More stories

  • in

    Internode elongation and strobili production of Humulus lupulus cultivars in response to local strain sensing

    Figure 4 illustrates the length of fertile internodes 20–40 within the various treatments of: FC, FN, F45, T45, N45, and B90. The FC, FN, and F45 treatments grew lengthier internodes from node 20–40 than the T45, N45, and B45 treatments (Fig. 4). Internode width, however, was greater in T45, N45, and B90 as compared to the undisturbed FC, FN, and F45 treatments (Table 1). The T45 and N45 treatments had a 27.9% and 26.6% reduction in internode elongation compared to the FC, FN, and F45 treatments. Of the treatments, B90 had the shortest internodes and widest internode thickness between node 20–40 (Tables 1, 2). Due to the shorter internode lengths in the mechanically affected treatments, the density of nodes per unit area was ~ 25% greater in T45 and N45 from node 20–40 and an additional 28% shorter in B90. In other words, B90 internodes were ~ 54% shorter between nodes 20–40 as compared to the untouched treatments and had the densest node concentration (cf Fig. 4 and Table 2). Both touched and bent bines were significantly reduced in elongation (Table 1; P  12–25. Thus, amassing many fertile nodes per vertical distance within a high sidewall greenhouse (e.g. ≥ 6 m) would be one viable means to increase the yield potential of hop in controlled environment production as long as plant resources did not become limiting. What’s more the 15.25 cm rise over run staircase created by the B90 internode bending treatment would allow for approximately double the bine length from the container to the top of a high sidewall greenhouse as compared to a vertically trellised bine (an additional direct step toward increasing node quantity per unit vertical production area). Secondly, the time and resource investment in overcoming the hop cultivar specific 11–24 infertile juvenile phase adds approximately three weeks to a single hop crop cycle e.g.11,36. Thus, it would be more time and space efficient to grow fewer crop cycles per annum that contain larger amounts of fertile nodes within a cycle as compared to additional cycles that contain the unfertile juvenile phase.In conclusion, repeated touch and/or bine bending within the active elongation zone of hop bines resulted in shortened internode length with higher cone production per given area. Mechanical stimuli did not reduce cone yield or flower quality. The results demonstrate that successive local internode strain can aid the control of internode elongation. Moreover, the study provides evidence that thigmomorphogenic cues can be used as a management tool to increase bine compactness and increase node density per unit area. This finding is especially important for growth control when production space is limiting and/or of high-value (e.g. greenhouse production)1. Hence, mechanical perturbation was an effective non-chemical means to control hop internode length. Nonetheless, models aimed at predicting internode length of hop bines in response to strain should still take into account a cultivar parameter. The results are practical on a commercial scale because the methods of touch and bending used in this study are easy to apply with minimal investment in labor, have a short time interval of application (approximately 5–10 s−1 per bine per 24 h), and the application duration is relatively short ~ 30 days out of the 90–120 day crop cycle, making this a practical endeavor when one considers that high value vine crops are already repeatedly handled by humans throughout their production cycle (e.g. viticulture grape and controlled environment cucumber production). More

  • in

    Effect of land use, habitat suitability, and hurricanes on the population connectivity of an endemic insular bat

    1.Ceballos, G. Mammal population losses and the extinction crisis. Science 296, 904–907 (2002).ADS 
    CAS 
    PubMed 
    Article 
    PubMed Central 

    Google Scholar 
    2.Meyer, C. F. J., Struebig, M. J. & Willig, M. R. Responses of tropical bats to habitat fragmentation, logging, and deforestation. In Bats in the Anthropocene: Conservation of Bats in a Changing World (eds Voigt, C. C. & Kingston, T.) 63–103 (Springer, 2016). https://doi.org/10.1007/978-3-319-25220-9_4.
    Google Scholar 
    3.Torres-Romero, E. J., Giordano, A. J., Ceballos, G. & López-Bao, J. V. Reducing the sixth mass extinction: understanding the value of human-altered landscapes to the conservation of the world’s largest terrestrial mammals. Biol. Conserv. 249, 108706 (2020).Article 

    Google Scholar 
    4.Mittermeier, R. A., Turner, W. R., Larsen, F. W., Brooks, T. M. & Gascon, C. Global biodiversity conservation: the critical role of hotspots BT—biodiversity hotspots: distribution and protection of conservation priority areas. In (eds Zachos, F. E. & Habel, J. C.) 3–22 (Springer, Berlin, 2011). https://doi.org/10.1007/978-3-642-20992-5_1.5.Bosso, L., Mucedda, M., Fichera, G., Kiefer, A. & Russo, D. A gap analysis for threatened bat populations on Sardinia. Hystrix Ital. J. Mammal. 27, 212–214 (2016).
    Google Scholar 
    6.Upham, N. S. Past and present of insular Caribbean mammals: understanding Holocene extinctions to inform modern biodiversity conservation. J. Mammal. 98, 913–917 (2017).Article 

    Google Scholar 
    7.Gould, W. A., Castro-Prieto, J. & Álvarez-Berríos, N. L. Climate change and biodiversity conservation in the Caribbean islands. In Encyclopedia of the World’s Biomes (eds Goldstein, M. & DellaSala, D.) 114–125 (Elsevier, 2020). https://doi.org/10.1016/B978-0-12-409548-9.12091-3.
    Google Scholar 
    8.Schoener, T. W., Spiller, D. A. & Losos, J. B. Variable ecological effects of hurricanes: the importance of seasonal timing for survival of lizards on Bahamian islands. Proc. Natl. Acad. Sci. 101, 177 LP – 181 (2004).ADS 
    Article 
    CAS 

    Google Scholar 
    9.Barnosky, A. D. et al. Has the Earth’s sixth mass extinction already arrived?. Nature 471, 51–57 (2011).ADS 
    CAS 
    PubMed 
    Article 
    PubMed Central 

    Google Scholar 
    10.Pimm, S. L. et al. The biodiversity of species and their rates of extinction, distribution, and protection. Science 344, 1246752–1246752 (2014).CAS 
    PubMed 
    Article 
    PubMed Central 

    Google Scholar 
    11.Turvey, S. T., Kennerley, R. J., Nuñez-Miño, J. M. & Young, R. P. The Last Survivors: current status and conservation of the non-volant land mammals of the insular Caribbean. J. Mammal. 98, 918–936 (2017).Article 

    Google Scholar 
    12.Andermann, T., Faurby, S., Turvey, S. T., Antonelli, A. & Silvestro, D. The past and future human impact on mammalian diversity. Sci. Adv. 6, eabb313 (2020).Article 

    Google Scholar 
    13.Turvey, S. T. & Crees, J. J. Extinction in the anthropocene. Curr. Biol. 29, R982–R986 (2019).CAS 
    PubMed 
    Article 
    PubMed Central 

    Google Scholar 
    14.Donihue, C. M. et al. Hurricane effects on neotropical lizards span geographic and phylogenetic scales. Proc. Natl. Acad. Sci. 117, 10429 LP – 10434 (2020).Article 
    CAS 

    Google Scholar 
    15.Gannon, M. R., Kurta, A., Rodríguez-Durán, A. & Willig, M. R. Bats of Puerto Rico: An Island Focus and a Caribbean Perspective (Texas Tech University Press, 2005).
    Google Scholar 
    16.Miller, G. L. & Lugo, A. E. Guide to the ecological systems of Puerto Rico. IITF-GTR-35. (2009).17.Guzmán-Colón, D. K., Pidgeon, A. M., Martinuzzi, S. & Radeloff, V. C. Conservation planning for island nations: using a network analysis model to find novel opportunities for landscape connectivity in Puerto Rico. Glob. Ecol. Conserv. 23, e01075 (2020).Article 

    Google Scholar 
    18.Gould, W. A. et al. The Puerto Rico Gap Analysis Project Volume 1: Land Cover, Vertebrate Species Distributions, and Land Stewardship. General technical reports IITF-39 vol. 1 https://www.fs.usda.gov/treesearch/pubs/38430 (2008).19.Gould, W. A. Puerto Rico gap analysis project. GAP Anal. Bull. 16, 71–79 (2009).
    Google Scholar 
    20.Gould, W. A., Quiñones, M., Solorzano, M., Alcobas, W. & Alarcon, C. Protected Natural Areas of Puerto Rico. Res. Map IITF-RMAP-02. Rio Piedras, PR US Dep. Agric. For. Serv. Int. Inst. Trop. For. (2011).21.Junta de Planificación. Plan de Uso de Terrenos, Guías de Ordenación del Territorio. 220 (2015).22.Gould, W. A., Wadsworth, F. H., Quiñones, M., Fain, S. J. & Álvarez-Berríos, N. L. Land use, conservation, forestry, and agriculture in Puerto Rico. Forests 8, 242–263 (2017).Article 

    Google Scholar 
    23.QGIS.org. QGIS Geographic Information System (2016).24.Martinuzzi, S., Gould, W. A., González, O. M. R., Quiñones, M. & Jiménez, M. E. Urban and rural land use in Puerto Rico. Res. Map IITF-RMAP-01. Rio Piedras, PR US Dep. Agric. For. Serv. Int. Inst. Trop. For. (2008).25.Gould, W. A., Martinuzzi, S. & González, O. M. R. High and low density development in Puerto Rico. Res. Map IITF-RMAP-11. Rio Piedras, PR US Dep. Agric. For. Serv. Int. Inst. Trop. For. (2008).26.Gannon, M. R. & Willig, M. R. The effects of Hurricane Hugo on bats of the Luquillo experimental forest of Puerto Rico. Biotropica 26, 320 (1994).Article 

    Google Scholar 
    27.Gannon, M. R. & Willig, M. R. Long-term monitoring protocol for bats: lessons from the Luquillo Experimental Forest of Puerto Rico. For. Biodivers. North Cent. South Am. Caribbean. Res. Monit. Man Biosph. Ser. 21, 271–291 (1998).
    Google Scholar 
    28.Gannon, M. R. & Willig, M. R. Island in the storm: disturbance ecology of plant-visiting bats on the hurricane-prone island of Puerto Rico. In Island Bats: Evolution, Ecology, and Conservation (eds Fleming, T. H. & Racey, P.) 281–301 (University of Chicago Press, 2009).
    Google Scholar 
    29.Jones, K. E., Barlow, K. E., Vaughan, N., Rodríguez-Durán, A. & Gannon, M. R. Short-term impacts of extreme environmental disturbance on the bats of Puerto Rico. Anim. Conserv. 4, 59–66 (2001).Article 

    Google Scholar 
    30.Rodríguez-Durán, A. & Vázquez, R. The bat Artibeus jamaicensis in Puerto Rico (West Indies): seasonality of diet, activity, and effect of a hurricane. Acta Chiropterologica 3, 53–61 (2001).
    Google Scholar 
    31.Rodríguez-Durán, A., Nieves, N. A. & Avilés-Ruiz, Y. Hurricane-mediated extirpation of a bat from an Antillean Island. Caribb. Nat. 78, 1–7 (2020).
    Google Scholar 
    32.Genoways, H. H. & Baker, R. J. Stenoderma rufum. Mamm. Species https://doi.org/10.2307/3503991 (1972).Article 

    Google Scholar 
    33.Kwiecinski, G. G. & Coles, W. C. Presence of Stenoderma rufum beyond the Puerto Rican bank. Occas. Pap. Museum Texas Tech Univ. https://doi.org/10.5962/bhl.title.156896 (2007).Article 

    Google Scholar 
    34.Liu, X. et al. Litterfall production prior to and during Hurricanes Irma and Maria in four Puerto Rican forests. Forests 9, 367 (2018).Article 

    Google Scholar 
    35.Rodríguez-Durán, A. Stenoderma rufum. IUCN Red List Threat. Species e.T20743A22065638 https://doi.org/10.2305/IUCN.UK.2016-1.RLTS.T20743A22065638.en (2016).Article 

    Google Scholar 
    36.Gannon, M. R. Foraging Ecology, Reproductive Biology, and Systematics of the Red Fig-Eating Bat (Stenoderma rufum) in the Tabonuco Rain Forest of Puerto Rico (Texas Tech University, 1991).
    Google Scholar 
    37.Meyer, C. F. J. & Kalko, E. K. V. Assemblage-level responses of phyllostomid bats to tropical forest fragmentation: land-bridge islands as a model system. J. Biogeogr. 35, 1711–1726 (2008).Article 

    Google Scholar 
    38.Estrada-Villegas, S., Meyer, C. F. J. & Kalko, E. K. V. Effects of tropical forest fragmentation on aerial insectivorous bats in a land-bridge island system. Biol. Conserv. 143, 597–608 (2010).Article 

    Google Scholar 
    39.Feng, Y., Negrón-Juárez, R. I. & Chambers, J. Q. Remote sensing and statistical analysis of the effects of hurricane María on the forests of Puerto Rico. Remote Sens. Environ. 247, 111940 (2020).ADS 
    Article 

    Google Scholar 
    40.Soto-Centeno, J. A. & Steadman, D. W. Fossils reject climate change as the cause of extinction of Caribbean bats. Sci. Rep. 5, 7971 (2015).ADS 
    CAS 
    PubMed 
    PubMed Central 
    Article 

    Google Scholar 
    41.Razgour, O. Beyond species distribution modeling: a landscape genetics approach to investigating range shifts under future climate change. Ecol. Inform. 30, 250–256 (2015).Article 

    Google Scholar 
    42.Rodríguez-Durán, A. Bat assemblages in the West Indies: the role of caves. In Island Bats: Evolution, Ecology and Conservation (eds Fleming, T. H. & Racey, P.) 265–280 (University of Chicago Press, 2009).
    Google Scholar 
    43.Nassar, J. M., Aguirre, L. F., Rodríguez-Herrera, B. & Medellín, R. A. Threats, status, and conservation perspectives for leaf-nosed bats. In Phyllostomid Bats: A Unique Mammalian Radiation (eds Fleming, T. H. et al.) 470 (University of Chicago Press, 2020).
    Google Scholar 
    44.Rodríguez-Durán, A. Nonrandom aggregations and distribution of cave-dwelling bats in Puerto Rico. J. Mammal. 79, 141–146 (1998).Article 

    Google Scholar 
    45.Rodríguez-Durán, A. & Padilla-Rodríguez, E. New records for the bat fauna of Mona Island, Puerto Rico, with notes on their natural history. Caribb. J. Sci. 46, 102–105 (2010).Article 

