SECBE Home
Contact SECBE

Data Collection

The complexity of both the construction and demolition process is dependent upon the particular project.  Factors, including site characteristics, geographical location and building type will determine the mechanics of the process and the composition of the likely C&D waste streams. 

Despite the variety and complexity of individual projects, this report has considered generic construction and demolition cycles.  Although it is acknowledged that both the construction and demolition processes are often integrated, with demolition taking place before construction, for the purpose of clarity, we have considered both the construction and demolition process as distinct processes. 

The figures below illustrate a generic demolition cycle, consisting of internal strip out, roof, walls, foundations and then site finish, and a generic construction cycle consisting of site investigation/ground work and site preparation, foundations, frame, envelopes (walls and roof), and internal fit out.  

Research into Cultural/Behavioural and Mechanical Barriers to Data Collection 

The South East Centre for the Built Environment (SECBE), in partnership with the South East England Development Agency (SEEDA), as part of the BREW Programme (2006/07) commissioned Temple Group Ltd (Temple) to research the cultural/behavioural and mechanical barriers to waste data collection.

The objective of this report was to progress an understanding of those significant cultural/behavioural and mechanical barriers to waste data collection, critical to the development and the adoption of more sustainable waste management practices in the construction sector. 

Our research methodology included data reviews, telephone interviews, site visits and desktop research into waste management practices in the UK and internationally.   Key findings of our research included:

This report also provides a set of recommendations to ensure those identified cultural/behavioural and mechanical barriers are successfully overcome. These included: 

Barriers to waste data collection

Construction and Demolition Process Waste Overview
The complexity of both the construction and demolition process is dependent upon the particular project.  Factors, including site characteristics, geographical location and building type will determine the mechanics of the process and the composition of the likely C&D waste streams. 

Despite the variety and complexity of individual projects, this report has considered generic construction and demolition cycles.  Although it is acknowledged that both the construction and demolition processes are often integrated, with demolition taking place before construction, for the purpose of clarity, we have considered both the construction and demolition process as distinct processes. 

The figures below illustrate a generic demolition cycle, consisting of internal strip out, roof, walls, foundations and then site finish, and a generic construction cycle consisting of site investigation/ground work and site preparation, foundations, frame, envelopes (walls and roof), and internal fit out.  

 

Demolition Cycle

 

 

 

Construction Cycle

 

Construction and Demolition waste management requires a great deal of coordination and expertise amongst key stakeholders.  Whilst the above processes (cycles) may appear simple, it is important to remember that in order to effect waste minimisation within this context, a large number of stakeholders need to be involved and to "own" or at least contribute to the effectiveness of the system. 

The contractor needs to have the experience and expertise to be able to act as the "hub of the wheel" to achieve waste reduction through the supply chain and in ensuring effective construction site waste management systems are in place.  The collection of accurate data, the monitoring of system performance and the communication of such results is of critical importance in managing a complex and interdependent system.

To effect change and savings, it is important to understand where the savings can be most efficiently achieved.  It has been shown that approximately 70%[1] of the opportunity for waste minimisation is within the design phase.  The remaining 30% is found within the operational phase - the construction site.  Of this 30% there are two key phases of the construction process that offer the greatest opportunity for waste minimisation and reduction which are the construction of the roof and the internal "fit out".

Therefore in attempting to develop an effective real time data system it is important to understand in holistic terms all the elements from the design phase through to construction and fit-out and the critical support systems such as supply chain management, on-site operational and technical constraints and site waste management.

This report will consider such factors in reviewing the SECBE RTDS pilot and in our recommendations for RTDS process improvements.

Research Methodology

Research Methods - Telephone Interviews, Site Visits and Data Review
A number of telephone interviews were conducted with those individuals with responsibility for either the promotion of improved site waste management or site waste management.

Other interviews were conducted with Kier Partnership Homes.  Site visits to several Wolseley sites (a leading supplier of building materials and services) and Wolsely client sites to understand at first hand, at a site level potential barriers to effective management construction and demolition waste.

