EIA Flashcards
Define ‘Life Cycle Assessment’ (LCA)
Life Cycle Assessment is an objective process to evaluate the environmental burdens associated with a product, process or activity, by identifying energy and materials used and wastes released to the environment, and to evaluate and implement opportunities to affect environmental improvements.
(SETAC, 1990)
What are the key objectives of LCA?
- Identify and quantify the environmental loads involved - e.g. the energy and raw materials consumed, the emissions and wastes generated
- System-wide examination (whole cycle)
- Multi-media approach (air, water, solid waste)
- Evaluate the potential environmental impacts of those loads (e.g. the car tyre)
- Assess the options available for reducing these environmental impacts
- Identify trade-offs among alternatives
- Identify opportunities to improve systems
- Done in high-impact areas first
- Support environmental decision making
- (e.g. right now gas is almost as cheap as coal, so we should invest more in gas to maybe kill coal industry)
What is meant by the term ‘product system’ in the context of LCA?
A product system is defined by ISO as a ‘collection of materially and energetically connected unit processes, which perform one or more defined functions.’
(ISO 14040, 2006)
What is meant by the term ‘system boundary’ in the context of LCA?
A system boundary establishes a specific set of criteria designating which unit processes are part of the product system.
(ISO 14040, 2006)
What is meant by the term ‘elementary flows’ (which includes both inputs and outputs) in the context of LCA?
Elementary flow is split into both inputs and outputs: inputs are the raw material or energy taken from the environment entering the product system; and outputs are the material or energy leaving the system that are released into the environment.
(ISO 14040, 2006)
Why is it important to consider the inter-linkages between resources and their life cycles?
The energy security, water security and food security sectors are harmoniously linked with one another, in that actions that take place in one sector will most likely directly impact upon one or the two other sectors also.
What is meant by the analysis of the Energy, Water and Food (EWF) Nexus and how it is implemented?
Analysis of the EWF Nexus includes the identification, integration and evaluation of linkages related to the inputs, outputs and environmental impacts of a product process operating within governed system boundaries across the energy, water and food sub-systems throughout their life cycle
Draw a schematic representing the EWF nexus in the context of LCA.
What are the LCA phases?
- Goal and scope definition (5-10%)
- Inventory analysis (70%)
- Impact assessment (10%)
- Interpretation (10%)
- Development and improvement
- Strategic planning
- etc.
What is involved in ‘Goal Definition’, in the Goal and Scope Definition LCA phase?
Goal definition:
- identify the decision context (e.g. CO2 emmissions from coal fired power plant),
- intended application (product development and improvement, strategic planning, public decision making, marketing, other, (e.g. reduce CO2 emmissions by x% by 20XX)
- identify the audience. (present information appropriately to the public etc.)
What is involved in ‘Scope Definition’, in the Goal and Scope Definition LCA phase?
- Describe the system to be studied, the functions of the system, the functional basis for comparison and the required level of detail.
- Comparison on the basis of an equivalent function (1000 liters of milk packed in glass, plastic bottles or packed in carton, instead of 1 glass bottle versus 1 carton)
- Define:
- the life stages to be covered,
- the impacts to be investigated,
- the impact assessment methods to be applied,
- the interpretation methods to be used,
- the assumptions made about data and method issues,
- value choices, limitations, data quality requirements,
- type of critical review and
- format of the report required.
In LCA, what is a cutoff?
An impact not under consideration because it’s effect is very small (e.g. <1.5% of overall)
What is the Inventory Analysis LCA phase?
Inventory Analysis is the LCA phase involving the compilation and quantification of inputs (e.g. raw materials and energy) and outputs (e.g. wastes and emissions) for a given product system throughout its life cycle.
Steps:
– preparing for data collection
– data compilation
– calculation procedures
– allocation and recycling
What happens in the Impact Assessment phase of an LCA?
- Life Cycle Impact Assessment is the 3rd phase of LCA
- The effects of the resource use and emissions generated are grouped and quantified into a limited number of selected and defined baseline impact categories which may then be weighted for importance
- Additional selection and definition of indicators and models
- Classification
- Characterisation (model convert to equivalent terms)
- Normlisation to e.g. EU standards i.e. make additive e.g. GWP (kg/CO2 eq.) (EU standards different to African standards, for e.g. eco toxisity valued less in African)
- Aggregation and/or weighing
- In the evaluation phase the normalized effect scores are multiplied by a weighing factor representing the relative importance of the effect.
What happens in the Interpretation phase of an LCA?
- Results interpreted and reported in the most informative way possible.
- The need and opportunities to reduce the impact of the product(s) or service(s) on the environment are systematically evaluated based on the data.