    Google Scholar 
    46.Rodríguez-Durán, A. & Feliciano-Robles, W. Conservation value of remnant habitat for neotropical bats on islands. Caribb. Nat. 35, 1–10 (2016).
    Google Scholar 
    47.Gómez-Ruiz, E. P. & Lacher, T. E. Modelling the potential geographic distribution of an endangered pollination corridor in Mexico and the United States. Divers. Distrib. 23, 67–78 (2017).Article 

    Google Scholar 
    48.Shah, V. B. & McRae, B. H. Circuitscape: a tool for landscape ecology. In Proceedings of the 7th Python in Science Conference, vol. 7, 62–66 (SciPy Conference California, 2008).49.McRae, B. H., Dickson, B. G., Keitt, T. H. & Shah, V. B. Using circuit theory to model connectivity in ecology, evolution, and conservation. Ecology 89, 2712–2724 (2008).PubMed 
    Article 
    PubMed Central 

    Google Scholar 
    50.Carroll, C., McRae, B. H. & Brookes, A. Use of linkage mapping and centrality analysis across habitat gradients to conserve connectivity of Gray wolf populations in Western North America. Conserv. Biol. 26, 78–87 (2012).PubMed 
    Article 
    PubMed Central 

    Google Scholar 
    51.Theobald, D. M., Reed, S. E., Fields, K. & Soulé, M. Connecting natural landscapes using a landscape permeability model to prioritize conservation activities in the United States. Conserv. Lett. 5, 123–133 (2012).Article 

    Google Scholar 
    52.Dutta, T., Sharma, S., McRae, B. H., Roy, P. S. & DeFries, R. Connecting the dots: mapping habitat connectivity for tigers in central India. Reg. Environ. Change 16, 53–67 (2016).Article 

    Google Scholar 
    53.Mallory, C. D. & Boyce, M. S. Prioritization of landscape connectivity for the conservation of Peary caribou. Ecol. Evol. 9, 2189–2205 (2019).PubMed 
    PubMed Central 
    Article 

    Google Scholar 
    54.Osipova, L. et al. Using step-selection functions to model landscape connectivity for African elephants: accounting for variability across individuals and seasons. Anim. Conserv. 22, 35–48 (2019).Article 

    Google Scholar 
    55.GBIF.org. GBIF Occurrence Download (2019). https://doi.org/10.15468/dl.atjvik56.Fick, S. E. & Hijmans, R. J. WorldClim 2: new 1-km spatial resolution climate surfaces for global land areas. Int. J. Climatol. 37, 4302–4315 (2017).Article 

    Google Scholar 
    57.Vermote, E. & NOAA CDR Program. NOAA Climate Data Record (CDR) of AVHRR Normalized Difference Vegetation Index (NDVI), Version 5 (2019). https://doi.org/10.7289/V5ZG6QH9.58.de Moraes, W. M. & Viveiros Grelle, C. E. Does environmental suitability explain the relative abundance of the tailed tailless bat, Anoura caudifer. Nat. Conserv. 10, 221–227 (2012).Article 

    Google Scholar 
    59.Gutiérrez, E. E., Boria, R. A. & Anderson, R. P. Can biotic interactions cause allopatry? Niche models, competition, and distributions of South American mouse opossums. Ecography 37, 741–753 (2014).Article 

    Google Scholar 
    60.Gutiérrez, E. E. et al. The taxonomic status of Mazama bricenii and the significance of the Táchira depression for mammalian endemism in the Cordillera de Mérida, Venezuela. PLoS ONE 10, 1–24 (2015).
    Google Scholar 
    61.Ancillotto, L., Mori, E., Bosso, L., Agnelli, P. & Russo, D. The Balkan long-eared bat (Plecotus kolombatovici) occurs in Italy—first confirmed record and potential distribution. Mamm. Biol. 96, 61–67 (2019).Article 

    Google Scholar 
    62.Alberdi, A., Aizpurua, O., Aihartza, J. & Garin, I. Unveiling the factors shaping the distribution of widely distributed alpine vertebrates, using multi-scale ecological niche modelling of the bat Plecotus macrobullaris. Front. Zool. 11, 77 (2014).PubMed 
    PubMed Central 
    Article 

    Google Scholar 
    63.Phillips, S. J., Anderson, R. P. & Schapire, R. E. Maximum entropy modeling of species geographic distributions. Ecol. Model. 190, 231–259 (2006).Article 

    Google Scholar 
    64.Phillips, S. J. & Dudík, M. Modeling of species distributions with Maxent: new extensions and a comprehensive evaluation. Ecography (Cop.) 31, 161–175 (2008).Article 

    Google Scholar 
    65.R Core Team. R: A Language and Environment for Statistical Computing (2018).66.Muscarella, R. et al. ENMeval: an R package for conducting spatially independent evaluations and estimating optimal model complexity for Maxent ecological niche models. Methods Ecol. Evol. 5, 1198–1205 (2014).Article 

    Google Scholar 
    67.Hirzel, A. H., Le Lay, G., Helfer, V., Randin, C. & Guisan, A. Evaluating the ability of habitat suitability models to predict species presences. Ecol. Model. 199, 142–152 (2006).Article 

    Google Scholar  More

  • in

    Isolation and screening of multifunctional phosphate solubilizing bacteria and its growth-promoting effect on Chinese fir seedlings

    Plant materialsIn April 2019, 2-year-old Chinese fir seedlings were collected from the Yalin Center of the Chinese Academy of Forestry in good condition and free from pests and diseases. (The use of Chinese fir seedlings in the experiment complies with national regulations).MediumPikovskava (PVK) solid medium: glucose 10 g, Ca3(PO4) 25 g, CaCO35g, (NH4)2SO40.5 g, NaCl 0.2 g, MgSO4 7H2O 0.1 g, KCl 0.1 g, MnSO4 0.002 g, FeSO4 7H2O 0.002 g, agar 18 g, Distilled water 1000 mL, pH 7.0.PVK liquid medium: PVK solid medium without agar.Luria-Bertan (LB) medium: tryptone 10 g, yeast extract powder 5 g, NaCl 10 g, agar 18 g, distilled water 1000 mL, pH7.0.LB liquid medium:LB solid medium without agar.Isolation and purification of endophytes from Chinese fir seedlingsThe roots, stems, and leaves of the selected Chinese fir seedlings were washed away with running water to remove the surface soil, and then washed with running water for 24 h to 36 h, and the surface moisture was absorbed with sterile filter paper. Weigh 1 g of roots, stems and leaves in a petri dish, and then carry out surface disinfection in a sterile operating table with 75% alcohol (C2H5OH) for 30 s, 5% sodium hypochlorite (NaClO) 10 min, wash the sterile water 7 times, and use sterile filter paper to absorb the water. The material after surface sterilization is cut into 2 mm × 2 mm with sterile surgical scissors, placed in a sterilized mortar and grated with a small amount of sterile quartz sand and ground into a homogenate, then diluted with sterile water to 10–1, 10–2 and 10–3, pipette to draw 150 µL of sample grinding fluid, spread on the medium, set the sterile water of the last rinse of Chinese fir tissue as a blank control, incubate with other plates under the same conditions, and verify whether the surface disinfection. Cultivate in a 28 ℃ incubator according to the characteristics of the colony phenotype, and use the streak separation method to further purify and isolate the strains until the isolation of the colony morphology is uniform for each isolate.Note: 75% C2H5OH: 75 mL absolute ethanol + 25 mL sterile deionized water; 5% NaClO: sodium hypochlorite solution with 10% available chlorine: sterile deionized water = 1:1.Characterization of PGP traitsDetermination of phosphorus solubilizing abilityThe strain was inoculated into PVK liquid medium and cultured at 28 ℃ for 180 days/min on a reciprocating shaker for 7 days, and then the pH value of the medium was measured. The culture solution was centrifuged at 8000 rpm for 15 min to remove bacterial cells. Take the supernatant and use the molybdenum antimony scandium colorimetric method23 to determine the soluble phosphorus content in the culture broth.Determination of nitrogenase activityAn aliquot of 200 µL fresh culture was inoculated to 20 mL of nutrient broth and incubated overnight at 30℃. Bacterial growth was collected by centrifugation and was washed twice using sterile water, and resuspended by liquid limited nitrogen culture medium (OD600 = 0.2). The 3 mL suspension was transferred to a 25 mL sterilized serum vial and 2.4 mL acetylene gas (99.9999%) was driven into the serum bottle, and then incubated at 30 °C for 12 h. The ethylene content and the protein of bacterial suspension were determined as You et al.24.1-Aminocyclopropane-1-carboxylate (ACC) deaminase activity determinationACC deaminase activity was determined by the method of Glick et al.25 using N-free medium (Nfb)26 for bacteria and minimal medium (MM)27 for actinomycetes containing 0.3 m mol L−1 ACC (Sigma, USA) as a sole nitrogen source. MM with 0.1% (w/v) NH4(SO4)2 was used as a positive control and cultivation without ACC was used as a negative control. After incubation at 28 ℃ for 7 days for non-actinomycete bacteria and 14 days for actinomycetes, colony growth on Nfb or MM with addition of ACC indicated ACC deaminase activity.Indole-3-acetic acid (IAA) productionIAA production was measured by colorimetric assay27. Bacterial isolates were cultured for 3 days in TY broth (without L-tryptophan or supplemented with 500 μg/mL of l-tryptophan) in the dark at 28 °C. Cells were removed from the culture medium by centrifugation at 13,000×g for 10 min; then, 1 mL of the supernatant was mixed vigorously with 2 mL of Salkowski’s reagent (4.5 g of FeCl3 per L in 10.8 M H2SO4). Samples were incubated at room temperature for 30 min and the IAA production was estimated from the optical density at 600 nm (OD600) by comparison with a standard curve prepared from known concentrations of IAA.Siderophore productionSiderophore production was examined by using chrome azurol S (CAS) agar28. Isolate was inoculated onto CAS agar, cultured at 28 °C for 2 days, and the positive strain was indicated by an orange halo around the bacterial colony. Determine the ratio (D/d) of orange aperture diameter (D) to colony diameter (d) to determine the iron-producing carrier capacity of the strain.Physiological and biochemical tests of phosphate-solubilizing bacteriaThe conventional physiological and biochemical identification of PSB is carried out according to the methods in the “Common Bacterial System Identification Manual”, which mainly includes Gram stain, glucose hydrolysis test, lactose hydrolysis test, methyl red test, Voges-Proskauer (VP) test, hydrogen sulfide production test, gelatin liquefaction Test, citrate utilization test, malonate utilization test, denitrification test.16 SrRNA gene sequencingTaking the screened multifunctional PSB as the object, the bacterial genomic DNA extraction kit of Beijing Bomed Biotechnology Co., Ltd. was used to extract the DNA of the strain, using the DNA as a template, and using the bacterial universal primer 27F (5′-AGAGTTTGATCCTGGCTCAG-3′) and 1492R (5′-GGTTACCTTGTTACGACTT-3′) PCR amplification, the amplification system is as follows: DNA template 1 uL, primer 27F 0.5 µL, 1492R 0.5 µL, 2 × TaqMix 12.5 µL, ddH2O10.5 µL. The PCR procedure is as follows: 93℃ for 3 min, 93℃ for 30 s, 56 ℃ for 30 s, 72℃ for 2 min, 32 cycles; 72 ℃ for 7 min. The amplified products were sequenced bidirectionally by BGI. After splicing the measured 16SrDNA sequences in ContigExpress, search in GenBank, EzTaxon, BIGSdb databases respectively, select the model strains with high homology. The phylogenetic tree was constructed by the neighbor-joining method using MEGA version 7.0 with the Kimura 2-parameter model29, the robustness of the tree was evaluated by performing bootstrap analyses based on 1000 replications30.Evaluation of plant growth promotion by individual inoculationPreparation of inoculumThe single colonies were picked out and incubated in LB broth at 180 rpm at 28 ℃ for 12 h. The above solution was inserted into 200 mL of LB broth at 1% inoculation, incubated at 180 rpm at 28℃ for 48 h and the cell pellet was resuspended in sterile distilled water and made up to a final concentration of 3 × 108 CFU/mL.Experimental seedlings and soilChinese fir seedlings were provided by the Experimental Center of Subtropical Forestry, Chinese Academy of Forestry (117° 67′ E, 27° 82′ N), Jiangxi Province, China. The use of Chinese fir seedlings in the experiment complies with national regulations. Five months old seedlings with vigorous and apparently disease and pest free were used. The height and root collar diameters of seedlings were 8.7 cm and 1.36 mm, respectively. The seedling container was made of non-woven fabric, the specification was 4.5 cm × 8.0 cm (Diameter × Height). The soil was consisted of nursery medium and loess at a ratio of 9:1, was thoroughly mixed and homogenized with 3 kg slow-release fertilizer per cubic. The slow-release fertilizer is produced by American Abbes (180 g kg−1 total N, 80 g kg−1 available P, and 80 g kg−1 total K, the fertilizer effect period is 9 months). The soil exhibited the following properties: 6.34 g kg−1 total N, 0.80 g kg−1 total P, 2.50 g kg−1 total K, and a pH-value of 6.00.Test designThe SSP2, JRP22 and HRP2, which were confirmed to have the characteristics of promoting plant growth, so pot experiments were conducted. To determine the effectiveness of phosphorus-solubilizing bacteria in plant growth of Chinese fir, a pot culture experiment was conducted between August and November 2019 in an open-sided greenhouse in Experimental Center of Subtropical Forestry, Chinese Academy of Forestry, Jiangxi Province, China. The experiment was carried out in three-factor orthogonal design with five replications for each treatment. The orthogonal experimental design of experiment is provided in Table 1, and strain, dilution ratio, inoculation method contained 3 levels. The pots with water was used as control (CK). For the irrigation of the rhizosphere (IR) treatments, 30 mL of diluted inoculum was added to the soil in the vicinity of the roots of Chinese fir. For the foliar spray (FS) treatments, 30 mL diluted bacterial cell suspension was inoculated in the leaves of Chinese fir by using a syringe. For the rhizosphere + foliar spray (IS) treatments, 15 mL of diluted inoculum was inoculated in the rhizosphere of seedlings, 15 mL was added to the leaves of seedlings by foliar spray. Each treatment contained sixteen seedlings for a total of nine treatments. A total of 3 inoculations were given in the middle of each month. The plant height and stem diameter were recorded before the first inoculation. The plants were harvested after 90 days (16 plantlets/replicate/treatment, i.e., a total of 80 plantlets per treatment) and the root biomass, stem biomass, leaf biomass, plant height and stem diameter were measured.Table 1 L9(34) Orthogonal design of experiment.Full size tableDetermination of growth indicatorsDuring the test, before each inoculation, the height of the seedlings was measured with a ruler and the ground diameter of the seedlings was measured with a vernier caliper. After the experiment, 10 plants of Chinese fir seedlings in average growth were randomly selected from each treatment, a total of 30 plants were washed with clean water to remove surface impurities, the filter paper was dried and the roots, stems, and leaves were put into paper bags respectively at 105 °C. After being degraded for 0.5 h, dried at 70 °C to a constant weight, weighed and recorded the biomass of each part.Determination of leaf and soil nutrient contentTotal N content of leaf and soil was measured by a 2300 Kjeltec Analyzer Unit (FOSS, Höganäs, Sweden). Total P and total K, total Mg and total Fe of leaf, soil TP, TK, AP and AK were extracted according to literature31 and were determined by ICP (Kleve, Germany).Determination of soil enzyme activitiesActivities of the soil urease, cellulase, sucrase, dehydrogenase and acid phosphatase were determined by spectrophotometry. Firstly, 0.05 g of soil was added to 450 mL of phosphate buffer solution (PBS, 0.1 mol L−1, pH 7.4). Then the solution was mixed by shaking, and centrifuged at 2000 rpm at 4 ℃ for 10 min and supernatant was collected with a new centrifugal tube. The supernatant and reagents were added according to the kit instructions (Shanghai Enzyme-linked Biotechnology Co., Ltd., Shanghai, China). Absorbance at 450 nm was measured on a SpectraMax Paradigm Multi-Mode detection platform (Molecular devices, San Jose, CA, USA).Data processing and analysisAll statistical analyses were performed using SPSS24. Data are presented in terms of means (± SE; standard error). Statistical differences were tested by one-factor ANOVA to evaluate the differences in the nutrient content of soil and plant growth status. In MEGA7.0, the Neighbor-Joining method was used to construct the phylogenetic tree, and the Bootstrap value was 1000. More

