Corrosive Substances
Corrosive substances are materials, such as strong acids and strong bases, that, through chemical reactions, cause visible destruction of biological tissues, and other materials. Acids are substances that have a high tendency to donate protons when completely dissociating into ions in water; whereas strong bases are substances that accept protons when completely dissociating into ions in water. Both are highly corrosive and catalyse the decomposition of biological molecules. (Burrows et al., 2021)
Primary reference(s)
Burrows et al., 2021. A. Burrows, J. Holman, S. Lancaster, T. Overton, A. Parsons, G. Piling, G. Price. Chemistry3 Fourth Edition (2021). ISBN-13: 978-0198829980. ISBN-10: 0198829981.
Annotations
Additional scientific description
Both acids and bases can cause major public harm. They are both principally corrosive because they catalyse hydrolysis reactions and other nucleophilic substitution reactions that result in decomposition of biological molecules. (Brown, 2018; Burrows et al., 2021; McMurry, 2004; Wade and Simek, 2022) Acids are chemical species that are capable of donating a proton (Bronsted Acid) or capable of forming a covalent bond with an electron pair (Lewis Acid). (IUPAC, 2014) The dissociation process of strong acids almost goes to completion, meaning almost all of the acid molecules break apart into ions, producing high concentrations of hydronium ions that can initiate undesirable chemical reactions. This characteristic is in contrast to weak acids, which only partially dissociate in water. (Wade and Simek, 2022) Examples of strong acids include hydrochloric acid, nitric acid (ICSC 0183, 2016), perchloric acid (ICSC 1006, 2000) and sulfuric acid (ICSC 0362, 2016).
Bases are chemical species that have an available pair of electrons capable of forming a covalent bond with a proton (BrΓΈnsted base) or with the vacant orbital of some other species (Lewis base). (IUPAC, 2014) The dissociation process of strong bases goes to completion, producing high concentrations of hydroxide ions. They have a high affinity for accepting protons which fully neutralises them. The strength of the base is measured by its ability to donate hydroxide ions in solution. Lewis theory defines a strong base as an electron pair donor, making them effective at forming bonds with electron-deficient species. (Atkins & Jones, 2010; Burrows et al.,2021; McMurry et al., 2004; Wade and Simek, 2022) Examples of strong bases include caesium hydroxide (ICSC 1592, 2006), calcium hydroxide (ICSC 0408, 1997), lithium hydroxide (ICSC 0913, 2009), potassium hydroxide (ICSC 0357, 2010) and sodium hydroxide (ICSC 0360, 2010).
Lewis acids are electron-pair acceptors that are able to react with a Lewis acid base to form a Lewis adduct, by sharing the electron pair donated by the Lewis base. (IUPAC, 2014)
πΏπΏπΏπΏπΏπΏπΏπΏπΏπΏ π΄π΄π΄π΄πΏπΏπ΄π΄ + πΏπΏπΏπΏπΏπΏπΏπΏπΏπΏ π΅π΅π΅π΅πΏπΏπΏπΏ β πΏπΏπΏπΏπΏπΏπΏπΏπΏπΏ π΄π΄π΄π΄π΄π΄π΄π΄π΄π΄π΄π΄
Acids and bases can form conjugate acid-base pairs, where the acid formed on protonation of a base is called the conjugate acid, and the base is the conjugate base. The conjugate acid always carries one unit of positive charge more than the base, but the absolute charges of the species are immaterial to the definition. (IUPAC, 2014h) Strong acid-base reactions are typically exothermic - the new bond formed between the proton and the base is stronger than the bond that was broken to release the proton, therefore the released energy raises the temperature of the surroundings. The strength of an acid is inversely proportional to the strength of its conjugate base - i.e. the conjugate base of a strong acid must be a weak base; and the conjugate base of a weak acid must be a strong base. In the reaction of an acid with a base, the equilibrium generally favours the weather acid and base. (Wade and Simek, 2022)
Metrics and numeric limits
Metrics are used to quantify the strength of acids, including their pH, pOH, pKa, and pKb; acidity/ionisation constants (Ka, Kb and Kw); degree of dissociations; and concentrations. pH (equation 1) is a measure of how acidic or alkaline a substance is, ranging (for aqueous solutions) from 0 (strongly acidic) to 14 (strongly basic).
