Unit of competency Outline
Date retreived
23/07/2026 12:13 AM AWST
23/07/2026 12:13 AM AWST
Whilst all efforts are made to provide accurate and timely information from the relevant source/documentation, please be aware that the information supplied may not be the most current version. The accuracy of the detail has not been confirmed by the Department and therefore should not be relied upon without first confirming the contents.
Investigate and plan the optimisation of anaerobic treatment processes
Investigate and plan the optimisation of anaerobic treatment processes
Unit of competency
National Code
NWP413A
NWP413A
State Code
D4825
D4825
TGA Status
Replaced
Replaced
DTWD Status
Replaced
Replaced
State Implementation and Classification
Approved Date
02/06/2011
Field of Education
030907 - Water And Sanitary Engineering
Original Release Date
02/06/2011
Nominal Hours
60
Description
This unit of competency describes the outcomes required to evaluate system performance and investigate and report on optimisation of anaerobic bioreactor processes.
Notes
Elements and Performance Criteria
1Evaluate anaerobic treatment process performance.
- 1.1 Review existing process performance data against relevant organisational or legislative requirements.
- 1.2 Review existing operational processes with reference to manufacturers and plant designers' specifications.
- 1.3 Identify the impact of incoming feed quality on anaerobic treatment processes as required.
- 1.4 Identify and coordinate any additional sampling and testing required for valid evaluation of current process performance
2Investigate anaerobic treatment plant configuration.
- 2.1 Review existing fault reports and other relevant plant asset information.
- 2.2 Investigate the operational status of plant components with reference to manufacturers' or plant designers' specifications.
3Investigate the operational options for process optimisation.
- 3.1 Review relevant fault and incident reports and remedial actions taken.
- 3.2 Investigate potential changes to operational processes to identify possible optimisation strategies.
4Develop and record a plan for process optimisation.
- 4.1 Determine plant configuration and revised operational processes for process optimisation.
- 4.2 Plan a trial to test the performance of the determined optimisation options.
- 4.3 Compile a report making recommendations on optimisation options.
The range statement relates to the unit of competency as a whole. It allows for different work environments and situations that may affect performance. Bold italicised wording, if used in the performance criteria, is detailed below. Essential operating conditions that may be present with training and assessment (depending on the work situation, needs of the candidate, accessibility of the item, and local industry and regional contexts) may also be included.
Organisational or legislative requirements may include:
organisational performance standards
standard operating procedures
quality assurance
federal, state and local environmental and water quality legislation
Processes may include:
upflow anaerobic sludge blanket reactors (UASB)
fluidised bed reactors
anaerobic digesters
high rate anaerobic lagoons (HRAL)
bulk volume fermenters (BVF)
Manufacturers' and plant designers' specifications may include:
organic loading rate
solids retention time
hydraulic loading rate
temperature
mixing strategy
volatile solids reduction
recycle flow rates
detention time
chemical oxygen demand (COD) removal
volatile fatty acids to alkalinity ratio
intended plant configuration
Incoming feed quality may include:
chemical oxygen demand (COD)
nutrients
pH and alkalinity
total and suspended solids
salt
inhibitory compounds, such as hydrogen sulphide or ammonia
temperature
Testing may include:
chemical oxygen demand (COD)
temperature
macro nutrients, such as nitrogen or phosphorus
micro nutrients, such as cobalt or iron
settling tests
pH
redox potential
volatile fatty acids
alkalinity
gas analysis
solids
Plant components may include:
valves
recycle pumps
mixers
covers
inlet distribution network
gas venting and extraction system
chemical and nutrient dosing equipment
solids removal launders
sampling ports
Potential changes to operational processes may include:
recirculation rates
addition of nutrients
temperature
pre-treatment to remove inhibitory or toxic substances
alkalinity and pH correction
flow or feed rate
mixing rate
sludge wastage rate
Organisational or legislative requirements may include:
organisational performance standards
standard operating procedures
quality assurance
federal, state and local environmental and water quality legislation
Processes may include:
upflow anaerobic sludge blanket reactors (UASB)
fluidised bed reactors
anaerobic digesters
high rate anaerobic lagoons (HRAL)
bulk volume fermenters (BVF)
Manufacturers' and plant designers' specifications may include:
organic loading rate
solids retention time
hydraulic loading rate
temperature
mixing strategy
volatile solids reduction
recycle flow rates
detention time
chemical oxygen demand (COD) removal
volatile fatty acids to alkalinity ratio
intended plant configuration
Incoming feed quality may include:
chemical oxygen demand (COD)
nutrients
pH and alkalinity
total and suspended solids
salt
inhibitory compounds, such as hydrogen sulphide or ammonia
temperature
Testing may include:
chemical oxygen demand (COD)
temperature
macro nutrients, such as nitrogen or phosphorus
micro nutrients, such as cobalt or iron
settling tests
pH
redox potential
volatile fatty acids
alkalinity
gas analysis
solids
Plant components may include:
valves
recycle pumps
mixers
covers
inlet distribution network
gas venting and extraction system
chemical and nutrient dosing equipment
solids removal launders
sampling ports
Potential changes to operational processes may include:
recirculation rates
addition of nutrients
temperature
pre-treatment to remove inhibitory or toxic substances
alkalinity and pH correction
flow or feed rate
mixing rate
sludge wastage rate
The evidence guide provides advice on assessment and must be read in conjunction with the performance criteria, required skills and knowledge, range statement and the Assessment Guidelines for the Training Package.