  • in

    Serum correlation, demographic differentiation, and seasonality of blubber testosterone in common bottlenose dolphins, Tursiops truncatus, in Sarasota Bay, FL

    1.Kellar, N. M. et al. Blubber testosterone: a potential marker of male reproductive status in short-beaked common dolphins. Mar. Mamm. Sci. 25(3), 507–522 (2009).CAS 
    Article 

    Google Scholar 
    2.Atkinson, S. & Yoshioka, M. Endocrinology of reproduction. In Reproductive biology and phylogeny of Cetacea. Whales, dolphins and porpoises (ed. Miller, D. L.) 171–192 (Science Publishers, 2007).
    Google Scholar 
    3.Cates, K. A. et al. Testosterone trends within and across seasons in male humpback whales (Megaptera novaeangliae) from Hawaii and Alaska. Gen. Comp. Endocrinol. 279, 164–173 (2019).CAS 
    PubMed 
    Article 

    Google Scholar 
    4.McKenna, T. J. et al. 2 A critical review of the origin and control of adrenal androgens. Baillieres Clin. Obstet. Gynaecol. 11(2), 229–248 (1997).CAS 
    PubMed 
    Article 

    Google Scholar 
    5.Sharpe, R. et al. Testosterone and Spermatogenesis identification of stage-specific, androgen-regulated proteins secreted by adult rat seminiferous tubules. J. Androl. 13, 172–184 (1992).CAS 
    PubMed 

    Google Scholar 
    6.Kita, S., Yoshioka, M. & Kashiwagi, M. Relationship between sexual maturity and serum and testis testosterone concentrations in short-finned pilot whales Globicephala macrorhynchus. Fish. Sci. 65(6), 878–883 (1999).CAS 
    Article 

    Google Scholar 
    7.Schroeder, J. P. & Keller, K. V. Seasonality of serum testosterone levels and sperm density in Tursiops truncatus. J. Exp. Zool. 249(3), 316–321 (1989).CAS 
    PubMed 
    Article 

    Google Scholar 
    8.Robeck, T. R. et al. Reproduction, growth and development in captive beluga (Delphinapterus leucas). Zoo Biol. 24(1), 29–49 (2005).Article 

    Google Scholar 
    9.Wells, R. Reproductive behavior and hormonal correlates in Hawaiian spinner dolphins, Stenella longirostris. In Reproduction in Whales, Dolphins, and Porpoises (eds Perrin, W. F. et al.) 465–472 (Reports of the International Whaling Commission, 1984).
    Google Scholar 
    10.Mogoe, T. et al. Functional reduction of the southern minke whale (Balaenoptera acutorostrata) testis during the feeding season. Mar. Mamm. Sci. 16(3), 559–569 (2000).Article 

    Google Scholar 
    11.Kjeld, M. et al. Changes in blood testosterone and progesterone concentrations of the North Atlantic minke whale (Balaenoptera acutorostrata) during the feeding season. Can. J. Fish. Aquat. Sci. 61(2), 230–237 (2004).CAS 
    Article 

    Google Scholar 
    12.Temte, J. L. Use of serum progesterone and testosterone to estimate sexual maturity in Dall’s porpoise Phocoenoides dalli. Fish. Bull. 89(1), 161–166 (1991).
    Google Scholar 
    13.Robeck, T. R. et al. Reproduction, growth and development in captive beluga (Delphinapterus leucas). Zoo Biol. Publ. Affil. Am. Zoo Aquar. Assoc. 24(1), 29–49 (2005).
    Google Scholar 
    14.Kirby, V. L. Endocrinology of marine mammals. In Handbook of Marine Mammal Medicine: Health (ed. Dierauf, L. A.) 303–351 (Disease and Rehabilitation CRC Press Inc, 1990).
    Google Scholar 
    15.Desportes, G., Saboureau, M. & Lacroix, A. Growth-related changes in testicular mass and plasma testosterone concentrations in long-finned pilot whales, Globicephala melas. J. Reprod. Fertil. 102(1), 237–244 (1994).CAS 
    PubMed 
    Article 

    Google Scholar 
    16.Kjeld, J., Sigurjonsson, J. & Arnason, A. Sex hormone concentrations in blood serum from the North Atlantic fin whale (Balaenoptera physalus). J. Endocrinol. 134(3), 405–413 (1992).CAS 
    PubMed 
    Article 

    Google Scholar 
    17.Boggs, A. S. et al. Remote blubber sampling paired with liquid chromatography tandem mass spectrometry for steroidal endocrinology in free-ranging bottlenose dolphins (Tursiops truncatus). Gen. Comp. Endocrinol. 281, 164–172 (2019).CAS 
    PubMed 
    PubMed Central 
    Article 

    Google Scholar 
    18.Weller, D. W. et al. Behavioral responses of bottlenose dolphins to remote biopsy sampling and observations of surgical biopsy wound healing. Aquat. Mamm. 23(1), 49–58 (1997).19.Krahn, M. M. et al. Stratification of lipids, fatty acids and organochlorine contaminants in blubber of white whales and killer whales. J. Cetac. Res. Manage. 6(2), 175–189 (2004).
    Google Scholar 
    20.Marsili, L. et al. Skin biopsies for cell cultures from Mediterranean free-ranging cetaceans. Mar. Environ. Res. 50(1–5), 523–526 (2000).CAS 
    PubMed 
    Article 
    PubMed Central 

    Google Scholar 
    21.Hobbs, K. E. et al. PCBs and organochlorine pesticides in blubber biopsies from free-ranging St. Lawrence River Estuary beluga whales (Delphinapterus leucas), 1994–1998. Environ. Pollut. 122(2), 291–302 (2003).CAS 
    PubMed 
    Article 
    PubMed Central 

    Google Scholar 
    22.Kellar, N. M. et al. Determining pregnancy from blubber in three species of delphinids. Mar. Mamm. Sci. 22(1), 1–16 (2006).Article 

    Google Scholar 
    23.Mingramm, F. et al. Evaluation of respiratory vapour and blubber samples for use in endocrine assessments of bottlenose dolphins (Tursiops spp.). Gen. Comp. Endocrinol. 274, 37–49 (2019).CAS 
    PubMed 
    Article 
    PubMed Central 

    Google Scholar 
    24.Galligan, T. M. et al. Blubber steroid hormone profiles as indicators of physiological state in free-ranging common bottlenose dolphins (Tursiops truncatus). Comp. Biochem. Physiol. A Mol. Integr. Physiol. 239, 110583 (2020).CAS 
    PubMed 
    Article 
    PubMed Central 

    Google Scholar 
    25.Dierauf, L. & Gulland, F. M. CRC Handbook of Marine Mammal Medicine: Health, Disease, and Rehabilitation (CRC Press, 2001).Book 

    Google Scholar 
    26.Champagne, C. D. et al. Comprehensive endocrine response to acute stress in the bottlenose dolphin from serum, blubber, and feces. Gen. Comp. Endocrinol. 266, 178–193 (2018).CAS 
    PubMed 
    Article 
    PubMed Central 

    Google Scholar 
    27.Kellar, N. M. et al. Variation of bowhead whale progesterone concentrations across demographic groups and sample matrices. Endang. Species Res. 22(1), 61–72 (2013).Article 

    Google Scholar 
    28.Richard, J. T. et al. Testosterone and progesterone concentrations in blow samples are biologically relevant in belugas (Delphinapterus leucas). Gen. Comp. Endocrinol. 246, 183–193 (2017).CAS 
    PubMed 
    Article 
    PubMed Central 

    Google Scholar 
    29.Hunt, K. E. et al. Multi-year patterns in testosterone, cortisol and corticosterone in baleen from adult males of three whale species. Conserv. Physiol. 6(1), coy049 (2018).CAS 
    PubMed 
    PubMed Central 
    Article 

    Google Scholar 
    30.Wells, R. S. Dolphin social complexity: lessons from long-term study and life history. In Animal Social Complexity: Intelligence, Culture, and Individualized Societies (eds de Waal, F. B. M. & Tyack, P. L.) 32–56 (Harvard University Press, 2003).
    Google Scholar 
    31.Brook, F. et al. Ultrasonographic imaging of the testis and epididymis of the bottlenose dolphin, Tursiops truncatus aduncas. J. Reprod. Fertil. 119(2), 233–240 (2000).CAS 
    PubMed 
    Article 

    Google Scholar 
    32.Wells, R. S. Social structure and life history of bottlenose dolphins near Sarasota Bay, Florida: Insights from four decades and five generations. In Primates and Cetaceans: Field Research and Conservation of Complex Mammalian Societies, Primatology Monographs (eds Yamagiwa, J. & Karczmarski, L.) 149–172 (Springer, 2014).
    Google Scholar 
    33.Barratclough, A. et al. Health assessments of common bottlenose dolphins (Tursiops truncatus): past, present, and potential conservation applications. Front. Vet. Sci. 6, 444 (2019).PubMed 
    PubMed Central 
    Article 

    Google Scholar 
    34.Champagne, C. D. et al. Blubber cortisol qualitatively reflects circulating cortisol concentrations in bottlenose dolphins. Mar. Mamm. Sci. 33(1), 134–153 (2017).CAS 
    Article 

    Google Scholar 
    35.Norman, A. W. & Litwack, G. Hormones (Academic Press, 1997).
    Google Scholar 
    36.Urian, K. et al. Seasonality of reproduction in bottlenose dolphins, Tursiops truncatus. J. Mammal. 77(2), 394–403 (1996).Article 

    Google Scholar 
    37.Wells, R. Reproduction in wild bottlenose dolphins: overview of patterns observed during a long-term study. in Bottlenose Dolphins Reproduction Workshop. AZA marine mammal taxon advisory group. 2000. Silver Springs, MD.38.Read, A. et al. Patterns of growth in wild bottlenose dolphins, Tursiops truncatus. J. Zool. 231(1), 107–123 (1993).Article 

    Google Scholar 
    39.Trego, M. L. et al. Comprehensive screening links halogenated organic compounds with testosterone levels in male Delphinus delphis from the Southern California bight. Environ. Sci. Technol. 52(5), 3101–3109 (2018).ADS 
    CAS 
    PubMed 
    PubMed Central 
    Article 

    Google Scholar 
    40.Kannan, K. et al. Toxicity reference values for the toxic effects of polychlorinated biphenyls to aquatic mammals. Hum. Ecol. Risk Assess. 6(1), 181–201 (2000).CAS 
    Article 

    Google Scholar 
    41.Jepson, P. D. et al. Relationships between polychlorinated biphenyls and health status in harbor porpoises (Phocoena phocoena) stranded in the United Kingdom. Environ. Toxicol. Chem. Int. J. 24(1), 238–248 (2005).CAS 
    Article 

    Google Scholar 
    42.Minter, L. & DeLiberto, T. Seasonal variation in serum testosterone, testicular volume, and semen characteristics in the coyote (Canis latrans). Theriogenology 69(8), 946–952 (2008).CAS 
    PubMed 
    Article 
    PubMed Central 

    Google Scholar 
    43.Preston, B. T. et al. Testes size, testosterone production and reproductive behaviour in a natural mammalian mating system. J. Anim. Ecol. 81(1), 296–305 (2012).PubMed 
    Article 
    PubMed Central 

    Google Scholar 
    44.Desportes, G., Saboureau, M. & Lacroix, A. Growth-related changes in testicular mass and plasma testosterone concentrations in long-finned pilot whales Globicephala melas. Reproduction 102(1), 237–244 (1994).CAS 
    Article 

    Google Scholar 
    45.Ryan, C. et al. Lipid content of blubber biopsies is not representative of blubber in situ for fin whales (Balaenoptera physalus). Mar. Mamm. Sci. 29(3), 542–547 (2013).CAS 
    Article 

    Google Scholar 
    46.Wells, R. S. et al. Bottlenose dolphins as marine ecosystem sentinels: developing a health monitoring system. EcoHealth 1(3), 246–254 (2004).Article 

    Google Scholar 
    47.Wells, R. S. et al. Integrating life-history and reproductive success data to examine potential relationships with organochlorine compounds for bottlenose dolphins (Tursiops truncatus) in Sarasota Bay Florida. Sci. Total Environ. 349(1–3), 106–119 (2005).ADS 
    CAS 
    PubMed 
    Article 
    PubMed Central 

    Google Scholar 
    48.Yordy, J. E. et al. Partitioning of persistent organic pollutants between blubber and blood of wild bottlenose dolphins: implications for biomonitoring and health. Environ. Sci. Technol. 44(12), 4789–4795 (2010).ADS 
    CAS 
    PubMed 
    Article 
    PubMed Central 

    Google Scholar 
    49.Kellar, N. M. et al. Low reproductive success rates of common bottlenose dolphins Tursiops truncatus in the northern Gulf of Mexico following the Deepwater Horizon disaster (2010–2015). Endang. Species Res. 33, 143–158 (2017).Article 