Equation 1: ππππ + ππππππ = 14
Strong acids have high concentrations of hydronium ions, typically giving low pH values close to zero when fully dissociated in water. The pKa (equation 2) is a measure of the concentration of hydrogen ions when there are equal concentrations of both the ionised and unionised form of a substance. Strong acids also tend to have pKa values below zero due to their equilibrium lying to the far right, resulting in negligible concentrations of undissociated acid. Whereas strong bases have high concentrations of hydroxide ions, typically giving high pH values close to 14 when fully dissociated in water. The pOH is a measure of the concentration of hydroxide ions in a solution. Strong bases also tend to have pOH values close to zero.
Equation 2: πππΎπΎππ+ πππΎπΎππ = πππΎπΎπ€π€
The acidity constant (Ka equation 3) is another equilibrium constant for splitting off a proton from a charged or uncharged acid. This metric is usually very high for a strong acid, indicating complete dissociation. (IUPAC, 2014) Due to this dissociation, the concentrations are also typically very high.
Equation 3: πΎπΎπππΎπΎππ = πΎπΎπ€π€
The ionisation constant is another equilibrium constant for quantifying the extent to which a base ionises in solution. This metric is usually very large for a strong base, indicating complete ionisation. The degree of dissociation is how much the strong base completely dissociates into ions when dissolved in water, producing hydroxide ions. Acids can be neutralised by strong bases, producing water and salt during the vigorous reaction. This is due to the high concentration of hydroxide ions, giving an overall high concentration for a strong base.
Key relevant UN convention / multilateral treaty
Occupational Safety and Health Administration (OSHA), Chemical Hazards and Toxic Substances: Controlling Exposure. (OSHA, 2024)
European Union (EUR), The Registration, Evaluation, Authorisation and Restriction of Chemicals (REACH) Regulation. (EUR-Lex, 2023)
United Nations Environment Programme (UNEP), Basel Convention on the Control of Transboundary Movements of Hazardous Wastes and Their Disposal (UNEP, 2011).
United Nations Environment Programme (UNEP), Rotterdam Convention on the Prior Informed Consent (PIC) Procedure for Certain Hazardous Chemicals and Pesticides in International Trade (UNEP, 2010).
United Nations Environment Programme (UNEP), Stockholm Convention on Persistent Organic Pollutants (POPs) (UNEP, 2019).
Organisation for the Prohibition of Chemical Weapons (OPCW), Chemical Weapons Convention (OPCW, 2024a,b).
United Nations Environment Programme (UNEP), Montreal Protocol on Substances that Deplete the Ozone Layer (UNEP, 2020)
Drivers
Hazard Drivers of corrosive substances, such as strong acids and bases, largely result from their widespread use in industry, as well as in laboratories, for chemical manufacture and synthesis. Industrial processes often use large amounts of acids or bases, such as sulfuric acid, sodium hydroxide and potassium hydroxide, which can lead to hazardous situations. Strong bases are also used in water treatment processes to adjust pH levels and neutralise acidic wastes.
Impacts
Impacts of strong acids include improper disposal or accidental release, which can lead to soil and water contamination, harming aquatic life and ecosystems, as well as acid rain (HIP MH0033), which is primarily caused by sulfuric and nitric acids - release of sulphur and nitrogen oxides can also lead to air pollution (HIP MH0018; HIP EN0001; HIP EN0002). (EPA, 2024) Acid rain (HIP MH0033) can lead to the corrosion of metals and infrastructure, resulting in leaks, structural failures, and costly repairs. Other impacts include human health risks - coming into contact with strong acids and bases can cause severe chemical burns, skin irritation, eye damage, and respiratory issues. Inhalation of strong acid or strong base vapours can lead to respiratory problems. (NIH, 2022)
Multi-hazard context
The figure below summarises common interactions between strong acids & strong bases and other hazards. This information should be used with caution and not be solely relied upon in Disaster Risk Management, particularly as some interactions may not have been included. Note that hazardous events occurring together or locally in space or time may not necessarily cause, amplify or be otherwise related to each other. Specific examples of multi-hazard context can be found in the βHazard driversβ and βImpactsβ sections above.
Multi-hazard diagram
Risk Management
Strategies include implementing strict safety protocols, providing adequate personal protective equipment (PPE), and conducting thorough employee training on the safe handling and storage of strong acids. (OSHA, 2024) Examples of safety implementations include installing fume hoods, ventilation systems, and acid-resistant materials that can minimise exposure and prevent accidental releases. Ensuring the proper disposal of chemicals through the treatment and disposal methods that minimise environmental impact. Adhering to regulatory requirements and industry standards can also mitigate risks. Further risk management strategies include developing comprehensive emergency response plans, including procedures for spill containment, evacuation, and medical treatment. (NFPA, 2020) In the case of a disaster, using spill kits and flushing the strong acids with plenty of water is advised.