The key comments are provided below and have been grouped under respective headings of cultural/behavioural and mechanical barriers.  It is important to note that although some of the issues raised during our research were quiet specific to the adoption of the BRE SMARTStart tool, many are general comments that would apply to other similar waste auditing tools.

A desktop study was also carried out to identify general industry cultural/behavioural and mechanical barriers to efficient waste data collection.  This involved desktop research into best practice in Canada, the USA, New Zealand, Australia and Europe and followed up with telephone interviews with key waste management professional known to members of the project team.

 

Findings - Telephone Interviews and Site Visits

Cultural/Behavioural Factors
A key issue is that the contractors do not see the waste as their issue or problem, they are hired to say install 40m of skirting and are given the materials to work with and have therefore no ownership of the issue. Therefore key is how materials are paid for and could a change to this help create ownership and therefore better management.

Mechanical Factors

 

General Comments

General Industry Research
As of April 2007, there does not appear to be a directly comparable waste data collection system in operation anywhere else in the developed world.  Targeted research was undertaken in Canada, the USA, New Zealand, Australia and Europe, to identify similar systems.  Two reasons why such a waste data collection system may have not as yet been developed are that there is the possibility, although unlikely, that such an initiative/system has not been thought of and that such initiatives may have been considered less important than other waste management matters.  Other findings include:


Discussion and key recommendations

Cultural/Behavioural Barriers
Cultural/behavioural barriers have been considered as one in this report, as both these factors are not mutually exclusive.  The general culture will influence people's values, and ultimately behaviour.  Influence can also operate in reverse, where individual behaviour, especially that of recognised leaders, can ultimately influence the cultural context.  

In cultural terms, despite a general increase in awareness of environmental issues and a number of voluntary waste initiatives, the issue of waste still remains an under represented one within the construction industry and to a much lesser degree to the demolition industry.

Whilst there are very hopeful signs of change illustrated by an increase specific regulation directed at the industry (see Section 4) it is almost certain that other factors will need to be considered, particularly cultural/behavioural barriers. Such barriers include:

Modelling Behaviour and Other Cultural/behavioural Factors
A number of different conceptual behavioural models have been used to help understand behaviour within a range of circumstances and environments.  Such conceptual models have also been used in understanding a community's attitude to environmental pollution and can be used in understanding attitudes to waste management.  Such models are useful in a general sense and provide useful rules of thumb or frames of reference to which individuals relate helping to identify appropriate ways forward.

Rational Choice Model
Rational choice model predict that people will act in their own best interests, or the best interest of the environment and industry in general when clear benefits can be identified.  Therefore it is critical that the necessary incentives are put in place (market based initiatives, regulations (See Section 4)) to ensure that the decision framework is adjusted that it will be in the best interest of a construction company to collect accurate and detailed waste data, which is critical to managing waste in a more sustainable manner.  In adopting a rational model approach it is clear that a top down approach would be most effective.  A regulatory framework with fair and balanced incentive and enforcement frameworks, which would include market based initiatives, would be most effective in effecting change.

Attitude Model
Attitude models rest on the assumption that attitudes of individuals and companies influence behaviour.  What the individual's perception of waste management initiatives, including the value of waste data collection is critical in understanding how attitudes and ultimately behaviours will influence attempts to manage waste sustainably. 

We all see things in different ways and have different perceptions or views of how we see the ‘real' world.  People do not generally receive information in a passive manner, automatically accepting it, but analyse and judge what it is being said, who is saying it, in order to decide what is significant and what can be disregarded as worthless. 

Personal expectations will play a key role in influencing that they "hear", and what they want to ‘hear'.  Personal values and perceptions shape the way we react to information in terms of delivery or changes in approach.

