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70 results for “Miscanthus”
Calculation of parameter values based on observations for the herbaceous biomass plantation PFT representing Miscanthus in JSBACH3.2
<p>This dataset provides the calculation of parameter values and the observational data that was collected from literature used in these calculations for the re-implementation of a herbaceous biomass plantation (HBP) PFT representing Miscanthus in the dynamic global vegetation model (DGVM) JSBACH3.2 (Egerer et al. subm., Nützel et al. in prep.). The parameters included are the maximum rubisco capacity (Vmax) at 25°C, the PEPcase CO2 specificity (k) and specific leaf area (SLA). Some of the observed parameter values were already compiled in a dataset by Li et al. (2018). These observations were therefore re-used in this dataset (which is specified within the dataset sheets) and complemented with additional observed values from literature that has become available since then or was not included in the study by Li et al. (2018). A detailed methodology of the parameter calculations for JSBACH3.2 can be found on the first sheet of the dataset. </p>
Supplementary dataset to "Draft genome assembly of the biofuel grass crop Miscanthus sacchariflorus"
<p><em>Miscanthus sacchariflorus</em> (Maxim.) Hack. is a C4 perennial rhizomatous biofuel grass crop. <em>M. sacchariflorus</em> is among the most widely distributed species within the genus, particularly at cold northern latitudes, and one of the progenitor species of the main biomass commercial crop <em>M. × giganteus</em>. We generated a 2.54 Gbps whole-genome assembly of the diploid <em>M. sacchariflorus</em> “Robustus 297” genotype, which represented ~59% of the expected genome size. We later anchored this assembly in the chromosomal-scale <em>M. sinensis</em> genome to improve its contiguity. We annotated 86,767 and 69,049 protein-coding genes in the unanchored and anchored, respectively. We estimated our assemblies include ~85% of the <em>M. sacchariflorus</em> genes based on homology, core markers and RNA-seq alignments stats. Raw data and further metadata are available under Bioproject PRJNA435476.</p> <ul> <li>Msac_v2.fasta: Unanchored whole-genome assembly (WGA) of M. sacchariflorus in FASTA format.</li> <li>Msac_v3.fasta: The previous WGA re-scaffolded with the M. sinensis public reference.</li> <li>Msac_v3.agp: Chromosomal position in the M. sinensis reference of the previous scaffolds in Msac_v3.fasta</li> <li>Msac_v2.gff3: Gene annotation of the unanchored WGA in GFF3 format, which contains 86,767 coding genes</li> <li>Msac_v3.gff3: Gene annotation of the anchored WGA in GFF3 format, which contains 69,049 coding genes</li> <li>Msac_v2.func_annot.tsv: Text table containing the functional annotation of the 86,767 coding genes in Msac_v2.gff3</li> <li>Msac_v2.repeats_annotation.gff3: Repeats annotation (Repeatmasker) of the unanchored reference.</li> <li>Msac_v2.masked.fasta.gz: Repeats-masked version (Repeatmasker) of Msac_v2.fasta</li> <li>all.satsuma.blocks_Msac_v2-vs-Msin.gz: Every alignment from scaffolds in Msac_v3.fasta into M. sinensis reference</li> <li>Msac_v2.orthology_Msin.tsv: Ortologous between Msac_v2 and M. sinensis</li> <li>Msac_v3-vs-Msin.tsv: Ortologous between Msac_v3 and M. sinensis</li> </ul>
Technoeconomic analysis of the biobased terephthalic acid production using miscanthus as feedstock.
<p>This dataset contains information of the technoeconomic assessment for the biobased PTA production using Miscanthus as feedstock.</p>
Miscanthus sinensis Andersson (BR0000024505635)
Belgium Herbarium image of <a href="https://www.plantentuinmeise.be">Meise Botanic Garden</a>.
Miscanthus sinensis Andersson (BR0000012293414)
Belgium Herbarium image of <a href="https://www.plantentuinmeise.be">Meise Botanic Garden</a>.
Miscanthus sinensis Andersson (BR0000025021745)
Belgium Herbarium image of <a href="https://www.plantentuinmeise.be">Meise Botanic Garden</a>.
Miscanthus sinensis Andersson (BR0000005689309)
Belgium Herbarium image of <a href="https://www.plantentuinmeise.be">Meise Botanic Garden</a>.
