Calculating Pollution Tolerance: A Guide To Understanding The Metrics

how to calculate pollution tolerance

The Pollution Tolerance Index is a method of measuring an organism's or community's response to pollution-induced selective pressures. It can be used to evaluate the level of pollution in an area by observing the presence or absence of certain taxa or groups of organisms, which are known to be more or less tolerant of polluted conditions. The Air Pollution Tolerance Index (APTI) is a specific index used to assess the resistance of plant species to air pollution. The APTI is calculated using a formula that takes into account various biochemical parameters such as ascorbic acid content, chlorophyll content, leaf extract pH, and relative water content. The Pollution-Induced Community Tolerance (PICT) is another approach that assesses the tolerance of a community to toxicants and can be applied to any ecosystem.

Characteristics Values
Calculation of Pollution Tolerance Index APTI (Air Pollution Tolerance Index) is calculated using the formula proposed by Singh and Rao (1983) where A is the ascorbic acid (mg g-1), T is the total chlorophyll (mg g-1 fresh weight), P is the pH of foliage extract, and R is the relative water content of leaf (%)
Plants with higher APTI are recommended for the development of vertical gardens
Ficus benghalensis is the most tolerant tree species to air pollution
The presence or absence of certain taxa or groups of organisms can be used to evaluate the level of pollution or human disturbance of a stream
The LPI (Leachate Pollution Index) is split into three sub-indices to provide better insight into the strength of various pollutants
Types of Tolerance Physiological adaptation, also known as phenotypic plasticity of an individual
Selection of favorable genotypes
Replacement of sensitive species by tolerant species in a community
Co-tolerance depends on the interaction of toxicants, their modes of action, detoxification mechanisms, and the targeted biological community
Examples of PICT (Pollution-Induced Community Tolerance) Application Bérard et al. (2004) validated the PICT tool by measuring photosynthetic activity for atrazine tolerance on edaphic microalgae
Boivin et al. (2002) studied soil microbial communities in industrial and agricultural contexts

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Calculating the Air Pollution Tolerance Index (APTI) of plants

The Air Pollution Tolerance Index (APTI) is used to assess how tolerant plant species are to air pollution and to identify those that can be useful for pollution removal. APTI is calculated using parameters that are affected by air pollutants, such as ascorbic acid content, total chlorophyll content, relative water content, and the pH of leaf extract.

To calculate the APTI value, four physiological and biochemical parameters—ascorbic acid, relative water content (RWC), pH, and chlorophyll concentration of leaf samples—are integrated. An APTI score of ≤ 11 indicates that the tree species are sensitive to air pollution, while a score of ≥ 17 indicates that they are tolerant.

The APTI of various plant species can be helpful in selecting suitable plants for the development of green spaces in urban and industrial areas. For example, in a study conducted in Lahore, Pakistan, Alstonia scholaris showed the maximum APTI value in residential areas, while Magnifera indica showed the minimum. In roadside areas, Magnifera indica showed the maximum APTI value, while Bougainvillea glabra showed the minimum.

Another study assessed the APTI of four roadside plants in Kathmandu Valley, Nepal: Alstonia scholaris, Nerium oleander, Tabernaemontana coronaria, and Thevetia peruviana. Cinnamomum camphora, one of the nine selected species in the study, showed the highest tolerance to air pollution based on the air pollution tolerance index.

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Calculating the Pollution Tolerance Index of aquatic invertebrates

The Pollution Tolerance Index is a method of evaluating the level of pollution or human disturbance in a stream by analysing the presence or absence of certain taxa or groups of organisms, which are known to be more or less tolerant of polluted conditions. This analysis breaks stream invertebrates into four groups, with Group 1 invertebrates being the most intolerant of pollution and Group 4 invertebrates being the most tolerant.

To calculate the Pollution Tolerance Index of aquatic invertebrates, one must first identify the groups of invertebrates present in the stream. This can be done through sampling methods such as dip netting, kick netting, or sediment sampling. Once a diverse array of invertebrates has been collected, they can be sorted and identified to the lowest taxonomic level possible. This may involve using field guides, taxonomic keys, or even genetic sequencing for difficult-to-identify species.

Each identified invertebrate species is then assigned to one of the four tolerance groups based on their known tolerance to pollution. Group 1 invertebrates are those that are intolerant of pollution and are typically not found in low-quality habitats. These may include stoneflies and mayflies, which are often indicators of a high-quality stream. Group 2 and Group 3 invertebrates have intermediate levels of pollution tolerance, with Group 3 being more tolerant than Group 2. Finally, Group 4 invertebrates are the most tolerant and can survive in streams with high levels of pollution and poor habitat quality.

After assigning each identified invertebrate to one of the four groups, the data can be analysed to calculate the Pollution Tolerance Index for that particular stream. This index value provides an indication of the overall health of the stream and the level of human disturbance it has experienced. A stream with a high Pollution Tolerance Index, dominated by Group 4 invertebrates, suggests a highly polluted environment. In contrast, a stream with a low Pollution Tolerance Index, characterised by Group 1 invertebrates, indicates a relatively pristine and healthy ecosystem.