    Google Scholar 
    50.Kellar, N. M. et al. Blubber cortisol: a potential tool for assessing stress response in free-ranging dolphins without effects due to sampling. PLoS ONE 10(2), e0115257 (2015).PubMed 
    PubMed Central 
    Article 
    CAS 

    Google Scholar 
    51.Harrison, R. & Ridgway, S. Gonadal activity in some bottlenose dolphins (Tursiops truncatus). J. Zool. 165(3), 355–366 (1971).Article 

    Google Scholar 
    52.Wells, R. S. & Scott, M. D. Bottlenose Dolphin: common bottlenose dolphin: Tursiops truncates. In Encyclopedia of Marine Mammals 3rd edn (eds Würsig, B. et al.) 118–125 (Academic Press/Elsevier, 2009).
    Google Scholar 
    53.R Core Team. R: A Language and Environment for Statistical Computing. 2020, R Foundation for Statistical Computing: 2020, Vienna, Austria. URL https://www.R-project.org/.54.Wells, R. S. & Scott, M. D. Common Bottlenose Dolphin: Tursiops truncates, in Encyclopedia of Marine Mammals 252 (Elsevier, 2009).
    Google Scholar  More

  • in

    Correspondence analysis, spectral clustering and graph embedding: applications to ecology and economic complexity

    Let us first describe the setting and introduce notation. The main object of analysis is a matrix A (a contingency table with (n_r) rows and (n_c) columns) that contains the counts of two variables. A common example from ecology is that (A_{ij}) contains some measure of abundance of species i (rows) in sampling site j (columns). The matrix A can also be a binary incidence matrix, containing either the presence (1) or absence (0) of species in sites. The matrix A can be interpreted as the bi-adjacency matrix of a bipartite network that connects species to sites. The network contains (n_r) nodes on one side (the species, given by the rows of A, indexed by i), and (n_c) nodes on the other side (the sites, given by the columns of A, indexed by j). In general, we will refer to the two sets of nodes as row nodes and column nodes, respectively. The degree of a row node i is defined by the row sum (r_i = sum _j A_{ij}), which gives the total abundance of species i in all sites. Likewise, the degree of a column node j is defined as the column sum (c_j = sum _i A_{ij}), which gives the total abundance of species in a site j. The degrees of the row and column nodes are given by the vectors (mathbf {r}= (r_1, r_2, dots , r_{n_r})^T) and (mathbf {c}= (c_1,c_2,dots ,c_{n_c})^T). We further define two square matrices, (D_r) ((n_r times n_r)) and (D_c) ((n_c times n_c)) as the diagonal matrices that have (mathbf {r}) and (mathbf {c}) on the diagonal, respectively. The sum (n = sum _{ij} A_{ij}) gives the total number of occurrences in the table (in the case of a species-site example, the total abundance of species).CA as canonical correlation analysisOne of the first derivations of CA was obtained by applying canonical correlation analysis to categorical variables12,19,22. Here we follow the derivation in Ref.1 (Chapter 9), where CA is derived as an application of canonical correlation analysis applied to a bipartite network, and to which we refer for further details. For ease of explanation, we will assume the network is defined by a binary presence-absence matrix (i.e. the network is unweighted), but the result generalizes to any contingency table (i.e. weighted bipartite networks).The aim is to assign a ‘score’ to each node in the network, under the assumption that row and column nodes with similar scores connect to each other. Hence, connected nodes get assigned similar scores, and the scores can be thought of as a latent variable that drive the formation of links in the network. In ecology, such latent variables are referred to as gradients2,3. Considering a bipartite network describing the occurrence of species in a set of sites, for example, the resulting scores may reflect some variable determining why species locate in specific sites, such as the temperature preference of a species and the temperature at a site. In practice, the interpretation of a gradient resulting from application of CA can be verified by correlating it with known environmental variables (e.g. data on the temperature of each site).Mathematically, such gradients can be inferred from the edges of the bipartite network. Recall that for a presence-absence matrix, the total number of edges in the bipartite network is given by (n = sum _{ij} A_{ij}). Let us construct a vector (mathbf {y}_r) of length n that contains, for each edge, the scores of the row node it connects to, and a vector (mathbf {y}_c) of length n that contains, again for each edge, the score of the column node it connects to. Given the assumption that edges connect row nodes and column nodes with similar scores, the node scores can be found by maximizing the correlation between (mathbf {y}_r) and (mathbf {y}_c), so that the row- and column scores for each edge are as similar as possible. Denoting the vector of length (n_r) containing the row scores by (mathbf {v}) and the vector of length (n_c) containing the column scores by (mathbf {u}), this leads to the optimization problem$$begin{aligned} max _{mathbf {v}, mathbf {u}} mathrm {corr}(mathbf {y}_r,mathbf {y}_c). end{aligned}$$
    (1)
    In order to obtain standardized scores, the constraints that (mathbf {y}_r) and (mathbf {y}_c) have zero mean and unit variance need to be added. Solving this problem using Lagrangian optimization, the solution is given by$$begin{aligned} D_r^{-1}A D_c^{-1} A^T mathbf {v}&= lambda mathbf {v}nonumber \ D_c^{-1}A^T D_r^{-1} A mathbf {u}&= lambda mathbf {u}. end{aligned}$$
    (2)
    The score vectors (mathbf {v}) and (mathbf {u}) can thus be found by solving an eigenvector problem. Following Ref.1 , they are subject to the constraint that (|mathbf {v}|=|mathbf {u}|=1). The general interpretation of the elements of (mathbf {v}) and (mathbf {u}) is as follows. Each row node (of A) is represented in (mathbf {v}), and each column node is represented in (mathbf {u}). The smaller the difference between the values of two row (column) nodes in (mathbf {v}) ((mathbf {u})), the more similar these nodes are. The similarity among row nodes that is reflected in (mathbf {v}) vectors arises because they are connected to a similar set of column nodes in the original bipartite network (vice versa for similarities in (mathbf {u})). In literature, this is referred to as row nodes being similar because of their similar ‘profile’11,23, and reciprocal averaging defines exactly how the scores are calculated in terms of the profiles and reduces to the same set of equations15. Both matrices on the left-hand side of Eq. (2) are row-stochastic and positive definite, and have identical eigenvalues that are real and take values between 0 and 1. Assuming that we have a connected network, sorting the eigenvalues in decreasing order leads to (1=lambda _1 > lambda _2 dots ge 0).It can be shown that the correlation between (mathbf {y}_r) and (mathbf {y}_c) for a given set of eigenvectors (mathbf {v}) and (mathbf {u}) is given by their corresponding eigenvalue, so that (lambda = mathrm {corr}^2(mathbf {y}_{r},mathbf {y}_{c})). Note that the correlations between the row and column vectors can be negative, meaning that merely the absolute value of the correlation between (y_r) and (y_c) is related to the (square root) of the eigenvalues. Iterative approaches to extract potential negative correlations exist in literature24. The node scores leading to the highest correlation are thus given by the eigenvectors associated with the largest eigenvalue. However, the eigenvectors corresponding to (lambda _1) have all constant values and represent the trivial solution in which all row nodes and all column nodes have equal scores (leading to a perfect correlation). This trivial solution does not satisfy the condition that the scores have to be centered, and thus it must be rejected. The solution to Eq. (1) is thus given by the eigenvectors (mathbf {v}_2) and (mathbf {u}_2), corresponding to the second largest eigenvalue (lambda _2), which corresponds to the square root of the (maximized) correlation. We notice here that this derivation leads to analogous results than observed in classical derivations of CA, where the matrix A is centered both with respect to the rows and to the columns.The second eigenvectors (mathbf {v}_2) and (mathbf {u}_2) hold the unique scores such that row- and column nodes with similar scores connect to each other. The second eigenvalue (lambda _2) indicates to what extent the row- and column scores can be ‘matched’, where high values (close to 1) indicate a high association between the inferred scores (the gradient) and the structure of the network.The higher order eigenvectors in Eq. (2) and their eigenvalues are solutions to Eq. (1) with the additional constraint that (mathbf {y}_r) and (mathbf {y}_c) are orthogonal to the other solutions. The vectors (mathbf {v}_3) and (mathbf {u}_3), for example, may represent other variables that drive the formation of links (e.g. precipitation, primary productivity, etc.) on top of the gradients described by (mathbf {v}_2) and (mathbf {u}_2). We note that, differently from notation in some CA literature, we here denote the k-th non-trivial eigenvector with the subscript k+1.CA as a clustering algorithmA completely different approach shows that the eigenvectors (mathbf {v}_2) and (mathbf {u}_2) (i.e. the second eigenvectors in Eq. (2)) can also be interpreted as cluster labels, obtained when identifying clusters in the network of similarities that is derived from the bipartite network.A similarity network can be constructed from a bipartite network by ‘projecting’ the bipartite network onto one of its layers (either the row nodes or the column nodes) through stochastic complementation18. Projecting the bipartite network defined by A onto its row layer leads to the (n_r times n_r) similarity matrix (S_r = A D_c^{-1} A^T). The entries of (S_r) represent pairwise similarities between row nodes of A, based on how many links they share with the same column node, weighted for the degree of each column node. Similarly, the (n_c times n_c) similarity matrix (S_c = A^T D_r^{-1} A) defines the pairwise similarities between the column nodes of A.Identifying clusters in the similarity network can be done by minimizing the so-called ‘normalized cut’20. The normalized cut assigns, for a given partition of a network into K clusters, a score that represents the strength of the connections between the clusters for that partition. A partition can be described by assigning a discrete cluster label to each node. Hence, minimizing the normalized cut is equivalent to assigning a cluster label to each node in the network in such a way that the clusters are minimally connected. Finding the discrete cluster labels that minimize the normalized cut in large networks is in general not possible20. However, a solution of a related problem can be obtained when the cluster labels are allowed to take continuous values as opposed to discrete values. Solutions of this ‘relaxed’ problem can be interpreted as continuous approximations of the discrete cluster labels.Minimizing the normalized cut in (S_r) leads to the generalized eigensystem20$$begin{aligned} (D_r – S_r) mathbf {v}= tilde{lambda } D_r mathbf {v}, end{aligned}$$
    (3)
    where the entries of the generalized eigenvector (mathbf {v}_2) corresponding to the second smallest eigenvalue (tilde{lambda }_2) of Eq. (3) hold the approximate cluster labels of the optimal partition into two clusters. It is easily shown that generalized eigenvectors in Eq. (3) are exactly the eigenvectors of Eq. (2), where the eigenvalues are related by (tilde{lambda }_k = 1 – lambda _k), where (k=1,2,dots ,n_r) (see “Suppl. Material A”).The matrix (L_r = D_r-S_r) is known as the Laplacian matrix of the similarity network defined by (S_r), and is well known in spectral graph theory25. The number of eigenvalues of (L_r) for which (tilde{lambda } = 0) (or equivalently (lambda = 1) in Eq. (2)) denotes the number of disconnected clusters in the network. Each of these ’trivial’ eigenvalues has a corresponding generalized eigenvector that has constant values for the nodes in a particular cluster, indicating cluster membership.The situation changes when the clusters are weakly connected. The optimal solution for partitioning the similarity network into two clusters is given by the eigenvector (mathbf {v}_2) associated to eigenvalue (lambda _2). Although continuous, the entries of (mathbf {v}_2) can be interpreted as approximations to cluster labels, which indicate for each row node to which cluster it belongs. In other words, nodes with high values in this eigenvector (i.e., high scores) belong to one cluster, and nodes with low scores to the other. A discrete partition can then be obtained from the approximate (continuous) cluster labels by discretizing them, for example by assigning all negative values to one cluster and all positive values to the other26. The corresponding eigenvalue (lambda _2) represents the quality of the partitioning, as determined by the normalized cut criterion. High values are indicative of a network that can be well partitioned into two clusters (two totally disconnected clusters would yield eigenvalues (lambda _1 = lambda _2=1)), whereas lower values correspond to a network that is less easily grouped into two clusters (i.e. the resulting clusters are more interconnected).Finding a partitioning into multiple, say K, clusters is more involved, where (Kle n_r) (or (Kle n_c) if working with column variables). Minimizing the normalized cut for K clusters yields a trace minimization problem of which the relaxed solution is given by the first K eigenvectors in Eq. (2)27. Because the first eigenvector in Eq. (2) is trivial, in practice we only require (K-1) eigenvectors (i.e., the 2nd, 3rd, … up to the Kth). The discrete cluster labels can then be obtained, for example, by running a k-Means algorithm on the matrix consisting of those (K-1) eigenvectors, a technique that is also known as spectral clustering28,29. How well the network can be partitioned into K clusters is given by the average value of the first K eigenvalues, i.e. (frac{1}{K} sum _{k=1}^K lambda _k)27.The clustering approach thus brings an alternative interpretation to CA results. A key observation is that the eigenvalues and eigenvectors in Eq. (2) are directly related to the generalized eigenvectors of the Laplacian of the similarity matrix (S_r), and thus hold information on the structure of the similarity network. The entries of the second eigenvector (mathbf {v}_2) can be interpreted as the approximate cluster labels of a two-way partitioning of the similarity network defined by (S_r). Although at first sight the interpretation of CA scores as cluster labels may seem different from the interpretation as a latent variable described above in “CA as canonical correlation analysis”, note that cluster labels can be seen as latent variables, albeit discrete rather than continuous.CA as a graph embedding techniqueA third interpretation of the eigenvectors and eigenvalues in Eq. 2 arises from a so-called graph embedding of the similarity matrix (S_r) (or (S_c)). Graph embeddings provide a way to obtain a low-dimensional representation of a high-dimensional network, that are used for example for graph drawing. A graph embedding represents the nodes of a graph as node vectors in a space, such that nodes that are ‘close’ in the network are also close in terms of their distance in the embedding. A key feature of these embeddings is that their dimensionality can be reduced in order to obtain a low-dimensional representation of the data, while retaining its most important structural properties (see Ref.1, chapter 10 for an overview of graph embedding techniques).As noted by several authors, CA is equivalent to graph embedding in the case of a similarity matrix obtained through stochastic complementation. For example, computing a 1-step diffusion map of the similarity matrix (S_r) leads exactly to the eigenvectors of Eq. (2)18,30. Also, the graph embedding using the Laplacian eigenmap has been shown to be equivalent to graph partitioning using the normalized cut, which is in turn equivalent to CA31. CA-specific type of embedding is based on the chi-square statistics and it is thus Euclidean.Embedding the similarity network (S_r) in a ((K-1))-dimensional space yields an ‘embedding matrix’ (X_r in mathbb {R}^{n_r times K-1}) (known in CA-related literature as ’principal coordinates’). Each row of (X_r) represents a node of (S_r) as a ‘node vector’ in the embedding. The rows of (X_r) can be seen as components of ((K-1))-dimensional basis vectors that span the embedding, and are identical to what is referred to as the ‘axes’ in CA. Every entry (X_{i,k}) represents the coordinate of row node i on the k’th basis vector, and can be seen as the ‘score’ of i on the k’th CA axis. An embedding matrix of (S_r) can defined as (X_r = [sqrt{lambda _2} mathbf {v}_2, dots , sqrt{lambda _K} mathbf {v}_{K}]), where the vectors (mathbf {v}_k) are the eigenvectors defined in (2), and each of them is weighted by the square root of their corresponding eigenvalue. We will refer to columns of the embedding matrix as ‘CA-axes’, given by (mathbf {x}_k = sqrt{lambda _k}mathbf {v}_k) (with (mathbf {x}_2) being the ’first CA axis’, and so on).The axes are constructed in such a way that they capture the largest amount of ‘variation’ or ‘inertia’ in the data, which is given by their corresponding eigenvalue11. The sum of all the eigenvalues gives the total variation in the data (in CA, this is referred to as the total inertia). CA decomposes the total variation in such a way that the first axis captures a maximal part of the variation, the second a maximal part of the remaining variation, and so on. A low-dimensional embedding that preserves the maximal amount of variation can thus be obtained by discarding the eigenvectors corresponding to smaller eigenvalues. The ‘quality’ of the embedding can then be expressed as the share of the total variation that is preserved in the embedding.A typical way of presenting CA results is by showing the first two coordinates of each row (or column) node, i.e. plotting (mathbf {x}_2) against (mathbf {x}_3), which is usually referred to as a ’correspondence plot’. Since the first two axes capture a maximal amount of inertia, such a plot is in a way the optimal two-dimensional representation of the data that captures the relations between the rows (or columns) of A. The distances between points in the correspondence plot approximate the similarities between nodes. How well the correspondence plot represents the similarities is given by the percentage of variation explained by the first two axes.Each axis can be interpreted as a latent variable that account for part of the total variation in the data. Since the axes in the embedding are given by a scaled version of the eigenvectors discussed above in “CA as canonical correlation analysis”, the interpretation of the eigenvalues as the amount of variation explained is complementary to the interpretation as the correlation between row and column scores which we also introduced above in “CA as canonical correlation analysis”. Furthermore, the axes spanning the K-dimensional embedding are exactly the generalized eigenvectors that follow from minimizing the normalized cut for K clusters31. Indeed, when there are clear clusters in the similarity network, they will show up in the embedding space as separate groups of points.Summarizing, we find three interpretations of CA axes and their corresponding eigenvalues: as latent variables that drive the formation of links in the bipartite network, as approximate clusters labels of a bi-partition of the similarity network, and as coordinates of an embedding of the similarity network. The different derivations of CA and their interpretations are summarized in Table 1.Table 1 Different interpretations of the eigenvectors and eigenvalues resulting from CA.Full size table More

