Chlorine
It is widely used in water purification, disinfection, and the production of plastics, pesticides, and other chemicals.
Chlorine has a distinctive green-yellow color and a pungent odor.
Exposure to high concentrations of chlorine can be hazardous, causing respiratory irritation and other health effects.
Researchers studying chlorine and its applications can utilize the PubCompare.ai platform to easily locate relevant protocols from literature, preprints, and patents, as well as leverage AI-driven comparisons to identify the most effective protocols and products for their chlorine-related studies.
This streamlines the research process and helps ensure more reliable and reproducible results.
Most cited protocols related to «Chlorine»
The amino acids composing the binding site of the mammalian cyclooxygenases considered in this study (Table
The latrine component of the sanitation intervention was a compound level intervention. The drinking water and handwashing interventions were household level interventions. The nutrition intervention was a child-specific intervention. We assessed the diarrhoea outcome among all children in the compound who were younger than 3 years at enrolment, which could underestimate the effect of interventions targeted only to index households (drinking water, and handwashing) or index children (nutrition). After the study results were unmasked, we analysed diarrhoea prevalence restricted to index children (ie, children directly targeted by each intervention).
The study protocol was approved by the Ethical Review Committee at The International Centre for Diarrhoeal Disease Research, Bangladesh (PR-11063), the Committee for the Protection of Human Subjects at the University of California, Berkeley (2011-09-3652), and the institutional review board at Stanford University (25863).
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Most recents protocols related to «Chlorine»
Example 8
Characterization of Absorption, Distribution, Metabolism, and Excretion of Oral [14C]Vorasidenib with Concomitant Intravenous Microdose Administration of [13C315N3]Vorasidenib in Humans
Metabolite profiling and identification of vorasidenib (AG-881) was performed in plasma, urine, and fecal samples collected from five healthy subjects after a single 50-mg (100 μCi) oral dose of [14C]AG-881 and concomitant intravenous microdose of [13C3 15N3]AG-881.
Plasma samples collected at selected time points from 0 through 336 hour postdose were pooled across subjects to generate 0—to 72 and 96-336-hour area under the concentration-time curve (AUC)-representative samples. Urine and feces samples were pooled by subject to generate individual urine and fecal pools. Plasma, urine, and feces samples were extracted, as appropriate, the extracts were profiled using high performance liquid chromatography (HPLC), and metabolites were identified by liquid chromatography-mass spectrometry (LC-MS and/or LC-MS/MS) analysis and by comparison of retention time with reference standards, when available.
Due to low radioactivity in samples, plasma metabolite profiling was performed by using accelerator mass spectrometry (AMS). In plasma, AG-881 was accounted for 66.24 and 29.47% of the total radioactivity in the pooled AUC0-72 h and AUC96-336 h plasma, respectively. The most abundant radioactive peak (P7; M458) represented 0.10 and 43.92% of total radioactivity for pooled AUC0-72 and AUC96-336 h plasma, respectively. All other radioactive peaks accounted for less than 6% of the total plasma radioactivity and were not identified.
The majority of the radioactivity recovered in feces was associated with unchanged AG-881 (55.5% of the dose), while no AG-881 was detected in urine. In comparison, metabolites in excreta accounted for approximately 18% of dose in feces and for approximately 4% of dose in urine. M515, M460-1, M499, M516/M460-2, and M472/M476 were the most abundant metabolites in feces, and each accounted for approximately 2 to 5% of the radioactive dose, while M266 was the most abundant metabolite identified in urine and accounted for a mean of 2.54% of the dose. The remaining radioactive components in urine and feces each accounted for <1% of the dose.
Overall, the data presented indicate [14C]AG-881 underwent moderate metabolism after a single oral dose of 50-mg (100 μCi) and was eliminated in humans via a combination of metabolism and excretion of unchanged parent. AG-881 metabolism involved the oxidation and conjugation with glutathione (GSH) by displacement of the chlorine at the chloropyridine moiety. Subsequent biotransformation of GSH intermediates resulted in elimination of both glutamic acid and glycine to form the cysteinyl conjugates (M515 and M499). The cysteinyl conjugates were further converted by a series of biotransformation reactions such as oxidation, S-dealkylation, S-methylation, S-oxidation, S-acetylation and N-dealkylation resulting in the formation multiple metabolites.
A summary of the metabolites observed is included in Table 2
Example 12
Plant transformation—The Arabidopsis thaliana var Columbia (To plants) were transformed according to the Floral Dip procedure [Clough S J, Bent A F. (1998) Floral dip: a simplified method for Agrobacterium-mediated transformation of Arabidopsis thaliana. Plant J. 16(6): 735-43; and Desfeux C, Clough S J, Bent A F. (2000) Female reproductive tissues were the primary targets of Agrobacterium-mediated transformation by the Arabidopsis floral-dip method. Plant Physiol. 123(3): 895-904] with minor modifications. Briefly, Arabidopsis thaliana Columbia (C010) T0 plants were sown in 250 ml pots filled with wet peat-based growth mix. The pots were covered with aluminum foil and a plastic dome, kept at 4° C. for 3-4 days, then uncovered and incubated in a growth chamber at 18-24° C. under 16/8 hours light/dark cycles. The T0 plants were ready for transformation six days before anthesis.