It is important to note that the Pollution Tolerance Index is just one aspect of assessing stream health and should be used in conjunction with other ecological indicators and water quality parameters for a comprehensive evaluation of aquatic ecosystem health. Additionally, the presence or absence of certain invertebrate groups can also provide insights into specific types of pollutants or disturbances affecting the stream, allowing for more targeted remediation efforts.

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Understanding pollution-induced community tolerance (PICT)

Pollution-induced community tolerance (PICT) is an approach to measuring the response of a community to pollution-induced selective pressures. It is an eco-toxicological tool that can be applied to any ecosystem, and it does not require the use of a representative test organism. PICT can be used to determine if a toxicant has disturbed a community of multiple types of organisms.

Community tolerance can increase in three ways:

  • Physical adaptations or phenotypic plasticity: This involves physiological adaptations, where individuals within a community develop a tolerance to a toxicant.
  • Selection of favourable genotypes: Over time, natural selection can favour the selection of tolerant genotypes over non-tolerant ones, leading to a shift in the population's genome.
  • Replacement of sensitive species by tolerant species: Natural selection can also cause a replacement of less tolerant species with more tolerant ones, altering the community's structure.

PICT has been applied in various contexts, including aquatic systems, soil microbial communities, and agricultural and industrial settings. For example, Tlili et al. (2020) combined PICT bioassays with passive sampling systems to study the effects of wastewater treatment on microbial communities. PICT has also been used to assess metal toxicity in soils and sediments, particularly chromium (Cr) pollution.

While PICT is a valuable tool, it is still considered preliminary. Further studies are needed to integrate PICT with chemical monitoring, controlled laboratory experiments, and modelling approaches to refine our understanding of co-tolerance patterns.

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Assessing the Air Quality Index (AQI)

The Air Quality Index (AQI) is a tool used by the EPA to communicate about outdoor air quality and health. It is an index for reporting air quality that includes six color-coded categories, each corresponding to a range of index values. The higher the AQI value, the greater the level of air pollution and the more serious the health concern.

An AQI value of 50 or below represents good air quality, while an AQI value over 300 represents hazardous air quality. AQI values at or below 100 are generally considered satisfactory, while values above 100 indicate unhealthy air quality, first for certain sensitive groups of people, then for everyone as AQI values increase. For each pollutant, an AQI value of 100 generally corresponds to an ambient air concentration that equals the level of the short-term national ambient air quality standard for protection of public health.

The AQI is calculated using an air pollutant concentration over a specified averaging period, obtained from an air monitor or model. Concentration and time represent the dose of the air pollutant. The function used to convert from air pollutant concentration to AQI varies by pollutant, as air pollutants vary in potency.

The AQI can increase due to an increase in air emissions, such as during rush-hour traffic, an upwind forest fire, or from a lack of dilution of air pollutants. The AQI pays particular attention to people who are sensitive to air pollution, providing them with advice on how to protect their health during air quality levels associated with low, moderate, high, and very high health risks.

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Calculating the Anticipated Performance Index (API)

The Anticipated Performance Index (API) is used to estimate the tolerance of plant species to air pollution. It is calculated using the Air Pollution Tolerance Index (APTI) in combination with several morphological characters of a plant, such as biological and socioeconomic dimensions. The API is particularly useful in selecting plant species that can improve air quality by cleaning up atmospheric pollutants and supporting recreational benefits.

The APTI is calculated using the formula proposed by Singh and Rao (1983) to assess the tolerance or resistance power of plants against environmental air pollution. The formula includes ascorbic acid (mg g−1), total chlorophyll (mg g−1 fresh weight), pH of foliage extract, and relative water content of the leaf (%). The APTI value ranges from sensitive (1-11), intermediate sensitive or tolerant (12-16), and tolerant (≥17).

To calculate the API, the APTI value is considered alongside other parameters of trees, such as biological and socioeconomic dimensions. The biological parameters include plant habit, canopy structure, type of plant, laminar structure, texture, hardiness, and economic value. The socioeconomic dimensions are also considered, although the specific details of these considerations are not readily available.

By combining the APTI value with these additional parameters, the API provides a more comprehensive assessment of a plant's anticipated performance and tolerance to air pollution. This information is valuable for developing green belt strategies and selecting specific tree species for urban heat reduction and air quality improvement.

Frequently asked questions

A Pollution Tolerance Index is a way to measure the response of pollution-induced selective pressures on a community. It is an eco-toxicological tool that can be used to understand community tolerance to pollution.

The Air Pollution Tolerance Index (APTI) is calculated using a formula that takes into account the ascorbic acid content, chlorophyll content, leaf extract pH, and relative water content of leaves.

The formula for APTI is APTI = A + T + P + R, where A is the ascorbic acid (mg g^-1), T is the total chlorophyll (mg g^-1 fresh weight), P is the pH of foliage extract, and R is the relative water content of the leaf (%).

The Pollution Tolerance Index for aquatic ecosystems can be calculated using the PICT (Pollution-Induced Community Tolerance) method, which involves in situ techniques such as passive sampling and bioassays on river biofilms.

APTI values can be categorised as sensitive (1-11), intermediately sensitive or tolerant (12-16), and tolerant (≥17). Plants with higher APTI values are more tolerant of air pollution.

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