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Typha

Typha is a genus of aquatic plants commonly known as cattails or bulrushes.
These plants are widely distributed across temperate and tropical regions, thriving in wetland environments such as marshes, swamps, and shallow ponds.
Typha plants are characterized by their distinctive cylindrical flowering spikes, which resemble brown sausages, as well as their long, linear leaves.
These hardy plants play a crucial role in aquatic ecosystems, providing food and habitat for a variety of wildlife.
Typha has also been used for centuries in traditional medicine and as a source of material for weaving and construction.
Researchers continue to explore the potential applications of Typha, including its use in wastewater treatment, biofuel production, and the development of novel biomaterials.
Wheter you're studying the ecology, physiology, or potential utilization of Typha, PubCompare.ai can help you discover the most accuarte and reproducible research protocols to optimize your studies.

Most cited protocols related to «Typha»

Annotation of the sequenced genomes was performed using DOGMA [55] (link), coupled with manual selections for start and stop codons and for intron/exon boundaries. We calculated the average cp genome size of subfamilies in Poaceae on the basis of the species listed in Table 3. We estimated the monocot mean cp genome size based on Acorus calamus (AJ879453) [56] (link), Dioscorea elephantipes (EF380353) [57] (link), Lemna minor (DQ400350) [58] (link), Oncidium Gower Ramsey (GQ324949) [59] (link), Phalaenopsis aphrodite (AY916449) [60] (link), Phoenix dactylifera (GU811709), and Typha latifolia (GU195652) [61] (link). The rpoC2 sequences from the grass family were aligned to the rpoC2 sequences of tobacco by MEGA 4.0 to determine the insertion size in the gene. We downloaded B. oldhamii and D. latiflorus cp genomes sequences from GenBank, and multiple alignments of eight bamboos cp genomes were made using MAFFT version 5 [62] (link). Full alignments with annotations were visualized using the VISTA viewer. The genetic divergence represented by p-distance was calculated by MEGA 4.0 with species of Arundinarieae as one group and those of Bambuseae as another.
We determined the three types of repeats, dispersed, tandem and palindromic, by first applying the program REPuter and then manually filtering the redundant output of REPuter. Gap size between palindromic repeats was restricted to a maximal length of 3 kb. Overlapping repeats were merged into one repeat motif whenever possible. A given region in the genome was designated as only one repeat type, and tandem repeat was prior to dispersed repeat if one repeat motif could be identified as both tandem and dispersed repeats. For coding, each repeat present in a given genome was ‘1’ and those absent were labeled as ‘0’. We performed MP analyses of this matrix using PAUP*4.0b10 [63] to implement exhaustive tree searches. Non-parametric bootstrap analysis was conducted under 1,000 replicates with TBR branch swapping.
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Publication 2011
Acorus calamus Codon, Terminator Dioscorea Exons Gene Insertion Genetic Drift Genome Introns Nicotiana Oncidium Phalaenopsis Phoenix dactylifera Poaceae Tandem Repeat Sequences Trees Typha
To demonstrate the use of the ARBIMON-acoustic application we created species-specific models for amphibians, birds, mammals, and insects based on recordings from a site in Puerto Rico and a site in Costa Rica. The species were selected to cover a range of taxa with different types of vocalizations. Vocalizations of frogs and birds were confidently identified based on our experience and comparisons with different sources of animal calls. Unfortunately, the two insect species, most likely cicadas, could not be captured and identified, but we carefully documented the call characteristics to assure that we modeled a specific species in each site.
The site in Puerto Rico, Sabana Seca (SS), is a small (180 ha) wetland near the Caribbean Primate Research Center (CPRC) in Toa Baja, Puerto Rico (18°25′56.01″ N and 66°11′45.62″ W). Typha dominguensis (cattail) is the dominant species in the wetland. This site is the only known locality of Eleutherodactylus juanariveroi (coqui llanero), an endangered frog species that was recently discovered (Rios-Lopez & Thomas, 2007 ). The major motivation for establishing a permanent recording station in Sabana Seca was to improve the information on the calling activity and population dynamics of E. juanariveroi. The station was established in March 2008, and for this study we present the results of species-specific identification models of the endemic frog species, E. juanariveroi, an exotic frog species Rana gryllo (pig frog), and an unidentified insect (insect #1).