  • in

    Decay stages of wood and associated fungal communities characterise diversity–decomposition relationships

    1.Bradford, M. A. et al. Climate fails to predict wood decomposition at regional scales. Nat. Clim. Chan. 4, 625–630 (2014).CAS 
    Article 
    ADS 

    Google Scholar 
    2.Crowther, T. W. et al. The global soil community and its influence on biogeochemistry. Science 365, eaav0550 (2019).CAS 
    PubMed 
    Article 
    PubMed Central 

    Google Scholar 
    3.Lustenhouwer, N. et al. A trait-based understanding of wood decomposition by fungi. Proc. Nat. Acad. Sci. USA 117, 11551–11558 (2020).CAS 
    PubMed 
    Article 
    PubMed Central 

    Google Scholar 
    4.Tilman, D. et al. Diversity and productivity in a long-term grassland experiment. Science 294, 843–845 (2001).CAS 
    PubMed 
    Article 
    ADS 
    PubMed Central 

    Google Scholar 
    5.Ammer, C. Diversity and forest productivity in a changing climate. New Phytol. 221, 50–66 (2019).PubMed 
    Article 
    PubMed Central 

    Google Scholar 
    6.Dickie, I. A., Fukami, T., Wilkie, J. P., Allen, R. B. & Buchanan, P. K. Do assembly history effects attenuate from species to ecosystem properties? A field test with wood-inhabiting fungi. Ecol. Lett. 15, 133–141 (2012).PubMed 
    Article 
    PubMed Central 

    Google Scholar 
    7.van der Wal, A., Ottosson, E. & de Boer, W. Neglected role of fungal community composition in explaining variation in wood decay rates. Ecology 96, 124–133 (2015).PubMed 
    Article 
    PubMed Central 

    Google Scholar 
    8.Hoppe, B. et al. Linking molecular deadwood-inhabiting fungal diversity and community dynamics to ecosystem functions and processes in Central European forests. Fung. Div. 77, 367–379 (2016).Article 

    Google Scholar 
    9.Purahong, W. et al. Determinants of deadwood-inhabiting fungal communities in temperate forests: Molecular evidence from a large scale deadwood decomposition experiment. Front. Microbiol. 9, Article 2120 (2018).10.Skelton, J. et al. Relationships among wood-boring beetles, fungi, and the decomposition of forest biomass. Mol. Ecol. 28, 4971–4986 (2019).CAS 
    PubMed 
    Article 

    Google Scholar 
    11.Toljander, Y. K., Lindahl, B. D., Holmer, L. & Hogberg, N. O. S. Environmental fluctuations facilitate species co-existence and increase decomposition in communities of wood decay fungi. Oecologia 148, 625–631 (2006).PubMed 
    Article 
    ADS 

    Google Scholar 
    12.Fukami, T. et al. Assembly history dictates ecosystem functioning: evidence from wood decomposer communities. Ecol. Lett. 13, 675–684 (2010).PubMed 
    Article 

    Google Scholar 
    13.Boddy, L. Fungal community ecology and wood decomposition process in angiosperms: From standing tree to complete decay of coarse woody debris. Ecol. Bull. 49, 43–56 (2001).
    Google Scholar 
    14.Boddy, L. & Heilmann-Clausen, J. Basidiomycete community development in temperate angiosperm wood. In Ecology of saprotrpophic basidiomycetes. (Eds. Boddy, L., Frankland, J.C., & van West, P.) 211–237 (Academic Press, 2008).15.Parfitt, D., Hunt, J., Dockrell, D., Rogers, H. J. & Boddy, L. Do all trees carry the seed of their own destruction? PCR reveals numerous wood decay fungi latently present in sapwood of a wide range of angiosperm trees. Fung. Ecol. 3, 338–346 (2010).Article 

    Google Scholar 
    16.Song, Z., Kennedy, P. G., Liew, F. J. & Schilling, J. S. Fungal endophytes as priority colonizers initiating wood decomposition. Func. Ecol. 31, 407–418 (2017).Article 

    Google Scholar 
    17.Cline, L. C., Schilling, J. S., Menke, J., Groenhof, E. & Kennedy, P. G. Ecological and functional effects of fungal endophytes on wood decomposition. Func. Ecol. 32, 181–191 (2018).Article 

    Google Scholar 
    18.Coates, D. & Rayner, A. D. M. Fungal population and community development in cut beech logs I. Establishment via the aerial cut surface. New Phytol. 101, 153–171 (1985).Article 

    Google Scholar 
    19.Fukasawa, Y., Osono, T. & Takeda, H. Beech log decomposition by wood-inhabiting fungi in a cool temperate forest floor: A quantitative analysis focused on the decay activity of a dominant basidiomycetes Omphalotus guepiniformis. Ecol. Res. 25, 959–966 (2010).Article 

    Google Scholar 
    20.Boddy, L. & Hiscox, J. Fungal ecology: principles and mechanisms of colonization and competition by saprotrophic fungi. Microbiol. Spec. 4, FUNK-0019-2016 (2016).
    Google Scholar 
    21.Rajala, T., Peltoniemi, M., Pennanen, T. & Makipaa, R. Fungal community dynamics in relation to substrate quality of decaying Norway spruce (Picea abies [L.] Karst.) logs in boreal forests. FEMS Microbiol. Ecol. 81, 494–505 (2012).CAS 
    PubMed 
    Article 

    Google Scholar 
    22.Rajala, T., Tuomivirta, T., Pennanen, T. & Mäkipää, R. Habitat models of wood-inhabiting fungi along a decay gradient of Norway spruce logs. Fung. Ecol. 18, 48–55 (2015).Article 

    Google Scholar 
    23.Rayner, A.D.M., & Boddy, L. Fungal decomposition of wood: Its biology and ecology. (Willey, 1988).24.Bunnell, F. L. & Houde, I. Down wood and biodiversity—Implications to forest practices. Environ. Rev. 18, 397–421 (2010).Article 

    Google Scholar 
    25.Wells, J. M. & Boddy, L. Interspecific carbon exchange and cost of interactions between basidiomycete mycelia in soil and wood. Func. Ecol. 16, 153–161 (2002).Article 

    Google Scholar 
    26.Hiscox, J. et al. Effects of pre-colonisation and temperature on interspecific fungal interactions in wood. Fung. Ecol. 21, 32–42 (2016).Article 

    Google Scholar 
    27.Fukasawa, Y., Osono, T. & Takeda, H. Wood decomposition abilities of diverse lignicolous fungi on nondecayed and decayed beech wood. Mycologia 103, 474–482 (2011).PubMed 
    Article 

    Google Scholar 
    28.Valentin, L. et al. Loss of diversity in wood-inhabiting fungal communities affects decomposition activity in Norway spruce wood. Front. Microbiol. 5, Article 230 (2014).29.Maynard, D., Crowther, T. W. & Bradford, M. A. Fungal interactions reduce carbon use efficiency. Ecol. Lett. 20, 1034–1042 (2017).PubMed 
    Article 

    Google Scholar 
    30.Woodward, S., & Boddy, L. Interactions between saprotrophic fungi. In Ecology of saprotrophic basidiomycetes (eds Boddy, L., Frankland, J.C., van West, P.) 125–141 (Academic Press, 2008).31.Gessner, M. O. et al. Diversity meets decomposition. Trends Ecol. Evol. 25, 372–380 (2010).PubMed 
    Article 
    PubMed Central 

    Google Scholar 
    32.Fukasawa, Y., Gilmartin, E. C., Savoury, M. & Boddy, L. Inoculum volume effects on competitive outcome and wood decay rate of brown- and white-rot basidiomycetes. Fung. Ecol. 45, 100938 (2020).Article 

    Google Scholar 
    33.O’Leary, J. et al. The whiff of decay: Linking volatile production and extracellular enzymes to outcomes of fungal interactions at different temperatures. Fung. Ecol. 39, 336–348 (2019).Article 

    Google Scholar 
    34.Boddy, L., Owens, E. M. & Chapela, I. H. Small scale variation in decay rate within logs one year after felling: effect of fungal community structure and moisture content. FEMS Microbiol. Ecol. 62, 173–184 (1989).Article 

    Google Scholar 
    35.Setälä, H. & McLean, M. A. Decomposition rate of organic substrates in relation to the species diversity of soil saprophytic fungi. Oecologia 139, 98–107 (2004).PubMed 
    Article 
    ADS 
    PubMed Central 

    Google Scholar 
    36.Yang, C. et al. Higher fungal diversity is correlated with lower CO2 emissions from dead wood in a natural forest. Sci. Rep. 6, 31066 (2016).CAS 
    PubMed 
    PubMed Central 
    Article 
    ADS 

    Google Scholar 
    37.Berg, B., & McClaugherty, C. Plant litter: Decomposition, humus formation, carbon sequestration (Springer, 2003).38.Fukasawa, Y., Takahashi, K., Arikawa, T., Hattori, T. & Maekawa, N. Fungal wood decomposer activities influence community structure of myxomycetes and bryophytes on coarse woody debris. Fung. Ecol. 14, 44–52 (2015).Article 

    Google Scholar 
    39.Fukasawa, Y., Hyodo, F. & Kawakami, S. Foraging association between myxomycetes and fungal communities on coarse woody debris. Soil Biol. Biochem. 121, 95–102 (2018).CAS 
    Article 

    Google Scholar 
    40.Fukasawa, Y. Fungal succession and decomposition of Pinus densiflora snags. Ecol. Res. 33, 435–444 (2018).Article 

    Google Scholar 
    41.Fukasawa, Y., Osono, T. & Takeda, H. Effects of attack of saprobic fungi on twig litter decomposition by endophytic fungi. Ecol. Res. 24, 1067–1073 (2009).Article 

    Google Scholar 
    42.Hiscox, J. & Boddy, L. Armed and dangerous—Chemical warfare in wood decay communities. Fung. Biol. Rev. 31, 169–184 (2017).Article 

    Google Scholar 
    43.Presley, G.N., Zhang, J., Purvine, S.O., & Schilling, J.S. Functional genomics, transcriptomics, and proteomics reveal distinct combat strategies between lineages of wood-degrading fungi with redundant wood decay mechanisms. Front. Microbiol. 11, article 1646 (2020).44.Hiscox, J., Savoury, M., Vaughan, I. P., Muller, C. T. & Boddy, L. Antagonistic fungal interactions influence carbon dioxide evolution from decomposing wood. Fung. Ecol. 14, 24–32 (2015).Article 

    Google Scholar 
    45.Zhang, X., Xu, C. & Wang, H. Pretreatment of bamboo residues with Coriolus versicolor for enzymatic hydrolysis. J. Biosci. Bioengineer. 104, 149–151 (2007).CAS 
    Article 

    Google Scholar 
    46.Horisawa, S., Inoue, A. & Yamanaka, Y. Direct ethanol production from lignocellulosic materials by mixed culture of wood rot fungi Schizophyllum commune, Bjerkandera adusta, and Fomitopsis palustris. Fermentation 5, 21 (2019).CAS 
    Article 

    Google Scholar 
    47.Schilling, J. S., Kaffenberger, J. T., Held, B. W., Ortiz, R. & Blanchette, R. A. Using wood rot phenotypes to illuminate the “Gray” among decomposer fungi. Front. Microbiol 11, 1288 (2020).PubMed 
    PubMed Central 
    Article 

    Google Scholar 
    48.Crawford, R. H., Carpenter, S. E. & Harmon, M. E. Communities of filamentous fungi and yeast in decomposing logs of Pseudotsuga menziesii. Mycologia 82, 759–765 (1990).Article 