Although a top down approach as suggested in the Rational Choice model can be a powerful way to change attitudes, a bottom up approach is likely to be very useful in effecting change in terms of sustainable waste management practices.  Such initiatives would include information sessions, education - tool box talk - case studies illustrating the true savings (and costs) of such initiatives and would also have consideration for the cultural (ethno-lingual) variability's across the construction industry to ensure particular groups are not left out of such initiatives (i.e. because of language barriers).  Moral leadership, at a company level and sectoral level through organisation such as the South East Centre for the Built Environment (SECBE), ReMade and Building Research Establishment (BRE), the National Industrial Symbiosis Programme (NISP), Waste and Resources Awareness Programme (WRAP) and Envirowise , Scottish Waste Awareness Group (SWAG in Scotland) will be critical to instituting change.

Aspects of both the top-down approach (Rational Choice Model) and the bottom-up approach (Attitude Model) will be important in developing an overall approach to a sustainable waste management, including data collection. 

Other Key Recommendations include:

Actions to effect change include:

Mechanical Barriers

The mechanical barriers in the collection of waste data a can be significant.  Such challenges must be overcome if the goal of sustainable construction is to be achieved.  Data is central to the overall process and therefore data must be of a sufficient quality that is also accurate.  Methods and units of measurement must be uniform across sites and it must be clear the end use of such data and how such data will help to contribute to the construction industry becoming more sustainable and self-sufficient.

A mechanical barrier, which is also, indirectly, a cultural/behavioural barrier, is the how waste data is recorded and measured.  As discussed it is important that there is a standardised method for recording waste data.  It is important that the waste categories used in waste check sheets are standardised and sufficiently prescriptive to ensure all waste types are recorded (mechanical barrier).  Although a more detailed categorisation approach will be more time consuming, the information collected is likely to be more accurate, therefore it is much easier for the data collector to see the inherent value in the data and how such data can contribute to a more sustainable waste management practices.  It is critical that data collectors see a purpose in the data collection process, thus ensuring higher levels of participation and motivation (cultural/behavioural barriers).

The information on which the tool relies is of a very low resolution, that is not to say that it is inaccurate, however it can only ever be considered to provide the most basic of guides to the types of waste generated on-site.  There does not appear to be any consistent, approach to training the individuals who undertake the assessment and therefore it is difficult to assess how objective the data is.  It is possible with the current system that an inaccurate assessment of the wastes management performance of the organisation could be presented, due to simple issues such as this.

Inspecting skips can place a significant operational burden on staff and it is important that such burdens are minimised where possible.  Therefore managing by variance a cost effective and time efficient method of collecting data on waste streams generated on-site. 

Another time efficient approach, which would also improve the quality of waste data collected is the segregation of waste on-site into inert, hazardous and timber waste streams.  Such an approach is discussed. Other operation constraints include issues around the double handing of the waste data which is not efficient. 

Real Time Data System
The primary objective of the Real Time Data System (RTDS) would be to minimise waste in the construction process through the accurate collection of waste data.  This data would enable immediate action to be taken on-site, through appropriate on-site feedback mechanisms.  Such data would also be used in designing out waste from the construction process through feedback mechanisms to the design team, procurement and the supply chain. 

A RTDS should be a one-touch approach so that when segregated, weighed or estimated by volume, data is entered in a handheld computer which then can be directly transferred to a central database.  Avoiding double handling of information will avoid mistakes associated with data transfer, incorrect data interpretation and would lessen burdens on staff in terms often time consuming process of data collection, thus reducing potential mechanical and behavioural barriers to waste data collection.

Managing by Variance
Manage by variance - an effective way to accomplish this, is to work with the site operative's expertise and knowledge (Expert Systems) so that they feel what they are doing makes sense and ultimately works.  The approach to this overall system should be to work by variances and allow, over time, for what is considered normal and what is considered a variance to change through time having regard to the particular stage of work improvements achieved, in terms of reduced waste generation.

The logic for such an approach is that only waste that is at variance from the waste that is found in a "normal" skip will be analysed in greater detail.  Normal skips will go straight to sorting and recovery, thus overcoming mechanical barriers and cultural/behavioural barriers by avoiding boring, repetitious work which can lead to impaired performance.