The other study site was La Selva Biological Station (LSBS) in Costa Rica (10°25′ N, 84°01′ W). This reserve encompasses approximately 1,510 ha of which 64% is primary tropical forest, and contains a high diversity of flora and fauna (Clark & Gentry, 1991 ). The objective of this project was to conduct broad acoustic monitoring within mature forest for all species that contribute to the acoustic community. For this site, we created species-specific identification models for six species: Tinamus major (great tinamou), Ramphastos swainsonii (chestnut-mandibled toucan), Oophaga pumilio (strawberry poison-dart frog), Diasporus diastema (tink frog), Alouatta palliata (mantled howler monkey), and an unidentified insect (insect #2).
In addition to the recordings from the two permanent stations described in this manuscript, other recordings have been added to the ARBIMON database from other permanent stations in Puerto Rico, Hawaii, and Arizona, and from portable recording systems in Puerto Rico, Costa Rica, Argentina, and Brazil. As of May 7, 2013, the system has >1.3 million 1-min recordings, which can be freely accessed through the project web page (arbimon.net).
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Publication 2013
Acoustics Alouatta palliata Amphibians Animals Anura Aves Biopharmaceuticals Caribbean People Cicada Endangered Species Forests Insecta Mammals Motivation Poisons Primates Rana Strawberries Typha Wetlands
We were interested in assessing the relationship between the presence of schistosome-competent snails and infection burden in nearby humans. Both B. globosus and B. truncatus were of interest as intermediate hosts of S. hematobium (55 (link), 56 (link)), causative agent of human urogenital schistosomiasis (SI Appendix, Text S3). Patchiness in snail distributions could arise from snails’ strong association with ephemeral environmental features like vegetation (SI Appendix, Text S3). Because we wanted to quantify snails as accurately as possible, we made independent measures of their density in open-water/mud-bottom habitat, nonemergent vegetation (e.g., Ceratophyllum spp., Ludwigia spp., and Potamogeton spp.), and emergent vegetation (e.g., Typha spp., Phragmites spp.) within each site.
We adopted an area-specific technique for snail surveys, which allowed us to explore the spatial and temporal scale of heterogeneity in snail density (details in SI Appendix, Text S3). To randomly select snail-sampling locations within each of the sites, we used Google Earth to delineate a boundary around each site (Fig. 1D). Fifteen random points were stratified across the 3 microhabitat types (emergent vegetation, nonemergent vegetation, and open water/mud bottom) in proportion to the area of those microhabitats within the boundary of the site. We exhaustively sampled each quadrat (76.2-cm length × 48.26-cm width × 48.26-cm height; area, 0.3677 m2), placed all snails found into labeled vials, and returned them to the laboratory, where they were counted, identified to species, measured (shell height to the nearest 0.01 mm), and screened for parasite infection by shedding and dissection. All trematode infections of fork-tailed cercariae (57 (link)) were placed individually on WhatmanFTA cards (GE Healthcare Life Sciences) for molecular identification (58 (link)) and sequenced, and only snails infected with S. hematobium or S. hematobium–bovis hybrids were considered to be infected (since these are the only species occurring in B. truncatus/globosus that are capable of infecting humans; refs. 59 (link) and 60 (link)). Cercariae on FTA cards and snail tissue vouchers were accessioned into the Schistosomiasis Collection at the Natural History Museum (SCAN) (61 (link)). Schistosome-competent snails can be sensitive to water conditions, so at each site, we also measured water flow rate, water temperature, salinity, turbidity, pH, and nitrate, nitrite, and phosphate (SI Appendix, Text S3).