    Google Scholar 
    49.Lumley, T. C., Gignac, L. D. & Currah, R. S. Microfungus communities of white spruce and trembling aspen logs and different stages of decay in disturbed and undisturbed sites in the boreal mixedwood region of Alberta. Can. J. Bot. 79, 76–92 (2001).
    Google Scholar 
    50.Fukasawa, Y., Osono, T. & Takeda, H. Microfungus communities of Japanese beech logs at different stages of decay in a cool temperate deciduous forest. Can. J. For. Res. 39, 1606–1614 (2009).CAS 
    Article 

    Google Scholar 
    51.Fukasawa, Y., Osono, T. & Takeda, H. Dynamics of physicochemical properties and occurrence of fungal fruit bodies during decomposition of coarse woody debris of Fagus crenata. J. For. Res. 14, 20–29 (2009).CAS 
    Article 

    Google Scholar 
    52.Maynard, D., Crowther, T. W. & Bradford, M. A. Competitive network determines the direction of the diversity-function relationship. Proc. Natl. Acad. Sci. USA 114, 11464–11469 (2017).CAS 
    PubMed 
    Article 

    Google Scholar 
    53.Kubart, A., Vasaitis, R., Stenlid, J. & Dahlberg, A. Fungal communities in Norway spruce stumps along a latitudinal gradient in Sweden. For. Ecol. Manag. 371, 50–58 (2016).Article 

    Google Scholar 
    54.MacArthur, R.H., & Wilson, E.O. The Theory of Island Biogeography. (Princeton University Press, 2001).55.Yachi, S. & Loreau, M. Biodiversity and ecosystem functioning productivity in a fluctuating environment: The insurance hypothesis. Proc. Natl. Acad. Sci. USA 96, 1463–1468 (1999).CAS 
    PubMed 
    Article 
    ADS 

    Google Scholar 
    56.Maynard, D. et al. Consistent trade-offs in fungal trait expression across broad spatial scales. Nat. Microbiol. 4, 846–853 (2019).CAS 
    PubMed 
    Article 

    Google Scholar 
    57.Talbot, J. M. et al. Endemism and functional convergence across the North American soil mycobiome. Proc. Natl. Acad. Sci. USA 111, 6341–6346 (2014).CAS 
    PubMed 
    Article 
    ADS 

    Google Scholar 
    58.Pyle, C. & Brown, M. M. Heterogeneity of wood decay classes within hardwood logs. For. Ecol. Manag. 114, 253–259 (1999).Article 

    Google Scholar 
    59.Carini, P. et al. Effects of spatial variability and relic DNA removal on the detection of temporal dynamics in soil microbial communities. mBio 11, e02776-19 (2020).60.Fukasawa, Y. & Matsuoka, S. Communities of wood-inhabiting fungi in dead pine logs along a geographical gradient in Japan. Fung. Ecol. 18, 75–82 (2015).Article 

    Google Scholar 
    61.Worrall, J. J., Anagnost, S. E. & Zabel, R. A. Comparison of wood decay among diverse lignicolous fungi. Mycologia 89, 199–219 (1997).Article 

    Google Scholar 
    62.Deacon, J. W. Decomposition of filter paper cellulose by thermophilic fungi acting singly, in combination, and in sequence. Tr. Br. Mycol. Soc. 85, 663–669 (1985).CAS 
    Article 

    Google Scholar 
    63.Fukasawa, Y. Effects of wood decomposer fungi on tree seedling establishment on coarse woody debris. For. Ecol. Manag. 266, 232–238 (2012).Article 

    Google Scholar 
    64.Toju, H., Tanabe, A. S., Yamamoto, S. & Sato, H. High-coverage ITS primers for the DNA-based identification of ascomycetes and basidiomycetes in environmental samples. PLoS ONE 7, e40863 (2012).CAS 
    PubMed 
    PubMed Central 
    Article 
    ADS 

    Google Scholar 
    65.Tanabe, A. S. & Toju, H. Two new computational methods for universal DNA barcoding: A benchmark using barcode sequences of bacteria, archaea, animals, fungi, and land plants. PLoS ONE 8, e76910 (2013).CAS 
    PubMed 
    PubMed Central 
    Article 
    ADS 

    Google Scholar 
    66.Osono, T. Metagenomic approach yields insights into fungal diversity and functioning. In Species diversity and community structure (eds Sota, T., Kagata, H., Ando, Y., Utsumi, S., & Osono, T.) 1–23 (Springer, 2014).67.Ohtsubo, Y., Ikeda-Ohtsubo, W., Nagata, Y. & Tsuda, M. GenomeMatcher: a graphical user interface for DNA sequence comparison. BMC Bioinform. 9, 376. https://doi.org/10.1186/1471-2105-9-376 (2008).CAS 
    Article 

    Google Scholar 
    68.Ovaskainen, O., & Abrego, N. Joint Species Distribution Modelling: With Application in R (Cambridge University Press, 2020).69.R Core Team. R: A language and environment for statistical computing. The R Foundation for Statistical Computing, Vienna, Austria. www.R-project.org (2019). More

  • in

    Competitive interactions as a mechanism for chemical diversity maintenance in Nodularia spumigena

    1.Stal, L. J. et al. BASIC: Baltic Sea cyanobacteria. An investigation of the structure and dynamics of water blooms of cyanobacteria in the Baltic Sea—Responses to a changing environment. Cont. Shelf Res. 23, 1695–1714 (2003).Article 
    ADS 

    Google Scholar 
    2.McGregor, G. B. et al. First report of a toxic Nodularia spumigena (nostocales/cyanobacteria) bloom in sub-tropical Australia. I. Phycological and public health investigations. Int. J. Env. Res. Public Health 9, 2396–2411 (2012).Article 

    Google Scholar 
    3.Popin, R. V. et al. Genomic and metabolomic analyses of natural products in Nodularia spumigena isolated from a shrimp culture pond. Toxins 12, 141 (2020).CAS 
    PubMed Central 
    Article 
    PubMed 

    Google Scholar 
    4.Seaman, M., Ashton, P. & Williams, W. Inland salt waters of southern Africa. Hydrobiologia 210, 75–91 (1991).CAS 
    Article 

    Google Scholar 
    5.Beutel, M. W., Horne, A. J., Roth, J. C. & Barratt, N. J. Saline Lakes 91–105 (Springer, 2001).Book 

    Google Scholar 
    6.Paerl, H. W. & Paul, V. J. Climate change: Links to global expansion of harmful cyanobacteria. Water Res. 46, 1349–1363 (2012).CAS 
    PubMed 
    Article 

    Google Scholar 
    7.Karjalainen, M. et al. Ecosystem consequences of cyanobacteria in the northern Baltic Sea. AMBIO J. Human Environ. 36, 195–202 (2007).CAS 
    Article 

    Google Scholar 
    8.Sotton, B., Domaizon, I., Anneville, O., Cattanéo, F. & Guillard, J. Nodularin and cylindrospermopsin: A review of their effects on fish. Rev. Fish Biol. Fish. 25, 1–19 (2015).Article 

    Google Scholar 
    9.Mazur-Marzec, H., Bertos-Fortis, M., Toruńska-Sitarz, A., Fidor, A. & Legrand, C. Chemical and genetic diversity of Nodularia spumigena from the Baltic Sea. Mar. Drugs 14, 209. https://doi.org/10.3390/md14110209 (2016).CAS 
    Article 
    PubMed Central 
    PubMed 

    Google Scholar 
    10.Voss, B. et al. Insights into the physiology and ecology of the brackish-water-adapted Cyanobacterium Nodularia spumigena CCY9414 based on a genome-transcriptome analysis. PLoS ONE 8, e60224–e60224. https://doi.org/10.1371/journal.pone.0060224 (2013).CAS 
    Article 
    PubMed 
    PubMed Central 
    ADS 

    Google Scholar 
    11.Le Manach, S. et al. Global metabolomic characterizations of Microcystis spp. highlights clonal diversity in natural bloom-forming populations and expands metabolite structural diversity. Front. Microbiol. https://doi.org/10.3389/fmicb.2019.00791 (2019).Article 
    PubMed 
    PubMed Central 

    Google Scholar 
    12.Welker, M. & von Döhren, H. Cyanobacterial peptides—Nature’s own combinatorial biosynthesis. FEMS Microbiol. Rev. 30, 530–563 (2006).CAS 
    PubMed 
    Article 

    Google Scholar 
    13.Kehr, J. C., Picchi, D. G. & Dittmann, E. Natural product biosyntheses in cyanobacteria: A treasure trove of unique enzymes. Beilstein J. Org. Chem. 7, 1622–1635. https://doi.org/10.3762/bjoc.7.191 (2011).CAS 
    Article 
    PubMed 
    PubMed Central 

    Google Scholar 
    14.Christiansen, G., Philmus, B., Hemscheidt, T. & Kurmayer, R. Genetic variation of adenylation domains of the anabaenopeptin synthesis operon and evolution of substrate promiscuity. J. Bacteriol. 193, 3822–3831 (2011).CAS 
    PubMed 
    PubMed Central 
    Article 

    Google Scholar 
    15.Ishida, K. et al. Biosynthesis and structure of aeruginoside 126A and 126B, cyanobacterial peptide glycosides bearing a 2-carboxy-6-hydroxyoctahydroindole moiety. Chem. Biol. 14, 565–576 (2007).CAS 
    PubMed 
    PubMed Central 
    Article 

    Google Scholar 
    16.Fewer, D.P. et al. The non-ribosomal assembly and frequent occurrence of the protease inhibitors spumigins in the bloom-forming cyanobacterium Nodularia spumigena. Mol. Microbiol. 73, 924–937. https://doi.org/10.1111/j.1365-2958.2009.06816.x (2009).CAS 
    Article 
    PubMed 

    Google Scholar 
    17.Portmann, C. et al. Isolation of aerucyclamides C and D and structure revision of microcyclamide 7806A: Heterocyclic ribosomal peptides from Microcystis aeruginosa PCC 7806 and their antiparasite evaluation. J. Nat. Prod. 71, 1891–1896 (2008).CAS 
    PubMed 
    Article 

    Google Scholar 
    18.Ersmark, K., Del Valle, J. R. & Hanessian, S. Chemistry and biology of the aeruginosin family of serine protease inhibitors. Angew. Chem. Int. Ed. 47, 1202–1223 (2008).CAS 
    Article 

    Google Scholar 
    19.Liu, L. et al. Pseudoaeruginosins, nonribosomal peptides in Nodularia spumigena. ACS Chem. Biol. 10, 725–733 (2015).CAS 
    PubMed 
    Article 

    Google Scholar 
    20.Itou, Y., Suzuki, S., Ishida, K. & Murakami, M. Anabaenopeptins G and H, potent carboxypeptidase A inhibitors from the cyanobacterium Oscillatoria agardhii (NIES-595). Bioorg. Med. Chem. Lett. 9, 1243–1246 (1999).CAS 
    PubMed 
    Article 

    Google Scholar 
    21.Bister, B. et al. Cyanopeptolin 963A, a chymotrypsin inhibitor of Microcystis PCC 7806. J. Nat. Prod. 67, 1755–1757 (2004).CAS 
    PubMed 
    Article 

    Google Scholar 
    22.Neilan, B. A., Pearson, L. A., Muenchhoff, J., Moffitt, M. C. & Dittmann, E. Environmental conditions that influence toxin biosynthesis in cyanobacteria. Environ. Microbiol. 15, 1239–1253. https://doi.org/10.1111/j.1462-2920.2012.02729.x (2013).CAS 
    Article 
    PubMed 

    Google Scholar 
    23.Halstvedt, C. B., Rohrlack, T., Ptacnik, R. & Edvardsen, B. On the effect of abiotic environmental factors on production of bioactive oligopeptides in field populations of Planktothrix spp. (Cyanobacteria). J. Plankton Res. 30, 607–617 (2008).CAS 
    Article 

    Google Scholar 
    24.Mazur-Marzec, H. et al. Diversity of peptides produced by Nodularia spumigena from various geographical regions. Mar. Drugs 11, 1–19. https://doi.org/10.3390/md11010001 (2012).CAS 
    Article 
    PubMed 
    PubMed Central 

    Google Scholar 
    25.Repka, S., Koivula, M., Harjunpa, V., Rouhiainen, L. & Sivonen, K. Effects of phosphate and light on growth of and bioactive peptide production by the Cyanobacterium anabaena strain 90 and its anabaenopeptilide mutant. Appl. Environ. Microbiol. 70, 4551–4560. https://doi.org/10.1128/aem.70.8.4551-4560.2004 (2004).CAS 
    Article 
    PubMed 
    PubMed Central 

    Google Scholar 
    26.Lehtimäki, J., Moisander, P., Sivonen, K. & Kononen, K. Growth, nitrogen fixation, and nodularin production by two Baltic Sea cyanobacteria. Appl. Environ. Microbiol. 63, 1647–1656 (1997).PubMed 
    PubMed Central 
    Article 

    Google Scholar 
    27.OECD. Test No. 201: Freshwater alga and cyanobacteria, growth inhibition test. OECD Guidelines for the Testing of Chemicals, Section 2. https://doi.org/10.1787/9789264069923-en (OECD
    Publishing, Paris, 2011).28.Vaas, L. A. I., Sikorski, J., Michael, V., Göker, M. & Klenk, H.-P. Visualization and curve-parameter estimation strategies for efficient exploration of phenotype microarray kinetics. PLoS ONE 7, e34846. https://doi.org/10.1371/journal.pone.0034846 (2012).CAS 
    Article 
    PubMed 
    PubMed Central 
    ADS 

    Google Scholar 
    29.Higo, S., Yamatogi, T., Ishida, N., Hirae, S. & Koike, K. Application of a pulse-amplitude-modulation (PAM) fluorometer reveals its usefulness and robustness in the prediction of Karenia mikimotoi blooms: A case study in Sasebo Bay, Nagasaki, Japan. Harmful Algae 61, 63–70 (2017).Article 

    Google Scholar 
    30.Qi, H., Wang, J. & Wang, Z. A comparative study of maximal quantum yield of photosystem II to determine nitrogen and phosphorus limitation on two marine algae. J. Sea Res. 80, 1–11 (2013).Article 
    ADS 

    Google Scholar 
    31.Briand, E., Bormans, M., Gugger, M., Dorrestein, P. C. & Gerwick, W. H. Changes in secondary metabolic profiles of Microcystis aeruginosa strains in response to intraspecific interactions. Environ. Microbiol. 18, 384–400. https://doi.org/10.1111/1462-2920.12904 (2016).CAS 
    Article 
    PubMed 

