Ammonium chloride 130mg/5ml / Diphenhydramine 14mg/5ml oral solution

Abstract Ammonium (NH 4 + ), a breakdown product of amino acids that can be toxic at high levels, is detected by taste systems of organisms ranging from C. elegans to humans and has been used for decades in vertebrate taste research. Here we report that OTOP1, a proton-selective ion channel expressed in sour (Type III) taste receptor cells (TRCs), functions as sensor for ammonium chloride (NH 4 Cl). Extracellular NH 4 Cl evoked large dose-dependent inward currents in HEK-293 cells expressing murine OTOP1 (mOTOP1), human OTOP1 and other species variants of OTOP1, that correlated with its ability to alkalinize the cell cytosol. Mutation of a conserved intracellular arginine residue (R292) in the mOTOP1 tm 6-tm 7 linker specifically decreased responses to NH 4 Cl relative to acid stimuli. Taste responses to NH 4 Cl measured from isolated Type III TRCs, or gustatory nerves were strongly attenuated or eliminated in an Otop1 −/− mouse strain. Behavioral aversion of mice to NH 4 Cl, reduced in Skn-1a −/− mice lacking Type II TRCs, was entirely abolished in a double knockout with Otop1 . These data together reveal an unexpected role for the proton channel OTOP1 in mediating a major component of the taste of NH 4 Cl and a previously undescribed channel activation mechanism.

Abstract licence: CC BY

Quaternary ammonium compounds (Quats) are a large class of permanently charged cationic chemicals that are used in a variety of consumer and industrial products for their antimicrobial properties. Didecyl dimethyl ammonium chloride (DDAC) and alkyl (C12, C14, C16) dimethyl benzyl ammonium chloride (C12-C16 ADBAC) are frequently used as active ingredients in antimicrobials and are the focus of the current hazard assessment. Robust toxicology databases exist for both DDAC and C12-C16 ADBAC; however, the majority of available studies for DDAC and C12-C16 ADBAC are unpublished, but have been submitted to and reviewed by regulatory agencies (i.e., EPA and European Chemicals Agency) to support antimicrobial product registration. With the objective of contributing to public understanding of the robust and complete toxicology database available for DDAC and C12-C16 ADBAC, a comprehensive review was conducted using available peer-reviewed literature and unpublished data submitted to and summarized by regulatory agencies. A review of available literature indicates that DDAC and C12-C16 ADBAC have similar hazard profiles. Both DDAC and C12-C16 ADBAC are poorly absorbed via the oral and dermal exposure routes (≤10%), are not systemically distributed, and are primarily excreted in feces. DDAC and C12-C16 ADBAC are not dermal sensitizers, are not specific developmental or reproductive toxicants, are not carcinogenic or genotoxic, and do not cause systemic toxicity. DDAC and C12-C16 ADBAC are irritating/corrosive to skin at high concentrations, and are acutely toxic via the oral, dermal (C12-C16 ADBAC only), and inhalation exposure routes; however, both DDAC and C12-C16 ADBAC are considered non-volatile and are not readily aerosolized. Both DDAC and C12-C16 ADBAC can cause toxicity in repeated dose oral toxicity studies with no-observed-adverse-effect levels ranging from 10 to 93.1 mg/kg-day for DDAC and 3.7-188 mg/kg-day for C12-C16 ADBAC in subchronic and chronic studies conducted with beagles, mice, and rats. The toxicological effects associated with reported lowest-observed-adverse-effect levels for both DDAC and C12-C16 ADBAC are consistently characterized by reduced food consumption, reduced mean body weight, reduced body weight gain, and local irritation. These effects are consistent with the mode of action of an irritating/corrosive chemical. Based upon currently available data, the main concern associated with exposure to DDAC and C12-C16 ADBAC is local effects through irritation.

Abstract licence: CC BY-NC-ND

Abstract Discharging untreated dye-containing wastewater gives rise to environmental pollution. The present study investigated the removal efficiency and adsorption mechanism of Acid Red 18 (AR18) utilizing hexadecyl-trimethyl ammonium chloride (HDTMA.Cl) modified Nano-pumice (HMNP), which is a novel adsorbent for AR18 removal. The HDTMA.Cl is characterized by XRD, XRF, FESEM, TEM, BET and FTIR analysis. pH, contact time, initial concentration of dye and adsorbent dose were the four different parameters for investigating their effects on the adsorption process. Response surface methodology-central composite design was used to model and improve the study to reduce expenses and the number of experiments. According to the findings, at the ideal conditions (pH = 4.5, sorbent dosage = 2.375 g/l, AR18 concentration = 25 mg/l, and contact time = 70 min), the maximum removal effectiveness was 99%. The Langmuir (R 2 = 0.996) and pseudo-second-order (R 2 = 0.999) models were obeyed by the adsorption isotherm and kinetic, respectively. The nature of HMNP was discovered to be spontaneous, and thermodynamic investigations revealed that the AR18 adsorption process is endothermic. By tracking the adsorption capacity of the adsorbent for five cycles under ideal conditions, the reusability of HMNP was examined, which showed a reduction in HMNP's adsorption effectiveness from 99 to 85% after five consecutive recycles.

Abstract licence: CC BY

The cementation medium for ureolytic microbially induced calcium carbonate precipitation (MICP) typically consists of urea and a calcium source. While some studies have augmented this basic medium, the effects of adding substrates such as ammonium chloride are unclear. The studies detailed in this paper sought to quantify the effect of the ammonium chloride augmentation of cementation medium (CM) on the process of MICP. An aqueous MICP study was initially carried out to study the effects of adding ammonium chloride to the urea–calcium cementation medium. This batch test also explored the effect of varying the concentration of calcium chloride dihydrate (calcium source) in the CM. A subsequent sand column study was undertaken, whereby multiple treatments of CM were injected over several days to produce a biocement. Six columns were prepared using F65 sand bioaugmented with Sporosarcina pasteurii, half of which were injected with the basic medium only and half with the augmented medium for treatment two onwards. Effluent displaced from columns was tested using ion chromatography and Nesslerisation to determine the calcium and ammonium ion concentrations, respectively, and hence the treatment efficiency. Conductivity and pH testing of effluent gave insights into the bacterial urease activity. The addition of 0.187 M ammonium chloride to the CM resulted in approximately 100% chemical conversion efficiency within columns, based on calcium ion measurements, compared to only 57% and 33% efficiency for treatments three and four, respectively, when using the urea–calcium medium. Columns treated with the CM containing ammonium chloride had unconfined compressive strengths which were 1.8 times higher on average than columns treated with the urea–calcium medium only.

Abstract licence: CC BY

The interaction between water vapor and atmospheric aerosol leads to enhancement in aerosol water content, which facilitates haze development, but its concentrations, sources, and impacts remain largely unknown in polluted urban environments. Here, we show that the Indian capital, Delhi, which tops the list of polluted capital cities, also experiences the highest aerosol water yet reported worldwide. This high aerosol water promotes secondary formation of aerosols and worsens air pollution. We report that severe pollution events are commonly associated with high aerosol water which enhances light scattering and reduces visibility by 70%. Strong light scattering also suppresses the boundary layer height on winter mornings in Delhi, inhibiting dispersal of pollutants and further exacerbating morning pollution peaks. We provide evidence that ammonium chloride is the largest contributor to aerosol water in Delhi, making up 40% on average, and we highlight that regulation of chlorine-containing precursors should be considered in mitigation strategies.

Abstract licence: CC BY