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Alnus

Alnus is a genus of deciduous trees and shrubs known as alders, commonly found in temperate and subarctic regions of the Northern Hemisphere.
These plants are valued for their ability to fix nitrogen in the soil, making them useful in reforestation and land reclamation efforts.
Alders are also an important source of wood, charcoal, and traditional medicines.
Reserach into the biology, ecology, and potential applications of Alnus species can provide valuable insights for a range of disciplines, from forestry and agriculture to phrmaceutical development.

Most cited protocols related to «Alnus»

Moorjani et al. (2011) (link) first observed that pairwise LD measurements across a panel of SNPs can be combined to enable accurate inference of the age of admixture, n. The crux of their approach was to harness the fact that the ALD between two sites x and y scales as end multiplied by the product of allele frequency differences δ(x)δ(y) in the mixing populations. While the allele frequency differences δ(⋅) are usually not directly computable, they can often be approximated. Thus, Moorjani et al. (2011) (link) formulated a method, ROLLOFF, that dates admixture by fitting an exponential decay end to correlation coefficients between LD measurements and surrogates for δ(x)δ(y). Note that Moorjani et al. (2011) (link) define z(x, y) as a sample correlation coefficient, analogous to the classical LD measure r, as opposed to the sample covariance (Equation 1) we use here; we find the latter more mathematically convenient.
We build upon these previous results by deriving exact formulas for weighted sums of ALD under a variety of weighting schemes that serve as useful surrogates for δ(x)δ(y) in practice. These calculations will allow us to interpret the magnitude of weighted ALD to obtain additional information about admixture parameters. Additionally, the theoretical development will generally elucidate the behavior of weighted ALD and its applicability in various phylogenetic scenarios.
Following Moorjani et al. (2011) (link), we partition all pairs of SNPs (x, y) into bins of roughly constant genetic distance, where ε is a discretization parameter inducing a discretization on d. Given a choice of weights w(⋅), one per SNP, we define the weighted LD at distance d as
Assume first that our weights are the true allele frequency differences in the mixing populations, i.e., w(x) = δ(x) for all x. Applying Equation 3, where F2(A, B) is the expected squared allele frequency difference for a randomly drifting neutral allele, as defined in Reich et al. (2009) (link) and Patterson et al. (2012) (link). Thus, a(d) has the form of an exponential decay as a function of d, with time constant n giving the date of admixture.
In practice, we must compute an empirical estimator of a(d) from a finite number of sampled genotypes. Say we have a set of m diploid admixed samples from population C indexed by i = 1, …, m, and denote their genotypes at sites x and y by xi, yi ε {0, 1, 2}. Also assume we have some finite number of reference individuals from A and B with empirical mean allele frequencies p^A() and p^B() . Then our estimator is where cov(X,Y)^=1m1i=1m(xix)(yiy) is the usual unbiased sample covariance, so the expectation over the choice of samples satisfies E[a^(d)]=a(d) (assuming no background LD, so the ALD in population C is independent of the drift processes producing the weights).
The weighted sum is a natural quantity to use for detecting ALD decay and is common to our weighted LD statistic a^(d) and previous formulations of ROLLOFF. Indeed, for SNP pairs (x, y) at a fixed distance d, we can think of Equation 3 as providing a simple linear regression model between LD measurements z(x, y) and allele frequency divergence products δ(x)δ(y). In practice, the linear relation is made noisy by random sampling, as noted above, but the regression coefficient 2αβend can be inferred by combining measurements from many SNP pairs (x, y). In fact, the weighted sum in the numerator of Equation 5 is precisely the numerator of the least-squares estimator of the regression coefficient, which is the formulation of ROLLOFF given in Moorjani et al. (2012, Note S1). Note that measurements of z(x, y) cannot be combined directly without a weighting scheme, as the sign of the LD can be either positive or negative; additionally, the weights tend to preserve signal from ALD while depleting contributions from other forms of LD.
Up to scaling, our ALDER formulation is roughly equivalent to the regression coefficient formulation of ROLLOFF (Moorjani et al. 2012 , Note S1). In contrast, the original ROLLOFF statistic (Patterson et al. 2012 (link)) computed a correlation coefficient between z(x, y) and w(x)w(y) over . However, the normalization term in the denominator of the correlation coefficient can exhibit an unwanted d-dependence that biases the inferred admixture date if the admixed population has undergone a strong bottleneck (Moorjani et al. 2012 , Note S1) or in the case of recent admixture and large sample sizes. Beyond correcting the date bias, the a^(d) curve that ALDER computes has the advantage of a simple form for its amplitude in terms of meaningful quantities, providing us additional leverage on admixture parameters. Additionally, we will show that a^(d) can be computed efficiently via a new fast Fourier transform-based algorithm.
