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Whatman filter paper

Manufactured by Cytiva
Sourced in United Kingdom, United States, Germany, Japan, Switzerland, China, India
About the product

Whatman filter paper is a laboratory filtration product designed for various filtering applications. It is manufactured to provide consistent quality and performance. The core function of Whatman filter paper is to separate solid particles from liquids or gases through the process of filtration.

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Market Availability & Pricing

Whatman filter papers are commercialized by Cytiva and available through authorized distributors. The prices vary depending on the specific grade and size, but no discontinued or obsolete models are mentioned. For example, Whatman Grade 1 Qualitative Filter Papers are available in various sizes, with prices ranging from approximately $15.20 to $142.75 per box of 100 sheets. Similarly, Whatman Grade 54 Quantitative Filter Papers are offered in multiple sizes, with prices between $55.00 and $1,229.00 per pack of 100 sheets.

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The spelling variants listed below correspond to different ways the product may be referred to in scientific literature.
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2 310 protocols using «whatman filter paper»

1

Green Synthesis of Citrus Nanoparticles

2025
The preparation of a Citrusfusion extract involved obtaining leaves from Citrus limon and Citrus medica for green synthesis of nanoparticles, leveraging their bioactive compounds. Fresh leaves were carefully harvested, sterilized, and ground into a fine paste. This paste was then macerated in autoclaved distilled water overnight, utilizing a specific weight-to-volume ratio. Subsequently, the macerated extract underwent triple filtration using centrifugation and Whatman filter paper to eliminate fibres and small leaf sediments, ensuring a pure extract. The Citrus limon and Citrus medica extracts were mixed into Citrusfusion extract with an equal 1:1 ratio. The clarified extract was then stored at 4 °C for preservation.
The phytochemical analysis of Citrus limon and Citrus medica leaf extracts involved a comprehensive assessment of their bioactive constituents, including phenols, tannins, flavonoids, saponins, anthocyanins, alkaloids, steroids, and carotenoids. The evaluation followed established protocols as outlined by [12 (link)], ensuring meticulous identification and characterization of these phytochemicals.
Citrus limon (lemon) and Citrus medica (citron) used in study was identified and authenticated by Dr. D. Narasimhan, Botanist, Chennai. A specimen of the plant was deposited at School of Life Sciences, BSACIST, Chennai (Accession number: SLS-BSAU-23,008).
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2

Cultivating Chlorococcum sp. Using Dairy and Paper Wastewater

2025
The dairy wastewater (DWW) and paper-and-pulp wastewater (PWW) utilized in this research was supplied by local dairy industry and paper-and-pulp industry located in KwaZulu-Natal Provine, South Africa. The DWW was collected from the storage tank containing both processing and cleaning wastewaters generated during dairy production. While the PWW sample was obtained from the secondary effluent treatment plant. Each wastewater sample (20 L) was filtered separately using Whatman filter paper to get rid of the solid particles. Subsequently, these filtered samples were combined in various proportions to make a wastewater mixture formulation ratio for the cultivation of Chlorococcum sp. A comprehensive analysis of the physicochemical characteristics of the DWW and PWW is presented in Table 1.

Physico-chemical parameters of DWW and PWW.

Table 1
ParameterUnitDairy wastewaterPaper and pulp wastewater
pH2.876.94
ColourWhiteBrown
CODmg/L876955
TNmg/L736.25562.25
TPmg/L27.071.20
Namg/L237.731153.73
Kmg/L27.7368.40
Camg/L50.8048.00
Mgmg/L5.4718.13
Femg/L0.240.04
Cumg/L0.010.004
Znmg/L0.130.04
Mnmg/L0.040.76
Almg/L0.150.52

TN-Total nitrogen, TP- Total phosphorous.

Thereafter the wastewater collection, a preliminary assessment was performed to evaluate the viability of DWW and PPW as a sole or combined medium, as well as treated or untreated for the cultivation of Chlorococcum sp. The pH of the treated wastewater was adjusted to pH 7.1 and autoclaved at 121 °C for 15 min before the wastewater was used for the cultivation. Then the cultivation experiments in an Erlenmeyer flask (100 mL working volume) were conducted under growth conditions of pH 7.1, ambient temperature, agitation speed (150 rpm) and cultivation duration of three weeks.
Furthermore, varied amount of DWW and PWW with or without BG11 medium supplementation was utilized to cultivate Chlorococcum sp with the most favourable condition (Table 2) then modelled and optimized.

