoma californica (Phylum Annelida) (7) Timarete luxuriosa (Phylum Annelida) (8) Encrusting bryozoan spp. (Phylum Bryozoa).