Publication 2013
Alleles Alnus Diet, Formula Diploidy Genotype Reproduction
As noted above, our ALDER formulation of weighted LD hones the original two-reference admixture dating technique of ROLLOFF (Moorjani et al. 2011 (link)), correcting a possible bias (Moorjani et al. 2012 , Note S1), and the one-reference technique (Pickrell et al. 2012 (link)), improving statistical power. Pickrell et al. (2012) (link) also observed that weighted LD can be used to estimate ancestral mixing fractions. We further develop this application now.
The main idea is to treat our expressions for the amplitude of the weighted LD curve as equations that can be solved for the ancestry fractions α and β = 1 − α. First consider two-reference weighted LD. Given samples from an admixed population C and reference populations A′ and B′, we compute the curve a^(d) and fit it as an exponential decay plus affine term: a^(d)M^end+K^ . Let a^0:=M^+K^/2 denote the amplitude of the curve. Then Equation 10 gives us a quadratic equation that we can solve to obtain an estimate α^ of the mixture fraction α, 2α^(1α^)F2(A,B)2=a^0, assuming we can estimate F2(A″, B″)2. Typically the branch-point populations A″ and B″ are unavailable, but their F2 distance can be computed by means of an admixture tree (Lipson et al. 2012 ; Patterson et al. 2012 (link); Pickrell and Pritchard 2012 (link)). A caveat of this approach is that α and 1 − α produce the same amplitude and cannot be distinguished by this method alone; additionally, the inversion problem is ill-conditioned near α = 0.5, where the derivative of the quadratic vanishes.
The situation is more complicated when using the admixed population as one reference. First, the amplitude relation from Equation 11 gives a quartic equation in α^ : 2α^(1α^)[α^F2(A,R)(1α^)F2(B,R)]2=a^0. Second, the F2 distances involved are in general not possible to calculate by solving allele frequency moment equations (Lipson et al. 2012 ; Patterson et al. 2012 (link)). In the special case that one of the true mixing populations is available as a reference, however—i.e., R′ = A—Pickrell et al. (2012) (link) demonstrated that mixture fractions can be estimated much more easily. From Equation 7, the expected amplitude of the curve is 2αβ3F2(A, B)2. On the other hand, assuming no drift in C since the admixture, allele frequencies in C are given by weighted averages of allele frequencies in A and B with weights α and β; thus, the squared allele frequency differences from A to B and C satisfy F2(A,C)=β2F2(A,B), and F2(A, C) is estimable directly from the sample data. Combining these relations, we can obtain our estimate α^ by solving the equation 2α^/(1α^)=a^0/F2(A,C)2. In practice, the true mixing population A is not available for sampling, but a closely related population A′ may be. In this case, the value of α^ given by Equation 12 with A′ in place of A is a lower bound on the true mixture fraction α (see Appendix A for theoretical development and Results for simulations exploring the tightness of the bound). This bounding technique is the most compelling of the above mixture fraction inference approaches, as prior methods cannot perform such inference with only one reference population. In contrast, when more references are available, moment-based admixture tree-fitting methods, for example, readily estimate mixture fractions (Lipson et al. 2012 ; Patterson et al. 2012 (link); Pickrell and Pritchard 2012 (link)). In such cases we believe that existing methods are more robust than LD-based inference, which suffers from the degeneracy of solutions noted above; however, the weighted LD approach can provide confirmation based on a different genetic mechanism.
Publication 2013
A.M.K Alnus Inversion, Chromosome Reproduction Trees
We fit discretized weighted LD curves a^(d) as M^end+K^ from Equation 9, using least-squares to find best-fit parameters. This procedure is similar to ROLLOFF, but ALDER makes two important technical advances that significantly improve the robustness of the fitting. First, ALDER directly estimates the affine term K that arises from the presence of subpopulations with differing ancestry percentages by using interchromosome SNP pairs that are effectively at infinite genetic distance (Appendix A). The algorithmic advances we implement in ALDER enable efficient computation of the average weighted LD over all pairs of SNPs on different chromosomes, giving K^ and, importantly, eliminating one parameter from the exponential fitting. In practice, we have observed that ROLLOFF fits are sometimes sensitive to the maximum inter-SNP distance d to which the weighted LD curve is computed and fit; ALDER eliminates this sensitivity.