Selected mixtures for the optimization model.

Table 2
MixtureBG11 (%)PWW (%)DWW (%)BG11+PWW + DWW (%)
DWBG25 (A)25075100
DWBG50 (B)50050100
DWPWBG25 (C)252550100
DWPWBG50 (D)502525100
A + B + C + D15050200400

DWBG25: Dairy wastewater (75 %) and blue-green algae 11 (25 %); DWBG50: Dairy wastewater (50 %) and blue-green algae 11 (50 %); DWPWBG25: Dairy wastewater (50 %), paper and pulp wastewater (25 %) and blue-green algae 11 (25 %); DWPWBG50: Dairy wastewater (25 %), paper and pulp wastewater (25 %) and blue-green algae 11 (50 %).

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3

Phytotoxic Assessment of Essential Oils

2025
The phytotoxic activity was evaluated against the seed germination and radicle emergence/elongation of two weeds, Lolium multiflorum Lam. and Trifolium pratense L., and two horticultural crops, Brassica napus L. and Hordeum vulgare L. The seeds were purchased from Blumen group srl (Emilia-Romagna, Italy). The seeds were surface-sterilized in 96% ethanol for 15 s and sown in Petri dishes (Ø = 90 mm) on three layers of Whatman filter paper. They were impregnated with 7 mL of deionized water, and then 7 mL of a water–acetone mixture (99.5:0.5, v/v) was used as the control since EOs were dissolved in this mixture due to their lipophilicity. Finally, 7 mL of the EO solution at different concentrations (1000, 500, 250 and 125 μg/mL) was tested. The controls carried out with the water–acetone mixture alone showed no differences in comparison to the controls in water alone. The germination conditions were 20 ± 1 °C, with a natural photoperiod. Seed germination was checked in Petri dishes every 24 h. A seed was considered germinated when the protrusion of the root became evident [60 (link)]. On the fifth day (after 120 h) for B. napus and H. vulgare and on the seventh day (after 168 h) for the other seeds, the effects on radicle elongation were determined by measuring the root length in cm. Each evaluation was replicated three times, using Petri dishes containing 10 seeds each. The data were expressed as the mean ± standard deviation for both germination and radicle elongation.
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4

Extraction of Bioactive Compounds from Albizia Gummifera Mistletoe Leaves

2025
Mistletoes of Albizia Gummifera (P. macrosolen L.) leaf was collected from Dambi Dollo University, integrated research area that was naturally available as wild plant Fig. 1 and cleaned systematically under running water then dried at room temperatures for six days. Then the dried leaf was grounded to make a powder. The solutions of leaf was prepared by taking 5 g leaf powder added to 50 ml of de-ionized water and then heated for 30 min in temperature of 70 °C to make soften the cell wall of leaf to release bioactive compounds. Then extract was cooled at room temperature then, filtered through What-man filter paper followed by centrifuge at 1500 rpm for 15 min to eradicate heavy substances, and then the upper pure solution was collected and preserved in a refrigerator at 4 °C for further uses. A leaf of Mistletoes of Albizia Gummifera (P. macrosolen L.) was gathered from Dambi Dollo University and Dambi Dollo Town, Oromia, Ethiopia. The plant we have used in this report was cultivated in Dambi Dollo University research center, Oromia, Ethiopia. This study complies with relevant international, national, institutional and legislative guidelines.
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5

Solvent Extraction and GC-MS Analysis

2025
The cultured solution was filtered using Whatman filter paper with an 11 μm pore size, and any remaining PE particles were rinsed with methanol. The filtered culture solution was then combined with ethyl acetate in a 1:1 ratio, vortexed for 10 min, and centrifuged at 13,000 rpm for 20 min to isolate the supernatant. The extract was analyzed using a gas chromatograph-mass spectrometer (GC-MS) (QP2020 NX, Shimadzu) equipped with an electron impact ionization source and a DB-5MS capillary column (Agilent, USA). The column temperature was programmed to increase from 40°C to 280°C at a rate of 6°C min–1, with an initial hold at 40°C for 2 min and a final hold at 280°C for 3 min. The chemical structures of the products were determined using the GC-MS data and the NIST/WILEY database.
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