Miscanthus sinensis Andersson (BR0000012550357)
Belgium Herbarium image of <a href="https://www.plantentuinmeise.be">Meise Botanic Garden</a>.
Miscanthus sinensis Andersson (BR0000025021752)
Belgium Herbarium image of <a href="https://www.plantentuinmeise.be">Meise Botanic Garden</a>.
Miscanthus sinensis Andersson (BR0000012553419)
Belgium Herbarium image of <a href="https://www.plantentuinmeise.be">Meise Botanic Garden</a>.
Miscanthus sinensis Andersson (BR0000014458712)
Belgium Herbarium image of <a href="https://www.plantentuinmeise.be">Meise Botanic Garden</a>.
Miscanthus sinensis Andersson (BR0000012552283)
Belgium Herbarium image of <a href="https://www.plantentuinmeise.be">Meise Botanic Garden</a>.
Miscanthus sinensis Andersson (BR0000012559695)
Belgium Herbarium image of <a href="https://www.plantentuinmeise.be">Meise Botanic Garden</a>.
Miscanthus sinensis Andersson (BR0000012417803)
Belgium Herbarium image of <a href="https://www.plantentuinmeise.be">Meise Botanic Garden</a>.
How much energy can giant reed and Miscanthus produce in marginal lands across Italy? A modelling solution under current and future scenarios
<p>This data were presented in the research paper “How much energy can giant reed and Miscanthus produce in marginal lands across Italy? A modelling solution under current and future scenarios”, currently accepted in the journal Global Change Biology Bioenergy (https://onlinelibrary.wiley.com/journal/17571707).<br>The study delivers a model-based evaluation of how much energy, in the form of biomethane and bioethanol, can be produced by giant reed and Miscanthus across Italy in 2000, 2055 and 2085. Marginal lands were defined as low profitable non-irrigated lands, without mechanization and/or nature conservation limitations. Our findings offer an estimation of achievable energy yields and related stability under current/future climate, identifying critical spots and opportunities at province and regional level across Italy.<br>This work was conducted by the Council for Agricultural Research and Economics and supported by the Italian Ministry of Agricultural, Food and Forestry Policies (MiPAAF) under i) the AGROENER project (D.D. n. 26329, April 1, 2016, http://agroener.crea.gov.it/) and ii) the AgriDigit-Agromodelli project (DM n. 36502 of 20/12/2018, https://www.progettoagridigit.it/il-progetto).</p> <p><br>The database used was split in two main datasets, one for the national case study and one for the provincial case study (Bologna province).<br>The national dataset consists of:<br>1) a gridded shape file (Marginal_Suitable_Areas_National.shp; 500 x 500 m resolution) including marginal lands suitable for Miscanthus and giant reed cultivation across Italy (code_nod field), together with related geographic coordinates;<br>2) a csv file (Results_National.csv) reporting the values of key output variables for each of the marginal lands considered. Output variables are:<br>a. USDA soil texture classification: 1= Loamy, 2=Sandy−loam, 3=Silty−loam, 4= Clay−loam, 5= Sandy−clay−loam, 6=Silty−clay−loam, 7=Loamy−sand, 8=Sandy−clay, 9=Silty−clay, 10=Silty, 11=Clay, 12=Heavy−clay, 13=Sandy.<br>b. soil organic carbon (SOC) classification: SOC≤1.5%=low, 1.5%<SOC≤3%,=medium, otherwise=high;<br>c. maximum soil depth (depth) classification: depth≤50 cm=shallow, otherwise=deep;<br>d. absolute values of aboveground biomass (AGB, Mg ha-1) and energy yields (Giga J ha-1) obtainable from bioethanol (ETA) and biomethane (MET) energy carriers simulated for giant reed (GR) and Miscanthus (MI) in the current scenario;<br>e. minimum (Mn) and maximum (Mx) AGB percentage (%) variations (compared to the baseline) estimated in 2055 (55) and 2085 (85) for RCP 4.5 (4.5) and RCP 8.5 (8.5) scenarios;<br>f. potentially assignable marginal lands to Miscanthus (2) and giant reed (1) crop species in Italy based on attainable energy yields under current (C_Base) and future (2085) time slices, considering the more pessimistic (C_8.5_85_MIN) and optimistic (C_4.5_85_MAX) AGB projection for both crops.