Second, because background LD is present in real populations at short genetic distances and confounds the ALD signal (interfering with parameter estimates or producing spurious signal entirely), it is important to fit weighted LD curves starting only at a distance beyond which background LD is negligible. ROLLOFF used a fixed threshold of d > 0.5 cM, but some populations have longer-range background LD (e.g., from bottlenecks), and moreover, if a reference population is closely related to the test population, it can produce a spurious weighted LD signal due to recent shared demography. ALDER therefore estimates the extent to which the test population shares correlated LD with the reference(s) and fits only the weighted LD curve beyond this minimum distance as in our test for admixture (Appendix B).
We estimate standard errors on parameter estimates by performing a jackknife over the autosomes used in the analysis, leaving out each in turn. Note that the weighted LD measurements from individual pairs of SNPs that go into the computed curve a^(d) are not independent of each other; however, the contributions of different chromosomes can reasonably be assumed to be independent.
Publication 2013
A.M.K Alnus Chromosomes Hypersensitivity Reproduction Seizures Single Nucleotide Polymorphism
We performed PCA by computing components for present-day populations and then projecting ancient individuals using the “lsqproject” and “shrinkmode” options in smartpca (ref. 48 (link)). Admixture graphs and f-statistics were implemented through ADMIXTOOLS (ref. 49 (link)). To obtain calendar dates of admixture, we combine the ALDER results (in generations in the past) with the ages of the Neolithic individuals, assuming an average generation time of 28 years50 (link),51 . All analytical procedures are described in full detail in Supplementary Information sections 4–9.
Publication 2017
Alnus Population Group
In total, 322 individuals from 38 populations were genotyped on different Illumina SNP arrays (all targeting > 500,000 SNPs) according to manufacturers’ specifications. Our data was combined with published data from Li et al. [20 (link)], Rasmussen et al. [21 (link)], Behar et al. [22 (link)], Yunusbayev et al. [15 (link)], Metspalu et al. [29 (link)], Fedorova et al. [23 (link)], Raghavan et al. [41 (link)], Behar et al. [42 (link)], and covered all the Turkic-speaking populations (373 individuals from 22 samples) from key regions across Eurasia and their geographic neighbors (see details about sample source in S1 Table). Individuals with more than 1.5% missing genotypes were removed from the combined dataset. Only markers with a 97% genotyping rate and minor allele frequency (MAF) > 1% were retained. The absence of cryptic relatedness corresponding to first and second degree relatives in our dataset was confirmed using King [43 (link)]. The filtering steps resulted in a dataset of 1,444 individuals remaining for downstream analyses. It is important to note that in our dataset there are 312,524 SNPs that are common for Human1M-Duo and 650k, 610k, and 550k Illumina BeadChips. Different analyses have different requirements regarding marker density and we therefore prepared two datasets. For Admixture, three-population test, and ALDER analyses that require minimum background LD, LD pruning on the combined 1M-Duo and 650k, 610k, and 550k dataset was performed. The marker set was thinned by excluding SNPs in strong LD (pairwise genotypic correlation r2 > 0.4) in a window of 1,000 SNPs, sliding the window by 150 SNPs at a time. This resulted in a dataset of 174,187 SNPs. Another dataset with a dense marker set for IBD sharing and wavelet transform admixture dating analyses was prepared. For this, the 1M-Duo genotyped samples (S1 Table) were excluded to increase the SNP overlap among remaining samples up to 515,841 markers. Genetic distances between SNPs in centiMorgans were incorporated from the genetic map generated by the HapMap project [44 (link)].
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Publication 2015
Alnus CFC1 protein, human Chromosome Mapping Reproduction Single Nucleotide Polymorphism

Most recents protocols related to «Alnus»

We conducted our research at the RNUP in Toronto, Ontario, Canada (43.8188° N, 79.1728° W). The RNUP is the first urban national park in Canada and is part of a pilot project carried out by Parks Canada to conserve urban biodiversity, Indigenous cultural landscapes, and agricultural heritage of the area [27 ]. It is an ecologically protected zone established in 2015 under the Rouge National Urban Park Act [28 ] that encompasses 80 km2 of forests, meadows, rivers, wetlands, and fragments of rare habitats such as oak savannah and Carolinian woodlands [27 ]. Situated at the center of the Canada’s largest metropolitan area (Fig 1), the park is surrounded by major highways, freight and passenger railways, residential, commercial, and industrial developments, and agricultural lands [27 ].