Single colonies of Agrobacterium carrying the binary vectors harboring the genes of some embodiments of the invention were cultured in YEBS medium (Yeast extract 1 gr/L, Beef extract 5 gr/L, MgSO4*7H2O, Bacto peptone 5 gr/L) supplemented with kanamycin (50 mg/L) and gentamycin (50 mg/L). The cultures were incubated at 28° C. for 48 hours under vigorous shaking to desired optical density at 600 nm of 0.85 to 1.1. Before transformation into plants, 60 μl of Silwet L-77 was added into 300 ml of the Agrobacterium suspension.
Transformation of T0 plants was performed by inverting each plant into an Agrobacterium suspension such that the above ground plant tissue was submerged for 1 minute. Each inoculated T0 plant was immediately placed in a plastic tray, then covered with clear plastic dome to maintain humidity and was kept in the dark at room temperature for 18 hours to facilitate infection and transformation. Transformed (transgenic) plants were then uncovered and transferred to a greenhouse for recovery and maturation. The transgenic T0 plants were grown in the greenhouse for 3-5 weeks until siliques were brown and dry, then seeds were harvested from plants and kept at room temperature until sowing.
For generating T1 and T2 transgenic plants harboring the genes of some embodiments of the invention, seeds collected from transgenic T0 plants were surface-sterilized by exposing to chlorine fumes (6% sodium hypochlorite with 1.3% HCl) for 100 minutes. The surface-sterilized seeds were sown on culture plates containing half-strength Murashig-Skoog (Duchefa); 2% sucrose; 0.5% plant agar; 50 mg/L kanamycin; and 200 mg/L carbenicylin (Duchefa). The culture plates were incubated at 4° C. for 48 hours and then were transferred to a growth room at 25° C. for three weeks. Following incubation, the T1 plants were removed from culture plates and planted in growth mix contained in 250 ml pots. The transgenic plants were allowed to grow in a greenhouse to maturity. Seeds harvested from T1 plants were cultured and grown to maturity as T2 plants under the same conditions as used for culturing and growing the T1 plants.
8 cities in Europe (Prague, Venice, Sardinia, Marseille, Leipzig,
Brussels, Stockholm, and Uppsala) were collected during summer 2021.
Samples from 3 public swimming pools in Germany were taken in February
2022. Grab samples from 6 DWTPs before and after disinfection, including
DWTP 1 and 2 in Germany (5 sets each of repeated samples every 2 weeks),
DWTP 3, 4, and 5 in Hungary (3 sets each of repeated samples every
2 months), and DWTP 6 in Spain (1 set of sample), were collected during
January-November 2021 (sampling details are given below). DWTP 1 uses
the mixture of groundwater and river bank filtrate as source water.
The treatment trains include aeration, gravel filtration, and chlorine
gas disinfection. DWTP 2 uses river bank filtrate and utilizes aeration,
flocculation, gravel filtration, and chlorine dioxide disinfection.
DWTP 3, 4, and 5 use river bank filtrate. In DWTP 3 and 4, the raw
water is directly disinfected using sodium hypochlorite and chlorine
gas, respectively, without additional treatment. In DWTP 5, the raw
water is treated by ozone and sand filtration for iron and manganese
removal, followed by chlorine gas disinfection. The disinfected water
from DWTP 3, 4, and 5 was used to provide drinking water to a city
in Hungary. Two sets of additional samples from 2 entry points to
the distribution system and 2 drinking water storage reservoirs within
this city were collected in September and November 2021. DWTP 6 uses
surface water, which is treated through flocculation and filtration
and by chlorine gas, as the final step.
Samples were collected
in prewashed 100 mL borosilicate brown glass bottles, transported
to the lab in the thermobox (10–12 °C), and enriched within
24 h of collection (see
was measured online or using a portable device (Pocket Colorimeter
II, HACH) during sampling, which was in the range of ∼0.2–0.3
mg/L as Cl2 except for DWTP 6 (i.e., ∼0.5–1.0
mg/L as Cl2). Lab tests suggested that some of the novel
halogenated sulfonic acids are not stable in the presence of a quenching
reagent (e.g., ascorbic acid,
residual chlorine during sampling. A control sample prepared with
100 mL of ultrapure water spiked with 0.3 mg/L chlorine was preserved
for 24 h, enriched, and analyzed following the same procedure as water
samples. Results indicated that no contamination can occur during
sample processing and analysis due to the potential presence of a
trace amount of chlorine in the disinfected samples. Detailed information
on sampling dates and water parameters is given in
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More about "Chlorine"
It is a key component in water purification, disinfection, and the production of various plastics, pesticides, and other chemicals.
The distinctive green-yellow color and pungent odor of chlorine make it readily identifiable.
Researchers studying chlorine and its applications can leverage the PubCompare.ai platform to seamlessly locate relevant protocols from literature, preprints, and patents.
This AI-driven platform also enables researchers to compare and identify the most effective protocols and products for their chlorine-related studies, streamlining the research process and ensuring more reliable and reproducible results.
In addition to chlorine, researchers may also encounter other related chemicals such as sodium hydroxide, sodium hypochlorite, sodium hypochlorite solution, hydrochloric acid, acetic acid, gallic acid, and acetonitrile.
These compounds often play complementary roles in chlorine-based processes and applications.
Sodium hydroxide, for example, is commonly used in the production of sodium hypochlorite, a widely used disinfectant.
Hydrochloric acid is another key chemical that interacts with chlorine, and acetic acid, gallic acid, and acetonitrile may be utilized in various analytical techniques and processes involving chlorine-based compounds.
By understanding the broader context of chlorine and its related chemicals, researchers can make more informed decisions, optimize their experimental designs, and ultimately achieve more robust and reproducible findings in their chlorine-focused studies.