Marraffini, M 1 2 3 4 5 6 7 8 9 10 11 INVASIBILITY OF COMMUNITIES Supplementary Materials Figure SM1. Experimental Setup. A. attachment of PVC frame that held experimental blocks attached to floating dock. B. View of diver (Heather Hawk) assisting with installation of a block. C. View of a tile several weeks after installation with solitary tunicates and Sabellidae tube worms that were attached using marine epoxy. D. Close up of treatment tiles in in block B showing that attachment of animals using marine epoxy. Photos A, B, D by Scott Gabara; photo C by Michelle Marraffini. 1 Marraffini, M 12 13 14 15 Figure SM2. Total number of recruits after 100 days plotted as a function of original species richness (A); original percent cover (B), and original percent of native species (C). Data are binned across other factors to examine the main effect in each panel. 16 17 18 19 2 Marraffini, M 20 21 22 Table SM1 Approximate sizes of adult organisms used in the experiment. Size is taken as the longest axis of a solitary animal and the diameter of a colonial animal. For anemones, this is their width in their non-contracted form. Species Phyla Body Plan Range of sizes (cm) Botrylloides violaceus (I) Watersipora subtorquata (I) Mytilus galloprovincialis (I) Bugula neritina (I) Ciona savignyi (I) Diplosoma listerianum (I) Botryllus "schlosseri"(I) Ascidia ceratodes (N) Balanus crenatus (N) Corynactis californica (N) Metridium senile (N) Aplidium californium (N) Distaplia occidentalis (N) Barentsia ramosa (N) Eudistylia polymorpha (N) Mytilus californianus (N) Chordata Bryozoa Mollusca Bryozoa Chordata Chordata Chordata Chordata Arthropoda Cnidaria Cnidaria Chordata Chordata Entoprocta Annelida Mollusca Colonial Colonial Solitary Colonial Solitary Colonial Colonial Solitary Solitary Solitary Solitary Colonial Colonial Colonial Solitary Solitary 5-10 5-10 7-10 5-8 4-8 3-7 2-6 7-10 1-2 1-2 3-6 5-10 3-7 2-6 10-20 7-10 23 24 25 3 Marraffini, M 26 27 Table SM2. Organisms recruited during the experiment. Listed in order of appearance and asterisks indicate species that were not originally used in treatments. Organism Phyla Annelida Chordata Chordata Chordata Bryozoa Chordata Chordata Annelida Arthropoda Bryozoa Annelida Lowest Taxonomic Level Spirorbis sp.* Diplosoma listerianum Ascidiacea (colonial)* Botrylloides violaceus Watersipora subtorquata Botryllus schlosseri Ciona savignyi Salmacina tribranchiata* Balanus crenatus Bugula neritina* Serpula columbiana* Native Status Native NIS Unknown NIS NIS NIS NIS Native Native NIS Native Date of Appearance Day of DOY Experiment 7/16/12 14 7/16/12 14 7/16/12 14 7/30/12 28 7/30/12 28 8/13/12 42 8/13/12 42 8/13/12 42 9/10/12 70 9/24/12 84 9/24/12 84 Successful Recruit Size (mm) N/A 2 2 2 1 2 2 2 2 1 2 28 29 4 Marraffini, M 30 31 32 33 Table S3. Estimates of variation explained by the GLMMs used in this experiment. ICC refers to interclass correlation, explaining the proportion of variance explained by random intercept over the variance of the residuals, interpreted as the total variance between groups (Zuur et al., 2009). Time is in days into the experiment. Model Table Time Response Components ICC Rc2 Rm2 R, PC, PNS, R:PC, Overall GLMM 4 100 Recruits 0.5 0.85 0.46 Time, Block Early R, PC, PNS, R:PC, S2 57 Recruits 0.5 0.66 0.32 Recruitment Time, Block Stachowicz R, PC, PNS, R:PC, 7 71 Recruits 0.5 0.66 0.31 Comparison Time, Block NIS R, PC, PNS, R:PC, Invasions S3 30 0.5 0.61 0.21 Recruits Time, Block 34 35 5 Marraffini, M 36 37 Table SM4. Estimated parameters from GLMM for the first 57 days. Model for cumulative recruitment during the first 57 days of the experiment. Fixed Random Parameter Estimate Std. Error P value Variance Intercept 1.0382 0.3650 0.00445 -- Richness (PR) 0.0435 0.0066 3.44e-07 -- Percent Cover (PC) 0.0118 0.0006 <2e-16 Percent Native Species (PPNS) -0.018 0.0002 <2e-16 R:PC 0.0003 0.0003 <2e-16 Time -0.0029 0.0019 <2e-16 -- Block -- -- -- 6.631e-01 Time -- -- -- 1.797e-05 -- 38 6 Marraffini, M 39 40 41 Table SM5. Estimated parameters from GLMM for the first 71 days. Model for cumulative recruitment during the first 71 days of the experiment, for comparison to previous experiments (6, 7). Fixed Random Parameter Estimate Std. Error P value Variance Intercept 1.2907 0.3387 0.00014 --- Richness (PR) -0.0349 0.0057 1.6e-09 Percent Cover (PC) -0.0203 0.0006 <2e-16 Percent Native Species (PPNS) -0.0034 0.0002 <2e-16 R:PC -0.0057 0.0002 <2e-16 Time 0.0223 0.0012 <2e-16 -- Block -- -- -- 5.713e-01 Time -- -- -- 6.955-06 -- 42 43 44 45 46 47 48 49 7 Marraffini, M 50 51 Table SM6. Estimated parameters from the best-fit GLMM on NIS recruitment. Modeling cumulative recruitment of NIS during the first month of the experiment. Fixed Random Parameter Estimate Std. Error P value Variance Intercept -0.0585 0.4528 0.897 -- Richness (PR) -0.013 0.0218 0.551 -- Percent Cover (PC) -0.0256 0.0023 <2e-16 Percent Native Species (PNS) -0.004 0.0009 8.39e-06 R:PC -0.0051 0.0009 4.95e-08 Time 0.0676 0.0095 1.01e-12 -- Block -- -- -- 0.6764 Time -- -- -- 0.0003 -- 52 8 Marraffini, M 53 Genetic Methods 54 When morphological identification was not feasible, genetic methods were used to 55 confirm the identity of recruited individuals (genus or species) and organisms in community 56 manipulations. A sample of DNA was extracted from fresh tissue using Promega© Wizard 96- 57 well DNA extraction kits following manufacturer’s protocol, with the additional step of tissue 58 maceration by bead beating before overnight incubation. Polymerase chain reaction (PCR) 59 amplified the COI region with primers jgLCO1490 and jgHCO2198 [1x Green Gotaq Master 60 Mix, Promega (Cat #PRM7123), 0.2 M BSA, 1.5 mM MgCl2, 0.2 μM of each primer] using a 61 three-step thermocycler program (three minute at 94C followed by 30 cycles of 94C for one 62 minute as a denaturation step, 47C for one minute as the annealing temperature, and an 63 extension step at 72C for one minute) using universal COI primers (Geller et al. 2013). PCR 64 products deemed successful as bright single bands visualized by agarose electrophoresis were 65 sequenced by the Sanger method (Elim Biopharmaceuticals, Hayward, CA). Geneious© software 66 (by Biomatters Ltd.) was used to assemble forward and reverse reads, and edited sequences were 67 compared to known sequences in Genbank (National Center for Biotechnology Information) and 68 a reference library developed in the San Francisco invasive species monitoring program (Geller 69 et al. 2013). Similarity of sequences from unknown specimens to a reference sequence of 95% 70 or greater was considered a match for identification. 71 Results 72 Ninety-three samples were successfully amplified by PCR and sent for Sanger 73 sequencing. Of these samples 61 sequences, showed strong quality sequences that could be 74 used for analysis (Table S4). This analysis helped resolve the identification of two species 75 (an anemone and Balanus sp.) too small for morphological identification. These specimens 9 Marraffini, M 76 had results from Genbank but the identifications were to species never recorded in this 77 area and the matches were suspect. Comparisons to the Geller database revealed better 78 matches and identifications of species known to inhabit these areas. Several specimens 79 remained unresolved as the samples failed to amplify or to give a clean, high quality 80 sequence. Further work is needed to resolve the identity of these samples. The unresolved 81 species were not assigned native or NIS status and were removed from analyses on 82 invasion success. 83 10 Marraffini, M 84 85 86 87 References Geller, J. , Meyer, C., Parker, M. and Hawk, H. 2013. Redesign of PCR primers for mitochondrial cytochrome c oxidase subunit I for marine invertebrates and application in all-taxa biotic surveys. Molecular Ecology Resources 13(5) 851-861. 11 88 89 90 91 Table S4. Field and molecular identifications of organisms used in treatments. Shows comparisons with Genbank database based on the best sequence. Number of Molecular Accession Percent Field Identification Final Identification Samples Identification Number Identical Anemone (small 4 Aiptasia pulchella HG423158.1 95 Unknown brown) Amphibalabus Balanus sp. 5 JQ035518.1 89 Unknown reticulatus Lamillaria sp. 4 Assiminea pecos DQ533844.1 83 Lamillaria sp. Botrylloides violaceus 7 Botrylloides violaceus GQ365691 100 Botrylloides violaceus Colonial Tunicate 3 Botryllus schlosseri JN083284 100 Botryllus schlosseri Botryllus schlosseri 3 Botryllus schlosseri JN083238 99 Botryllus schlosseri Bugula sp. (brown) 1 Bugula neritina KC129832.1 99 Bugula neritina Bugula sp. (white) 1 Bugula stolonifera KC129849.1 100 Bugula stolonifera Encrusting Bryozoa 2 Celleporaria oculata AY168607.1 94 Unknown Corynactis californica 1 Corynactis californica AB441257.1 100 Corynactis californica HM473366. Sabellid sp. 3 Eudistylia vancouveri 90 Eudistylia polymorpha 1 Sabellid sp. (smaller 2 Megalomma splendida HM473463 98 Megalomma splendida tube) Mytilus galloprovincalis 6 Mytilus galloprovincalis GQ480284.1 100 Mytilus galloprovincalis Sponge (yellow) 3 Haliclona xena JN242209.1 99 Haliclona sp. Anemone (small) 5 Metridium senile HG423143 99 Metridium senile Mytilus californianus 4 Mytilus californianus GQ902188.1 99 Mytilus californianus Watersipora sp. 2 Watersipora sutorquata DQ417456.1 99 Watersipora sutorquata Tube (Amphipod) 1 Ericthonius brasiliensis JX545463 89 Amphipoda Diplosoma listerianum 4 Diplosoma listerianum KF791868.1 99 Diplosoma listerianum Total 61 Marraffini, M 92 93 Table S5. Field and molecular identifications of organisms unresolved by Genbank. Shows comparisons with Genbank database and Geller lab database based on the best sequence. Field Genbank Accession Percent Geller Lab Percent Finial Identification Identification Number Identical Identification Identification Identification Anemone Aiptasia pulchella HG423158.1 95 Diadumene lineata 100 Diadumene lineata (small brown) Balanus sp. Amphibalabus JQ035518.1 89 Balanus crenatus 98 Balanus crenatus reticulatus (haplotype A) 94 13