Our study site is situated in the southern portion of the RNUP. In the early 1990s, the area was restored to a wetland complex of vernal pools, and more permanent ponds of various sizes with littoral vegetation including alders (Alnus spp.), cattails (Typha spp.), sedges (Carex spp.), and willows (Salix spp.) [21 ]. More recently, invasive species, such as European common reed (Phragmites australis), garlic mustard (Alliaria petiolate), purple loosestrife (Lythrum salicaria), and reed canary grass (Phalaris arundinacea) have become ubiquitous. Once restoration efforts were completed, the Toronto Zoo’s Adopt-A-Pond Wetland Conservation Program began wetland surveys to evaluate species occurrence in the area. The surveys found three at-risk turtle species: Painted Turtle (Chrysemys picta), Snapping Turtle (Chelydra serpentina), and the globally endangered [33 ] Blanding’s Turtle. In Canada, Painted and Snapping turtles are designated as ‘Special Concern’ by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC) [34 , 35 ], and Blanding’s Turtle is designated as ‘Endangered’ [36 ].
In 2005, the Blanding’s Turtle population within the park boundary was known to be comprised of three adult turtles (two males and one female) and a juvenile. Two additional adult turtles (one male and one female) were discovered in 2006 in an adjacent creek approximately 4 km from the RNUP (Toronto Zoo [Unpublished]). Given that the Blanding’s Turtle population in the RNUP was presumed functionally extinct, the Toronto Zoo initiated a headstarting program in 2012 to supplement the wild population [21 ]. A preliminary population viability analysis (PVA) showed that 40 headstarted turtles with 1:1.5 male:female sex ratio would need to be released each year for 20 years to reach a self-sustaining population of 150 adult Blanding’s Turtles (Toronto Zoo [Unpublished]). The first release occurred in 2014 with 10 juveniles, followed by 21 in 2015, 36 in 2016, 49 in 2017, 49 in 2018, 48 in 2019, 57 in 2020 for a total of 270 headstarted turtles released to date (Toronto Zoo [Unpublished]). An additional 184 hatchlings were released without headstarting because the number of eggs that hatched exceeded the capacity of the Toronto Zoo rearing facility.
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Publication 2023
Adult Alnus Carex Plant Dietary Supplements Eggs Europeans Extinction, Psychological Females Forests Garlic Invasive Species Lythrum salicaria Males Mustard Natural Springs Phalaris Rivers Turtle Typha Wetlands Willow
This study was carried out in north Portugal, within the county of Vila Real (Figure 1). The study area presents a Csb type of climate, i.e., a temperate climate with a dry or temperate summer [45 (link)]. The landscape is characterized by continuous and discontinuous urban areas intercalated with agricultural patches, forests, and semi-natural vegetation.
Blue spaces, mostly lotic environments, belong to the Corgo River Basin, a tributary on the right bank of the Douro River, which has the largest river catchment in the Iberian Peninsula. The riparian forests of blue spaces, associated with alder (Alnus glutinosa), ash (Fraxinus angustifolia), willow (Salix sp.), and thickets and nettle (Celtis australis), encompass several uncommon and confined plant species [46 (link)]. Additionally, these habitats are particularly biodiverse and important for the conservation of endangered endemic aquatic animals. Concerning green spaces, remnant oak forests (Quercus sp.) and heathlands (Erica sp. and Calluna sp.) are particularly relevant for their floristic biodiversity and the occurrence of species of conservation concern (e.g., Veronica micrantha). Anyhow, in the location of the study area, which is in the transition from the “Atlantic” to the “Mediterranean” biogeographic regions, even highly humanized areas such as planted forests, vineyards, pastures, cropland, and vegetable and public gardens contain a diversity of intermingled species and habitats [47 (link)].
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Publication 2023
Alnus Animals Ash Tree Calluna Celtis Climate Forests Quercus Rivers Urtica dioica Vegetables Veronica Willow
Monitoring activities were conducted during spring 2022 on five natural Alnus glutinosa stands located in the central part of Portugal, the districts of Aveiro and Guarda (Table 1). The altitude of survey sites ranged from 9 to 750 m. a.s.l.
At each site, mature alder trees were visually checked for the presence of typical Phytophthora disease symptoms, including wilting of foliage, shoot and twigs dieback, sudden death, bleeding cankers, and root and collar rot. In Sites 2 and 3, four linear transects of 50 m were randomly established to evaluate disease incidence and mortality rate, expressed as the number of symptomatic trees out of the total number of trees (DI = n/N × 100) and the number of dead trees out of the total number of trees (M = d/N × 100), respectively [19 ].
