Showing posts with label redox potential. Show all posts
Showing posts with label redox potential. Show all posts

Wednesday, 18 June 2025

An In-silico Analysis and Narrative Synopsis Confirming the Invalidity of ORP Use in Estimating Aqueous H2 Concentration | Chapter 4 | Recent Developments in Chemistry and Biochemistry Research Vol. 6

The aim of the study is to conduct an In-Silico Analysis and provide a Narrative Synopsis Confirming the Invalidity of ORP Use in Estimating Aqueous H2 Concentration. Oxidation-Reduction Potential (ORP) is often used to characterize functional beverages, specifically alkaline ionized water and hydrogen water. Numerous health benefits including antioxidant effects have been attributed to a negative ORP value. However, a greater negative ORP value is often incorrectly interpreted to mean a greater degree of health benefits and/or a high concentration of H2. However, ORP is not specific to H2 gas but any redox-active molecules. Recent fatalities have occurred due to conflating a negative ORP with health benefits due to the use of toxic chemicals to induce a negative ORP. Additionally, when ORP meters are used to estimate H2 gas, the readings can be highly unreliable. For example, hydrogen meters use the Nernst equation to calculate the concentration of H2 based on the measured ORP value. Unfortunately, due to the fundamental limitations of the ORP meter, the calculated H2 value may be very inaccurate. Using the Nernst equation, we performed an in-silico analysis of the ORP as a function of pH, temperature, and H2 concentration. Our analysis shows that a one-unit increase in pH (e.g., 7-8) influences the ORP by as much as increasing the H2 concentration by 100 times (e.g., 1 to 100 mg/L). Similarly, at a saturated H2 concentration (1.57 mg/L) and pH 7, every ΔT of 20°C changes the ORP by ≈ 30 mV. This is comparable to changing the H2 concentration by a factor of 10 (0.1 mg/L to 1 mg/L).  Moreover, to measure H2 within 0.1 mg/L, ORP meters need to have an accuracy of about 0.8 mV. However, ORP meters have an error range of at least ±10 mV, which corresponds to a potential error in measured H2 concentration of nearly 2 mg/L (≈125% error). This analysis shows that pH, temperature, and intrinsic ORP errors can individually influence the ORP greater than the entire contribution of dissolved H2 within normally used ranges. Consequently, this can easily result in a water sample with a greater negative ORP than another despite having significantly less H2. Thus, it becomes impossible to consistently determine if one water sample has more H2 than another water sample. However, the analyses and calculations were performed only with the variables included in the equations, which can be considered a limitation of this study. Finally, we can only conclude, based on a negative ORP reading, that, excluding the possibility of other reductive redox couples, some level of dissolved H2 is present in the water. Accordingly, ORP and ORP-based H2 meters are not reliable for testing or comparing the concentration of H2 in water. Inherent fluctuations in the ORP meter, combined with the significant influence that even small deviations in pH and temperature have on the ORP, will always dominate the ORP measurement.

 

Author (s) Details

Tyler W. LeBaron
Molecular Hydrogen Institute, Enoch, Utah, USA and Department of Kinesiology and Outdoor Recreation, Southern Utah University, Cedar City, Utah, USA.

 

Randy Sharpe
H2 Analytics, Henderson, NV, USA.

 

 

Please see the book here: https://doi.org/10.9734/bpi/rdcbr/v6/1788

Saturday, 15 March 2025

A Review on Sources, Hydrochemical and Temporal Changes of Arsenic Contamination in the Groundwater of Ballia and Ghazipur Districts, India | Chapter 9 | Geography, Earth Science and Environment: Research Highlights Vol. 7

Arsenic contamination in groundwater has emerged as a significant environmental and public health challenge, both nationally and globally. Recent assessments of groundwater samples from key regions in the north-eastern states of India reveal arsenic concentrations ranging from 50 to 986 µg/L, exceeding the permissible limits set by the World Health Organization (WHO) and the Bureau of Indian Standards (BIS), which are 10 µg/L and 50 µg/L, respectively. The seasonal behavior of arsenic is largely governed by geochemical processes, wherein iron (III) oxyhydroxide decomposition during the monsoon season releases arsenic into the groundwater, while its adsorption onto iron (III) oxyhydroxide occurs during the pre-monsoon season.

This study examines the sources, hydro-chemical characteristics, and seasonal variations of arsenic in groundwater within the Ballia and Ghazipur districts of Eastern Uttar Pradesh. As predicaments in the environment are due to its mobilization under natural geogenic conditions as well as anthropogenic activities. Arsenic mineral is not present in As contaminated alluvial aquifer but As occurs adsorbed on hydrated ferric oxide (HFO) and generally coats clastic grains derived from Himalayan mountains. As is released to the groundwater mainly by bio-remediated reductive dissolution of HFO with corresponding oxidation of organic matter. The development of strongly reductive dissolution of mineral oxides (Fe and Mn) at near-neutral pH may lead to desorption and ultimately release of As into the groundwater. As release through the geochemical process is a more important factor in alluvial aquifers causing As contamination rather than sources of arsenic. During the monsoon, rising water tables and flood conditions contribute to arsenic dilution, whereas prolonged moisture retention restricts groundwater movement, affecting arsenic dispersion. This study highlights the impact of hydrological cycles on arsenic behavior, providing insights for effective groundwater management in arsenic-affected regions.

 

Author (s) Details

Akbare Azam
Department of Chemistry, Govt. Girls’ P. G. College Ghazipur, Uttar Pradesh, India.

 

Hemant Kumar Nirala
Department of Chemistry, Govt. Girls’ Degree College Saiyadraja Chandauli, Uttar Pradesh, India.

 

J. K. Pandey
Department of Chemistry, St. Andrew’s College Gorakhpur, Uttar Pradesh, India.

 

Ruby Ahmed
Department of Chemistry, Shibli National College Azamgadh, Uttar Pradesh, India.

 

Trinath Mishra
Department of Chemistry P. G. College, Ghazipur, Uttar Pradesh, India.

 

Manisha
Department of Home Science, Govt. Degree College Sahjanwa, Gorakhpur, Uttar Pradesh, India.

 

Sankatha Prasad Sonkar
Department of Chemistry Govt. P. G. College Chunar Mirzapur, Uttar Pradesh, India.

 

Awanish Kumar Pandey
Department of Chemistry S. M. M. Town P. G. College Ballia, Uttar Pradesh, India.

 

Please see the book here:- https://doi.org/10.9734/bpi/geserh/v7/4743