Segregation on Site Options
Segregated skips can be provided to reflect particular waste streams or the phase of the project, which will have characteristic waste streams.  Segregation at source minimise the resources required, in terms of time required to sort skips and to categories the range of waste type in such general waster skips.Mechanical barriers to be overcome include space constraints on an active site.  Cultural/behavioural barriers, which could result in cross contamination (i.e. worker disposing of paint to a waste timber skip - all this waste is them considered to be hazardous, with disposal and cost implications).  Such cost impacts must be avoided where possible to ensure site managers do not loose interest and revert back to the contemporary system where general skips are used on-site to manage waste.

Please refer to the SECBE report entitled Waste Management Programme Development of a Real-time Data System for more detail on the concept of real time data systems, managing by variance and segregation on-site.

Waste Management Hierarchy
In managing waste, each company must have due regard to the waste management hierarchy: Reduce, Re-use, Recover and Recycle.  It is also important that attainable targets are set for each site and that the necessary resources (i.e. segregated skips, nominated on-site waste management representative) are made available  and that appropriate training and education programmes developed and implemented.  This is critical in terms of overcoming both mechanical and cultural/behavioural barriers to waste data collection.

 

Key Recommendations include:

 

Conclusions and recommendations for further work

Conclusions
Research carried out in developing this report, which addresses the cultural/behavioural and mechanical barriers to data collection, included a review of the success/failures of a waste audit tool (BRE SMARTStart), used as part of a wider waste management pilot study run by SECBE.   Those involved in the project including builders, waste contractors and consultants were interviewed to get site level feedback on the practicalities on the SMARTStart tool specifically, and waste audit tools generally.  The review also included research into the broader, more general mechanical and cultural/behavioural barriers to data collection.  Behaviour models have also been suggested, to help conceptualise peoples decision making process, important when considering appropriate initiatives - whether top-down or bottom-up, which help to push forward the sustainable construction waste agenda. 

Key Conclusions included:

  • It is important, to manage the expectations of all parties concerned including regulators and the construction sector that "sustainable construction" can not be achieved through a "step change" process. Gradual improvements through the adoption of initiatives such as the SMARTStart and other waste audit tools represent a first step and will increase awareness of waste management issues and foster innovation
  • Meaningful and committed partnerships with suppliers, regulators and waste management companies is critical in trying to find a sustainable solution to waste management
  • The adoption of the Pilot Study waste audit tool encountered a number of mechanical barriers to successful adoption. These included:
  • Waste categories were not prescriptive enough
  • Lack of agreed reporting metrics and assessment methodology which can lead result in inaccuracies;
  • Skip assessments are laborious and time consuming
  • A key benefit of the SmartStart system was that it increased awareness of waste issues on-site, facilitates a more analytical approach to waste management and is a useful tool in motivating subcontractors to be more waste conscious;
  • There is general, sector wide interest in the development and adoption of a more sustainable way to manage waste - and a waste audit tool is critical to this end. Therefore it is important that organisations such as SEEDA, SECBE or BRE develop improved and better focused approach to waste management, alone or in consultation.
  • The inclusion of the use of managing by variance and working with the expertise of the users, and the use of segregated skips will likely will help to ensure that certain mechanical barriers can be overcome
  • Training, education, management buy-in will all help to overcome the quite significant cultural/behavioural barriers sustainable waste management

Recommendations for Further Work
The recommendations from this review are for SECBE and SEEDA to progress to a site based study to test the conclusions from this review.  The key tasks would be:

  • Further development of the Rational Choice Model and the Attitude Model so that rather than being generic, high level rule of thumb models, they will more closely reflect the South East region. This is particularly important given the increased demand for workers from across Europe and Asia, thereby changing the cultural (ethno-lingual) profile of the construction industry which one hopes to change, adopting a more sustainable approach to waste management.
  • Additional study to investigate further the mechanical barriers to data collection, appropriate reporting metrics and waste categories.