- Includes quality, completeness, sensitivity and consistency analysis/checks
- Address the uncertainty and accuracy of the results.
- Conclusions are drawn
- Highlight limitations
- Recommendations are derived.
- All relate to the goal and scope of the research
- Should include a review by independent experts
What is a functional unit?
A functional unit is a quantified description of the performance of the product systems, which is used as a reference unit
What does gate-to-gate, cradle-to-gate, and cradle-to-grave mean in the context of LCA?
They are each a type of LCA
- Gate-to-gate: Considers production of good only (e.g. takes place just at plant)
- Cradle-to-gate: Raw materials to finished good (no use or end life considerations)
- e.g. build coal power station close to coal source to save on transport
- Cradle-to-grave: Considers everything from harvesting materials to the disposal of the finished goods and wastes (landfill or recycled), and the life-time of the infrastructure (demolition?)
What are the system boundaries, typically?
- Natural resource aquisition
- Materials production
- Intermediate products manufacturing
- Assembly manufacturing
- Use
- End-of-life
What is a reference flow?
A quantified amount of product(s), including product parts, necessary for a specific product system to deliver the performance described by the functional unit
In LCA, what are some environmental interventions and economic flows?
In Life Cycle Inventory Analysis (phase 2), what calculation procedures need to be done?
- relate process data to the functional unit (matrix algebra)
- allocation of multiple processes (multiple outputs, multiple inputs, re-use and recycling)
- e.g. coal power plant
- fly ash: utilized in road construction, and used to stabalize heavy soil; contains heavy metals
- once coal power plant closes down need to find new ways to produce gypsum
- Particulate matter potent
- aggregation over all unit processes in the inventory table
List the possible baseline impact categories present in a LCIA.
- Depletion of abiotic resources
- e.g. fuel consumption, coal, copper, natural gas
- Impact of land use
- Climate change
- Human toxicity
- Ecotoxicity (diff. animals in diff. env - diff. comparison)
- freshwater aquatic ecotoxicity
- marine aquatic ecotoxicity
- terrestrial ecotoxicity
- Photo-oxidant formation
- photooxidation from NOx from exhaust fumes
- Acidification
- SOx, NOx
- Eutrophication
- fertilizers e.g. nitrates, phosphates
Results still difficult to understand due to differences in scale and units e.g. local toxicity vs global climate change
During LCIM, normalization does what?
Normalisation relates the results to a reference value, for example, total world impacts in 2002. Result is often referred to as the normalised environmental profile.
But even after normalisation, there is no clear answer:
- aggregation of (normalised) impact category results into a single index
- subjective weighting factors increase the priority given to impactcategories we think are important, and decrease the priority given to those we think are unimportant
In order to gain a better understanding of the relative size of an effect, a normalization step is required. Each effect calculated for the life cycle of a product is benchmarked against the known total effect for this class.
- Normalization enables you to see the relative contribution from the material production to each already existing effect.
- Normalization considerably improves our insight into the results. However, no final judgement can be made as not all effects are considered to be of equal importance.
How do impact categories relate to damage categories?
If all the scores for one product are higher than those for another, it is easy enough to conclude which is the more environmentally friendly. But if one has a higher score for acidification, while the other has a higher score for the greenhouse effect it becomes difficult to justify such a conclusion.
Interpretation depends on what two factors:
- The relative size of the effect compared to the size of the other effects. It is important to see whether a seemingly arbitrary score of say 100% refers to a very high or an extremely low effect level. This is normalisation.
- The relative importance attached to the various environmental effects. This is evaluation.
Environmental impact monitoring aims at determining what?
Determining the occurence and magnitude of an impact. It is also important to establish that the perceived change is a consequence of the project under consideration and not the function of some other cause.
The changes might result, for example, from natural variations in the parameter monitored or may be the result of some other development in the vicinity and, thus, not related to the projet under consideration.
What are ‘reference monitoring locations’?
During environmental impact monitoring, it is common practice to use reference monitoring locations in order to ensure that an impact is assigned correctly to a project. The reference locations are selected in areas similar to the treatment (impact monitoring) locations where the impacts are not expected to occur.
For example, a number of river quality monitoring stations may be put downstream of an industrial effluent discharge point, together with reference stations upstream and downstream of the same river and its tributaries.
There are several techniques of gathering and monitoring environmental data. The basic techniques
include:
o Grab sampling techniques with periodic data analysis
o Automated sampling techniques with periodic data analysis
o Automated continuous monitoring and data analysis
o Biological monitoring systems
What are the disadvantages of using traditional monitoring techniques?
What is the advantage of using continuous monitoring techniques over these traditional monitoring techniques?