At each site, representative trees were randomly chosen for sampling (Table 1). Rhizosphere soil samples (about 1 L of soil and fine roots) were collected around the collar of 38 declining alder trees. Among these, eight trees were chosen for the collection of bark tissue samples, taking small fragments from the border of bleeding cankers on the stem. In Sites 2 and 3, the occurrence of Phytophthora species was also monitored in the water streams using nylon mesh bags containing 10 young cork oak (Quercus suber L.) leaves as bait [10 (link),20 ]. The nylon mesh bags were positioned near the root systems of the selected alder trees.
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Publication 2023
Alnus Nylons Phytophthora Plant Roots Quercus suber Rhizosphere Stem, Plant Sudden Death Trees
To confirm Koch’s postulates for new host–pathogen associations, the pathogenicity of five Phytophthora species was tested by inoculation on 1-year-old common alder seedlings grown in plastic pots (5 cm diameter, 0.5 L volume). Ten seedlings were inoculated with a representative isolate of each species, and ten were used as control. The seedlings were inoculated by wounding at the base of the stem using the protocol reported by Bregant et al. [10 (link)].
All inoculated seedlings were kept in controlled conditions at 21 °C and watered regularly for 30 days. At the end of the experimental period, seedlings were checked for the presence of internal (necrotic lesion) and external (wilting and exudates) disease symptoms. For each seedling, the outer bark was carefully removed with a scalpel, and the length of the necrotic lesion surrounding each inoculation point was measured.
The re-isolation of isolates was attempted by transferring 5 pieces of inner bark taken around the margin of the necrotic lesions onto PDA+. Growing colonies were subcultured onto CA and PDA, incubated in the dark at 20 °C and identified by morphological and molecular analyses.
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Publication 2023
Alnus Cortex, Cerebral Exudate isolation Marijuana Abuse Necrosis Pathogenicity Phytophthora Stem, Plant Vaccination
We divide plant taxa into two groups based on their temperature and precipitation preferences. We calculate the climatic niche centroids of plant taxa from the last 18,000 y (SI Appendix, Table S8). We then calculate the ratio of MAP to MAT for each plant taxon, where the temperature and precipitation are scaled separately to the range 0–1 (Fig. 2B, Inset). We divide plant taxa into two groups based on the precipitation/temperature ratios: Tsuga, Abies, Alnus, Picea, Betula, and Fagus compose a cold and wet taxa group for which the precipitation to temperature ratio is higher than 0.5. Fraxinus, Quercus, Pinus, Cupressaceae, Ulmus, Cyperaceae, Salix, Poaceae, Artemisia, and Amaranthaceae compose the warm and dry taxa group (Fig. 2A). We plot the niche overlap values for cold/wet and warm/dry plant taxa over time to evaluate whether one group showed consistently higher niche overlap than the other (Fig. 2B).
Publication 2023
Abies Alnus Amaranthaceae Artemisia Ash Tree Betula Climate Cold Temperature Cupressaceae Cyperaceae Fagus Picea Pinus Plants Poaceae Quercus Tsuga Ulmus Willow

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More about "Alnus"

Alnus, also known as alder, is a genus of deciduous trees and shrubs that are commonly found in temperate and subarctic regions of the Northern Hemisphere.
These plants are highly valued for their ability to fix nitrogen in the soil, making them invaluable in reforestation and land reclamation efforts.
Alders are an important source of wood, charcoal, and traditional medicines, and their potential applications have been the subject of extensive research.
Alnus species have been studied for their biology, ecology, and potential applications in a wide range of disciplines, from forestry and agriculture to pharmaceutical development.
Researchers have utilized various techniques and tools to investigate the properties and characteristics of these plants, including ImmunoCAP, Abbott Enzymatic Creatinine assay, Phadia 250, Orthophosphoric acid, Ethanol, Acetone, DNeasy Plant Mini Kit, Hydrochloric acid, Furfurylamine, and Architect ci8200.
These studies have provided valuable insights into the nitrogen-fixing capabilities of Alnus, its potential use in reforestation and land reclamation, and its role as a source of valuable resources such as wood, charcoal, and traditional medicines.
Additionally, the research has explored the potential pharmaceutical applications of Alnus, which could lead to the development of new and innovative products.
Alders are a fasinating and versatle genus of plants that have captivated the interest of researchers and practitioners across multiple fields.
By leveraging the latest technologies and techniques, researchers can continue to uncover the secrets of these remarkable trees and shrubs, and unlock their full potential for the benefit of society.