</p> <p><br>The provincial dataset (case study in the Bologna province) consists of:<br>1) a gridded shape file (Marginal_Suitable_Areas_Provincial.shp, 500 x 500 m resolution) including marginal lands suitable for Miscanthus and giant reed cultivation across the Bologna province (code_nod field), together with related geographic coordinates;<br>2) a csv file (Results_Provincial.csv) reporting the values of key output variables for each of the marginal lands considered. Output variables are:<br>a. absolute values of simulated energy (EN, Giga J ha-1) from bioethanol (ETA) and biomethane (MET) for giant reed (GR) and Miscanthus (MI) in 1995,<br>b. energy percentage variations (compared to the baseline) estimated in 2085 for more optimistic (EN_Mx, i.e., RCP 4.5_max) and pessimistic (EN_Mn, i.e., RCP 8.5_min) projections for giant reed (GR) and Miscanthus (MI) and<br>c. coefficients of variations (CV, %) computed for the whole 30-year period centred on 1995 (B) and 2085 for RCP 4.5_max (CV_Mx) and RCP 8.5_min (CV_Mn) for giant reed (GR) and Miscanthus (MI) in the Bologna province.</p>
Figure 2 Stigmaeopsis sabelisi n in Description of two new species of Stigmaeopsis, Banks 1917 (Acari, Tetranychidae) inhabiting Miscanthus grasses (Poaceae)
Figure 2 Stigmaeopsis sabelisi n. sp.: A – Femur, genu, tibia and tarsus I of female; B – Femur, genu, tibia and tarsus II of female; C – Femur, genu, tibia and tarsus III of female; D – Femur, genu, tibia and tarsus IV of female.
Figure 6 A in Description of two new species of Stigmaeopsis, Banks 1917 (Acari, Tetranychidae) inhabiting Miscanthus grasses (Poaceae)
Figure 6 A – Stigmaeopsis longus (Saito), from Saito (1990) with some modification. Hysterosomal seta h3 was omitted; B – Stigmaeopsis nanjingensis (Ma et Yuan). New drawing by Y. Saito (specimen collected on June 20, 2014 in Fuzhou, China); C – Stigmaeopsis tenuinidus (Zhang et Zhang). New drawing by Y. Saito (specimen collected on May 20, 2015 in Fuzhou, China); D – Stigmaeopsis celarius Banks, from Saito et al. (2004) with some modification. Hysterosomal seta h3 was omitted.
Figure 8 A in Description of two new species of Stigmaeopsis, Banks 1917 (Acari, Tetranychidae) inhabiting Miscanthus grasses (Poaceae)
Figure 8 A – Conical spinneret of Stigmaeopsis continentalis Saito et Lin (dorsal view of this species appears in Figure 4A); B – Conical spinneret of Stigmaeopsis sabelisi Saito et Sato (Dorsal view of this species appears in Figure 1A); C – Stigmaeopsis miscanthi (Saito), from Saito (1990) with some modification. Hysterosomal seta h3 was omitted; D – Stigmaeopsis malkovskii (Wainstein), from Wainstein (1956) with modifications. Hysterosomal seta h3 was omitted; E – Stigmaeopsis meghalayensis (Gupta et Gupta), from Gupta and Gupta (1994) with modifications. Hysterosomal seta h3 was omitted.
Figure 7 A in Description of two new species of Stigmaeopsis, Banks 1917 (Acari, Tetranychidae) inhabiting Miscanthus grasses (Poaceae)
Figure 7 A – Stigmaeopsis takahashii Saito et Mori, from Saito et al. (2004) with some modification. Hysterosomal seta h3 was omitted; B – Stigmaeopsis saharai Saito et Mori, from Saito et al. (2004) with some modification. Hysterosomal seta h3 was omitted; C – Stigmaeopsis temporalis Saito et Ito, from Saito et al. (2016) with some modification. Hysterosomal seta h3 was omitted; D – Stigmaeopsis tegmentalis Saito et Lin, from Saito et al. (2016) with some modification. Hysterosomal seta h3 was omitted.
Figure 4 Stigmaeopsis continentalis n in Description of two new species of Stigmaeopsis, Banks 1917 (Acari, Tetranychidae) inhabiting Miscanthus grasses (Poaceae)
Figure 4 Stigmaeopsis continentalis n. sp.: A – Dorsum of female; B – Distal segment of palpus of female; C – Distal segment of palpus of male; D – Aedeagus.
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