- Traditional monitoring techniques involving periodic sampling are often used in industry to monitor environmental variables.
- These methods have the disadvantage that by the time these samples are analysed the impact of the pollutant on the environment can have already occurred.
- Furthermore, with this type of sampling all but the most rudimentary (i.e. undeveloped/basic) process control techniques are impossible to use.
- Recent improvements in the continuous monitoring technology can allow certain environmental
attributes to be monitored continuously in real time, thus allowing a control system to be established
Planning permissions for the operation of mining licenses often require, environmental monitoring and sampling of particular environmental variables at what frequencies
frequencies far beyond those which could be achieved by none automated methods.
However, most environmental data collection techniques are, for the most part, not automated.
The manual or semi computerised analysis of large volumes of data of the different environmental variables in different systems does not facilitate the accurate collation of the data or allow for the introduction of an automated control system.
What are grab sampling techniques usually used for?
Simple data gathering techniques such as grab sampling are often used for the evaluation of water quality, soil quality and gaseous emissions. These methods have the disadvantage that by the time these samples are analysed the impact of the pollutant on the environment could have already occurred. This has a particular importance in sensitive areas such as effluent discharge into rivers or ground water control in and around tailings dams.
Briefly describe what continuous monitoring means.
The more sophisticated approach is that of continuous monitoring of the environment. A precise definition of continuous monitoring is rather difficult due to a number of different implementations.
Generally the term ‘Continuous’ is applied to all monitoring instrumentation that has the ability to repeatedly monitor one or more attributes at a regular interval.
The frequency of the measurement may be defined by the user, or by the physical limits of the monitor.
Some types of environmental data are not suitable to be continuously monitored, nor would the continuous monitoring of these parameters be useful. Give examples.
An example of this would be a study of soil contamination, in which samples would be taken at regular intervals in time to study the cumulative effects.
Other examples would include biological surveys which would be virtually impossible to automate and the day to day results would not yield useful information.
Give exclusive examples of typical continuously monitored environmental variables
- River water quality
- Flow rate
- Water quality at ground water wells
- Chemical content
- Noise
- Leq, Lmax, Ln, L10
-
Air quality
- Ambient dust,
- gaseous emissions
- Meteorology
- Wind direction,
- wind v,
- rainfall,
- T,
- humidity
- sunshine hours
Give examples of typical periodically monitored environmental variables
- Soil quality
- metals
- nitrates, sulphides
- Org content
- pH
- Soil herbage
- bio-diversity, bio-population
- metal cont.
- Water quality
- BOD, COD
- Biological surveys
- bio-diversity, bio-population
- metals
- general condition
- Air quality
- Dust deposition
- composition
What are the potential impacts associated with mining?
- Acid Mine Drainage Formation (open cast)
- Erosion and Sedimentation
- Chemical Releases – Cyanide (used at Tara) & other
- Air emissions/air quality
- Stacks for drying product in place for ~25 years before being put out of use (Tara)
- Fugitive dust emissions (e.g. off road or tailings pond)
- Ventilation raises that pump not-so-fresh air out of mine to surface
- Habitat modification
- Surface water pollution
- Groundwater pollution
- Noise
- Complaints
- Ground vibration
- Blast vibration twice a day
- Development blasting in morning / production blasting in evening
- Biggest source of complaint
- Tailings pond failure (disaster)
- slurry-soild water mixture flows into nearby valleys
What is the main disadvantage of using non-automated environmental collection techniques?
The manual or semi-computerised
analysis of large volumes of data of the different environmental variables in different systems does not facilitate the accurate collation of the data or allow for the introduction of an automated control system.
Planning permissions for the operation of mining licenses often require, environmental monitoring and sampling of particular environmental variables at frequencies far beyond those which could be achieved by none automated methods.
What are the advantages of using continuous monitoring systems?
- Continuous Data in Time
- Instantaneous data
- Remedial action/closed circuit control possible
- Sampling error is minimised
- Less labour required
- A large amount of data
What are the disadvantages of using continuous monitoring systems?
- Complex to install, maintain and operate
- Difficult to tailor a suitable ‘Customised’ system
- Calibration has to be carried out at regular intervals
- System is only as accurate as instrument
- Skilled labour required
- A large amount of data to process
- Initial capital cost
- Not suitable for all environmental attributes
Give an example of a particular type of environmental data that is not suitable to be continuously monitored and why.
The study of soil contamination, or bio-diveristy in animal health studies, in which samples would be taken at regular intervals in time to study the cumulative effects.
The continuous monitoring of these parameters are not useful as the day to day results would not yield useful information.
What are the potential sources of air pollution at the Tara Mine site?