Critical aspects for assessment and evidence required to demonstrate competency in this unit
The candidate should demonstrate the ability to evaluate system performance and investigate and report on optimisation of anaerobic bioreactor processes including:
reviewing existing anaerobic treatment process performance with reference to historical data, differences in feed water quality and plant configuration
identifying data deficiencies and organising additional data collection through appropriate sampling and testing
assessing fault reports and investigating the current operational status of anaerobic treatment process plant components
investigating current and potential chemical addition practices
planning trials to test the performance of the determined anaerobic treatment process optimisation options
preparing reports with recommendations
Context of and specific resources for assessment
Access to the workplace and resources, including:
documentation that should normally be available in a water industry organisation
relevant codes, standards and government regulations
Where applicable, physical resources should include equipment modified for people with disabilities.
Access must be provided to appropriate learning and assessment support when required.
Assessment processes and techniques must be culturally appropriate, and appropriate to the language and literacy capacity of the candidate and the work being performed.
Validity and sufficiency of evidence requires that:
competency will need to be demonstrated over a period of time reflecting the scope of the role and the practical requirements of the workplace
where the assessment is part of a structured learning experience the evidence collected must relate to a number of performances assessed at different points in time and separated by further learning and practice
a decision of competence only taken at the point when the assessor has complete confidence in the person's competence over time and in various contexts
all assessment that is part of a structured learning experience must include a combination of direct, indirect and supplementary evidence
where assessment is for the purpose of recognition (RCC/RPL), the evidence provided will need to be authenticated and show that it represents competency demonstrated over a period of time
assessment can be through simulated project-based activity and must include evidence relating to each of the elements in this unit
In all cases where practical assessment is used it will be combined with targeted questioning to assess the underpinning knowledge. Questioning will be undertaken in a manner appropriate to the skill levels of the operator and cultural issues that may affect responses to the questions, and will reflect the requirements of the competency and the work being performed.
Critical aspects for assessment and evidence required to demonstrate competency in this unit
The candidate should demonstrate the ability to evaluate system performance and investigate and report on optimisation of anaerobic bioreactor processes including:
reviewing existing anaerobic treatment process performance with reference to historical data, differences in feed water quality and plant configuration
identifying data deficiencies and organising additional data collection through appropriate sampling and testing
assessing fault reports and investigating the current operational status of anaerobic treatment process plant components
investigating current and potential chemical addition practices
planning trials to test the performance of the determined anaerobic treatment process optimisation options
preparing reports with recommendations
Context of and specific resources for assessment
Access to the workplace and resources, including:
documentation that should normally be available in a water industry organisation
relevant codes, standards and government regulations
Where applicable, physical resources should include equipment modified for people with disabilities.
Access must be provided to appropriate learning and assessment support when required.
Assessment processes and techniques must be culturally appropriate, and appropriate to the language and literacy capacity of the candidate and the work being performed.
Validity and sufficiency of evidence requires that:
competency will need to be demonstrated over a period of time reflecting the scope of the role and the practical requirements of the workplace
where the assessment is part of a structured learning experience the evidence collected must relate to a number of performances assessed at different points in time and separated by further learning and practice
a decision of competence only taken at the point when the assessor has complete confidence in the person's competence over time and in various contexts
all assessment that is part of a structured learning experience must include a combination of direct, indirect and supplementary evidence
where assessment is for the purpose of recognition (RCC/RPL), the evidence provided will need to be authenticated and show that it represents competency demonstrated over a period of time
assessment can be through simulated project-based activity and must include evidence relating to each of the elements in this unit
In all cases where practical assessment is used it will be combined with targeted questioning to assess the underpinning knowledge. Questioning will be undertaken in a manner appropriate to the skill levels of the operator and cultural issues that may affect responses to the questions, and will reflect the requirements of the competency and the work being performed.
Replaced By
| State Code | National Code | Title | Type |
|---|---|---|---|
| AVX90 | NWPTRT093 | Assess and improve anaerobic digestion processes | Unit of competency |
| State Code | National Code | Title | Type |
|---|---|---|---|
| D246 | NWP40107 | Certificate IV in Water Operations | Qualification |