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Publication 2019
Cercaria Dissection Genetic Heterogeneity Helix (Snails) Homo sapiens Hybrids Infection Ludwigia Nitrates Nitrites Parasitic Diseases Phosphates Potamogeton Radionuclide Imaging Salinity Schistosoma Schistosomiasis Snails Tissues Trematode Infections Typha Urinary Schistosomiasis
We measured habitat where we found gartersnakes through tracking and visual observations. Fourth-order habitat measurements included vegetative, environmental, and hydrologic characteristics (Table 1) recorded at each snake point, in a 1-m-diameter plot, and along four 2.5-m transects sensu [10 ,39 ,55 ,56 ] (Fig 2). At each snake point, we measured aspect and slope, water depth, distance to water, and canopy cover (>1m in height). Within a 1-m-diameter plot centered on the snake point, we recorded number of plant stems (≥1 cm diameter) rooted in the plot and percentages of ground cover type, submerged vegetation, and surface shade. In plots, we also recorded percentage of low-height cover (≤1 m), which included vegetation (living or dead), woody debris, deep loose litter, or human-made structures that a snake could use for potential cover. We defined ground cover as anything a snake could be on top of when aboveground (Fig 3). We used ocular estimates of cover classes [57 ] in the following percentages: 0, <1, 1–5, 5–25, 25–50, 50–75, 75–95, >95. On four intersecting 2.5-m transects, we quantified vegetation type (grass, forb, cattail, sedge/rush, shrub, tree, or none) at every 0.5m mark. We measured habitat only at unique snake locations, which excluded points <3 m from a previous location for that snake (to avoid overlap in measurements) that had been measured in <4 weeks [10 ,55 ].
To compare used and available habitat, we quantified fourth-order habitat variables at snake points and paired random points [10 ,58 ]. This matched-pairs design is more robust than unmatched studies for assessing habitat selection because each random location represents a true absence [59 –61 (link)]. This technique also controls for variation in environmental conditions and enables more accurate modeling of habitat selection by ensuring that each random location is available to that individual at that time [62 ,63 ]. We randomized the distance (between 5 and 155 m) and bearing of the paired point from each snake point using a random number generator. If a random point occurred on private land or in an area not accessible to snakes, a new location was determined.
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Publication 2018
Eye Homo sapiens Poaceae Snakes Stem, Plant Trees Typha
The four Amblyseius swirskii lines used in the experiments derived from two origins, each reared in two different ways. Two lines were founded with specimens from a commercially mass-reared population obtained from Koppert B.V. (The Netherlands) while the other two lines were founded with free-living specimens collected on citrus trees in Israel. No specific permission was required to collect the mites on the citrus trees because those trees were located on public grounds and A. swirskii is not an endangered or protected species. In the laboratory, all four lines were reared on separate artificial arenas for about 11 months (~30 generations) before conducting the experiments. One line of each population origin was reared with cattail pollen Typha angustifolia (Nutrimite; Biobest, Belgium), and the other line with two-spotted spider mites, Tetranychus urticae (Tetranychidae). Each rearing arena consisted of an acrylic plate (200 x 200 mm) placed on top of a water-saturated foam cube in a plastic box half-filled with tap water. Wet tissue paper was wrapped around the edges to establish a border between the acrylic plate and the surrounding water, and to prevent the predatory mites from escaping. Additionally, cotton wool fibres under coverslips served as shelters and oviposition sites for the predatory mites. Pollen was dusted onto arenas twice per week. Tetranychus urticae was reared on whole common bean plants Phaseolus vulgaris grown at room temperature 23 ± 2°C and 16:8 h L:D photoperiod. The spider mites were brushed from infested leaves onto glass plates, using a mite brushing machine (BioQuip®, USA), and then from glass plates onto the rearing arenas. Depending on the population origin (KO for Koppert; IL for Israel) and rearing food (PO for pollen; SM for spider mites), the henceforth-used acronyms of the four lines are KO-PO, KO-SM, IL-PO and IL-SM.