- There are 4 air extraction stacks associated with the minerals processing plant (or Mill):
- These stacks are the crusher, the lead loadout, the zinc loadout and the zinc dryer
- Ventillation raises
- Dry tailings
- Roads
The air quality impacts from minerals extraction (primary extraction of minerals + on-site processing) sources occur at what scale?
The air quality impacts from these sourcs occur at what is defined as a local scale in air quality modelling, primarily distances up to 10km.
Air pollutants at this scale are contained within what is termed the boundary layer of the atmosphere.
What are the five factors that define the air pollution caused by minerals extraction?
- The spatial extent of the source. This can be of 3 types over 3 dimensions: point, line and area.
- The temporal extent or duration of the source. A source of air pollution may be instantaneous or occur over a period of time, or intermittently over a period of time.
- The type of air pollutant released. Primarily particulates, mainly in the form of dust.
- The effect of air pollution on the recipient.
- Minerals extraction is also likely to occur in or result in complex or highly varying surface topography. This can have a considerable influence on the dispersion of an air pollutant.
What are some of the typical sources of air pollution from minerals extraction activities (including processing of minerals)
- Point
- Ventillation outlets
- Processing plants
- Drilling
- Line
- Truck haulage routes (can be treated as point sources over small temporal scale)
- Area
- Tailings dams
- Spoil heaps
- Storage areas
Blasting operations are temporally classified as what?
- Classified depending on the time scale of interest
- On a small time scale, say daily, blasting operations will be instantaneous sources of pollution.
- On larger time scales, say over a year, they could be considered as continuous sources of air pollution.
What is the Planetary Boundary Layer?
The part of the atmosphere directly influenced by the Earth’s surface.
The process of entrainment does what to pollutants?
Traps pollutants within the boundary layer.
Objective measurements of sound levels are an indispensable part of any environmental noise
protection program. Environmental noise levels vary greatly – noise is often impulsive or contains
pure tones.
Assessing a fluctuating noise level means getting what?
a value for a level that is, in simple terms, the
average level.
The “equivalent continuous sound level”, the Leq is known across the globe as the essential averaged parameter.
What is Leq, and how is it measured?
Leq is a measure of the averaged energy in a varying sound level.
It is not a direct measure of annoyance. Extensive research, however, has shown the Leq to correlate well with annoyance. It is obvious, though, that a noise level acceptable on a Wednesday afternoon may be distressing early on Sunday. Corrections for time of day may, therefore, be applied.
The Leq is measured directly with an integrating sound level meter (SLM)
An analysis of the statistical distributions of sound levels is a useful tool when assessing noise.
Why?
The analysis not only provides useful information about the variability of noise levels, but is also prominent in many standards as the basis for assessing background noise.
For example, L90, the level exceeded for 90% of the measurement time, is used as an indicator of background noise levels while L10 or L5 are sometimes used to indicate the level of noise events.
What are the different kinds of SLMs?
- A number of different types of noise measurement equipment are commercially available with various levels of sophistication.
- The range includes instruments that are capable of:
- measuring basic time varying sound pressure level
- calculating statistical noise indices over time.
Integrating or integrating averaging sound level meters will measure what?
the ‘A’-weighted equivalent sound level, LAeq.
Statistical sound level meters will calculate what?
the statistical noise measurement parameters such as LA90, LA10, LAmin, LAmax as well as the LAeq.
Environmental noise measurement using sound level meters, microphones and calibrators by both the Operator and the Regulator of have to comply with what?
a range of national and international standards
e.g. ISO standard in UK
What’s the difference between basic and more advanced SLM instruments?
- Basic instruments may need to be manually interrogated and the results read off and recorded manually.
- More sophisticated models may be equipped with a noise logging facility. This will allow the meter to be set up to take one sample over a pre-defined period, store the result in its memory, start another measurement, and repeat the process continuously.
- All meters are able to able to measure in terms of dB(A) noise levels, this being the most commonly used scale for environmental noise assessment.
Modern sound level meters usually have a wide dynamic range of around 80dB and can measure peak levels of over 140dB. And the measurement scales go down as low as 20dB(A).
What does this range allow for?
And what is the disadvantage of measuring as low as 20dB?
The range means that they can measure background (LA90) levels of say, 30 dB and still capture LAmax, levels of over 100 dB.
Some meters at low levels produce electrical noise and when combined with thermal noise from some microphones, can start to influence the results, so in practice any level measured below 25dB(A) should be viewed with caution.
What is it common to prescribe to the Equivalent continuous sound level, Leq?
- Because the Leq is defined as the steady sound level that contains the same amount of acoustic energy as the fluctuating level over the prescribed time.