Monitoring
The section and the table below offer an overview of monitoring strong acids & strong bases. This information can be used for forecasting within a national early warning system (EWS). Since EWS capacities and processes differ across countries, the most current and specific information regarding EWS should be obtained from the appropriate national or regional agency/authority responsible for disaster management.
| Which institution(s) produce(s) Disaster Risk Data/Information? | Regulatory agencies; health and safety agencies; fire services; manufacturers of chemicals provide material safety data sheets |
| How is the Hazard Observed/Monitored/Forecast? | Sensors; monitoring and alarm systems; preventative maintenance and inspection |
References
Atkins & Jones, 2010. P. Atkins & L. Jones. Chemical Principles: The Quest for Insight Fifth Edition (2010). Pages 306-307. ISBN-13: 978-1-4292-1955-6. ISBN-10: 1-4292-1955-6.
Brown et al., 2018. T. L. Brown, H. E. LeMay, B. E. Bursten, C. Murphy, P. Woodward. Chemistry: The Central Science Fourteenth Edition (2018). ISBN: 978-0134414232.
Burrows et al., 2021. A. Burrows, J. Holman, S. Lancaster, T. Overton, A. Parsons, G. Piling, G. Price. Chemistry3 Fourth Edition (2021). ISBN-13: 978-0198829980. ISBN-10: 0198829981.
EUR-Lex, 2023. The Registration, Evaluation, Authorisation and Restriction of Chemicals (REACH) Regulation. European Union (EUR). Accessed 11 May 2024.
ICSC 2024. International Chemical Safety Cards (ICSC). International Labour Organization (ILO). Accessed 29 Aug 2024.
IUPAC, 2014. IUPAC Compendium of Chemical Terminology, 3rd edition (2006). International Union of Pure and Applied Chemistry (IUPAC). Accessed 25 May 2024.
McMurry et al., 2004. J. McMurry, R. C. Fay, J. K. Robinson. Chemistry Fourth Edition (2004). ISBN-13: 978-0131402089. ISBN-10: 0131402080.
NFPA, 2020. NFPA 1620 Standard for Pre-Incident Planning (2020). National Fire Protection Association (NFPA). Accessed 11 May 2024.
NIH, 2022. Hazardous Substances Data Bank (HSDB) (2022). NIH National Library of Medicine, National Center for Biotechnology Information. Accessed 11 May 2024.
OPCW, 2024a. Chemical Weapons Convention: Article II: Definitions and criteria. Organisation for the Prohibition of Chemical Weapons (OPCW). Accessed 6 April 2024.
OPCW, 2024b. Chemical Weapons Convention: Verification Annex, Part IV(A), paras. 15-19. Organisation for the Prohibition of Chemical Weapons (OPCW). Accessed 6 April 2024.
OSHA, 2024. Chemical Hazards and Toxic Substances: Controlling Exposure. Occupational Safety and Health Administration (OSHA). Accessed 11 May 2024.
UNECE, 2023. Globally Harmonised System (GHS) of Classification and Labelling of Chemicals (2023). United Nations Economic Commission for Europe (UNECE). Accessed 11 May 2024.
UNEP, 2011. Basel Convention on the Control of Transboundary Movements of Hazardous Wastes and Their Disposal (2011). United Nations Environment Programme (UNEP). Accessed 4 May 2024.
UNEP, 2010. Rotterdam Convention on the Prior Informed Consent (PIC) Procedure for Certain Hazardous Chemicals and Pesticides in International Trade (2010). United Nations Environment Programme (UNEP). Accessed 4 May 2024.
UNEP, 2019. Stockholm Convention on Persistent Organic Pollutants (POPs) (2019). United Nations Environment Programme (UNEP). Accessed 4 May 2024.
UNEP, 2020. Montreal Protocol on Substances that Deplete the Ozone Layer (2020). United Nations Environment Programme (UNEP). Accessed 12 May 2024.
Wade and Simek, 2022. L. G. Wade Jr and J. W. Simek. Organic Chemistry Tenth Edition (2022). ISBN-13: 978-1292424255. ISBN-10: 1292424257.