Prey used in the experiments were Western flower thrips Frankliniella occidentalis (Thripidae) and two-spotted spider mites T. urticae. Frankliniella occidentalis was reared on detached primary leaves of common bean P. vulgaris placed upside down on a 1% agar solution in a closed petri dish (140 mm Ø, 20 mm height). The lid of the petri dish had a hole (10 mm Ø) covered with gauze for ventilation. Only first instar larvae were used as prey in the experiments. To obtain first instar larvae, adult thrips females were randomly taken from the stock population, reared on whole green beans inside glass jars, and placed on detached bean leaves inside petri dishes for oviposition. After 24 h, the females were removed and after another ~70 to 80 h the first instar larvae hatched [40 (link)].
Predator rearing arenas, thrips rearing units and experimental cages were kept in climate chambers at 25±1°C, 65±5% relative humidity and 16:8 h L:D photoperiod.
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Publication 2016
Agar Citrus Climate Females Food Humidity Hyperostosis, Diffuse Idiopathic Skeletal Larva Mites Oviposition Phaseolus vulgaris Pollen Tetranychidae Thysanoptera Tissues Trees Typha Woman

Most recents protocols related to «Typha»

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
The PPR (41.7° to 54.7°N latitude, 92.5° to 114.5°W longitude) covers ~820,000 km2 of the Great Plains in the United States and Canada and is home to millions of depressional wetlands (16 ). These depressions were formed during the Wisconsin glaciation, approximately 12,000 years ago (17 ). The underlying glacial till has low permeability, allowing depressions to fill and hold water and to ultimately develop into palustrine and lacustrine ecosystems made up of wetlands, ponds, and shallow lakes. We collectively refer to these depressional waterbodies as “wetlands” because the majority of them are less than 1 ha (0.01 km2) in size, less than 1 m deep, and seasonally (nonpermanent) ponded, meeting the definition of a wetland (sensu the Cowardin classification system) (61 ). In the PPR, larger wetlands often are shallow (<2 m) and have similar biogeochemical processes as smaller wetlands (62 ). Wetlands contain methanogenic microbial communities that are adapted to anoxic saturated soils, where they decompose organic material and produce CH4 (9 (link)). PPR wetlands range from fresh to hypersaline (up to three times more saline than the ocean) (17 ). This salinity is attributable to groundwater transport of dissolved sulfate through the ion-rich glacial till. PPR wetlands with higher sulfate concentrations have suppressed CH4 emissions (23 ), albeit high dissolved organic carbon concentrations in some PPR wetlands can support CH4 production in the presence of sulfate (24 (link)). Larger wetlands in topographically lower landscape positions tend to accumulate groundwater-derived solutes, while smaller, shallower wetlands are filled with rainwater and snowmelt (45 ). Vegetation characteristics of PPR wetlands are influenced by water depth and chemistry, typically with concentric zones with open water with submerged aquatic vegetation toward their centers and marshes and meadows with floating and emergent macrophytes such as Typha toward their edges (37 , 44 ).
The climate of the PPR is continental with a north to south temperature gradient ranging from ~2° to 8°C mean annual temperature and a northwest to southeast precipitation gradient ranging from ~400 to 900 mm year−1 (63 , 64 (link)). The PPR is centered on the confluence of tropical Pacific Ocean (El Niño–Southern Oscillation), eastern Pacific Ocean (Pacific Decadal Oscillation), and North Atlantic (Atlantic Multidecadal Oscillation) oscillations (65 ). Synergistic effects from synchronization of these oscillations lead to decadal periods of drought and deluge that influence groundwater levels. Wetland surface water is also extremely sensitive to variability in seasonal and annual precipitation (66 ). Thus, the size and hydroperiod of PPR wetlands are the result of complex interactions between long-term climate and short-term weather. An extreme multiyear drought from 1988 to 1992 led to the drying of many wetlands, with 1991 having the lowest wetland extent (45 ). Following the extreme drought, much of the PPR experienced a shift to a wetter climate. Annual precipitation in 2011 was one of the highest on record, and 2011 had some of the highest numbers of wetlands with ponded water (45 ). Therefore, we use 1991 and 2011 as extreme dry and wet years, respectively, in our modeling.