    Google Scholar 
    32.Koek, M. M., Muilwijk, B., van der Werf, M. J. & Hankemeier, T. Microbial metabolomics with gas chromatography/mass spectrometry. Anal. Chem. 78, 1272–1281 (2006).CAS 
    PubMed 
    Article 

    Google Scholar 
    33.R Development Core Team. R: A language and environment for statistical computing. (R Foundation for Statistical Computing, Vienna, Austria, 2020).34.Medlock, G. L. et al. Inferring metabolic mechanisms of interaction within a defined gut microbiota. Cell Syst. 7, 245-257.e247. https://doi.org/10.1016/j.cels.2018.08.003 (2018).CAS 
    Article 
    PubMed 
    PubMed Central 

    Google Scholar 
    35.Paul, C., Mausz, M. A. & Pohnert, G. A co-culturing/metabolomics approach to investigate chemically mediated interactions of planktonic organisms reveals influence of bacteria on diatom metabolism. Metabolomics 9, 349–359. https://doi.org/10.1007/s11306-012-0453-1 (2013).CAS 
    Article 

    Google Scholar 
    36.Schatz, D. et al. Ecological implications of the emergence of non-toxic subcultures from toxic Microcystis strains. Environ. Microbiol. 7, 798–805 (2005).CAS 
    PubMed 
    Article 

    Google Scholar 
    37.Jensen, A., Rystad, B. & Skoglund, L. The use of dialysis culture in phytoplankton studies. J. Exp. Mar. Biol. Ecol. 8, 241–248 (1972).Article 

    Google Scholar 
    38.Kobayashi, K., Takata, Y. & Kodama, M. Direct contact between Pseudo-nitzschiaámultiseries and bacteria is necessary for the diatom to produce a high level of domoic acid. Fish. Sci. 75, 771–776 (2009).CAS 
    Article 

    Google Scholar 
    39.McVeigh, I., & Brown, W. In vitro growth of chlamydomonas chlamydogama bold and haematococcus pluvialis flotow em. Wille in mixed cultures.
    Bulletin of the Torrey Botanical Club, 81(3), 218–233. https://doi.org/10.2307/2481813 (1954).CAS 
    Article 

    Google Scholar 
    40.Sieg, R. D., Poulson-Ellestad, K. L. & Kubanek, J. Chemical ecology of the marine plankton. Nat. Prod. Rep. 28, 388–399 (2011).CAS 
    PubMed 
    Article 

    Google Scholar 
    41.Yamasaki, A. An overview of CO2 mitigation options for global warming—Emphasizing CO2 sequestration options. J. Chem. Eng. Japan 36, 361–375 (2003).CAS 
    Article 

    Google Scholar 
    42.Hajdu, S., Hoglander, H. & Larsson, U. Phytoplankton vertical distributions and composition in Baltic Sea cyanobacterial blooms. Harmful Algae 6, 189–205 (2007).Article 

    Google Scholar 
    43.Berman-Frank, I. & Dubinsky, Z. Balanced growth in aquatic plants: Myth or reality? Phytoplankton use the imbalance between carbon assimilation and biomass production to their strategic advantage. Bioscience 49, 29–37 (1999).Article 

    Google Scholar 
    44.Kruskopf, M. & Flynn, K. J. Chlorophyll content and fluorescence responses cannot be used to gauge reliably phytoplankton biomass, nutrient status or growth rate. New Phytol. 169, 525–536. https://doi.org/10.1111/j.1469-8137.2005.01601.x (2006).CAS 
    Article 
    PubMed 

    Google Scholar 
    45.Raven, J. A. & Beardall, J. Chlorophyll fluorescence and ecophysiology: Seeing red?. New Phytol. 169, 449–451. https://doi.org/10.1111/j.1469-8137.2006.01637.x (2006).CAS 
    Article 
    PubMed 

    Google Scholar 
    46.Li, Q. et al. A large-scale comparative metagenomic study reveals the functional interactions in six bloom-forming microcystis-epibiont communities. Front. Microbiol. https://doi.org/10.3389/fmicb.2018.00746 (2018).Article 
    PubMed 
    PubMed Central 

    Google Scholar 
    47.Harke, M. J. et al. A review of the global ecology, genomics, and biogeography of the toxic cyanobacterium Microcystis spp. Harmful Algae 54, 4–20 (2016).PubMed 
    Article 

    Google Scholar 
    48.Caldwell, D. Associations between photosynthetic and heterotrophic prokaryotes in plankton. in Abstracts of the third International Symposium on Photosynthetic Prokaryotes (ed Nichols, J. M) (University of Liverpool, UK, 1979).49.Park, H. D. et al. Degradation of the cyanobacterial hepatotoxin microcystin by a new bacterium isolated from a hypertrophic lake. Environ. Toxicol. Int. J. 16, 337–343 (2001).CAS 
    Article 
    ADS 

    Google Scholar 
    50.Berg, C. et al. Dissection of microbial community functions during a cyanobacterial bloom in the Baltic Sea via metatranscriptomics. Front. Mar. Sci. 5, 55 (2018).Article 

    Google Scholar 
    51.Humbert, J.-F. et al. A tribute to disorder in the genome of the bloom-forming freshwater cyanobacterium Microcystis aeruginosa. PLoS ONE 8, e70747. https://doi.org/10.1371/journal.pone.0070747 (2013).CAS 
    Article 
    PubMed 
    PubMed Central 
    ADS 

    Google Scholar 
    52.Toporowska, M., Mazur-Marzec, H. & Pawlik-Skowrońska, B. The effects of cyanobacterial bloom extracts on the biomass, Chl-a, MC and other oligopeptides contents in a natural Planktothrix agardhii population. Int. J. Env. Res. Public Health 17, 2881 (2020).CAS 
    Article 

    Google Scholar 
    53.Grabowska, M., Kobos, J., Toruńska-Sitarz, A. & Mazur-Marzec, H. Non-ribosomal peptides produced by Planktothrix agardhii from Siemianówka Dam Reservoir SDR (northeast Poland). Arch. Microbiol. 196, 697–707 (2014).CAS 
    PubMed 
    PubMed Central 
    Article 

    Google Scholar 
    54.Penn, K., Wang, J., Fernando, S. C. & Thompson, J. R. Secondary metabolite gene expression and interplay of bacterial functions in a tropical freshwater cyanobacterial bloom. ISME J. 8, 1866–1878 (2014).CAS 
    PubMed 
    PubMed Central 
    Article 

    Google Scholar 
    55.Neilan, B. A. et al. Nonribosomal peptide synthesis and toxigenicity of cyanobacteria. J. Bacteriol. 181, 4089–4097 (1999).CAS 
    PubMed 
    PubMed Central 
    Article 

    Google Scholar 
    56.Long, B. M., Jones, G. J. & Orr, P. T. Cellular microcystin content in N-limited Microcystis aeruginosa can be predicted from growth rate. Appl. Environ. Microbiol. 67, 278–283 (2001).CAS 
    PubMed 
    PubMed Central 
    Article 

    Google Scholar 
    57.Qu, J. et al. Determination of the role of microcystis aeruginosa in toxin generation based on phosphoproteomic profiles. Toxins 10, 304 (2018).PubMed Central 
    Article 
    CAS 
    PubMed 

    Google Scholar 
    58.Raven, J. A. Cyanotoxins: A poison that frees phosphate. Curr. Biol. 20, R850–R852 (2010).CAS 
    PubMed 
    Article 

    Google Scholar 
    59.Utkilen, H. & Gjølme, N. Iron-stimulated toxin production in Microcystis aeruginosa. Appl. Environ. Microbiol. 61, 797–800 (1995).CAS 
    PubMed 
    PubMed Central 
    Article 

    Google Scholar 
    60.Gan, N. et al. The role of microcystins in maintaining colonies of bloom-forming Microcystis spp. Environ. Microbiol. 14, 730–742 (2012).CAS 
    PubMed 
    Article 

    Google Scholar 
    61.Pomati, F., Rossetti, C., Manarolla, G., Burns, B. P. & Neilan, B. A. Interactions between intracellular Na+ levels and saxitoxin production in Cylindrospermopsis raciborskii T3. Microbiology 150, 455–461 (2004).CAS 
    PubMed 
    Article 

    Google Scholar 
    62.Seigler, D. & Price, P. W. Secondary compounds in plants: Primary functions. Am. Nat. 110, 101–105 (1976).CAS 
    Article 

    Google Scholar 
    63.Zilliges, Y. et al. The cyanobacterial hepatotoxin microcystin binds to proteins and increases the fitness of Microcystis under oxidative stress conditions. PLoS ONE 6, e17615 (2011).CAS 
    PubMed 
    PubMed Central 
    Article 
    ADS 

    Google Scholar 
    64.Meissner, S., Fastner, J. & Dittmann, E. Microcystin production revisited: Conjugate formation makes a major contribution. Environ. Microbiol. 15, 1810–1820. https://doi.org/10.1111/1462-2920.12072 (2013).CAS 
    Article 
    PubMed 

    Google Scholar 
    65.Orr, P. T., Willis, A. & Burford, M. A. Application of first order rate kinetics to explain changes in bloom toxicity—The importance of understanding cell toxin quotas. J. Oceanol. Limnol. 36, 1063–1074. https://doi.org/10.1007/s00343-019-7188-z (2018).CAS 
    Article 
    ADS 

    Google Scholar 
    66.Rantala, A. et al. Phylogenetic evidence for the early evolution of microcystin synthesis. Proc. Natl. Acad. Sci. USA 101, 568–573 (2004).CAS 
    PubMed 
    Article 
    ADS 

    Google Scholar 
    67.Orr, P. T. & Jones, G. J. Relationship between microcystin production and cell division rates in nitrogen-limited Microcystis aeruginosa cultures. Limnol. Oceanogr. 43, 1604–1614 (1998).CAS 
    Article 
    ADS 

    Google Scholar 
    68.Burford, M. A. et al. Understanding the winning strategies used by the bloom-forming cyanobacterium Cylindrospermopsis raciborskii. Harmful Algae 54, 44–53 (2016).PubMed 
    Article 

    Google Scholar 
    69.Pierangelini, M. et al. Constitutive cylindrospermopsin pool size in Cylindrospermopsis raciborskii under different light and CO2 partial pressure conditions. Appl. Environ. Microbiol. 81, 3069–3076. https://doi.org/10.1128/aem.03556-14 (2015).CAS 
    Article 
    PubMed 
    PubMed Central 

    Google Scholar 
    70.Falkowski, P. G., Sukenik, A. & Herzig, R. Nitrogen limitation in Isochrysis galbana (Haptophyceae). II. Relative abundance of chloroplast proteins. J. Phycol. 25, 471–478 (1989).CAS 
    Article 

    Google Scholar 
    71.Turpin, D. H. Effects of inorganic N availability on algal photosynthesis and carbon metabolism. J. Phycol. 27, 14–20 (1991).CAS 
    Article 

    Google Scholar 
    72.Moffitt, M. C. & Neilan, B. A. Characterization of the nodularin synthetase gene cluster and proposed theory of the evolution of cyanobacterial hepatotoxins. Appl. Environ. Microbiol. 70, 6353–6362 (2004).CAS 
    PubMed 
    PubMed Central 
    Article 

    Google Scholar 
    73.Fewer, D. P. et al. New structural variants of aeruginosin produced by the toxic bloom forming cyanobacterium Nodularia spumigena. PLoS ONE 8, e73618 (2013).CAS 
    PubMed 
    PubMed Central 
    Article 
    ADS 

    Google Scholar 
    74.Fujii, K. et al. Comparative study of toxic and non-toxic cyanobacterial products: Novel peptides from toxic Nodularia spumigena AV1. Tetrahedron Lett. 38, 5525–5528 (1997).CAS 
    Article 

    Google Scholar 
    75.Ishida, K. et al. Plasticity and evolution of aeruginosin biosynthesis in cyanobacteria. Appl. Environ. Microbiol. 75, 2017–2026 (2009).CAS 
    PubMed 
    PubMed Central 
    Article 

    Google Scholar 
    76.Suikkanen, S., Fistarol, G. O. & Granéli, E. Allelopathic effects of the Baltic cyanobacteria Nodularia spumdigena, Aphanizomenon flosaquae and Anabaena lemmermannii on algal monocultures. J. Exp. Mar. Biol. Ecol. 308, 85–101 (2004).Article 

    Google Scholar 
    77.Suikkanen, S., Engström-Öst, J., Jokela, J., Sivonen, K. & Viitasalo, M. Allelopathy of Baltic Sea cyanobacteria: No evidence for the role of nodularin. J. Plankton Res. 28, 543–550. https://doi.org/10.1093/plankt/fbi139 (2006).CAS 
    Article 

    Google Scholar 
    78.Żak, A. & Kosakowska, A. The influence of extracellular compounds produced by selected Baltic cyanobacteria, diatoms and dinoflagellates on growth of green algae Chlorella vulgaris. Estuar. Coast. Shelf Sci. 167, 113–118 (2015).Article 
    ADS 

    Google Scholar 
    79.Śliwińska-Wilczewska, S., Felpeto, A. B., Możdżeń, K., Vasconcelos, V. & Latała, A. Physiological effects on coexisting microalgae of the allelochemicals produced by the bloom-forming cyanobacteria Synechococcus sp. and Nodularia spumigena. Toxins 11, 712 (2019).PubMed Central 
    Article 
    CAS 
    PubMed 

    Google Scholar 
    80.Gross, E. M. Allelopathy of aquatic autotrophs. Crit. Rev. Plant Sci. 22, 313–339 (2003).Article 

    Google Scholar 
    81.Legrand, C., Rengefors, K., Fistarol, G. O. & Graneli, E. Allelopathy in phytoplankton-biochemical, ecological and evolutionary aspects. Phycologia 42, 406–419 (2003).Article 

    Google Scholar 
    82.Leao, P. N., Vasconcelos, M. T. & Vasconcelos, V. M. Allelopathy in freshwater cyanobacteria. Crit. Rev. Microbiol. 35, 271–282. https://doi.org/10.3109/10408410902823705 (2009).CAS 
    Article 
    PubMed 

    Google Scholar 
    83.MacKintosh, C., Beattie, K. A., Klumpp, S., Cohen, P. & Codd, G. A. Cyanobacterial microcystin-LR is a potent and specific inhibitor of protein phosphatases 1 and 2A from both mammals and higher plants. FEBS Lett. 264, 187–192 (1990).CAS 
    PubMed 
    Article 