- It is common to prescribe periods of:
- 1 hour (L1h),
- 24 hour (L24h),
- the day time hours from 7:00 a.m. to 7:00 p.m. (Lday), and
- the night time hours from 11:00 p.m. to 7:00 a.m. (Lnight).
What is Day average sound level, Lday?
The equivalent continuous sound level in decibel determined over all the day periods of a year (the 12 hour time period from 07:00 to 19:00) is called day average sound level
What is Evening average sound level, Levening?
The equivalent continuous sound level in decibel determined over all the evening periods of a year (the 4 hour time period from 19:00 to 23:00) is called evening average sound level.
What is Night average sound level, Lnight?
The equivalent continuous sound level in decibel determined over all the night periods of a year (the 8 hour time period from 23:00 to 07:00) is called night average sound level.
What is Day-evening-night average sound level, Lden and how is it calculated?
Lden is a long-term noise annoyance indicator recommended for use in strategic noise mapping by the Environmental Noise Directive 2002/49/EC.
Levening and Lnight have a 5 and 10 dB weighting applied to each respectively to take account of the difference in annoyance due to the time of day.
What is Day-night average sound level, Ldn?
This is an average sound level taken over a 24-hour period, modified to account for the increased undesirable effect of noise at night.
10 dB is added to the actual sound level for the hours from 23:00 to 07:00. before the 24-hour energy average is taken.
What is Maximum A-weighted sound level, LAmax?
The highest sound level measured on a sound level meter, during a designated time interval or event, using fast time-averaging and A-weighting is defined as maximum A-weighted sound level.
Why are noise levels rarely constant?
What are the exceptions to this?
- because the overall sound pressure is usually the result of numerous different sources of noise, each of which may be varying in strength from one instant to the next.
- Exceptions tend to be when one particularly constant source is very loud compared to the rest (e.g. close to an extract fan in a factory wall) or when all noise sources are at large distances from the receiver (e.g. in the bedroom of a remote house at night).
- Therefore it is usual to quantify a noise level over a specified period of time.
Describe what “Percentile Parameters” used in characterising environmental noise are.
- The Ln value is the noise level exceeded for n% of the measurement period, which must be stated.
- The Ln value can be any value above 0 and up to 100.
- The time period of the measurement should be specified and it should be long enough to obtain a representative sample of the background level.
- E.g. LA90, LA10, LA50
- LA90 is the lowest statistical reading, and that the LA10 is higher and the LA50 lies between them.
Describe LA90.
- The most commonly used percentile level is the LA90 which is the 90th percentile level and is level exceeded for 90% of the measurement time.
- It will be above the Lmin and has been adopted as a good indicator of the “background” noise level.
- Whilst it is not the absolute lowest level measured in any of the short samples, it gives a clear indication of the underlying noise level, or the level that is almost always there in between intermittent noisy events.
Describe LA10.
- LA10 is the tenth percentile, or the level exceeded for 10% of the time, and was often used for road traffic noise assessments since it had been shown to give a good indication of people’s subjective response to road traffic noise.
- Although the LAeq has been largely superseded its use for road traffic, it may still be found in acoustic reports discussing road traffic noise and is used to assess road traffic noise where a noisy road is being planned.
- The LA10 can be useful in assessing the overall noise climate, for example if the LA90 LA10 LAeq are all within a few dB then this can be taken as an indication that the noise source is fairly constant.
What is the objective of Environmental Impact Assessment (EIA)?
- The objective of EIA is not to force decision makers to adopt the least environmentally damaging alternative. If this were the case, few developments would take place.
- Environmental impact is but one of the issues addressed by decision makers as they seek to balance the often competing demands of development and environmental protection.
- Social and economic factors may be far more pressing.
- As decision makers may be dealing with a disparate range of information on which to base a decision, integration has been a recurrent problem.
- Economic and environmental analyses, for example, tend to be treated seperately. In fact, they are closely interrelated.
Define ‘environmental impact’
A projected change in the value of one or more measures of environmental quality resulting from an action, compared with the condition of the environment had that action not taken place.
An impact can have both spatial and temporal effects and is hence, four dimensional.
An impact can also be direct (primary) or indirect (secondary, tertiary, etc.).
What are the stages of EIA?
- Impact identification
- Forecasting of impacts
- Evaluation of impacts
- Communication of results
List the main criteria used in choosing a suitable environmental impact assessment method for a development project.
- Is the method comprehensive?
- Is the method selective?
- Is the method mutually exclusive?
- Does the method yield estimates of the confidence limits to be assigned to the predictions?
- Is the method objective?
- Does the method predict interactions?