The PPR is intensively used for agricultural crop and biofuels production, which has led to extensive wetland drainage and upland conversion from prairie grassland to cropland (16 ). Drainage reduces CH4 emissions and soil organic carbon stocks but increases CO2 and nitrous oxide (N2O) emissions (22 (link), 67 ). Upland conversion from grassland to cropland can affect CH4 emissions indirectly through increased nutrient loading, resulting in increased CH4 emissions (38 (link)). However, wetlands nested in croplands are also subject to tillage and aeration of soils, thereby lowering CH4 emissions (22 (link)). Wetland drainage often results in consolidation of water from multiple smaller wetlands into one larger wetland. These larger wetlands are deeper with fewer fluctuations in water levels, as well as greater coverage of invasive emergent hybrid cattail, all of which favors CH4 production and emissions (37 ). Consolidation of wetlands also targets the smallest wetlands changing the distribution of wetland size classes, albeit the vast majority of wetlands are still <1 ha.
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Publication 2023
Agricultural Crops Anoxia Biofuels Carbon Climate Dissolved Organic Carbon Drainage Droughts Ecosystem El Nino-Southern Oscillation Hybrids Marshes Methanobacteria Microbial Community Nutrients palustrine Permeability Saline Solution Salinity Sulfates, Inorganic Typha Wetlands
LLNWP (123°41′~123°48′ E, 42°15′~42°18′ N) is an urban wetland park that is located in the south of Northeast China, close to Shenyang City. This is a location that is well-known in China for its old industrial base, located at the junction of the Liao River, Fan River, and Chai River. The study area was 776.74 hm2 (Figure 2). The climate is a temperate continental monsoon climate, with an average annual temperature of 6.3 °C, average annual precipitation of 700 mm, an annual sunshine duration of 2801 h, and a frost-free period of 127–165 days. The wetland is located on the alluvial plain of the Liao River and the first terrace of the Chai River, with flat terrain and an altitude of 50.5 m~61.8 m. The topography is composed of alluvial plains–floodplains–flat depressions in the low terraces, and the soil consists of meadow soil and paddy soil. Water resources are abundant, and most groundwater levels are between 1.0 m and 3.0 m. LLNWP is mainly comprised of natural wetlands combined with the restoration and reconstruction of artificial wetlands. The northeast and southern areas mainly consist of artificial wetlands, and the remaining areas are comprised of natural wetlands. The natural wetland types are mainly freshwater river wetlands and swamps, and the artificial wetlands are mainly paddy fields and reservoir ponds. The water flow is mainly horizontal, but there will be some vertical water flow changes due to miniature terrain drops. LLNWP has a total of 9.1 million aquatic plants of 26 species, including reeds, cattails, and water onions. The main vegetation in the natural wetland is reeds, lotus, wild rice stems, etc. In the northeast artificial wetland, the main vegetation types are reeds and rice; the southern right side mainly includes landscape plants, including calamus, cattails, etc., and the southern left side is dominated by rice plants. As the main function of the artificial wetland is to restore the original degraded natural wetland, LLNWP contains less porous materials of three main types: limestone, zeolite and crushed stone. This area possesses crucial value in providing animal and plant habitats and breeding grounds, maintaining species diversity, and ensuring urban ecological security.