    Google Scholar 
    84.Pflugmacher, S. Possible allelopathic effects of cyanotoxins, with reference to microcystin-LR, in aquatic ecosystems. Environ. Toxicol. Int. J. 17, 407–413 (2002).CAS 
    Article 
    ADS 

    Google Scholar 
    85.Tilahun S. Exclusive partitioning of intra- and extra-cellular cyanotoxins: limitation of the conventional procedure. Environ. Sci. Pollut. Res. Int. 27(14), 17427–17428. https://doi.org/10.1007/s11356-020-08256-8 (2020).Article 
    PubMed 

    Google Scholar 
    86.Park, H. D. et al. Temporal variabilities of the concentrations of intra-and extracellular microcystin and toxic Microcystis species in a hypertrophic lake, Lake Suwa, Japan (1991–1994). Environ. Toxicol. Water Qual. Int. J. 13, 61–72 (1998).CAS 
    Article 
    ADS 

    Google Scholar 
    87.Tsuji, K. et al. Stability of microcystins from cyanobacteria: Effect of light on decomposition and isomerization. Environ. Sci. Technol. 28, 173–177 (1994).CAS 
    PubMed 
    Article 
    ADS 
    PubMed Central 

    Google Scholar 
    88.Schatz, D. et al. Towards clarification of the biological role of microcystins, a family of cyanobacterial toxins. Environ. Microbiol. 9, 965–970 (2007).CAS 
    PubMed 
    Article 
    PubMed Central 

    Google Scholar 
    89.Makower, A. K. et al. Transcriptomics-aided dissection of the intracellular and extracellular roles of microcystin in Microcystis aeruginosa PCC 7806. Appl. Environ. Microbiol. 81, 544–554 (2015).PubMed 
    PubMed Central 
    Article 
    CAS 

    Google Scholar 
    90.Kaplan, A. et al. The languages spoken in the water body (or the biological role of cyanobacterial toxins). Front. Microbiol. 3, 138 (2012).CAS 
    PubMed 
    PubMed Central 
    Article 

    Google Scholar 
    91.Svercel, M. Negative allelopathy among cyanobacteria. in Cyanobacteria: Ecology, Toxicology and Management. (ed Ferrao-Filho, A. S.) 27–46 (Nova Science Publishers, New York, NY, USA, 2013).
    Google Scholar 
    92.Wiegand, C. & Pflugmacher, S. Ecotoxicological effects of selected cyanobacterial secondary metabolites a short review. Toxicol. Appl. Pharmacol. 203, 201–218. https://doi.org/10.1016/j.taap.2004.11.002 (2005).CAS 
    Article 
    PubMed 

    Google Scholar 
    93.Agrawal, M. & Agrawal, M. K. Cyanobacteria–herbivore interaction in freshwater ecosystem. J. Microbiol. Biotechnol. Res. 1, 52–66 (2011).
    Google Scholar 
    94.Sadler, T. & von Elert, E. Dietary exposure of Daphnia to microcystins: No in vivo relevance of biotransformation. Aquat. Toxicol. 150, 73–82. https://doi.org/10.1016/j.aquatox.2014.02.017 (2014).CAS 
    Article 
    PubMed 

    Google Scholar 
    95.Rohrlack, T., Christiansen, G. & Kurmayer, R. Putative antiparasite defensive system involving ribosomal and nonribosomal oligopeptides in cyanobacteria of the genus Planktothrix. Appl. Environ. Microbiol. 79, 2642–2647 (2013).CAS 
    PubMed 
    PubMed Central 
    Article 

    Google Scholar 
    96.Sivonen, K. et al. Occurrence of the hepatotoxic cyanobacterium Nodularia spumigena in the Baltic Sea and structure of the toxin. Appl. Environ. Microbiol. 55, 1990–1995 (1989).CAS 
    PubMed 
    PubMed Central 
    Article 

    Google Scholar 
    97.Burbage, C. D. & Binder, B. J. Relationship between cell cycle and light-limited growth rate in oceanic Prochlorococcus (MIT9312) and Synechococcus (WH8103) (Cyanobacteria). J. Phycol. 43, 266–274. https://doi.org/10.1111/j.1529-8817.2007.00315.x (2007).Article 

    Google Scholar 
    98.Lei, L., Dai, J., Lin, Q., Peng, L. Competitive dominance of Microcystis aeruginosa against Raphidiopsis raciborskii is strain-and temperature dependent. Knowl. Manag. Aquat. Ecosyst. 421, 36. https://doi.org/10.1051/kmae/2020023 (2020).Article 

    Google Scholar  More

  • in

    Restoration and risk reduction of lead mining waste by phosphate-enriched biosolid amendments

    1.Schulthess, C. P. & Huang, C. P. Adsorption of heavy metals by silicon and aluminum oxide surfaces on clay minerals. Soil Sci. Soc. Am. J. 54, 679–688 (1990).ADS 
    Article 

    Google Scholar 
    2.City of Joplin Health Department. Report to Jasper County EPA Superfund citizen’s task force. City of Joplin Health Department, Joplin, MO (1995).3.Beyer, W. N., Pattee, O. H., Sileo, L., Hoffman, D. J. & Mulhern, B. M. Metal contamination in wildlife living near two zinc smelters. Environ. Pollut. Ser. A38, 63–86 (1985).Article 

    Google Scholar 
    4.Khan, D. H. & Frankland, B. Effects of cadmium and lead on radish plants with particular reference to movement of metals through soil profile and plant. Plant Soil 70, 335–345 (1983).CAS 
    Article 

    Google Scholar 
    5.Ruby, M. V., Davis, A., Kempton, J. H., Drexler, J. & Bergstrom, P. D. Lead bioavailability: Dissolution kinetics under simulated gastric conditions. Environ. Sci. Technol. 26, 1242–1248 (1992).ADS 
    CAS 
    Article 

    Google Scholar 
    6.Ruby, M. V., Davis, A. & Nicholson, A. In-situ formation of lead phosphates in soils as a method to immobilize lead. Environ. Sci. Tchnol. 28, 646–654 (1994).ADS 
    CAS 
    Article 

    Google Scholar 
    7.Nriagu, J. O. Lead orthophosphates-IV: Formation and stability in the environment. Geochim. Cosmochim. Acta 38, 887–898 (1974).ADS 
    CAS 
    Article 

    Google Scholar 
    8.Ma, Q. Y., Logan, T. J. & Traina, S. J. Lead immobilization from aqueous solutions and contaminated soils using phosphate rocks. Environ. Sci. Technol. 27, 1118–1126 (1995).ADS 
    Article 

    Google Scholar 
    9.Xu, Y. & Schwartz, F. W. Lead immobilization by hydroxyapatite in aqueous solutions. J. Contam. Hydrol. 15, 187–206 (1994).ADS 
    CAS 
    Article 

    Google Scholar 
    10.Zhang, P. C., Ryan, J. A. & Yang, J. In vitro soil Pb solubility in the presence of hydroxyapatite. Environ. Sci. Technol. 32, 2763–2768 (1998).ADS 
    CAS 
    Article 

    Google Scholar 
    11.Osborne, L. R., Baker, L. L. & Strawn, D. G. Lead immobilization and phosphorus availability in phosphate-amended, mine-contaminated soils. J. Environ. Qual. 44(1), 183–190 (2015).Article 

    Google Scholar 
    12.Yang, J. J., Mosby, D. E., Casteel, S. W. & Blanchar, R. W. Lead immobilization using phosphoric acid in smelter-contaminated urban soil. Environ. Sci. Technol. 35, 3553–3559 (2001).ADS 
    CAS 
    Article 

    Google Scholar 
    13.Tang, X., Yang, J., Goyne, K. W. & Deng, B. Long-term risk reduction of lead contaminated urban soil by phosphate treatment. Env. Eng. Sci. 26(12), 1747–1754 (2009).CAS 
    Article 

    Google Scholar 
    14.Tang, X. & Yang, J. Long-term stability of risk assessment of lead mill waste treated by soluble phosphate. Sci. Total Environ. 438, 299–303 (2012).ADS 
    CAS 
    Article 

    Google Scholar 
    15.Brown, S. L. & Chaney, R. L. A rapid in-vitro procedure to a mimicked in-situ remediation study of metal-contaminated soils characterize the effectiveness of a variety of in-situ lead remediation with emphasis on Cd and Pb. J. Environ. Qual. 23, 58–63 (1997).
    Google Scholar 
    16.Li, Y. M., Chaney, R. L., Siebielec, G. & Kerschner, B. Response of four turf grass cultivars to limestone and biosolids-compost amendment of a zinc and cadmium contaminated soil at Palmerton, Pennsylvania. J. Environ. Qual. 29, 1440–1447 (2000).CAS 
    Article 

    Google Scholar 
    17.Basta, N. T., Gradwhol, R., Snethen, K. L. & Schroder, J. L. Chemical immobilization of lead, zinc and cadmium in smelter-contaminated soils using biosolids and rock phosphate. J. Environ. Qual. 30, 1222–1230 (2001).CAS 
    Article 

    Google Scholar 
    18.Brown, S., Chaney, R. L., Hallfrisch, J. G. & Xue, Q. Effects of biosolids processing on lead bioavailability in an urban soil. J. Environ. Qual. 32, 100–108 (2003).CAS 
    Article 

    Google Scholar 
    19.Mosby, D.E., Miller, S., Bishop, C., Mehuys, J. Former and abandoned lead and zinc mines demonstration project. Final Report. Missouri Department of Nature Resources, Jefferson City, MO (2002).20.Singh, S. P., Ma, L. Q., Tack, F. G. & Verloo, M. G. Trace metal leachability of land-disposed dredged sediments. J. Environ. Qual. 29, 1124–1142 (2000).CAS 
    Article 

    Google Scholar 
    21.Yang, J., Tang, X. & Wang, Z. Y. Water quality and ecotoxicity as influenced by phosphate and biosolid treatments in lead-contaminated soil and mine waste. J. Environ. Monit. Rest. 3, 21–33 (2007).
    Google Scholar 
    22.Ma, L. Q. & Rao, G. N. Chemical fractionation of cadmium, copper, nickel, and zinc in contaminated soils. J. Environ. Qual. 26, 259–264 (1997).CAS 
    Article 

    Google Scholar 
    23.Bhattacharyya, P., Chakrabarti, K., Chakraborty, A., Tripathy, S. & Powell, M. A. Fractionation and bioavailability of Pb in municipal solid waste compost and Pb uptake by rice straw and grain under submerged condition in amended soil. Geosci. J. 12, 41–45 (2008).ADS 
    CAS 
    Article 

    Google Scholar 
    24.Brady, N. & Weil, R. The Nature and Property of Soils (Prentice Hall, 2002).
    Google Scholar 
    25.Fu, H. et al. Cadmium and lead speciation as affected by soil amendments in calcareous soil. Environ. Eng. Sci. https://doi.org/10.1089/ees.2017.0307 (2017).Article 

    Google Scholar 
    26.Xu, J. C., Huang, L. M., Chen, C., Wang, J. & Long, X. X. Effective lead immobilization by phosphate rock solubilization mediated by phosphate rock amendment and phosphate solubilizing bacteria. Chemosphere 237, 124540 (2019).ADS 
    CAS 
    Article 

    Google Scholar 
    27.Kungolos, A. et al. Toxic properties of metals and organotin compounds and their interactions on daphnia magna and vibrio fischeri. Water Ai, Soil Pollut. 4, 101–110 (2004).CAS 
    Article 

    Google Scholar 
    28.Eighmy, T. T. et al. Heavy metal stabilization in municipal solid waste combustion dry scrubber residue using soluble phosphate. Environ. Sci. Technol. 31, 3330–3338 (1997).ADS 
    CAS 
    Article 

    Google Scholar 
    29.Crannell, B. S. et al. Heavy metal stabilization in municipal solid waste combustion bottom ash using soluble phosphate. Waste Manag. 20, 135–148 (2000).CAS 
    Article 

    Google Scholar 
    30.Bubb, J. M. & Lester, J. N. Impact of heavy metals on low land rivers and implications for the man and the environment. Sci. Total Environ. 100, 207–258 (1991).ADS 
    CAS 
    Article 

    Google Scholar 
    31.Zhang, M. K. et al. Solubility of phosphorus and heavy metals in potting media amended with yard waste-biosolids compost. J. Environ. Qual. 33, 373–379 (2004).CAS 
    Article 

    Google Scholar 
    32.Xian, X. Effect of chemical forms of cadmium, zinc, and lead in polluted soils on their uptake by cabbage plants. Plant Soil 113, 257–264 (1989).CAS 
    Article 

    Google Scholar 
    33.Zhang, M. K. et al. Phosphorus and heavy metal attachment and release in sandy soil aggregate fractions. Soil Sci. Soc. Am. J. 67, 1158–1167 (2003).ADS 
    CAS 
    Article 

    Google Scholar 
    34.Pierzynski, G. M. & Schwab, A. P. Bioavailability of zinc, cadmium, and lead in a metal contaminated alluvial soil. J. Environ. Qual. 22, 247–254 (1993).CAS 
    Article 

    Google Scholar 
    35.Samaras, V., Tsadilas, C.D. Distribution and availability of six heavy metals in a soil treated with sewage sludge. In Proceedings of International Conference Biogeochemistry of Trace Elements, Berkeley, CA (1997).36.Scheckel, K. G. & Ryan, J. A. Spectroscopic speciation and quantification of lead in phosphate-amended soils. J. Environ. Qual. 33, 1288–1295 (2004).CAS 
    Article 

    Google Scholar 
    37.Lang, F. & Kaupenjohann, M. Effect of dissolved organic matter on the precipitation and mobility of the lead compound chloropyromorphite in solution. Eur. J. Soil Sci. 54, 139–147 (2003).CAS 
    Article 

    Google Scholar 
    38.Shi, Q. et al. Lead immobilization by phosphate in the presence of iron oxides: Adsorption versus precipitation. Water Res. 179, 115853 (2020).CAS 
    Article 

    Google Scholar 
    39.Andrunik, M., Wolowiec, M., Wojnarski, D., Zelek-Pogudz, S. & Bajda, T. Transformation of Pb, Cd, and Zn minerals using phosphates. Minerals. 10, 342 (2020).CAS 
    Article 

    Google Scholar 
    40.Guo, J. H. et al. Stablizing lead bullets in shooting range soil by phosphate-based surface coating. AIMS Environ Sci. 3(3), 474–487 (2016).CAS 
    Article 

    Google Scholar  More