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Publication 2023
Animals Calamus Calculi Climate Limestone Lotus Onions Oryza sativa Plants Reconstructive Surgical Procedures Rivers Secure resin cement Stem, Plant Sunlight Typha Water Resources Wetlands Zeolites
Shandong Zoucheng Taiping National Wetland Park (ZWP, 116°47’05” ~ 116°50’13” E, 35°24’51” ~ 35°26’12” N), built in 2017, is located in the west of Zoucheng City, Shandong Province, which is a typical coal mining subsidence area in the North China Plain. ZWP has a catchment area of 10.02 km2. The Shili Lake Ecological Wetland Park (JWP, 116°39’33” ~ 116°40’16” E, 35°22’11” ~ 35°23’2” N), built in 2019, is located in Jining, Shandong Province. JWP has a catchment area of 2.06 km2. The three habitats were generated by the restoration of the farmland which was destroyed by the coal mining subsidence. Specifically, the areas which were less affected by the coal mining subsidence were restored to the farmland, and wetlands were those areas which have been standing water for a long time. Lakeside grasslands were generated by the accumulation of soil obtained through excavating the surface layer of the part that was heavily affected by the coal mining subsidence. In these two areas, the main soil types are hydromorphic soils, with poor permeability but high soil fertility. The mean annual temperature is 14.2°C and the mean annual precipitation is 743 mm. The main vegetation types in wetlands are Typha orientalis C. Presl and Phragmites australis (Cav.) Trin. ex Steud. The main crop grown in farmlands is Zea mays L. The tillage managements in both parks are no-tillage and crop residues were left on the soil surfaces. The lakeside grasslands are dominated by Setaria viridis (L.) P. Beauv. and Liriope spicata Lour.
In October 2021, we selected three habitats (wetland, lakeside grassland and farmland) in ZWP and JWP (Fig 1). We set five 1 m × 1 m sampling sites in each habitat. At each sampling site, using a five-spot sampling method, samples of 0–20 cm topsoil were collected with a soil sampler. Each park collected fifteen bags of soil samples. And geographical co-ordinate of each site was collected by an app named the Sky Map (Shandong) as well as GPS positioning. There was no farmland in JWP, so to complete the experimental design we selected farmland nearby as a substitute (JN). JN was restored in 2012 and less affected by coal mining subsidence than the farmland in ZWP (ZN). All samples were stored at 4°C for analysis of nitrogen and the different forms of SOC firstly, then samples were naturally air-dried and sieved to 2 mm for soil properties analysis. A total of 30 bags were collected from the research areas and all experiments were completed within two months.
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Publication 2023
Crop, Avian Disease Management Fertility Liriope spicatum Nitrogen Permeability Setaria Plants Typha Wetlands Zea mays
Samples were collected 2.5 km away from the electrolytic zinc refinery in San Luis Potosi, S. L. P., Mexico, at coordinates 22°09′06.3″ N 101°02′14.3″ W, where Cd contamination has been previously reported [21 (link),48 (link)]. Twenty complete plants (15–40 cm long) of Typha latifolia and 100 g of surrounding soil were collected in December 2014. The samples were transported to the laboratory in a plastic bag, stored at 4 °C, and used for bacteria isolation and heavy metal analysis.
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Publication 2023
Bacteria Electrolytes isolation Metals, Heavy Plants Typha Zinc

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More about "Typha"

Discover the versatile world of Typha, the genus of aquatic plants also known as cattails or bulrushes.
These hardy, wetland-dwelling species thrive in marshes, swamps, and shallow ponds across temperate and tropical regions.
Typha's distinctive cylindrical flowering spikes, resembling brown sausages, and their long, linear leaves make them instantly recognizable.
Typha plays a crucial role in aquatic ecosystems, providing food and habitat for a variety of wildlife.
Historically, these plants have been used in traditional medicine and as a source of material for weaving and construction.
Today, researchers continue to explore Typha's potential applications, including its use in wastewater treatment, biofuel production, and the development of novel biomaterials.
Whether you're studying the ecology, physiology, or utilization of Typha, PubCompare.ai can help you discover the most accurate and reproducible research protocols.
Leverage AI-driven comparisons to identify the best Typha-related products and procedures, such as DNA extraction kits, acetonitrile, FEG 450 electron microscopes, sulfuric acid, D/MAX-2500 X-ray diffractometers, isorhamnetin compounds, TM3000 tabletop microscopes, PacBio Sequel II sequencing platforms, and Agilent 1290 Infinity II LC systems.
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